The Ertebølle Fisheries of Denmark, 5400-4000 B.C
Transcript of The Ertebølle Fisheries of Denmark, 5400-4000 B.C
The Ertebølle Fisheries of Denmark, 5400-4000 B.C.
by
Kenneth C. Ritchie
A dissertation submitted in partial fulfillment of the requirements for the
degree of
Doctor of Philosophy
(Anthropology)
at the
University of Wisconsin – Madison
2010
The Ertebølle Fisheries of Denmark, 5400-4000 B.C.
submitted to the Graduate School of the University of Wisconsin-Madison
in partial fulfillment of the requirements for the degree of Doctor of
Philosophy
By
Kenneth C. Ritchie
Date of final oral examination: April 12, 2010
Month and year degree to be awarded: May 2010
The dissertation is approved by the following members of the Final Oral
Committee:
T. Douglas Price, Professor of Anthropology, Chair
Jonathan Mark Kenoyer, Professor of Anthropology
Sissel Schroeder, Associate Professor of Anthropology
Larry Nesper, Associate Professor of Anthropology
William Aylward, Associate Professor of Classics
Table of Contents
1. Introduction
1.1. Problem statement 10
1.2. Project results 11
2. Background
2.1. History of Ertebølle research in Denmark 16
2.2. The Ertebølle period in Denmark 19
2.2.1. Chronology 20
2.2.2. Settlement 22
2.2.3. Subsistence 23
2.2.4. Fishing technology 24
2.2.5. Other technology 31
2.2.6. Fishing before and after the Ertebølle period 34
2.2.7. Mesolithic fishing in other parts of Europe 36
2.3. Bone isotope studies of diet 42
2.4. Theoretical basis 49
2.5. Zooarchaeological quantification 60
3. Creating the Record
3.1. Deposition, preservation and recovery 66
3.1.1. Initial deposition 66
3.1.2. Post-depositional events 69
3.1.3. Excavation 72
3.2. Laboratory analysis 74
4. Materials
4.1. Sites analyzed for this project 78
4.1.1. Asnæs Havnemark 78
4.1.2. Dragsholm and Bøgebjerg 82
4.1.3. Fårevejle 88
4.1.4. Havnø 91
4.1.5. Jesholm I 92
4.1.6. Lollikhuse 93
4.1.7. Nederst 94
4.2. Sites from the literature 97
5. Results
5.1. Recovery and preservation 108
5.1.1. Differential recovery 108
5.1.2. Differential preservation 119
5.2. Intra-site variability 141
5.3. Regional differences 168
6. Discussion
6.1. The individual sites 178
6.2. Fishing technology 187
6.3. Seasonality 196
6.4. The social lives of fishing foragers 204
7. Conclusions and Future Opportunities for Research
7.1. Conclusions 207
7.2. Future research opportunities 210
8. Acknowledgements 212
9. Works cited 215
Appendix I: Notes on fish taxonomy and identification 242
Appendix II: Comparative collection prepared for the project 249
Appendix III: Summary data for analyzed fish assemblages 251
Appendix IV: Complete notes for analyzed assemblages 260
List of Figures
Figure
1. Map of Denmark with selected sites
2. An overview of Paleolithic/Mesolithic chronology
3. Bone harpoon
4. Leister reconstruction
5. Fishhooks from Nederst
6. Fishhooks from Asnæs Havnemark
7. Net float
8. Fish trap
9. Modern dugout
10. Tybrind Vig paddle
11. Core and flake axes from Dragsholm
12. Ground stone axe from Dragsholm
13. Bone tools from Dragsholm
14. Ertebølle pottery
15. Diet breadth model
16. High search/pursuit cost ratio
17. High pursuit/search cost ratio
18. Effect of changes in search costs
19. Effect of changes in pursuit costs
20. Correlation between NTAXA and NISP
21. Anguillidae ceratohyal measurement
22. Gadidae otolith measurement
23. Anguillidae cleithrum measurement
24. Vertebra measurement
25. Excavations at Asnæs Havnemark
26. Trench 3 at Asnæs Havnemark
27. Dragsholm and Bøgebjerg excavations
28. North wall of Trench 11 displaying clear stratigraphy
29. Excavations at Fårevejle
30. Horizontal distribution of fish remains in Trench 1 at Fårevejle
31. Western wall of Trench 1 at Fårevejle
32. Excavation in Trench 1 at Fårevejle
33. Excavation at Havnø in 2006
34. Almost underwater archaeology at Jesholm I
35. Human burial from Nederst
36. Dog burial from Nederst
37. Processing matrix samples through nested geologic screens
38. Relative percentages of fish types by screen size at Dragsholm
39. Relative percentages of fish types by screen size at Asnæs Havnemark
40. Relative percentages of fish types by screen size at Nederst
41. Relative abundance by level for Trench 11 at Dragsholm
42. Cod lengths Level 8 Dragsholm
43. Cod lengths Level 7C Dragsholm
44. Gadid lengths Level 8 Dragsholm
45. Gadid lengths Level 7C Dragsholm
46. Gadid lengths Level 7B Dragsholm
47. Gadid lengths from all levels combined
48. Flatfish sizes from Dragsholm (all levels)
49. Flatfish sizes from Level 7B Dragsholm
50. Flatfish sizes from Level 7CDragsholm
51. Flatfish sizes from Level 8 Dragsholm
52. Relative abundance by level for Trench 1 at Fårevejle
53. Relative abundance by level for Trenches 2 and 3 at Bøgebjerg
54. Relative abundance by level at Asnæs Havnemark
55. Cod sizes from all levels Asnæs Havnemark
56. Cod sizes from the Culture Layer Asnæs Havnemark
57. Cod sizes from the Shell Layer Asnæs Havnemark
58. Cod sizes from the Brown Surface Asnæs Havnemark
59. Cod sizes from the Grey Layer Asnæs Havnemark
60. Anguillidae size distribution at Asnæs Havnemark
61. Relative abundance by level at Lollikhuse
62. Relative abundance by level at Nederst skalydynge I
63. Relative abundance for Nederst skaldynge II
64. Relative abundance within Level 10 at Nederst
65. Relative abundance within Level 13 at Nederst
66. Relative abundance within Level 20 at Nederst
67. Relative abundance within the Shell at Nederst
68. Relative abundance within the Culture layer at Asnæs Havnemark
69. Relative abundance within Layer 7B at Dragsholm
70. Relative abundance within Layer 7C at Dragsholm
71. Relative abundance within Layer 8 at Dragsholm
72. Anguillidae size distribution at Nederst
73. Pleuronectidae size distribution at Nederst
74. Relative abundance for two squares at Norsminde
75. Relative abundance for three samples in the N-column at Ertebølle
76. Relative abundance (minus Syngnathidae) for three samples in the N-column at
Ertebølle
77. Percentages of fish by site
78. Relative abundance of Gadidae (larger fish) versus mesh-size
79. Relative abundance of Gadidae (larger fish) versus mesh-size using screen-test
results
80. NTAXA versus (Log) NISP for selected sites
81. Plot of Shannon index values
82. Plot of Shannon index values versus (Log) NISP
83. Hypothesized seasonal resource availability
List of Tables
Table
1. Key to fish families
2. Distribution of fish remains at Asnæs Havnemark
3. Distribution of fish remains at Dragsholm
4. Distribution of fish remains at Bøgebjerg
5. Distribution of fish remains at Fårevejle
6. Context information for samples from skaldynge II at Nederst
7. Context information for samples from skaldynge I at Nederst
8. Distribution of fish remains for skaldynge I at Nederst
9. Distribution of fish remains at Smakkerup Huse
10. Other Late Mesolithic sites with fish bones
11. Identified fish remains from the screen-test samples at Asnæs Havnemark
12. Identified fish remains from the screen-test samples at Dragsholm
13. Comparison by screen size for the screen test samples from Dragsholm
14. Comparison by screen size for the screen test samples from Asnæs Havnemark
15. Comparison by screen size for the screen test samples from Nederst
16. Results from Asnæs Havnemark by excavator
17. Results from Dragsholm by excavator
18. Results from Fårevejle by excavator
19. Weights from Asnæs Havnemark
20. Weights from Fårevejle
21. Weights from Bøgebjerg
22. Weights from Dragsholm
23. Examination of degree of completeness of vertebrae at Asnæs Havnemark
24. Examination of degree of completeness of vertebrae at Nederst
25. Examination of degree of completeness of vertebrae at Dragsholm
26. Expected versus actual presence Gadidae from Asnæs Havnemark
27. Expected versus actual presence Anguillidae from Asnæs Havnemark
28. Expected versus actual presence Pleuronectidae from Asnæs Havnemark
29. Expected versus actual presence of Gadidae elements from Dragsholm
30. Expected versus actual presence of Gadidae by level from Dragsholm
31. Expected versus actual presence of Gadidae elements from Dragsholm, otoliths
omitted
32. Expected versus actual presence of Pleuronectidae elements from Dragsholm
33. Expected versus actual presence of Pleuronectidae by level from Dragsholm
34. Expected versus actual presence of Anguillidae elements from Dragsholm
35. Expected versus actual presence of Gadidae elements from Fårevejle
36. Expected versus actual presence of Pleuronectidae elements from Fårevejle
37. Expected versus actual presence of Anguillidae elements from Fårevejle
38. Expected versus actual presence of Gadidae elements from Bøgebjerg
39. Expected versus actual presence of Pleuronectidae elements from Bøgebjerg
40. Expected versus actual presence of Gadidae elements from Nederst
41. Expected versus actual presence of Pleuronectidae elements from Nederst
42. Expected versus actual presence of Anguillidae elements from Nederst
43. Expected versus actual presence of Trachinidae elements from Nederst
44. Expected versus actual presence of Gadidae elements from Lollikhuse
45. Combined actual versus expected percentage values for Gadidae
46. Combined actual versus expected percentage values for Pleuronectidae
47. Combined actual versus expected percentage values for Anguillidae
48. Vertebra count by level for Trench 11 at Dragsholm
49. Relative abundance by level for Trench 11 at Dragsholm
50. Gadid sizes from Dragsholm
51. Pleuronectidae sizes from Dragsholm
52. Vertebra count by level for Trench 1 at Fårevejle
53. Relative abundance by level for Trench 1 at Fårevejle
54. Cod sizes at Fårevejle based on otoliths
55. Pleuronectidae sizes at Fårevejle based on first vertebrae
56. Vertebra count by level for Trenches 2 and 3 at Bøgebjerg
57. Relative abundance by level for Trenches 2 and 3 at Bøgebjerg
58. Vertebra count by level at Asnæs Havnemark
59. Relative abundance by level at Asnæs Havnemark
60. Cod sizes at Asnæs Havnemark based on otoliths
61. Anguillidae sizes by level at Asnæs Havnemark based on ceratohyal
62. Vertebra counts by level at Lollikhuse
63. Relative abundance by level at Lollikhuse
64. Vertebra counts by level at Nederst skaldynge I
65. Relative abundance by level at Nederst skaldynge I
66. Anguillidae sizes by level at Nederst
67. Pleuronectidae sizes by level at Nederst
68. Percentage of fish by family for sites on Jutland
69. Percentage of fish by family for sites on Zealand
70. NISP and NTAXA for selected sites
71. NTAXA for Ertebølle sites
72. Occurrence of Trachinidae
73. Ubiquity of Trachinidae at six sites
74. Evaluating technology and specialization versus generalization
75. Occurrence of Scombridae
76. Occurrence of Belonidae
77. Seasonality based on otolith growth rings for Nederst
78. Seasonality based on otolith growth rings for Norsminde
79. Seasonality of catch from 1885 fishery data (cod, flatfish, mackerel and garfish)
80. Seasonality of catch from 1885 fishery data (herring and eel)
1. Introduction
1.1 Problem statement
The Late Mesolithic Ertebølle period in Denmark (ca. 5400-4000 B.C.) has
attracted the interest of archaeologists and other researchers for a number of reasons
including: excellent conditions of preservation for organic materials that provide almost
unparalleled information on both past human societies and environmental conditions; an
archaeological record interpreted as showing a sedentary, complex society based on a
hunter-gatherer economy; and the continuation of this hunter-gatherer economy in
close proximity to nearby agriculturists for at least a thousand years before a sudden
transformation of society that rapidly led to the construction of monumental structures
that are some of the most impressive records of Early Neolithic cultures known in
Europe. One aspect of the Ertebølle culture that must be recognized is that it was
primarily a coastal adaptation with a focus on marine resources, especially fish.
Evidence for this includes site locations, animal remains recovered from sites,
technology (e.g., dugout canoes, fish hooks, harpoons, leisters, fish fences/traps) and
dietary studies using isotopic analyses of human (and sometimes dog) bones
(Andersen 1995, Enghoff 1994a, Fischer 1993, Fischer et al. 2007, Noe-Nygaard 1988,
Pedersen 1995, Richards et al. 2003, Tauber 1981). Because of the importance of fish
during the Ertebølle period, the recovery and analysis of archaeological fish remains
provides an excellent source of information about many aspects of culture. Despite the
exemplary archaeological record and long history of research, a number of questions
regarding the fishery of the Ertebølle period remain. While the types of fish that were
exploited are known, their relative contributions to subsistence, the seasonality of
exploitation and even the preferred methods of procurement are generally not well
understood. Compounding these knowledge lacunae, the information that is available
has often been generalized without due consideration for regional and temporal
differences. Finally, while the settlement pattern of the Ertebølle period has often been
described as mostly sedentary (e.g., Madsen et al. 1900, Price 2000, Rowley-Conwy
1983), markers for occupation of sites in every season and other evidence supporting
this claim remain elusive. This study of archaeological fish remains combines source
criticism (i.e., review of excavation and analysis methodology to assess the quality of
the data) with new laboratory analyses of fish bones to address these questions.
1.2 Project results
Identification of over 110,000 fish bones from 8 sites (Asnæs Havnemark,
Bøgebjerg, Dragsholm, Fårevejle, Havnø, Jesholm I, Lollikhuse and Nederst) is a
significant contribution from this study to our understanding of subsistence during the
Ertebølle period. Combined with previously published results, ca. 222,000 fish bones
from dozens of sites constitute an enormous data set available for investigations (see
map in Figure 1 for site locations). Consideration of how these data are converted into
archaeological interpretations is an important topic that must be explicitly examined
(and is, see below), but for now it is sufficient to report two major findings from this
project: fishing activities were more specialized in eastern than in western Denmark and
there is evidence that the fishery was considerably more dynamic than previously
acknowledged. Most sites in eastern Denmark display a marked dominance of fish from
the cod family (Gadidae, see Table 1 for fish families) in the recovered remains, while in
western Denmark the most common fish varies between sites and some sites (e.g.,
Bjørnsholm and Nederst) show a highly diversified fishery. Furthermore, where it is
possible to separate site deposits chronologically (especially Dragsholm, but also other
sites), there are often diachronic changes in the relative percentage of fishes and/or the
sizes of the fish most commonly captured. Examining changes through time during the
Ertebølle period by comparing different sites is complicated by dating issues, but even
here there appears to be at least some support for variability.
Questions about the comparability of data from different sites are
addressed by this project and represent an important advance in studies of Ertebølle
subsistence. Differential recovery is an issue of fundamental importance in the creation
of any excavated data set, but its full impact has seldom been recognized or addressed
with regard to Mesolithic fish remains. Many of the Ertebølle sites that have produced
fish remains were excavated without the use of screens to aid in the recovery of smaller
specimens. For this reason, they generally have fish bone assemblages with few
specimens and the representativeness of the samples is very much in question. These
sites are included here for the sake of completeness, but they do not form part of the
dataset that is used for quantitative analysis. Even where screens were used, the mesh
size of the screens is not always the same – raising doubts as to whether any
differences noted between sites are an artifact of different recovery techniques or real
variability in human activities. Experiments with recovery using various mesh-size
screens at three sites (Asnæs Havnemark, Dragsholm and Nederst) allow evaluation of
the impact of different methods of excavation on fish assemblages from Ertebølle sites.
Not surprisingly, smaller mesh-sizes lead to the recovery of smaller fish remains. Since
certain types of fish almost never grow to large size (e.g., herring and eel) these fishes
can contribute a significant percentage of the overall assemblage only on those sites
that were excavated with smaller mesh-size screens. This is especially important in light
of the fact that larger (3.5-4 mm) mesh screens were used on excavations in eastern
Denmark and smaller (0.5-2 mm) mesh was used on most excavations in western
Denmark. A second aspect of differential recovery that has not previously been
recognized in connection with fish bones from Ertebølle sites is the impact of excavator
bias. By comparing the results from different people at the same site, using the same
excavation techniques, it can be shown that the skill and experience of the excavator
affects the recovered assemblage. In general, better excavation technique results in the
recovery of a larger diversity of skeletal elements and more specimens from smaller fish
species.
Another important finding of this study is the importance of considering
intra-site variation in fish assemblages. Previous discussions of fish remains from
Ertebølle sites have treated the materials as if they came from undifferentiated deposits.
While summary data for entire sites are presented here, investigation of variation within
the deposits is also highlighted. With this approach, differences in fishing can be
observed either vertically (e.g., Dragsholm, Bøgebjerg and Fårevejle) or horizontally
(e.g., Norsminde and Nederst). Interpretation of the precise causes of the variability
requires consideration of site-specific contextual information, but recognizing Ertebølle
fisheries as dynamic rather than static phenomena presents interesting interpretative
opportunities. The importance of these findings will undoubtedly lead to more
comprehensive analysis and publication of results from other sites in the future.
Finally, creating faunal data is only significant for archaeology in so far as it
advances understanding of past human culture. To date, a failure to come to grips with
the methodological and theoretical challenges associated with interpreting fish bone
data has limited conclusions to post hoc, qualitative statements about the nature of
fishing. Diet breadth modeling introduced from the evolutionary framework of behavioral
ecology is used to generate predictions about why assemblages differ from each other.
Recognizing the factors that shift foraging behaviors between more generalized or
specialized strategies and the effect this has on other aspects of culture allows fish
bone data to contribute to cultural interpretations. While still incorporating environmental
variables, the effects of different technologies (fishing tools and watercraft) on foraging
decisions are emphasized by this approach. The seasonal subsistence cycle,
territoriality, and group social organization are other topics addressed by the results.
Ending the current torpor in the study of Ertebølle fishing through firmly grounded,
quantitative analyses of the rich data set that is available provides fresh insights into the
Late Mesolithic period in Denmark.
Family Examples English Dansk
Ammodytidae Hyperoplus/Ammodytes Sand-eel Tobis
Anguillidae Anguilla anguilla Eel Ål
Belonidae Belone belone Garfish Hornfisk
Callionymidae Callionymus lyra Dragonet Stribet fløjfisk
Carangidae Trachurus trachurus Atlantic horse mackerel Hestemakrel
Clupeidae Clupea harengus, Alosa sp. Herring, shad Sild, majfisk
Cottidae Myoxocephalus scorpius Bull-rout Almindelig ulk
Cyprinidae
Tinca tinca, Rutilus rutilus, Abramis
abramis
Tench, roach, common
bream Suder, skalle, brasen
Dasyatidae Dasyatis pastinaca Common stingray Pilrokke
Engraulidae Engraulis engrasicholus Anchovy Ansjos
Esocidae Esox lucius Pike Gedde
Gadidae
Gadus morhua, Melanogrammus
aeglefinus, Pollachius virens Cod, haddock, saithe Torsk, kuller, sej
Gasterosteidae Gasterosteus aculeatus 3-spined stickleback Trepigget hundestejle
Gobiidae Gobius niger Black goby Sort kutling
Lamnidae Lamna nasus Porbeagle Sildehaj
Moronidae Dicentrarchus labrax European sea bass Havbars
Percidae Perca fluviatilis, Sander lucioperca Perch, pike-perch Aborre, sandart
Pleuronectidae
Pleuronectes platessa, Platichthys flesus,
Limanda limanda Plaice, flounder, dab Rødspætte, skrubbe, ising
Rajidae Raja clavata Thornback ray Sømrokke
Salmonidae Salmo trutta, Coregonus sp., Salmo salar Trout, whitefish, salmon Ørred, laks, helt
Scombridae Scomber scombrus Atlantic mackerel Makrel
Scophthalmidae Psetta maxima, Scophthalmus rhombus Turbot, brill Pighvarre, slethvarre
Sparidae Spondyliosoma cantharus Black sea bream Havrude
Squalidae Squalus acanthias Spurdog Pighaj
Syngnathidae Syngnathus sp. Pipefish Tangnål
Trachinidae Trachinus draco Greater weever Almindelig fjæsing
Triakidae Galeorhinus galeus, Mustelus sp. Topeshark, smoothhound Gråhaj, glathaj
Triglidae Trigla lucerna, Eutrigla gurnardus Tub gurnard, grey gurnard Rød knurhane, grå knurhane
Xiphiidae Xiphias gladius Swordfish Sværdfisk
Zoarcidae Zoarces viviparus Viviparous eelpout Ålekvabbe
Table 1: Key to fish families found in Danish Mesolithic assemblages (see Appendix I for
more information).
Figure 1: Map of Denmark with selected sites from the text. (Numbers 1-7 show sites
that were analyzed for this project.) 1:Havnø 2:Jesholm I 3:Nederst 4:Asnæs
Havnemark 5:Bøgebjerg and Dragsholm 6:Fårevejle 7:Lollikhuse 8:Yderhede and
Østenkær 9:Bjørnsholm and Ertebølle 10:Lystrup Enge 11:Norsminde 12:Tybrind Vig
and Ronæs Skov 13:Møllegabet II 14:Smakkerup Huse 15:Vedbæk complex of sites.
2. Background
2.1 History of Ertebølle Research in Denmark
Stone Age archaeology can be said to have begun in Denmark, when
Christian Jürgensen Thomsen was hired to catalog and organize the collections of the
Danish Royal Commission for the Collection and Preservation of Antiquities (forerunner
to the National Museum) and created the three-age system of an early Stone Age,
intermediate Bronze Age and later Iron Age (Thomsen 1836). Although research on
prehistoric archaeology had begun earlier, it was the publication of his scheme that truly
began the process of dividing prehistory into sequential periods, defined on aspects of
material culture. Important as this early step was, it was left to subsequent researchers
to develop a modern, scientific archaeology (see Fischer and Kristiansen 2002 for a
more complete discussion of the development of Danish Stone Age archaeology,
including English translations of some of the seminal writings by important figures. The
information in this section is based on this source, except where specifically noted
otherwise). While recognizing the significance of the three-age system for organizing
archaeological information, it is also appropriate to mention a negative effect of its
introduction: the beginnings of a segmented approach to prehistory that led to an
overemphasis on typological traits and the boundaries between periods. It would take
many decades before archaeologists shifted their attention to the processes that
created the cultural variation revealed by the differences in material culture.
The formation of the Lejre Committee, later known as the First Kitchen
Midden Commission, marked a crucial stage for archaeology, defining it as an
independent research discipline and instituting the practice of interdisciplinary research
involving branches of the natural sciences. In the 1840-60s, the zoologist Johannes
Japetus Smith Steenstrup, geologist Johan Georg Forchhammer and archaeologist
Jens Jacob Asmussen Worsaae examined several shell midden sites in Denmark to
answer the question of whether they were natural or man-made occurrences. In addition
to concluding that the sites were indeed, anthropogenic, these investigations also set
new standards for excavation and documentation of the results. Equally significant was
the realization by Worsaae that the Stone Age could be further subdivided into an
earlier period (represented by the kitchen middens) and a later period (known from the
megalithic monuments and related materials). Steenstrup vehemently opposed this
division and publicly criticized Worsaae’s conclusions. Time has proven Worsaae’s
interpretation to be sound, but it is interesting that much of Steenstrup’s mistrust of it
was based on opposition to the concept of a progression from a simple to a more
advanced state – a critique of unilineal cultural evolution that would not sound out of
place in some theoretical discussions today.
In the latter part of the 19th century, after a renewed series of disputes
between professional archaeologists and others with an interest in the topic over the
subdivision of the Stone Age, a Second Kitchen Midden Committee was established
under the leadership of Sophus Müller. Some previously excavated shell midden sites
were revisited and new locations were also tested. The results were published in 1900
in Affaldsdynger fra Stenalderen I Danmark: undersøgte for Nationalmuseet, a volume
that remains an important reference work for Stone Age research over a century later
(Madsen et al. 1900). While confirming Worsaae’s interpretation, the investigations also
resulted in the recognition that some of the middens contained materials from both
earlier and later periods. These excavations also established the methodology of
digging in square meter units, subdivided into 10-20 cm levels, and rigorously tabulating
the artifacts recovered from each context. Unfortunately, Müller’s autocratic personality
caused many natural scientists to leave the National Museum, leaving it reliant on
external experts to perform this type of work.
This deficit in expertise continued until new leadership came to the National
Museum in the form of Therkel Mathiassen in the 1930s. Recognizing the importance of
the new science of palynology, he instigated a series of investigations specifically
focused on bog sites where ancient pollen can be preserved. This ultimately led to the
return of the natural sciences to the National Museum in the form of the bog-geological
laboratory. The other important impact of palynology on archaeology was the
introduction of an empirically-based ecological perspective to the study of prehistory.
Another contribution by Mathiassen was the initiation of an ambitious series of surveys
throughout Denmark aimed to expand the number of known sites to allow study of
settlement patterns. The results of surveys along the major inland waterways in central
Jutland led Mathiassen to define a distinctive inland Mesolithic culture named after one
of the rivers (Gudenå) along which it occurred, beginning a long-running debate over
whether inland and coastal sites were used by the same people or represented distinct
adaptations (Mathiassen 1937). The Third Kitchen Midden Committee was formed
during this period, with its most important product being the 1942 publication of the
results of excavations on Djursland peninsula, especially at Dyrholmen. These results
linked archaeological cultural units with changes in vegetation and sea-level and also
led to further subdivision of both the early and the later periods of the Stone Age. The
ecological approach to archaeology institutionalized the inclusion of natural science
research into archaeological investigations, while leading to some tension between
interpretations offered by the proponents of the various disciplines involved in the
research. Attempts to resolve this conflict by the integration of archaeological and
natural science perspectives, most notably by the research of Jørgen Troels-Smith in
the Åmose of Zealand, met with only limited success, and a period of limited progress in
Stone Age research followed.
The 1960s and 1970s saw a return to vigorous investigation of the Danish
Stone Age that has continued to the present day, in part inspired by researchers and
theoretical perspectives imported from abroad. A focus on economic processes inspired
new research into the Ertebølle and subsequent Neolithic periods through survey,
excavation, floral and faunal analyses, and archaeometry. Although some fish bones
had been identified from excavations as early as the 19th century, Inge Bødker Enghoff
expanded the number of fish bones identified from Ertebølle sites by an order of
magnitude and publicized the importance of heretofore discounted smaller fish species.
Excavation (and re-excavation) of shell midden sites by Søren H. Andersen and Erik
Johansen constituted a ‘Fourth Kitchen Midden Committee’ (Kristiansen 2002:25). As a
result of the new activity, ideas about mobility, settlement, subsistence and social
components of Stone Age cultures were reevaluated and, where necessary,
reformulated. One major advance that occurred was the recognition that the previously
discussed distinctive ‘Gudenå culture’ that existed along the inland riverways of Jutland
was in fact the result of repeated use of the same localities by multiple Mesolithic
cultures – including Ertebølle (Andersen 1971a). Another significant development was
the advent of underwater surveys and excavations of submerged Ertebølle sites (e.g.,
Fischer 1993). This has proven especially important for understanding fishing
technology through the recovery of organic artifacts that are only rarely recovered from
terrestrial sites (Andersen 1985). New survey projects on Zealand, initiated by T.
Douglas Price, focused on regional settlement systems.
This dynamic period of research continues, with insights accumulating
apace. New finds emerge from every season of excavation and new approaches to the
existing data alter our understanding of the period. It is now appropriate give a brief
overview of the archaeological evidence in order to understand the current state of
knowledge about the Ertebølle period.
2.2 The Ertebølle period in Denmark
Ertebølle is the final hunter-gatherer tradition in areas of modern day
Denmark, Southern Sweden and Northern Germany, dated to ca. 5400-4000 B.C. in
Denmark. The Ertebølle replaces the Kongemose culture in the middle of the Atlantic
climactic period, a time of complex interaction between isostasy and eustasy that made
for a dynamic coastal zone. During the Ertebølle period people experienced repeated
episodes of the sea intruding upon the land and then retreating; changes that were at
times so rapid that they would have been noticeable in an individual’s lifetime (C.
Christensen 1995, Donner 1995, Hede 2003, Schmölcke et al. 2006). On land,
Denmark was largely covered by climax forests of lime, oak and hazel (Aaby 1993).
The development of the Ertebølle culture from the preceding Kongemose
was influenced by changes in environmental conditions, but it was also at least partly in
response to the spread of Linearbandkeramik (LBK) farming groups through central
Europe around 5500 B.C. Evidence for contact with the subsequent farming groups that
emerged around 5000 B.C. (e.g., Rössen, Michelberg) includes T-shaped antler axes,
bone combs and rings, Danubian shaft-hole axes and (after 4600 B.C.) pottery (Arias
1999, Fischer 2003, Klassen 2002, Petersen 1984).
Ertebølle culture is not completely uniform throughout Denmark and eastern
and western groups can be distinguished based on the distribution of T-shaped antler
axes, bone combs and rings, Danubian shaft-hole axes, bone harpoon styles, bird-bone
points and pottery form and decoration (Klassen 2002, Petersen 1984, Prangsgaard
1992). The dividing line seems to be at the Great Belt channel separating Funen and
Zealand, although the demonstrated ability of Ertebølle people to cross the seas
suggests that this border should not be considered impermeable. Smaller regional
groupings can also be discerned (see below).
2.2.1 Chronology
The Ertebølle period in Denmark stretches from approximately 5400-4000
cal B.C., corresponding to about the second half of the Atlantic climatic period (see
Figure 2 for an overview of Paleolithic/Mesolithic chronology for Denmark, including
cultural, geological and ecological changes). The Ertebølle period is often divided into
early, middle and late phases (respectively labeled Trylleskov, Stationsvej and
Ålekistebro in the East), although previously (especially in western Denmark) a
dichotomous division between aceramic and ceramic periods (Dyrholmen I and
Dyrholmen II) was preferred. In addition to pottery, changes in blade production
techniques, projectile points, stone axes and other flint tool types are used to define the
sub-phases (Petersen 1984).
2.2.2 Settlement
The Ertebølle culture is best known from the famous shellmiddens
(køkkenmøddinger in Danish) including the eponymous site on the Limfjord in northern
Jutland, but the shellmiddens are only known from northern and northeastern Denmark
– and even here other sites exist without the shell deposits (Andersen 2008). While
primarily a coastal culture, inland sites are also known – especially near rivers and
lakes. Many sites appear to have been occupied year-round, but special purpose sites
are also known (e.g., Agernæs, Aggersund and Ringkloster) (Andersen 1991, Møhl
1978, Richter and Noe-Nygaard 2003). The remains of domestic features are not
common on most sites; those found generally consist of pits and hearths built of stone
or clay, but the impoverished record may be misleading as other constructions of
perishable materials could easily disappear without leaving a trace. Three Danish sites
have features that have been interpreted as the remains of houses: Lollikhuse, Nivå and
Møllegabet (O. Jensen 2001, Skaarup 1995, Sørensen 1992). The structures were
slightly built and modestly sized (from ca. 2x3 m to 4x6 m), with room for perhaps one
or two families.
Coastal sites were usually placed at locations with good fishing possibilities,
especially at the mouths of estuaries or centrally located within them (Andersen 2007,
Fischer 1993, 2007). Preference seems to have been given to locations that faced onto
at least partially sheltered waters (not surprising, given the limited ability of dugout
canoes to manage in rough seas) although exposed coasts were also used. In his
analysis of shell midden placement, Andersen has noted that the largest middens are
spaced 9-15 km apart and often surrounded by smaller satellite middens (2007:34). Axe
styles have been used as markers of group territories on Zealand, with an estimate of 6-
8 groups for the whole of the island (Petersen 1984). Clusters of human burials (e.g.,
Nederst, Bøgebakken) have been interpreted as cemeteries (Larsson 1990, Price et al.
1995), surely a marker of strong attachment to a territory, but other researchers are not
convinced of the formal cemetery status (Meiklejohn et al. 1998). Recent publication of
evidence for cremation burials highlights the complex nature of Mesolithic mortuary
ritual (Petersen and Meiklejohn 2003).
2.2.3 Subsistence
The only domesticates unequivocally possessed by people of the Ertebølle
period were dogs, and while undoubtedly eaten on some occasions, the numerous dog
burials suggest they were more than just a food source. The vast majority of foods had
to have come from wild animals and plants.
Fish remains numbering in the millions have been encountered during
excavations on Ertebølle sites and shellfish are found in similarly astounding quantities
at some sites (Andersen 2008a). Initially characterized as a cod and flounder focused
fishery (Clark 1975), later researchers have emphasized the role of eel and other fishes
(Enghoff 1986, 1991, Smart 2003). Evidence from this project demonstrates the veracity
of the suggestion that fisheries varied regionally and an all-inclusive description of an
Ertebølle fishery in Denmark is not warranted (Enghoff 1994a:89). Fishing was not
restricted to the coast during this period, as freshwater fish are represented in some
assemblages even at coastal sites, but considering the totality of identified specimens
from Ertebølle sites, marine or brackish-water fish have been recovered in much greater
numbers (Enghoff 1986). Inland sites have generally produced much smaller fish bone
assemblages than coastal ones and some inland sites even have bones from fully
marine species (Enghoff 1994a). Finally, it should be noted that in addition to their role
as food, fish could sometimes provide raw materials for tools (Noe-Nygaard 1971).
Mammals, both marine and terrestrial, also played an important role in
subsistence. Roe deer (Capreolus capreolus), red deer (Cervus elaphus) and wild pig
(Sus scrofa) were the most important food species, but a wide variety of other animals
are found in faunal assemblages (e.g., Bratlund 1991, Enghoff 2009, Hede 2005,
Richter and Noe-Nygaard 2003). Some animals were probably targeted more for their
furs than their food value (Richter 2005, Trolle-Lassen 1987), and widespread use of
antler for tools may have been part of the reason for cervid hunting. A noticeable
difference between eastern and western Denmark is the paucity of aurochs (Bos
primigenius) and moose (Alces alces) specimens in eastern assemblages during the
Ertebølle period, as these animals are believed to have already been extinct on the
islands by this time (Aaris-Sørensen 1998). Birds (especially waterfowl) were targeted
for food and may have also been hunted as a source of raw materials; the more fragile
nature of their bones may mean they were more important than their representation in
archaeological assemblages suggests (Noe-Nygaard 1987).
The role of plants in Ertebølle subsistence regimes is generally not well
known. Fruits (e.g., apple, hawthorn, raspberries), roots (e.g., sea beets), seeds (e.g.,
floating sweet grass) and other plant parts (e.g., reed stems), have been documented
from a few sites (especially Tybrind Vig, Halsskov and Smakkerup Huse), but even
when present, they are rare, and it is not clear if this is because of
preservation/recovery effects or because they played only a minor role in diets (see
Kubiak-Martens 1999 and 2002, Mason 2005, Perry 2005 for a complete listing of
species identified). Hazelnuts are a notable exception to the dearth of evidence for plant
use, as nutshells are recovered in considerable quantities from many Mesolithic
deposits. They may have been a food source that was easily procured by the young and
old who were not able to participate in other subsistence activities (e.g., hunting and
fishing). Different plant foods are available seasonally from the spring through fall, and
nuts may have been stored as a dietary supplement for the winter (Kubiak-Martens
1999). Considering the diversity of fish, mammals, birds and plants available to the
Ertebølle people, their resource base can be described as a rich one (while not
discounting the episodic shortages that would have inevitably occurred). Faced with
obtaining many different resources, the Ertebølle people developed a toolkit with its own
impressive diversity.
2.2.4 Fishing technology
The tools of the fisherman include both the implements used to capture fish
and the watercraft used to gain access to them or transport the catch back to camp.
Even when fishing is conducted from shore, watercraft greatly expand the number of
locations that can be reached and expand the potential catch (Ames 2002). Capture
technology is often divided into active (requiring participation of a fisherman) and
passive (unattended) methods; although for archaeological purposes this distinction
may be less useful in that many remains (hooks, nets, fences/weirs) could be from
active or passive fishing depending on how they were used (Brinkhuizen 1983, Rostlund
1952, Åhrberg 2007). Nevertheless, the following fishing implements will be presented
in generally descending order from active to passive usage.
Fish spears/leisters and bone harpoons are implements that indisputably
require wielding by a person to function. Ertebølle bone harpoons are the tip of thrusting
weapons presumably designed to detach from the shaft and remain lodged in the prey
while an attached line aids in recovery of the animal (see Figure 3). Harpoons were
likely intended to capture sea mammals such as seals or small whales but could also
have been employed against large fish, especially when they came in to shallow waters
to spawn (e.g., pike). Wooden prongs from leisters are found on many coastal sites and,
“are always numerous on Middle and Late Ertebølle sites with good preservation
conditions for organics,” (Andersen 1995:57). Two different prongs are recognized: a
short version for hard substrates and a longer one for softer substrates (Andersen
1985). A very well-preserved specimen recovered from Næbbet with a hazel shaft and
hawthorn prongs lashed together with vegetable fibers allows reconstruction of their
appearance (see Figure 4) (Skaarup 1995:399). Bone points that are commonly found
on Ertebølle sites have been hypothesized to be fastened in the center of the leister
(Andersen 1995), although this claim is disputed (Pickard and Bonsall 2007:178). The
total time to construct a fish spear is estimated to be less than four hours (Lindström
1996:142).
Figure 3: Bone harpoon (Andersen 1971b). Figure 4: Leister reconstruction
(Skaarup 1983).
Fishhooks are an active fishing method when used in angling and passive
when multiple examples are attached to a long-line that is deployed with floats and
weights and checked periodically. The absence of barbs on most or all Ertebølle
examples argues against their use in a long-line fishery. Until quite recently hooks were
thought to have been carved only from large mammal long bones, but finds of hook
preforms at the Asnæs Havnemark excavation in 2007 show that bird bones (e.g., ulnas
from swans, Cygnus sp.) could also be used (Ulrich Schmölcke personal
communication 2007). Based on experimental work, production time for a single
fishhook is estimated at about one and a half hours (Harm Poulsen personal
communication 2009). It has been suggested that composite hooks of wood and bone
were also used, but the evidence is inconclusive (Jønsson and Pedersen 1983). Hooks
have been recovered in many sizes ranging from ca. 2-5 cm in length and at least two
forms are apparent: a u-shaped bend with long shank variety and a rarer v-shaped
variety where the point extends almost as far up the shank to where the line is attached
(see Figure 5, far left for an example; also Figure 6 third row from the top, third from the
left). Different sizes and shapes of hooks would have been selected depending on the
intended catch. At least 77 hooks or preforms are known from the following Danish
sites:
Ertebølle - 5 (4 from Madsen, 1 from Andersen) (Madsen et al 1900:67-68, Andersen 1986:58) Bjørnsholm – 7 (Andersen 1993:83, Enghoff 1994a:84) Tybrind Vig – 6 (one with line still attached) (Andersen 1985:60-61) Kolind – 2 (1 with barb) (Mathiassen et al 1942:44) Dyrholmen – 1 (Mathiassen et al 1942:44) Nederst – 10 (Enghoff 1994a:84) (but only 6 are listed in case file and photographed) Aggersund – 1 (Andersen 1995:57) Smakkerup Huse – 6 (2 whole and 4 fragments) (Price and Gebauer 2005:117) Dragsholm – minimum 7 Sønderholm – 1 (with barb) (Jønsson and Pedersen 1983:180) Bloksbjerg - 1 (Westerby 1927:102-104) Mejlgård - 1 (Madsen et al 1900:67) Asnæs Havnemark – 31 complete or partial hooks and preforms (see Figure 6) Sølager – 1 (Skaarup 1973)
Ingvorstrup -1 (Niels Axel Boas personal communication2009)
Figure 5: Fishhooks from Nederst (photo courtesy of Niels Axel Boas).
Figure 6: Examples of fishhooks and 6 preforms from Asnæs Havnemark. (Drawn by K. Ritchie)
Nets can be produced in a variety of configurations depending on whether
they are intended to be used actively as seine or dip nets or passively as pound or gill
nets. Fishing with nets would be more or less selective for type of fish depending on the
style. Finds of knotted fibers that have been interpreted as possible portions of fishing
nets are known from Tybrind Vig and the German site of Friesack, but they are too
fragmentary to provide information about how they would have been employed
(Andersen 1985, Gramsch 1987). Stronger evidence for net fishing during the Ertebølle
period comes from finds of net floats (Møllegabet I – Figure 7; Tybrind Vig, Tågerup)
and perforated stones that were likely net sinkers (Vængesø and Kolind I), though the
ways in which the nets were employed is still not apparent (Andersen 1985, Karsten
and Knarrström 2003, Mathiassen 1948, Skaarup 1983). Construction time varies
depending on the overall size of the net and the size of the mesh, but some examples
are estimated to require as many as 2200 hours (Lindström 1996:139).
Figure 7: Net float (Skaarup 1983).
The most passive of the fishing methods for which there is archaeological
evidence from the Ertebølle period are fish fences and traps. While fish fences or weirs
can be used to facilitate spearing or dip netting, this is usually done in rivers (Rostlund
1952). The coastal and lacustrine locations of the Ertebølle finds likely means they were
used in conjunction with basket traps. Neolithic fish fences were often sturdily built and
could be impressively long, but the evidence suggests that Mesolithic constructions
were smaller and less robust (Pedersen 1997). The number of long, straight poles
required for construction of the fences has been construed as evidence for
management (coppicing) of hazel groves to provide raw materials (K. Christensen
1997). Numerous finds of sections of fences and whole or partial basket traps
demonstrate that this method was widely employed during the Mesolithic period,
although whether it was always a mainstay of the fishery as has been claimed is
debatable (Andersen 1995, Fischer 2007, Pedersen 1995, Enghoff 1994a).
Construction of each basket trap may have required 10-15 hours and the fences many
more depending on their height and length (Lindström 1996). Once built however, they
would have provided a relatively high-return on effort during their use-life.
Figure 8: Fish trap (Andersen 1995).
Dugout canoes and paddles can be seen as a part of fishing technology
even if they were not directly used to capture fish. By allowing access to offshore fishing
grounds and expanding the stretch of coastline that could be exploited from a
settlement, canoes increased the harvest of fish. How far Mesolithic people fished from
the coast is debated (e.g., Clark 1948, Coles 1971, Pickard and Bonsall 2004), but the
generally shallow near-shore waters of the Danish coast and large size of some of the
Gadidae specimens argue strongly that canoes were used to transport fishermen to
offshore fishing grounds. Canoes would also have been useful in setting and retrieving
nets and placing fish fences. In contrast with Neolithic examples that were hewn from
many types of trees, Mesolithic dugout canoes were constructed from lime tree trunks –
although this difference may be due to sampling bias as Mesolithic canoes are known
from coastal areas and Neolithic examples come from inland sites (C. Christensen
1990, Nielsen and Gebauer 2005). Estimates of canoe lengths range up to 10 m for one
example from Tybrind Vig and there is even evidence that some examples contained
hearths onboard (Andersen 1986). Experimental reconstruction of dugout canoes
suggests that two people might have produced one with about a week’s labor (see
Figure 9) (C. Christensen 1990:140). Paddles were made from a wider variety of wood
(including ash, oak, hazel, lime and willow) and are either of a heart-shaped or elliptical
form (C. Christensen 1990). Famous examples from Tybrind Vig were carved with
intricate patterns which may have been intended as markers of group identity (Figure
10) (Andersen 1986).
Figure 9: Modern dugout (photo Niels Axel Boas). Figure 10: Tybrind Vig paddle
(Andersen 1986).
2.2.5 Other technology
Many areas of Denmark are blessed with rich deposits of high-quality flint
which allowed flint-knapping technology to become highly evolved. Certainly the
numerous tool and debitage finds on Ertebølle settlements attest to the importance of
stone tools in the time before metal tools arrived. Chipped stone tools that are
commonly found include: transverse arrow points, axes, scrapers, knives, borers, burins
and blades (Figure 11). The quantities of flint debitage on sites can be enormous.
Figure 11: Core and flake axes from Dragsholm.
Ground stone axes
While rare, imported stone axes (e.g. Danubian shaft-hole axes, jadeite
axes) show that ground stone technology (traditionally associated with Neolithic
cultures) was already being used in the Late Mesolithic period in Denmark (Figure 12)
(Klassen 2002). While trade in the axes may have been of a ‘down-the-line’ nature, they
nevertheless demonstrate far-ranging contacts between Ertebølle and other peoples.
Figure 12: Ground stone axe from Dragsholm.
Bone and antler tools
Animals were a central focus in the lives of Ertebølle hunter-gatherers and
provided furs/skins, sinews, bones and antlers as raw material, in addition to meat.
Many different types of tools were fashioned from bone or antler materials including:
antler axes, awls, ulna ‘daggers’, fishhooks, pressure flakers, and bone points (Figure
13). Some pieces of worked bone feature intricate geometric engravings (Nash 1998).
Figure 13: Bone tools from Dragsholm.
Pottery
Ertebølle people adopted ceramic technology around 4600 B.C., producing
two types of pottery: pointed bottom vessels for cooking or storage (see Figure 14) and
lamps. Investigation of burned food remains on potsherds has shown small cod and
plants were part of the menu, and ongoing archaeometric investigations promise further
dietary details to come (Andersen and Malmros 1984, Heron et al. 2007)
Figure 14: Ertebølle pottery.
Shell beads
Personal decorations such as animal tooth pendants, amber and shell
beads demonstrate the importance placed on personal adornment during the Ertebølle.
At least one shell bead was recovered during the excavation at Fårevejle. Recently, a
new type of shell bead has been described from Havnø that features a grooved
circumference instead of a central hole for attachment (Andersen 2008b). During the
analysis of the Nederst fish materials an example of this type of bead was found,
making Nederst only the second site with such a find.
This brief overview does not cover all of the different classes of material
evidence that have been recovered from Ertebølle sites, nor does it give an exhaustive
treatment of the categories mentioned. Hopefully what it does accomplish is instill a
sense of a well-adapted, technologically-sophisticated people living in a bountiful
environment. Appreciating that Ertebølle people were not ‘poor savages’ merely
struggling to stay alive makes investigation of the decisions that shaped their lifestyles
all the more compelling.
2.2.6 Fishing before and after the Ertebølle period
Studying the Ertebølle fishery is best done with due consideration for the
fisheries of the preceding and subsequent cultures; unfortunately, much less information
is available with which to assess these periods. In Europe, evidence for the use of fish
dates back to at least the Upper Paleolithic, although finds of fish in Denmark from this
period are probably not archaeological (Clark 1948, Rosenlund 1976). During the early
part of the Mesolithic (Maglemose period: 9700-6400 B.C.) finds of fish bones on
settlement sites are known from several locations. The fish that were taken were
freshwater species such as pike and wels (Siluris glanis) (Rosenlund 1976), but this is
not surprising as for the most part the coast was far from modern day Denmark. Early
Mesolithic coastal settlement and exploitation of marine resources is probably
underestimated due to eustatic sea-level rise that has inundated the archaic shorelines
(Price 1987:242). During the Kongemose period of the middle Mesolithic (ca. 6400-5400
B.C.) sea-levels were rising quickly and, “the ‘Fishing Stone Age’ had begun,” (C.
Christensen 1995:15). Sites such as Vænget Nord, Stationsvej 19, Carstensminde, and
Villingebæk Øst A demonstrate that marine (and diadromous) fish were now the focus
of the fishery, although a minor freshwater component is present in some of the
assemblages (Enghoff 1994, Rosenlund 1976). Gadidae and Pleuronectidae appear to
be the favored prey, although this is based mainly on two sites on Zealand with
reasonably large assemblages. The Kongemose culture is not well understood in
general, due to the relatively limited number of known sites (especially those with good
organic preservation). Hopefully future excavations will reveal more about the
immediate forerunner of the Ertebølle period.
The Ertebølle period is the last Mesolithic culture in Denmark; it is followed
by the early Neolithic Trichterbecher (TRB) culture after 4000 B.C. While in some ways
subsistence seems to have changed gradually during the transition to the Neolithic (wild
plants and animals continue to be important resources and some coastal sites continue
to be used), isotopic evidence shows a more radical abandonment of marine resources
(Fischer et al. 2007, Richards et al. 2003, Tauber 1981 – see section 2.3 for a more
complete discussion of this topic). Debate rages as to possible explanations for this shift
away from marine resources (Fischer 2007, Hedges 2004, Liden et al. 2004, Milner et
al. 2004), and recent work suggests that it may not be as abrupt as sometimes
described (Price 2005, Price et al. 2007). Zooarchaeological investigations tend to
support the hypothesis that marine resources were largely abandoned during this
transitional period, as fish remains (excepting shellfish) are extremely scarce at Early
Neolithic sites. Bjørnsholm has the only published early TRB fish assemblage of any
size, and it is only 252 specimens (Enghoff 1991). Other sites that may contain Early
Neolithic fish remains include Norsminde (1 specimen), Fårevejle, Åkonge, Magleholm,
Muldbjerg I and Sølager; although dating of some of these assemblages is uncertain
(Enghoff 1989, 1994, 1995, Rosenlund 1976). In contrast with the lack of fish bone
material, fishing technology (in the form of fish fences and traps) is well-documented
and dated from the Early Neolithic period (Pedersen 1995, 1997). Underwater
archaeological investigations near the island of Nekselø have documented fish fences
(dated 3550-2950 B.C.) stretching nearly a quarter of a kilometer into the ocean in
waters that were originally up to 5 meters deep (Fischer 2007:60-61). The amount of
labor and materials required for such a construction was enormous; it is difficult to
imagine this commitment of effort without the expectation of large catches of fish in
return. Possible explanations for the conflicting evidence for early Neolithic fishing
include: lack of attention to recovering fish bones during excavation of Neolithic sites,
poor preservation at these sites and changes in how fish remains were discarded
(Enghoff 1995, Fischer 2007, Milner et al 2004). In addition to the enigma of why
archaeologists have found evidence for fishing structures but few fish remains from the
Neolithic is the puzzle of why people would abandon (if they did) a resource that had
contributed so much to their survival for generations.
2.2.7 Mesolithic fishing in other parts of Europe
One of the reasons that Denmark’s Late Mesolithic economy has received
so much attention is the extraordinary amount of information available (e.g., great
quantities of fish bones). Although nowhere as rich as the Danish record (both in
numbers of sites where fish bones have been recovered and in the total number of fish
bones), other coastal areas of Europe have also produced information about their
Mesolithic fisheries. Southern Sweden and Northern Germany are of particular interest
because of the presence of other Ertebølle groups.
In Scania, southwestern Sweden, it was during the Kongemose period that
the earliest traces of fixed fishing devices and fish bones documenting exploitation of
marine waters occur. “Herring totally dominates the finds, followed by plaice, cod, eel
and salmon species…people caught or perhaps more likely hunted large tuna out in the
Öresund,” (Andersson et al. 2004:91). Significant Ertebølle fish bone assemblages are
known from sites such as Tågerup and Skateholm (Karsten and Knarrström 2003,
Jonnson 1986). The number of species exploited increased, cod increased in
importance and more pelagic species such as saithe or pollock suggest that some
fishing may have been conducted in deeper waters (Andersson et al. 2004:117, Karsten
and Knarrström 2003:183). The remains of fish fences, basket traps, birch bark rolls
interpreted as net floats and stone net sinkers document some of the fishing technology
employed (Karsten and Knarrström 2003).
Norway is outside of the Ertebølle culture area, but does have evidence for
coastal occupations during the Late Mesolithic. In eastern Norway, “fish bones are
surprisingly few,” and, “the location of [the] sites, close to ancient seashores, should
indicate marine adaptation; yet the remains of terrestrial mammals dominate,” (Mansrud
2009:199). One exception to this fish bone scarcity would be Skoklefald by the Oslo
fjord, which produced a total faunal assemblage of 632 bones, 97% of which are fish,
dominated (81%) by herring but with minor contributions from cod, haddock and pollock.
The size of the bones indicates that many small fish were caught (Bjerck 2007:12-13).
Western Norway has better fish bone evidence. At Kotedalen the assemblage contained
97% marine species including cod, saithe and pollock, seal and otter in significant
numbers (Bjerck 2007:12). Just north of Kotedalen, on the coast, is the site of
Grønehelleren at the mouth of the Sognefjord. Here there are 233 bones from the
Mesolithic layers, dominated (58%) by fish (saithe, cod and pollock) (Bjerck 2007:15).
Still further north on the coast is the Skatestraumen area with more than 40 sites, the
osteological material being dominated by fish (Bjerck 2007:12). In the very far north of
Norway (near Varanger, Finnmark) is the site of Mortensnes Loc. 8/R12 with 4368 fish
specimens. The assemblage is dominated by cod, but with seven other species present
(Bjerck 2007:13).
Northern Germany is another region with Ertebølle culture settlement sites.
The fish remains here are especially interesting because until quite recently very few
had been recovered (Hartz et al. 2002). Recent fieldwork and laboratory analysis has
changed this dramatically, and now there are over 40,000 fish bones identified from
Middle and Late Mesolithic sites (Schmölcke 2009 personal communication). Three
concentrations of sites can be identified on the shores of the Baltic Sea: the western
side of Mecklenburg Bay, the eastern side of the bay (Wismar Bight) and the island of
Rügen further to the east. The sites of Grube-Rosenfelde LA 83 (4900-4800 B.C.),
Grube-Rosenhof LA 58 (4800-4500 B.C.) and Neustadt LA 156 (4500-4100 B.C.) lie on
the western side of Mecklenburg Bay and all date to the Ertebølle period. The Grube-
Rosenfelde assemblage (NISP = 207) is dominated by eel (72.5%) and cod, with
stickleback, flatfish, perch and sea trout also present. Grube-Rosenhof has a larger
assemblage (NISP = 3846) and is dominated by cod (72.2%) with eel, flatfish and
cyprinids also making substantial contributions (11 other fishes are present). The
Neustadt assemblage is dominated by cod (69%), with flatfish in second place. It is the
only German site where fishhooks have been recovered so far and is also of note
because it is the only Ertebølle assemblage that contains sturgeon remains (Sönke
Hartz personal communication 2009, Schmölcke et al. 2006:434). On the eastern side
of the bay, in and near the Wismar Bight, lie the sites of Jäckelberg–Huk (6300-6000
B.C.), Jäckelgrund–Orth (6000-5700 B.C.), Jäckelberg–Nord (5500-5100 B.C.),
Timmendorf–Nordmole I and Timmendorf–Nordmole II (5100-4800 B.C.). Jäckelberg–
Huk, dating to before the Ertebølle period and the incursion of saltwater into the bay, is
dominated by freshwater species (mostly perch, pike and cyprinids), while the later sites
contain mostly gadids, eel and flatfish in various combinations (with some additional,
mostly marine, species). Timmendorg-Nordmole I is of special interest for the remains
of conger eel (Conger conger), the only Ertebølle site where it has been identified. The
three sites in the area of the island of Rügen with sizable fish assemblages are Lietzow-
Buddelin, Parow-Sportboothafen, and Bergen-Breetzer Ort. The first site is dominated
by flatfish (48.2%) followed by perch (28.6%), while the second two sites produced
mostly perch bones (68.7 and 94.1%) (Schmölcke et al. 2006, Schmölcke et al. 2009,
Schmölcke personal communication 2009).
Dabki 9, a Late Mesolithic site on the eastern edge of the Ertebølle culture
area in Pomerania, Poland dating to 5250-4150 B.C., is the subject of ongoing
investigations, but earlier fish bone results show an assemblage with 44.1% pike, 20.9%
perch and 15.4% bream (Kabacinski et al 2009:552). One other area of the eastern
Baltic has produced sizable fish assemblages from the period, and here too the focus
was on freshwater species. In Estonia, “fishing during the Mesolithic and Early Neolithic
was centered on the exploitation of local waters: for millennia pike-perch were fished in
the estuary and bay of the Pärnu River,” and perch and pike were also taken (Kriiska
and Lõugas 2009:174).
Just west of the Ertebølle culture area in coastal areas of Germany, the
Netherlands and Belgium; the Late Mesolithic culture continued for a long period after
the arrival of LBK farmers just to the south. As in Southern Scandinavia, the stability of
the Mesolithic lifestyle has been hypothesized to be a result of a reliance on aquatic
resources. Isotopic analysis of human bones has confirmed that fishing (especially
freshwater species) and the collection of seafood was important, although actual fish
remains are infrequent (Arias 1999, Louwe Kooijmans 2007). Two exceptions are the
Polderweg and De Bruin sites that have produced good evidence for pike fishing
(Louwe Kooijmans 2007).
Moving northwards into the islands of Britain, Ireland and other islands of
the North Sea, fishing is also believed to have been very important for subsistence,
despite the relative scarcity of fish remains as evidence. Especially for southern Britain,
the explanation that is often given is that rising sea-levels have destroyed or submerged
the evidence in what should have been rich fishing grounds such as the lower Thames
estuary (Woodman 2000:247). In Scotland, where isostatic uplift has matched or
outpaced sea-level rise, some fish remains have been recovered from Mesolithic sites,
although only in modest quantities. In the east, at the site of Morton in Fife County, the
presence of turbot, haddock and large specimens of cod has led to the conclusion that
at least some of the fish were caught in deep, offshore waters from boats (Coles
1971:361). Mesolithic fishing in Scotland is best known from the shell midden sites on
Oronsay, a small island off the western coast. The sites of Cnoc Coig, Cnoc Sligeach,
Caisteal nan Gillean II and Priory all demonstrate a productive fishery; one that was
largely focused on catching saithe (Mellars and Wilkinson 1980). Otolith analysis
suggested that each midden represents a different season of fishing, but this claim is
now being challenged based on additional lines of evidence (Parks 2009). Further off
the coast of Scotland but to the north lie the Shetland Islands. Recent excavations at
the shell midden site of West Voe resulted in the recognition of a previously unknown
Mesolithic presence on the islands. Although fish remains are scarce, small fish, saithe,
herring, mackerel and shark or ray have been identified (Melton and Nicholson
2007:98).
Ireland represents another insular setting that presumably presented
excellent fishing opportunities for the inhabitants. Archaeologically, “large
concentrations of these pieces [flint tools] are found at key fishing locations on islands,
lakeshores, and river fords, possibly in the last instance associated with the building of
fish weirs,” (Woodman 2000:236) suggesting that fishing was important. The absence of
large mammals (other than wild pigs) has also been suggested as a reason for the
importance of marine resources in the Mesolithic, a hypothesis that has been supported
by isotopic analysis (Woodman 2000). Mesolithic fish remains are scarce, but two sites
shed some light on the topic. At Mount Sandel (occupied ca. 7000-6000 B.C.) in
Northern Ireland, salmon and eel remains have been recovered from a site near the
River Bann. At Ferriter’s Cove (5600-5700 BP), analysis of fish bones discovered during
archaeological excavations has shown evidence of fish species including wrasse,
whiting, tope and ray, suggesting that fishing took place during summer and autumn
(Woodman et al. 1999). The excavation of fishing structures near Dublin demonstrates
that considerable effort was expended in the pursuit of fish (McQuade and O’Donnell
2009).
Returning to the continent, in Brittany, on the French Atlantic coast, the
Late Mesolithic sites are interpreted as being the result of a sedentary population with
an economy based on marine resources. Shellfish, gilthead bream, labroids, scienids,
rays, sharks, cetaceans and seals have been identified in the faunal assemblages, and
stable isotope analysis shows that a significant portion of the protein in diet came from
marine sources, particularly at Hoëdic (Schulting 1998). Other large shell midden sites
include: Beg-an-Dorchenn, Beg-er-Vil and Téviec; there are two smaller ones at Saint-
Gildas with only shellfish remains. Of particular note is that at least four species of crabs
were exploited (Dupont et al. 2007:131). One exceptional fish find from Brittany is a fish
mandible with a carved quadrangular motif (Arias 1999:420-421). From other areas
bordering the Bay of Biscay, the sites of La Riera, Tito Bustillo, Los Canes, Laminak II,
Cueva de Amalda, all have fish assemblages that are dominated by salmonids (Zapata
et al. 2007:150). The Pico Ramos cave shell midden is interesting because of the
remains of cartilaginous fish. This suggests that fish remains may be scarce in this
region because of the poor preservation of sharks and rays, if they were common prey
(Zapata et al. 2007).
Continuing southwards along the Atlantic coast into the Cantabrian region,
researchers have claimed that despite the presence of shell middens and fish remains,
the settlement pattern is not consistent with an economy oriented towards the sea (most
major sites are a couple of kilometers from the coast) (Arias 1999:414). Eleven sites
have produced fish bone assemblages, but few have been studied in depth. Work in
progress at La Garma A and Asturian middens at Poza l’Egua,m El Aguila, Covajorno,
Colomba and Puerto de Vidiago II should reveal more information about the fisheries in
this region (Fano 2007:138-139). Finally, the shell middens in central and southern
Portugal contain numerous fish remains, especially meagre (Argyrosomus regius) and
gilthead (Sparus aurata); although large species such as sharks, rays and tuna are also
present (Arias 1999:409).
Given the diverse environmental and cultural contexts represented by the
assemblages discussed above, it is not surprising that it is difficult to generalize about
the nature of later Mesolithic fishing in Europe. Where freshwater species are the
majority of an assemblage, pike, perch and/or Cyprinidae are likely to dominate. For
sites near the North Sea with mostly marine or diadromous fish, eel, flatfish and
(especially) Gadidae are the common fishes. Further west and south (sites near the
Atlantic Ocean), eel, Salmonidae, sharks and rays seem more important. The presence
of tuna in assemblages from Portugal and Sweden, and large Gadidae at some sites
bordering the North Sea are strong evidence for offshore fishing, even if a deep-sea
Mesolithic fishery cannot be proven (Pickard and Bonsall 2004). Despite the occurrence
of fish fences and basket traps in several locations, it must be acknowledged that
multiple fishing technologies were employed by Mesolithic fishermen in varying
combinations. Looking at the evidence for fishing during the Late Mesolithic at coastal
sites outside of Denmark one fact in particular stands out: with the possible exception of
Northern Germany, fish remains are not as numerous on sites in other areas nor are
there so many sites that have produced fish assemblages. While the recent dramatic
increase in fish bones from Northern German sites offers reason for optimism that other
areas may experience a similar renaissance in fish bone studies, currently the region
that offers the best opportunity for understanding fishing during the Late Mesolithic is
Denmark (even if the results are not necessarily directly transferable to other areas).
2.3 Bone isotope studies of diet
Stable isotope analysis of bones has rapidly increased in importance as a
source of information on subsistence since its inception just a few decades ago.
Advantages of the method include a focus on individuals’ diets, examination of what
was eaten as opposed to what was discarded and the potential for recognition of dietary
components that are often discriminated against by preservation issues (i.e., plant
foods, but see below) (Lee-Thorp 2008). Examining diet at the individual (as opposed to
the family or larger group level) is usually not possible in traditional dietary analyses
(e.g., faunal studies) because refuse is deposited collectively. In the rare instances
where individual deposits are preserved (coprolites), the foods that are identified only
cover the most recent 24-48 hours. The issues of studying what was discarded versus
what was eaten and problems of differential preservation of materials raise doubts
about whether archaeological refuse can be deciphered into a complete picture of past
diet. In contrast, directly studying the composition of bones offers opportunities to ‘see’
past food consumption without the filters that can severely distort the archaeological
record. Isotopic studies are not without their own limitations and these will be described
more fully below.
The basis of the isotopic method for researching dietary questions is that,
“elements differ slightly in their nuclear mass as a result of differences in the number of
neutrons, leading to small but significant differences in their thermodynamic and kinetic
properties. Molecules containing the higher-mass, rarer isotope tend to accumulate in
the thermodynamically most stable component of a system—for instance, in the liquid
rather than gaseous phase—or are slower to react in mass-sensitive kinetic reactions,”
(Lee-Thorp 2008:927). In practice this means that it is possible to determine the trophic
level of food, what types of plants contributed to the diet, marine versus freshwater
versus terrestrial origins or other information about the food’s environment by examining
the isotopic ratio of one or more elements. “By convention, stable isotope ratios are
expressed in the δ notation, in parts per thousand (per mille or ‰) relative to an
international standard, as δxZ = (Rs/Rref − 1) × 1000, where R is the isotope ratio
(13C/12C, 15N/14N, 18O/16O, D/H or 34S/32S). For carbon isotopes, the standard is the
marine limestone PDB; oxygen and hydrogen isotopes may be expressed relative to
PDB or to Standard Mean Ocean Water (SMOW), depending on the material being
analysed; for nitrogen isotopes it is Ambient Inhalable Reservoir (AIR); and for sulphur
isotopes it is the Canyon Diablo Triolite meteorite (CDT). Negative values denote that
the sample has lower abundances of the heavier isotope than does the standard,” (Lee-
Thorp 2008:926). Bone is the most commonly examined archaeological material in
isotopic analysis due to preservation, but some other biological materials can be used
when present. Collagen (the organic part of bone) turns over regularly while apatite
(bone mineral) is more stable. Collagen breaks down more quickly than apatite, but it
appears that even when a large proportion of the original collagen molecules have
disappeared, the isotopic composition remains intact (Collins et al. 2002). On the other
hand, “bone apatite is vulnerable to the kinds of diagenesis that may frequently
influence isotope composition, while enamel remains relatively immune,” (Lee-Thorp
2008:931).
δ13C (carbon)
Stable isotopes of carbon were used in the first studies of diet through bone
chemical analysis and continue to be at the forefront of research. There are two topics
that are commonly addressed by carbon isotope studies: plant use and marine versus
terrestrial dietary focus. Plants are grouped into two major groups, depending on their
photosynthetic processes (a third group, succulents, is less commonly encountered)
and named after the number of carbon atoms that are initially fixed (C3 and C4) (Lee-
Thorp 2008). C3 plants are common, but C4 plants are generally limited to tropical
grasses (e.g., maize, millet, sugar cane). Because C3 plants are more depleted in 13C
than C4 ones, it is possible to determine what proportion of the diet came from each of
the two groups. Although of great interest in, for example, North America as a means to
study the spread of maize agriculture (Buikstra and Milner 1991, van der Merwe and
Vogel 1978), it is of little relevance for European Mesolithic studies. What is of interest
is the difference in 13C between marine and terrestrial food sources. Because the
source of carbon for the first links in marine food chains is mainly dissolved
bicarbonates that are enriched in 13C compared to atmospheric CO2, bone isotope
analyses that show more negative 13C values reveal a dominance of terrestrial foods in
the diet while more positive values point to marine foods (Lee-Thorp 2008). Terrestrial
plant δ13C values vary between -24 to -36 ‰ depending on environmental conditions,
with a global mean of -26.5 ‰ (Smith and Epstein 1971, O’Leary 1981, Farquhar et al.
1989). For marine resources there is some variability, but the mean is −20 ‰ (Smith
and Epstein 1971).
The δ13C values that are measured from the bones of consumers are not
the same as the foods they eat for a couple of reasons. “Carbon isotope ratios in bone
apatite should reflect sources of dietary energy, which is effectively the whole diet, while
collagen reflects mainly dietary protein,” (Price et al. 2007:212). There is an enrichment
of δ13C between diet and bone collagen of approximately 5 ‰ (van der Merwe and
Vogel 1978). The enrichment between diet and bone apatite averages 12 ‰, but varies
according to body mass and other biological factors (Ambrose and Norr 1993, Cerling
and Harris 1999, DeNiro and Epstein 1978, Krueger and Sullivan 1984; Lee-Thorp et al.
1989, Passey et al. 2005). There is an additional enrichment of 1-2 ‰ for each trophic
level of the food chain (Lee-Thorp 2008).
One of the first published studies to take advantage of the isotopic
differences in 13C between marine and terrestrial food sources was a study of skeletons
from the Danish Mesolithic (Tauber 1981). The sharp break at around 4000 B.C.
between more enriched (marine-based diet) collagen from Mesolithic skeletons and less
enriched (terrestrial-based diet) skeletons from the Neolithic pointed to a distinct shift in
subsistence that neatly coincided with observed changes in material culture.
Subsequent studies that have increased the sample of skeletons from Denmark and
expanded the geographical range to include Britain, northwestern France and Portugal
have generally confirmed the initial results showing very little dietary contribution from
marine resources after the onset of the Early Neolithic (Lubell et al. 1994, Richards and
Hedges 1999, Schulting and Richards 2001, Richards et al. 2003, although see Liden et
al. 2004 for contradictory evidence from Sweden). A less often discussed trend is an
increase in the contribution of marine foods from the early to the late Mesolithic,
culminating with all individuals, “younger than 5500 B.C. show[ing] a predominance of
marine resources in the diet,” (Price and Gebauer 2005:155). The dominance of marine
resources is seen even in Mesolithic samples from inland locations (Fischer et al. 2007).
It is important to note that very few Mesolithic or Neolithic samples represent a situation
where all foods came from either a marine or a terrestrial environment. Late Mesolithic
people with a marine-based diet have isotopic values that indicate up to 40 % of the
foods consumed by some individuals came from terrestrial sources, while some
Neolithic samples are consistent with approximately the same amount of marine-based
resources in a terrestrially-dominated subsistence regime (Price and Gebauer
2005:155).
Recent discussions have centered on the conflict between the
archaeological evidence for marine resource use in the Early Neolithic (i.e., shellfish
deposits, continuing use of coastal sites, stationary fishing structures) and the isotopic
evidence showing a switch to a terrestrial diet (Bailey and Milner 2002, Fischer 2007,
Hedges 2004, Milner et al. 2004). Suggested reasons for the discrepancy include
sample bias, the use of estuarine resources that incorporate a great deal of transported
terrestrial carbon, complications from variations in salinity and the effect of low protein
diets on collagen isotopes (Milner et al. 2004). In regards to the last point, it is
suggested that, “a diet dominated by plant food might include up to 20 percent of marine
protein without raising the δ13C values of bone collagen above -21 per mil,” (Milner et al.
2004:18). Research continues to understand the impact of variations in salinity on
isotopic values (Craig et al. 2006, Grupe et al. 2009), but it is already clear that it is
important to measure the local isotope signatures of marine and terrestrial resources in
order to make dietary inferences. Resources obtained from freshwater environments
seem to be especially confounding for dietary studies as, “the more freshwater food
there was in the diet, the more it hampers a possible marine isotope signature in human
bone collagen δ13C values,” (Fischer 2007:66). Lake size and the sources of carbon
both seem to affect the δ13C values from freshwater sources (Dufour et al. 1999, Post
2002). The role of diadromous fish complicates matters greatly, because of their
residence in both marine and freshwater environments (Fischer 2007). In light of the
many factors that affect carbon isotope measurements, and thus dietary interpretations,
analyses that combine multiple elements provide more robust interpretations.
δ15N (nitrogen)
Nitrogen is another element with staple isotopes that are useful in dietary
reconstructions. Although some variability in δ15N is the results of the source of the
nitrogen or environmental factors (Dufour et al. 1999, Katzenberg and Weber 1999, Liu
and Kaplan 1989, Richards and Hedges 1999), the most important factor is the trophic
level of the foods consumed, with a δ15N enrichment of 2-6 ‰ for each step up the food
chain (DeNiro and Epstein 1981, Minigawa and Wada 1984, Schoeninger and DeNiro
1984, Sealy et al. 1987). This is especially interesting where freshwater or marine
resources are a significant portion of the diet, as aquatic food chains tend to be much
longer than terrestrial ones. In situations involving marine resources, nitrogen isotopes
can reinforce the results of carbon isotope analyses and potentially indicate what types
of marine foods were consumed (Lee-Thorp 2008, Richards and Hedges 1999). In non-
maritime settings where carbon isotopes are mainly useful for distinguishing C3- from
C4-based diets, δ15N can help to determine the subsistence contribution of freshwater
fish (Dufour et al. 1999, Katzenberg and Weber 1999). Nitrogen isotope analysis is
complicated by, “variability in the diet tissue enrichment with protein level, dietary items,
or between species, and difficulties with determination of the appropriate (herbivore)
isotopic baseline,” (Reynard and Hedges 2008:1934).
Regarding the Late Mesolithic dataset, nitrogen isotope analyses have
tended to support the trend observed with the carbon results: lower δ15N values in
Neolithic skeletal samples compared to Late Mesolithic ones agree with a shift from
higher trophic level aquatic resources to terrestrial plants and herbivores, although with
exceptions. The low δ15N value of the individual from Tybrind Vig (8.5 ‰) is more in line
with a terrestrial diet, despite the coastal location with abundant evidence for marine
fishing, and bone samples from graves near the Vedbæk fjord suggest that shellfish or
small fish were the major source of protein for three out of five individuals, despite the
evidence for large specimens of cod in several faunal assemblages in the area (Enghoff
1994, Richards et al. 2003) Within the Mesolithic period, an increase in δ15N values
from the early to the later Mesolithic agrees with the carbon isotope results that show a
shift to more reliance on aquatic (especially marine) resources (Fischer et al. 2007).
Aside from dietary studies involving human bones, isotopic studies are also
proving useful in studies of the environments where resources were obtained. In
Northern Germany, on the Schlei estuary, differences in nitrogen isotope values
between the Viking period settlement of Hedeby and the nearby early medieval city of
Schleswig are interpreted as demonstrating that codfish were imported over longer
distances during the Viking period than afterwards (Grupe et al. 2009). A study of wild
and domesticated cattle (Bos primigenius and Bos taurus) from Danish sites has
demonstrated increasingly closed canopy forest coverage during the Mesolithic based
on values from wild cattle and a clear difference in habitat between wild and early
domestic cattle (with domestic cattle feeding in more open grassland areas) (Noe-
Nygaard et al. 2005). Further studies of environmental effects on bone isotope values
and measurements of local isotopic signatures offer increasingly refined interpretations
of human and animal behavior; adding to the number of elements included in isotopic
studies is another way to improve them.
δD (hydrogen)
Isotopes of hydrogen that are tightly bound into organic molecules are
beginning to be studies as an additional line of evidence for studies of dietary trophic
level (Lee-Thorp 2008). Studies of wild animals in Britain have been able to distinguish
between herbivores, omnivores and carnivores based on δD (Birchall et al. 2005).
Archaeological samples from Britain, Hungary and Peru have demonstrated that the
technique holds similar promise for the study of diet in ancient bones (Reynard and
Hedges 2008). Enrichment of δD from herbivores to omnivores is around 30-50 ‰, and
from omnivores to humans around 10-20 ‰ (Reynard and Hedges 2008:1938).
Hydrogen isotopes have the potential to reveal geographical origin information because
of variability in precipitation and may also prove useful as an independent indicator of
marine protein in the diet (Reynard and Hedges 2008). Further studies are needed to
confirm the efficacy of the technique and determine whether any biological or
environmental considerations have been overlooked.
δ34S (sulfur)
Another element with isotopes that are proving useful in distinguishing
marine from terrestrial foods in dietary studies is sulfur. Based primarily on local
geology, terrestrial and freshwater δ34S values range from ca. -20 to +20 ‰ compared
to a more uniform marine value of +20 ‰ (Krouse and Herbert 1988, Peterson and Fry
1987, Rees et al. 1978). In many (but not all) locations the enrichment of marine
isotopes distinguishes dietary food sources, although with the reservation that terrestrial
resources in coastal areas may incorporate marine sulfur from the ‘sea spray effect’
(McArdle et al. 1998). Although the technique has potential, not all of the sources of
variation have been identified. Results of animal bones studies from Danish shell
middens showed samples with the most negative δ34S values (indicating
terrestrial/freshwater diet) were the most enriched in 13C (pointing to a marine diet)
(Craig et al. 2006). Still, because sulfur isotopes do not seem to be strongly affected by
a trophic level effect, they may be a useful adjunct to studies using carbon and nitrogen
isotopes (Lee-Thorp 2008, Privat et al. 2007). Sulfur isotopes also offer some potential
for provenance studies of humans and animals (Katzenberg and Krouse 1989;
Rossman et al. 1998).
2.4 Theoretical basis
“All we can be sure of in interpreting any archaeological record is that the community
responsible for it was successful enough to leave a deposit, that it can have achieved
this only through a successful routine of acquiring food, and that, in other words, its
settlement pattern must at least have been consistent, with success in the food quest,”
(Clark 1983:295-296).
The point in history where the discipline of archaeology evolved from the
diversion of antiquarianism was when people began to realize that the recovery of
artifacts was not an end in itself, but only a means to understanding the past. Since
then, a great deal of thought and discussion has been devoted to constructing
frameworks for translating data produced from material evidence into information about
past human societies, a process that continues today (e.g., Binford 2001). While some
aspects of archaeological research have developed a multitude of theoretical
approaches, faunal analysis is dominated by behavioral ecology, an evolutionary, or
neo-Darwinian, approach to understanding human culture.
Behavioral ecology has its roots in the cultural ecology perspective
pioneered by Julian Steward, which attempted to explain relationships between society,
environment and technology (Steward 1955), modified by concepts borrowed from the
natural sciences. In an effort to focus on the core areas of culture, Steward paid
particular attention to subsistence, especially as it was affected by the environment.
Although hailed by some as a major advance in thinking about the past, the cultural
ecology approach came under fire from processualists (among others) because it aimed
to, “explain the origin of particular cultural features and patterns which characterize
different areas rather than to derive general patterns applicable to any cultural-
environmental situation,” (Steward 1955:36). Other objections raised include, “a strong
bias towards inductive argument…after-the-fact construction of explanations; a bias
toward equilibrium or homeostatic models; and the use of non-refutable hypotheses”
(Smith and Winterhalder 1981:3). Proponents of the behavioral ecology approach which
supplanted it noted that cultural ecology was flawed due to, “its implicit belief in the
importance of the group, as opposed to the individual, as the adaptive unit,” (Shennan
2002:140). While also seeking to achieve a better understanding of the relationship
between society, environment and technology, behavioral ecology proposes to improve
on cultural ecology by employing testable hypotheses, formulated in a hypothetico-
deductive manner, to search for nomothetic explanations of individuals’ behaviors.
Although behavioral ecology can address many types of activities (e.g.
mating, predator avoidance), when used by zooarchaeologists it most often relates to
resource procurement. Three different lines of inquiry within this topic are addressed by
the models: diet breadth (also called prey choice or optimal diet), habitat movement (or
patch choice) and time allocation (patch use/marginal value theory), but with the
realization that this division is a heuristic device and should not be taken as reflecting
actual partitioning in how these questions are perceived by the organism(s) in question
(Bird and O’Connell 2006, Winterhalder and Smith 2000). Examples of habitat
movement and time allocation modeling exist, but by far the most popular question in
optimal foraging research has been which foods are included in the diet under varying
circumstances (see Bird and O’Connell 2006, Kelly 1995, Shennan 2002, Winterhalder
and Smith 2000 for comprehensive surveys of archaeological studies of diet breadth).
To date, optimal foraging has made relatively few inroads into studies of fish remains
(some exceptions include: Aswani 1998, Barber 2003, Bliege Bird and Smith 2005, Bird
and Bliege Bird 2000, Broughton 2002, Lindström 1996, Sosis 2000). This project will
apply the diet breadth model as an aid in interpreting the fish bone assemblages of the
Danish Ertebølle period.
Evaluating diet breadth is a popular endeavor for zooarchaeologists
because diet breadth modeling aims to make specific predictions about what game
should be included in archaeological assemblages, based on knowledge of animal
behaviors and biology combined with information about human activities and
technology, which can then be compared against the actual record. Search costs
incurred while looking for game are contrasted with pursuit costs (also known as
handling costs) to determine whether a rational forager will pursue a particular type of
game when it is encountered or continue looking for a more highly valued target
species. Search costs are usually tied to resource density (low density equals high
search costs) while pursuit costs are a factor of both the cost to capture and process the
prey for consumption. Resources are ranked in descending order of rate of return
(usually energy gain minus energy cost, but see below), and new types are added to the
diet until the next addition would lower the overall return rate (see Figure 15 for a
graphic representation of this, from Winterhalder 1981:24).
Figure 15: Diet Breadth Model plotting decreasing average search costs versus
increasing average pursuit costs, as additional resource types are added to the diet.
Optimal diet breadth is marked by the arrow at the intersection of the two curves (after
Winterhalder 1981:24).
The change in search costs is a downward sloping curve because as more items are
included in the diet the chances of encountering some desired resource increase,
thereby reducing the cost incurred looking. Conversely, the pursuit curve slopes
upwards because as lower ranked resources are added to the diet the average cost of
capturing and processing resources increases. In archaeological cases it will be difficult
(or impossible) to accurately determine the return rates of individual resources for
ranking and to plot the two curves with a degree of precision that would allow
determination of specific numbers of resources in the diet, but by modeling how the
curves respond to changing conditions it is possible to predict expansion or contraction
of diet breadth.
Tests of the model have shown that, “while the diet breadth model seems to
give good predictions within plant resources and animal resources, it does not seem to
work so well between them, probably at least partly because energy is not the sole
criterion of value as far as food is concerned,” (Shennan 2002:147). It is likely that this
statement fails to consider that fishing is different in many ways from pursuit of other
animals, and it may be more reasonable to designate three categories: plants, fish and
other animals. For this project, use of the diet breadth model is restricted to the category
of fish resources, with an aim to characterize the nature of the fisheries at different sites.
Instead of focusing on whether (and when) specific fishes are incorporated into the diet,
the overall richness of the assemblage (number of types of fish) and the importance
(relative frequency within the assemblage) of the individual fishes will be used to
determine whether the fishery is more generalized or specialized.
There are a number of important points that must considered for this model
to be successfully applied. First, the currency used in evaluating the transaction is often
energy (calories), but this is not a given. Other nutritional factors can be substituted for
energy (e.g., fat, protein, carbohydrates, vitamins, trace minerals), and may prove to be
a more revealing limiting factor in some situations. Perhaps more intriguingly, recent
studies have sought to incorporate ideological factors (i.e., status) alongside
considerations of nutrition (e.g., Bird and Smith 2005, Hildebrandt and McGuire 2002,
Sosis 2000). Because of the large numbers of unknowns in regard to search, pursuit
and processing costs, attempting a very precise definition of returns would not be
justified. The currency for this project will be energy, with energy gain read from the
archaeological record in the form of relative abundance of remains from different types
of fish (with some consideration of size and calorie-yield), and costs estimated by time
requirements. Second, search and pursuit costs are not fixed, but depend on the
technology available to the forager, prey populations and environmental changes. This
introduces the difficulty of choosing an appropriate temporal scale for evaluation. In
ethnographic research, the unit of study is often an individual foraging expedition, but
this degree of resolution is rarely (if ever) possible to achieve with archaeological data.
Because of the multi-year accumulations of fish remains that are the record for this
project, diet breadth decisions can only be judged on a very broad basis: was the fishing
strategy more specialized or generalized? Related to the topic of temporal scale is the
question of the information available to the forager. Diet breadth models were originally
created using the tenets of games theory under the conditions of random searching in
an environment with randomly and evenly placed resources, but this is certainly not a
reasonable assumption for most cases of human foraging because it (among other
issues) ignores learning through experience. Part of the successful forager’s toolkit is
knowledge of animal characteristics combined with information garnered from past
forays and other foragers that allows efforts to be focused on places that are most likely
to result in encounters. Due to the long-term nature of the archaeological record being
studied, it must be accepted that random searching does not characterize much of the
foraging activities, as repeated fishing activities taught Ertebølle fishermen where (and
when) to concentrate their efforts. This is in some ways an advantage, as better
knowledge of conditions means that the choice of a specialized or generalized strategy
was the result of more rational, deliberate decision making and is thus more amenable
to modeling. The goals of a forager are a final important consideration, and one which is
often neglected in the formulation and testing of hypotheses. Maximizing returns and
minimizing risk are two goals that are often seen in opposition to each other. Solving
models for only one goal may create unrealistic behavioral expectations, but solving for
both simultaneously is often unfeasible. This study of diet breadth will assign
maximization as the goal, as the other resource groups would provide a margin of
safety to minimize the risk of absolute procurement failure. There is, however, another
kind of risk associated with resource procurement: that associated with danger to the
forager while out seeking food. For Mesolithic fishermen with dugout canoes, this was at
times a non-trivial risk. Maximization as a goal also makes sense from this perspective,
as the higher the rate of return, the less time of exposure to danger was necessary.
Having introduced the diet-breadth model and discussed some of the inherent
assumptions, now it is time to put the model into operation.
Modeling various configurations of the search and pursuit curves shows
that “an optimal forager with a high search-cost/pursuit-cost ratio will tend toward a
generalized diet breadth <Figure 16>. Conversely, a forager with a high pursuit-
cost/search-cost ratio will tend toward diet breadth specialization <Figure 17>. Any
factor which causes an increase in the search costs of an optimal forager will produce a
stepwise enlargement of its diet breadth. Conversely, a factor decreasing search costs
will lead to a restriction of diet breadth <Figure 18>. Any factor reducing pursuit costs of
the optimal forager will produce an enlargement of its diet breadth. Conversely, a factor
increasing pursuit costs of a forager will produce diet breadth specialization <Figure
19>,” (Winterhalder 1981:25, figures are added for illustration of the points).
Figure 16: High search/pursuit cost ratios Figure 17: High pursuit/search cost
ratios increase diet breadth (generalized diet). Decrease diet breadth (specialized diet).
Figure 18: Effect of changes in search costs. Figure 19: Effect of changes in pursuit
costs.
(Dashed grey line indicates the initial state, while arrows mark the new optimal diet
points)
With an understanding of how diet breadth is determined by comparison of
the search and pursuit curves and responds to changes in them, the next step in
applying the model is describing what factors affect the location of the curves. As
already noted, search costs are highly dependent on the density of prey. This is a rather
unremarkable observation. What is surprising is that, “a resource’s abundance alone
cannot be used to predict whether it will be utilized…the decision to include a resource
depends on the abundance of higher-ranked resources,” (Kelly 1995:86-87). An edible
and ubiquitous resource may be ignored unless search costs for more desirable
resources increase to the point that diet breadth expands to include it. Search costs
increase when target species are less abundant or environmental conditions make them
more difficult to locate. Species abundance varies over both the short and the long term.
Short term variations (i.e. diurnal movements or seasonal migrations) should play little
role in optimal breadth modeling in archaeological cases, unless a site was only
occupied on a seasonal basis (or fishing activities at a year-round site were seasonally
restricted) or for a very limited duration. Although determining the season of occupation
for Ertebølle sites remains a challenging endeavor, the sites that produced the
assemblages included in this study generally have many of the characteristics of base
camps (e.g., diverse toolkits) that were occupied for at least most of the year, so short
term fluctuations will be discounted when characterizing diet breadth (although
seasonality will play a role when discussing the details of the generalized and
specialized fisheries). Differences in species abundance that affect diet breadth will
therefore be considered to be the result of either longer term temporal, or spatial,
variability. For Ertebølle fishermen, environmental conditions (especially sea-levels, but
also water temperatures, salinity and coastline morphology) would have been the major
driver of increased search costs, at times or places making target species less
abundant and/or harder to find.
Search costs decrease when resources abound or as a result of favorable
conditions in the landscape, accumulated knowledge of prey locations, or improvements
in technology (i.e., faster transportation) that increase the likelihood of prey encounters.
Familiarity with prey species and their favored locations would obviously increase the
chances of encountering them, but it is difficult to assess variability in this factor during
the Ertebølle period for several reasons. First, it should be noted that marine fishing did
not begin in Denmark during the Ertebølle period. Sites such as Cartsensminde,
Stationsvej 19 and Vænget Nord show that already in the preceding Kongemose period
(6400-5400 B.C.) fishermen in Denmark were capturing many of the same species that
were the basis of the Ertebølle fishery (Enghoff 1994a, Rosenlund 1976). Some
knowledge of fish behavior was present at the start of the Ertebølle period, and while it
undoubtedly increased as fishing continued, it is also probable that in some groups
there were at times decreases as experienced fishermen were unexpectedly lost due to
accidents or other causes. The environmental variability that characterizes the period
also means that there must have been a continuing effort to upgrade the knowledge
base as prime fishing locations moved in response to environmental changes. Absent
any compelling evidence for increases in knowledge lowering search costs, this factor
will be treated as a constant. Improved technology in the form of dugout canoes is
another matter. While watercraft are also known from previous periods (at least from
paddles, which surely signify that boats were also present), more widespread availability
of canoes or improved performance are plausible ways in which technology could have
reduced search costs in some fisheries (C. Christensen 1990). In summary, the size of
fish stocks and environmental conditions could have either increased or decreased diet
breadth (through displacement of the search curve) depending on their nature, while
more or better canoes would have lowered the search curve and led to increased
specialization.
Pursuit has two components in the diet breadth model: capture costs and
processing costs. The process of capturing prey after it has been encountered during
the search phase can be more or less costly depending on the experience of the
fisherman, the nature of the prey, the timing of the encounter and perhaps most
importantly, the technology involved. The extent of a fisherman’s experience can be an
important factor in whether he is successful when fishing, but archaeological deposits
from settlements do not allow differentiation of individual forager efforts so this factor
must be treated as a constant. The specific type of fish pursued, when it is pursued and
how it is pursued are all interconnected variables, but the method of capture is the one
of interest for archaeological diet breadth modeling. As foragers adopt increasingly
sophisticated fishing technology, catching fish becomes easier. Whether costs decrease
is a complicated affair, balancing the benefits of increased efficiency in procurement
with the concomitant costs incurred fashioning the technology. For expensive tools,
greater efficacy may actually result in lower efficiency (Bird and O’Connell 2006:153).
Because tools can be made during periods when other foraging activities are not
possible (at night by the fire, during inclement weather, etc.) and by group members
who do not actively forage (e.g., young, old and infirm individuals), construction costs
are not generally included in diet breadth models even though they can be considerable
(over 2200 hours for a 100’x4.5’ gill net with ½” mesh size according to Lindström
1996:139). Accordingly, increased investment in fishing gear will lower the pursuit curve
and lead to an expansion of diet breadth. Fish hooks and spears require relatively little
time to make, while fish weirs/fences and nets require considerably more. According to
the diet breadth model, fisheries that rely more heavily on hooks and spears will be
more specialized while those that focus on nets and traps will be more generalized.
Interestingly, the degree of prey selectivity for the different implements predicted by
optimal foraging theory corresponds to that predicted by a combination of ecological
theory and fish behavior (Bowdler and McGann 1996:91, Enghoff 1994a:84).
Processing costs for resources range from almost zero for foods that are
eaten in their natural state to very high for foods that must undergo extensive
treatments to make them edible. The nature of the resource is the major determining
factor, but the purpose of the processing (i.e., immediate or delayed consumption) and
the technology involved can also be significant (Testart 1982). As the focus of this study
is fish, differences in processing costs between resource types can probably be
assigned minimal importance. There is of course, the potential to make fish preparation
a very time intensive activity (e.g., sushi). On a more pedestrian level, small fish may
require more processing per unit weight than larger fish if the aim is to provision with
pure meat portions (e.g., fillets), but there is little reason to believe this was the case in
the Mesolithic (Enghoff 1991:116). There are many ways to prepare fish for the table
that require little labor. Large and small fish can be eaten raw or boiled whole (or
eviscerated) with inedible parts trimmed away or skimmed off the surface of the pot,
avoided during consumption, or simply passed through the digestive tract. Direct or
indirect roasting with fire require similarly small commitments of effort. If the fish are
destined for delayed rather than immediate consumption processing costs can be
considerably higher. Depending on the desired length of storage, size and fat content of
the fish, storage conditions, technology available and climate; processing fish for
storage can run the gamut from simple air drying to elaborate procedures involving
precision butchery and careful salting and/or smoking. To date, there is no definitive
archaeological evidence that Mesolithic people had an elaborate gastronomic tradition
or stored fish for later consumption (although it seems almost indubitable they did this, if
only in the most rudimentary of fashions), so all things considered, it is probably
defensible to treat processing costs for different fish as a constant.
Taking into account both search and pursuit costs, what predictions can be
made about the Ertebølle fisheries? Environmental conditions will affect the catch in two
ways: determining the abundance of fish in an area and the difficulty of locating them. In
areas with large fish populations and/or where locating fish is easy, the search curve is
lower and a more specialized fishery will result. In areas with less favorable conditions,
a more generalized fishery will prevail. Changes in environmental conditions will lead to
more specialized or more generalized foraging depending on whether conditions are
becoming more or less favorable for fishing. Technology will have an effect on both
search and pursuit costs. Better transportation technology (canoes during the Late
Mesolithic) can lower search costs and reduce diet breadth. If instead of investing in
transportation technology a group devotes more resources to capture technology (i.e.,
nets and traps), pursuit costs will be low (or declining) and the fishery will be more
generalized.
Before turning to the question of how to compare these predictions with the
archaeological results, a few final thoughts on characterizing Ertebølle fisheries are in
order. First and most importantly, while it is convenient to refer to specialized or
generalized strategies to emphasize variability it must be remembered that the reality is
of fisheries that occur somewhere along a continuum between these two endpoints.
When characterizing an assemblage as representative of a specialized strategy, this is
only true in relation to the other assemblages with which it is compared. Second, finds
from archaeological sites show that multiple technologies were used at the same site
(e.g., excavations at Tybrind Vig produced evidence for fish traps, fish fences,
fishhooks, leister prongs and a net float), indicating that groups used a mix of
techniques in their fisheries (Andersen 1995, Pickard and Bonsall 2007). Different fishes
are best captured with different fishing gear, but seasonally variable fish behaviors and
environmental conditions also require flexibility. Because of the longer-term
accumulations that characterize the assemblages analyzed for this project, the overall
nature of the fishing strategy at a site is revealed, even though specific events may
deviate from this norm. How to quantify the assemblages in order to compare them with
each other is the next topic which must be addressed.
2.5 Zooarchaeological quantification
Identifying what factors affect diet breadth and how they are affected by it
allows archaeologists to make predictions about the effects on foraging societies of the
decision about whether to generalize or specialize. Having done this, it is necessary to
turn to the archaeological record to identify how this can be detected and what diet
breadth decisions were made. Excavation and laboratory identification of the resultant
materials are major undertakings in a faunal analysis, but their end product, while rich in
data, does not provide sufficient information for archaeologists with which to make
interpretations about the past. Primary data available from fish bone remains includes
the taxa present, the elements identified and any measurements taken to describe the
size of the elements. While somewhat informative in their own right (e.g., species lists),
these data are most useful when they are converted into a form that allows
interpretations about the use and importance of different fishes. Derived data that will be
used to compare the fishing strategies from various sites include the diversity and
heterogeneity of the assemblages, along with size/age estimates.
One of the simplest and most commonly used statistics in faunal analysis is
the number of taxa present (NTAXA). Although it is based on the species list of an
assemblage, it is not quite as straightforward as merely tallying the entries. One reason
for this is the necessity of selecting a single taxonomic level of specificity (i.e. species,
genus, family, order or class) to use (Lyman 2008). The choice of taxonomic level
involves a tension between trying to be as specific as possible to highlight differences
between contexts, while still including all (or most) of the data. Using Ertebølle fish
assemblages as an example, basing NTAXA on the species level may produce the
highest level of diversity in assemblages, but it may also omit certain types of fish (e.g.
sea trout or salmon) that are only identified to genus. Selecting genus as the level will
include these fish, but may exclude gadids, if they are only represented by vertebrae
and other non-species/genus diagnostic elements. Moving up the taxonomic ladder will
continually increase the inclusivity of identified specimens while decreasing the diversity
(NTAXA) of the assemblage. As an extreme example, class could be the chosen
taxonomic level: grouping specimens as either osteichthyes (bony) or chondrichthyes
(cartilaginous) fishes. Virtually all identifiable fish specimens could be assigned to one
of these categories, but assemblages could only have an NTAXA of zero, one or two –
providing little information for inter-site comparisons. There is no single ‘right’ answer to
what taxonomic level should be used; the decision depends on the research questions
to be addressed and the nature of the assemblages involved. Most importantly, the level
must be made explicit and it must be applied consistently. Based on the fishes
represented in the assemblages and their behavioural similarities and differences, the
family level is chosen as the appropriate taxonomic level for most of the analyses in this
study. (See Table 1 for a list of the families from Ertebølle assemblages and Appendix I
for a discussion of the members and other relevant information.)
There is a second, less obvious, issue involved in using NTAXA to compare
sites which involves the sizes of the assemblages. When dealing with less common
taxa, the greater the sample size, the more likely they are to be detected. Indeed, the
positive correlation between number of identified specimens (NISP) and NTAXA has
been repeatedly demonstrated (Lyman 2008; see Figure 20 for a graph of NTAXA
versus (Log) NISP for 22 Ertebølle assemblages). Using family rather than species as
groups for analyses and relying on relative abundances and diversity indices helps to
mitigate the impact of different sample sizes when comparing assemblages.
Figure 20: Correlation between NTAXA and (Log) NISP (N = 22, r = 0.55399, P = 0.0075).
Moving beyond taxonomic levels and sample size, a further complication of
using NTAXA as a means of comparing sites is that it says nothing about the degree of
overlap amongst taxa (Lyman 2008). Stating that two sites both have an NTAXA of five
may be quite misleading when seeking to compare the sites if one site has five
freshwater fishes and the other, five saltwater ones. The sites clearly have little in
common, despite sharing an NTAXA rating. This is not particularly significant when
analyzing diet breadth in terms of generalized versus specialized strategies, but it is
important to consider the actual fishes present when discussing other aspects of the
fisheries at the various sites.
Having established a measure of diversity (NTAXA), it is now possible to
begin to compare sites to see how the fish components of their faunal assemblages
differs, but further examples will illustrate why NTAXA may be even less satisfactory
than already discussed. Suppose two sites, each with three distinct contexts containing
fish as shown below:
Site A
Level 1: Gadidae, Clupeidae, Belonidae, Anguillidae, Triglidae
Level 2: Gadidae, Clupeidae, Belonidae, Anguillidae, Triglidae
Level 3: Gadidae, Clupeidae, Belonidae, Anguillidae, Triglidae
Site B
Level 1: Gadidae
Level 2: Gadidae
Level 3: Gadidae, Clupeidae, Belonidae, Anguillidae, Triglidae
Both sites have an NTAXA of five and are identical in family representation, but it is not
at all clear that the assemblages display the same diversity. One easily calculated
statistic that can help to illuminate the differences between the two sites is ubiquity, or
the frequency of occurrence of different taxa in different contexts (Lyman 2008).
Generating a ubiquity index, Site A has three out of three (100%) ubiquity for all five
families, while Site B has a three out of three (100%) index for Gadidae, but one out of
three (33.3%) for the other four families. Ubiquity can be a useful statistic, and will be
used in discussions of seasonality and fishing methods later, but since the sites from
the literature are not published in a level of detail that allows calculation of ubiquity for
their assemblages, its value for comparing sites is somewhat limited. A different
approach is needed.
Adding one more level of information (NISP) to the assemblages allows
comparison of the relative abundance of the different fishes. Calculation is very
straightforward, with the total number of specimens for each taxon divided by the total
number of specimens in the assemblage. Returning to Sites A and B, but adding
hypothetical NISP to the families produces the following information:
Site A
Level 1: Gadidae 100 specimens, Clupeidae 100 specimens, Belonidae 100 specimens,
Anguillidae 100 specimens, Triglidae 100 specimens
Level 2: Gadidae 100 specimens, Clupeidae 100 specimens, Belonidae 100 specimens,
Anguillidae 100 specimens, Triglidae 100 specimens
Level 3: Gadidae 100 specimens, Clupeidae 100 specimens, Belonidae 100 specimens,
Anguillidae 100 specimens, Triglidae 100 specimens
Site B
Level 1: Gadidae 100 specimens
Level 2: Gadidae 100 specimens
Level 3: Gadidae 900 specimens, Clupeidae 100 specimens, Belonidae 100 specimens,
Anguillidae 100 specimens, Triglidae 100 specimens
Site A now has an NISP of 1500, evenly divided among the 5 families and 3 contexts
(each layer has 33.3% of the total, and each family makes up 20% of the total in the
layer and for the site). Site B also has an NISP of 1500, but Levels 1 and 2 have 6.7%
of the total, while Level 3 has the remaining 86.7%, and Gadidae makes up 100% of the
total for the first two levels and 69% for Level 3, 73.3% for the assemblage as a whole
(the other families are each 7.7% of the total for Level 3 and 6.7% overall). Stating that
at two sites with equally large assemblages, Site B has 73.3% Gadidae and 6.7%
Clupeidae, Belonidae, Anguillidae and Triglidae and Site A has 20% for all five families
gives a clear indication of the difference between the assemblages. Clearly, relative
abundance communicates a great deal of information about an assemblage, but there is
one more measure that can be calculated to help compare multiple sites.
The Shannon-Wiener index (also called the Shannon-Weaver index or more
simply the Shannon index) is used to measure the diversity of an assemblage in terms
of its richness (NTAXA) and evenness of distribution (how equal the relative
abundances are) in one number that can be easily compared to the values from other
assemblages. It is calculated as:
H = Σ Pi (ln Pi)
where Pi is the relative abundance of the individual taxon, which is multiplied by the
natural logarithm of that relative abundance and then summed with the values for all of
the other taxa in the assemblage. The sum of the values is multiplied by negative one to
convert it to a positive number. Smaller values indicate that specimens are
predominantly from one or a few taxa, while larger values show that multiple taxa make
important contributions (Lyman 2008). For the assemblages from Sites A and B above
the calculations are:
Site A NISP Proportion ln P P(ln P)
Gadidae 300 0,200 -1,609 -0,322
Clupeidae 300 0,200 -1,609 -0,322
Belonidae 300 0,200 -1,609 -0,322
Anguillidae 300 0,200 -1,609 -0,322
Triglidae 300 0,200 -1,609 -0,322
Total 1500 -1,609
Shannon index = 1,609
Site B NISP Proportion ln P P(ln P)
Gadidae 1100 0,733 -0,310 -0,227
Clupeidae 100 0,067 -2,708 -0,181
Belonidae 100 0,067 -2,708 -0,181
Anguillidae 100 0,067 -2,708 -0,181
Triglidae 100 0,067 -2,708 -0,181
Total 1500 -0,950
Shannon index = 0,950
One important consideration when using the Shannon index to compare sites is that it is
dependent on the richness (NTAXA) of the assemblage, and thus can be affected by
the assemblage size as discussed above. Before relying on Shannon indices to discuss
inter-site variability, it is necessary to ensure that differences in the indices are not
caused merely by the sizes of the assemblages. This can be accomplished by plotting
NTAXA and the Shannon indices versus assemblage size (NISP, or more usually,
logarithmically transformed NISP) to check for correlations (Lyman 2008). This is not
necessary for Sites A and B that have equal NISP values, but will be done when
examining the archaeological assemblages. The next sections will discuss the origins of
the primary data and provide information about the contexts from which they came.
3. Creating the Record
3.1 Deposition, preservation and recovery
The first steps in the long chain of events leading up to the final conclusions
of this project began many millennia ago. The decisions made by people during the
Ertebølle period involving what fish were caught, how they were processed and
consumed, and the manner of disposal of the uneaten remains played an important role
in the creation of the archaeological data. Subsequent processes of erosion and
deposition, along with chemical and mechanical weathering of the bones also
significantly affected the fish assemblages long before the first trowel began excavating
the sites to expose the remains. Even the excavations altered the final product, as
decisions about where and how to excavate sites determined what would be recovered.
Collectively, these processes that describe the transition from fish swimming in the
ocean to the archaeological assemblage spread on the laboratory table are referred to
as taphonomy (Lyman 1994, Wheeler and Jones 1989).
3.1.1 Initial deposition
In regards to the initial deposition of archaeological materials analysts are
to some extent caught in a circular trap. While one goal of research is to understand the
processes that created the deposits, some assumptions about the nature of these
processes are inherent in the arguments constructed to interpret the data. As an
example: one goal of analyzing fish bones from archaeological sites is to gain
understanding about the ways in which fish were procured. The premise is that the
sizes and species of fish present in an assemblage are (at least partly) an artifact of the
technology used to catch them (i.e., fish traps catch a wide range of species and sizes
of fish, while hook and line fishing selects for size, and to some extent, species) (e.g.,
Greenspan 1998, Pickard and Bonsall 2004, Rick et al. 2001). However, an assemblage
that is interpreted as being largely the result of hook and line fishing because of low
taxonomic diversity and a predominance of larger fish is based on the intermediate
assumption that a representative sample of the fish that are caught are incorporated
into the deposits that are later recovered. This may be likely for activities that take place
at a home base site, but not so if they occur at a specialized procurement camp. If fish
traps were used at a specialized base camp to capture a diverse array of fish but only
selected individuals were returned to a home base, the assemblage from the home
base could end up with the signal for hook and line fishing without that technology being
a part of the fishery. The problem is further compounded if fishing technology is then
used as one line of evidence in classifying the nature of the site.
Another issue when comparing sites is chronological scale. This affects the
analysis in two regards. First, while all of the sites are from the Ertebølle period, this
covers a time span from ca. 5400-4000 B.C. Variations through time in the shapes of
projectile points and axes and other aspects of lithic technology, coupled with the
addition of pottery to the toolkit in the middle and late part of the period, provide
convincing proof that Ertebølle culture was not static (Andersen in press, Petersen
1984). In light of this, it is reasonable to ask if subsistence activities also changed, and if
so, the appropriateness of comparing deposits from earlier periods with later ones. The
short answer is that the presence or absence of change through time in fish
procurement remains an open question, although it appears present in at least some
assemblages (discussed in the Results section below). Concerning the sites included in
this project it can be seen that, with some exceptions, most of the fish material comes
from the middle or late parts of the Ertebølle period, even in sites with earlier
components (see individual site descriptions in the Materials section).
The second aspect of chronology concerns site formation: were materials
deposited over short or long periods of time, and did they accumulate steadily or
periodically (i.e., was the site used seasonally or year-round)? These questions are
especially important when seeking to answer questions about methods of capture and
processing. While a specialized subsistence strategy may provide distinctive signatures
in faunal remains (low taxonomic diversity), specialization may be confused with a more
generalist approach when multiple procurement/consumption episodes are
amalgamated into a single refuse deposit (Colley 1987:19). Similarly, seasonal markers
may prove misleading when it is assumed that all associated materials derive from the
same season in a deposit that spans many months (or even years). It is considered a
given that the assemblages used in this project were not created by singe-deposition
events, although there is some potential that some individual contexts could have been.
When characterizing the assemblages, noting their internal homogeneity (or lack
thereof) can illuminate whether the overall impression of the fishery is the result of a
consistent fishing strategy or an accumulation of many different ones. Again, careful
consideration of the nature of the deposits and explicit statements about the
assumptions used in interpretations are essential.
Certainly it is the case that deposits at many coastal Ertebølle sites are, at
least in part, outcast deposits. An advantage of these types of deposits is that the
materials seem not to display marked variation horizontally, so that samples from a few
areas of the site are more likely to capture an accurate picture of the overall situation.
Vertical variation is another story. Data from many sites are not published in a manner
that allows close examination of potential differences between layers. The shellmidden
sites of Fårevejle, Lollikhuse, Norsminde, Nederst, and to some extent, Ertebølle and
Bjørnsholm (the only ones with data available at a level of detail that allow study of
intra-site distributional variation) present a different challenge for analysis. While
shellmiddens themselves represent long-term accumulations of cultural material,
specific areas within the middens may represent very short-term events, even individual
meal deposits (Andersen 2004:402). This offers the potential for fine-grained
observations of fishing activities, but only if the relevant materials are kept separate
during excavation and analysis. Additionally, because shell middens accumulate
vertically and horizontally, samples should come from multiple layers and also multiple
areas of the site if the goal is examine possible changes over time. Because most of the
remaining well-preserved shell middens are protected areas, in many cases this will not
be possible – but archaeologists must use caution in assuming that the area that was
sampled is representative of the entire site. In the case of shell middens, this seems
more likely to not be the case. Analysis of fish remains from Nederst has shown that
different areas of the midden can have very different assemblages (see more about this
in the Results section), and this is also true of the material from Norsminde (Enghoff
1989:45). The Ertebølle, Bjørnsholm and Fårevejle shellmiddens suffer from a limited
sampling breadth, as in each case the fish remains were taken from a trench that
transected the midden in one location (Enghoff 1986 and 1991). Considering that the
trench excavated at Bjørnsholm was (mostly) one meter wide in a midden that was
estimated to extend over 325 meters in length (Andersen 1993), some skepticism is in
order as to the representativeness of the sample. More information about the extent of
excavation and nature of the individual sites and deposits appears below.
3.1.2 Post-depositional events
After initial deposition, the second stage of taphonomy concerns the long
interval up to the time of the bone’s ultimate recovery. Understanding this journey is an
essential, but exceedingly complicated, part of any faunal analysis. Not all of the bones
that were initially present are preserved or identifiable today. This can be true because
of the nature of the bones themselves (bones with a higher fat content and poorly
ossified specimens are less likely to preserve in an identifiable form), because of how
the fish were processed for consumption (with boiling or eating fish whole being
especially damaging to preservation potential), because of scavenging by dogs or other
animals, or due to environmental impacts (chemical or mechanical weathering) (Butler
and Schroeder 1998, Jones 1986, Lyman 1994, Nicholson 1992, 1993, 1996a, 1996b,
1998, Wheeler and Jones 1989). Even those bones that survive can be transported
from their original location by bioturbation or geological processes.
The extent to which differential preservation affects assemblages is
particularly vexing, in no small part because it involves negative evidence. Are certain
types of bones absent because they were not preserved or because they were never
deposited in the first place? Nicholson’s experimental studies of fishbone preservation
under varying conditions (1996a, 1996b, 1998) present an actualistic approach to this
question that is invaluable for the insights it offers, even if her ultimate conclusions
(attempts at quantifying archaeological fishbone are ‘frequently unhelpful’ and most
contexts should be described merely on the presence/absence of species) displays a
singular lack of optimism for scientific problem-solving and ignores a great deal of work
addressing the impact of differential preservation of faunal remains on interpretations
(e.g., Behrensmeyer 1991, Lyman 1991, Marean 1991, Marean and Spencer 1991,
Nichol and Wild 1984, Stiner 1992). Some of the results of Nicholson’s work are
predictable: fish bones often deteriorate more rapidly than other types of bones, even
from animals of the same size and weight (living in water in a state of neutral buoyancy,
fish skeletons do not have to withstand the same gravitational stresses that terrestrial
animals do, and thus are less robust) and gadid caudal vertebrae breakdown at a faster
rate than thoracic vertebrae (caudal vertebrae are smaller and less robust than thoracic
vertebrae from the same fish) (Nicholson 1996a). Other results are less obvious, or
even counter-intuitive: soil pH and drainage, while playing a role, may not be the
primary determinant of bone survivorship (microbial action may be the critical factor),
food preparation affects bones in different ways depending on the method (filleting
exposes bone immediately to destructive agents, hastening the start of decay, baking
seemed to have little effect, while boiling greatly increased the deterioration of bone), in
some cases, herring (with small, oily bones) survived in contexts where cod (with large,
low-fat bones) did not, and the appearance of bones was a poor predictor of collagen
preservation in them (Nicholson 1996a, 1996b, 1998). While some of these results may
have important implications for archaeological analysis, it is important to note that the
experiment ran over the course of seven years – whether some or all of these patterns
would hold up over thousands of years cannot be stated with certainty. A further study
by Nicholson attempted to determine if bone density was a good predictor of which
elements would survive, and again counter-intuitively, concluded that it was not. This
was not an actualistic study, instead attempting to measure the density of bones (using
water displacement as the volume measure) and then using the derived densities to
rank elements in a predicted survivorship ranking. When compared against the actual
proportions of elements from three archaeological sites in the United Kingdom, she
found no correlation between density and relative abundance. The shape of the bone
seemed to be the relevant factor in predicting which bones were more likely to survive
(Nicholson 1992). As the author herself acknowledges, there are serious potential
problems with her approach to measuring the volume of the bones (and by extension,
the derived density measures). Furthermore, bone density varies within elements. Given
that archaeological specimens are rarely whole elements, an average density value for
an element may bear little relationship to the actual density of the part that is usually
recovered. At the least, these studies suggest the importance of questioning
assumptions about taphonomic processes before accepting their implications.
Experimental archaeology is not the only path to exploring the effects of
differential preservation, and as seen in some of the other works cited in the paragraph
above, several researchers have approached the problem with inductive reasoning. By
examining patterns of relative abundance both between species and between individual
elements within the same species, inferences are drawn about the degree to which an
archaeological assemblage has been altered by taphonomic effects. Russ and Jones
(2009) develop a method of evaluating the survivorship of different skeletal elements in
their study of the fish remains from a Paleolithic cave site in the Apennine Mountains of
central Italy. The method identifies a minimum number of individuals (MNI) that must
have been present to account for the most common element in the assemblage for each
taxon (ignoring size) and then uses the number of each type of bone in a skeleton (e.g.,
every fish has two dentale) to predict the minimum number of each element that should
have originally been present. The actual number of that element is divided by the
predicted number to derive what proportion of the expected number was actually
identified. In this way it is possible to quantify which elements actually had the best
survivorship. In their study of Salmo trutta, some elements associated with the oral
region survived the best, with other cranial elements and vertebrae faring much worse
(Russ and Jones 2009: 157). Different taxa would be expected to vary in their elemental
survivorship rates based on element density and morphology, but in general it might be
expected that elements associated with the jaws, which experience more stresses,
would be more resilient. This general pattern was confirmed in the assemblages
analyzed for this project, although not for Pleuronectidae (see further discussion in
Section 5 Results).
Other approaches to evaluating differential preservation of the materials
include qualitative assessment, calculating the ratio of identified to the total amount of
fish bone, and quantifying the degree of vertebra fragmentation. Qualitative statements
about the condition of specimens can be an important source of information about how
well preserved an assemblage is, but are difficult to compare between assemblages
and (especially) between analysts. Examining the proportion of the bone that was
identifiable (either by count or by weight) offers some information about the condition of
the bones in a quantified manner, although it is a very rough characterization and
suffers from a number of methodological flaws (discussed more fully in the Results
section). For some assemblages that were analyzed for this project, an attempt was
made to characterize the condition of the vertebrae by assigning them to categories
depending on the degree of completeness. This approach has its own problems;
nonetheless, the results show that the identified vertebrae in these assemblages
generally survived in a fairly complete state, suggesting that preservation was relatively
good. As indicated in the beginning of this section on post-depositional processes, this
stage of taphonomy is complicated and difficult to assess. The more lines of evidence
that are introduced, the more confidence is created in the assessment of bone
survivorship.
3.1.3 Excavation
The decisions made by archaeologists about where and how to excavate
have an enormous impact on what faunal remains are recovered and can potentially
create a very significant bias in the results. At the broadest scale, which locations are
recognized as containing archaeological remains and determined to warrant excavation
depends on numerous factors. It is a certainty that not all of the places that originally
had Ertebølle settlements still survive with material evidence of this occupation today,
and it is almost as certain that not all of the surviving sites have been located. Even of
the known sites, not all have been subject to excavation. In short, the materials
available for analysis are a sample of a dataset of unknown size and their
representativeness is not assured. This limitation is certainly not unique to fish bone
analyses, nor is it reason to abandon them. Short of adopting a nihilistic philosophy of
epistemology (and abandoning archaeology altogether), the practical effects of
recognizing this sampling problem are restricted to encouraging further fieldwork and
remaining open to reinterpreting the existing evidence based on new finds. On a
narrower scale (that of the individual site) sampling questions have important
implications for representativeness, as discussed concerning chronology in the initial
deposition section above. Some sites have been excavated in their entirety (i.e.,
Norsminde), but this is rare. The more common situation of one or more trenches
sampling parts of the deposits requires due consideration of the nature of the site and
its probable extent in forming judgments about how well the sample represents the
whole. Information about the size of the excavations at the individual sites is given in the
site descriptions below, as well as an indication of the nature of the deposits.
How a site is excavated is as important as the decision of where to
excavate in regards to the representativeness of the sample. Regarding fish bone
assemblages, screening activities are probably the most important influence. Whether
matrix is screened and if so, if matrix is washed through or dry-screened, combined with
the decision of what mesh-size screens are used all factor into what fish bones will be
recovered from a site. Predictably, bones from smaller fishes (e.g., Clupeidae) are
recovered more frequently when smaller mesh-size screens are employed. Experiments
with different size screens to quantify the effects of differential recovery from two sites
are fully described under the individual site descriptions for Asnæs Havnemark and
Dragsholm in the Materials section, and the findings (including some data from Nederst)
are in the Results section. Briefly, bulk matrix samples were taken from the deposits at
the two sites and processed through a series of nested geologic screens to separate the
remains into 4, 2 and 1 mm fractions. Fish bones were sorted from each fraction and
identified, allowing an assessment of how using progressively smaller mesh-size
screens would have altered the overall assemblage (recovered with 4 mm mesh).
3.2 Laboratory analysis
Evaluating the ways in which initial deposition, subsequent preservation
and finally, excavation decisions and methods affect faunal assemblages is commonly
recognized as an important step in assessing factors that have altered the information
available for archaeological interpretation from that originally created by past human
societies. Less thought is generally given to the ways in which laboratory analysis of the
bones also affects the data. Proper identification of the bones depends upon the
comparative collection available (and to a lesser extent, other sources of information
such as published and online references), the skill of the analyst and decisions about
how to record identified specimens. When, where and how measurements of length and
weight are taken also determine what information is produced by the analysis.
As part of this project, the author developed a personal comparative
collection of some of the more common fish available in the North and Baltic Sea areas.
Currently, this consists of 47 individuals encompassing 39 different types of fish. The
fish were primarily obtained from commercial sources (fishmongers), with a few caught
by sport fishing (the author or his father). Most of the fish were obtained in Denmark,
although the pike and walleyed pike were caught in Wisconsin, and some of the fish
purchased from fishmongers may have come from some distance away from the study
area (e.g., anchovy and sardine). Preparation of the specimens involved boiling/soaking
in clean water, and manual removal of soft tissues. See Appendix II for a list of the
species in the author’s collection. Recognizing that this collection was not complete
either in regards to the range of species or to the size/age groups within species,
access to the comparative collection at the Archaölogisch-Zoologische Arbeitsgruppe of
the Archaölogisches Landesmuseum at Schoss Gottorf in Schleswig, Germany was
established to provide broader species coverage. The collection in Schleswig is
recognized as one of the largest and most complete comparative fish assemblages in
Northern Europe. Several multi-day trips to the museum allowed identification of some
of the more difficult specimens, not least because of the assistance of Dr. Ulrich
Schmölcke and Dr. Dirk Heinrich. Additional information on fish bone morphology,
taxonomy, biology and methods of identification came from published and electronic
resources (v. Busekist 2004, Cannon 1987, Casteel 1976, Enghoff 1994a, Härkönen
1986, Marine Fish Identification Portal 2009, Matsui 2007, Muus and Dahlstrom 1964
and 1967, Wheeler and Jones 1989).
Inter-analyst variation in the identification of fish bones is an especially
under-addressed problem; no doubt in part because of a lack of desire on the part of
practitioners to highlight the embarrassing fact that some identifications are erroneous.
One exception to the general silence on this topic comes from a study involving five
analysts considered experts in fish bone identification (three with PhDs in Anthropology,
one with a PhD in Zoology, and one PhD in Wildlife and Fisheries Biology) who
independently analyzed the same group of approximately 120 fish specimens (Gobalet
2001). Multiple types of variation are evident in the results of the identifications, but of
particular note are the inter-analyst discrepancies in the number of identified specimens
(from a low of 53 to a high of 69) and the number of species (from a low of 4 to a high of
18). Considering that many fish assemblages from Ertebølle sites are at least one to
two orders of magnitude larger than the one used in this study, the potential for analyst
bias to significantly skew results is certainly present. Fortunately, analysis of Ertebølle
period assemblages from Denmark has been conducted by relatively few individuals
(although the actual number is at least seven, the vast majority have been identified by
either the author or Inge B. Enghoff). Late Mesolithic assemblages from Northern
Germany and Southern Sweden have primarily been identified by Ulrich Schmölcke and
Leif Jonsson, respectively. Still, the possibility for error remains. Among the solutions
that Gobalet recommends is only accepting identifications when the comparative
methods and criteria of discrimination are explicitly discussed (2001). Appendix I
discusses the types of fish found in Ertebølle assemblages and the general and specific
issues involved in identifying their remains.
One group of fishes that deserves special attention consists of species that
have been identified in Mesolithic assemblages but are extremely rare or absent in
Danish waters today. Fish in this category include anchovy (Engraulis encrasicholus),
smoothhound (Mustelus sp.), common stingray (Dasyatis pastinaca), European sea
bass (Dicentrarchus labrax), black sea bream (Spondyliosoma cantharus) and
swordfish (Xiphias gladius) (Enghoff et al. 2007). There are two issues that their
presence raises. First, the existence of these species in archaeological assemblages,
outside of their current (more southerly) ranges, is often cited as supporting evidence
for warmer climactic conditions during the Late Mesolithic period (e.g., Enghoff 1991,
Enghoff et al. 2007). A second and less favorable result of acknowledging the presence
of species that are not currently indigenous to Danish waters is that it greatly expands
the list of potential species for identification purposes for all archaeological specimens.
No comparative collection can contain enough individuals to comprehensively document
the whole piscine fauna of the Atlantic Ocean and related waters and, even if one
existed, it is doubtful that an analyst could search out every possible match for an
element before identifying it. Part of faunal analysis is developing an understanding of
the geographical and chronological conditions that limit the number of potential species
to a manageable quantity. When some southerly species are identified the pool of
possible matches for other specimens increases, too. The result is that species
identifications often become somewhat less reliable, although this varies by family or
order by the number of members. In practice, this emphasizes the tension between
accuracy of identification and the level of taxonomic specificity chosen and supports the
selection of the family level as most appropriate.
Other than weights, metric data was only collected on a few selected
elements: Anguillidae ceratohyale and cleithra, Gadidae and Pleuronectidae first
vertebrae and Gadidae otoliths. Many other elements can be measured and other fishes
could have been included (Morales and Rosenlund 1979), but it was judged unlikely that
the greatly increased time required would have provided sufficient additional information
to justify the effort. Measurements were taken with a digital caliper accurate to 0.1 mm
in the locations as shown in Figures 21-24.
Figure 21: Anguillidae ceratohyal measurement. Figure 22: Gadidae otolith
measurement.
Figure 23: Anguillidae cleithrum measurement Figure 24: Vertebra measurement (not a first
vertebra).
4. Materials
4.1 Sites analyzed for this project
The assemblages that were analyzed for this project were selected either
because of the author’s participation in the excavations (Asnæs Havnemark,
Dragsholm, Fårevejle and Jesholm I – all under the direction of T. Douglas Price) or at
the request of the principle investigator (Bøgebjerg – T. Douglas Price, Havnø – Søren
H. Andersen, Lollikhuse – Søren A. Sørensen and Nederst – Niels Axel Boas).
Summary results for each site are presented in Appendix III and full results in Appendix
IV.
4.1.1 Asnæs Havnemark:
The fish remains from this site are from an excavation that took place in the
summer of 2007 under the direction of T. Douglas Price. Six excavators working for 5
weeks (from June 18th to July 20th) opened up a series of test pits and 3 trenches (see
Figure 25). Excavation of the trenches was carried out by means of shovel and trowel
(Figure 26), with the matrix being water-screened in the field through 4mm mesh-size
sieves. In addition to a large quantity of flint tools and debitage, Ertebølle and TRB
pottery as well as animal remains were recovered. Much of the animal bone was from
fish. Although squares were excavated according to natural layers, radiocarbon dates
indicate that the materials derive from a relatively short (approximately 300 year) time
span at the end of the Late Ertebølle and beginning of the Early TRB periods. Still,
materials from the layers were kept separate during excavation and analysis (see Table
2 for the distribution of fish remains by layer).
Figure 25: Excavations at Asnæs Havnemark (drawing courtesy of T. Douglas Price).
Square meters Weight (g) NISP
Trench 1
Culture layer 6 942 11808
Grey layer 2 106 1307
Other 1 28 228
Total 9 1076 13343
Trench 2
Culture layer 7 235 3538
Other 2 28 220
Total 9 263 3758
Trench 3
Culture layer 3 1116 17447
Shell 3 375 5612
Brown surface 2 422 4301
Total 8 1913 27360 Table 1: Distribution of fish remains by trench and level at Asnæs Havnemark.
The first column of the table (Square meters) refers to the number of individual squares
that produced fish bone material for that provenience and is not the same as the total
number of squares excavated. The culture layer was a very dark brown or black layer
that contained most of the finds (including fish bones). Underneath that, in some places,
was a continuation of the culture layer with a relatively high content of shells,
designated the shell layer. In Trench 1, the layer underneath the culture layer was
named the grey layer, while in Trench 3 the layer underneath the shell layer was the
brown surface. The contexts labelled ‘other’ include a few remains taken from a backdirt
pile from Trench 1 and a small sample of a second culture layer about a meter below
the first in Trench 2, discovered while cleaning the profile prior to making a section
drawing. This deeper culture layer was not otherwise excavated. The table makes clear
that the majority of the fish remains come from the culture layer.
Figure 26: Trench 3 at Asnæs Havnemark.
During the excavation of Trenches 1 and 2, it was quickly realized that
recovery of the large numbers of fishbones present would create an insurmountable
obstacle to excavation across an area broad enough to answer questions about the
nature of the site in the time available. The decision was made to take samples from
Trench 3 that would allow inferences about the nature of the unexamined deposits. In
light of this, it should be noted that while most of the squares in Trenches 1 and 2 have
samples taken by water-screening through 4 mm mesh-size screens, only selected
squares in Trench 3 have similar treatment. In addition to the 4 mm mesh-size water-
screening, experience from the site of Dragsholm had suggested the need for samples
that incorporated a smaller screen size to test the effects of differential recovery. To this
end, bulk samples of 2 liters (in one case, 5 liters – square 135 East, 133 North, culture
layer) were taken from several of the proveniences and washed through nested
geologic screens of 8, 4, 2 and 1 mm sizes. The 8 mm screen was used to quickly
remove larger stones and protect the more delicate faunal material; fish bone from this
fraction was immediately after combined with the 4 mm fraction for identification. The
matrix from the 2 and 1 mm fractions was sorted with the aid of a binocular microscope
(4-6x magnifications Nikon SMZ 800) to ensure complete recovery. Identification of the
1 mm fraction bones was done under 6-12x magnifications using a Wild Heerbrugg
binocular microscope. Although an attempt was made to identify as many elements as
possible in the 4 and 2 mm fractions, only vertebra were identified in the 1 mm fraction
(although stickleback dorsal spines, flounder dermal denticles and spurdog teeth were
also noted, but not included in the bone counts from these samples).
For the rest of the assemblage, sample weights were taken with an
electronic scale accurate to 1 gram, and for the larger samples, weights were taken for
the total non-vertebral elements, Gadidae vertebrae, Anguillidae vertebrae and the rest
of the identified vertebrae separately. Non-vertebral specimens were identified as to
type of fish, element, and where appropriate, side. Selected elements (some first
vertebrae, Anguillidae ceratohyal and Gadidae otoliths) were measured with an
electronic caliper accurate to 0.1 mm for use in size estimations. This same general
procedure was followed for all of the other assemblages, with a few exceptions and
variations. In all, 47,760 specimens were identified from Asnæs Havnemark, from 17
fish families.
4.1.2 Dragsholm and Bøgebjerg:
The recent excavations at the site of Dragsholm – those that produced the
fish bone assemblage presented in this report – were excavated over the course of
three summers (2002-2004) under the direction of T. Douglas Price. The first summer’s
campaign consisted of just one week in August, when a series of 5 test pits and one
trench (measuring 1x20 m) were put in to test the presence and preservation of
materials at the site (see Figure 27). Five personnel were involved in the excavation.
Because of time pressures excavation proceeded relatively rapidly, although water-
screening (with 4 mm mesh screen) was used to facilitate recovery of smaller artifacts
(i.e., fish bones). Not all squares and layers were screened, and none of the fish
materials from this trench (Trench 2) have so far been analyzed. Results from this first
season were very promising, with a large quantity of lithic and organic remains
recovered. Fish bone totaled 722 grams. (See Table 3 for a complete listing of fish
remains by trench and level for Dragsholm and Table 4 for Bøgebjerg, but note that
parts of some trenches were not excavated and/or screened to recover fish bones.)
Year Square meters Total weight ID weight NISP
Trench 2
Level 6 2002 1 2 0 0
Level 7A 2002 1 1 0 0
Level 7C 2002 10 693 0 0
Level 7D 2002 1 4 0 0
Level 9 2002 4 22 0 0
Total 17 722 0 0
Trench 3
Level 7 2003 2 3 0 0
Level 7A 2003 4 8 1 1
Level 7B 2003 3 23 0 0
Level 7C 2003 9 1300 358 2161
Level 7D 2003 6 497 2 9
Level 8 2003 5 395 76 356
Level 9 2003 1 14 0 0
Total 30 2240 437 2527
Trench 4
Level 7A 2003 4 133 0 0
Level 7B 2003 6 1573 249 1585
Level 7C 2003 6 401 1 5
Level 8 2003 1 5 0 0
Total 17 2112 250 1590
Trench 5
Level 7A 2003 3 62 0 0
Level 7B 2003 8 224 56 618
Level 7C 2003 7 859 160 1054
Level 8 2003 6 1308 118 662
Level 10 2003 1 1 0 0
Total 25 2454 334 2334
Trench 11
Level 6 2004 3 3 3 3
Level 7A 2004 10 78 78 459
Level 7B 2004 10 813 813 5357
Level 7C 2004 11 2696 2696 20887
Level 8 2004 10 1060 1060 5906
Total 44 4650 4650 32612 Table 3: Distribution of fish remains by trench and level at Dragsholm.
The stratigraphy within the deposits is rather distinct (see Figure 28),
representing a series of marine transgressions and regressions followed by later peat
development, re-deposition of fill when the drainage canal was dug and plowzone. Level
6, a sandy layer with a high content of rocks and archaeological materials, likely
contains materials eroded from higher areas during the final major marine
transgressions. Ceramic typology and the presence of cattle teeth suggest a Neolithic
date for the material, but in any case, very little fish bone was recovered from these
deposits. Levels 7A, 7B and 7C are sandy deposits distinguished from each other by
the particle size of the sands, iron oxidation marks, and color (probably resulting from
different inclusions in the sand such as charcoal). These deposits are also interpreted
as being affected by transgressions/re-deposition, although perhaps to a less extreme
extent than Level 6. Materials in these deposits date to the Late/Middle Ertebølle, based
on lithic typology and the presence of Mesolithic ceramics. The deepest level to produce
significant amounts of fish bone is Level 8, thought to be largely in situ outcast deposits.
Typologically, the materials date to the Middle Ertebølle period, a conclusion supported
by a radiocarbon date on red deer bone of 5019-5000 B.C. (AAR-8189) (Price 2004).
Figure 28: North wall of Trench 11 displaying clear stratigraphy.
Square meters Weight (g) NISP
Level 1 5 10 97
Level 2 1 <1 1
Level 3 2 60 372
Level 5 3 31 303
Level 7 6 161 1776
Other 4 3 43
Total 21 265 2592 Table 4: Distribution of fish remains by level at Bøgebjerg (Trenches 2 and 3 combined).
The deposits from Bøgebjerg seem to be somewhat earlier than those at
nearby Dragsholm (based on flint typology and the absence of ceramics), but still within
the Ertebølle period. Some of the same processes of transgression/regression with the
resultant erosion and re-deposition of materials undoubtedly took place here, although
layer descriptions are somewhat vaguer for these deposits. From the field notes: after
testing a few samples and recovering very little, Levels 1 and 2 were not screened
during excavation. Level 1 is described as decomposed gyttja and Level 2 a
decomposed peat. Level 3 is described as a very thin lens (or pockets) of fine sand
overlying the reddish-brown clay of Level 4, although the labels of the fish bone
samples indicate they came from Level 3 (none from Level 4). Level 5 is grayish- to
yellowish-brown sand with some silt mixed in. Level 6 contains coarse sand and gravel,
similar in some regards to Level 6 at Dragsholm, probably resulting from erosion and re-
deposition of other deposits. No fish bones were found in this layer. Finally, Level 7 is a
siltier layer, distinguished by the presence of shell (especially mussel). It contained the
majority of the fish bones found at the Bøgebjerg.
In 2003, another campaign of excavation was conducted with 11
excavators working over the course of 8 weeks (although not all participated for the
entire period at this site). A second series of 6 test pits was excavated to further define
the extent of the archaeological deposits and the site stratigraphy. Afterwards, Trenches
3, 4 and 5 (14, 20 and 16 square meters respectively) were excavated by hand (shovel
and trowel), with water-screening of the matrix from many of the proveniences. Again, a
large quantity of artifacts was recovered, including 6806 grams of fish bone. In a search
for materials and/or features from the part of the site that was dry land during the
periods of occupation, a series of 5 trenches (Trenches 6-10) were machine-excavated.
No fish bone material (and little material of any kind) was found in these trenches.
Approximately one hundred meters north of the site of Dragsholm, another site,
Bøgebjerg, was also excavated in 2003 (after testing with one trench in 2002). A series
of 6 trenches comprising over 140 square meters was excavated by machine and hand,
with water-screening of some of the deposits. A total of 265 grams of fish bone was
recovered, all of it from Trenches 2 and 3. This material has been analyzed, and is
included in the results section.
The final campaign at Dragsholm was in 2004, when 6 excavators worked
for about 2 weeks on Trench 11 – a 16 square meter area immediately north of Trench
5. This trench was extremely rich in fish remains (and other artifacts). A total of 4650
grams of fish bone was recovered. Of particular interest was the large number of
Gadidae otoliths recovered from this trench, especially concentrated in four square
meters of Level 8. In addition to the regular water-screening of matrix with 4 mm mesh,
13 small samples (approximately 10 liters total) were processed through nested
geologic screens to check for the presence of small bones that might be missed using
the 4 mm mesh. The samples were originally taken from Layer 7B, based on the
observation by the excavators that some areas of this layer seemed to be especially
rich in charcoal and smaller bones. Later, samples were taken from other layers for fine
screening. Unfortunately, the samples from layers other than 7B contained few fish
bones – limiting the potential for comparison. The samples were processed by drying,
then sifting through nested 8, 4, 2 and 1 mm geologic screens, with the bones from the
8 and 4 mm screens combined for analysis. Fish bones were picked from the various
fractions by visual inspection – with the 1 mm fraction done under 4-6x magnifications
using a binocular microscope (Nikon SMZ 800). Similar to the samples from Asnæs
Havnemark, identification of the 1 mm fraction bones was done under 6-12x
magnification using a Wild Heerbrugg binocular microscope, and an attempt was made
to identify as many elements as possible in the 4 and 2 mm fractions, but not in the 1
mm. Only vertebra were identified in the 1 mm fraction (although stickleback dorsal
spines, flounder dermal denticles and spurdog teeth were also noted, but not included in
the bone counts from these samples). Results of this screen-test experiment are
presented later. Dragsholm produced 40,502 identified specimens, from 18 families,
while the Bøgebjerg assemblage was 2592 specimens from 10 families.
4.1.3 Fårevejle:
Investigations at Fårevejle that produced the fish remains included in this
project were conducted in the summers of 2004 and 2005, again, under the direction of
Dr. T. Douglas Price. In 2004, 8 excavators working for 6 weeks opened up a trench 2
by 19 meters, with additional areas opened by machine to expose stratigraphy and
search for features outside of the shell midden (see Figure 29).
Figure 29: Excavations at Fårevejle (note that all elevations below 3.0 asm are the
same shade of grey). (Map by K. Ritchie)
Fish remains were recovered from 16 square meters: a total of 210 grams.
Deposits were hand excavated and water-screened through 4 mm mesh to recover
artifacts. Work was resumed in the summer of 2005, primarily focused on removing a 2
by 2 meter baulk that was left in place in the middle of Trench 1 in the first season. A
second trench (10 square meters) was opened 8 meters away, but very few fish
remains (about 8 grams total) were recovered in this area. Trench 1 provided an
additional 70 grams of fish bone material (site total, both seasons = 288 g). The midden
area in Trench 1 was separated into seven natural layers (and several sub-layers)
during excavation based on the color and texture of the matrix, the types and amount of
shell in the matrix, whether it was predominantly burnt, crushed or whole shell, and the
number and size of rocks (see Table 5 for a breakdown of where the fish remains came
from and Figure 31 for a section photograph). Levels 2-4 may be mostly Neolithic
deposits (based on ceramic typology), whereas Level 5 and below date to the Ertebølle
period. The distribution of fish bones within the midden was not uniform (nor was the
thickness of the midden or the individual levels). Figure 30 shows how the number of
fish bones varied in the midden on a North-South transect.
Square meters Weight (g) NISP
Trench 1
Level 2 1 <1 4
Level 3 3 14 127
Level 4 8 48 366
Level 5 10 88 953
Level 6 18 102 981
Level 7 11 25 209
Level 8 5 3 41
Other 2 <1 2
Total 58 280 2683
Trench 2 14 8 55 Table 5: Distribution of fish remains by level at Fårevejle.
Figure 30: Horizontal distribution of fish remains in Trench 1 at Fårevejle.
Fish remains recovered from earlier excavations at Fårevejle include one specimen
Anguillidae, 38 specimens Gadidae, and 8 specimens Pleuronectidae (Degerbøl
1945:146, Winge 1900:121, cited in Rosenlund 1976:31). The recent excavations and
analysis resulted in an assemblage of 2738 identified specimens from 12 different
families of fish.
Figure 31: Western wall of Trench 1 (108 and 109 North) at Fårevejle.
Figure 32: Excavation in Trench 1 at Fårevejle.
4.1.4 Havnø:
Havnø is a shell midden site on the eastern coast of the Jutland peninsula
that has been under excavation by Søren Andersen for the past several years (Figure
33). The site has both Mesolithic and Neolithic deposits; some of the fish remains may
date to the more recent period. In general, fish bones are not common in the midden
(although not all of the matrix was screened). The 114 samples analyzed for this project
included only 330 identified fish bones, limiting the potential discussion of the
assemblage. However, like Jesholm I, Havnø is notable for the wide variety of fishes
appearing in a small assemblage, with at least nine families represented. Five
specimens of Anguillidae and 2 of Pleuronectidae are recorded from excavations
conducted in 1888 and 1894 by the National Museum (Degerbøl 1945:133-146, Winge
1900:110, cited in Rosenlund 1976:32).
Figure 33: Excavation at Havnø in 2006.
4.1.5 Jesholm I:
Excavations at Jesholm I on the northern coast of the Djursland peninsula
took place over the course of three months in the spring of 2008 (Figure 34). Although
preservation of organic materials (wood and bone) was good, very few fish bones were
recovered during excavation. Outcast deposits were repeatedly sampled (approximately
10 liters at a time), using water-screening with 1.5 mm mesh-size screens, but
ultimately only 11 samples produced fish bones (and four additional specimens were
recovered without screening). A total of just 38 specimens were identified (an additional
18 vertebrae and two otoliths were recovered but not identified). The very small sample
size limits interpretation, but it is noteworthy that the assemblage includes
representatives of seven different families of fish. Typologically, the layers that
contained fish bone can be assigned to the Early Ertebølle period.
Figure 34: Almost underwater archaeology at Jesholm I.
4.1.6 Lollikhuse:
Lollikhuse is a shell midden site near Roskilde fjord in northern Zealand,
best known as the location of one of the rare Ertebølle house features. Excavated under
the direction of Søren Sørensen over the course of several seasons beginning in 1989,
the site has produced a large quantity of fish remains, a portion of which (2669
specimens representing 8 families) have been identified for this project. In all, 91
samples covering 36 square meters (in places divided into up to six 10 cm levels) have
been analyzed. The great majority of the fish remains come from outcast deposits, with
nine samples (93 specimens) coming from an area that may have been dry land when
they were deposited. The house feature at the site is dated typologically by flint artifacts
in the fill to the Early Ertebølle period, but other parts of the site also have Late
Ertebølle materials. At this point it is not possible to date the fish samples with more
precision than the extended Ertebølle period. The assemblage was recovered in the
field by dry-screening, using a 4.5 mm mesh-size (Søren A. Sørensen 1992 and
personal communication 2008).
4.1.7 Nederst:
The materials from this site are the results of excavations conducted over a
series of five seasons (1987-1992). While a final report has not been written, field notes
indicate that the site is a shell midden consisting of three distinct deposits (skaldynge
‘shell heap’ I, II and III). The result of an analysis of fishbone samples from skaldynge II
has been published in summary form (Enghoff 1994a), while samples from skaldynge I
were analyzed as part of this project. Skaldynge I was the largest of three areas,
estimated at 130x50 m. Both human and dog burials (see Figures 35 and 36) were
excavated from the area. Skaldynge II was the smallest of the three (45x20 m), but it
also contained human burials. Skaldynge III was discovered just north of skaldynge II,
with an estimated size of 75x35 m. In addition to the burials, notable finds include six
fishhooks and at least one fishhook preform. The numerous burials, rich material culture
and large fish bone assemblage make Nederst a very interesting Ertebølle site, but the
lack of publication makes interpretation of the results somewhat difficult. As will be
shown later in the Results section, the spatial heterogeneity of the fish assemblage at
Nederst is an important characteristic that warrants further investigation as more
information becomes available.
Figure 35: Human burial from Nederst (photo courtesy of Niels Axel Boas).
Figure 36: Dog burial from Nederst (photo courtesy of Niels Axel Boas).
The previously published assemblage (6476 specimens) from skaldynge II
was identified from 19 samples from 15 square meters covering four levels and four
features (see Table 6 for complete sample information). Although the results for the
individual contexts are not known, it is clear that the majority of the samples originate
from either the designated shell layers (S) or Level C5, reported as the culture layer with
some shell, a high charcoal content, many animal bones, and ceramics from both the
Ertebølle and Neolithic periods. Level C10 describes the areas around the stone and
clay-built fireplaces and is described as especially rich in charcoal particles. Level B lies
underneath the shell midden, and contains much gravel and some grayish materials
that are intrusive from the overlying culture layer. Materials from skaldynge II date from
the whole of the Ertebølle period and some part of the Neolithic, although more specific
dating of the contexts is not yet available. The majority of the fish bones are thought to
derive from the Mesolithic parts of the deposits. Recovery of fish bones was aided by
water-screening in the field using 6 mm mesh-size screens, with some samples
processed through 1.5 mm screens to test the effect of differential recovery.
X East North Level Other level Feature
3712 309 328 C5 S
3492 311 328 C5 S
3553 312 329 C5 S
3478 313 330 C5 S
3768 314 329 C5 S
3973 318 335 S
3872 318 337 C10 Stone fireplace
3907 319 336 C10 Stone fireplace
4000 321 335 S
3948 321 335 C5 S
4049 321 336 B
4025 323 336 S
3906 323 336 S
3886 323 336 C5 S
3922 324 336 S
3669 324 340 Trashpit
3433 324 340 Trashpit
4062 325 336 C10 S Stone fireplace
3915 C10 Stone fireplace Table 6: Context information for samples from skaldynge II at Nederst.
Fifteen samples from 12 square meters, covering 5 levels and one feature,
were analyzed from skaldynge I as part of this project (see Table 7 for specific sample
information and Table 8 for fish distribution by level – weights are not available). As with
the skaldynge II assemblage, most of the samples come from either the shell layers or
Level C10 (note that several samples have two layer designations, with the second
being shell). Additional levels include: Level C12, a culture layer in the shell midden with
crushed and whole shell (especially oysters), level C13, a mixture of fire-reddened
sand, burnt crushed shell and charcoal particles and Level C20, grey-black and brown-
black culture layer in the area of fireplaces, filled with charcoal particles and crushed
shell. Typological dating places most of the deposits in the Ertebølle period, with Level
C20 attributed to the Younger Ertebølle. The identified assemblage from skaldynge I at
Nederst consists of 13,779 specimens from 12 families.
X East North Level Other level Feature
108 199 299 Dog burial
4915 201 297 S
5110 202 298 C12
8484 251 290 C10
8813 251 290 C13 S
8502 252 289 C10 S
8594 252 289 C13
8492 252 290 C10
8566 252 290 C13
8769 252 297 C10 S
9110 256 300 C20 S
9483 257 303 S
9347 259 305 C20 S
9469 259 306 C20 S
9394 260 304 C10 S Table 7: Context information for samples from skaldynge I at Nederst.
Square meters NISP
Level 10 5 1931
Level 12 1 2034
Level 13 3 368
Level 20 3 3620
Shell 2 4969
Other 1 857
Total 15 13779 Table 8: Distribution of fish remains by level for skaldynge I at Nederst.
4.2 Sites from the literature
Previously published records of fish remains from coastal sites of the
Danish Ertebølle can be divided into three categories: 1) large, recently analyzed
assemblages from modern excavations published in considerable detail (i.e., Ertebølle,
Bjørnsholm, Norsminde and Smakkerup Huse), 2) recently done but small assemblages
(i.e., Ronæs Skov and Agernæs) or recently excavated and analyzed assemblages that
are only presented in summary form, and 3) the results of older excavations and/or
analysis, which in many cases include a very small number of specimens. All of these
sites offer information about fishing during the Ertebølle period, but the size and quality
of the data sets varies, necessitating different treatments.
The first group, which contains the most useful and comparable data, is
worth considering in some detail. As the locus classicus for the period, the shell midden
at Ertebølle, on the Limfjord in northern Jutland, seems an appropriate place to begin.
Excavations in the late 19th century produced a small, but impressively diverse (8
families) assemblage, including 25 Gasterosteidae specimens (Gasterosteus
aculeatus), a small fish that is usually only recovered with fine-mesh screening
(Degerbøl 1945:125-151, Winge 1900:81-82, cited in Rosenlund 1976:30). The site was
again excavated from 1979-84, under the direction of Søren H. Andersen and Erik
Johansen, with the fish bone material coming from a 1x29 m long trench transecting the
midden and a 20x20 cm column sample. The one meter width of the transecting trench
is an important fact when evaluating the representativeness of the sample, as the
overall length of the midden is estimated at 140 m (Anderson and Johansen 1986).
Another sampling issue is that the deposits were not systematically screened (except
for the N-column sample). Rather, when fish bones were noticed during excavation the
matrix in that area was collected as a bulk sample and the fish bones later sorted out in
the laboratory with the aid of a binocular microscope. Although the controlled recovery
allowed by working in the laboratory doubtless means that few (if any) bones were
missed from the matrix samples, because the taking of samples relied on observation
by the excavators that fish bones were present, it is not possible to be equally confident
that all of the fish bones from the trench itself were collected.
On a more positive note, fish bones are described as well or even
excellently preserved; suggesting that bone loss may be relatively low in the midden
deposits (Enghoff 1986:63). The N-column sample, divided into 27 samples by either
natural layers or arbitrary 5 cm levels, was completely screened (through mesh-sizes
down to 0.5 mm). For purposes of inter-site comparison, the 9462 specimen
assemblage taken from the trench is the basis of comparison, although the N-column
sample is used in the discussion of intra-site variability (Enghoff 1986). The site
stratigraphy is somewhat complex, but since the assemblage is only reported in
aggregate, knowledge of individual contexts is not a necessity (see Andersen and
Johansen 1986 for a complete discussion). The chronology of the site is revealed
through 26 radiocarbon dates spanning 700 years, all of them coming from the Late
Mesolithic period (Andersen and Johansen 1986:50). A total of 9462 specimens from 16
fish families were identified from the trench deposits (Enghoff 1986:66-67). Several
thousand more were identified from the N-column sample, although the exact number is
unclear because the bone counts were ‘adjusted’ to make all of the samples equivalent
to a 2 kg sample standard (Enghoff 1986:70).
Bjørnsholm is a second shell midden site on the Limfjord (approximately 8
km from Ertebølle) that was subject to both early and more recent excavations. First
excavated in the 1930s under the direction of H.C. Broholm, it was revisited under the
direction of Søren H. Andersen from 1985-91. The early excavation produced just
twelve fish bones (Esocidae, Cyprinidae and Anguillidae), but the more recent work has
proven that the site is in fact, rich in fish remains (Enghoff 1991, Rosenlund 1976). The
recently analyzed material comes from a 1x28 m long trench transecting the midden,
with three smaller trenches enlarging the width in a few places out to three meters
(although the smaller trenches were not fully excavated). Natural layers were
distinguished during excavation (and materials bagged separately) where possible, in
other areas arbitrary levels were set at 5 or 10 cm intervals (Andersen 1991:59). Fish
remains were recovered by sieving in the field with 2-3 mm mesh-size screens (both
wet- and dry-screening was done), with one square that was especially rich in fish
bones receiving special treatment. Square K was excavated in 5 cm layers which were
first sieved through the 2-3 mm screen in the field, then an approximately 2 kg sample
of the material that passed through this screen was put through a 0.6mm sieve to
examine the effects of differential recovery. Cyprinidae and Gasterosteidae were most
frequently missed by the field screen, with Anguillidae also being missed to a significant
degree. Because the entire matrix is reported as having been screened, the
assemblage can be confidently regarded as representative of the whole trench.
However, the narrow width of the trench (in a midden extending to 325 m in length)
does raise the question of whether it is representative of the entirety of the site deposits.
The fish bones from the midden are described as being homogenously distributed with
regard to species occurrence, but without information on specific contexts it is not
possible to evaluate the uniformity of relative abundances (Enghoff 1991:113).
Preservation of the bones is recorded as good, and only a few of them are burnt
(Enghoff 1991:106). Like the Ertebølle midden, Bjørnsholm is extensively radiocarbon
dated (28 datings), and covers an extended period (ca. 1500 years), although the great
majority of the fish remains come from the Mesolithic portion of the deposits, and most
of the archaeological material overall dates to the Late Ertebølle period (Andersen
1991:75). A total of 11,490 specimens were identified from 24 separate fish families in
the Mesolithic deposits (Enghoff 1991:107).
Norsminde is a third shell midden site on the Jutland peninsula, although
further south and on a small fjord along the eastern coast. Unlike the previous two sites,
Norsminde was unknown until recently, being first discovered by survey work in 1972.
The site was excavated from 1972-89 under the direction of Søren Andersen, and is
described as being completely excavated. Originally, the midden was oval-shaped and
30 m long, varying in width from 5-12 m (Andersen 1989). Fish remains were recovered
by two methods: hand collection of specimens that were noted during excavation
(without the use of screens) and screening of bulk samples in the laboratory. It is not
clear what portion of the overall assemblage is attributable to each of the methods, what
quantity of matrix was taken as bulk samples, nor the mesh-size used in screening them
(although some were processed through 0.5 mm mesh-size) (Enghoff 1989:42). The
distribution of fish bone in the midden is described as ‘uneven’, and despite the overall
dominance of Pleuronectidae in the assemblage, this is the result of a preponderance of
these fish in an approximately seven square meter area containing the ‘fish layer’ -
outside of this area the midden is actually dominated by Gadidae. Bone preservation is
described as highly variable, ranging from very poor to very good (Enghoff 1989:42-45).
Despite the extensive excavation of this midden, questions about sample size and the
method of recovery preclude absolute confidence in the representativeness of the
assemblage, although it is possibly quite good. On the subject of chronology,
Norsminde is another example of a site that has been extensively radiocarbon dated,
revealing a span of occupation for the midden proper that is ca. 700 years long,
covering the Late Ertebølle and Early Neolithic periods (Andersen 1989:29). Despite the
presence of considerable Neolithic-era materials, only a single fish bone was recovered
from deposits attributed to this period (Enghoff 1989:45). A total of 8921 specimens
(given as 9158 in Enghoff 1994a, when 237 dermal denticles from Platichthys flesus are
included, increasing the relative percentage of Pleuronectidae by 1%) were identified,
from 16 families (Enghoff 1989:42).
Smakkerup Huse is the fourth site that offers a large assemblage,
combined with recent excavation and detailed publication. It differs from the first three
sites both in geography (it is on the island of Zealand, not the peninsula of Jutland) and
the nature of the site (the fish remains come from outcast deposits, not from a shell
midden). Although likely discovered by construction activity in the early 20th century and
collected by avocational and professional archaeologists over the course of decades,
the site was not excavated until 1989, and then again in 1995-97. Excavation was
conducted with trowels and shovels, under the direction of T. Douglas Price, with the
majority of the matrix water-screened through 4 mm mesh-size screens. There is some
confusion surrounding the contexts containing identified fish bone, as Appendix XIII
(Price and Gebauer 2005:270) gives fish weights from an area of only 22 square
meters, all apparently from the location of the 1996 excavation, but the site NISP is
equal to the combined totals of the 1995, 1996 and 1997 excavations (Larsen 2000). It
seems likely that the fish bones actually have a more extensive horizontal distribution.
There is also a discrepancy between the total weights of the fish samples listed in
Appendix XIII and the total given in Table 2.3 (Price and Gebauer 2005:49). Vertically,
the fish remains come from 8 of the designated layers, with three of these making only
minor contributions (see Table 9). Layers 5 and 5G (grey sand with gravel or gyttja)
have the greatest weight of fish bones and are dated to the Late Ertebølle. Layer 27
(brown sandy gyttja) dates to the Middle Ertebølle, as does presumably, Layer 26
(although it is not separately described). Layer 13 dates to the Late Ertebølle, so it is
probably safe to assume that Layers 10 and 12 do as well (Price and Gebauer
2005:47). The fish bones are described as well-preserved, and only a few examples are
burnt (Larsen 2005:103). A total of 9332 specimens were identified, representing 11 fish
families (Larsen 2005:104).
Layer Square meters Weight (g)
5 13 752,9
10 1 0,5
12 1 15,0
13 1 0,3
17 6 99,8
26 8 532,3
27 17 389,1
5G 8 107,3
Total 55 1897,2 Table 9: Distribution of fish remains by level at Smakkerup Huse (Price and Gebauer 2005:270).
The second category of sites from the literature include those that are
published in detail but have very small assemblages (i.e., Agernæs and Ronæs Skov)
and those that are published only in summary form (i.e., Tybrind Vig, Nivågård,
Møllegabet II and the Mesolithic sites around the Vedbæk fjord) (Enghoff 1994a and
2009, O. Jensen 2001, Richter and Noe-Nygaard 2003, Trolle-Lassen 1984). Three
other shell midden sites on Jutland (Visborg, Vængesø III and Krabbesholm) have been
analyzed and are mentioned in the literature, but no information is available about the
nature of their assemblages (Enghoff et al. 2007). Agernæs, a Late Ertebølle hunting
station on the northern coast of the island of Fyn, was excavated under the direction of
Anders Jæger during 1985-89. Unfortunately, while carefully excavated and with
exquisite stratigraphical information available, only five fish specimens are recorded (3
Gadidae and one each Pleuronectidae and Squalidae) (Richter and Noe-Nygaard
2003:17). Ronæs Skov, an underwater Ertebølle site on the northwestern coast of Fyn,
was investigated during 1992-2004 under the direction of Søren Andersen. Excavation
techniques were exemplary, and matrix was screened using an effective mesh-size
down to 2-3 mm, but surprisingly few fish remains were recovered (Andersen 2009:23).
Of the 109 identified specimens, most are Gadidae, with Squalidae, Salmonidae,
Gasterosteidae and Pleuronectidae also present (Enghoff 2009:245). Tybrind Vig, the
famous underwater Ertebølle site just a few kilometers up the coast from Ronæs Skov,
was also excavated under the direction of Søren H. Andersen, in the period 1978-1988.
Excavated in a manner similar to Ronæs Skov, the fish assemblage has been only
minimally published, such that all that is currently known is that Gadidae dominate, with
Scophthalmidae, Pleuronectidae, Squalidae and Gasterosteidae described as common.
Other fish present include Cottidae, Anguillidae, Clupeidae, Scombridae, Salmonidae
and Zoarcidae (Trolle-Lassen 1984). The large number of fishing implements recovered
during excavation makes this an extremely interesting site for discussion of the
Ertebølle fishery, but until the assemblage is more fully published, its usefulness is
limited. Nivågård, one of a number of Mesolithic sites around the Nivå fjord in
northeastern Zealand, is another intriguing assemblage because of the associated
archaeological finds – in this case, remains of a hut structure (although actually located
at Nivå 10, it is less than 100 m distant from Nivågård). Excavations under the direction
of Ole Lass Jensen in 1992 produced a sizeable fish assemblage, but it is only reported
in summary form. Pleuronectidae are the dominant fish (60%), followed by Gadidae
(25%). Other fish mentioned as being present include Clupeidae, Ammotydiae,
Gasterosteidae, Esocidae, Percidae and Cyprinidae (O. Jensen 2001:124). Møllegabet
II is an underwater site that was excavated in 1990 and 1991 under the direction of Ole
Grøn and Jørgen Skaarup. The site is of special interest because of a feature
interpreted as a boat burial. Little information is available on the fish remains, but what
is published is that 95% of the bones were Gadidae, with Squalidae, Scombridae,
Pleuronectidae and Anguillidae also present (Grøn and Skaarup 1991). The final sites in
this second category include the Mesolithic sites in the area of the Vedbæk fjord in
northeastern Zealand, excavated under the direction of Eric Brinch Petersen and Peter
Vang Petersen during the period 1975-85. The sites include: Stationsvej 19,
Henriksholm B, Magleholm, Maglemosegård, Maglemosegårds Vænge and Vænget
Nord. The first and the last of these sites date to the Kongemose period, the rest are
from the Ertebølle period. Excavated with the use of 3.5 mm mesh-size screens, the
total number of identified specimens from the complex is an impressive 35,932.
Unfortunately, the assemblages are not published in detail, and the only information
available is relative abundances of the fishes (Enghoff 1994a).
The last group of sites consists of earlier excavations, where less
sophisticated recovery methods have likely resulted in severe biases in the fish
assemblages. This can be seen at some of the sites discussed above with both early
and later excavation campaigns. Many of these early excavations also produced very
few fish remains. Because of these limitations, the data must be considered somewhat
unreliable and can only play a limited role in forming cultural interpretations. Knud
Rosenlund deserves credit for his excellent work collecting and summarizing the data
(1976). Table 10 provides some basic information about the assemblages from these
sites.
Site Region NISP Ga
did
ae
Ple
uro
ne
ctid
ae
An
gu
illid
ae
Clu
pe
ida
e
Sco
mb
rid
ae
Be
lon
ida
e
Eso
cid
ae
Pe
rcid
ae
Cyp
rin
ida
e
Ga
ste
roste
ida
e
Sq
ua
lid
ae
Oth
er
Argusgrunden Lolland 11 7 4
Bjørnsholm N Jutland 12 4 7 1
Bloksbjerg NE Zealand 60 ? ? 60
Brabrand E Jutland 1 1
Drøsselholm W Zealand 3 3
Dyrholmen I E Jutland 1 1
Ertebølle N Jutland 186 8 18 39 6 11 2 77 25
Fannerup E Jutland 16 13 1 1 1
Fjellenstrup NE Zealand 0 ?
Fårevejle NW Zealand 47 38 8 1
Godsted Lolland 0 ?
Gudumlund N Jutland 0 ? ?
Havelse NE Zealand 69 26 35 ? 2 1 5
Havnsø N Zealand 2 2
Havnø N Jutland 7 2 5
Jordløse By N Zealand 1 1
Jordløse Mose N Zealand 0 ?
Kassemose NE Zealand 205 170 35
Klintesø N Zealand 98 80 8 8 1 1
Koholm Mose NE Zealand 0 ?
Kolding Fjord E Jutland 1 1
Kolind E Jutland 7 4 3
Mejlgård E Jutland 223 30 155 32 1 3 2
Mejlgård E Jutland 3 3
Mejlgård E Jutland 312 24 176 75 27 10
Mosegården X N Zealand 1 1
Muldbjerg W Zealand 224 111 110 3
Nekselø NW Zealand 21 19 2
Nivå NE Zealand 41 12 15 1 13
Norslund E Jutland 314 300 10 1 3
Ordrup Næs NW Zealand 174 14 150 10
Præstelyngen W Zealand 0 ? ? ? ? ?
Sakskøbing Lolland 0 ?
Saltpetermosen NE Zealand 890 1 2 110 740 13 24
Skellingsted W Zealand 0 ?
Sparregård Falster 104 10 94
Sølager N Zealand 3641 3400 100 27 18 74 21 1
Vedbæk Boldbaner NE Zealand 22 10 11 1
Vejleby NE Zealand 1359 500 850 1 8
Ølby Lyng NE Zealand 3864 3700 150 1 1 1 11
Total 11920 8359 1672 191 19 159 212 919 126 133 38 81 11
Table 10: Other Late Mesolithic sites with fish bones (from Rosenlund 1976). Note some
numbers are approximate and ‘?’ represents an indeterminate number of specimens.
Three Zealand sites from this category deserve special mention: Ølby Lyng
and Sølager because of the size of their assemblages, and Ordrup Næs because of its
proximity to the sites in northwestern Zealand that were analyzed for this project and the
unusual nature of its assemblage. Ølby Lyng is an Ertebølle culture site on the eastern
coast of Zealand, a few kilometers north of Køge. It was excavated in 1962 and 1963
under the direction of David Liversage. Although the recovery methods are not known,
the overwhelming dominance of Gadidae (ca. 3700 of ca. 3900 specimens) is a striking
characteristic of the assemblage. An interesting interpretation offered by the analyst is
that the disproportionately low number of head elements from Gadidae at the site
suggests drying of fish for storage (Møhl 1970:77). Gadidae also dominate the
assemblage at Sølager, a shell midden first investigated in the 19th century, then re-
excavated under Carsten Neergaard from 1901-07 (which produced the fish
assemblage in Table 10). Sølager lies at the mouth of the Roskilde fjord, where it meets
the Isefjord in northern Zealand. Ordrup Næs was excavated during 1937-39, under the
direction of C.J. Becker. It lies on the northern coast of Zealand, approximately 10-12
km north and west of Dragsholm, Bøgebjerg and Fårevejle, and contains artifacts from
the Ertebølle and Early Neolithic periods. Although the assemblage representativeness
is questionable due to the early date of excavation, it is interesting because it is
dominated by Scombridae, with a number of Belonidae specimens as well. These two
migratory species are only present in Danish waters during the warmer months, so the
fact that the assemblage is almost solely composed of these fish (there are also 14
Gadidae specimens) points to a highly seasonal fishery.
One final group of sites that deserves mention is the non-coastal
settlements. Ringkloster (located on the shore of Skanderborgsø in central Jutland) and
several inland sites on Zealand (including Drøsselholm, Jordløse Mose, Nøddekonge,
Præstelyngen, Trustrup, Vejkonge, Øgårde and Åkonge) have all produced some fish
remains, although the total number of specimens is generally lower than at the coastal
sites (Enghoff 1994a, 1994b, Rosenlund 1976).
Esocidae, Percidae and Cyprinidae are the most common fishes at the inland sites,
although migratory (Anguillidae and Salmonidae) and even marine (Gadidae and
Pleuronectidae) fishes have been identified at some inland sites. Based on
environmental considerations (i.e., winter flooding of site locations), fishing at the inland
sites is considered to have been a summer activity on Zealand (Enghoff 1994a).
Conversely, Ringkloster has been interpreted as being occupied during the
winter/spring (Rowley-Conwy 1994). Having introduced the sites and fish assemblages
that form the basis of the study, now it is time to turn to its results.
5. Results
5.1 Recovery and preservation
Before turning our attention to what the data generated by this project can
reveal about past human culture it is appropriate to examine the ways in which the
project has increased our understanding of the quality of the data and the ways in which
it may be distorted during the process of producing it. Differential recovery (due to
varying mesh-sizes used in screening and individual excavator bias) and differential
preservation are two areas of taphonomy that can be evaluated with the aid of the fish
bone data. Intra-site variation is another important topic that has not received enough
attention in fish bone studies of the Danish Ertebølle, but is critical to understanding
cultural dynamism.
5.1.1 Differential recovery
The question of whether to use screens to sift matrix and aid in the recovery
of smaller artifacts during excavations has largely been resolved in favor of their use,
although with the caveat that screening is not always possible (e.g., in peat deposits).
Less easily determined is what mesh-size is appropriate for the screens. Finer mesh
sizes produce more complete artifact recovery, but at the expense of slowing
excavation and thus limiting the area sampled. The effect of screen-size on recovery
rates is not a new topic in zooarchaeology (e.g., Casteel 1972, Clason and Prummel
1977, Payne 1972, Shaffer 1992, Thomas 1969), but the variability in sites and research
questions precludes formulaic prescriptions. Recent investigations have moved beyond
merely documenting the losses associated with larger mesh-sizes and started to focus
on the ways in which they alter the archaeological indices that are produced from fish
bone assemblages (Enghoff 2005, Gargett and Vale 2005, Nagaoka 2005, Olson and
Walther 2007, Vale and Gargett 2002, Zohar and Belmaker 2002). Species richness,
diversity, evenness, and population size/age structures are all affected when smaller
mesh-size screens recover the remains of smaller fish. Until now, the effects of mesh
size have not often been quantified for Ertebølle assemblages (see Enghoff 1991 for an
exception). Screen-test samples that were specially processed from two sites (Asnæs
Havnemark and Dragsholm) comprehensively address this question (Figure 37), while
materials from a third site (Nederst) are also relevant to the discussion.
Figure 37: Processing matrix samples through nested geologic screens.
As described under the individual site descriptions in the Materials section and below,
14 bulk samples totaling 31 liters were taken at Asnæs Havnemark and 13 samples
totaling approximately 10 liters were taken at Dragsholm for processing through nested
geologic screens for the purpose of evaluating the effect of mesh-size on the recovery
of fish remains. The screens separated the material into 4, 2 and 1 mm fractions, from
which the fish bones were sorted and identified. Some testing of the effects of mesh-
size was also done during the excavations at Nederst using 1.5 and 6 mm mesh-sizes
and this data is also included here. Tables 11 and 12 display the specimens that were
identified from the samples at Asnæs Havnemark and Dragsholm that are compared by
mesh-size in Tables 13 and 14; Table 15 shows the results from Nederst.
Gad
idae
An
gu
illi
dae
Sco
mb
rid
ae
Clu
peid
ae
Co
ttid
ae
Ple
uro
necti
dae
Gaste
roste
idae
Zo
arc
idae
Tra
ch
inid
ae
Tri
gli
dae
Go
bii
dae
Cyp
rin
idae
Salm
on
idae
Syn
gn
ath
idae
Sq
uali
dae
4mm vertebra 873 106 7 2 15 22 0 0 0 2 0 1 0 0 0
2mm vertebra 720 410 92 102 58 26 0 8 0 2 0 1 1 0 1
1mm vertebra 86 27 18 0 9 6 39 4 9 0 3 0 0 1 0
Total vertebra 1679 543 117 104 82 54 39 12 9 4 3 2 1 1 1
% ID vertebra 63,3% 20,5% 4,4% 3,9% 3,1% 2,0% 1,5% 0,5% 0,3% 0,2% 0,1% 0,1% 0,0% 0,0% 0,0%
Parasphenoid 23 2
Vomer (left half) 13
Vomer (right half) 12
Vomer (whole) 5 5
Mesethmoid 5
Frontal 1
Exoccipital 1
Prooticum 2
Pterotic 13 1
Sphenotic 17
Opisthotic 16
Basibranchial 1
Premaxillary 36
Maxillary 36 6 1 1
Dentary 21 4
Angular 46 8 1
Retroarticular 4
Quadrate 64 6 2 1
Palatine 17 1
Ectopterygoid 11 1
Preopercle 5 2
Opercle 15 1
Interopercle 7
Subopercle 1
Symplectic 13
Hyomandibular 14 5
Ceratohyal 11 11
Epihyal 13 4
Hypohyal 1
Interhyal 3
Urohyal 2
Epibranchial 6
Posttemporal 48 1
Supracleithrum 29 3
Cleithrum 16 2
Pharyngeal plate 6 1
Pharyngobranchial 4
Branchiostegal ray 5
Os anale 1
Dorsal spine/plate 5 1
Otolith 28
Total non-vertebra 565 55 0 2 14 5 5 0 0 1 0 0 1 0 0
NISP 2244 598 117 106 96 59 44 12 9 5 3 2 2 1 1
% NISP 68,1% 18,2% 3,6% 3,2% 2,9% 1,8% 1,3% 0,4% 0,3% 0,2% 0,1% 0,1% 0,1% 0,0% 0,0%
Table 11: Identified fish remains from the screen-test samples at Asnæs Havnemark.
Gad
idae
An
gu
illi
dae
Plu
ero
necti
dae
Clu
peid
ae
Co
ttid
ae
Zo
arc
idae
Go
bii
dae
Sco
mb
rid
ae
Belo
nid
ae
Gaste
roste
idae
Tri
gli
dae
Tra
ch
inid
ae
Syn
gn
ath
idae
Sq
uali
dae
4mm vertebra 193 3 135 0 7 0 0 5 6 0 5 1 0 2
2mm vertebra 288 158 71 79 23 10 2 3 0 0 2 4 0 2
1mm vertebra 71 82 4 15 0 20 7 0 1 3 0 0 4 0
Total vertebra 552 243 210 94 30 30 9 8 7 3 7 5 4 4
% ID vertebra 45,8% 20,1% 17,4% 7,8% 2,5% 2,5% 0,7% 0,7% 0,6% 0,2% 0,6% 0,4% 0,3% 0,3%
Parasphenoid 4 1
Vomer (left half) 6
Vomer (right half) 11
Vomer (whole) 0 1 2
Mesethmoid 6
Prooticum 2
Sphenotic 4
Opisthotic 2
Premaxillary 31
Maxillary 11 1
Dentary 22 10
Angular 5 3 2
Retroarticular 1
Quadrate 15 2
Palatine 5
Ectopterygoid 4
Opercle 3
Interopercle 1
Symplectic 4
Hyomandibular 1
Ceratohyal 2
Epihyal 3 1
Hypohyal 1
Interhyal 1
Urohyal 1 1
Epibranchial 5
Posttemporal 25 3
Supracleithrum 11 2
Pharyngeal plate 2
Branchiostegal ray 4
Os anale 2
Dorsal spine/plate 2 1
Otolith 2
Total non-vertebra 186 8 19 2 1 0 0 0 10 2 0 0 0 1
NISP 738 251 229 96 31 30 9 8 17 5 7 5 4 5
% NISP 51,4% 17,5% 16,0% 6,7% 2,2% 2,1% 0,6% 0,6% 1,2% 0,3% 0,5% 0,3% 0,3% 0,3%
Table 12: Identified fish remains from the screen test samples at Dragsholm.
From Dragsholm, 1435 specimens were identified. Although they come
from all four levels of the site that produced most of the fish remains (Level 6 produced
only three identified specimens during the course of excavation and was not sampled
for this experiment), they are not evenly distributed between levels. Samples were
initially taken from Level 7B because excavators noted high concentrations of fish bone
in certain areas that also had high concentrations of small pieces of charcoal. It was
only near the end of the excavation that samples were taken from other levels for
comparison purposes – and these unfortunately failed to sample areas rich in fish bone
material. Level 7B produced 8 of the 13 samples and 1329 identified specimens, Level
7A had 2 samples and only 10 specimens, Level 7C had 2 samples and 80 specimens,
and Level 8 had 1 sample and 16 specimens. Since the results from the regular
excavation show differences between the levels (see section 5.2 Intra-site variability),
the summary screen test results should be seen as most relevant to Level 7B and are,
perhaps, not generally applicable. With this reservation in mind, a look at Table 13
reveals some interesting results.
Ga
did
ae
Ple
uro
ne
cti
da
e
An
gu
illid
ae
Clu
pe
ide
a
Co
ttid
ae
Zo
arc
ida
e
Sc
om
bri
da
e
Be
lon
ida
e
Tri
glid
ae
Oth
er
Ide
nti
fie
d
Un
ide
nti
fie
d
4mm vertebra 193 135 3 0 7 0 5 6 5 3 357 37
% 4mm 54,1% 37,8% 0,8% 0,0% 2,0% 0,0% 1,4% 1,7% 1,4% 0,8% 9,4%
2mm vertebra 288 71 158 79 23 10 3 0 2 8 642 152
% 4 and 2mm 48,1% 20,6% 16,1% 7,9% 3,0% 1,0% 0,8% 0,6% 0,7% 1,1% 15,9%
1mm vertebra 71 4 82 15 0 20 0 1 0 14 207 138
% 4, 2 and 1mm 45,8% 17,4% 20,1% 7,8% 2,5% 2,5% 0,7% 0,6% 0,6% 2,1% 21,3%
Table 13: Comparison of identified and unidentified vertebrae by screen size for the
screen test samples from Dragsholm.
Table 13 displays the number of identified vertebrae for each fraction
individually, and the relative abundances cumulatively. That is to say, the row ‘% 4mm’
displays the results considering only the 4 mm fraction, ‘% 4 and 2mm’ combines the
results of these two fractions and ‘% 4, 2 and 1mm’ combines all three. Thus, the
relative abundances (percentages) display the results of an effective screen size of 4,
then 2 and finally 1 mm. Overall, the number of identified vertebrae was greatest from
the 2 mm fraction (642 or 53% of the total), followed by the 4 mm fraction (357 or 30%)
and the 1 mm fraction (207 or 17%). Clearly the use of 4 mm screens during excavation
meant that many fish bones were not recovered. What is even more interesting is the
effect on the relative abundances (see Figure 38). Gadidae and Pleuronectidae
percentages decline noticeably with a change from an effective screen size of 4 to 2
mm, and then slightly more with a change to an effective screen size of 1 mm.
Anguillidae move in the opposite direction, increasing their representation with smaller
mesh sizes. Clupeidae (both herring and shad), Zoarcidae and Gobiidae were only
recovered in the 2 and 1 mm fractions, while Syngnathidae (pipefish) and
Gasterosteidae (three-spined stickleback) were only detected with the 1 mm screen. As
a final note, the percentage of unidentified vertebrae more than doubles from the 4 mm
to the 1 mm effective mesh-size results.
Figure 38: Graph of relative percentages of fish types by screen size at Dragsholm.
With the experience from Dragsholm in mind, sampling during the
excavation at Asnæs Havnemark began almost immediately and covered a broader
range of contexts. Moreover, based on radiocarbon dating, the occupation seems to be
relatively short in duration and differences between levels seem to be fairly minor. For
all of these reasons, the summary results of the screen test can probably be considered
valid for most of the contexts at Asnæs Havnemark. Table 14 presents the results from
Asnæs Havnemark in the same format as Table 13 for Dragsholm.
Ga
did
ae
An
gu
illid
ae
Ple
uro
ne
cti
da
e
Clu
pe
ida
e
Co
ttid
ae
Sc
om
bri
da
e
Ga
ste
ros
teid
ae
Oth
er
Ide
nti
fie
d
Un
ide
nti
fie
d
4mm vertebra 873 106 22 2 15 7 0 3 1028 48
% 4mm 84,9% 10,3% 2,1% 0,2% 1,5% 0,7% 0,0% 0,3% 4,5%
2mm vertebra 720 410 26 102 58 92 0 13 1421 244
% 4 and 2mm 65,0% 21,1% 2,0% 4,2% 3,0% 4,0% 0,0% 0,7% 10,7%
1mm vertebra 86 27 6 0 9 18 39 17 202 152
% 4, 2 and 1mm 63,3% 20,5% 2,0% 3,9% 3,1% 4,4% 1,5% 1,2% 14,3%
Table 14: Comparison of identified and unidentified vertebrae by screen size for the
screen test samples from Asnæs Havnemark.
Again, the 2 mm fraction produced the largest number of identified
vertebrae (1421 or 54% of the total), followed by the 4 mm fraction (1028 or 39%) and
the 1 mm fraction (202 or 8%). As at Dragsholm, a significant portion of the fish remains
present in the deposits were probably missed using 4 mm screens during excavation.
Considering relative abundances (see Figure 39), Gadidae show a fairly large
percentage decline with increasingly finer mesh sizes, while Anguillidae, Clupeidae,
Cottidae and Scombridae increase. In contrast with the results at Dragsholm,
Pleuronectidae are little changed, perhaps because they comprise only a small
percentage of the vertebrae. Syngnathidae (pipefish) and Gasterosteidae (three-spined
stickleback) would not have been detected at the site without the aid of the 1 mm mesh-
size screen. At Asnæs Havnemark the percentage of unidentified vertebrae more than
triples from the 4 mm to the 1 mm effective mesh-size results, although the levels are
somewhat lower than at Dragsholm.
Figure 39: Graph of relative percentages of fish types by screen size at Asnæs
Havnemark.
The excavations at Nederst also produced sets of fish remains divided by
screen size, although the site is not well-published and it is not possible to precisely
reconstruct the methodology that produced them from the case file. From the samples
that were analyzed in connection with this project, six contexts have assemblages from
both coarse (6 mm) and fine (1.5 mm) mesh screens. It is not known if the same
quantity of matrix was screened through both the coarse and the fine mesh screens, but
clearly more vertebrae were identified from the fine mesh fraction (see Table 15).
Similar to the pattern noted above, generally larger fish (i.e., Gadidae and
Pleuronectidae) decrease in relative abundance when smaller mesh-size screens are
used, while generally smaller fish (e.g., Anguillidae, Clupeidae and Zoarcidae) increase
(see Figure 40). Again, Gasterosteidae (three-spined stickleback) were only detected
with the use of small mesh-size screens. The percentage of unidentified vertebrae is
larger in the fine mesh than in the coarse mesh fraction, although it remains relatively
low in the Nederst assemblage.
Tra
ch
inid
ae
Ple
uro
ne
cti
da
e
An
gu
illid
ae
Ga
did
ae
Zo
arc
ida
e
Clu
pe
ida
e
Oth
er
Ide
nti
fie
d
Un
ide
nti
fie
d
Fine-mesh vertebrae 878 643 599 164 163 93 25 2565 227
% 34,2% 25,1% 23,4% 6,4% 6,4% 3,6% 1,0% 8,1%
Coarse-mesh vertebrae 316 432 59 138 18 6 5 974 29
% 32,4% 44,4% 6,1% 14,2% 1,8% 0,6% 0,5% 2,9% Table 15: Comparison of identified and unidentified vertebrae by screen size for the
screen test samples from Nederst.
Figure 40: Graph of relative percentages of fish types by screen size at Nederst.
The results from screen test experiments at Dragsholm, Asnæs Havnemark
and Nederst all point to the importance of considering excavation methods when
evaluating Ertebølle fish assemblages. The number of species that are identified
increases with finer mesh, as elements from smaller fish (e.g., Gasterosteidae,
Syngnathidae and Gobiidae) are not recovered at all with 4 mm mesh. Assemblage
diversity indices that consider relative abundances are also affected, as fish such as
Clupeidae, Anguillidae and Zoarcidae increase from very minor presences with 4mm
mesh to significant contributors with 2 or 1 mm mesh-sizes. Rather obviously, as the
relative abundance of smaller fish increases, the percentage of larger fish (e.g.,
Gadidae and Pleuronectidae) must decrease – even as their absolute abundances also
increase with smaller mesh screens. In general, the use of better recovery methods will
increase the size of an assemblage and change its proportional composition. What
cannot be generalized is the specific ways in which assemblages change in response to
screen size. It is, unfortunately, not possible to create algorithms to adjust the results of
excavation using coarse mesh screening to reflect what would have been recovered
using finer mesh without screen test samples from the specific contexts in question, as
it is not possible to assess whether the absence (or impoverishment) of smaller fish is
an artifact of recovery or actual conditions within the deposits. This research highlights
the importance of sampling to evaluate the effects of mesh-size decisions at future
excavations and using caution when comparing previously excavated assemblages
where this was not done. There is another aspect of differential recovery, excavator
bias, which can also be identified in fish bone assemblages, although solutions may be
harder to find.
The effect of excavator bias on archaeological assemblages is not often
addressed, at least partly because of the difficulty in doing so. The same context cannot
be excavated multiple times to evaluate the skill of the individuals doing the work.
Nonetheless, post hoc analysis can be conducted to search for patterns indicative of
systematic biases introduced by excavators. Fish bone assemblages are especially
amenable to such investigation in that over-representation of bones of large-sized fish
and/or elements that are distinctive in form can be the result of less experienced
excavators systematically missing smaller and/or less distinctive specimens (Heinrich
1994). Three sites that were analyzed as part of this project provide evidence that
supports excavator bias as a factor in recovery.
Asnæs Havnemark is a good test case to begin with because approximately
95% of the vertebrae are from two families: a larger-sized one, Gadidae (86%) and a
smaller-sized one Anguillidae (9%). Comparing the results of individual excavators (see
Table 16), marked discrepancies occur in the relative abundances of these two types of
fish. Excavators C, D and E were much more successful at recovering specimens of
large-sized fish (Gadidae). The over-representation of distinctive elements as a result of
excavator bias is displayed by the varying proportions of non-vertebra in the NISP
(Table 16, right-hand column). The reasoning behind using this value as a measure of
excavator bias is that while vertebrae are easily recognized by all excavators, other
elements (especially when only partially present) can be overlooked by individuals who
are not experienced at recognizing them. Once again, it appears that Excavators C, D
and E may have influenced the results, in this case by recovering many vertebrae while
missing other elements. (Note that gross NISP is not a good indicator of recovery rates,
as excavators sampled different numbers of contexts for fish bones.)
Excavator NISP Gadidae Anguillidae Non-vertebra %
A 28795 81% 13% 16%
B 2064 87% 6% 22%
C 9722 92% 4% 6%
D 2824 96% 1% 11%
E 570 96% 1% 5% Table 16: Results from Asnæs Havnemark by excavator (4 mm mesh-size water-
screening).
The results from Dragsholm and Fårevejle are more difficult to evaluate,
given that the vast majority of the bones come from either Gadidae or Pleuronectidae
(both generally larger-sized fish), but differences in the percentage of non-vertebra in
the NISP by excavator are again apparent (see Tables 17 and 18).
Excavator NISP Gadidae Anguillidae Non-vertebra %
A 7792 55% 1% 10%
B 6482 61% 1% 9%
I 10572 65% 2% 16%
J 3308 66% 1% 19%
K 2343 58% 1% 4% Table 17: Results from Dragsholm by excavator (4 mm mesh-size water-screening).
Excavator NISP Gadidae Anguillidae Non-vertebra %
A 587 58% 1% 16%
B 700 51% 4% 19%
D 335 68% 0% 8%
I 533 57% 2% 19%
J 519 43% 2% 10% Table 18: Results from Fårevejle by excavator (4 mm mesh-size water-screening)
The effects of differential recovery must be borne in mind when discussing
fish bone assemblages, although fortunately it is possible to begin to evaluate their
nature and extent. Screen mesh-size plays a major role in determining both how many
fish remains are recovered and the representation of smaller fish in the assemblage
(with finer mesh screens increasing both of these attributes). To aid in comparison of
assemblages, future excavations should incorporate sampling of the deposits to test the
effects of the mesh-size used in recovery. For the two sites on Zealand discussed here,
it is interesting to note that while some species were missed by coarser mesh screens,
relative abundance data suggests that the general nature of the assemblages was
accurately assessed by the excavation method employed (i.e., Gadidae dominate the
assemblages). The role of excavator bias in differential recovery is a thornier issue
because while it seems to be a factor, it is harder to quantify and mitigate. Ichthyo-
archaeologists can help by training other field archaeologists, but this approach will
have limited efficacy, as there are many archaeologists and teaching about the many
different elements (and which portions are likely to preserve) would take a prohibitive
amount of time. Having a trained faunal analyst responsible for field recovery is
probably the ideal situation, with bulk sampling in the field for later processing by a
trained analyst as a second choice. A third option is to focus on comparing the
vertebrae in assemblages (as opposed to NISP), although this does not address the
discrimination that seems to occur against smaller vertebrae. At a minimum, awareness
of these sources of bias means that they can be explicitly considered when discussing
fish remains. Differential recovery is not the only potential reason that an archaeological
assemblage will not be fully representative of the initially deposited fish remains;
differential preservation must also be evaluated.
5.1.2 Differential preservation
In most circumstances not all of the fish remains that are initially deposited
survive to be recovered during excavation. The size and robustness of the bone, type of
fish, and environmental conditions (e.g., temperature, soil type and hydrology) are three
important factors that determine how long a bone will survive after deposition. Similar to
the situation with excavator bias, post hoc analysis of results can point to patterns in the
data that are indicative of preservation biases. Three approaches are employed here in
an attempt to assess fish bone preservation at some of the sites analyzed for the
project: the ratio of unidentified to identified bone, the degree of completeness of
identified bones and the actual versus expected presence of different elements.
Comparing the amount of identified and unidentified fish bone is done by
weight, not specimen count, and should only be considered a rough approximation of
the nature of the assemblage. (Weights were taken with an electric scale, accurate to
the gram.) There are a number of issues that interfere with how much (and how
accurate) information this method can provide. The first and greatest weakness is that it
examines the assemblage from the perspective of those specimens that were
recovered. Fish bones that had completely disappeared, or were so fragmentary that
they were missed during excavation play no role in the analysis. Second, the
unidentified fraction of the assemblage involves some degree of uncertainty by
definition, meaning that is highly likely that some bone material comes from animals
other than fish. Finally, the amount of matrix adhering to the bones plays a role – some
of the very dirty bones include a significant amount of weight that is not from skeletal
materials (although this should affect both fractions, if not necessarily equally). Despite
these reservations, higher proportions of identified bones should indicate assemblages
that are better preserved. Tables 19-22 show the weights from the sites of Asnæs
Havnemark, Fårevejle, Bøgebjerg and Dragsholm.
Gross weight (grams) 3746
Shell, charcoal, stone, etc. 145
Net weight bone 3601
Unidentified bone fragments 352
Unidentified vertebrae 136
Identified vertebrae 2589
Identified non-vertebrae 524
Unidentified total 488 14%
Identified total 3113 86% Table 19: Weights from Asnæs Havnemark.
Gross weight (grams) 288
Shell, charcoal, stone, etc. 43
Net weight bone 245
Unidentified bone fragments 63
Unidentified vertebrae 0
Identified vertebrae 148
Identified non-vertebrae 34
Unidentified total 63 26%
Identified total 182 74%
Table 20: Weights from Fårevejle (unidentified vertebrae not weighed separately).
Gross weight (grams) 265
Shell, charcoal, stone, etc. 15
Net weight bone 250
Unidentified bone fragments 62
Unidentified vertebrae 5
Identified vertebrae 183
Identified non-vertebrae 0
Unidentified total 67 27%
Identified total 183 73% Table 21: Weights from Bøgebjerg (non-vertebra elements not weighed separately).
Gross weight (grams) 5253
Shell, charcoal, stone, etc. 869
Net weight bone 4384
Unidentified bone fragments 1620
Unidentified vertebrae 63
Identified vertebrae 2137
Identified non-vertebrae 564
Unidentified total 1683 38%
Identified total 2701 62% Table 22: Weights from Dragsholm.
The four tables show that the percentage of the weight of unidentified bone ranges from
a low of 14% at Asnæs Havnemark to a high of 38% at Dragsholm, with Fårevejle and
Bøgebjerg approximately halfway in between. The majority of the bone (by weight) was
identified at every site, although the high percentage of unidentified bone at Dragsholm
recommends further scrutiny of the assemblage. Another way in which to study the
preservation of an assemblage is to evaluate the completeness of the identified bones.
Evaluating bone preservation by completeness shares some weaknesses
with the identified/unidentified ratios, but also has some advantages. Like the ratio
method, examining completeness only takes into account specimens that were
recovered during excavation. However, because it deals only with identified fish
specimens bird and mammal bones cannot influence the results. Also, since it involves
counts rather than weights, dirty bones are less of a problem (although adhering matrix
can certainly reduce the potential for identifying bones). This method considers only
vertebrae, minimizing the impact of excavator bias, although mesh-size can still affect
the results by discriminating against more fragmentary specimens (all three sites here
were excavated with 4 mm mesh). A final consideration is that while the method
attempts to measure the degree of fragmentation of vertebrae, because it uses only
identified specimens there is certainly an element of bias towards a seeming higher
degree of fragmentation for those species that remain identifiable even with relatively
incomplete specimens (e.g., Scombridae).
Collecting the data was done during the normal course of identification for
all of the material from Asnæs Havnemark and Nederst and selected samples were re-
analyzed for Dragsholm. Vertebra specimens were assigned to one of three categories:
less than 50% complete, 50-75% complete, and more than 75% complete (neural and
haemal spines were not included in this assessment). There was unavoidably some
subjectivity in making these assignments, but because one analyst made all of the
decisions this is not thought to present a major source of error. The results from the
three sites are in good agreement, with the most complete vertebrae representing by far
the largest percentage of the identified specimens, followed by the second most
complete category, with the percentage of identified vertebra specimens that are less
than half complete representing only 5-12% of the total (see Tables 23, 24 and 25). The
high percentage of mostly complete vertebrae fits with the identified/unidentified ratios
in pointing towards relatively good preservation in the assemblages. Some intra-site
variability between species is worth noting, as well as inter-site differences.
<½ complete ½ - ¾ complete >¾ complete Total
Gadidae 1548 3936 25393 30877
Gadidae 5,0% 12,7% 82,2%
Anguillidae 164 344 3218 3726
Anguillidae 4,4% 9,2% 86,4%
Pleuronectidae 8 49 778 835
Pleuronectidae 1,0% 5,9% 93,2%
Cottidae 0 4 359 363
Cottidae 0,0% 1,1% 98,9%
Scombridae 47 119 325 491
Scombridae 9,6% 24,2% 66,2%
Totals 1767 4452 30073 36292
4,9% 12,3% 82,9%
Table 23: Examination of degree of completeness of vertebrae at Asnæs Havnemark.
<½ complete ½ - ¾ complete >¾ complete Total
Pleuronectidae 374 709 4499 5582
Pleuronectidae 6,7% 12,7% 80,6%
Anguillidae 166 397 1996 2559
Anguillidae 6,5% 15,5% 78,0%
Trachinidae 19 161 1782 1962
Trachinidae 1,0% 8,2% 90,8%
Gadidae 332 381 702 1415
Gadidae 23,5% 26,9% 49,6%
Clupeidae 16 242 544 802
Clupeidae 2,0% 30,2% 67,8%
Zoarcidae 0 15 206 221
Zoarcidae 0,0% 6,8% 93,2%
Totals 907 1905 9729 12541
7,2% 15,2% 77,6%
Table 24: Examination of degree of completeness of vertebrae at Nederst.
<½ complete ½ - ¾ complete >¾ complete Total
Gadidae 681 1305 3329 5315
Gadidae 12,8% 24,6% 62,6%
Anguillidae 9 21 76 106
Anguillidae 8,5% 19,8% 71,7%
Pleuronectidae 171 367 1489 2027
Pleuronectidae 8,4% 18,1% 73,5%
Cottidae 0 2 152 154
Cottidae 0,0% 1,3% 98,7%
Belonidae 38 25 117 180
Belonidae 21,1% 13,9% 65,0%
Scombridae 37 48 89 174
Scombridae 21,3% 27,6% 51,1%
Totals 898 1743 5135 7776
11,5% 22,4% 66,0% Table 25: Examination of degree of completeness of vertebrae at Dragsholm (select
samples).
At Asnæs Havnemark (Table 23), overall completeness is quite high,
although Scombridae are markedly more fragmented than the other fish. This may
relate to the high fat content of the bones or, as previously noted, may be a factor of
these bones being identifiable even with small fragments. The Nederst assemblage
(Table 24) has a slightly higher degree of fragmentation, with Gadidae being especially
affected. Clupeidae are also more likely to be at least partly broken, a reasonable
situation as the bones are rather fragile. The small number of bones falling in the less
than half complete category for Clupeidae may be due to lack of recovery, as the bones
are rather small even when whole. Dragsholm (Table 25) has a higher overall degree of
fragmentation than the other two sites. Again, Scombridae are more fragmented than
the other fishes. Dragsholm also had enough Squalidae to evaluate, although only two
categories were used: more and less than 50% complete. Of the 278 specimens, almost
60% were less than half complete. Squalidae vertebrae are fragile bones and also, like
Scombridae, are identifiable from small fragments. Comparing the three sites, Asnæs
Havnemark has the least fragmented vertebrae and Dragsholm has the most, with
Nederst occupying a middle position. Individual fishes vary in their tendency towards
fragmentation (or at least in the identifiability after fragmentation), although the degree
of fragmentation for each fish seems to be consistent between sites, with one exception.
The high degree of fragmentation of Gadidae at Nederst may be related to their low
relative abundance (ca. 12%) in the assemblage; perhaps suggesting a different
processing method at this site.
The third approach to examining differential preservation in the
assemblages focuses on the presence of specific skeletal elements within individual
species. First, an MNI figure is established for the specific type of fish based on the
most commonly represented element (for this, lefts and rights of paired elements are
treated as unique elements). Next, the MNI figure is multiplied by the number of
elements per fish (here, paired elements are combined) to derive an expected number
of elements. Finally, the actual number of elements identified is divided by the expected
number of that element to derive a percent presence (see Russ and Jones 2009 for a
more complete discussion of the method). (Note that when a paired element is the most
common element it may not have 100% presence because of an imbalance between
the numbers of left and right examples identified.) For example, at the site of Asnæs
Havnemark the minimum number of Gadidae present is 831, based on the count of first
vertebrae (see Table 26). Using 53 as the number of vertebrae per fish, 44043 is the
expected number of vertebrae (831 x 53). In fact, 32120 Gadidae vertebrae were
identified, meaning that there were only about 73% as many as would be expected.
Other elements are present at approximately 13 to 54% of their expected values. It is
worth emphasizing that the MNI figure is a minimum and its relationship to the actual
number of fish that contributed to the assemblage is unknowable.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 831 - - 1 831 100%
All vertebra 32120 - - 53 44043 73%
Parasphenoid 330 - - 1 831 40%
Otoliths 889 454 435 2 1662 53%
Angular 645 293 352 2 1662 39%
Quadrate 546 290 256 2 1662 33%
Maxillary 473 217 256 2 1662 28%
Premaxillary 457 233 224 2 1662 27%
Posttemporal 401 187 214 2 1662 24%
Supracleithrum 273 138 135 2 1662 16%
Dentary 236 131 105 2 1662 14%
Hyomandibular 210 111 99 2 1662 13%
Table 26: Expected versus actual presence of selected Gadidae elements from Asnæs
Havnemark.
Table 27 presents similar data for Anguillidae from Asnæs Havnemark.
Here, left ceratohyal is the most common element, making 48 the minimum number of
fish represented. Vertebrae are present at about 65% of their expected rate, with other
elements in the range of 8-92%. With the exception of parasphenoid and opercle at the
low end and vomer at the high end, approximately 20-40% of the expected numbers of
non-vertebra elements are actually present in the assemblage. Pleuronectidae values
are shown in Table 28, with vertebrae producing the estimate of the minimum number of
fish present. Other types of fish at Asnæs Havnemark occur in low numbers (especially
in regards to non-vertebra elements) that do not warrant calculation of expected
presence values.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 18 - - 1 48 38%
All vertebra 3580 - - 115 5520 65%
Vomer 44 - - 1 48 92%
Parasphenoid 4 - - 1 48 8%
Ceratohyal 90 48 42 2 96 94%
Cleithrum 40 17 23 2 96 42%
Anguloarticular 35 16 19 2 96 36%
Dentary 34 14 20 2 96 35%
Maxillary 21 12 9 2 96 22%
Quadrate 17 11 6 2 96 18%
Hyomandibular 17 10 7 2 96 18%
Opercle 9 3 6 2 96 9% Table 27: Expected versus actual presence of selected Anguillidae elements from
Asnæs Havnemark.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 28 - - 1 29 97%
All vertebra 855 - - 30 870 98%
Angular 2 2 0 2 58 3%
Quadrate 9 3 6 2 58 16%
Maxillary 2 1 1 2 58 3%
Premaxillary 0 0 0 2 58 0%
Posttemporal 3 1 2 2 58 5%
Supracleithrum 3 1 2 2 58 5%
Dentary 0 0 0 2 58 0%
Hyomandibular 4 1 3 2 58 7% Table 28: Expected versus actual presence of selected Pleuronectidae elements from
Asnæs Havnemark.
Based on the identified/unidentified weight ratios and completeness of
vertebrae values at Asnæs Havnemark, it would seem to be a site with good fish bone
preservation. How do the actual to expected values there compare with another site
such as Dragsholm, where preservation may not be as good? Tables 29, 32 and 34
give the values for Gadidae, Pleuronectidae and Anguillidae from the Dragsholm
assemblage.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 885 - - 1 1107 80%
All vertebra 19580 - - 53 58671 33%
Parasphenoid 226 - - 1 1107 20%
Otoliths 2140 1033 1107 2 2214 97%
Angular 407 208 199 2 2214 18%
Quadrate 437 222 215 2 2214 20%
Maxillary 426 212 214 2 2214 19%
Premaxillary 917 474 443 2 2214 41%
Posttemporal 319 157 162 2 2214 14%
Supracleithrum 241 119 122 2 2214 11%
Dentary 272 132 140 2 2214 12%
Hyomandibular 90 52 38 2 2214 4% Table 29: Expected versus actual presence of selected Gadidae elements from Dragsholm.
At Dragsholm, the minimum number of Gadidae is 1107, based on the right
otoliths. This may be problematic, in that a great number of otoliths were found
concentrated in just a few square meters in Level 8, where as elsewhere (and in other
levels) they were much less common. Table 30 shows that the Level 8 percent
presence values are much lower than the other levels because of the high estimate for
minimum number of fish represented by otoliths. The right-hand column in the table
shows the result of excluding otoliths from the calculations – percentages that are much
more in line with the other levels. Because of this information, the numbers for the site
as a whole were recalculated without otoliths, with the results presented in Table 31.
Gadidae 7B 7C 8 8 (-otolith)
Element % presence % presence % presence % presence
First vertebra 100% 100% 14% 100%
All vertebra 30% 44% 5% 37%
Otoliths 0% 14% 97%
Angular 16% 25% 4% 28%
Quadrate 14% 27% 4% 26%
Maxillary 20% 26% 4% 28%
Premaxillary 57% 48% 9% 63%
Posttemporal 11% 17% 4% 31%
Parasphenoid 10% 22% 6% 46%
Supracleithrum 5% 13% 3% 22%
Dentary 8% 16% 3% 23%
Hyomandibular 2% 6% 1% 4% Table 30: Expected versus actual presence of Gadidae by level from Dragsholm. The
right-hand column, ‘8 (-otolith)’ present the results for Level 8 with otoliths omitted.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 885 - - 1 885 100%
All vertebra 19580 - - 53 46905 42%
Parasphenoid 226 - - 1 885 26%
Otoliths
Angular 407 208 199 2 1770 23%
Quadrate 437 222 215 2 1770 25%
Maxillary 426 212 214 2 1770 24%
Premaxillary 917 474 443 2 1770 52%
Posttemporal 319 157 162 2 1770 18%
Supracleithrum 241 119 122 2 1770 14%
Dentary 272 132 140 2 1770 15%
Hyomandibular 90 52 38 2 1770 5% Table 31: Expected versus actual presence of selected Gadidae elements from
Dragsholm, otoliths omitted.
With otoliths excluded, first vertebrae become the most common element and the
minimum number of fish is 885. Lowering the minimum number of Gadidae has the
effect of increasing the percent presence of the other elements, though the changes are
not extreme. Comparing the results with Asnæs Havnemark, the percentages of non-
vertebra elements are similar, but slightly lower at Dragsholm (with the exception of
premaxillary and parasphenoid which are higher). The difference is in the percent
presence of vertebrae. First vertebrae are the most common element at both sites, so
they have values of 100%. All vertebrae on the other hand, have a presence of 73% at
Asnæs Havnemark and only 42% at Dragsholm. Many expected vertebrae appear to be
missing from the Dragsholm assemblage, either due to conditions of preservation or
recovery (many of the Gadidae at the site are small, so some vertebrae may not have
been recovered with the 4 mm screens). This matches well with the results showing a
higher degree of fragmentation of the identified vertebrae at the site. What about the
other fish at Dragsholm?
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 275 - - 1 308 89%
All vertebra 9228 - - 30 9240 100%
Angular 15 9 6 2 616 2%
Quadrate 35 22 13 2 616 6%
Maxillary 17 5 12 2 616 3%
Premaxillary 6 2 4 2 616 1%
Posttemporal 20 13 7 2 616 3%
Supracleithrum 11 7 4 2 616 2%
Dentary 8 4 4 2 616 1%
Hyomandibular 17 5 12 2 616 3% Table 32: Expected versus actual presence of selected Pleuronectidae elements from
Dragsholm.
Pleuronectidae are notably different from Gadidae in the much lower
percent presence of non-vertebra elements (see Table 32). Comparing the different
levels at the site shows that this is consistently true (see Table 33). Pleuronectidae
display a similar pattern at Asnæs Havnemark, and also at other sites (shown below,
Tables 36, 39 and 41), with non-vertebra elements always significantly under-
represented for this type of fish.
Pleuronectidae 7B 7C 8
Element % presence % presence % presence
First vertebra 100% 68% 100%
All vertebra 71% 100% 99%
Angular 1% 3% 1%
Quadrate 4% 4% 7%
Maxillary 1% 3% 0%
Premaxillary 0% 1% 1%
Posttemporal 1% 5% 0%
Supracleithrum 1% 2% 1%
Dentary 1% 1% 0%
Hyomandibular 0% 3% 3% Table 33: Expected versus actual presence of Pleuronectidae by level at Dragsholm.
Anguillidae were the third type of fish from Dragsholm that were present in
sufficient quantities to warrant calculation of percent presence values. Although
ceratohyal and vomer values are high at Dragsholm, all of the non-vertebra elements
have lower values than at Asnæs Havnemark (compare Table 27 with Table 34). This is
also true when comparing the values from Dragsholm with those of Fårevejle and
Nederst (see below, Tables 37 and 42). In general, while some individual specimens at
Dragsholm were very well preserved, overall conditions of preservation at Dragsholm do
not seem to be as good as at the other sites in the study.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 9 - - 1 9 100%
All vertebra 313 - - 115 1035 30%
Parasphenoid 0 - - 1 9 0%
Vomer 6 - - 1 9 67%
Ceratohyal 11 8 3 2 18 61%
Cleithrum 3 1 2 2 18 17%
Anguloarticular 0 0 0 2 18 0%
Dentary 2 0 2 2 18 11%
Maxillary 1 1 0 2 18 6%
Quadrate 2 0 2 2 18 11%
Hyomandibular 0 0 0 2 18 0%
Opercle 0 0 0 2 18 0% Table 34: Expected versus actual presence of selected Anguillidae elements from Dragsholm.
Regarding the other sites, the results for Gadidae, Pleuronectidae and
Anguillidae at Fårevejle are presented in Tables 35, 36 and 37. Gadidae and
Pleuronectidae values from Bøgebjerg appear in Tables 38 and 39. Nederst provided
values for Gadidae, Pleuronectidae, Anguillidae and Trachinidae – the only site with
enough of this type of fish to justify calculating percent presence (see Tables 40, 41, 42
and 43). Finally, Lollikhuse provides values only for Gadidae (Table 44).
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 29 - - 1 36 81%
All vertebra 1260 - - 53 1908 66%
Parasphenoid 18 - - 1 36 50%
Otoliths 39 22 17 2 72 54%
Angular 25 16 9 2 72 35%
Quadrate 23 9 14 2 72 32%
Maxillary 32 17 15 2 72 44%
Premaxillary 68 32 36 2 72 94%
Posttemporal 15 7 8 2 72 21%
Supracleithrum 10 4 6 2 72 14%
Dentary 16 7 9 2 72 22%
Hyomandibular 2 1 1 2 72 3% Table 35: Expected versus actual presence of selected Gadidae elements from Fårevejle.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 21 - - 1 32 66%
All vertebra 958 - - 30 960 100%
Angular 2 0 2 2 64 3%
Quadrate 7 4 3 2 64 11%
Maxillary 2 1 1 2 64 3%
Premaxillary 1 1 0 2 64 2%
Posttemporal 5 2 3 2 64 8%
Supracleithrum 7 4 3 2 64 11%
Dentary 1 1 0 2 64 2%
Hyomandibular 7 3 4 2 64 11% Table 36: Expected versus actual presence of selected Pleuronectidae elements from Fårevejle.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 1 - - 1 5 20%
All vertebra 44 - - 115 575 8%
Parasphenoid 5 - - 1 5 100%
Vomer 2 - - 1 5 40%
Ceratohyal 5 2 3 2 10 50%
Cleithrum 6 4 2 2 10 60%
Anguloarticular 0 0 0 2 10 0%
Dentary 3 1 2 2 10 30%
Quadrate 3 2 1 2 10 30%
Hyomandibular 2 1 1 2 10 20%
Opercle 0 0 0 2 10 0% Table 37: Expected versus actual presence of selected Anguillidae elements from Fårevejle.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 45 - - 1 45 100%
All vertebra 1319 - - 53 2385 55%
Parasphenoid 7 - - 1 45 16%
Angular 3 1 2 2 90 3%
Quadrate 2 1 1 2 90 2%
Maxillary 12 4 8 2 90 13%
Premaxillary 42 25 17 2 90 47%
Posttemporal 8 3 5 2 90 9%
Supracleithrum 5 2 3 2 90 6%
Dentary 9 2 7 2 90 10%
Hyomandibular 2 1 1 2 90 2%
Otoliths 0 0 0 2 90 0% Table 38: Expected versus actual presence of selected Gadidae elements from Bøgebjerg.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 15 - - 1 30 50%
All vertebra 897 - - 30 900 100%
Angular 1 0 1 2 60 2%
Quadrate 0 0 0 2 60 0%
Maxillary 4 2 2 2 60 7%
Premaxillary 0 0 0 2 60 0%
Posttemporal 1 1 0 2 60 2%
Supracleithrum 0 0 0 2 60 0%
Dentary 0 0 0 2 60 0%
Hyomandibular 2 0 2 2 60 3%
Table 39: Expected versus actual presence of selected Pleuronectidae elements from
Bøgebjerg.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 17 - - 1 33 52%
All vertebra 1237 - - 53 1749 71%
Parasphenoid 22 - - 1 33 67%
Otoliths 59 33 26 2 66 89%
Angular 29 19 10 2 66 44%
Quadrate 26 12 14 2 66 39%
Maxillary 51 29 22 2 66 77%
Premaxillary 53 30 23 2 66 80%
Posttemporal 23 12 11 2 66 35%
Supracleithrum 34 20 14 2 66 52%
Dentary 30 13 17 2 66 45%
Hyomandibular 6 1 5 2 66 9% Table 40: Expected versus actual presence of selected Gadidae elements from Nederst.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 158 - - 1 179 88%
All vertebra 5366 - - 30 5370 100%
Angular 21 5 16 2 358 6%
Quadrate 45 28 17 2 358 13%
Maxillary 65 24 41 2 358 18%
Premaxillary 37 20 17 2 358 10%
Posttemporal 12 5 7 2 358 3%
Supracleithrum 53 30 23 2 358 15%
Dentary 5 2 3 2 358 1%
Hyomandibular 18 8 10 2 358 5% Table 41: Expected versus actual presence of selected Pleuronectidae elements from Nederst.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 30 - - 1 34 88%
All vertebra 2423 - - 115 3910 62%
Vomer 26 - - 1 34 76%
Parasphenoid 5 - - 1 34 15%
Ceratohyal 59 34 25 2 68 87%
Cleithrum 35 19 16 2 68 51%
Anguloarticular 15 8 7 2 68 22%
Dentary 10 6 4 2 68 15%
Maxillary 0 0 0 2 68 0%
Quadrate 12 5 7 2 68 18%
Hyomandibular 9 5 4 2 68 13%
Opercle 5 4 1 2 68 7% Table 42: Expected versus actual presence of selected Anguillidae elements from
Nederst.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 60 1 60 100%
All vertebra 2003 40 2400 83%
Parasphenoid 15 - - 1 60 25%
Vomer 17 - - 1 60 28%
Angular 17 9 8 2 120 14%
Quadrate 29 17 12 2 120 24%
Maxillary 20 13 7 2 120 17%
Premaxillary 17 9 8 2 120 14%
Posttemporal 30 14 16 2 120 25%
Supracleithrum 8 5 3 2 120 7%
Dentary 13 9 4 2 120 11%
Hyomandibular 26 16 10 2 120 22% Table 43: Expected versus actual presence of selected Trachinidae elements from
Nederst.
Element No. Identified L R No. per fish Expected no. % presence
First vertebra 12 - - 1 12 100%
All vertebra 358 - - 53 636 56%
Parasphenoid 1 - - 1 12 8%
Otoliths 0 0 0 2 24 0%
Angular 6 3 3 2 24 25%
Quadrate 1 0 1 2 24 4%
Maxillary 5 2 3 2 24 21%
Premaxillary 12 7 5 2 24 50%
Posttemporal 2 1 1 2 24 8%
Supracleithrum 3 1 2 2 24 13%
Dentary 1 1 0 2 24 4%
Hyomandibular 0 0 0 2 24 0% Table 44: Expected versus actual presence of selected Gadidae elements from
Lollikhuse.
In order to facilitate comparisons the percentage values are collected into
tables: Table 45 for Gadidae, Table 46 for Pleuronectidae and Table 47 for Anguillidae.
Concerning Gadidae, it can be seen that Nederst has the highest overall percent
presence values, followed by Fårevejle. Lollikhuse and Dragsholm have the lowest.
Vertebrae are well represented at Asnæs Havnemark, Fårevejle and Nederst, less so at
the other three sites (with Dragsholm the lowest). In regards to specific elements,
maxillary, premaxillary and otoliths generally have the highest presence, while
hyomandibular has the lowest. As previously discussed, Pleuronectidae non-vertebra
elements are very poorly represented in the assemblages, although Nederst and
Fårevejle seem to fair somewhat better than the other sites. It is difficult to say that any
element (other than vertebrae) is well-represented, but quadrate seems to be the best
of the lot. Two of the sites were too low in Anguillidae elements for meaningful
calculations, but amongst the other four, Asnæs Havnemark and Nederst stand out for
having the highest percent presence values. Ceratohyal, vomer and cleithrum are the
best represented elements.
Unequivocal statements about conditions of preservation at individual sites
based on the percent presence data are not possible due to uncertainty about the
causes of variation. Differences in the processing of fish for consumption (and
especially in the disposal of waste) might have affected what bones were initially
deposited and differential recovery biases played a role in which bones were recovered
during excavation. Assuming that some of the variability is attributable to preservation,
the data would indicate that non-vertebra elements survive better from Gadidae and
Anguillidae than Pleuronectidae, but vertebrae generally have the best chances of
survival overall (this is a close call for Anguillidae). Asnæs Havnemark, Fårevejle and
Nederst have the best preservation, while Dragsholm, Bøgebjerg and Lollikhuse have
the worst. In the final analysis what seems indisputable is that not all of the bones of the
fish that were caught 6-7000 years ago are part of the archaeological data set, in part
because of post-depositional destruction. Although this is an utterly unsurprising
conclusion, it is worth stating explicitly.
Gadidae Asnæs Dragsholm Fårevejle Bøgebjerg Nederst Lollikhuse
Element % presence % presence % presence % presence % presence % presence
First vertebra 100% 100% 81% 100% 52% 100%
All vertebra 73% 42% 66% 55% 71% 56%
Otoliths 53% 54% 3% 89% 0%
Angular 39% 23% 35% 2% 44% 25%
Quadrate 33% 25% 32% 13% 39% 4%
Maxillary 28% 24% 44% 47% 77% 21%
Premaxillary 27% 52% 94% 9% 80% 50%
Posttemporal 24% 18% 21% 16% 35% 8%
Parasphenoid 40% 26% 50% 6% 67% 8%
Supracleithrum 16% 14% 14% 10% 52% 13%
Dentary 14% 15% 22% 2% 45% 4%
Hyomandibular 13% 5% 3% 0% 9% 0%
Table 45: Combined actual versus expected percentage values for Gadidae.
Pleuronectidae Asnæs Dragsholm Fårevejle Bøgebjerg Nederst Lollikhuse
Element % presence % presence % presence % presence % presence % presence
First vertebra 97% 89% 66% 50% 88%
All vertebra 98% 100% 100% 100% 100%
Angular 3% 2% 3% 2% 6%
Quadrate 16% 6% 11% 0% 13%
Maxillary 3% 3% 3% 7% 18%
Premaxillary 0% 1% 2% 0% 10%
Posttemporal 5% 3% 8% 2% 3%
Supracleithrum 5% 2% 11% 0% 15%
Dentary 0% 1% 2% 0% 1%
Hyomandibular 7% 3% 11% 3% 5%
Table 46: Combined actual versus expected percentage values for Pleuronectidae.
Anguillidae Asnæs Dragsholm Fårevejle Bøgebjerg Nederst Lollikhuse
Element % presence % presence % presence % presence % presence % presence
First vertebra 38% 100% 20% 88%
All vertebra 65% 30% 8% 62%
Ceratohyal 94% 61% 50% 87%
Vomer 92% 67% 40% 76%
Cleithrum 42% 17% 60% 51%
Anguloarticular 36% 0% 0% 22%
Dentary 35% 11% 30% 15%
Maxillary 22% 6% 0% 0%
Quadrate 18% 11% 30% 18%
Hyomandibular 18% 0% 20% 13%
Opercle 9% 0% 0% 7%
Parasphenoid 8% 0% 100% 15%
Table 47: Combined actual versus expected percentage values for Anguillidae.
The preceding topics, though varied in focus and approach, all address the
quality of the fish bone data – specifically, how well does the information provided by
excavation and analysis reflect the actual fisheries that were responsible for the
assemblages? The effect of screening with different mesh-sizes was shown to impact
the assemblages in two ways: smaller screen sizes increase the overall number of fish
bones recovered and larger screen sizes create a bias against smaller fish (and this is
reflected in the relative abundance of species). The absolute number of fish bones
recovered is not of fundamental importance (except in so far as larger samples are
more likely to contain species of fish that are sparsely represented; fish that are by
definition of only minor importance to subsistence). What is critical is that the samples
that are taken accurately represent the deposits. Screening studies from Asnæs
Havnemark, Dragsholm and Nederst have shown that using smaller mesh-size screens
during excavation would have increased the number of types of fish recovered and
changed the relative abundances of the assemblages. Fishes that were only recovered
with the smaller mesh-sizes include Gasterosteidae, Syngnathidae, Zoarcidae and
Gobiidae. These are quite small fishes, and even with the enhanced recovery
techniques occurred in very limited numbers. Based on the available information, their
economic importance at these three sites can be described as minimal. (See Enghoff
1986 and 1991 for descriptions of the assemblages from Ertebølle and Bjørnsholm,
where Gasterosteidae may have played a more important role. Jonsson 1986 also
reports that Gasterosteidae may have had some economic importance at Skateholm.)
Much more significant are the changes in relative abundance caused by the use of
smaller mesh-sizes, as generally small fishes such as Clupeidae and Anguillidae are
recovered in much greater numbers. Although the number of specimens for all fish
increased with the use of smaller mesh-sizes in the screening experiments at Asnæs
Havnemark and Dragsholm, relative abundances shifted away from larger fish (e.g.,
Gadidae and Pleuronectidae) towards the smaller ones (e.g., Anguillidae and
Clupeidae). This finding must be borne in mind when using data from other sites that
were excavated with larger mesh screens, although whether they would actually
experience analogous shifts with finer screening cannot be established. It should also
be remembered that while finer screening increased the abundance of smaller fishes,
the change was relatively modest and Gadidae remained the dominant fish in both
assemblages. Excavator skill as a source of recovery bias was also considered and
found to be potentially significant. Less skilled excavators tend to be better at recovering
larger specimens and elements that are easily recognized (i.e., vertebrae). Variations in
relative abundances between excavators due to the under-representation of smaller
vertebrae were not large (possibly because smaller fish were a minor part of the overall
assemblages), but still must be considered as a source of error. More worrisome is the
tendency of less-skilled excavators to overlook non-vertebra elements in the course of
excavation. In some instances, there is significant variation between the highest and
lowest recovery rates of these elements at a site. Using only vertebra counts to
calculate relative abundances (not NISP) may help to alleviate this problem, but for
other indices that rely on non-vertebra elements (e.g., actual versus expected presence)
this is not a possibility. The best option is for fish bone samples to be excavated by
archaeologists who are highly familiar with the materials to be recovered.
Differential preservation at the sites was examined by comparing the
weights of identified and unidentified fractions, tabulating the degree of fragmentation of
vertebrae and calculating the ratio of the actual to the expected presence of a number
of different types of elements. The weight of unidentified bone was a minority portion of
the overall assemblage weight in every instance, although at Dragsholm it approached
40%. Examining the degree of fragmentation revealed an intriguing difference between
Gadidae vertebrae at Nederst and those at Asnæs Havnemark and Dragsholm,
although overall the results indicated that vertebrae remained fairly complete in the
assemblages. This finding must be tempered by remembering that fragmentary
vertebrae may not have been identifiable, and thus would not be included. Finally, the
ratios of actual to expected presence showed that it is likely that a number of bones that
were initially deposited are now missing from the assemblages. This seems to be
especially true for non-vertebra elements of Pleuronectidae; another reason to compare
results using vertebrae when possible. Differences in ratios between sites attest that
conditions of preservation were not equal, with Dragsholm, Bøgebjerg and Lollikhuse
seemingly most affected by bone loss. It cannot be ruled out that some of the variation
may result from differences in initial deposition or differential recovery. In summary,
preservation and recovery can definitely influence archaeological fish assemblages and
should be considered when using data from them. In many instances the introduced
biases are not so great as to preclude the use of the fish data, but this should be
evaluated on a case-by-case basis and, where possible, allowances made for them.
Preservation at the sites that were analyzed for this project can be described as fairly
good and reasonable confidence that the identified assemblages are indicative of
prehistoric activities is justified. Having surveyed some of the issues with data quality in
a review of the methodological results, now it is time to describe some of the other
findings of the project that bear more directly on cultural interpretations.
5.2 Intra-site variability
Many Ertebølle sites are the result of either long-term or repeated
occupations that span centuries, but to date interpretations based on fish bones have
largely treated the Mesolithic components of sites as if they were uniform entities,
despite acknowledgement that both the quantity of fish bone and types of fish vary
between contexts at some sites (e.g., Enghoff 1989 and 1991). An appreciation of the
variation within assemblages can lead to a better understanding of the dynamic nature
of Ertebølle culture.
At Dragsholm the number of identified specimens varies considerably from
level to level, although this information by itself is not particularly informative as the
length of occupation represented by the deposits is uncertain. What is of interest are
some of the other changes that occur. Table 48 presents the counts of fish specimens
by level from Trench 11 and Table 49 presents this data transformed into relative
abundances (fishes that have values less than 0.5% in every level are omitted from the
table). Gadidae and Pleuronectidae are the two fishes of primary interest, as the others
are very minor components. Looking at the progression from Level 7B to 8 (younger to
older), Gadidae increase in abundance at the expense of Pleuronectidae (there is also a
slight decline in the combined abundance of the other species). Level 7A is an
exception to this pattern with a high percentage of Gadidae, but it is also a much
smaller sample than the others. The changes in relative abundance are shown
graphically in Figure 41.
Ga
did
ae
Ple
uro
ne
cti
da
e
Co
ttid
ae
Sq
ua
lid
ae
Be
lon
ida
e
Sc
om
bri
da
e
An
gu
illid
ae
Tra
ch
inid
ae
Tri
glid
ae
Clu
pe
ida
e
Zo
arc
ida
e
Sa
lmo
nid
ae
Pe
rcid
ae
Es
oc
ida
e
Cy
pri
nid
ae
Ide
nti
fie
d
7A vertebra 290 86 13 6 1 0 2 6 3 1 0 0 0 0 0 408
7B vertebra 2509 1672 134 75 126 13 41 21 45 10 4 3 0 0 1 4653
7C vertebra 10956 5374 293 359 301 321 242 91 63 76 7 6 5 2 1 18096
8 vertebra 2292 786 34 28 26 55 15 13 5 3 2 1 0 1 0 3261 Table 48: Vertebra count by level for Trench 11 at Dragsholm.
Ga
did
ae
Ple
uro
ne
cti
da
e
Co
ttid
ae
Sq
ua
lid
ae
Be
lon
ida
e
Sc
om
bri
da
e
An
gu
illid
ae
Tra
ch
inid
ae
Tri
glid
ae
7A vertebra 71% 21% 3% 1% 0% 0% 0% 1% 1%
7B vertebra 54% 36% 3% 2% 3% 0% 1% 0% 1%
7C vertebra 61% 30% 2% 2% 2% 2% 1% 1% 0%
8 vertebra 70% 24% 1% 1% 1% 2% 0% 0% 0% Table 49: Relative abundance by level for Trench 11 at Dragsholm.
Figure 41: Relative abundance by level for Trench 11 at Dragsholm.
By itself, the shift in abundance is an interesting finding, but it is even more intriguing
when combined with fish size information. Gadidae size estimations were based on
measurements of otoliths and first vertebrae. The otoliths in the assemblage were
identified to species and to side (left or right), then measured for maximum length and
width. In many cases, breakage prevented the measurement of a maximum length and
otoliths that were eroded were not measured at all. From a total of 2152 otoliths, 1524
are cod (Gadus morhua), 33 are saithe/pollock (Pollachius sp.), 7 are whiting
(Merlangius merlangus) and the remaining 588 are cod family, unspecified. Of the cod
otoliths, 787 were suitable for length measurements (728 from Level 8 and 59 from
Level 7C). Fish total length (TL) was estimated using otolith length (OL) by means of a
linear regression formula:
TL = -202.13 + 48.37(OL) (Härkönen 1986:90)
Fish weight (FW) was estimated from fish length (TL) by means of a different regression
formula:
FW = 0.0039621(TL)3.2375 (Olson et al. 2008:2817)
The lower half of Table 50 presents summary information derived from otolith lengths,
and Figures 42 and 43 present the size distributions graphically. Average sizes are
larger in Level 8 than 7C (by 2.8 cm or ca. 125 g) but more striking is the size of the
largest cod present: ca. 900 g in Level 7C versus over 2 kg in Level 8.
Unfortunately, comparisons with Levels 7B and 7A are not possible with this
approach because no otoliths were recovered from these levels. For this reason, a
second set of size estimates was calculated using the width of the posterior centrum of
first vertebrae. First vertebrae are more difficult to identify to species than otoliths and
so the following information includes measurements for all of the gadid first vertebrae
that were complete in the relevant dimension. Based on the information from the
otoliths, cod are by far the dominant species in the assemblage so any error introduced
by the presence of other species should be minimal. Weight estimates were based on
total length using the formula above, while total length was derived from measurements
of first vertebra width (W) using the formula:
TL = 87.3172(W)0.8260 (Enghoff 1983:89)
A total of 553 first vertebrae were measured (6 from Level 7A, 94 from Level 7B, 385
from Level 7C and 68 from Level 8) and the summary results are shown in the upper
half of Table 50. Figures 44-47 present the size distributions graphically for Levels 8,
7C, 7B and the whole assemblage (Level 7A had only six specimens and did not
warrant a graph). Average cod sizes ranged from 33 cm (ca. 330 g) in Level 7B to 41
cm (ca. 630 g) in Level 8. Very intriguingly, there is a progression of increasing average
sizes from Levels 7B through 8 (with Level 7A appearing out of step) which echoes the
progression of increasing relative abundance of Gadidae seen above. Not only do the
older layers have a higher proportion of Gadidae, but the fish are larger. This can also
be seen with the largest specimen from each of the layers, as successive layers show
an increasingly large ‘trophy’ fish (here, Level 7A fits with the other levels in this
pattern). Comparing Level 7B with Level 8, the weights of both the average and the
largest fish are approximately twice as heavy in the older layer. One final note on Table
50 is that it is satisfying to see the good agreement between the average sizes as
calculated for otoliths and first vertebrae in Levels 7C and 8, although the largest fish
sizes are greater with the first vertebra method.
Figure 44: Gadid lengths Level 8 Dragsholm. Figure 43: Cod lengths Level 8 Dragsholm.
Figure 45: Gadid lengths Level 7C Dragsholm. Figure 42: Cod lengths Level 7C Dragsholm.
Figure 46: Gadid lengths Level 7B Dragsholm.
Figure 47: Gadid lengths from all levels combined.
First vertebrae 7A 7B 7C 8
N = 6 94 385 68
Mean length (cm) 36,5 33,0 36,3 40,5
Std Dv 5,5 4,7 6,7 8,1
Median length 37 32 36 38
Smallest length 27 25 17 23
Largest length 44 50 57 64
Mean weight (g) 453 327 445 634
Small weight 169 126 41 107
Large weight 805 1222 1917 2761
Otoliths 7C 8
N = 59 728
Mean length (cm) 36,5 39,3
Std Dv 5,3 6,2
Median length 36 39
Smallest length 25 16
Largest length 45 58
Mean weight (g) 453 575
Small weight 130 32
Large weight 898 2051 Table 50: Gadid sizes from Dragsholm.
Having identified a change in Gadidae size that seems to correspond with the change in
relative abundance, it is natural to examine Pleuronectidae to see if they also differ in
size between levels. No otoliths from these fish were recovered so first vertebra
measurements provided the only way to estimate sizes. The maximum width (W) of the
posterior face of the first vertebrae were measured and used to estimate total length
(TL) with the regression formula:
TL = 69.7268(W)0.9068 (Enghoff 1989:46)
A total of 131 vertebrae were suitable for measurement (none from Level 7A, 29 from
Level 7B, 84 from Level 7C and 18 from Level 8). Table 51 shows the summary data
and Figures 48 through 51 show the size distributions by level and for the site as a
whole. Estimated average sizes are 28 cm in Levels 7B and 7C and 30cm in Level 8.
There are no published formulas for deriving weight from length for Pleuronectidae, but
using lengths and weights of comparative specimens a very rough estimate would be a
50-60 g difference in weight for the 2 cm difference in length. There is a range of 37-42
cm for the largest fish in each level, with Level 7C having the biggest specimen.
Although the average fish in Level 8 are slightly larger than the other two levels it is hard
to attach great significance to this given the relatively small difference in weight this
represents. Unlike Gadidae, the Pleuronectidae size estimates do not suggest much
change in the fishery. Anguillidae size estimates are available for only 14 elements, 12
of which are from Level 7C, so comparisons are not meaningful. It is however,
interesting to examine the results from other sites.
First Vertebra 7A 7B 7C 8
N = 0 29 84 18
Mean length (cm) 28,0 27,6 30,3
Std Dv 4,1 4,2 3,6
Median length 27,8 27,3 30,3
Smallest length 20,0 17,7 24,5
Largest length 37,5 41,8 37,0
Figure 48: Flatfish size from Dragsholm. Table 51: Flatfish sizes from Dragsholm.
Figure 49: Flatfish size from Level 7B Dragsholm. Figure 50: Flatfish size from Level
7C Dragsholm.
Figure 51: Flatfish size from Level 8 Dragsholm.
The vertebra counts from Fårevejle are presented in Table 52 and
converted to relative abundances in Table 53 (again omitting the fishes that are a very
minor component). Looking at the data graphically (Figure 52), the pattern is similar to
Dragsholm with increasing abundance of Gadidae and decreasing Pleuronectidae
progressing from younger to older layers. Level 5 is the only part of the graph that does
not fit the overall pattern. Based on ceramic typology, Levels 3 and 4 may contain
mostly Neolithic materials, which would mean that there is a clear increase in Gadidae
(and corresponding decrease in Pleuronectidae) with increasing age in the Mesolithic
levels. This conclusion must be qualified by the relatively small sample size for the
individual levels. Only 21 cod otoliths were available for size estimations and there is no
obvious patterning to size distribution within the midden (see Table 54 for the
estimates). It is noteworthy that the average size of the cod is 45 cm (ca. 1 kg) – much
larger than those at the nearby site of Dragsholm. Only 18 first vertebrae are available
for size estimates of Pleuronectidae and the results also do not show any size
progression between levels (see Table 55).
Gad
idae
Pleuronectidae
Angu
illidae
Belonidae
Clupeidae
Cyp
rinidae
Scombridae
Esocidae
Cottidae
Salm
onidae
Iden
tified
Level 3 vertebra 55 52 0 1 0 0 0 0 0 0 108
Level 4 vertebra 179 127 8 0 0 1 0 1 0 0 316
Level 5 vertebra 368 435 15 7 0 4 0 1 0 0 830
Level 6 vertebra 479 292 20 7 6 2 2 0 1 1 810
Level 7 vertebra 125 39 4 0 2 0 0 0 1 0 171
Level 8 vertebra 26 9 0 0 0 0 0 0 0 0 35
Table 52: Vertebra count by level for Trench 1 at Fårevejle.
Gad
idae
Pleuronectidae
Angu
illidae
Belonidae
Clupeidae
Level 3 vertebra 51% 48% 0% 1% 0%
Level 4 vertebra 57% 40% 3% 0% 0%
Level 5 vertebra 44% 52% 2% 1% 0%
Level 6 vertebra 59% 36% 2% 1% 1%
Level 7 vertebra 73% 23% 2% 0% 1%
Level 8 vertebra 74% 26% 0% 0% 0% Table 53: Relative abundance by level for Trench 1 at Fårevejle.
Figure 52: Relative distribution by level for Trench 1 at Fårevejle.
East North Level OL (mm) TL (cm) Weight (g)
141 112 3 12,3 39 574
141 112 3 14,1 48 1098
140 112 4 13,2 44 807
141 113 4 16,1 58 1990
141 109 5 11,5 35 411
141 109 5 11,6 36 429
141 111 5 12,2 39 552
141 109 5 13,7 46 961
141 109 5 14,0 48 1063
141 109 5 16,3 59 2100
141 114 6 13,5 45 897
140 113 6 13,8 47 994
140 113 6 14,5 50 1248
140 112 7 10,4 30 242
140 112 7 13,2 44 807
140 112 7 17,4 64 2782
140 109 8 11,2 34 359
140 109 8 12,3 39 574
140 109 8 12,5 40 621
140 109 8 14,0 48 1063
140 112 8 15,2 53 1543 Table 54: Estimated cod sizes at Fårevejle based on otolith measurements.
East North Level W (mm) TL (cm)
141 112 4 4,2 26
140 112 4 4,8 29
141 112 4 4,9 29
141 112 4 5,2 31
141 110 5 3,4 21
141 109 5 3,9 24
141 111 5 4,6 28
141 109 5 4,7 28
141 109 5 4,9 29
141 111 5 5,0 30
140 109 5B 5,2 31
141 111 5 5,6 33
140 108 5 5,9 35
140 109 6 4,2 26
140 109 6F 4,9 29
141 111 6 5,2 31
140 112 7 4,5 27
140 112 7 4,5 27 Table 55: Estimated Pleuronectidae sizes at Fårevejle based on first vertebrae.
Based on the results from Dragsholm and Fårevejle it would be tempting to
hypothesize a general trend during the Ertebølle period of increasing Gadidae and
decreasing Pleuronectidae with increasing age of the deposits, but the results from
Bøgebjerg (just a hundred meters from Dragsholm and several kilometers from
Fårevejle) show that it is not that simple. Table 56 shows the vertebra counts by level
and Table 57 converts these to relative abundances, while Figure 53 displays the
information graphically. At Bøgebjerg, the deeper (older) deposits show the percentage
of Pleuronectidae increasing (although still remaining secondary to Gadidae). Size
information for Gadidae estimated from first vertebrae does not help (only 38 specimens
could be measured, and of these 20 come from Level 7), as Levels 1, 5 and 7 have
average weights of 400-500 g, while Level 3 (N = 5) has an average of 760 g. An
interesting observation, whose meaning is not clear, is the high proportion of Gadidae
first, second and third vertebrae in Levels 1 and 3: 37 of 70 and 106 of 234,
respectively. Remembering that Gadidae average 53 vertebrae, there is a clear
discrepancy here between the actual count and what would be expected, although the
small sample sizes warn against interpreting too much from this information.
Regardless, the reversal of the pattern of increasing Gadidae relative abundance with
depth seen at the first two sites is an interesting result.
G
ad
ida
e
Ple
uro
ne
ctid
ae
Be
lon
ida
e
Co
ttid
ae
An
gu
illid
ae
Scom
bri
da
e
Sq
ua
lid
ae
Tra
chin
ida
e
Clu
pe
ida
e
Ide
ntifie
d
Level 1 vertebra 70 16 1 2 0 0 0 3 0 92
Level 3 vertebra 234 46 2 7 1 0 0 4 0 294
Level 5 vertebra 153 114 8 9 6 2 2 1 0 295
Level 7 vertebra 852 721 91 38 13 18 10 4 2 1749
Table 56: Vertebra count by level for Trenches 2 and 3 at Bøgebjerg.
Ga
did
ae
Ple
uro
ne
ctid
ae
Be
lon
ida
e
Co
ttid
ae
An
gu
illid
ae
Sco
mb
rid
ae
Sq
ua
lid
ae
Tra
ch
inid
ae
Clu
pe
ida
e
Level 1 vertebra 76% 17% 1% 2% 0% 0% 0% 3% 0%
Level 3 vertebra 80% 16% 1% 2% 0% 0% 0% 1% 0%
Level 5 vertebra 52% 39% 3% 3% 2% 1% 1% 0% 0%
Level 7 vertebra 49% 41% 5% 2% 1% 1% 1% 0% 0% Table 57: Relative abundance by level for Trenches 2 and 3 at Bøgebjerg.
Figure 53: Relative abundance by level for Trenches 2 and 3 at Bøgebjerg.
The results from Asnæs Havnemark are displayed in Tables 58 and 59 and
Figure 54. Radiocarbon dates suggest a relatively short duration of occupation (ca. 300
years) and the relative abundances show only a slight tendency for decreasing Gadidae
and increasing Anguillidae with increasing depth. (The deposits from the grey layer
have a high percentage of Gadidae but were collected exclusively by Excavators C and
D, both of whom produced an under-representation of smaller specimens. This context
is also impoverished in the percentage of the NISP comprised of non-vertebra
elements, suggesting that excavator bias may be appreciably distorting the results for
this layer).
Ga
did
ae
An
gu
illid
ae
Ple
uro
ne
cti
da
e
Co
ttid
ae
Sc
om
bri
da
e
Clu
pe
ida
e
Tri
glid
ae
Be
lon
ida
e
Tra
ch
inid
ae
Sq
ua
lid
ae
Zo
arc
ida
e
Sa
lmo
nid
ae
Cy
pri
nid
ae
Sy
ng
na
thid
ae
Ide
nti
fie
d
Culture layer 24878 2261 637 358 222 107 82 34 21 25 4 7 1 0 28637
Shell 3636 687 64 97 150 44 10 2 7 5 3 1 0 0 4706
Brown surface 2608 611 116 34 62 16 14 2 5 0 10 5 7 0 3490
Grey layer 1116 43 26 6 9 0 4 3 0 0 1 0 0 1 1209
Table 58: Vertebra count by level at Asnæs Havnemark.
Ga
did
ae
An
gu
illid
ae
Ple
uro
ne
cti
da
e
Co
ttid
ae
Sc
om
bri
da
e
Clu
pe
ida
e
Culture layer 87% 8% 2% 1% 1% 0%
Shell 77% 15% 1% 2% 3% 1%
Brown surface 75% 18% 3% 1% 2% 0%
Grey layer 92% 4% 2% 0% 1% 0%
Table 59: Relative abundance by level at Asnæs Havnemark.
Figure 54: Relative abundance by level at Asnæs Havnemark.
Cod otoliths were in good supply in the Asnæs Havnemark assemblage, so
they were used for size estimates using the same formulas as at Dragsholm. Table 60
presents summary data for the different levels and Figures 55 through 59 display size
distributions. It was not necessary to calculate values on first vertebrae, as all of the
levels at Asnæs Havnemark had reasonably large samples of otoliths. In line with the
homogeneity of the relative abundance numbers, both the average and the largest sizes
of cod are quite uniform between the levels.
Otoliths
Culture
layer Shell
Brown
surface
Grey
layer
N = 196 84 81 27
Mean length (cm) 32,8 33,7 33,9 32,6
Std Dv 6,4 6,2 6,8 8,1
Median length 32 32 25 31
Smallest length 20 21 20 20
Largest length 52 53 51 49
Mean weight (g) 320 350 356 314
Small weight 64 74 59 61
Large weight 1415 1496 1329 1175 Table 60: Estimated cod sizes at Asnæs Havnemark based on otoliths.
Figure 55: Cod sizes from all levels Asnæs Havnemark.
Figure 56: Cod sizes from the Culture layer. Figure 57: Cod sizes from the Shell layer.
Figure 58: Cod sizes from the Brown surface. Figure 59: Cod sizes from the Grey layer.
Anguillidae lengths (TL) were estimated from measurements of the ceratohyal (K) using
the regression formula:
TL = 345.2232(K)0.7460 (Enghoff 1986:69)
Table 61 displays the summary information by level and in total for the size estimates.
Figure 60 shows the size distribution for the whole assemblage graphically. Note that
there is very little difference between the levels for the average sizes.
All Culture Shell Brown
N = 79 42 13 24
Mean 61 62 59 62
StdDv 11 12 11 9
Median 60 62 60 60
Smallest 42 42 42 49
Largest 86 86 74 80 Table 61: Anguillidae sizes by level at Asnæs Havnemark based on ceratohyal.
Figure 60: Anguillidae size distribution at Asnæs Havnemark.
Asnæs Havnemark provides a good example of a site with relatively
homogenous deposits that is dominated by a single type of fish; Lollikhuse provides
another, albeit with a different fish. Tables 62 and 63 present the vertebra count and
relative abundance data for the site. Figure 61 illustrates the generally uniform relative
abundances, dominated in every level by Pleuronectidae. Level 0 is the most out of line
with the other levels, but this may be due mostly to a very small sample size (N = 39).
The uniform (and uncharacteristically high) abundances of Belonidae are an unusual
feature of this site, as this fish is usually a very minor component of assemblages. Size
estimates are only available for nine Anguillidae elements and provide no information on
intra-site variability.
Ple
uro
ne
cti
da
e
Ga
did
ae
Be
lon
ida
e
An
gu
illid
ae
Clu
pe
ida
e
Sc
om
bri
da
e
Tri
glid
ae
Ide
nti
fie
d
0 23 13 3 0 0 0 0 39
10 146 11 4 6 3 0 0 170
20 70 17 11 4 0 0 0 102
30 1034 128 114 34 8 2 1 1321
40 268 80 23 16 0 4 0 391
50 37 11 3 0 0 2 0 53
60 47 6 7 2 0 1 0 63 Table 62: Vertebra counts by level at Lollikhuse.
Ple
uro
ne
cti
da
e
Ga
did
ae
Be
lon
ida
e
An
gu
illid
ae
Clu
pe
ida
e
Sc
om
bri
da
e
Tri
glid
ae
0 59% 33% 8% 0% 0% 0% 0%
10 86% 6% 2% 4% 2% 0% 0%
20 69% 17% 11% 4% 0% 0% 0%
30 78% 10% 9% 3% 1% 0% 0%
40 69% 20% 6% 4% 0% 1% 0%
50 70% 21% 6% 0% 0% 4% 0%
60 75% 10% 11% 3% 0% 2% 0%
Table 63: Relative abundance by level at Lollikhuse.
Figure 61: Relative abundance by level at Lollikhuse.
One additional site has fish bone information available at a level of detail
that allows close scrutiny of intra-site variation, and despite insufficient information
about the contexts, it is in some ways the most interesting. As part of this project, 14
samples from skaldynge I (shell heap I) at Nederst were analyzed and the results are
presented in Tables 64 and 65. One look at the graph in Figure 62 reveals that the
levels here show great variability (note that unlike at the other sites, progressing from
left to right on the graph does not necessarily signify increasing age of the deposits).
Figure 63 shows the summary results from skaldynge II, showing still another pattern of
relative abundances (data from Enghoff 1994a).
Le
vel
Ple
uro
ne
cti
da
e
An
gu
illid
ae
Tra
ch
inid
ae
Ga
did
ae
Clu
pe
ida
e
Zo
arc
ida
e
Sc
om
bri
da
e
Co
ttid
ae
Sa
lmo
nid
ae
Sy
ng
na
thid
ae
Ide
nti
fie
d
10 1432 134 46 53 75 4 0 4 1 0 1749
12 681 595 224 156 185 3 9 0 2 0 1855
13 74 81 154 15 9 3 0 4 1 0 341
20 1003 544 1057 287 91 175 3 13 12 2 3187
Shell 2073 784 387 652 441 28 7 0 5 1 4378
Table 64: Vertebra counts by level at Nederst skaldynge I.
Le
ve
l
Ple
uro
ne
cti
da
e
An
gu
illid
ae
Tra
ch
inid
ae
Ga
did
ae
Clu
pe
ida
e
Zo
arc
ida
e
10 82% 8% 3% 3% 4% 0%
12 37% 32% 12% 8% 10% 0%
13 22% 24% 45% 4% 3% 1%
20 31% 17% 33% 9% 3% 5%
Shell 47% 18% 9% 15% 10% 1% Table 65: Relative abundance by level at Nederst skaldynge.
Figure 62: Relative abundance by level at Nederst skalydynge I.
Figure 63: Relative abundances for skaldynge II (Enghoff 1994a).
The differences in relative abundances between levels clearly show that the fishery was
not a uniform phenomenon, but a look within the levels provides even more proof of
this. Figures 64-67 illustrate the assemblages of the individual square meters within four
of the levels at Nederst (only one square from Level 12 was analyzed). It is readily
apparent that attempts to characterize levels with aggregate values serves to conceal
the true nature of individual contexts. Compare this situation with Figures 68-71,
showing the results by square for the Culture Layer at Asnæs Havnemark and three
layers from Dragsholm. Although not identical, almost any individual square meter at
Asnæs Havnemark or Dragsholm would give a reasonably accurate impression of the
level as a whole. Additional evidence for variability in the Nederst skaldynge I
assemblage comes from fish size estimates. Table 66 for Anguillidae and Table 67 for
Pleuronectidae, although suffering from small sample sizes in a few instances, show
that Level 10 in particular is distinguished by larger average fish sizes than the other
levels. (Figures 72 and 73 show the size distributions for Anguillidae and
Pleuronectidae.) Although many of the other sites have displayed some differences
between contexts, Nederst’s variability is much greater than any site seen so far. Two
previously analyzed and published sites, Norsminde and Ertebølle, suggest that this not
a unique occurrence.
Figure 64: Relative abundances within Level 10 at Nederst.
Figure 65: Relative abundances within Level 13 at Nederst.
Figure 66: Relative abundances within Level 20 at Nederst.
Figure 67: Relative abundances within the Shell at Nederst.
Figure 68: Relative abundances within the Culture layer at Asnæs Havnemark.
Figure 69: Relative abundances within Layer 7B at Dragsholm (squares with NISP < 10
omitted).
Figure 70: Relative abundances within Layer 7C at Dragsholm (squares with NISP < 10
omitted).
Figure 71: Relative abundances within Layer 8 at Dragsholm (squares with NISP < 10 omitted).
Level 10 Level 12 Level 13 Level 20 Shell
N = 4 10 3 16 14
Mean (cm) 63 49 56 49 50
StdDv 7 12 7 14 15
Median 64 44 56 46 50
Smallest 54 32 49 37 35
Largest 70 70 62 82 88 Table 66: Anguillidae sizes by level at Nederst.
Figure 72: Anguillidae size distribution at Nederst.
Level 10 Level 12 Level 13 Level 20 Shell
N = 30 20 2 20 46
Mean (cm) 27 22 25 23 25
Std Dev 3 4 5 5 5
Median 27 22 25 25 25
Smallest 22 13 21 14 15
Largest 33 30 28 34 52 Table 67: Pleuronectidae sizes by level at Nederst.
Figure 73: Pleuronectidae size distribution at Nederst.
Norsminde, like Nederst, was extensively excavated (completely in the case
of Norsminde), but the data is not published in a manner that allows comprehensive
investigation of intra-site variability (Enghoff 1989). Two squares (31/28 and 32/28) are
reported individually, and the relative abundances in these adjacent contexts indicate a
non-uniform assemblage (see Figure 74). Additionally, while the majority of the
assemblage comes from a limited area designated the ‘fish layer’ and is dominated by
Pleuronectidae, outside of this concentration the majority of the fish (783 out of 854
specimens) are Gadidae (Enghoff 1989:45). Again, the impression is of a site with
considerable differences between various parts of the midden.
Figure 74: Relative abundances for two squares at Norsminde (Enghoff 1989).
The shell midden at Ertebølle was sampled by a single, one meter wide
trench, limiting the potential to examine horizontal variation within the deposits. A
column sample was processed to recover fish remains, and this information is published
by levels, allowing a review of vertical differences in the assemblage (Enghoff 1986:70).
Most of the individual samples have few identified specimens, limiting their reliability,
but samples N13, 14 and 15 in the middle of the column are sufficiently large to warrant
closer examination. Figure 75 presents the relative abundances for these three
contexts, while Figure 76 presents the same three without three-spined stickleback
(Gasterosteidae) (this fish was highly concentrated in the N-column and its abundance
here is not considered representative for the site as a whole) (Enghoff 1986:68). Even
without Gasterosteidae, the three samples appear different, with a much higher
frequency of Cyprinidae in the lower samples.
Figure 75: Relative abundances for three samples in the N-column at Ertebølle (Enghoff
1986).
Figure 76: Relative abundances (minus Gasterosteidae) for three samples in the N-
column at Ertebølle (Enghoff 1986).
From the examples discussed above, it is clear that many assemblages
(especially shell middens) have substantial internal variability and this has implications
for both interpretation and future excavations. Whether the changing catches were a
result of environmental or cultural factors (or both) is difficult to ascertain, but regardless
of causation, the fact that fisheries in the same locations changed through time reveals
a previously unappreciated flexibility. It is not possible to say whether the variation
between levels at any of the sites is related to diet breadth changes by comparing
indices of richness or heterogeneity because in every instance NTAXA is significantly
correlated to NISP, but the results do show that Ertebølle fisheries were not a static
phenomenon.
Intra-site variability also has some important implications for excavation
strategies and sampling. Although there is no substitute for empirically establishing the
nature of individual site deposits, one general pattern can be proposed: outcast deposits
display more internal uniformity than shell middens. Further work is necessary to more
conclusively confirm or deny this, but the available evidence supports the statement.
Assuming that it is true, the representativeness of fish assemblages from single, narrow
trenches transecting shell middens is questionable (e.g., Bjørnsholm: sampled by a one
meter wide trench in a shell midden that stretches for over 325m) (Andersen 1991:59-
60). If at all possible, future shell midden excavations should emphasize collecting fish
samples from horizontally and vertically dispersed contexts in an attempt to capture a
more comprehensive picture of the fish assemblages. Conversely, when excavating
outcast deposits more emphasis can be placed on obtaining equivalent samples from
multiple levels. It may be a wise strategy to terminate the collection of fish remains from
parts of levels that are already well-sampled in order to concentrate resources on
increasing sample-sizes from under-represented contexts.
5.3 Regional differences
Perhaps the most important finding of this project is a real difference
between fisheries in the western and eastern parts of Denmark. Previously, although
regional variability in fish assemblages was recognized (Enghoff 1994a:89), the
distinction was not made between an eastern fishery largely focused on Gadidae (and
secondarily on Pleuronectidae) and a western fishery that is highly variable and not
easily categorized (see Figure 77 and Tables 68 and 69). Differential recovery has not
been discussed as a potential source of regional variation, despite the fact that all of the
assemblages in the East were recovered with coarse mesh-sizes, while those in the
West were collected using finer mesh-sizes. Figure 78 shows a plot of the percentage of
Gadidae at sites versus the mesh-size used during excavation. With the exception of
one site in the West dominated by Gadidae (Lystrup Enge) and two in the East
dominated by Pleuronectidae (Maglemosegårds Vænge and Lollikhuse), the correlation
between larger mesh-size and a high proportion of Gadidae in fish assemblages
appears quite strong. Fortunately, the screen-test results available from Dragsholm and
Asnæs Havnemark provide a good argument that the observed regional difference in
preferred fish is real, and not merely an artifact of differential recovery (Figure 79). Two
previously described sites (Ølby Lyng and Sølager) that are not included in Figure 77
because of probable differential recovery issues are nonetheless interesting as
additional examples of eastern sites that are heavily dominated by Gadidae.
Figure 77: Percentages of fish by site. First group is Jutland, second is Northwest
Zealand and the third is Northeast Zealand. Note that Østenkær and Jesholm are not
included because of small sample sizes, and for Stationsvej 19 all indeterminate flatfish
have been included as Pleuronectidae.
Bjø
rns
ho
lm (
1)
Ert
eb
ølle
(2
)
Ha
vn
ø
Je
sh
olm
I
Ly
str
up
En
ge
(4
)
Ne
de
rst
I
Ne
de
rst
II (
4)
No
rsm
ind
e (
3)
Yd
erh
ed
e (
4)
Øs
ten
kæ
r (4
)
NISP 11490 9462 330 38 9233 13779 6476 9158 523 11
Gadidae 10% 8% 4% 8% 74% 12% 23% 29% 2%
Pleuronectidae 1% 1% 8% 16% 23% 43% 21% 58% 52% 9%
Anguillidae 56% 17% 73% 11% 1% 19% 38% 8% 8% 18%
Cyprinidae 14% 67% P
Trachinidae 6% 5% 50% 17% 2% P 1%
Belonidae P 1% 3% P
Clupeidae P 1% 3% 3% 1% 6% 14% 3%
Scombridae 2% P P P P
Cottidae P P P 3% P P P 1%
Gasterosteidae 7% 1% P 1% P 1%
Squalidae P P 8% P P P 32%
Zoarcidae P P 1% P 2% 2% P 1%
Triglidae P P 3% P P 1%
Percidae P 3%
Esocidae P P P 45%
Salmonidae P P 3% P P 1% 27%
Sparidae 1%
Scophthalmidae P P P P P P
Carangidae P
Gobiidae P P P
Moronidae P P
Callionymidae P
Ammodytidae P P Table 68: Percentage of fish by family for sites on Jutland (P = rounds to 0%).
(1) Data from Enghoff 1991. (2) Data from Enghoff 1986. (3) Data from Enghoff 1989.
(4) Data from Enghoff 1994a and only published in summary form.
As
næ
s H
av
ne
ma
rk
Bø
ge
bje
rg
Dra
gs
ho
lm
Få
rev
ejle
Sm
ak
ke
rup
Hu
se
(5
)
He
nri
ks
ho
lm-B
(4
)
Lo
llik
hu
se
Ma
gle
ho
lm (
4)
Ma
gle
mo
se
gå
rd (
4)
Ma
gle
mo
se
gå
rds
Væ
ng
e (
4)
Sta
tio
ns
ve
j 1
9 (
4)
Væ
ng
et
No
rd (
4)
NISP 44461 2592 39067 2738 9332 10893 2669 650 12784 6324 4547 734
Gadidae 86% 55% 66% 58% 70% 51% 15% 69% 48% 23% 79% 44%
Pleuronectidae 2% 35% 25% 38% 18% 39% 70% 5% 46% 71% 46%
Anguillidae 9% 1% 1% 3% 2% 1% 3% P 2% 2% P 3%
Cyprinidae P P P 1% P P 1% 2% P
Trachinidae P P P P P
Belonidae P 4% 2% 1% 7% 1% 10% P 1% P
Clupeidae P P P P P P P P P P 4% P
Scombridae 1% 1% 1% P 1% 4% 1% 1% P P P P
Cottidae 1% 2% 1% P P P P P P
Gasterosteidae P P P
Squalidae P 1% 2% P 1% 3% P 22% P 1% P 4%
Zoarcidae P P P
Triglidae P P P P P P
Percidae P P P P P
Esocidae P P 1% P 1% P P 1% 1%
Salmonidae P P P P P P P P
Sparidae P
Scophthalmidae P P P P P P P* 1%
Carangidae
Gobiidae P
Moronidae
Callionymidae P
Ammodytidae
Table 69: Percentage of fish by family for sites on Zealand (P = rounds to 0%).
(4) Data from Enghoff 1994a and only published in summary form. Note that Stationsvej
19 has 15% indeterminate flatfish not shown here (it seems unlikely that all 15% are
Scophthalmidae, based on the results from all other sites in Denmark that are
dominated by Pleuronectidae). (5) Data from Larsen 2005.
Figure 78: Relative abundance of Gadidae (larger fish) versus mesh-size of screen used during recovery. (Ertebølle is plotted at 0.5 mm mesh, the smallest size used for sieving the N-column, although other areas that were recognized during excavation as being rich in fish bone were taken as bulk samples and hand-sorted under a stereo-microscope in the laboratory) (Enghoff 1986:63). Additionally, a screen size of 1.5 mm is plotted for Lystrup Enge, which is only described as being excavated with “fine-mesh sieving,” (Enghoff 1994a:69).
Figure 79: Relative abundance of Gadidae versus mesh-size of screen used during recovery substituting the screen-test results (with an effective 1 mm mesh size) for the regular assemblages from Asnæs Havnemark and Dragsholm.
Documenting the differences in the fisheries of the eastern and western
areas of Denmark by noting which species dominate the individual assemblages is a
step forward, but a more quantitative measure of difference is available with the
Shannon index of heterogeneity. Because of the data that are required for calculating
the index (precise relative abundances) and the choice to omit two sites with very small
assemblages (Havnø and Jesholm I), not all sites were included in this analysis
(although values were calculated for all sites with any published relative abundance
information and these are presented in section 6.2 below with the reservation that they
are only approximations because of the limitations of the data). The sites that were used
are listed in Table 70, along with their NISP and NTAXA (at the family level).
Bjø
rns
ho
lm
Ert
eb
ølle
Ne
de
rst
I
No
rsm
ind
e
Sm
ak
ke
rup
Hu
se
As
næ
s H
av
ne
ma
rk
As
næ
s S
cre
en
-te
st
Dra
gs
ho
lm
Dra
gs
ho
lm S
cre
en
-te
st
Få
rev
ejle
Bø
ge
bje
rg
Lo
llik
hu
se
NISP 11490 9462 13779 9158 9332 44461 3299 39067 1435 2738 2592 2669
NTAXA 24 17 11 16 11 15 14 16 13 12 10 8
Table 70: NISP and NTAXA for selected sites.
Figure 80: NTAXA versus (Log) NISP for selected sites.
Plotting NTAXA versus the logarithmically transformed NISP values shows there is not
a statistically significant correlation between the two (N = 12, r = 0.43704, P = 0.1554),
so use of the Shannon index is warranted (Figure 80). Figure 81 shows the Shannon
index values by site arranged from highest to lowest, with the western sites in blue and
the eastern sites in red.
Figure 81: Plot of Shannon index values. (Western sites are blue and eastern sites are
red.)
It is again necessary to test to see whether differences in the index values are driven by
assemblage size and this is done in Figure 82. It does not appear that the Shannon
index values are significantly correlated with (Log) NISP (N = 12, r = 0.26571, P =
0.4039), so the differences can be attributed to causes other than assemblage size.
Figure 82: Plot of Shannon index values versus (Log) NISP.
The association of higher index values with the western sites and lower
values with eastern ones is fairly distinct. The higher value for the Dragsholm screen-
test assemblage may be attributable to the fact that most of the samples come from
Layer 7B – which had more diverse and evenly distributed results than the other levels.
It is fair to say that the screen-test results are not representative of the site as a whole.
The Asnæs Havnemark screen-test samples have the second highest Shannon index of
the eastern sites, although the value is reasonably close to the rest of this group. The
NTAXA values for the western sites are similar or only slightly higher than the eastern
sites, but when relative abundances are factored in the eastern sites show less
heterogeneity. Greater heterogeneity is linked with a broader subsistence base, so the
results from calculating the Shannon index support the earlier impression of a
generalized fishing strategy in western Denmark and a more specialized strategy in
eastern Denmark.
One further difference between the eastern and western coastal sites
concerns the water salinity requirements of the fish that were caught. In the East,
saltwater species are by far the dominant portion of the assemblages (note that some
saltwater fish can tolerate varying degrees of brackishness such as the waters of
estuaries); however most of the eastern assemblages have a small freshwater
component (especially Esocidae and Cyprinidae) as well. In western Denmark this is
not the case: two sites on the Limfjord (Bjørnsholm and Ertebølle) have significant
amounts of Cyprinidae and lesser quantities of Percidae and Esocidae, but freshwater
species are otherwise almost completely absent from the western assemblages.
Diadromous fish tell a somewhat different story. Anguillidae are present in the
assemblage of every Danish site investigated so far, but with the exception of Asnæs
Havnemark, they are at most only a few percent of the total NISP for the eastern sites.
In contrast, on western sites, with the exception of Lystrup Enge, Anguillidae are never
less than 8% of the total. At Bjørnsholm and Havnø they are well over half of the total
identified fish bones. The significance of these observations is not immediately obvious,
but it is curious that the sites in the West with a broader diet breadth seem to have been
less likely to have taken advantage of freshwater fishes. It must be borne in mind that
on the whole, freshwater fishes were of only minor significance at the coastally located
settlements (with two exceptions). At inland locations they were the dominant type of
fish of course, but even here saltwater species could be found (i.e., Ringkloster)
(Enghoff 1994b). At a rough approximation, perhaps 5 % of the total number of fish
bones identified from all Ertebølle sites in Denmark came from exclusively freshwater
species (mostly from just two sites: Åkonge and Ertebølle). With the exception of the
Åmose on Zealand and the vicinity of the Limfjord in northern Jutland, freshwater lakes
and rivers do not seem to have been a focus of the Ertebølle fishery.
6. Discussion
Discovering the species, elements and size of the specimens that are
present in archaeological assemblages is an engaging and rewarding endeavor.
Analyses that inform about the ways in which these data are biased by taphonomic and
other factors also make important contributions to our knowledge. In the results sections
it was shown that fish bone assemblages differ between eastern and western Denmark,
and that at some sites, there is variation within an assemblage that most likely indicates
change through time. Ultimately, however, archaeologists are interested in how material
evidence reveals past human behavior, and for that we must turn to the specific
characteristics of the fish assemblages that can be used to generate cultural
interpretations.
6.1 The individual sites
Asnæs Havnemark
Excavations at Asnæs Havnemark revealed a site that was incredibly rich in
fish bones; so much so that they were only sampled from some of the units. Even so,
ca. 3.2 kg of fish bone material was recovered, all of which has been examined. The
total of 47,760 identified specimens makes it the largest Ertebølle assemblage analyzed
so far. Seventeen families of fish were identified, containing a minimum of 22 different
types of fish. Gadidae were represented by Gadus morhua, Melanogrammus
aeglefinus, Pollachius sp. and Merlangius merlangus, with Gadus morhua (cod) being
most common (at 75.1 %, with 5.1 % Merlangius merlangus, 1.0 % Pollachius sp., 0.4
% Melanogrammus aeglefinus and 18.4 % unspecified gadid – based on identifications
of 899 otoliths). Flatfish were represented by Platichthys flesus (although Pleuronectes
platessa and Limanda limanda may also be present) and Psetta maxima/Scophthalmus
rhombus. Clupeidae remains consisted of both Clupea harengus and Alosa sp.
(although only 13 Alosa vertebrae were identified). Preservation of the fish bones was
generally good, with over 95% of the identified vertebrae being more than half complete.
All of the skeletal elements seemed to have been discarded in the same location (ca.
14% of the NISP is non-vertebra), even though not all elements were recovered and
identified in equal proportions.
Gadidae dominate the assemblage with 86% of the total NISP, followed by
Anguillidae at 9%. Screen tests experiments on the effect of using smaller mesh-size
(NISP = 3299) increased the relative abundance of Anguillidae (to 18.2%) and some
other species, but Gadidae remained the dominant fish (68.1%) Freshwater fish are
very rare (only 8 Cyprinidae vertebrae), but diadromous fish include eel, shad, and
trout/salmon. These results are very much in accord with the site’s location far out on
the Asnæs peninsula with no significant bodies of freshwater in the vicinity. The rocky,
exposed shoreline near the site; dominance of Gadidae (including large individuals of
Gadus morhua and Melanogrammus aeglefinus); and recovery of numerous fishhooks
and preforms suggest that angling (probably offshore in boats) played a major role in
the fishery. This interpretation is supported by the very few Trachinidae specimens in
the assemblage (0.1 %), a fish that is often used as a marker of fishing with stationary
structures (see section 6.2 below). The presence of Callionymidae is of note as this fish
has only been identified in one other Ertebølle assemblage (Norsminde).
The approximately 18 kg of other animal bones from the site have not yet
been analyzed, but seal, red deer, roe deer, wild boar, dog, beaver, raptor and swan
have already been recognized by the excavators. It would be a mistake to assess the
relative importance of fish versus other animals based on the bone weights at this site,
as fish bones were only collected from some squares while all other animal bones were
retained during excavation. The fish bones represent a minimum of hundreds of
individuals, demonstrating that they were an important part of the diet.
Determination of the seasons of occupation for Asnæs Havnemark will
require completion of an analysis of the other faunal remains, but the fish offer some
initial insights (see more on this topic below in section 6.3). Summer occupation is
suggested by the presence of Scombridae and Belonidae, although both are rare (ca.
1% and 0.1%). The predominance of Gadidae in the assemblage (including large
individuals of Gadus morhua and Melanogrammus aeglefinus) may be evidence of a
winter fishery. Seal, swan, and deer bones support a fall/winter occupation, as this is
when these animals are most profitably hunted (Rowley-Conwy 1984).
Dragsholm
Excavations at Dragsholm produced an enormous quantity of fish bones
(ca. 12.2 kg), of which 40,502 specimens have been identified so far. All of the fish
remains from Trench 11 have been analyzed, along with samples from Trenches 3, 4
and 5. To date, eighteen fish families have been recognized in the material, including at
least 25 different fishes. Gadidae are represented by Gadus morhua, Pollachius sp.,
Merlangius merlangus, with Gadus morhua being the most common (70.1 %, with
Pollachius sp. at 1.5 %, Merlangius merlangus at 0.3 % and 27.3 % unspecified gadid -
based on the identification of 2152 otoliths). Many different flatfishes were recognized,
including: Platichthys flesus, Limanda limanda, Pleuronectes platessa and Psetta
maxima. Clupeidae included both Clupea harengus and Alosa sp., while Salmonidae
were represented by Coregonus sp. and Salmo sp. Preservation of the fish bones was
variable, ranging from very good to somewhat poor. Over 88% of the identified
vertebrae were more than half complete, but the relatively low ratio of vertebra identified
versus the number that would be expected based on the estimated minimum number of
fish suggests that more bones are ‘missing’ from this assemblage than at the other
sites. Almost 16.9% of the total NISP consists of non-vertebra elements, which supports
the conclusion that all fish remains were discarded in the same locations (even if not all
elements were equally affected by taphonomic factors).
Gadidae dominate the assemblage at 66.5 %, followed by Pleuronectidae
at 24.9 % and all other species at 8.6%, although this varies somewhat between levels.
Level 7B had the highest proportion of Pleuronectidae (36.1 %) and ‘other’ species
(10.2 %). Screening experiments testing the effect of smaller mesh size (NISP = 1435)
increased the proportion of ‘other’ species to 31.1% (especially Anguillidae at 16.0 %
and Clupeidae at 6.7 %), but the samples were mostly taken from Level 7B. Even with
smaller mesh-size screens, Gadidae remain the dominant type of fish at the site.
Freshwater fish (including Percidae, Esocidae and Cyprinidae) are very rare, evidenced
by only 11 specimens. Diadromous fish are also present (Anguillidae and Salmonidae)
but comprise just 0.9 % of the total. The location of Dragsholm on a narrow waterway
connecting the sheltered waters of the Lammefjord with the Kattegat provided
opportunities for fishing in a variety of environments. The many different types of fish in
the assemblage support exploitation of a variety of locations, although the dominance of
Gadidae (including individuals up to 64 cm in length) suggests that much of the fishing
may have been conducted out in the deeper waters of the Kattegat. The fish hooks
recovered from the site (one of which was 5 cm long) were likely part of this fishery.
Spear fishing in the shallow waters of the fjord would have been a productive way to get
flatfish and traps set in the passageway between the fjord and open sea would have
captured many of the migratory fishes. The relative scarcity of freshwater fish implies
there were no large bodies of fresh water in the vicinity; or if there were, they were not
important fishing locations.
Analysis of the 17.6 kg of other animal remains from Dragsholm is not
complete, but the excavators’ recognition of roe deer, red deer, wild pig, dog,
unspecified bird, and unspecified small and medium mammals shows a broad-based
hunting strategy. Although an impressive amount of mammal and bird bone was
recovered, when compared with the weight of fish bones it would seem to indicate that
fishing was a very important part of the subsistence regime. Based solely on the
number of otoliths from Trench 11, over a thousand Gadidae contributed to the deposits
at the site.
The presence of Scombridae and Belonidae specimens in reasonable
quantities (1.2 and 2.2% respectively) gives firm proof of summer occupations of the
site. Conversely, the dominance of Gadidae (including several large individuals) is
consistent with fishing in the cooler months of the year. The cervids and other mammals
may be further support for fall/winter occupations, although definitive statements
involving mammal and bird remains awaits completion of their analysis. In addition to
the faunal evidence, the wide range of tools and other material evidence recovered from
the site is consistent with a base camp that was occupied year-round.
Bøgebjerg
The site of Bøgebjerg lies approximately 100 meters north of Dragsholm
and offered many of the same environmental conditions to its inhabitants, although flint
typology and the absence of ceramics suggest that it may have been occupied slightly
earlier. It was not as rich in finds as Dragsholm (only 265 g of fish bones and ca. 550 g
of other animal bones), but provides an interesting point of comparison. All of the fish
remains have been analyzed and the 2,592 identified specimens document 10 families
of fish. Preservation of the fish bones was generally good. Non-vertebra elements are
not well represented at Bøgebjerg (only 4.8 % of the total NISP), possibly suggesting
some degree of off-site processing. Levels 1 and 3 have an unusually high proportion of
the first through third vertebra of Gadidae (52.9 and 45.3 % of the total Gadidae
vertebrae respectively), but the small sample size discourages attaching great
significance to this observation. Overall, Gadidae dominate the assemblage with 55.4 %
of the total, followed by Pleuronectidae at 35.4 %. As at Dragsholm, these percentages
vary somewhat by layer. The presence of Sparidae (one specimen) is notable, as this
family of fishes is generally found in more southerly waters today.
The ratio of fish bone to other animal bone (by weight) implies that fishing
was an important part of subsistence at the site, but both assemblages are fairly small.
No detailed information on the non-fish animal bones is available. Seasonality
information from the fish remains is similar to that noted above, with Belonidae (4.3 %)
and Scombridae (0.8 %) demonstrating spring/summer occupation while the dominance
of Gadidae (including large individuals up to 52 cm in length) suggests that fishing was
also conducted in the fall/winter.
Fårevejle
Only a few kilometers to the north of Dragsholm and Bøgebjerg, also on the
Lammefjord, lies the shell midden site of Fårevejle. Despite the presence of great
quantities of mollusk shells, other evidence of human activities was somewhat sparse in
the midden. Approximately 228 g of fish bones were recovered during excavation, all of
which have been examined. The 2,783 identified specimens encompass 12 families and
a minimum of 14 different types of fish. Gadidae are represented by Gadus morhua and
Pollachius sp.; flatfish by Psetta maxima/Scophthalmus rhombus and Platichthys flesus.
Preservation of the fish bones was generally quite good and the proportion (15.4 %) and
types of non-vertebra elements are in line with what would be expected if complete
skeletons were deposited in the midden. Again, Gadidae dominate the assemblage at
57.7 % followed by Pleuronectidae at 38.1 %, varying somewhat by layer. The presence
of a few Cyprinidae and Esocidae vertebrae indicates either that a body of freshwater
was nearby or the fjord had very low salinity in this location. The size of Gadidae at the
site is rather large (mean = 46.7 cm, with the length of 7 of the 25 individuals estimated
from otolith measurements being more than 50 cm) which is best explained by an
emphasis on hook-and-line fishing.
The ca. 1.4 kg of other animal bone recovered from the site is still awaiting
analysis, but the excavators’ noted roe deer, red deer, wild pig and unspecified bird
remains. Comparing the weights of fish and other animal bones implies that fishing was
not as important as other subsistence activities at this site; a point that is perhaps made
obvious by the extensive evidence for gathering shellfish. Growth-ring analysis of shells
from other middens has shown that gathering mollusks was primarily done during the
late winter or spring during the Ertebølle period (Milner 2002). Assuming this was also
the case at Fårevejle and adding the evidence for Gadidae fishing (with individuals up to
66 cm in length) and hunting of cervids, cool season occupation of the site is indicated.
Evidence for summer occupation is scarcer, as both Scombridae and Belonidae are
rare in the assemblage (0.1 and 0.6 % respectively). Fårevejle may be an example of a
resource extraction locale that was seasonally visited from other base camps on the
Lammefjord.
Lollikhuse
Further east on the island of Zealand, on the shores of the Roskilde fjord, is
the shell midden site of Lollikhuse. Fish bone samples from earlier phases of excavation
were analyzed for this project, but subsequent excavation has produced an unknown
quantity of fish material that awaits examination. From the part of the assemblage
analyzed, 2,668 identified specimens indicate the presence of 8 families of fish. One
family (Squalidae) is recognized only on the basis of three dorsal spines; given the lack
of other skeletal elements and the fact that Squalidae spines have been identified as
tools (Noe-Nygaard 1971), it may not be part of the fishery at this site. Preservation of
the bones was only fair, and many specimens were unidentifiable due to a hard, thick
encrustation of matrix. Only 3.6% of the identified specimens were non-vertebrae, which
is the lowest proportion yet observed. Pleuronectidae dominate the assemblage at
70.4%, followed by Gadidae at 15.1 %. No freshwater fish were identified, but migratory
fish are present (Anguillidae). It is surprising that eel represent only 3 % of the
assemblage, as this was the major fishery in the Roskilde fjord in historic times
(Drechsel 1890). The proportion of Belonidae (9.9 %) is the highest recorded from any
Ertebølle site and demonstrates an emphasis on fishing in the spring and early summer.
The presence of Scombridae supports this observation, although they are present in
much smaller quantities (0.9 %). Neither Gadidae size estimates nor information on the
rest of the faunal material is available, precluding inferences about other seasons of
occupation.
Havnø
Moving to the Jutland peninsula, a small assemblage was examined from
the shell midden site of Havnø on the Mariager fjord. With only 330 identified
specimens, strong statements about the nature of the fishery conducted by the site’s
inhabitants are probably not warranted, but the diverse nature of the assemblage (9
families present) is remarkable considering its size. Anguillidae were the most common
fish (at 72.7 %) and combined with the Salmonidae specimens (3.3%) demonstrate that
diadromous fish were important. Spring or summer occupation of the site is indicated by
the presence of 11 Belonidae specimens, although other seasons of occupation cannot
be excluded. The Havnø excavations have produced a large mammal and bird
assemblage that awaits analysis, but no information is yet available.
Nederst
Three different shell-heaps are present at this site in the middle of the
Djursland peninsula in central Jutland, located on the former Kolind fjord. Samples from
skaldynge II were identified by Inge B. Enghoff and given summary publication (1994a).
From this area of the site 6,476 specimens were identified, with Anguillidae (38 %),
Gadidae (23 %), Pleuronectidae (21 %) and Clupeidae (14%) being the most common
fishes. The relatively high percentage of herring and the absence of freshwater species
were notable features of the assemblage (Enghoff 1994:82).
Samples from skaldynge I were analyzed for this project, resulting in the
identification of a further 13,779 specimens. Preservation of the fish bones was
generally good, with over 93% of the identified vertebrae being more than half complete.
Both the proportion of non-vertebra elements (10.8 % of the total NISP) and types of
elements identified support the interpretation that complete skeletons were deposited in
the midden. Many of the fish bones from Nederst were burned (6.1 % of the identified
vertebrae), although the majority of the burned bones were concentrated in one square
(201 East 297 North). Of the ten families of fish from skaldynge I, Pleuronectidae (43.3
%), Anguillidae (19.3 %), Trachinidae (16.8 %) and Gadidae (12.4 %) were the most
important. The lack of a single dominant type of fish and the high relative abundance of
multiple fishes suggests a generalized fishing strategy; perhaps emphasizing the use of
stationary fishing structures that were unselective in their catch. The large number of
Trachinidae bones (the highest proportion of any Ertebølle assemblage) is also
evidence for the use of fish fences and traps. As in skaldynge II, no freshwater fishes
were identified, although diadromous fishes (Anguillidae and Salmonidae) are present.
Of special note is the Pleuronectidae individual estimated to have been 52 cm long; the
largest Mesolithic example of this fish to date.
Numerous fish remains from Nederst have not yet been examined and the
other classes of faunal material have received little analysis. Comprehensive publication
of the site is still in process. Because of these limitations it is difficult to discuss
seasonality or site function. Scombridae are present in the material but scarce (0.2%)
and there are no specimens from Belonidae. Gadidae are a fairly minor component of
the assemblage and consist mostly of small individuals (the largest is 45 cm). Summer
may have been the primary season of occupation and/or fishing activity, but this is by no
means definitive.
Jesholm I
Excavations at Jesholm I on the northern coast of the Djursland peninsula
produced surprisingly few fish bones considering the presence of numerous sharpened
or otherwise worked pieces of wood that are interpreted as the remains of fishing
structures. Other animal bones and flint artifacts were recovered in some quantity,
indicating that the excavation trenches did sample outcast deposits, but despite water-
screening of numerous samples (with 1.5 mm mesh-size screens) only a handful of fish
bones were recovered. The 38 identified specimens include elements from 8 families; a
level of diversity in a small assemblage that is as impressive as that at Havnø. No
Scombridae or Belonidae are present, but with so few identified fish bones statements
about seasonality of occupation are not justified.
6.2 Fishing technology
One of the first questions that arises with any discussion of subsistence
resources is how they were obtained. For the Ertebølle period, there is solid
archaeological evidence for fishing by means of traps, nets, spears/leisters and hooks
(e.g., Andersen 1995, Pedersen 1995). Because almost all of the components of fishing
gear were made from organic materials, they are only occasionally preserved. This
means that while we have convincing proof that all of these methods were practiced it is
not possible to judge which techniques were preeminent based on the scattered
remains that have been recovered. Instead, clues to the fishing methods employed
come from the fish assemblages that were captured by them. It has become accepted
wisdom that, “the main fishing tool used by the Ertebølle fishermen was a stationary,
self-fishing trap, which was left in place near the coast for a period of at least one night,”
based on the species richness of fish assemblages, the behaviors of these species and
the size of the fish (Enghoff 1994a:83-84, emphasis in the original). It is worth
investigating each of these supporting lines of evidence in turn.
The relatively high species richness of Ertebølle assemblages has been
interpreted as meaning that they represent, “an uncritical sample of whatever fish was
present in the local coastal waters,” (Enghoff 1994a:83, emphasis in original), and thus
reflect the use of untended traps. While intuitively appealing in some regards, this
reasoning relies upon a few untested assumptions. The first of these is that the number
of species found in an assemblage is a significant portion of the local fish fauna.
Unfortunately, we have only two means of knowing what the local fauna would have
been: analogy (with modern or historic data obtained under different environmental
conditions than those of the Late Atlantic period and also potentially altered by heavy
commercial fishing activities) or from sub-fossil fish remains (which, in this area and this
period, come from archaeological deposits). A second reservation (already raised
during the introduction of NTAXA) is that the presence or absence of a particular type of
fish carries the same amount of information regardless of how many specimens are
actually present. Table 71 shows the number of taxa (at the family level) present at
many Ertebølle sites. The first row includes every taxon present at the site, while the
second row includes only those that are present in quantities greater than 1%.
Jutland NW Zealand NE Zealand
Bjø
rns
ho
lm
Ert
eb
ølle
Ha
vn
ø
Je
sh
olm
I
Ly
str
up
En
ge
Ne
de
rst
I
Ne
de
rst
II
No
rsm
ind
e
Yd
erh
ed
e
Øs
ten
kæ
r
As
næ
s H
av
ne
ma
rk
Bø
ge
bje
rg
Dra
gs
ho
lm
Få
rev
ejle
Sm
ak
ke
rup
Hu
se
He
nri
ks
ho
lm-B
Lo
llik
hu
se
Ma
gle
ho
lm
Ma
gle
mo
se
gå
rd
Ma
gle
mo
se
gå
rds
Væ
ng
e
Sta
tio
ns
ve
j 1
9
Væ
ng
et
No
rd
24 17 9 8 15 10 11 16 13 4 15 10 16 12 11 17 8 10 16 15 11 11
6 4 7 8 2 6 6 4 4 4 3 4 4 3 4 4 4 3 3 4 3 4 Table 71: NTAXA for Ertebølle sites, first row includes all taxa and the second only
those that are present greater than 1 %. (Note that Østenkær has NISP 11 and Jesholm
I NISP 38, so all taxa are greater than 1 %.)
It is clear from the data in Table 71 that there are many types of fish at most
of the sites, but it is equally clear that many of them are only present in trace amounts.
Some fishes are present with just one specimen out of the thousands identified for that
site (e.g., Callionymidae at Asnæs Havnemark and Sparidae at Bøgebjerg). Relying on
NTAXA data as the basis for behavioral interpretations without consideration of relative
and absolute abundances is likely to result in misleading conclusions.
The role of fish behaviors as support for concluding that fish traps were the
preferred method of capture in the Ertebølle fishery stems from two observations: all but
one of the fish species in the assemblages are found at least occasionally in coastal
waters and greater weever (Trachinus draco, family Trachinidae) occurs on many of the
sites’ species lists. While agreeing that most of the species discussed spend some or all
of their lives in coastal waters, the relevance of this to discussions of method of capture
is unclear. It does rule out an exclusive deep-sea fishery. The Trachinidae evidence is
more intriguing and warrants further scrutiny. The reasoning behind using Trachinidae
as proof of fishing by self-fishing traps is that, “the greater weever lies buried in the
bottom sediment during the day and swims around during evening and particularly
during night,” (Enghoff 1994a:84). However, more recent fisheries biology research has
shown that, “for lesser weever [Echiichthys vipera] in the North Sea…the diel rhythm in
food intake, with high ingestion from midnight until noon, and low ingestion in the
afternoon and evening, appears to be similar among the two species [Echiichthys vipera
and Trachinus draco ],” (Bagge 2004:942). Trachinidae may be predominantly a
nighttime feeder, but they also feed (and are vulnerable to capture) at other times during
the day. Because of this, the presence of a few Trachinidae bones in an assemblage
cannot be taken as evidence for a nocturnal fishery. Instead of relying on mere
presence/absence data of Trachinidae, if relative abundances are considered a more
nuanced picture is revealed (see Table 72).
Jutland NW Zealand NE Zealand
Bjø
rns
ho
lm
Ert
eb
ølle
Ha
vn
ø
Je
sh
olm
I
Ly
str
up
En
ge
Ne
de
rst
I
Ne
de
rst
II
No
rsm
ind
e
Yd
erh
ed
e
Øs
ten
kæ
r
As
næ
s H
av
ne
ma
rk
Bø
ge
bje
rg
Dra
gs
ho
lm
Få
rev
ejle
Sm
ak
ke
rup
Hu
se
He
nri
ks
ho
lm-B
Lo
llik
hu
se
Ma
gle
ho
lm
Ma
gle
mo
se
gå
rd
Ma
gle
mo
se
gå
rds
Væ
ng
e
Sta
tio
ns
ve
j 1
9
Væ
ng
et
No
rd6% 5% 50% 17% 2% P 1% P P P P P
Table 72: Occurrence of Trachinidae - cited as evidence for the use of stationary fishing
structures.
First, note that Trachinidae are present in only 12 of 22 assemblages (55%), making
general statements about the Ertebølle fishery based on this one species suspect.
Using a ubiquity index to evaluate the six assemblages which have the requisite level of
detail available shows an even weaker basis for using the presence of Trachinidae to
characterize the overall fishery; with the exception of Nederst, they are present in only
about one third or less of the contexts at these sites (Figure 73). Using the presence of
mostly low numbers of Trachinidae bones in a few contexts at some sites as evidence
for an overall preference for trap fishing during the Ertebølle period is an unwarranted
generalization.
Site Total contexts Trachinidae contexts Ubiquity % Trachinidae vertebra Total vertebra % vertebra
Asnæs Havnemark 23 8 35% 33 38423 0,1%
Asnæs screen-test 14 3 21% 9 2651 0,3%
Bøgebjerg 21 6 29% 12 2468 0,5%
Dragsholm 59 19 32% 155 32468 0,5%
Dragsholm screen-test 13 3 23% 5 1206 0,4%
Fårevejle 72 10 14% 15 2317 0,6%
Lollikhuse 90 0 0% 0 2574 0,0%
Nederst 15 14 93% 2041 12291 16,6%
Table 73: Ubiquity of Trachinidae at six sites.
If instead of characterizing the Ertebølle fishery as a whole, the goal is to
describe individual site or regional fisheries, the Trachinidae evidence becomes more
convincing. Returning to the information in Table 72, Bjørnsholm, Havnø and Nederst
have considerable percentages of Trachinidae in their assemblages and might be good
candidates for fisheries that were heavily reliant on stationary fishing structures
(Jesholm I also has a high percentage of Trachinidae, but a total NISP of only 38).
These are precisely the assemblages that have the highest indices of heterogeneity (the
Shannon index for Havnø is 1.09, but it is a very small assemblage and this value may
not be reliable), an unsurprising result, given that fish traps are a mostly non-selective
method of fishing that catch a diverse array of fishes. The eastern sites, where Shannon
indices are lower, have few or no specimens of Trachinidae. Exactly as would be
expected, where fisheries are more specialized, the evidence for fish trap usage is
lowest. This is not to suggest that fish traps were not widely used during the Ertebølle
period, merely that they were not universally the most important means of procuring
fish. What is the evidence for the relative importance of the other methods of fishing?
The remains of fish spears or leisters are a frequent find at sites with
favorable conditions of preservation and may be even more common if the bone points
that are part of many tool inventories are a spear component as has been suggested
(Andersen 1995). The two styles of leister prongs found at Tybrind Vig (short for hard
substrates and long for soft substrates) are evidence for a sophisticated spear fishery
(Andersen 1985). Furthermore, it has been suggested that the clay hearths found in
some dugout canoes may have been for the purpose of maintaining fires to attract fish
at night, a practice that is well-known ethnographically (Rostlund 1952:295). Exactly
how the fish were captured after they approached the canoe is not known, but spearing
would certainly have been one option. This is in line with the ethnographic record which
shows that, “in traditional fisheries harpoons and leisters were generally used for
subsistence fishing only in conjunction with other techniques and gear, such as poisons,
lures, ground baits, weirs and barriers, which concentrate the fish,” (Pickard and Bonsall
2004:3, emphasis added). Anadromous and catadromous fishes (e.g., Salmonidae and
Anguillidae) are particularly vulnerable to spear fishing when they are concentrated in
rivers and streams. Marine fishes such as Pleuronectidae that occupy waters conducive
to spear fishing (e.g., shallow lagoons, fjords and littoral zones) during parts of the year
could also have been preferred prey for this method (Olson 2008:31, Olson and Walther
2007:9). Because significant quantities of a fish could be taken by spearing only at
specific times and locations depending on the behavior of the fish, heavy reliance on
spearing would produce a narrow diet-breadth (specialized fishery) unless it was
possible to target multiple fishes at different times during the year and the remains
ended up in the same deposits.
“Nets have been portrayed as the most efficient type of fishing gear and
their manufacture as evidence for a specialized fishing economy. The use of nets
requires skill, investment of time both in terms of manufacture and maintenance, and
considerable raw materials,” (Pickard and Bonsall 2004:3). There are many types of
nets, and they may be used both actively (e.g., seine nets, dip nets) and passively (e.g.,
pound nets, gill nets). Depending on the type of net, where and when it is employed, net
fishing can be either selective or non-selective for the fishes it catches. Generally, net
fishing catches a broad variety of fishes, with the only selection occurring in the size of
the fish caught based on the mesh-size of the net. The evidence for Ertebølle net-
fishing in Denmark consists only of net-weights and net-floats; without more information
about what types of nets were used detailed discussion of this fishery is not possible.
The final fishing technique for which there is archaeological evidence is
hook-and-line fishing. Although fishhooks can be employed passively when they are
employed en masse on set-lines, the absence of barbs on most or all of the Ertebølle
examples argues against the use of this technique as the fish could free themselves
before the set-line was retrieved. The preferred method of using the fishhooks must
have been active angling by the fishermen. Use of fishhooks is a selective fishing
method, with the fishes caught being largely determined by hook size, bait and fishing
location (and depth). Many fishes can be caught with hooks on at least some occasions,
but the method is more favorable for certain fishes, especially Gadidae. It has been
observed that, “at Scandinavian sites there is a clear co-occurrence of gadidae (cod,
ling, saithe, and related species) and bone fishhooks,” (Pickard 2002, cited in Pickard
and Bonsall 2004). The explanation of this co-occurrence is that, “for cod, which
seasonally stay in coastal waters, but not often in the immediate vicinity of the shore,
methods such as hook and line fishing would be more efficient,” (Olson et al.
2008:2819-2820). Even until the mid-20th century, hand-lining with baited hooks was a
preferred method for catching codfish (Kurlansky 1997). Cod are a gregarious fish, so
when a school is found many individuals can be captured without exhausting the fishing
location. Because they are voracious feeders that readily take the hook and congregate
in large numbers, Gadidae hook-and-line fishing in favorable locations offered the
potential for enormous returns.
Returning to diet breadth modeling, it will be remembered that greater
investment in fishing technology will lower the pursuit curve, thus expanding the number
of species in the diet and creating a more generalized fishing strategy. Stationary fishing
structures require the highest investment of resources. Fishes that were likely targeted
by these structures were eel, cyprinids (perhaps as by-catch in the eel fishery), and
Trachinidae, although many other fishes could also be taken (Enghoff 1986, 1994a).
Nets were another expensive technology, but without better information about the types
of nets that were used it is difficult to specify what they targeted. To the extent that they
capture all fish in the area where they are employed (that are larger than the net mesh-
size), they represent an unselective fishing technique. Spears require relatively little
investment and are selective in the fish they capture. Flatfish may have been
particularly targeted by spearfishing (Olson and Walther 2007). Hook-and-line fishing is
similarly inexpensive to employ and selective in its application. Gadidae and Cottidae
are fish that are especially likely to have been taken on fishhooks (Enghoff 1994a:84,
Pickard and Bonsall 2004). Table 74 presents the Shannon index values for the various
sites along with the most common fish in the assemblage and the percentage of
Trachinidae. The sites in italics are only published in summary form (with relative
abundances rounded to the nearest integer), so the Shannon index values should be
considered approximate. Higher Shannon index values indicate a more generalized
fishery. Trachinidae values are included because this fish is often cited as evidence for
the use of stationary fishing structures. The greater the abundance of Trachinidae in the
assemblage, the more reliance on stationary structures in the fishery can be inferred.
Examining the table, it is clear that in the lower part of the chart (where lower Shannon
index values indicate a more specialized fishery) Gadidae and Pleuronectidae are the
most common fishes. This agrees with the expectation that these fish are most often
taken with fishhooks and spears: low investment technologies. The scarcity of
Trachinidae specimens in these assemblages also argues against a strong reliance on
stationary fishing structures. Moving up the table into the more generalized fisheries, the
most common type of fish shifts away from Gadidae and Pleuronectidae to eel,
Cyprinidae and Trachinidae; the species that are targeted by stationary fishing
structures. The increasing abundance of Trachinidae in the assemblages supports the
importance of stationary structures in the fishery. With the exception of Lystrup Enge
(where a specialized fishery focused on Gadidae), the sites on Jutland reflect a strategy
of high investment in unselective fishing technology coinciding with a wide diet breadth.
On Zealand (and Bornholm), less investment in capture technology was made, but the
fisheries were more selective. This resulted in a narrower diet breadth as the fishers
focused on taking Gadidae, and secondarily Pleuronectidae. The fact that Gadidae are
almost always the most common fish when diet breadth is narrow is a striking result. It
strongly suggests that cod (and other members of the family) were the highest ranked
resource in the fish category and other types of fish were only targeted when Gadidae
were not available in sufficient numbers. In fact, at the five sites with the most
generalized fishing strategies Gadidae are the second most common species at only
one site (Nederst skaldynge II where they are 23% of the total), and are otherwise
ranked third or fourth in abundance (maximum 12% of the total NISP). Further evidence
comes from other lands bordering the North and Baltic seas where (excepting
assemblages consisting of mostly freshwater species) Gadidae are often the most
abundant fish (see section 2.2.7). The primacy of codfish only fails in Brittany and areas
to the south. The southern distribution limit of cod today is in the middle of the Bay of
Biscay; as they cannot tolerate waters that are too warm (Marine Species Identification
Portal, Muus and Dahlstrøm 1964). With the warmer temperatures of the Atlantic period
climatic optimum, it is easy to imagine this boundary being somewhat farther north,
meaning cod were simply not available at the southern sites.
Lowering the pursuit curve through better capture technology is not the only
path to a narrow diet breadth; it can also result from high search costs. Since there is no
evidence that canoes were better or more common in eastern Denmark, differences in
transportation technology did not create the difference in diet breadth. Environmental
conditions could also have affected the search curve. If, for example, fish were more
abundant or easier to find in eastern Denmark the search curve would be lower and diet
breadth narrower. In regards to Gadidae, this may in fact have been the case. In recent
times, the highest commercial catches of cod and their spawning grounds are located in
the eastern and southern parts of the Kattegat (Vitale et al. 2008). Furthermore,
research has shown that cod prefer rough (rocky or gravelly) bottoms (Wieland et al.
2009), meaning the sandier western parts of the Kattegat were less desirable. Ertebølle
fishermen in western Denmark may not have had the luxury of specializing in fishing for
Gadidae and so turned to other fishes to meet their needs.
Shannon Common Trachinidae Region
Jesholm 1,56 Trachinidae 50% Jutland
Nederst I 1,52 Flatfish 17% Jutland
Bjørnsholm 1,52 Eel 6% Jutland
Nederst II 1,51 Eel 2% Jutland
Yderhede 1,26 Flatfish 1% Jutland
Norsminde 1,12 Flatfish <1% Jutland
Ertebølle 1,09 Cyprinid Jutland
Havnø 1,09 Eel 5% Jutland
Bøgebjerg 1,05 Gadidae <1% Zealand
Henriksholm 1,04 Gadidae <1% Zealand
Vænget Nord 1,04 Flatfish Zealand
Dragsholm 1,00 Gadidae <1% Zealand
Smakkerup 0,97 Gadidae Zealand
Lollikhuse 0,95 Flatfish Zealand
Fårevejle 0,89 Gadidae Zealand
Maglemosegård 0,88 Gadidae <1% Zealand
Magleholm 0,83 Gadidae Zealand
Maglemosegårds Vænge 0,78 Flatfish Zealand
Lystrup Enge 0,65 Gadidae Jutland
Stationsvej 19 0,65 Gadidae Zealand
Asnæs Havnemark 0,60 Gadidae <1% Zealand
Grisby 0,42 Gadidae Bornholm Table 74: Evaluating technology and specialization versus generalization.
6.3 Seasonality
Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov. Dec.
Cod
Mackerel
Eel
Small whales Small whales
Harp seal
Grey seal pups
Fur animals Fur animals
Land mammals
Swans Swans
Ducks Ducks
Hazel nuts
Acorns
Fruits
Plants
Cockles
Mussles
Oysters
Figure 83: Hypothesized seasonal resource availability (redone from Rowley-Conwy
1984).
Faunal studies and seasonality questions are inextricably linked for
Ertebølle research. The first reason is that faunal data provides much of the evidence
for what periods of the year sites where occupied (from the presence of migratory
animals, tooth eruption patterns, long-bone epiphysis fusion, growth rings in mollusk
shells, otolith growth rings and the hypothesized optimal timing of exploitation of
individual resources – see Figure 83) (Carter 2009, Enghoff 1994a, Milner 2002,
Rowley-Conwy 1984, 1993). The second is that understanding subsistence economy (at
least the animal-based part of it, which is what we have the most material evidence for
at Ertebølle sites) requires knowledge of when individual resources were procured. Fish
remains have provided crucial information for the first topic (e.g., Enghoff 1987, 1989,
1991, 2009, Larsen 2005), and as evidence about a major food source, are intimately
involved in the second.
Discerning the timing of site occupation provides information about the
nature of the site (e.g., resource extraction camp versus home base) and in aggregate
reveals much about the overall settlement pattern (degree of residential mobility). Fish
remains have contributed to site seasonality studies because of the presence of
migratory species such as mackerel and garfish (Scombridae and Belonidae) that are
present in Danish waters for only a part of the year and through growth ring analysis of
otoliths. Although somewhat equivocal, the optimal season of exploitation for some
types of fish can also contribute seasonality information.
Scombridae (in the form of Scomber scombrus) may remain present in
Danish waters during the winter months, but do so near the bottom in deep waters
where they remain largely inactive and inaccessible. In April-May they re-enter coastal
waters and resume feeding, spawn in June-July, and then retreat from coastal areas in
August-September in preparation for another winter’s dormancy or migration (Muus and
Dahlstrøm 1964:140). Because they are available only from April until September (with
Mesolithic technology), their presence in assemblages proves that fishing took place
during these months. Table 75 shows that Scombridae are present at 17 out of the 22
sites. Four of the sites that do not have Scombridae have relatively few identified fish
remains (N = 523 or less). It is fair to say that almost all of the coastal Ertebølle sites
have evidence for summer activities.
Bjø
rns
ho
lm
Ert
eb
ølle
Ha
vn
ø
Je
sh
olm
I
Ly
str
up
En
ge
Ne
de
rst
I
Ne
de
rst
II
No
rsm
ind
e
Yd
erh
ed
e
Øs
ten
kæ
r
As
næ
s H
av
ne
ma
rk
Bø
ge
bje
rg
Dra
gs
ho
lm
Få
rev
ejle
Sm
ak
ke
rup
Hu
se
He
nri
ks
ho
lm-B
Lo
llik
hu
se
Ma
gle
ho
lm
Ma
gle
mo
se
gå
rd
Ma
gle
mo
se
gå
rds
Væ
ng
e
Sta
tio
ns
ve
j 1
9
Væ
ng
et
No
rd
2% P P P P 1% 1% 1% P 1% 4% 1% 1% P P P P
Table 75: Occurrence of Scombridae - seen as markers for warm season occupation at
Danish sites.
Where Scombridae are part of the fish assemblage, it can be stated that
they were used as fishing locations during the summer on at least one occasion.
Unfortunately, it is impossible to know much more than this from presence/absence
data. Looking at the relative abundance data from Table 75, it is clear that Scombridae
are usually only a minor component of the assemblages where they are present. Ordrup
Næs (introduced in section 4.2) represents one possible exception, with Scombridae
and Belonidae comprising the majority of the assemblage, although it was excavated in
the 1930s and there are only ca. 174 identified bones from the site (Rosenlund 1976).
Based on the low relative abundances of Scombridae at most sites, it is not possible to
make a strong argument that most assemblages are primarily the result of summer
fishing, although at least some fishing took place then.
Belonidae (in the form of Belone belone) are another type of fish that are
used as a marker of warm-season activity in the assemblages in which they are
present. Their migratory pattern is similar to Scombridae, entering coastal waters in
April-May, spawning in May-June and retreating from Danish waters again in the fall
(Muus and Dahlstrøm 1964:88). Though present at 14 of the 22 sites (see Table 76),
they are also generally a minor component of the assemblages (although Lollikhuse and
Smakkerup Huse are two sites where they are somewhat common). Again, summer
fishing activity is indicated at more than half of the sites, but it is not possible to say that
most of the fishing took place then, based on the relative abundances of these two
migratory species.
Bjø
rns
ho
lm
Ert
eb
ølle
Ha
vn
ø
Je
sh
olm
I
Ly
str
up
En
ge
Ne
de
rst
I
Ne
de
rst
II
No
rsm
ind
e
Yd
erh
ed
e
Øs
ten
kæ
r
As
næ
s H
av
ne
ma
rk
Bø
ge
bje
rg
Dra
gs
ho
lm
Få
rev
ejle
Sm
ak
ke
rup
Hu
se
He
nri
ks
ho
lm-B
Lo
llik
hu
se
Ma
gle
ho
lm
Ma
gle
mo
se
gå
rd
Ma
gle
mo
se
gå
rds
Væ
ng
e
Sta
tio
ns
ve
j 1
9
Væ
ng
et
No
rdP 1% 3% P P 4% 2% 1% 7% 1% 10% P 1% P
Table 76: Occurrence of Belonidae - seen as markers for warm season occupation at
Danish sites.
Another line of evidence for seasonality of catch comes from growth-ring
analysis of fish otoliths. Fish otoliths grow continually over the life of the fish by the
deposition of aragonite to the outer surfaces of the otolith. The appearance of the
deposits varies, with opaque bands forming during periods of rapid growth of the fish
and more translucent ones forming during slower growth periods. Because the period of
rapid growth occurs when water temperatures are warmer and food more abundant, a
cross-section of the otolith can reveal the season of capture (and also the age) of the
fish (Van Neer et al. 2004). To date, five Danish Mesolithic sites have been studied with
growth-ring analysis in an attempt to understand the seasonality of fishing. The analysis
was done by E. Steffensen at the Danish Institute for Fisheries and Marine Research
(Enghoff 1994a). Table 77 presents the data from 99 Gadidae otoliths from the site of
Nederst (skaldynge II), and Table 78 presents the results from 158 Gadidae and 58
Pleuronectidae otoliths from Norsminde. Additionally, 11 Gadidae otoliths were
analyzed from both Ertebølle and Bjørnsholm (with September as the inferred season of
capture) and 20 cod otoliths were analyzed from Maglemosegård (although described
as poorly preserved, traces of a summer zone are found on the edges of 13 of them)
(Enghoff 1994a:80-81).
Season: Winter/spring Summer Summer/autumn Autumn Winter
Cod 2 75 1 1 9
Saithe 8 3
Total 2 83 1 1 12
% 2% 84% 1% 1% 12% Table 77: Seasonality based on otolith growth rings for Nederst (based on data from
Enghoff 1994a:80).
Season: Winter/spring Spring Summer Autumn Winter
Cod 46 49 12 25
Saithe 6 13 4 3
Gadidae 52 62 16 28
% 33% 39% 10% 18%
Flounder 1 36 15 4
Plaice 2
Pleuro. 1 38 15 4
% 2% 66% 26% 7%
Total 1 52 100 31 32
% 0% 24% 46% 14% 15% Table 78: Seasonality based on otolith growth rings for Norsminde (based on data from
Enghoff 1994a:81).
Two questions are relevant with regards to the otolith seasonality data: how
reliable is the information provided and does it support the claim that most fishing took
place during summer? Concerning the reliability of otolith seasonality data, there is
good reason to question how accurate the results are. Along with the presentation of the
Danish data the author notes, “The transition from rapid summer growth to slow winter
growth does not happen simultaneously in all individuals of a fish population. In recent
cod from southern Kattegat and the Belts, Denmark, the hyaline winter zone may start
to form in September in some individuals, and the opaque summer zone may start to
form as early as February (E. Steffensen, personal communication),” (Enghoff
1994a:80). Furthermore, another study analyzing sections of recent Pleuronectidae
specimens from the North Sea found that, “during almost all months of the year opaque
and hyaline otoliths can be found within the plaice population, be it in different
frequencies,” (Van Neer et al. 2004:460). Similar results were found with haddock
otoliths. In addition to the season (month) of capture; place of capture and fish age also
affect the ratios of opaque to hyaline otoliths and there is even variation from year to
year in otherwise similar samples of modern specimens, meaning that in archaeological
contexts which are not clearly single deposition events with large samples and 100%
representation of one of the two types of outer band, the possibility for assigning definite
seasonality of capture is almost nonexistent (Van Neer et al. 2004:461-462). While
these results are discouraging, it should be emphasized that they concern optical
analysis of growth rings to determine season of capture. Recent work with stable
isotope signatures offers the potential for more satisfactory seasonality data, as the
incremental growth of the otoliths is a real and useful phenomenon – the difficulties lie in
unlocking the information stored in them. The six cod otoliths from Norway that were
studied using the new stable isotope technique to discern seasonality of capture all
displayed signals consistent with fish that were caught in winter or early spring
(Hufthammer et al. 2009). Given the many difficulties involved with optical growth ring
analysis, the probability that the archaeological assemblages are not single deposition
events, and the small size of three out of five samples, statements about the seasonality
of fishing that produced the assemblages are not definitive based on this evidence. As a
final note, it should be pointed out that even if the data were considered more reliable,
the two large otolith assemblages (from Nederst and Norsminde) would actually reveal
fishing occurring during much of the year (Tables 77 and 78). Again, stable isotope
analysis should produce more convincing data in the future, and to that end it is
fortuitous that over 2400 gadid otoliths are available from Dragsholm and another 900
from Asnæs Havnemark.
The presence of migratory species has been shown to provide only limited
seasonality information and the extant analyses of otolith growth rings are at least
somewhat inconclusive – how then, can seasonality information be obtained for these
Ertebølle assemblages? The answer lies in an examination of the non-migratory fish in
the assemblages and information about their behaviors and optimal seasons of
exploitation. Fishes such as Anguillidae, Pleuronectidae, Trachinidae and Cyprinidae
rest in a state of hibernation during the winter and are difficult to obtain (Bagge
2004:941, Olson 2008:32). Conversely, in southern Sweden, “cod was captured mainly
in fall and winter, and to a lesser extent during spring and summer” (Olson 2008:35).
There is some differentiation between adult and juvenile Gadidae given that, “small
cods occupy shallow waters at most seasons of the year. Larger cod are active in
deeper waters some distance away from the shore,” (Olson 2008:32) and, “adult cod
and haddock are known to enter sea lochs and frequent shingle or rocky shores at
various times of the year to feed, and are commonly angled from the shore in winter,”
(Pickard and Bonsall 2004:7). A look at the 19th century fishery data for Denmark lends
support to the warm season/cold season division of fish catches, although with the
caveat that fishing techniques were not the same in the Ertebølle period and the 19th
century AD (see Tables 79 and 80). As expected, plaice, sole, turbot, mackerel, garfish,
and herring were mostly caught in the period from April to September, while cod were
mostly caught from October to March. Eel are an interesting case in that the season of
capture relies on the fishing method, with spearing being mostly conducted during the
cooler months and the rest of the fishery taking place in the warm months (Drechsel
1890, Moustgaard 1987). Returning to the Ertebølle evidence, the eastern sites that are
characterized as more specialized fisheries have evidence for cool season fishing in the
predominance of Gadidae in many of the assemblages, including many adult
specimens. They also have evidence for warm season fishing from many of the other
fishes (e.g., Scombridae, Pleuronectidae and Belonidae). For the western sites that
display a more generalized fishery, the evidence for cool season fishing is much less,
with Gadidae generally comprising only a small part of the various assemblages and
represented by mostly juvenile individuals (Enghoff 1994a:74-75).
Cod Plaice Sole Turbot Mackerel Garfish
January 11% 2% 0% 1% 0% 0%
February 11% 3% 0% 1% 0% 0%
March 12% 8% 3% 2% 0% 0%
April 7% 10% 46% 22% 0% 7%
May 5% 15% 32% 35% 1% 62%
June 2% 21% 11% 24% 49% 24%
July 1% 16% 4% 7% 38% 5%
August 1% 10% 1% 4% 11% 2%
September 6% 8% 2% 1% 1% 0%
October 15% 4% 1% 1% 0% 0%
November 16% 2% 0% 1% 0% 0%
December 13% 1% 0% 1% 0% 0% Table 79: Seasonality of catch from 1885 fishery data (Drechsel 1890).
Herring (pound net) Herring (other nets) Eel (hand net) Eel (other net) Eel (spear) Eel (hook)
January 0% 0% 0% 0% 22% 0%
February 1% 0% 0% 0% 20% 0%
March 27% 1% 0% 0% 14% 0%
April 37% 3% 1% 5% 11% 2%
May 21% 3% 9% 16% 2% 7%
June 8% 1% 22% 23% 2% 16%
July 2% 2% 27% 28% 2% 41%
August 0% 10% 19% 14% 1% 32%
September 1% 57% 12% 7% 0% 5%
October 1% 16% 10% 5% 1% 6%
November 1% 6% 0% 2% 10% 0%
December 1% 0% 0% 0% 15% 0% Table 80: Seasonality of catch from 1885 fishery data (Drechsel 1890).
Using fish remains to get information about the seasonality of site use
remains an elusive goal. Otolith growth ring analysis by optical means has been shown
to be largely unreliable for archaeological specimens, but future studies focused on
staple isotope analysis have the potential to unlock the information from this resource.
Behavioral characteristics of the fishes that are present in the assemblages currently
offer the best seasonality information. Where Gadidae are present in large numbers,
especially adult specimens, they provide an argument for fishing during the cooler
months of the year, while many other fishes indicate warm season activities. Thus, the
specialized fisheries of eastern Denmark show evidence for year-round fishing, while
the generalized ones in western Denmark appear more focused on warm-season
fishing.
Why the people of western Denmark did not concentrate on fishing in the
cooler parts of the year is an important question. On the one hand, it may simply be that
the main prey species that is amenable to winter fishing (Gadidae) was generally scarce
in the fishing grounds near to the known settlements on Jutland (as discussed above).
On the other hand, it may have been resource abundance rather than scarcity that
influenced the decision. Although complete faunal analyses of many sites that are
included in this project have not been conducted, some general facts are known about
animal populations that may be important. Aurochs and moose are still available on
Jutland during the Ertebølle period, but extinct in the East (Aaris-Sørensen 1998).
Several other large and medium mammal species also went extinct during the Atlantic
or early Sub-boreal periods on the eastern islands (Aaris-Sørensen 1980). Studies of
roe deer populations have shown a decrease in body-size on the Danish islands from
the Boreal to the Atlantic periods, but no similar diminution occurred in Jutland. No
single cause for the body-size reduction of the insular deer population has been
established, but limited food supply (possibly as a result of the spread of climax forest)
is suggested as a possible factor (P. Jensen 1991). It should also be noted that Jutland
is at least three times the size of Zealand and while not all land is equally productive,
the enormous disparity in land mass certainly implies that more terrestrial fauna were
available on Jutland. Since land mammals are seen as being especially important to
subsistence during the fall and winter (see Figure 83), it may be that not enough
terrestrial animals were available in the East to meet their winter subsistence needs and
so they relied more heavily on aquatic resources. This is only a hypothesis, and needs
to be tested with further faunal analysis and more comprehensive diet breadth modeling
that attempts to incorporate all animal resources.
6.4 The social lives of fishing foragers
“Included in the strategies of maintaining a fishery as a basis for subsistence, and as
part of the daily life in a coastal foraging society, technology, social organization,
ideology and environment must interplay. Any changes that may occur within these
intertwined factors will always have an impact on the other parts of the interplay,” (Olson
2008:38)
Moving from the subsistence data available from the remains of past meals
to a greater understanding of the community organization, ideology and other aspects of
the social lives of the people who prepared and consumed those meals is a difficult
task, but one worth undertaking (e.g., Miracle 2002, Olson 2008). Even if we cannot
know the full details about these topics, increased knowledge about how the groups
provisioned themselves offers some insights into the rest of their culture. At the simplest
of levels, “the production and maintenance of fishing implements confirm, apart from the
well developed fishing strategies, and skilled craftsmanship, that fishing was, to a large
extent, on the peoples’ minds, even when not fishing,” (Olson 2008:38). In eastern
Denmark, the evidence for fishing in all seasons suggests that fish was not just on the
mind but in the belly throughout the year. Beyond simply satisfying hunger, fishing may
have involved striving for prestige through the capture of spectacularly large individuals
(as it does today). Bringing a meter long cod (or even larger tuna or swordfish) into
camp must surely have caused more of a commotion than a mess of 10 cm long roach,
even if the latter were able to contribute an equivalent amount of food. Conversely,
mass catches of fish of any size could have been important for provisioning feasts to
mark important dates on the calendar and/or social aggregations. Brian Hayden has
proposed that the ability to generate food surpluses sufficient for feasting may have
been the mechanism of aggrandizement amongst complex hunter-gatherers that
eventually necessitated the adoption of domesticated plants and animals (1995). The
imported groundstone axes may be the material markers of social connections to other
regions, maintained by feasting and controlled by individuals and groups who aspired to
wealth and power (Klassen 2002). The prevalence of these axes in eastern Denmark
stresses the importance of maritime exchange as they, “probably arrived in Denmark by
boat across the Baltic,” (Fischer 2003:411). If so, this means that building and owning
watercraft was not just an aid to subsistence pursuits, but also a means to acquiring
prestige. The impressive size of some of the canoes and the effort sometimes devoted
to decorating paddles certainly imply that these were important and highly-valued
possessions.
The allocation of labor to other maritime technologies required
organizational decisions that would have provided another opportunity for individuals to
differentiate themselves. Creation of fishing nets may have consumed hundreds of
person-hours in preparation time before the first fish was brought ashore with them
(Lindström 1996). Constructing fish fences and traps may have required an even longer
term planning horizon, if the coppicing of hazel groves years in advance to provide raw
materials is included in the production process (K. Christensen 1997, Pedersen 1995).
Where seasonal runs of fish were exploited (e.g., Anguillidae, Belonidae and
Salmonidae), preparations included monitoring fishing grounds for the appearance of
fish and scheduling the labor necessary to capture and process a briefly available, but
abundant catch. Coordinating the efforts necessary to construct the required
implements, employ them and then distribute the proceeds required a managerial
function that directed the entire population of a settlement.
Other aspects of labor were also affected by the type of fishing strategy
chosen by a group. Specialized fisheries, to the extent they relied on active hook-and-
line fishing away from shore, would have different labor requirements than a fishery
focusing on more passive techniques such as fish traps. Once a fish trap is emplaced
almost anyone can perform the chore of emptying the baskets one or more times a day,
but paddling a dugout canoe on the sea is a job for fit adults (or at a minimum
adolescents). Net fishing conducted with seine nets would have placed similarly high
demands on group members in their prime, especially if conducted with the aid of
watercraft. Taking dugout canoes out on the seas also carried an element of risk, as
sudden changes in weather could easily doom a small craft. Strong social bonds to a
larger community could help to ameliorate the risk of losing a family’s primary provider
at sea.
Another consideration for foragers that depended on fishing for a large part
of their diet was the importance of, “access to the areas where abundant catches could
be expected… efforts to maintain these rights must also have been included in the
fisheries,” (Olson 2008:38). The evidence for increased territoriality in the Late
Mesolithic (Petersen 1984) is very likely tied to the strengthening of intra-group bonds to
promote a united front in defending these (and other) rights against encroachment from
other groups. The prevalence of interpersonal violence seen on Late Mesolithic
skeletons is probably symptomatic of the increased conflict brought about by
competition for control of the most desirable resource procurement locations
(Meiklejohn et al. 1998). Since the easiest way to control fishing grounds was to occupy
the shore locations in the vicinity, reliance on fishing would have provided an incentive
to increased sedentism. The fact that so many Ertebølle sites are situated on the coast,
have evidence for multiple seasons of occupation and are often in good fishing
locations, is further evidence that maintaining access to areas where many fish could be
caught was an important consideration when groups decided where to settle. One effect
of the predominance of coastal settlements is that the Ertebølle people were primarily
connected by maritime, linear lines of communication, increasing the distance over
which social networks could be maintained (Ames 2002, Andersen 2008, Yesner 1980).
While by no means an exhaustive list; centrality to everyday life, the
potential for garnering prestige, the probable necessity of a managerial function for
coordinating fishing-related activities and an increase in territoriality are all ways that a
subsistence regime emphasizing fishing would have affected the social lives of its
practitioners. The fisheries of western Denmark that were heavily reliant on stationary
fishing structures were especially challenged by organizing labor to build the structures
and then dividing the catch amongst those involved. In eastern Denmark, the maritime
lines of communication of an insular population and the potential prestige of capturing
large Gadidae were probably more important social considerations. If the hypothesis
that terrestrial mammal populations were inadequate to meet the needs of the people
on Zealand is true, conflicts over access to fishing grounds would have been especially
fierce.
7. Conclusions and Future Opportunities for Research
7.1 Conclusion
The addition of over 110,000 identified fish bones to the Ertebølle dataset is
a major contribution of this project. By increasing the geographical coverage of Zealand,
the new assemblages allow more meaningful comparisons between the fisheries of
eastern and western Denmark. The previously recognized regional differences between
Danish Ertebølle groups have largely involved stylistic elements of tool design or
articles of personal adornment. While important as markers of group identity and inter-
group contact, they do not prove fundamental behavioral variability in the same way that
the fishery differences do: regional subsistence variability gets to the core of Ertebølle
culture. A comparison of fish assemblage heterogeneity (with NTAXA and Shannon
index values) demonstrates that sites in eastern Denmark had a narrower diet breadth
than those in the west. Furthermore, the specialized fisheries in the east were almost
always focused on Gadidae. An emphasis on hook-and-line fishing, especially during
the cooler months of the year, is a probable corollary of the overall dominance of
Gadidae and the large size of some of the individual specimens at the eastern sites.
This is a distinctly different interpretation than the warm-season, stationary structure-
focused fishery that has previously been proposed as the model for the Danish
Ertebølle, based largely on the results of assemblages from shell midden sites on
Jutland.
While discovering accurate generalizations (e.g., Anguillidae are present in
virtually all assemblages, freshwater species are a minor component of the Ertebølle
fishery) is a useful endeavor, so is the recognition of variability. This is especially so in
the case of the Late Mesolithic fisheries of Denmark, where the variability is regionally
patterned. The focus on Gadidae on the islands of eastern Denmark may be partly a
response to the more limited opportunities for hunting mammals during the late fall to
early spring. If so, access to good fishing grounds would have been particularly
important for group survival and would have been incentive to remain permanently in
prime locations. Competition for particular locations promoted territorial claims and
could have provided the incentive for violent confrontations between rival groups
(Yesner 1980:731-732).
Non-violent competition may have been an important part of life for
Ertebølle society, as individuals or groups sought to increase their status relative to
other members of society. Garnering prestige through the capture of impressive fish
specimens or provisioning of feasts with hefty catches of fish would have helped to
distinguish aggrandizers. Control of long-distance social networks or the managerial
functions necessitated by an increasingly complex economy would have distinguished
certain elements of society.
Finally, as discussed in the introduction when reviewing reasons why this
period is popular amongst archaeological researchers, the Ertebølle culture is important
as the ultimate hunter-gatherer tradition in Denmark that was supplanted by the Early
Neolithic farming culture through a process of indigenous adoption (Price 2000). “The
last hunters were the first farmers,” (Price and Gebauer 1995:8). Because of this, it is
necessary to understand Late Mesolithic culture in order to study how and why these
hunter-gatherers eventually chose to adopt the use of domesticated plants and animals.
Examining changes in subsistence between the Late Mesolithic and Early Neolithic is
one important way this can be done. The changes can be described as occurring either
gradually or abruptly depending on which aspects of subsistence are emphasized (i.e.,
use of wild resources or marine versus terrestrial foods) (Richards et al. 2003, Rowley-
Conwy 2004). It seems increasingly clear that an explanation of the transition that
focuses solely on a critical shortage of resources (e.g., Larsson 1990, Rowley-Conwy
1984) overlooks critical social changes that had already begun during the Late
Mesolithic. The difference in the Ertebølle fisheries of eastern and western Denmark
argue against resource shortage as a driving force in the transition to agriculture,
because different sites reflect reliance on different resources that would not have been
equally affected by environmental changes. Furthermore, the changes through time
identified in some of the assemblages show that Ertebølle fisheries were able to
respond to shifts in resource availability by targeting different species. Although
subsistence is a critically important part of culture, it is also necessary to consider how it
impacts other areas of life. Gathering prestige may have been as important a part of a
fishing expedition as gathering food.
The complex nature of Ertebølle subsistence is confirmed by closer
examination of the contribution made by fishes. Multiple fishing strategies were
employed to provide a substantial and reliable source of food, and differences in the
focus of fishing show that Ertebølle fishermen carefully reflected on both subsistence
requirements and local conditions when planning their activities. Any thoughts about a
people passively accepting whatever bounty of the sea happened to appear before
them are untenable, as the evidence shows a deliberate and sophisticated exploitation
of the marine environment. Excavation, identification, quantification and interpretation of
ancient fish bones require a great commitment of resources, but with proper attention to
method and theory the archaeological payoff is commensurate with the costs incurred.
7.2 Future research opportunities
Most archaeological projects are as important for the questions generated
as the answers provided and this one is no exception. From a methodological
standpoint, the findings discussed here highlight the need for comprehensive sampling
to evaluate what bones are missed because of the mesh-size chosen for screening
operations. Investigating the effects of screen-size on assemblages from different types
of sites and in different regions may allow for corrections to be made to previously
obtained results so that it is possible to compare them without fear that differential
recovery is significantly biasing the results. The extents to which excavator skill and
experience affect field recovery of fish bones also deserve more study. Taphonomy is a
subject that can always use more attention. Experimental work with bone degradation
under different conditions and innovative statistical analyses of archaeological
assemblages both hold out promise for a better understanding of the effects of
differential preservation.
The intra-site variation noted in some of the assemblages begs for further
investigations within existing collections and on newly discovered sites to better
understand its nature and extent. Comparison with Ertebølle assemblages outside of
Denmark will also prove interesting in this regard and for evaluating regional variation
on a broader scale. Having recognized differences in the fish fauna, another obvious
direction for future research is expanding investigations to include other types of
subsistence resources (e.g., mammals, birds and plants). Expanding diet breadth
modeling to incorporate the full range of subsistence resources will allow better
predictions of foraging behavior to compare against the archaeological record.
Experimental work with prehistoric fishing technologies can provide useful information
about potential costs and benefits to improve foraging models.
Archaeometric research continues to complement traditional faunal analysis
in the quest to better understand past diets and environments. Isotopic analysis of
otoliths is an especially promising area of research for fish bone studies as it offers the
potential for definitive season of catch data. Otoliths and other skeletal elements can
also be analyzed with this technique to provide information about past environmental
conditions and fish migrations. Additional human and bone isotope studies will continue
to enhance our understanding of the temporal and geographical variability in diets and
environment. I aim to pursue these topics in the near future to attempt to resolve some
of the questions that were raised by this project.
Other promising lines of archaeological chemistry work include residue
analysis of potsherds and flint tools to enable us to see the relationship between fish
bones and other classes of material evidence. These studies may also shed light on the
poorly understood processing and preparation of marine foods. Comparisons between
assemblages can always be improved by additional dating work (especially direct dating
of fish specimens and fishing technology). Better chronological control can also help to
link changes in archaeological materials with changes in environmental conditions.
As always, some of the most exciting future information is likely to come
from techniques that are not yet developed. Of course, new excavations and analysis of
curated but unexamined collections will also provide important data. Regardless of the
techniques employed, Ertebølle studies in general and fish bone analyses in particular
will remain dynamic areas of research for years to come.
8. Acknowledgements
A project of this magnitude cannot be completed without the support and
assistance of many individuals. Although it is probably not possible to name every one
of them, I would nonetheless like to try to thank some. If I have overlooked anyone it is
inadvertent and not due to a lack of gratitude for the help.
First and foremost I would like to thank my wife Lone for her companionship
and support during the excavation, analysis and writing phases of this project. I also
thank her for many engaging discussions on prehistory and the time she spent reading
and commenting on various drafts of this paper. Although not as actively engaged in the
archaeological work as Lone, I am also grateful to the rest of my family for their
unwavering support and encouragement during the long process. I especially
appreciate all of you listening to my complaints when I was frustrated and feeling like I
would never finish.
My debt of gratitude to Doug Price is enormous and on many levels. I will
never forget the spring day in 2002 when he stopped me in the hallway to ask if I
wanted to take part in his excavations that summer. It opened a doorway into Danish
and Mesolithic archaeology that has taken my life down a path I had never anticipated.
In addition to allowing me to participate on his excavations over the course of five
summers, he trusted me with the task of examining the fish bones recovered. I am also
grateful for his friendship and guidance during the process of bringing this project to
fruition. The final result is much better because of his participation.
Sissel Schroeder deserves many thanks for bringing me into the graduate
program at the University of Wisconsin, supporting my studies there, and guiding my
research along the way. I thank the other faculty and staff at the UW for teaching me
about archaeology (and a few other topics) and helping me to negotiate the sometimes
winding road to finishing my degree. My gratitude extends to the faculty and staff of the
UW-La Crosse and the Mississippi Valley Archaeology Center for getting my started on
my career as an archaeologist.
I want to thank Jens Nielsen for being a kind and patient mentor as I tried to
learn about Danish prehistory and how archaeology is conducted in Denmark. More
than that, I am grateful for his friendship and the many great experiences I had because
he was so welcoming to the American graduate students who invaded his life. I also
thank the other fine people at the Kalundborg Museum who welcomed us and helped
make the excavations possible. Thanks to Egon ‘Columbus’ Iversen for his many
contributions as an avocational archaeologist and his help obtaining some of the harder
to get fish for my comparative collection. I am very much in the debt of my fellow
excavators for making life in the field and at the summer house enjoyable, for many
stimulating conversations, and of course, for their perseverance and patience in picking
thousands upon thousands of fish bones from the screens so that I had the material to
examine. And thanks to the Nisse for keeping watch over us.
I would also like to express my gratitude to Søren H. Andersen for
generously sharing his knowledge of the Danish Mesolithic and for allowing me to
examine the fish bones from Havnø. I want to acknowledge the good folks at the
Conservation Department out at Moesgård who were always happy to see me and
share their laboratory space (and microscopes) with me. I had many a good
conversation out there; some were even about archaeology. I thank Niels Axel Boas
and Djurslands Museum for allowing me to excavate at Jesholm I and giving me access
to the fish bones from Nederst. The Danish Fishery Museum there also provided me
with great information about the history of fishing in Denmark. Thanks to Søren A.
Sørensen for permission to look at the fish bones from Lollikhuse and answering all of
my questions about the assemblage. The people at the Zoological Institute in
Copenhagen were very welcoming during my visits and answered many questions,
especially Knud Rosenlund and Inge B. Enghoff.
Finally, and certainly not least, I want to thank the Center for Baltic and
Scandinavian Archaeology at Schloss Gottorf, Schleswig, Germany for allowing me
access to their excellent comparative collection, the extraordinary hospitality on my
visits there, and funding support during the final stages of writing. I especially thank
Ulrich Schmölcke and Dirk Heinrich for sharing their knowledge of fish identification with
me and being as excited as I am about fish.
Once again, a huge ‘thank you’ to all, and I hope you see your contribution
in the final product. It has been a long road, but I am a better person at the end of it.
Ken Ritchie
Århus, Denmark
January 2010
9. Works cited
Aaris-Sørensen, Kim
1980 Depauperation of the mammalian fauna of the island of Zealand during the Atlantic
period. Vidensk. Meed. Dansk Naturh. Foren. 142:131-138.
1998 Danmarks Forhistoriske Dyreverden: Om skovelefanter, næsehorn, bisoner,
urokser, mammuter og kæmpehjorte. Gyldendals, Værløse, Denmark.
Ahlström, Torbjörn
2003 Mesolithic Human Skeletal Remains from Tågerup, Scania, Sweden. In Mesolithic
on the Move, edited by L. Larsson, H. Kindgren, K. Knutsson, D. Loeffler and A.
Åkerlund, pp.478-484. Oxbow Books, Oxford.
Ambrose, S. H. and L. Norr
1993 Experimental evidence for the relationship of the carbon isotope ratios of whole
diet and dietary protein to those of bone collagen and carbonate. In Prehistoric
human bone: archaeology at the molecular level edited by J. B. Lambert and G.
Grupe, pp.1–37. Springer-Verlag, Berlin.
Ames, Kenneth
2002 Chapter 2: Going by Boat: The Forager-Collector Continuum at Sea. In Beyond
Foraging and Collecting: Evolutionary Change in Hunter-Gatherer Settlement
System, edited by B. Fitzhugh and J. Habu, pp.19-52. Kluwer Academic, New
York.
Amorosi, Thomas, James Wollett, Sophia Perdikaris and Thomas McGovern
1996 Regional zooarchaeology and global change: problems and potentials. World
Archaeology 28(1):126-157.
Andersen, Søren H.
1971a Gudenaakulturen. Hostebro Museum Årsskrift 1970-71:14-32.
1971b Ertebøllekulturens harpooner. KUML 1971:73-126.
1985 Tybrind Vig: A Preliminary Report on a Submerged Ertebølle Settlement on
the West Coast of Fyn. Journal of Danish Archaeology 4:52.70.
1986 Mesolithic dugouts and paddles from Tybrind Vig, Denmark. Acta Archaeologica
57:87-106.
1989 Norsminde: A “Køkkenmødding” with Late Mesolithic and Early Neolithic
Occupation. Journal of Danish Archaeology 8:13-40.
1991 Bjørnsholm. A Stratified “køkkenmødding” at the Central Limfjord, North Jutland.
Journal of Danish Archaeology 10:59-93.
1995 Coastal adaptation and marine exploitation in Late Mesolithic Denmark – with
special emphasis on the Limfjord region. In Man and the Sea in the Mesolithic,
edited by A. Fischer, pp.41-66. Oxbow Books, Oxford.
2001 Oldtiden i Danmark: Jægerstenalderen. Sesam, Denmark.
2004 Danish Shell Middens Reviewed. In Mesolithic Scotland and its Neighbours,
edited by A. Saville, pp.393-412. Society of Antiquaries of Scotland, Edinburgh.
2007 Shell Middens (“Køkkenmøddinger”) in Danish Prehistory as a reflection of the
marine environment. In Shell Middens of Atlantic Europe, edited by N. Milner, O.
Craig and G. Bailey, pp.31-45. Oxbow Books, Oxford.
2008a Shell Middens (“Køkkenmøddinger”): The Danish Evidence. In Early Human
Impacts on Megamolluscs, edited by A. Antczak and R. Cipriani, pp.135-156.
BAR International Series 1865, Oxford.
2008b Perlepynt. Skalk 2:16-17.
2009 Ronæs Skov: Marinarkæologiske undersøgelser af kystboplads fra Ertebølletid.
Jysk Arkæologisk Selskab, Højbjerg, Denmark.
Andersen, Søren H. and Erik Johansen
1986 Ertebølle Revisited Journal of Danish Archaeology 5:31-61.
Andersen, Søren H. and Claus Malmros
1984 Madskorpe på Ertebøllekar fra Tybrind Vig. Aarbøger for nordisk Oldkyndighed og
Historie 78-95.
Andersson, Magnus, Per Karsten, Bo Knarrström and Mac Svensson
2004 Stone Age Scania. Riksantikvarieämbetets Forlag Skrifter No. 52, Malmö,
Sweden.
Antczak, Andrzej and Roberto Cipriani
2008 Early Human Impact on Megamolluscs. BAR International Series 1865, Oxford.
Arias, Pablo
1999 The Origins of the Neolithic Along the Atlantic Coast of Continental Europe: A
Survey. Journal of World Prehistory 13(4): 403-464.
Aswani, Shankar
1998 Patterns of marine harvest effort in southwestern New Georgia, Solomon Islands:
resource management or optimal foraging? Ocean and Coastal Management
40:207-235.
Bagge, Ole
2004 The biology of the greater weever (Trachinus draco) in the commercial fishery of
the Kattegat. ICES Journal of Marine Science 61:933-943.
Bailey, Geoff and Nicky Milner
2002 Coastal hunter-gatherers and social evolution: marginal or central? Beyond
Farming 4(1):1-22.
Barber, Ian
2003 Sea, Land and Fish: Spatial Relationships and the Archaeology of South Island
Maori Fishing. World Archaeology 35(3):434-448.
Barrett, James H.
1993 Bone Weight, Meat Yield Estimates and Cod (Gadidae): a Preliminary Study of the
Weight Method. International Journal of Osteoarchaeology 3:1-18.
1997 Fish trade in Norse Orkney and Caithness: a zooarchaeological approach.
Antiquity 71:616-638.
Behrensmeyer, Anna K.
1991 Terrestrial vertebrate accumulations. In Taphonomy: releasing the data locked in
the fossil record, edited by P. Allison and D. Briggs, pp.291-335. Plenum Press,
New York.
Binford, Lewis
2001 Constructing Frames of Reference. University of California Press, Los Angeles.
Birchall, J., T.C. O’Connell, T.H.E. Heaton, R.E.M. Hedges
2005 Hydrogen isotope ratios in animal body protein reflect trophic level. Journal of
Animal Ecology 74:877-881.
Bird, Douglas W. and Rebecca Bliege Bird
2000 The Ethnoarchaeology of Juvenile Foragers: Shellfishing Strategies among
Meriam Children. Journal of Anthropological Anthropology 19:461-476.
Bird, Douglas W. And James F. O’Connell
2006 Behavioral Ecology and Archaeology. Journal of Archaeological Research 14:143-
188.
Bird, Rebecca Bliege, and Smith, Eric A.
2005 Signaling theory, strategic interaction, and symbolic capital. Current Anthropology
46(2):221-248.
Bjerck, Hein
2007 Mesolithic coastal settlements and shell middens (?) in Norway. In Shell Middens
in Atlantic Europe, edited by N. Milner, O. Craig and G. Bailey, pp.5-30. Oxbow
Books, Oxford.
Bowdler, Sandra and Sally McGann
1996 Prehistoric Fishing at Shark Bay, Western Australia. In Prehistoric Hunter-Gatherer
Fishing Strategies, edited by M. Plew, pp.84-113. Boise State University, Boise.
Bratlund, B.
1991 The Bone Remains of Mammals and Birds from the Bjørnsholm Shellmidden.
Journal of Danish Archaeology 10:97-104.
Brinkhuizen, Dick
1983 Some notes on recent and pre- and protohistoric fishing gear from Northwestern
Europe. Palaeohistoria 25:7-54
Broughton, Jack M.
2002 Prey spatial structure and behavior affect archaeological tests of optimal foraging
models: examples from the Emeryville Shellmound vertebrate fauna. World
Archaeology 34(1):60-83.
Buikstra, Jane E. and George R. Milner
1991 Isotopic and archaeological interpretations of diet in the central Mississipi valley.
Journal of Archaeological Science 18:319–29.
v. Busekist, Jörg
2004 “Bone Base Baltic Sea”, a computer supported identification system for fish
bones. Version 1.0 for MS-Windows CD-ROM. http://www.bioarchiv.de, University
of Rostock, Germany.
Butler, Virginia and Roy Schroeder
1998 Do Digestive Processes Leave Diagnostic Traces on Fish Bones? Journal of
Archaeological Science 25:957-971.
Cannon, Debbi Yee
1987 Marine Fish Osteology: A Manual for Archaeologists. Archaeology Press, Burnaby,
B.C.
Carter, Richard
2009 One pig does not a winter make. New Seasonal evidence at the Early Mesolithic
sites of Holmegaard and Mullerup and the Late Mesolithic site of Ertebølle in
Denmark. In Mesolithic Horizons, edited by S. McCartan, R. Schulting, G. Warren
and P. Woodman, pp.115-121. Oxbow Books, Oxford.
Casteel, Richard W.
1972 Some Biases in the Recovery of Archaeological Faunal Remains. Proceedings of
the Prehistoric Society 38:382-388.
1976 Fish Remains in Archaeology. Academic Press, London, New York, San
Francisco.
Cerling, T. E. and J.M. Harris
1999 Carbon isotope fractionation between diet and bioapatite in ungulate mammals
and implications for ecological and paleoecological studies. Oecologia 120:247–
263.
Christensen, Charlie
1990 Stone Age dug-out boats in Denmark: Occurrence, age, form and reconstruction.
In Experimentation and Reconstruction in Environmental Archaeology, edited by
D. Robinson, pp. 119-142. Oxbow Books, Oxford.
1995 The littorina transgressions in Denmark. In Man and Sea in the Mesolithic, edited
by A. Fischer, pp.15-22. Oxbow Books, Oxford.
Christensen, Kjeld
1997 Træ fra fiskegærder – skovbrug i stenalderen. In Storebælt i 10.000 år, edited by
L. Pedersen, A. Fischer and B. Aaby, pp.147-156. A/S Storebæltsforbindelsen,
Copenhagen.
Clark, Grahame
1948 The Development of Fishing in Prehistoric Europe. The Antiquaries Journal 28:45-
85.
1975 The Earlier Stone Age Settlement of Scandinavia. Cambridge University Press,
Cambridge.
1983 Coastal Settlement in European Prehistory with Special Reference to
Fennoscandia. In Prehistoric Settlement Patterns: Essays in Honor of Gordon R.
Willey, edited by E.Z. Vogt and R. M. Leventhal. University of New Mexico Press
and Peabody Museum, Cambridge, MA.
Clason, A.T. and W. Prummel
1977 Collecting, Sieving and Archaeozoological Research. Journal of Archaeological
Science 4:171-175.
Coles, J.M.,
1971 The early settlement of Scotland: excavations at Morton, Fife. Proceedings of the
Prehistoric Society 38:284–366.
Colley, S.M.
1987 Fishing for Facts. Can We Reconstruct Fishing Methods from Archaeological
Evidence? Australian Archaeology 24:16-26.
Collins, M. J., Nielsen-Marsh, C. M., Hiller, J., Smith, C. I., Roberts, J. P., Prigodich, R. V.,
Wess, T. J., Csap, J., Millard, A. R., and Turner-Walker, G.
2002 The survival of organic matter in bone: a review. Archaeometry 44:383–94.
Craig, O.E. Craig, R. Ross, Søren H. Andersen, Nicky Milner, G.N. Bailey
2006 Focus: sulphur isotope variation in archaeological marine fauna from northern
Europe. Journal of Archaeological Science 33:1642-1646.
Degerbøl, M.
1945 Subfossile Fisk fra Kvartærtiden i Danmark. Vidensk. Medd. Bind 106,
Copenhagen.
DeNiro, M. J. and S. Epstein
1978 Influences of diet on the carbon isotope distribution in animals. Geochimica et
Cosmochimica Acta 42:495–506.
1981 Influence of diet on the distribution of nitrogen isotopes in animals. Geochimica et
Cosmochimica Acta 45:341-351.
Donner, Joakim
1995 The Quaternary History of Scandinavia. Cambridge University Press, Cambridge.
Drechsel, C. F.
1890 Oversigt over vore Saltvandsfiskerier. Danskfiskerimuseum, Grenaa.
Dufour, E., H. Bocherens and A. Mariotti
1999 Palaeodietary implications of isotopic variability in Eurasian lacustrine fish.
Journal of Archaeological Science 26:617–627.
Dupont, Catherine, Rick Schulting and Anne Tresset
2007 Prehistoric shell middens along the French Atlantic façade: the use of marine and
terrestrial resources in the diets of coastal human populations. In Shell Middens in
Atlantic Europe, edited by N. Milner, O. Craig and G. Bailey, pp.123-135. Oxbow
Books, Oxford.
Enghoff, Inge B.
1983 Size Distribution of Cod (Gadidae) and Whiting (Merlangius merlangus) (Pisces,
Gadidae) from a Mesolithic Settlement at Vedbaek, North Zealand, Denmark.
Vidensk Meedr dansk naturh. Foren. 144:83-97.
1986 Freshwater Fishing from a Sea-Coast Settlement, the Ertebølle locus classicus
Revisited. Journal of Danish Archaeology 5:62-76.
1989 Fishing from the Stone Age Settlement of Norsminde. Journal of Danish
Archaeology 8:41-50.
1991 Mesolithic Eel-fishing at Bjørnsholm, Denmark, Spiced with Exotic Species.
Journal of Danish Archaeology 10:105-118.
1994a Fishing in Denmark during the Ertebølle Period. International Journal of
Osteoarchaeology 4:65-96.
1994b Freshwater fishing at Ringkloster, with a supplement of marine fishes. Journal of
Danish Archaeology 12:99-106.
1995 Fishing in Denmark during the Mesolithic Period. In Man and Sea in the Mesolithic,
edited by A. Fischer, pp.67-74. Oxbow Books, Oxford.
2005 Viking Age fishing in Denmark, with particular focus on the freshwater site Viborg
methods of excavation, and smelt fishing. Proceedings of the 13th Meeting of the
ICAZ Fish Remains Working Group in October 4th – 9th, Basel/August 2005,
edited by H.H. Plogmann.
2009 Dyreknogler fra Ronæs Skov-bopladsen. In Ronæs Skov: Marinarkæologiske
undersøgelser af kystboplads fra Ertebølletid, Søren H. Andersen, pp.243-271.
Jysk Arkæologisk Selskab, Højbjerg, Denmark
Enghoff, Inge B., Richard MacKenzie and Einar Eg Nielsen
2007 The Danish fish fauna during the warm Atlantic period (ca. 7000-3900B.C.):
Forerunner of Future Changes? Fisheries Research 87:167-180.
Eriksson, Gunilla and Ilga Zagorska
2003 Do dogs eat like humans? Marine isotope signals in dog teeth from inland
Zvejnieki. In Mesolithic on the Move, edited by L. Larsson, H. Kindgren, K.
Knutsson, D. Loeffler and A. Åkerlund, pp.160-168. Oxbow Books, Oxford.
Fano, Miguel A.
2007 The use of marine resources by the Mesolithic and Early Neolithic societies of
Cantabrian Spain: the current evidence. In Shell Middens in Atlantic Europe,
edited by N. Milner, O. Craig and G. Bailey, pp.136-149. Oxbow Books, Oxford.
Farquhar, G. D., J.R. Ehleringer and K.T. Hubick
1989 Carbon isotope discrimination and photosynthesis. Annual Review of Plant
Physiology and Plant Molecular Biology 40:503–537.
Fischer, Anders
1993 Stenalderbopladser i Smålandsfarvandet: En teori afprøvet ved
dykkerbesigtigelse. Miljøministeriet, Skov- og Naturstyrelsen, Copenhagen.
1995 Man and Sea in the Mesolithic. Oxbow Books, Oxford.
2003 Trapping up the rivers and trading across the sea – steps towards the
Neolithisation of Denmark. In Mesolithic on the Move, edited by L. Larsson, H.
Kindgren, K. Knutsson, D. Loeffler and A. Åkerlund, pp.405-413. Oxbow Books,
Oxford.
2007 Coastal fishing in Stone Age Denmark – evidence from below and above the
present sea level and from human bones. In Shell Middens of Atlantic Europe,
edited by N. Milner, O. Craig and G. Bailey, pp.54-69. Oxbow Books, Oxford.
Fischer, Anders and Kristian Kristiansen
2002 The Neolithisation of Denmark: 150 years of debate. J.R. Collis, Dorset, UK.
Fischer, Anders, Jesper Olsen, Mike Richards, Jan Heinemeier, Arny E. Sveinbjörnsdottir, and
Pia Bennike
2007 Coast-inland mobility and diet in the Danish Mesolithic and Neolithic: evidence
from stable isotope values of humans and dogs. Journal of Archaeological Science
34:2125-2150.
Gargett, Robert and Deborah Vale
2005 There’s something fishy going on around here. Journal of Archaeological Science
32:647-652.
Gebauer, Anna Birgitte and T. Douglas Price
1992 Transitions to Agriculture in Prehistory. Prehistory Press, Madison, WI.
Gobalet, Kenneth W.
2001 A Critique of Faunal Analysis; Inconsistency among Experts in Blind Tests. Journal
of Archaeological Science 28:377-386.
Gramsch, Bernhard
1987 Ausgrabungen auf dem mesolitischen Moorfundplatz bei Friesack, Bezirk
Potsdam. Veröffentlichungen des Museums für Ur- und Frühgeschichte Potsdam
21:75-100.
Greenspan, Ruth L.
1998 Gear Selectivity Models, Mortality Profiles and the Interpretation of Archaeological
Fish Remains: A Case Study from the Harney Basin, Oregon. Journal of
Archaeological Science 25:973-984.
Grupe, Gisela, Dirk Heinrich and Joris Peters
2009 A brackish water aquatic foodweb: trophic levels and salinity gradients in the
Schlei fjord, Northern Germany, in Viking and medieval times. Journal of
Archaeological Science 36:2125-2144.
Grøn, Ole and Jørgen Skaarup
1991 Møllegabet II – A Submerged Mesolithic Site and a “Boast Burial” from Ærø.
Journal of Danish Archaeology 10:38-50.
Hartz, Sönke, Dirk Heinrich and Harald Lübke
2002 Coastal Farmers – the Neolithisation of northern-most Germany. In The
Neolithisation of Denmark, edited by A. Fischer and K. Kristiansen, pp.321-340.
Hayden, Brian
1995 A New Overview of Domestication. In Last Hunters-First Farmers: New
Perspectives on the Prehistoric Transition to Agriculture, edited by T.D: Price and
A.B. Gebauer, pp.243-299. School of American Research Press, Santa Fe, New
Mexico.
Hede, Signe Ufeldt
2003 Prehistoric settlements and Holocene relative sea-level changes in northwest
Sjælland, Denmark. Bulletin of the Geological Society of Denmark 50:141-149.
2005 The Finds: Mammal, Bird and Amphibian Bones. In Smakkerup Huse: A Late
Mesolithic Coastal Site in Northwest Zealand, Denmark, edited by T.D. Price and
A.B. Gebauer, pp.91-102. Aarhus University Press, Århus.
Hedges, Robert E.M. and Linda M. Reynard
2007 Nitrogen isotopes and the trophic level of humans in archaeology. Journal of
Archaeology Science 34:1240-1251.
Heinrich, Dirk
1994 The fish remains from Durankulak/Bulgaria and from some other sites: Are they
biased by the excavator? Papers presented at the 6th Meeting of the I.C.A.Z. Fish
Remains Working Group, Neumünster.
Heron, Carl, Oliver Craig, Marcus Forster, Ben Stern and Søren H. Andersen
2007 Residue analysis of ceramics from prehistoric shell middens in Denmark. In Shell
Middens of Atlantic Europe, edited by N. Milner, O. Craig and G. Bailey, pp.78-85.
Oxbow Books, Oxford.
Hildebrandt, William R. And Kelly R. McGuire
2002 The Ascendance of Hunting during the California Middle Archaic: An Evolutionary
Perspective. American Antiquity 67(2):231-256.
Hufthammer, Anne K., Hans Høie, Arild Folkvord, Audrey Geffen, Carin Andersson, Ulysses S.
Ninnemann
2009 Seasonality of human site occupation based on stable oxygen isotope ratios of
cod otoliths. Journal of Archaeological Science (2009).
Härkönen, Tero
1986 Guide to the Otoliths of the bony fishes of the Northeast Atlantic. Danbiu Aps,
Hellerup, Denmark.
James, Stephen R.
1997 Methodological Issues Concerning Screen Size Recovery Rates and Their Effects
on Archaeofaunal Interpretations. Journal of Archaeological Science 24:385-397.
Jensen, Ole Lass
2001 Kongemose- og Ertebøllekultur ved den fosille Nivåfjord. In Danmarks
Jægerstenalder – Status og Perspektiver, edited by O.L. Jensen, S. Sørensen and
K.M. Hansen, pp.115-130. Hørsholm Egns Museum, Hørsholm, Danmark.
Jensen, Ole Lass, Søren Sørensen and Keld Møller Hansen
2001 Danmarks Jægerstenalder – Status og Perspektiver. Hørsholm Egns Museum,
Hørsholm, Danmark.
Jensen, Philip
1991 Body Size Trends of Roe Deer (Capreolus capreolus) from Danish Mesolithic
Sites. Journal of Danish Archaeology 10:51-58.
Johansson, Axel Degn
1995 The Ertebølle Culture in South Zealand, Denmark. In Man and the Sea in the
Mesolithic, edited by A. Fischer. Oxbow Books, Oxford.
1998 Ældre Stenalder I sydlige Norden. SDA John Petersen, Farum, Denmark.
Jones, Andrew K.G.
1986 Fish bone survival in the digestive system of the pig, dog and man: some
experiments. In Fish and Archaeology, edited by D. Brinkhuizen and A. Clason,
pp.53-61. BAR International Series No. 294, Oxford.
Jonsson, Leif
1986 Fish Bones in Late Mesolithic Human Graves at Skateholm, Scania. BAR
International Series No. 294, Oxford.
Jønsson, Bente and Lisbeth Pedersen
1983 Sønderholm: En østsjællansk boplads fra Ertebøllekulturen – kendt, glemt og
genfundet. Antikvariske Studier 6:173-185.
Kabacinski, J., Dirk Heinrich and Thomas Terberger
2009 Dabki revisited: new evidence on the question of the earliest cattle in Pomerania.
In Mesolithic Horizons, edited by S. McCartan, R. Schulting, G. Warren and P.
Woodman, pp.548-555. Oxbow Books, Oxford.
Karsten, Per and Bo Knarrström
2003 The Tågerup Excavations. Berlings Skogs, Trelleborg, Sweden.
Katzenberg, M.A. and H.R. Krouse
1989 Application of stable isotope variation in human tissue to problems of identification.
Canadian Society of Forensic Science Journal 22:7-19.
Katzenberg, M.A. and A. Weber
1999 Stable isotope ecology and palaeodiet in the Lake Baikal region of Siberia.
Journal of Archaeological Science 26:651-659.
Kelly, Robert L.
1992 Mobility/sedentism: Concepts, Archaeological Measures and Effects. Annual
Review of Anthropology 21:43-66.
1994 The Foraging Spectrum: Diversity in Hunter-Gatherer Lifeways. Smithsonian
Institution Press, Washington D.C.
Klassen, Lutz
2002 The Ertebølle Culture and Neolithic continental Europe: traces of contact and
interaction. In The Neolithisation of Denmark, edited by A. Fischer and K.
Kristiansen, pp.321-340. J.R. Collis, Dorset, UK.
Kriiska, Aivar and Lembi Lõugas
2009 Stone Age settlement sites on an environmentally sensitive coastal area along the
lower reaches of the River Pärnu (south-western Estonia), as indicators of
changing settlement patterns, technologies and economies. In Mesolithic
Horizons, edited by S. McCartan, R. Schulting, G. Warren and P. Woodman,
pp.167-175. Oxbow Books, Oxford.
Kristiansen, Kristian
2002 The Birth of Ecological Archaeology in Denmark. In The Neolithisation of
Denmark, edited by A. Fischer and K. Kristiansen, pp.9-32. J.R. Collis, Dorset, UK.
Kristiansen, Kristian and Carsten Paludan-Müller
1978 New Directions in Scandinavian Archaeology. Nationalmuseet, Copenhagen.
Krouse, H.R. and M.K. Herbert
1988 Sulphur and carbon isotope studies of food webs. In Diet and Subsistence:
Current Archaeological Perspectives, edited by B.V. Kennedy and G.M. LeMoine,
G.M., pp. 315-322. University of Calgary Archaeological Association, Calgary.
Krueger, H. W. and C.H. Sullivan
1984 Models for carbon isotope fractionation between diet and bone. In Stable Isotopes
in Nutrition, edited by J. F. Turnlund and P. E. Johnson, pp.205–222. ACS
Symposium Series 258, American Chemical Society, Washington, DC.
Kubiak-Martens, Lucyna
1999 The plant food component of the diet at the late Mesolithic (Ertebølle) settlement
at Tybrind Vig, Denmark. Vegetation History and Archaeobotany 8:117-127
2002 New evidence for the use of root foods in pre-agrarian subsistence recovered from
the late Mesolithic site at Halsskov, Denmark. Vegetation History and
Archaeobotany 11:23-31.
Kurlansky, Mark
1997 Cod: A Biography of the Fish that Changed the World. Penguin, New York.
Larsen, Charlotte Sedlacek
2000 En palaeoøkologisk rekonstruktion af den sen atlantiske kystboplads Smakkerup
Huse, Saltbaek Vig, NV-Sjaelland, Danmark, baseret på fiskeknoglemateriale.
Unpublished manuscript, Geological Institute: University of Copenhagen.
2005 Chapter 6: The Finds: Fish Bones and Shell. In Smakkerup Huse: A Late
Mesolithic Coastal Site in Northwest Zealand, Denmark, edited by T.D. Price and
A.B. Gebauer, pp.103-114. Aarhus University Press, Århus.
Larsson, Lars
1990 The Mesolithic of Southern Scandinavia. Journal of World Prehistory 4(3):257-
309.
Lee-Thorp, J.A.
2008 On Isotopes and Old Bones. Archaeometry 50(6):925-950.
Lee-Thorp, J. A., J.C. Sealy and N.J. van der Merwe
1989 Stable carbon isotope ratio differences between bone collagen and bone apatite,
and their relationship to diet. Journal of Archaeological Science 16:585–599.
Liden, Kerstin, Gunilla Eriksson, Bengt Nordqvist, Anders Götherström and Erik Bendixen
2004 ”The wet and the wild followed by the dry and the tame” – or did they occur at the
same time? Diet in Mesolithic-Neolithic southern Sweden. Antiquity 78:23-33.
Lillie, M.C. and K. Jacobs
2006 Stable isotope analysis of 14 individuals from the Mesolithic cemetery of
Vasilyevka II, Dnieper Rapids region, Ukraine. Journal of Archaeological Science
33:880-886.
Lillie, M., M.P. Richards and K. Jacobs
2003 Stable isotope analysis of 21 individuals from the Epipalaeolithic cemetery of
Vasilyevka III, Dnieper Rapids region, Ukraine. Journal of Archaeological Science
30:743-752.
Lindström, Susan
1996 Great Basin Fisherfolk: Optimal Diet Breadth Modeling the Truckee River
Aboriginal Subsistence Fishery. In Prehistoric Hunter-Gatherer Fishing Strategies,
edited by M.G. Plew, pp.114-79. Boise State University, Boise.
Liu, K. and I.R. Kaplan,
1989 The eastern tropical Pacific as a source of 15N-enriched nitrate in seawater off
southern California. Limnology and Oceanography 34(5):820–830.
Louwe Kooijmans, Leendert P.
1980 Archaeology and Coastal Change in the Netherlands. In Archaeology and Coastal
Change, edited by F.H. Thompson, pp.106-133. Society of Antiquaries, London.
2007 The Gradual Transition to Farming in the Lower Rhine Basin. Proceedings of the
British Academy 144:287-309.
Lubell, David, Mary Jackes, Henry Schwarcz, Martin Knyf and Christopher Meiklejohn
1994 The Mesolithic-Neolithic Transition in Portugal: Isotopic and Dental Evidence of
Diet. Journal of Archaeological Science 21:201-216.
Lyman, R. Lee
1991 Taphonomic problems with archaeological analysis of animal carcass utilization
and transport. In Beamers, bobwhites and blue-points: tributes to the career of
Paul W. Parmalee, edited by J. Purdue, W. Klippel and B. Styles, pp.125.138.
Illinois State Museum Scientific Papers vol. 23, Springfield.
1994 Vertebrate Taphonomy. Cambridge University Press, Cambridge.
2008 Quantitative Paleozoology. Cambridge University Press, Cambridge.
Madsen, A.P., S. Müller, C. Neergaard, C. Petersen, E. Rostrup, K. Steenstrup, & H. Winge
1900 Affaldsdynger fra Stenalderen i Danmark Undersøgte for Nationalmuseet. C.A.
Reitzel, Copenhagen.
Mansrud, Anna
2009 Animal bone studies and the perception of animals in Mesolithic society. In
Mesolithic Horizons, edited by S. McCartan, R. Schulting, G. Warren and P.
Woodman, pp.198-202. Oxbow Books, Oxford.
Marean, Curtis
1991 Measuring the post-depositional destruction of bone in archaeological
assemblages. Journal of Archaeological Science 18:677-694.
Marean, Curtis and L. Spencer
1991 Impact of carnivore ravaging on zooarchaeological measures of element
abundance. American Antiquity 56:645-658.
Marine Species Identification Portal
2009 The Marine Species Identification Portal is an initiative of ETI BioInformatics in the
Key to Nature programme (a project in the EC e-contentPlus Programme).
http://species-identification.org
Mason, Sarah
2005 Chapter 4: The Finds: Wood and Other Plant Remains. In Smakkerup Huse: A
Late Mesolithic Coastal Site in Northwest Zealand, Denmark, edited by T.D. Price
and A.B. Gebauer, pp.80-83. Aarhus University Press, Århus.
Mathiassen, Therkel
1935 Blubber Lamps in the Ertebølle Culture? Acta Archaeologica VI:139-152.
1937 Gudenaa-kulturen. En mesolitisk Inlandsbebyggelse i Jylland. Aarbøger for
Nordisk Oldkyndighed og Historie 1937:1-186.
1948 Danske Oldsager i Ældre Stenalder. København.
Mathiassen, Therkel, Magnus Degerbøl and J. Troels-Smith
1942 Dyrholmen: En Stenalderboplads paa Djursland. Det Kongelige Danske
Videnskabernes Selskab, Copenhagen.
Matsui, Akira
2007 Fundamentals of Zooarchaeology in Japan and East Asia. Kansai Process
Limited, Kyoto-shi, Japan.
McArdle, M., N.P. Liss, P. Dennis
1998 An isotopic study of atmospheric sulphur at three sites in Wales and at Mace
Head, Eire. Journal of Geophys. Res. Atmos. 103:31079-31094.
McCartan, Sinéad B., Rick Schulting, Graeme Warren and Peter Woodman.
2009 Mesolithic Horizons. Oxbow Books, Oxford.
McQuade, Melanie and Lorna O’Donnell
2009 The excavation of Late Mesolithic fish traps remains from the Liffey estuary,
Dublin, Ireland. In Mesolithic Horizons, edited by S. McCartan, R. Schulting, G.
Warren and P. Woodman, pp.889-894. Oxbow Books, Oxford.
Meiklejohn, Christopher, Erik Brinch Petersen and Verner Alexandersen
1998 The Later Mesolithic Population of Sjælland, Denmark, and the Neolithic
Transition. In Harvesting the Sea, Farming the Forest, edited by M. Zvelebil, L.
Domanska and R. Dennell, pp.203-212. Sheffield Academic Press, Sheffield.
Mellars, Paul and M.R. Wilkinson
1980 Fish Otoliths as Indicators of Seasonality in Prehistoric Shell Middens: the
Evidence from Oronsay (Inner Hebrides). Proceedings of the Prehistoric Society
46:19-44.
Melton, Nigel D. and Rebecca A. Nicholson
2007 A Late Mesolithic-Early Neolithic midden at West Voe, Shetland. In Shell Middens
in Atlantic Europe, edited by N. Milner, O. Craig and G. Bailey, pp.94-100. Oxbow
Books, Oxford.
Milner, Nicky
2002 Incremental Growth of the European Oyster Ostrea edulis. BAR International
Series 1057, Oxford.
Milner, Nicky, Oliver Craig and Geoffrey Bailey
2007 Shell Middens in Atlantic Europe. Oxbow Books, Oxford.
Milner, Nicky, Oliver Craig, Geoff Bailey, K. Pedersen and Søren H. Andersen
2004 Something fishy in the Neolithic? A re-evaluation of stable isotope analysis of
Mesolithic and Neolithic coastal populations. Antiquity 78:9-22.
Minagawa, M. and E. Wada
1984 Stepwise enrichment of 15N along food chains: further evidence and the relation
between δ15N and animal age. Geochimica et Cosmochimica Acta 48:1135-1140.
Miracle, Preston
2002 Mesolithic Meals from Mesolithic Middens. In Consuming passions and patterns of
consumption, edited by P. Miracle and N. Milner. Oxbow Books, Oxford.
Miracle, Preston and Nicky Milner
2002 Consuming passions and patterns of consumption. Oxbow Books, Oxford.
Morales, Arturo and Knud Rosenlund
1979 Fish Bone Measurements: An Attempt to Standardize the Measuring of Fish
Bones from Archaeological Sites. Steenstrupia, Copenhagen.
Moustgaard, Poul H.
1987 At vove for at vinde: Dansk fiskeri skildret af A.J. Smidth 1859-63. Dansk
Fiskerimuseum, Grenaa.
Muus, Bent J. and Preben Dahlstrøm
1964 Havfisk og Fiskeri. G.E.C. Gads Forlag, Copenhagen.
1967 Europas Ferskvands fisk. G.E.C. Gads Forlag, Copenhagen.
Møhl, Ulrik
1970 Oversigt over Dyreknoglerne fra Ølby Lyng. En østsjællandsk kystboplads med
Ertebøllekultur.Aarbøger for nordisk Oldkyndighet og Historie 1970:43-77.
1978 Aggersund-bopladsen Zoologisk Belyst: Svanejagt som Årsag til Bosættelse?
Kuml 1978:57-75.
Nagaoka, Lisa
2005 Differential recovery of Pacific Island fish remains. Journal of Archaeological
Science 32:941-955.
Nash, George
1998 Exchange, Status and Mobility: Mesolithic portable art of southern Scandinavia.
BAR International Series 710, Oxford.
Nichol, R.K. and C.J. Wild
1984 “Numbers of Individuals” in Faunal Analysis: the Decay of Fish Bone in
Archaeological Sites. Journal of Archaeological Science 11:35-51.
Nicholson, Rebecca A.
1992 An Assessment of the Value of Bone Density Measurements to Archaeological
Studies. International Journal of Osteoarchaeology 2:139-154.
1993 A Morphological Investigation of Burnt Animal Boneand an Evaluation of its Utility
in Archaeology. Journal of Archaeological Science 20:411-428.
1996a Fish bone diagenesis in different soils. Archaeofauna 5:79-91.
1996b Bone degradation, Burial Medium and Species Representation: Debunking the
Myths, An Experiment-based Approach. Journal of Archaeological Science
23:513-533.
1998 Bone Degradation in a Compost Heap. Journal of Archaeological Science 25:393-
403.
Nielsen, Jens and Anna Birgitte Gebauer
2005 Dugout Canoes. In Smakkerup Huse, A Late Mesolithic Coastal Site in Northwest
Zealand, Denmark, edited by T.D. Price and A. B. Gebauer. Aarhus University
Press, Aarhus.
Noe-Nygaard, Nanna
1971 Spurdog Spines from Prehistoric and Early Historic Denmark: An unexpected raw
material for precision tools. Bulletin of the Geological Society of Denmark 21:18-
33.
1987 Taphonomy in archaeology with special emphasis on man as a biasing factor.
Journal of Danish Archaeology 6:7-62.
1988 δ13C-values of dog bones reveal the nature of changes in man’s food resources
at the Mesolithic-Neolithic transition, Denmark. Chemical Geology (Isotope
Geoscience Section) 73:87-96.
Noe-Nygaard, Nanna, T. Douglas Price and Signe U. Hede
2005 Diet of aurochs and early cattle in southern Scandinavia: evidence from 15N and 13C stable isotopes. Journal of Archaeological Science 32:855-871.
O’Connor, T.P.
1996 A critical overview of archaeological animal bone studies. World Archaeology
28(1):5-19.
O’Leary, M.
1981 Carbon isotope fractionation in plants. Phytochemistry 20:553–567.
Olson, Carina
2008 Neolithic Fisheries: Osteoarchaeology of Fish Remains in the Baltic Sea Region.
Theses and Papers in Osteoarchaeology No. 5, Stockholm.
Olson, Carina, Karin Limburg and Mikael Söderblom
2008 Stone Age fishhooks – how were they dimensioned? Morphology, strength test,
and breakage pattern of Neolithic bone fishhooks from Ajvide, Gotland, Sweden.
Journal of Archaeological Science 35:2813-2823.
Olson, Carina and Yvonne Walther
2007 Neolithic cod (Gadidae) and herring (Clupea harengus) fisheries in the Baltic Sea,
in the light of fine-mesh sieving: a comparative study of subfossil fishbone from the
late Stone Age sites at Ajvide, Gotland, Sweden and Jettböle, Åland, Finland.
Environmental Archaeology 12(2):175-185.
Paludan-Müller, Carsten
1978 High Atlantic Food Gathering in Northwest Zealand, Ecological Conditions and
Spatial Representation. In New Directions in Danish Archaeology, edited by K
Kristiansen and C. Paludan-Müller, pp.120-157. National Museum, Copenhagen.
Parks, Rachel
2009 Seasonal resource scheduling in the Mesolithic and Neolithic of Scotland. In
Mesolithic Horizons, edited by S. McCartan, R. Schulting, G. Warren and P.
Woodman, pp.521-526. Oxbow Books, Oxford.
Passey, B. H., T.F. Robinson, L.K. Ayliffe, T.E. Cerling, M. Sponheimer, M.D. Dearing, B.L.
Roeder and J.R. Ehleringer
2005 Carbon isotope fractionation between diet breadth, CO2, and bioapatite in different
mammals. Journal of Archaeological Science 32:1459–1470.
Payne, S.
1972 Partial recovery and sample bias: the results of some sieving experiments. In
papers in economic prehistory, edited by E. Higgs, pp.49-64. Cambridge
University Press, Cambridge.
Pedersen, Lisbeth
1995 7000 years of fishing: stationary fishing structures in the Mesolithic and afterwards.
In Man and the Sea in the Mesolithic, edited by A. Fischer, pp.75-86. Oxbow
Books, Oxford.
1997 De satte hegn i havet. In Storebælt i 10.000 år, edited by L. Pedersen, A. Fischer
and B. Aaby, pp.124-143. A/S Storebæltsforbindelsen, Copenhagen.
Pedersen, Lisbeth, Anders Fischer and Bent Aaby
1997 Storebælt i 10.000 år. A/S Storebæltsforbindelsen, Copenhagen.
Perdikaris, Sophia
1999 From chiefly provisioning to commercial fishery: long-term economic change in
Arctic Norway. World Archaeology 30(3):388-402.
Perry, David
2005 Chapter 4: The Finds: Wood and Other Plant Remains. In Smakkerup Huse: A
Late Mesolithic Coastal Site in Northwest Zealand, Denmark, edited by T.D. Price
and A.B. Gebauer, pp.79-80. Aarhus University Press, Århus.
Petersen, Erik Brinch and Christopher Meiklejohn
2007 Historical Context of the Term ‘Complexity’ in the South Scandinavian Mesolithic.
Acta Archaeologica 78(2):181-192.
2003 Three cremations and a funeral: aspects of burial practice in Mesolithic Vedbæk.
In: Lars Larsson et al. (eds), Mesolithic on the Move, 485–93. Oxford.
Petersen, Peter Vang
1984 Chronological and Regional Variation in the Late Mesolithic of Eastern Denmark.
Journal of Danish Archaeology 3:7-18.
Peterson, B.J. and B. Fry
1987 Stable Isotopes in Ecosystem Studies. Annual Review Ecological Systems 18:293-
320.
Pickard, Catriona and Clive Bonsall
2004 Deep-sea Fishing in the European Mesolithic: Fact or Fantasy? European Journal
of Archaeology 7(3):273-290.
2007 Late Mesolithic coastal fishing practices: the evidence from Tybrind Vig, Denmark.
In On the Road: Studies in Honor of Lars Larsson, edited by B. Hårdh, K. Jennbert
and D. Olausson, pp.176-183. Almqvist and Wiksell, Stockholm.
Plew, Mark G.
1996 Prehistoric Hunter-Gatherer Fishing Strategies. Boise State University, Boise.
Poulsen, Rene Taudal, Andrew B. Cooper, Poul Holm and Brian R. MacKenzie
2007 An abundance estimate of ling (Molva molva) and cod (Gadidae) in the
Skagerrak and the northeastern North Sea, 1872. Fisheries Research 87:196-207.
Post, D.M.
2002 Using stable isotopes to estimate trophic position: models, methods, and
assumption. Ecology 83:703-718.
Prangsgaard, K.
1992 Introduktion af keramik i den yngre Ertebølle-kultur i Sydskandinavian. LAG 3:29-
52. Moesgård, Århus.
Price, T. Douglas
1987 The Mesolithic of Western Europe. Journal of World Prehistory 1(3):225-305.
2000 The Introduction of Farming in Northern Europe. In Europe’s First Farmers, edited
by T.D. Price, pp.260-300. Cambridge University Press, Cambridge.
2004 Beretning for udgravning af udsmidslag fra Ertebølle of tidlig neolitikum i Juli-
August 2002 og 2003. Odsherred Museum, Denmark.
Price, T. Douglas and Gary Feinman
1995 Foundations of Social Inequality. Plenum Press, New York.
Price, T. Douglas and Anne Birgitte Gebauer
1995 Last Hunters-First Farmers. School of American Research Press, Santa Fe.
2005 Smakkerup Huse, A Late Mesolithic Coastal Site in Northwest Zealand, Denmark.
Aarhus University Press, Aarhus, Denmark.
Price, T. Douglas, Anne B. Gebauer and Lawrence H. Keeley
1995 The Spread of Farming into Europe North of the Alps. In Last Hunters-First
Farmers, edited by T.D. Price and A.B. Gebauer, pp.95-126. School of American
Research Press, Santa Fe.
Privat, Karen L., Tamsin C. O’Connell, Robert E.M. Hedges
2007 The distinction between freshwater- and terrestrial-based diets: methodological
concerns and archaeological applications of sulphur stable isotope analysis.
Journal of Archaeological Science 34:1197-1204.
Rees, C.E., W.J. Jenkins and J. Monster
1978 The sulphur isotopic composition of ocean water sulphate. Geochimica et
Cosmochimica Acta 42:377-381.
Reitz, Elizabeth and Elizabeth Wing
1999 Zooarchaeology. Cambridge University Press, Cambridge.
Renouf, M.A.P.
1991 Sedentary Hunter-Gatherers: A Case for Northern Coasts. In Between Bands and
States, edited by S. A. Gregg, pp.89-107. Center for Archaeological
Investigations, Southern Illinois University at Carbondale Occasional Paper No. 9,
Carbondale, IL.
Reynard, Linda M. and Robert E.M. Hedges
2008 Stable hydrogen isotopes of bone collagen in palaeodietary and
palaeoenvironmental reconstruction. Journal of Archaeological Science 35:1934-
1942.
Richards, Michael P., T. Douglas Price and Eva Koch
2003 Mesolithic and Neolithic Subsistence in Denmark: New Stable Isotope Data.
Current Anthropology 44(2):288-295.
Richards, Michael P. and Robert E.M. Hedges
1999 Stable Isotope Evidence for Similarities in the Types of Marine Foods Used by
Late Mesolithic Humans at Sites Along the Atlantic Coast of Europe. Journal of
Archaeological Science 26:717-722.
Richards, Michael P. and P.A. Mellars
1998 Stable isotopes and the seasonality of the Oronsay middens. Antiquity 72:178-
184.
Richter, Jane
2005 Selective hunting of pine marten, Martes martes, in Late Mesolithic Denmark.
Journal of Archaeological Science 32:1223-1331.
Richter, Jane and Nanna Noe-Nygaard
2003 A Late Mesolithic Hunting Station at Agernæs, Fyn, Denmark: Differentiation and
Specialization in the late Ertebølle-Culture, heralding the Introduction of
Agriculture? Acta Archaeologica 74:1-64.
Rick, Torben C., Jon M. Erlandson and Rene L. Vellanoweth
2001 Paleocoastal Marine Fishing on the Pacific Coast of the Americas: Perspectives
from Daisy Cave, California. American Antiquity 66(4):595-613.
Ringrose, T.J.
1993 Bone Counts and Statistics: A Critique. Journal of Archaeological Science 20:121-
157.
Rosenlund, Knud
1976 Catalogue of subfossil Danish vertebrate – fishes. Zoologisk Museum,
Copenhagen.
Rossman, A., B. Kornexl, G. Versini, F. Pichlmayer and G. Lamprecht
1998 Origin assignment of milk from alpine regions by multielement stable isotope ratio
analysis (Sira). La Rivista di Scienza dell’Alimentazione 27:9-21.
Rostlund, Erhard
1952 Freshwater Fish and Fishing in Native North America. University of California
Press, Berkeley and Los Angeles.
Rowley-Conwy, Peter
1983 Sedentary hunters; the Ertebølle example. In Hunter-Gatherer Economy in
Prehistory, edited by G. Bailey, pp.111-126. Cambridge University Press,
Cambridge.
1984 The laziness of the short-distance hunter: the origins of agriculture in western
Denmark. Journal of Anthropological Archaeology 3:300-324.
1993 Season and Reason: The Case for a Regional Interpretation of Mesolithic
Settlement Patterns. In Hunting and Animal Exploitation in the Later Palaeolithic
and Mesolithic of Eurasia, edited by G.L. Peterkin, H.M. Bricker and P. Mellars,
pp.179-188. Archaeological Papers of the American Anthropological Association
Number 4, Washington, D.C.
1994 Meat, Furs and Skins: Mesolithic Animal Bones from Ringkloster, a Seasonal
Hunting Camp in Jutland. Journal of Danish Archaeology 12:87-98.
1998 Cemeteries, Seasonality and Complexity in the Ertebølle of Southern Scandinavia.
In Harvesting the Sea, Farming the Forest, edited by M. Zvelebil, L. Domanska
and R. Dennell, pp. 193-202. Sheffield Academic Press, Sheffield.
2004 How the West was Lost: A reconsideration of agricultural origins in Britain, Ireland,
and Southern Scandinavia. Current Anthropology 45:S83-113.
Russ, Hannah and Andrew K.G. Jones
2009 Late Upper Palaeolithic fishing in the Fucino Basin, central Italy, a detailed
analysis of the remains from Grotta di Pozzo. Environmental Archaeology
14(2):155-162.
Schoeninger, M. and M. DeNiro
1984 Nitrogen and carbon isotopic composition of bone collagen from marine and
terrestrial animals. Geochimica et Cosmochimica Acta 48:625-639.
Schmölcke, Ulrich, Elisabeth Endtmann, Stefanie Klooss, Michael Meyer, Dierk Michaelis,
Björn-Henning Rickert and Doreen Rößler
2006 Changes of sea level, landscape and culture: A review of the south-western Baltic
area between 8800 and 4000B.C.. Palaeogeography, Palaeoclimatology and
Palaeoecology 240:423-438.
Schmölcke, Ulrich, Glykou, Aikatrina, Heinrich, Dirk
2009 Faunal development in the southwestern Baltic area. Berichte der Römisch-
Germanischen Kommission 88:241-253.
Sealy, J.C., N.J. Van der Merwe, J.A. Lee-Thorp and J.L. Lanham
1987 Nitrogen isotope ecology in southern Africa: implications for environmental and
dietary tracing. Geochimica et Cosmochimica Acta 51:2707-2717.
Shaffer, B.S.
1992 Quarter Inch Screening: Understanding Biases in Recovery of Vertebrate Faunal
Remains. American Antiquity 57:129-136.
Shennan, Stephen
2002 Genes, Memes and Human History: Darwinian Archaeology and Cultural
Evolution. Thames and Hudson, London.
Simms, Steven R.
1987 Behavioral Ecology and Hunter-Gatherer Foraging. BAR International Series 381,
Oxford.
Skaarup, Jørgen
1973 Hesselø-Sølager: Jagtstationen der südskandinavischen Trichterbecherkultur.
Akademisk Forlag, Copenhagen.
1983 Submarine stenalderbopladser I det sydfynske øhav. Antikvariske Studier 6:137-
161.
1995 Hunting the hunters and fishers of the Mesolithic: twenty years of research on the
sea floor south of Funen, Denmark. In Man and the Sea in the Mesolithic, edited
by A. Fischer, pp.397-401. Oxbow Books, Oxford.
Smart, David J.Q.
2003 Later Mesolithic Fishing Strategies and Practices in Denmark. BAR International
Series No.1119, Oxford.
Smith, Bruce and Eric A. Winterhalder
1981 New Perspectives on Hunter-Gatherer Socioecology. In Hunter-Gatherer Foraging
Strategies: Ethnographic and Archaeological Analyses, edited by B. Winterhalder
and E. Smith, pp.1-12. University of Chicago Press, Chicago.
Smith, B. N., and S. Epstein
1971 Two categories of 13C/12C ratios for higher plants. Plant Physiology 47:380–384.
Sosis, Richard
2000 Costly signaling and torch fishing on Ifaluk atoll. Evolution and Human Behavior
21:223-244.
Stafford, Michael
1999 From Forager to Farmer in Flint. Aarhus University Press, Aarhus.
Steward, Julian
1955 Theory of culture change. University of Illinois Press, Urbana.
Stiner, Mary
1992 Overlapping species “choice” by Italian Upper Pleistocene predators. Current
Anthropology 33:433-451.
Street, Martin, Michael Baales, Erwin Cziesla, Sönke Hartz, Martin Heinen, Olaf Jöris, Ingrid
Koch, Clemens Pasda, Thomas Terberger, and Jürgen Vollbrecht
2001 Final Palaeolithic and Mesolithic Research in Reunified Germany. Journal of World
Prehistory 15(4):365-453.
Sørensen, Søren
1992 Lollikhuse – a Dwelling Site under a Kitchen Midden. Journal of Danish
Archaeology 11:19-29.
Tauber, H.
1981 13C evidence for dietary habits of prehistoric man in Denmark. Nature 292:332-
333.
Testart, Alain
1982 The Significance of Food Storage among Hunter-Gatherers: Residence Patterns,
Population Densities, and Social Inequalities. Current Anthropology 23(5):523-537.
Thomas, D.H.
1969 Great Basin Hunting Patterns: A Quantitative Method for Treating Faunal
Remains. American Antiquity 34:392-401.
Thomsen, Christian Jürgensen
1836 Ledetraad til nordisk Oldkyndighed. S.L. Møllers, Copenhagen.
Trolle-Lassen, Tine
1984 A preliminary report on the archaeological and zoological evidence of fish
exploitation from a submerged site in Mesolithic Denmark. C.N.R.S. Centre de
Recherches Archéologiques. Notes et Monographies Technigues 16, 133-143.
1987 Human exploitation of fur animals in Mesolithic Denmark – a case study.
Archaeozoologia 1(2):85-102.
Vale, Deborah and Robert Gargett
2002 Size Matters: 3mm Sieves do not Increase Richness in a Fishbone Assemblage
from Arrawarra I, an Aboriginal Shell Midden on the Mid-north Coast of New South
Wales, Australia. Journal of Archaeological Science 29:57-63.
van der Merwe, N. J. and J. C. Vogel
1978 13C content of human collagen as a measure of prehistoric diet in Woodland North
America. Nature 276:815–816.
Van Neer, W., A. Ervynck, L. Bolle and R. Milner
2004 Seasonality Only Works in Certain Parts of the Year: the Reconstruction of Fishing
Seasons through Otolith Analysis. International Journal of Osteoarchaeology
14:457-474.
Vitale, F., P. Börjesson, H. Svedäng and M. Casini
2008 The spatial distribution of cod (Gadidae L.) spawning grounds in the Kattegat,
eastern North Sea. Fisheries Research 90:36-44.
Westerby, Erik
1927 Stenalderbopladser ved Klampenborg. Nogle Bidrag til Studiet af den mesolitiske
Periode. Copenhagen.
Wheeler, A. and A. K. G. Jones
1989 Fishes. Cambridge University Press, Cambridge.
Wieland, Kai, Eva Maria Fenger Pedersen, Hans J. Olesen, Jan E. Beyer
2009 Effect of bottom type on catch rates of North Sea cod (Gadus morhua) in surveys
with commercial fishing vessels. Fisheries Research 96:244-251.
Willis, Lauren, Metin Eren and Torben Rick
2007 Does butchering fish leave cutmarks? Journal of Archaeological Science 35:1438-
1444.
Winge, Herluf
1900 Knogler af Dyr. In Affaldsdynger fra Stenalderen i Danmark, Madsen et al.,
Copenhagen.
Winterhalder, Bruce
1981 Optimal Foraging Strategies and Hunter-Gatherer Research in Anthropology:
Theory and Models. In Hunter-Gatherer Foraging Strategies, edited by B.
Winterhalder and E. Smith, pp.13-35. University of Chicago Press, Chicago.
Winterhalder, Bruce and Eric Alden Smith
1981 Hunter-Gatherer Foraging Strategies. University of Chicago Press, Chicago.
2000 Analyzing Adaptive Strategies: Human Behavioral Ecology at Twenty-Five.
Evolutionary Anthropology 51-72.
Woodman, Peter
2000 Getting back to basics: transitions to farming in Ireland and Britain. In Europe’s
First Farmers, edited by T.D. Price, pp.219-259. Cambridge University Press,
Cambridge.
Woodman, Peter, Elizabeth Anderson and Nyree Finlay
1999 Excavations at Ferriter’s Cove, 1983-95: last foragers, first farmers in the Dingle
Peninsula. Wordwell, Bray, Ireland.
Yesner, David
1980 Maritime Hunter-Gatherers: Ecology and Prehistory. Current Anthropology
21(6):727-750.
Zapata, Lydia, Nicky Milner and Eufrasia Rosello
2007 Pico Ramos cave shell midden: the Mesolithic-Neolithic transition by the Bay of
Biscay. In Shell Middens in Atlantic Europe, edited by N. Milner, O. Craig and G.
Bailey, pp.150-157. Oxbow Books, Oxford.
Zohar, Irit and Miriam Belmaker
2005 Size does matter: methodological comments on sieve size and species richness in
fishbone assemblages. Journal of Archaeological Science 32:635:641.
Zvelebil, Marek
1996 The Agricultural Frontier and the transition to farming in the circum-Baltic region.
In The Origins and Spread of Agriculture and Pastoralism in Eurasia, edited by D.
R. Harris. Smithsonian Institution Press, Washington D.C.
2006 Mobility, contact, and exchange in the Baltic Sea basin 6000–2000 B.C.. Journal
of Anthropological Archaeology 25:178-192.
Zvelebil, Marek, Lucyna Domanska and Robin Dennell
1998 Harvesting the Sea, Farming the Forest. Sheffield Academic Press, Sheffield.
Aaby, B.
1993 Flora. In Digging into the Past, edited by S. Hvass and B. Storgaard, pp.24-27.
Jysk Arkæologisk Selskab, Århus.
Åhrberg, Eva Schaller
2007 Fishing for storage: Mesolithic short term fishing for long term consumption. In
Shell Middens of Atlantic Europe, edited by N. Milner, O. Craig and G. Bailey,
pp.46-53. Oxbow Books, Oxford.
Åkerlund, Agneta
2000 Separate Worlds? Interpretation of the Different Material Patterns of the
Archipelago and the Surrounding Mainland Areas of East-Central Sweden in the
Stone Age. European Journal of Archaeology 3(1):7-29.
Appendix I Notes on fish taxonomy and identification
(Except where noted, this information is from: Muus and Dahlstrøm 1964, 1967; Marine Species
Identification Portal.)
Gadidae
Identified in Ertebølle assemblages
Cod (Gadidae), haddock (Melanogrammus aeglefinus), pollack (Pollachius pollachius), saithe
(Pollachius virens), ling (Molva molva) and whiting (Merlangius merlangus)
Other members of this family that occur in Danish waters
Poor cod (Trisopterus minutes), Norway pout (Trisopterus esmarki), blue whiting
(Micromesistius poutassou), tadpole-fish (Raniceps raninus), hake (Merluccius merluccius),
torsk (Brosme brosme)
Elements that are commonly used to distinguish between members of this family include otolith,
vomer, parasphenoid, maxillary, premaxillary, dentary and first or second vertebrae (Enghoff
1994). In attempts to separate elements from these species, it is generally necessary for the
specimen to be mostly complete and undamaged. Because of this, in many cases the majority
of specimens can only be assigned to the family Gadidae, severely limiting the ability to quantify
differences in the species composition of gadid remains between sites. Size information is
normally provided from measurements of otoliths or first and second vertebrae, although other
elements are also potentially useful for this purpose (Enghoff 1994a, Härkönen 1986, Morales
and Rosenlund 1979).
Pleuronectidae
Identified in Ertebølle assemblages
Flounder (Platichthys flesus), plaice (Pleuronectes platessa) and dab (Limanda limanda)
Other members of this family that occur in Danish waters
Halibut (Hippoglossus hippoglossus), long rough dab (Hippoglossoides platessoides), lemon
sole (Microstomus kitt), and witch (Glyptocephalus cynoglossus)
Elements of these fish that can be used to distinguish species include dermal denticles (only
present in flounder), urohyal, frontal, and pteroticum (Enghoff 1994a). Size information is
derived from measurements of the first vertebra or os anale (Enghoff 1994a).
Halibut, which can be amongst the largest of flatfishes (Denmark’s record is 5.3 kg), is curiously
absent from Ertebølle assemblages in Denmark (although one vertebra has been identified from
a Kongemose site – Carstensminde), despite the belief that they were once much more
common in the Kattegat than they are today (Drechsel 1890:194; Purnell et al. 2004).
Scophthalmidae
Identified in Ertebølle assemblages
Turbot (Psetta maxima) and brill (Scophthalmus rhombus)
Other members of this family that occur in Danish waters
Norwegian topknot (Phrynorhombus norvegicus) and topknot (Zeugopterus punctatus)
Two other families of the order Pleuronectiformes are present in Danish waters today, but
have not been identified from Ertebølle sites:
Bothidae
Scaldfish (Arnoglossus laterna)
Soleidae
Common sole (Solea solea) and solenette (Buglossidium luteum)
The absence of sole is especially interesting, as they have been of some commercial
importance dating back to at least the 1800s (Drechsel 1890).
Because of the very small number of Scophthalmidae recovered, they are included with
Pleuronectidae for quantification purposes.
Anguillidae
Identified in Ertebølle assemblages
Eel (Anguilla anguilla)
Size estimates can be made based on dentale, cleithrum, and ceratohyal (Enghoff 1994).
Cyprinidae
Identified in Ertebølle assemblages
Common bream (Abramis brama), tench (Tinca tinca), roach (Rutilus rutilus) and rudd
(Scardinius erythrophthalmus), crucian carp (Carassius carassius), white bream (Blicca
bjoerkna)
Other members of this family that occur in Danish waters
This is a large family of fishes, however only the species listed above are likely to have been
exploited by humans because of the small size of the other members.
Species specific elements include the basioccipital and pharyngeal bone, and sometimes, the
opercle (Enghoff 1994a). Fish size estimates for tench can be derived from measurement of the
opercle. For roach, it can be derived from measurement of the first and second vertebrae – but
as these are not species specific elements, in most cases size estimates for cyprinids must
come from comparison with comparative specimens of known size (Enghoff 1994a).
Triglidae
Identified in Ertebølle assemblages
Grey gurnard (Eutrigla gurnardus) and tub gurnard (Trigla lucerna)
Although often difficult to distinguish between elements of the two species (dorsal plates are an
exception), there are fortunately no other members of the family likely to be present. It seems
that grey gurnard is more common where species identification is possible.
Cottidae
Identified in Ertebølle assemblages
Bull-rout (Myoxocephalus scorpius)
Other members of this family that occur in Danish waters
Fatherlasher (Taurulus bubalis) and Norway bullhead (Micrenophrys lilljeborgii)
Salmonidae
Identified in Ertebølle assemblages
Sea trout (Salmo trutta), Atlantic salmon (Salmo salar) and whitefish (Coregonus sp.)
While whitefish are somewhat distinct, trout and salmon are very difficult to separate based on
osteological evidence. In any case, all three species are uncommon, even in the assemblages
where they are present.
Clupeidae
Identified in Ertebølle assemblages
Herring (Clupea harengus), shad (Alosa alosa and Alosa fallax)
Other members of this family that occur in Danish waters
Sprat (Sprattus sprattus)
Engraulidae
Identified in Ertebølle assemblages
Anchovy (Engraulis encrasicholus)
Belonidae
Identified in Ertebølle assemblages
Garfish (Belone belone)
Syngnathidae
Identified in Ertebølle assemblages
Pipefish (Syngathidae sp.)
Gasterosteidae
Identified in Ertebølle assemblages
Three-spined stickleback (Gasterosteus aculeatus), fifteen-spined stickleback (Spinachia
spinachia)
Other members of this family that occur in Danish waters
Nine-spined stickleback (Pungitius pungitius)
Esocidae
Identified in Ertebølle assemblages
Pike (Esox lucius)
Zoarcidae
Identified in Ertebølle assemblages
Viviparous eelpout (Zoarces viviparous)
Siluridae
Identified in Ertebølle assemblages
Wels (Siluris glanis)
The order of Perciformes is a very large group of fishes, comprised of multiple suborders,
families and genera. Members of this group that are of interest archaeologically for the Danish
Ertebølle include: gobiids, dragonets, mackerel, Atlantic horse mackerel, perch, pike-perch,
sand-eels, weever, black sea bream, swordfish and European sea bass. Generally speaking, it
is possible to distinguish elements of these fish from each other with little difficulty, but this is
less true when other members of the order that are potentially present are included.
Gobiidae
Fish of the goby family, are represented by many genera, and many species within those
genera. They are rare in Danish Mesolithic assemblages, so reporting them at the level of family
(at least for quantification) is appropriate. The author’s gobiid identifications compared favorably
with Gobius niger, although it should be noted that the specimen in the collection at the
Landesmuseum in Schleswig that was used for comparison is an archaeological example from
the Viking age site of Hedeby (aka Haithabu).
Callionymidae
Identified in Ertebølle assemblages
Dragonet (Callionymus lyra)
Scombridae
Identified in Ertebølle assemblages
Mackerel (Scomber scombrus)
Carangidae
Identified in Ertebølle assemblages
Atlantic horse mackerel (Trachurus trachurus)
Percidae
Identified in Ertebølle assemblages
Perch (Perca fluviatilis), zander (Sander lucioperca), ruffe (Gymnocephalus cernua)
Ammodytidae
Sand eel (any of a number of members of the genera Ammodytes and Hyperoplus)
Trachinidae
Identified in Ertebølle assemblages
Greater weever (Trachnius draco)
Sparidae
Black sea bream (Spondyliosoma cantharus)
Xiphiidae
Swordfish (Xiphias gladius)
Moronidae
European sea bass (Dicentrarchus labrax)
A final group of fish to be included would be the non-bony fishes (the class Chondrichthyes)
that are nevertheless sometimes identified in archaeological assemblages, either from ossified
skeletal elements, teeth, dermal denticles or tail spines. With the exception of spurdog (Squalus
acanthias, family Squalidae), elements from these fish are quite rare on Mesolithic sites. Other
sharks that are found include porbeagle (Lamna nasus), topeshark (Galeorhinus galeus) and
smoothhound (Mustelus sp.), while rays consist of thornbacks (Raja clavata) and common
stingrays (Dasyatis pastinaca). Spurdog are relatively easily recognized by their distinctive
vertebrae and dorsal spines. The other fish of this class are so uncommon that they are of little
consequence for assemblage quantification, with the exception of generating NTAXA. It might
be efficient to consider the entire class together, but family is useful for so many of the other fish
that it might be used for the sake of uniformity (with smoothhound and topeshark in Triakidae,
porbeagle in Lamnidae, spurdog in Squalidae, thornback rays in Rajidae and common stingray
in Dasyatidae).
Appendix II
Comparative collection prepared for the project
English Danish
1. Anarhichas lupus Wolffish Havkat
2. Anguilla anguilla Eel Ål
3. Belone belone Garfish Hornfisk
4. Centrolabrus exoletus Rock cook Småmundet gylte
5. Chimaera monstrosa Ghost shark Havmus
6. Clupea harengus Herring Sild
7. Coregonus sp. Whitefish Helt
8. Ctenolabrus rupestris Goldsinny wrasse Havkaruds
9. Dicentrarchus labrax Sea bass Havbars
10. Engraulis encrasicolus Anchovy Ansjos
11. Esox lucius Pike Gedde
12. Esox lucius Pike Gedde
13. Eutrigla gurnardus Grey gurnard Grå knurhane
14. Eutrigla gurnardus Grey gurnard Grå knurhane
15. Gadus morhua Cod Torsk
16. Gadus morhua Cod Torsk
17. Gadus morhua Cod Torsk
18. Limanda limanda Dab Ising
19. Melanogrammus aeglefinus Haddock Kuller
20. Merlangius merlangus Whiting Hvilling
21. Merlangius merlangus Whiting Hvilling
22. Merlangius merlangus Whiting Hvilling
23. Microstomus kitt Lemon sole Rødtunge
24. Molva molva Ling Lange
25. Myoxocephalus scorpius Bullrout Almindelig ulk
26. Osmerus eperlanus Smelt Smelt
27. Pholis gunnellus Butterfish Tangspræl
28. Platichthys flesus Flounder Skrubbe
29. Pleuronectes platessa Plaice Rødspætte
30. Pollachius pollachius Pollock Lubbe
31. Psetta maxima Turbot Pighvarre
32. Salmo salar Salmon Laks
33. Salmo trutta Sea trout Ørred
34. Sander vitreus Walleyed pike cf. Sandart
35. Sardina pilchardus Sardine Sardin
36. Scomber scombrus Mackerel Makrel
37. Sebastes marinus Redfish Rødfisk
38. Sparidae Sea bream Dorade
39. Spinachia spinachia 15 spined stickleback Tangsnarre
40. Squalus acanthias Spurdog Pighaj
41. Syngnathus sp. Pipefish Tangnål
42. Trachinus draco Greater weever Fjæsing
43. Trachnius draco Greater weever Fjæsing
44. Trachurus trachurus Horse mackerel Hestemakrel
45. Trachurus trachurus Horse mackerel Hestemakrel
46. Trigla lucerna Tub gurnard Rød knurhane
47. Zoarces viviparous Eelpout Ålekvabbe
Gadid
ae
Anguill
idae
Ple
uro
nectidae
Cott
idae
Scom
bridae
Clu
peid
ae
Triglid
ae
Belo
nid
ae
Squalid
ae
Tra
chnid
ae
Zoarc
idae
Salm
onid
ae
Cyprinid
ae
Calli
onym
idae
First vertebra 831 18 28 22 0 5 4 1 0 1 0 0 0 0
Other vertebra 31763 3591 830 475 444 162 106 40 30 32 18 13 8 1
Total vertebra 32594 3609 858 497 444 167 110 41 30 33 18 13 8 1
Angular 645 35 2 5
Branchiostegal ray 38
Ceratohyal 76 90
Cleithrum 168 40 1
Cranium, unsp. 1 1
Dentale 236 34 3 4
Dorsal spine/plate 14 10
Ectopterygoid 76 6
Epibranchial 55
Epihyal 39 25
Exoccipital 21
Frontal 4
Hyomandibular 210 17 4 2
Hypohyal 5
Interhyal 13
Interopercle 10
Maxillary 473 21 2 10 2
Mesethmoid 25
Opercle 31 9 19 1
Opisthotic 9
Os anale 7
Otolith 889
Palatine 54 1
Parasphenoid 330 4 8 3
Pharyngeal plate 13 1
Pharyngobranchial 5
Postcleithrum 2
Posttemporal 401 3 2 1
Premaxillary 457 3
Preopercle 22 16
Prooticum 4
Pterotic 53
Quadrate 546 17 9 11 2 1
Retroarticular 9
Sphenotic 71
Subopercle 2
Supracleithrum 273 3 17
Supraoccipital 3
Symplectic 72
Urohyal 2 4
Vomer (left half) 72
Vomer (right half) 64
Vomer (whole) 43 44 1 1
Total non-vertebra 5509 340 40 104 0 4 26 4 10 1 0 0 0 0
Total 38103 3949 898 601 444 171 136 45 40 34 18 13 8 1
Identified fish specimens from Asnæs Havnemark.
Gadid
ae
Ple
uro
nectidae
Belo
nid
ae
Cott
idae
Anguill
idae
Scom
bridae
Squalid
ae
Tra
chnid
ae
Clu
peid
ae
Sparidae
First vertebra 45 15 0 6 0 0 0 0 0 0
Other vertebra 1289 890 103 50 20 20 15 12 2 1
Total vertebra 1334 905 103 56 20 20 15 12 2 1
Angular 3 1
Branchiostegal ray 1
Cranium, unsp. 1
Dentary 9 8 1
Hyomandibular 2 2
Maxillary 12 4
Mesethmoid 1
Os anale 3
Palatine 1
Parasphenoid 7
Posttemporal 8 1
Premaxillary 42
Pterotic 1 1
Quadrate 2
Sphenotic 1
Supracleithrum 5
Symplectic 1
Vomer (left half) 2
Vomer (right half) 3
Vomer (whole) 1
Total non-vertebra 102 13 8 1 0 0 0 0 0 0
Total 1436 918 111 57 20 20 15 12 2 1 Identified fish specimens from Bøgebjerg.
Gadid
ae
Ple
uro
nectidae
Belo
nid
ae
Squalid
ae
Cott
idae
Scom
bridae
Anguill
idae
Tra
chnid
ae
Triglid
ae
Clu
peid
ae
Zoarc
idae
Salm
onid
ae
Perc
idae
Esocid
ae
Cyprinid
ae
First vertebra 885 275 15 31 9 7 4 3
Other vertebra 19059 9169 660 680 498 458 307 148 136 88 14 11 5 4 2
Total vertebra 19944 9444 675 680 529 458 316 155 140 91 14 11 5 4 2
Angular 407 15 2
Basibranchial 3
Branchiostegal ray 20
Ceratobranchial 1 1
Ceratohyal 53 11 1
Cleithrum 34 2 3
Cranium, unsp. 8 1
Dentale 272 8 190 2 1
Dorsal spine/plate 42 7
Ectopterygoid
Epibranchial 36
Epihyal 23
Exoccipital 2 1
Frontal 3 2
Hyomandibular 90 17 2
Hypohyal 3 2
Interhyal 4
Interopercle 1
Maxillary 426 17 2 1 1
Mesethmoid 5
Opercle 9 1 1 1 1
Opisthotic 2
Os anale 52
Otolith 2142
Palatine 21 9
Parasphenoid 226
Pharyngeal plate 7
Pharyngobranchial 4 2
Posttemporal 319 20 1
Premaxillary 917 6 1
Preopercle 16 1 2
Prootic 3 14
Pterotic 6 21
Quadrate 437 35 1 2
Retroarticular 1
Sphenotic 27
Supracleithrum 241 11 2 1
Supraoccipital 1
Symplectic 3
Urohyal 19 1
Vomer (left half) 105
Vomer (right half) 123
Vomer (whole) 31 25 6
Total non-vertebra 6021 276 190 42 11 0 26 9 10 14 0 0 0 0 0
Total 25965 9720 865 722 540 458 342 164 150 105 14 11 5 4 2
Identified fish specimens from Dragsholm.
Gadid
ae
Ple
uro
nectidae
Anguill
idae
Belo
nid
ae
Clu
peid
ae
Cyprinid
ae
Esocid
ae
Cott
idae
Scom
bridae
Squalid
ae
Salm
onid
ae
First vertebra 29 21 1 0 0 0 0 0 0 0 0
Other vertebra 1244 939 46 15 8 7 2 2 2 0 1
Total vertebra 1273 960 47 15 8 7 2 2 2 0 1
Angular 25 2
Ceratohyal 5 5
Cleithrum 12 5 6
Dentale 16 1 3 2 1
Dorsal spine/plate 1
Ectopterygoid 2 2
Epibranchial 2
Epihyal 1 2 1
Hyomandibular 2 7 2
Hypohyal 1 1
Interhyal 1
Maxillary 32 2
Opercle 1
Os anale 22
Otolith 39
Palatine 2
Parasphenoid 18 4 5
Pharyngeal plate 1
Pharyngobranchial 2
Postcleithrum 3
Posttemporal 15 5
Premaxillary 68 1
Pterotic 3
Quadrate 23 7 3
Retroarticular 1
Supracleithrum 10 7
Symplectic 5
Urohyal 7
Vomer (left half) 7
Vomer (right half) 10
Vomer (whole) 4 4 2
Total non-vertebra 307 83 27 2 0 0 1 0 0 1 0
Total 1580 1043 74 17 8 7 3 2 2 1 1 Identified fish specimens from Fårevejle.
An
gu
illid
ae
Ple
uro
ne
ctid
ae
Tra
ch
inid
ae
Ga
did
ae
Sa
lmo
nid
ae
Be
lon
ida
e
Clu
pe
ida
e
Zo
arc
ida
e
Co
ttid
ae
First vertebra 4 1
Other vertebra 175 19 15 13 11 11 9 2 1
Total vertebra 179 20 15 13 11 11 9 2 1
Angular 6 1
Ceratohyal 11
Cleithrum 17
Dentale 4 1
Epihyal 2
Frontal 4
Hyomandibular 4
Maxillary 1
Opercle 3
Os anale 3
Palatine 1
Parasphenoid 3
Posttemporal 1
Quadrate 3
Vomer (whole) 4
Total non-vertebra 61 6 1 1 0 0 0 0 0
Total 240 26 16 14 11 11 9 2 1
Identified fish specimens from Havnø.
Tra
ch
inid
ae
Ple
uro
ne
ctid
ae
An
gu
illid
ae
Ga
did
ae
Sq
ua
lid
ae
Clu
pe
ida
e
Co
ttid
ae
Tri
glid
ae
Total vertebra 14 5 3 2 3 1 1 0
Basipterygium 1
Cleithrum 1
Epihyal 1
Maxillary 1
Opercle 3
Preopercle 2
Total non-vertebra 5 1 1 1 0 0 0 1
Total 19 6 4 3 3 1 1 1
Identified fish specimens from Jesholm I.
Ple
uro
nectidae
Gadid
ae
Belo
nid
ae
Anguill
idae
Scom
bridae
Clu
peid
ae
Squalid
ae
Triglid
ae
First vertebra 43 12 3
Other vertebra 1790 358 262 68 24 13 1
Total vertebra 1833 370 265 68 24 13 0 1
Angular 6
Ceratohyal 3
Cleithrum 9
Dentale 1
Dorsal spine/plate 3
Maxillary 5
Os anale 44
Parasphenoid 1
Posttemporal 2
Premaxillary 12
Pterotic
Quadrate 1
Supracleithrum 3
Urohyal 3
Vomer (whole) 2
Total non-vertebra 47 33 0 12 0 0 3 0
Total 1880 403 265 80 24 13 3 1 Identified fish specimens from Lollikhuse.
Ple
uro
nectidae
Anguill
idae
Tra
chin
idae
Gadid
ae
Clu
peid
ae
Zoarc
idae
Scom
bridae
Cott
idae
Salm
onid
ae
Gaste
roste
idae
First vertebra 158 30 60 17 32 1
Other vertebra 5266 2432 1981 1231 786 221 30 21 21 4
Total vertebra 5424 2462 2041 1248 818 221 30 22 21 4
Angular 21 15 17 29
Branchiostegal ray 14
Ceratohyal 2 59 8 1
Cleithrum 3 36 7 8
Dentale 5 12 13 30
Ectopterygoid 31 1
Epibranchial 7
Epihyal 10 13 4 14
Frontal 7 4
Hyomandibular 18 9 26 6
Hypohyal 4 2
Interhyal 4
Interopercle 2
Maxillary 65 20 51
Mesethmoid 4 3
Opercle 5 42 7
Os anale 69
Otolith 2 59
Palatine 32 9 21
Parasphenoid 1 5 15 22
Pharyngeal plate 5
Pharyngobranchial 12 3
Postcleithrum 1
Posttemporal 12 30 23
Premaxillary 37 17 53
Prootic 21
Pterotic 4
Quadrate 45 12 29 26
Sphenotic 7
Subopercle 1
Supracleithrum 53 8 34
Symplectic 4
Urohyal 67
Vomer (left half) 10
Vomer (right half) 9
Vomer (whole) 46 26 17 2
Total non-vertebra 543 199 271 454 21 0 0 0 0 0
Total 5967 2661 2312 1702 839 221 30 22 21 4
Identified fish specimens from Nederst skaldynge I.
Appendix IV
Complete notes for analyzed assemblages
Årby Sb 365 Asnæs Havnemark
125E 128N Culture Layer Trench 1 21June2007 VLS Weight: <1g Cod family 1 vertebra C 125E 131N Culture Layer Trench 1 22June2007 KJG Weights: <1g otoliths, 2g fragments no ID, 1g vertebra no ID, 1g non-vertebra, 14g cod, <1g other vertebra Cod family 1 basioccipital 5 first vertebra 13 second vertebra 13 third vertebra 116 vertebra C (2 burnt) 31 vertebra B 10 vertebra A 2 otoliths 1L 2R posttemporal 1R supracleithrum (burnt) 1R ectopterygoid 1R quadrate 1L ceratohyal 1R pterotic Flatfish 1 first vertebra (3.9mm) 3 vertebra C Eel 1 vertebra C Bull-rout 2 vertebra C Gurnard 1 vertebra C Unidentified 6 vertebra C (1 burnt) 6 vertebra B 126E 131N Culture Layer Trench 1 Partial square, western half 25June2007 KJG Weights: 1g vertebra no ID, 3g fragments no ID, 3g non-vertebra, 29g cod, <1g other vertebra Cod family 3 basioccipital 13 first vertebra 26 second vertebra (1 burnt) 11 third vertebra 220 vertebra C 65 vertebra B 24 vertebra A 2 parasphenoid (1 fragment) 1L dentary 3R maxillary (1 fragment) 1L 2 whole vomer (2 whole are burnt) 2L 1R premaxillary 1L 1R quadrate (2 fragment) 2L 2R angular (1 burnt) 1R posttemporal Flatfish 7 vertebra C 1 vertebra B Eel 3 vertebra C Bull-rout 1 vertebra C 1 vertebra B Gurnard 2 vertebra C Unidentified 4 vertebra too dirty 3 vertebra C 2 vertebra B (nothing identifiable, so not kept separate)
125E 132N Culture Layer Trench 1 22June2007 TLS Weights: 6g otoliths, 24g fragments no ID, 13g non-vertebra, 5g vertebra no ID, 129g cod, 5g other vertebra Cod family 23 basioccipital 52 first vertebra (1 burnt) 72 second vertebra (2 burnt) 57 third vertebra 1276 vertebra C 306 vertebra B 97 vertebra A 9L 9R premaxillary (3 fragment) 2L 2R dentary 4L 1R 1 whole vomer (3 burnt) 9L 7R maxillary (2 frag. 5 burnt) 8 parasphenoid (2 frag. 2 burnt) 1L 1R cleithrum 2L 3R hyomandibular 7L 7R posttemporal (2 burnt) 12L 16R angular (2 frag. 1 burnt) 2R supracleithrum (1 burnt) 8L 9R quadrate (2 burnt) 1 mesethmoid 1L opercle 1L palatine (burnt) 1L pteroticum 1L interhyal 1 R opisthotic 89 otoliths & 15 fragments Flatfish 4 first vertebra (3.3, 4.2, 4.2, 5.4mm) 4 vertebra B 30 vertebra C (includes at least one turbot) 1 ectopterygoid (burnt) Eel 2 first vertebra 11 vertebra C (1 burnt) 1 vertebra B 1R anguloarticulare 1R cleithrum 1L ceratohyal (1.9mm) Bull-rout 1 first vertebra (4.1mm) 13 vertebra C 1 parasphenoid 1L preopercle 1 supracleithrum Mackerel 1 vertebra B 1 vertebra A Spurdog 2 vertebra C 1 dorsal spine Garfish 2 vertebra C 1 fragment dentary Trout/salmon 1 vertebra B Gurnard 1 first vertebra 6 vertebra C 1 vertebra B 1R opercle 1R posttemporal (grey gurnard) Weever 2 vertebra C Unidentified 29 vertebra too dirty 8 vertebra C 18 vertebra B 125E 132N Culture Layer Trench 1 25June2007 TLS Bag 2 Weights: 2g otoliths, 4g non-vertebra, 2g fragments no ID, 1g vertebra no ID, 31g cod, 1g other vertebra Cod family 4 basioccipital 13 first vertebra 28 second vertebra 17 third vertebra 309 vertebra C (1 burnt) 86 vertebra B 30 vertebra A 6L 1R quadrate 1 parasphenoid 2L dentary 1L 2R hyomandibular 1L cleithrum 2L 2R posttemporal 1L sphenotic 1L pterotic 1L 4R premaxillary (1 frag. 1 burnt) 1L 2R ceratohyal 5L 8R angular 2L 2R maxillary (1 burnt) 1L 3R 1 whole vomer (the whole one is burnt) Flatfish 6 vertebra C 1 urohyal (burnt) Eel 5 vertebra C 1 vertebra B 1L quadrate 1R ceratohyal (2.5mm) Mackerel
2 vertebra C Garfish 2 vertebra C 1 vertebra B Unidentified 3 vertebra too dirty 1 vertebra C 3 vertebra B 125E 132N Grey below culture layer Trench 1 25June2007 TLS Weights: 2g fragments no ID, <1g vertebra no ID, 1g non-vertebra, 11g cod, <1g other vertebra Cod family 4 basioccipital 1 first vertebra 7 second vertebra 2 third vertebra 87 vertebra C (1 burnt) 40 vertebra B 12 vertebra A 5 otoliths 1L 1R angular 1L 2 whole vomer 2L posttemporal 1L quadrate Flatfish 2 vertebra C 2 vertebra B Eel 1 vertebra C Mackerel 1 vertebra C 1 vertebra B 1 vertebra A Bull-rout 2 vertebra C Gurnard 1 vertebra C Unidentified 6 vertebra C 126E 132N Culture Layer Trench 1 26June2007 TLS Weights: 1g fragments no ID, 5g non-vertebra, 6g cod, <1g other vertebra Cod family 1 first vertebra 1 second vertebra 18 vertebra C 1 vertebra B 1L dentary 2R supracleithrum 2L maxillary 2L angular (1 >3kg fish) 5 parasphenoid 1R eiphyal 1R ceratohyal 2L quadrate (1 burnt) 1R premaxillary (1 fragment) Mackerel 1 vertebra B (fairly large) Eel 1 vomer 125E 133N Culture Layer Trench 1 25June2007 VLS 1 of 3 Weights: 1g otoliths, 6g non-vertebra, 8g fragments no ID, 12g vertebra no ID, 131g cod, 5g other vertebra Cod family 24 basioccipital 31 first vertebra 44 second vertebra (1 burnt) 45 third vertebra 1289 vertebra C 190 vertebra B 57 vertebra A 2R preopercle 2 parasphenoid (3 fragments) 2L 3R premaxillary (1 burnt) 5L 5R angular 7L 4R quadrate 3L 1R maxillary (1 frag. 4 burnt) 1L vomer 1L dentary 2L cleithrum 2L 1R hyomandibular 2R posttemporal 1R ceratohyal 1L ectopterygoid 1R symplectic 1L exoccipital 1 supraoccipital Flatfish 1 first vertebra (4.0mm) 40 vertebra C 1 vertebra B Eel 43 vertebra C 2 vertebra B 1L ceratohyal (3.2mm) 1 parasphenoid
Bull-rout 17 vertebra C (1 burnt) 1 vertebra B Mackerel 1 vertebra C 2 vertebra B 1 vertebra A Spurdog 1 vertebra A 1 dorsal spine (possibly used) Gurnard 1 vertebra C Unidentified 74 vertebra too dirty 11 vertebra C 19 vertebra B 125E 133N Culture Layer Trench1 26June2007 VLS 2 of 3 Weights: 2g otoliths, 10g non-vertebra, 13g fragments no ID, 8g vertebra no ID, 119g cod, 4g other vertebra Cod family 20 basioccipital 48 first vertebra 71 second vertebra 39 third vertebra 1127 vertebra C 209 vertebra B 56 vertebra A 1R hypohyal 7L 4R premaxillary 4 parasphenoid 15L 17R angular 3L 12R maxillary (1 burnt) 1L 4R hyomandibular 4L 5R quadrate 2L 1R 1 whole vomer 1L 1R dentary 1L 2R supracleithrum 4L 6R posttemporal 2 mesethmoid 1L 1R ceratohyal 1R cleithrum (1 fragment) 1L 1R sphenotic 1R pterotic 1R palatine 1L ectopterygoid Flatfish 25 vertebra C Eel 1 basioccipital 43 vertebra C (2 burnt) 5 vertebra B 1 vertebra A 1L dentary 1R quadrate 1 vomer Bull-rout 1 first vertebra (4.1mm) 8 vertebra C 1L maxillary Mackerel 1 vertebra B 1 vertebra A Garfish 1 vertebra C Weever 1 vertebra C Herring 1 vertebra Cyprinid 1 vertebra C Shad 1 vertebra C Unidentified 62 vertebra too dirty 12 vertebra C 20 vertebra B 125E 133N Culture Layer Trench 1 27June2007 VLS 3 of 3 Weights: 10g otoliths, 14g vertebra no ID, 23g fragments no ID, 21g non-vertebra, 322g cod, 9g eel, 11g other vertebra Cod family 46 basioccipital (1 burnt) 108 first vertebra 148 second vertebra 115 third vertebra 3322 vertebra C (2 burnt) 524 vertebra B 141 vertebra A 145 otoliths and 19 fragments 10L 8R premaxillary (1 fragment) 1L 1R 7 whole vomer 16L 12R maxillary (9 burnt) 5L 5R dentary (3 frag. 2burnt)
15L 20R angular (1 fragment) 10L 12R quadrate (2 burnt) 9 parasphenoid (4 fragments) 1 epibranchial 3L 1R epihyal 2L 3R ceratohyal 5L 3R hyomandibular 4L 2R posttemporal 2L 3R supracleithrum 5L 4R cleithrum (2 fragments) 6L 1R sphenotic 2L 1R symplectic 1L 2R opercle 1L 2R ectopterygoid 2 mesethmoid 1R palatine 1R preopercle 2L pterotic 1L exoccipital Flatfish 84 vertebra C (1 burnt) 14 vertebra B 3 vertebra A Eel 2 basioccipital 216 vertebra C (6 burnt) 28 vertebra B 12 vertebra A 1 vomer 1L anguloarticulare 1R cleithrum 1L 1R epihyale (1 burnt) 2R ceratohyal (2.4, 1.4mm) Garfish 19 vertebra C 2 vertebra B 2 vertebra A Bull-rout 1 basioccipital 1 first vertebra (3.4mm) 50 vertebra C 1 vertebra B 1R angular 1L opercle Herring 2 vertebra C Trout/salmon 2 vertebra C Mackerel 21 vertebra C 7 vertebra B 3 vertebra A (all but two are small) Weever 1 vertebra C Eelpout 1 vertebra C Spurdog 2 vertebra C 8 vertebra A Gurnard 17 vertebra C Shad 2 vertebra C Unidentified 94 vertebra too dirty 28 vertebra C 48 vertebra B 125E 133N Grey below culture layer Trench 1 28June2007 VLS Weights: 3g non-vertebra, <1g cod Cod family 1 first vertebra 4 parasphenoid 2R premaxillary 1L 1R ceratohyal (1 frag.) 1L 1R angular 1 R cleithrum Spurdog 1 dorsal spine (definitely used) 125E 133N Grey below culture layer Trench 1 28June2007 VLS Weights: 4g otoliths, 6g fragments no ID, 3g vertebra no ID, 3g non-vertebra, 77g cod, 4g other vertebra Cod family 7 basioccipital 28 first vertebra 34 second vertebra 32 third vertebra 765 vertebra C 108 vertebra B 43 vertebra A 41 otoliths & 5 fragments 4L premaxillary (2 fragment) 3L quadrate 1L 1R maxillary 1L ceratohyal 2L 1 whole vomer 3 parasphenoid 5L 4R angular (1 fragment) 1L 2R dentary 1L opercle 1L hyomandibular
3L sphenotic Flatfish 1 first vertebra (3.3mm) 15 vertebra C 6 vertebra B Eel 35 vertebra C (6 burnt) 7 vertebra B Bull-rout 4 vertebra C Gurnard 3 vertebra C Spurdog 1 vertebra A Mackerel 6 vertebra C (1 penultimate) 1 vertebra B (all small) Garfish 2 vertebra C 1 vertebra B Eelpout 1 vertebra C Unidentified 15 vertebra too dirty 7 vertebra C 11 vertebra B Back-dirt cultural layer with shells Trench 1 JN Weights: 27g fragments and shell no ID, 2g vertebra no ID, 1g non-vertebra, 25g cod, <1g other vertebra Cod family 3 basioccipital 7 first vertebra 8 second vertebra 16 third vertebra 164 vertebra C 12 vertebra B 2 otoliths 1 parasphenoid 1L premaxillary 1L epihyal 1L 1R maxillary 1R sphenotic Flatfish 4 vertebra C Eel 1 first vertebra 3 vertebra C Mackerel 1 vertebra C (fairly large) Spurdog 1 vertebra A Bull-rout 1 vertebra C Unidentified 8 vertebra too dirty 136E 131N Culture Layer Trench 2 28June2007 LRA Weight: <1g vertebra no ID, 1g cod Cod family 1 second vertebra 1 third vertebra 5 vertebra C (2-3 burnt?) 3 vertebra B 1 otolith Unidentified 1 vertebra C 134E 132N Culture Layer Trench 2 22June2007 KCR Weights: 3g fragments no ID, <1g vertebra no ID, <1g non-vertebra, 2g cod, <1g other vertebra Cod family 2 basioccipital (1 burnt) 2 first vertebra 1 second vertebra (burnt) 1 third vertebra (burnt) 26 vertebra C (10 burnt) 4 vertebra B 1 vertebra A 1L 1R dentary 1L1R posttemporal 1 parasphenoid 3L premaxillary (1 burnt) 1R cleithrum
Flatfish 3 vertebra C Herring 2 vertebra C (1 burnt) Bull-rout 2 vertebra C Unidentified 1 vertebra too dirty 1 vertebra C 135E 132N Culture Layer Trench 2 25June2007 KCR Weights: 1g otoliths, 5g fragments no ID, <1g vertebra no ID, 3g non-vertebra, 15g cod, 1g other vertebra Cod family 4 basioccipital 5 first vertebra 12 second vertebra 9 third vertebra 176 vertebra C 33 vertebra B 9 vertebra A 6 otoliths & 5 fragments 3 parasphenoid (1 fragment) 1L 1R angular 5L 3R posttemporal 2L 1R vomer 1L dentary 1R epihyal 1L ectopterygoid 3L 4R quadrate 2L 2R maxillary 3L 2R premaxillary (1 fragment) 3L 3R supracleithrum 1L palatine 1R symplectic Flatfish 8 vertebra C Eel 1 basioccipital 10 vertebra C 1 vertebra A 3 vomer 1L 1R dentary 1L 1R eiphyale 1R cleithrum Bull-rout 1 basioccipital 7 vertebra C Weever 1 vertebra C Spurdog 3 vertebra A Unidentified 3 vertebra C 1 vertebra B 136E 132N Culture Layer Trench 2 25June2007 LRA Weights: 1g otoliths, 3g fragments no ID, <1g vertebra no ID, 3g non-vertebra, 12g cod, 2g other vertebra Cod family 3 basioccipital 2 first vertebra 9 second vertebra 11 third vertebra (1 burnt) 150 vertebra C 34 vertebra B 9 vertebra A 13 otoliths & 5 fragments 1L epihyal 1L pterotic 1R vomer 1R interhyal 2R premaxillary 3 parasphenoid (1 fragment) 1R symplectic 1L 1R dentary 1L 1R maxillary 1R angular 1L 1R posttemporal 1L 3R supracleithrum (1 frag.) 1L 9R quadrate 1 epibranchial 1L opercle 2L ectopterygoid 1R hyomandibular Flatfish 8 vertebra C Eel 1 basioccipital 18 vertebra C 6 vertebra B 1 vertebra A 1R hyomandibular Trout/salmon 1 vertebra A (probable)
Weever 2 vertebra C Bull-rout 3 vertebra C Spurdog 2 dorsal spines 134E 133N Culture Layer Trench 2 25June2007 KCR Weights: <1g otoliths, 2g bone fragments no ID, <1g vertebra no ID, 3g non-vertebra, 10g cod, 1g other vertebra Cod family 2 basioccipital 2 first vertebra 3 second vertebra 3 third vertebra 99 vertebra C 21 vertebra B 1 vertebra A 7 otoliths & 2 fragments 1 parasphenoid 1L dentary 1L supracleithrum 1L 1R angular 1L palatine 2L 1R premaxillary 2L 2R posttemporal 2L 1R quadrate 1L 2R maxillary (2 burnt) 1L hyomandibular 1L 2R 1 whole vomer (whole is whiting) 1R ceratohyal Flatfish 1 first vertebra (3.9mm) 4 vertebra C Eel 7 vertebra C 2 vertebra B 1L ceratohyal (2.6mm) Spurdog 2 vertebra A Herring 1 vertebra C Bull-rout 2 vertebra C (burnt?) Garfish 1 first vertebra (burnt?) Weever 2 vertebra C Unidentified 3 vertebra C 3 vertebra B 135E 133N Culture Layer Trench 2 26June2007 KCR Weights: 3g otoliths, 12g non-vertebra, 7g fragments no ID, 45g cod, 5g other vertebra Cod family 20 basioccipital 20 first vertebra 21 second vertebra 21 third vertebra 534 vertebra C 114 vertebra B 35 vertebra A 38 otoliths & 5 fragments 5L 3R dentary (1 frag.) 6 parasphenoid (1 frag.) 9L 6R premaxillary (3 frag.) 8L 13R posttemporal 3L 1R hyomandibular 9L 10R quadrate (1 frag.) 1L cleithrum (1fragment) 5L 5R angular (1 frag.) 6L 4R supracleithrum 1R supracleithrum haddock 3L 2R vomer 7L 7R maxillary 1L palatine 4 branchiostegal ray 1L exoccipital 1L interopercle 1L 2R retroarticular 1L preopercle 1 supraoccipital 2L sphenotic 1L pterotic 1 loose tooth Flatfish 1 first vertebra (3.1mm) 39 vertebra C 2 vertebra B 1R quadrate 1 os anale Eel 40 vertebra C (6 burnt?) 7 vertebra B 1R quadrate 1L 2R dentary 2 vomer 1R ceratohyal (1.7mm) 2L cleithrum 1L maxillary (in 2 pieces) Bull-rout
2 first vertebra (2.9, 3.5mm) 14 vertebra C 1 parasphenoid 1L preopercle 1R subopercle 1L posttemporal Weever 1 first vertebra 11 vertebra C 1R quadrate Spurdog 2 vertebra C 2 dorsal spines (both used?) Gurnard 3 vertebra C 1 dorsal spine Herring 1 vertebra C Mackerel 1 vertebra B 1 vertebra A Garfish 2 vertebra C Unidentified 8 vertebra C 8 vertebra B 136E 133N Culture Layer Trench 2 26June2007 LRA Weights: 6g otoliths, 21g non-vertebra, 17g fragments no ID, 2g vertebra no ID, 79g cod, 6g other vertebra Cod family 25 basioccipital 44 first vertebra 49 second vertebra 45 third vertebra 826 vertebra C 160 vertebra B 66 vertebra A 74 otoliths & 9 fragments 5L 11R angular 17L 17R premaxillary (6 frag.) 14L 12R quadrate 9L 13R posttemporal 2L 3R cleithrum (2 frag.) 2 branchiostegal rays 1 mesethmoid 1L 2R opercle 3 epibranchial 1R exoccipital 1L 2R palatine 1R interopercle 2L ectopterygoid 16 parasphenoid (5 frag.) 4L 1R hyomandibular 4L 5R dentary 4L 4R 4 whole vomer 9L 6R supracleithrum 16L 17R maxillary (1 burnt) 1R pteroticum 2L symplectic 3L 1R sphenotic 2L interhyal 1L 2R epihyal 1R ceratohyal Flatfish 4 first vertebra (4.1, 3.4, 5.2, 4.3mm) 48 vertebra C 4 vertebra B 1R quadrate 1L angular Eel 62 vertebra C 14 vertebra B 7 vertebra A 1L dentary 2L 2R ceratohyal (3.4, 2.4, 2.8, 2.0mm) 1 vomer 1L quadrate 4R cleithrum Mackerel 2 vertebra C 1 vertebra B Trout/salmon 1 vertebra C Spurdog 1 vertebra C 2 vertebra B 2 vertebra A Bull-rout 2 basioccipital 1 first vertebra (3.8mm) 20 vertebra C 1L maxillary 1L quadrate Gurnard 2 vertebra C 1R quadrate 1 dorsal plate (grey gurnard) Unidentified 10 vertebra C 7 vertebra B 134-136E 131-132N Layer 15 T6 28June2007 KCR Weight: <1g Cod family
2 vertebra C 1L posttemporal Flatfish 1 fragment os anale North end of Trench 2 2.0x0.3m bottom of trench, culture layer #2 29June2007 KCR Weights: 5g fragments no ID, <1g vertebra no ID, 4g non-vertebra, 14g cod, 1g other vertebra Cod family 2 basioccipital 7 first vertebra 13 second vertebra (1 burnt) 6 third vertebra 88 vertebra C 28 vertebra B 17 vertebra A 5L 4R dentary (3 frag.) 1L 2R ectopterygoid (1 burnt) 1L 1R vomer 1L 1R quadrate 1L 2R posttemporal (1 burnt) 1 epibranchial 1L 1R ceratohyal 1L symplectic 7 parasphenoid (5 frag.) 5L 5R premaxillary (1 fragment, 1 burnt) 1L 1R cleithrum (1 frag.) 3L supracleithrum 1L 4R maxillary 1L 1R angular 1L epihyal 1L interopercle 1L pterotic Flatfish 11 vertebra C Eel 2 vertebra C (1 burnt) 1 vertebra B Bull-rout 1 vertebra C Gurnard 1 non-vertebra element, unnamed, but matched with part from comparative collection 1 dorsal spine Unidentified 2 vertebra C 3 vertebra B 122E 136N Brown Shell Trench 3 17July2007 LRA selectively picked Weights: 8g otoliths, <1g fragments no ID, 3g non-vertebra, 2g cod, <1g other vertebra Cod family 1 basioccipital 3 first vertebra 1 third vertebra 8 vertebra C 3 vertebra B 1 vertebra A 74 otoliths & 6 fragments 1R pharyngeal plate 4 parasphenoid 1L 1R premaxillary 2R maxillary 2R angular Eel 1 vertebra C 1 vertebra B Bull-rout 2 vertebra C 123E 136N Shell Trench 3 12July2007 KJG Weight: 2g Cod family 1 fourth vertebra (16.0mm) 124E 135N Culture Layer Trench 3 11July2007 KCR (270gram sample from 144liters) Weights: 2g otoliths, 41g non-vertebra, 25g fragments no ID, 12g vertebra no ID, 147g cod, 2g flatfish, 7g eel, 3g other vertebra Cod family 40 basioccipital 57 first vertebra 62 second vertebra 65 third vertebra 48 fourth vertebra 43 fifth vertebra 6 sixth vertebra 1697 vertebra C (2 burnt, at least 1 haddock) 229 vertebra B 91 vertebra A 20 otolith and 7 fragments 7L 12R dentary (4 fragments, 4 and 2 fragments burnt) 6L 7R 2 whole vomer (4 burnt) 16L 24R premaxillary (1 fragment, 7 and 1 fragment burnt) 27L 47R angular (2 burnt) 34 parasphenoid (7 fragments, 5 burnt) 2 interhyal
13L 10R cleithrum (4 fragments, 3 burnt) 7L 2R ceratohyal (1 burnt) 2L 3R epihyal (2 burnt) 19L 13R supracleithrum (5 burnt) 5L 1R palatine 27L 18R quadrate (2 fragments, 1 burnt) 23L 27R maxillary (8 burnt) 23L 22R posttemporal (2 burnt) 13L 12R hyomandibular (3 frag.) 2 pharyngeal plates 5 epibranchial (1 burnt) 1 pharyngobranchial 1L 1R opercle 1L interopercle 1L 1R preopercle 6L 4R pterotic 1L 1R exoccipital 2L 1R sphenotic 4 branchiostegal rays 8 symplectic 2 retroarticular 3L 5R ectopterygoid (3 burnt) Flatfish 1 basioccipital 2 first vertebra (4.9 & 3.3mm) 41 vertebra C 1 vertebra B 1 os anale Eel 1 basioccipital 1 first vertebra 230 vertebra C 36 vertebra B 12 vertebra A 4 vomer (1 burnt) 3L 3R ceratohyal (3 burnt) (2.5, 2.2, 2.1, 3.0, 1.9 and 2.6mm) 2L 1R anguloarticulare (1 burnt) 2R opercle 1R epihyale 2L hyomandibular 1L dentale 3L 2R cleithrum 1R maxillary Mackerel 23 vertebra C 5 vertebra B 2 vertebra A Bull-rout 3 first vertebra (3.9, 4.0,1 no measure) 34 vertebra C 6 supracleithrum 3L 2R opercle 3L 3R preopercle (3 burnt) 2 parasphenoid 1 vomer Gurnard 4 vertebra C 1R maxillary Herring 11 vertebra C Trout/salmon 1 vertebra C Spurdog 1 vertebra C 1 vertebra B 3 vertebra A Eelpout 1 vertebra C Shad 1 vertebra C Dragonet 1 vertebra C Unidentified 103 vertebra too dirty 50 vertebra C 17 vertebra B 124E 135N Culture Layer Trench 3 11July2007 KCR remaining 4/5ths of sample Weights: 3g otoliths, 142g non-vertebra, 95g fragments no ID, 577g cod, 9g flatfish, 41g eel, 11g other vertebra, 50g vertebra no ID Cod family 150 basioccipital 212 first vertebra 206 second vertebra 231 third vertebra 172 fourth vertebra (at least 1 haddock) 6893 vertebra C (includes 5
th and 6
th vertebra) 1175 vertebra B
397 vertebra A (2 calcined) 52 otoliths and 26 fragments 1L 4R 2 whole vomer whiting 14L 18R 8 whole vomer cod 7L 3R 5 whole vomer gadid 19L 13R dentary cod 1L 3R dentary whiting 20L 20R dentary gadid (3 frag.) 51L 37R premaxillary gadid 126L 131R angular (1 frag.) 117L 104R quadrate 45L 44R hyomandibular (6 frag.) 74L 75R maxillary (1 frag.) 54L 55R supracleithrum 65L 71R posttemporal
117 parasphenoid (5 frag.) 33 epibranchial 4L 4R pharyngeal plate 3 pharyngobranchial 33L 29R cleithrum (47 frag.) 13L 16R ceratohyal (7 frag.) 6L 7R epihyal 16L 19R sphenotic 30 symplectic 1 postcleithrum 8L 6R preopercle (8 frag.) 11L 16R ectopterygoid 8L 14R palatine 14 branchiostegal rays 10 mesethmoid 4 retroarticular 1L supracleithrum haddock 6L 6R opercle 3L interopercle 5L 5R exoccipital 11 pterotic 37L 34R premaxillary cod (1 calcined) 1L cleithrum haddock (large) Flatfish 1 basioccipital 5 first vertebra (3.2, 3.8, 4.7 5.3 and 3.6mm) 206 vertebra C (1 burned) 11 vertebra B 2 vertebra A 1 vomer 1 fragment dentary 2L 4R quadrate 2R hyomandibular 1L 1R maxillary 1L 1R supracleithrum 1R posttemporal 3 os anale (2 fragments) 4 ectopterygoid 1R palatine Eel 9 basioccipital 4 first vertebra 1268 vertebra C 155 vertebra B 88 vertebra A 15 vomer 6L 5R hyomandibular 6L 1R quadrate 5L 8R anguloarticulare 4L 3R epihyale 3L 5R dentale 2L 1R frontale 1L 3R opercle 20L 13R ceratohyal (2.0, 2.0, 1.8, 1.6, 1.3, 1.4, 1.4, 1.7, 1.6, 1.4, 1.5, 2.9, 2.9, 3.2, 3.0, 2.0, 2.3, 2.5, 2.0, 2.2, 2.3, 2.2, 1.9, 2.1 and 9 no measure) 6L 8R cleithrum 2 parasphenoid 6L maxillary Mackerel 99 vertebra C (all but 2 very small) 51 vertebra B 18 vertebra A Garfish 4 vertebra C Spurdog 4 vertebra C 4 vertebra B 16 vertebra A 3 dorsal spines Herring 2 first vertebra 72 vertebra C 9 vertebra B 3 vertebra A 2 prooticum Eelpout 2 vertebra C Trout/salmon 2 vertebra C 3 vertebra A Bull-rout 7 basioccipital 8 first vert (3.4, 2.3, 3.1, 2.5, 2.5, 2.4, 2.4mm and 1 no measure) 147 vertebra C 1 vertebra B 2R dentary 2L premaxillary 1R angular 4L 4R quadrate 3L 4R maxillary 1 parasphenoid 5L 5R opercle 2L 2R subopercle 1L 3R preopercle 1L 2R supracleithrum 1R circumorbital element (?) Gurnard 1 basioccipital 1 first vertebra (3.1mm) 39 vertebra C 2 vertebra B 1L quadrate 1R maxillary 3 parasphenoid 1 pharyngeal plate 1R cleithrum 3 dorsal spines 3 dorsal plates (grey gurnard) Unidentified 435 vertebra too dirty 152 vertebra no ID C 149 vertebra no ID B 124E 135N Shell Trench 3 17July2007 KCR 24liters Weights: 11g otoliths, 51g non-vertebra, 21g fragments no ID, 10g no ID vertebra, 2g flatfish, 17g eel, 187g cod, 6g other vertebra
Cod family 45 basioccipital 90 first vertebra 76 second vertebra 77 third vertebra 77 fourth vertebra 60 fifth vertebra 30 sixth vertebra 2727 other vertebra C (2 burnt) 244 vertebra B (3 burnt) 159 vertebra A 23L 9R dentary (8 burnt, 4 fragments) 11L 5R 4 whole vomer (2 burnt) 21L 26R premaxillary (5 fragments, 21 and 2 fragments burnt) 45 parasphenoid (5 frag., 4 burnt) 35L 37R angular (5 fragments, 3 burnt) 32L 41R maxillary (24 burnt) 38L 33R quadrate (3 burnt) 15L 24R supracleithrum (9 burnt) 10L 16R cleithrum (10 fragments, 8 and 2 fragments burnt) 2L 6R ceratohyal (2 burnt) 3L 1R epihyal 3L 5R palatine (3 burnt) 25L 33R posttemporal (29 burnt) 21L 18R hyomandibular (2 fragments, 5 burnt) 1 interhyal (burnt) 4 epibranchial 1 pharyngobranchial 5L 6R pterotic (2 burnt) 1L 4R sphenotic (2 burnt) 2L 2R opercle (2 burnt) 6 mesethmoid (1 burnt) 5 branchiostegal rays (3 burnt) 11 symplectic (1 burnt) 5 L 2R ectopterygoid (4 burnt) 1L 1R preopercle (1 burnt) 1L exoccipital (burnt) 158 otoliths and 21 fragments 1L 5R opisthotic 1R cleithrum (haddock, large) Flatfish 2 first vertebra (4.3 and 3.5mm) 59 vertebra C (2 burnt) 1 vertebra B 2 vertebra A 1R supracleithrum 1L 1R posttemporal 1 urohyal 1L quadrate Eel 6 basioccipital 4 first vertebra 615 vertebra C (10 burnt, 1 calcined) 58 vertebra B (2 burnt) 30 vertebra A (1 calcined) 1L hyomandibular 1 parasphenoid 1 R quadrate (burnt) 1L 3R dentale (2 fragment, 2 burnt) 1L 1R anguloarticulare (1 burnt) 2L 1R epihyale (1 burnt) 1L opercle 6 vomer (3 burnt) 1L 4R cleithrum (3 burnt) 7L 8R ceratohyal (10 burnt) (2.7, 2.8, 2.1, 2.3, 2.6, 1.3, 2.7, 1.4, 1.8, 2.3, 2.0, 1.4, 1.4 and 2 no measure) 2L 3R maxillary (3 fragments) Mackerel 114 vertebra C (1 penultimate) 35 vertebra B 6 vertebra A Bull-rout 1 basioccipital 3 first vertebra (2.7, 3.1, 3.1) 93 vertebra C 1L premaxillary 3 parasphenoid 2L angular 1L quadrate 1L opercle 5 supracleithrum 2L 2R preopercle (1 frag. 3 burnt) 1 R subopercle Gurnard 1 first vertebra (4.0mm) 9 vertebra C 2 dorsal plates (grey gurnard) Weever 7 vertebra C Herring 3 first vertebra 35 vertebra C 6 vertebra B Garfish 2 vertebra C Trout/salmon 1 vertebra C 1 vertebra A Spurdog 5 vertebra C 20 vertebra A Eelpout 3 vertebra C Unidentified 76 vertebra too dirty 59 vertebra C 31 vertebra B 124E 135N Shell Trench 3 19July2007 KCR selectively picked
Weight: 3g non-vertebra Cod family 2 parasphenoid 1L angular (much >3kg fish) 124E 135N Shell Trench 3 19July2007 KCR selectively picked Weights: <1g otoliths, <1g fragments no ID, 3g non-vertebra, 19g cod Cod family 2 third vertebra (large) 17 vertebra C (large) 3 otoliths (fairly small) 1L 2R premaxillary (large) 2 parasphenoid (large) 124E 135N Brown Surface Trench3 19July2007 KCR 96liters Weights: 10g otoliths, 72g non-vertebra, 43g fragments no ID, 5g flatfish, 19g eel, 285g cod, 13g no ID vertebra, 5g other vertebra Cod family 33 basioccipital 53 first vertebra 74 second vertebra (3 burnt) 78 third vertebra (2 burnt) 84 fourth vertebra (3 burnt) 55 fifth vertebra (3 burnt) 14 sixth vertebra 2000 other vertebra C (36 burnt, includes haddock) 201 other vertebra B (3 calcined, 2 burnt) 246 other vertebra A (5 burnt) 24L 18R dentary (2 fragments, 4 burnt) 39 parasphenoid (10 fragments) 6L 8R 2 whole vomer (3 burnt) 23L 25R premaxillary (9 fragments and 23 burnt) 20L 13R supracleithrum (1 fragment, 15 burnt) 4L 4R ceratohyal (2 fragments) 1L 3R epihyal (2 burnt) 1L 2R hypohyal (3 burnt) 17L 33R maxillary (21 burnt) 25L 37R angular (2 frag. 23 burnt) 32L 25R quadrate (20 burnt) 22L 22R posttemporal (23 burnt) 12L 8R hyomandibular (6 burnt) 11L 13R cleithrum (16 burnt) 5 epibranchial (3 burnt) 1L pharyngeal plate 2R opercle (burnt) 5L 2R palatine (6 burnt) 1L 2R interopercle (1 burnt) 3L 2R sphenotic (3 burnt) 6 branchiostegal rays (all burnt) 3 mesethmoid (2 burnt) 12 symplectic (3 burnt) 6L 4R pterotic 1L 3R exoccipital 7L 11R ectopterygoid (15 burnt) 4 interhyal (4 burnt) 1 postcleithrum 1L 1R opisthotic 1 basibranchial 1R cleithrum (haddock, medium) 84 otoliths, 23 fragments Flatfish 1 basioccipital 6 first vertebra (4.3, 3.7, 4.9, 3.8, 4.3 and 4.5mm) 109 vertebra C (5 burnt, 2 ultimate) 1 vertebra A 1L angular 1L 1R hyomandibular 1 os anale (burnt) 1 ectopterygoid (burnt) Eel 8 basioccipital 5 first vertebra 580 vertebra C (23 burnt) 16 vertebra B 8 vertebra A 9 vomer (6 burnt) 6L 7R anguloarticulare (8 burnt) 4L 8R dentale (10 burnt) 1L 1R hyomandibular (2 burnt) 3L 2R quadrate (burnt) 1L frontale (burnt) 1L 1R opercle (2 burnt) 2L 7R epihyale (6 burnt) 5L 2R cleithrum (4 burnt) 3L 5R maxillary 12L 12R ceratohyal (16 burnt) (3.1, 2.9, 2.0, 2.5, 2.7, 1.9, 1.6, 2.6, 2.5, 2.2, 2.8, 1.9, 1.9, 1.9, 1.6, 2.1, 2.6, 1.9, 1.9, 2.1, 2.1, 2.1, and 2.3mm) Mackerel 52 vertebra C 10 vertebra B 12 vertebra A Garfish 2 vertebra C Bull-rout 2 first vertebra (3.6, 3.9mm) 30 vertebra C 1L dentary 1 supracleithrum 1L 1 R hyomandibular 2R opercle (1 burnt) 1R posttemporal Spurdog 3 vertebra A Trout/salmon
5 vertebra C Herring 1 first vertebra 6 vertebra C Weever 1 basioccipital 4 vertebra C Gurnard 1 first vertebra (3.6mm) 13 vertebra C 1 ventral spine 1 dorsal spine 1 dorsal plate Eelpout 10 vertebra C Shad 9 vertebra C Cyprinid 7 vertebra C Unidentified vertebra 57 too dirty 69 vertebra C (1 burnt) 26 vertebra B 125E 135N Shell Trench 3 03July2007 TDP selectively picked Weights: 5g otoliths, 5g fragments no ID, 4g non-vertebra, 55g cod, <1g other vertebra Cod family 2 basioccipital 6 first vertebra 3 second vertebra 7 third vertebra 159 vertebra C 13 vertebra B 3 vertebra A 38 otoliths & 1 fragment 2 branchiostegal rays (2 burnt) 1R interhyal 1R angular 4 parasphenoid 1R sphenotic 1R opercle 1L 1R dentary 1L 1R ceratohyal 1R cleithrum 1L 1R maxillary 1L 2R posttemporal Flatfish 2 vertebra C Eel 4 vertebra C 2 vertebra A (1 burnt) 1L dentary 1L epihyal Bull-rout 1R supracleithrum Mackerel 1 vertebra C Unidentified 2 vertebra C 130E 135N Culture Layer Trench 3 02July2007 LRA (all fish bones picked) Weight: <1g fragments no ID, <1g vertebra no ID, 1g non-vertebra, 2g cod Cod family 2 third vertebra 13 vertebra C 2 vertebra B 1 vertebra A 2 fragments otoliths 1L 1R premaxillary 1 parasphenoid 1R angular Eel 1L anguloarticulare Bull-rout 1L maxillary Unidentified 1 vertebra C 134E 135N Culture Layer Trench 3 03July2007 KCR Weights: 3g otoliths, 9g non-vertebra, 10g fragments no ID, 1g vertebra no ID, 56g cod, 3g other vertebra Cod family
10 basioccipital 20 first vertebra 32 second vertebra 39 third vertebra 689 vertebra C (5 burnt) 100 vertebra B 42 vertebra A 37 otoliths & 4 fragments 1 supraoccipital 1L 1R ectopterygoid 1R pterotic 1R opercle 6 parasphenoid (3 frag.) 4L 5R dentary (2 burnt) 5L 5R maxillary (4 burnt) 7L 9R premaxillary (2 frag., 2burnt, 2 calcined) 3L 7R posttemporal (2 burnt) 4L 6R quadrate (3 burnt) 3L 2R vomer (3 burnt) 3L 3R supracleithrum (3 burnt) 3L 1R cleithrum (1 frag.) 3L 2R angular 1L interhyal (burnt) 1L hypohyal 1R hyomandibular 1 branchiostegal ray 2R sphenotic 2 epibranchial 1R pharyngeal plate 1L 1R symplectic (1 burnt) 2R palatine (2 burnt) 1L epihyal Flatfish 24 vertebra C (5 burnt) 2 vertebra B Eel 1 first vertebra 20 vertebra C (4 burnt) 4 vertebra B 2 vertebra A 1R dentary (in 2 pieces) 1 vomer 1L ceratohyal (2.5mm) 1R angular Spurdog 6 vertebra C 6 vertebra A Mackerel 2 vertebra C 2 vertebra B 1 vertebra A Bull-rout 6 vertebra C 1R opercle 1L quadrate 1R angular (burnt) Herring 2 vertebra C 2 prooticum Gurnard 1 vertebra C Garfish 3 fragments dentary Unidentified 2 vertebra too dirty 10 vertebra C 12 vertebra B Årby 365 Asnæs Havnemark Geologic Screen Samples 121E 134N Feature A7 Upper Layer Trench 3 18July2007 VLS 2 liters 2mm Cod family 1 first vertebra (4.1mm) 3 second vertebra 2 third vertebra 1 fourth vertebra 2 fifth vertebra 70 other vertebra Flatfish 1 first vertebra 5 other vertebra Eel 2 basioccipital 19 other vertebra Herring 13 vertebra Bull-rout 5 vertebra Mackerel 1 vertebra Unidentified 18 vertebra 121E 134N Feature A7 Lower Layer Trench 3 19July2007 VLS 2 liters 2mm Cod family 2 second vertebra 2 third vertebra 1 fourth vertebra 1 sixth vertebra 32 other vertebra
Eel 1 basioccipital 17 other vertebra Herring 3 vertebra Bull-rout 1 first vertebra 1 other vertebra Mackerel 1 vertebra Unidentified 8 vertebra 125E 135N Shell Trench 3 04July2007 LRA 2 liters 2mm Cod family 1 basioccipital 2 second vertebra 2 third vertebra 1 fifth vertebra 37 other vertebra Flatfish 2 vertebra Eel 34 vertebra Herring 4 vertebra Bull-rout 6 vertebra Mackerel 5 vertebra Unidentified 18 vertebra 125E 133N Culture Layer Trench 1 25June2007 VLS 2 liters 2mm Cod family 3 first vertebra (3.8, 2.8, 2.3mm) 1 second vertebra 1 third vertebra 2 fourth vertebra 1 fifth vertebra 40 other vertebra Flatfish 1 vertebra Eel 20 vertebra Herring 1 first vertebra 3 vertebra Bull-rout 6 vertebra Mackerel 5 vertebra Unidentified 24 vertebra 124E 135N Brown Surface Trench 3 18July2007 KCR 2 liters 2mm Cod family 1 first vertebra (3.1mm) 1 fourth vertebra 27 other vertebra 1R otoliths Flatfish 1 vertebra Eel 2 basioccipital 1 first vertebra 58 other vertebra Herring 3 vertebra Mackerel
9 vertebra Bull-rout 3 vertebra Unidentified 18 vertebra 124E 135N Shell Trench 3 17July2007 KCR 2 liters 2mm Cod family 3 basioccipital 3 second vertebra 1 third vertebra 4 fourth vertebra 1 fifth vertebra 113 other vertebra Flatfish 6 vertebra Eel 1 basioccipital 1 first vertebra 75 other vertebra Herring 1 first vertebra 15 other vertebra Bull-rout 1 first vertebra 11 other vertebra Mackerel 15 vertebra Trout/salmon 1 vertebra Unidentified 32 vertebra 124E 135N Culture Layer Trench 3 06July2007 KCR 2 liters 2mm Cod family 2 basioccipital 2 first vertebra (3.7, 2.3mm) 2 second vertebra 1 third vertebra 3 fourth vertebra 2 fifth vertebra 71 other vertebra Flatfish 4 vertebra Eel 1 basioccipital 39 other vertebra Herring 7 vertebra Bull-rout 8 vertebra Mackerel 9 vertebra Unidentified 24 vertebra 136E 133N Culture Layer Trench 2 25June2007 LRA 2 liters 2mm Cod family 1 second vertebra 2 fourth vertebra 19 other vertebra Eel 8 vertebra Herring 11 vertebra Bull-rout 3 vertebra Unidentified 2 vertebra 125E 132N Culture Layer Trench 1 22June2007 TLS 2 liters 2mm
Cod family 2 first vertebra (4.3, 3.5mm) 2 third vertebra 2 fourth vertebra 1 sixth vertebra 35 other vertebra Flatfish 1 vertebra Eel 1 first vertebra 9 other vertebra Herring 4 vertebra Bull-rout 1 vertebra Mackerel 1 vertebra Unidentified 11 vertebra 135E 133N Culture Layer Trench 2 29June2007 KCR 5 liters 2mm Cod family 1 basioccipital 1 second vertebra 2 third vertebra 1 fourth vertebra 1 fifth vertebra 33 other vertebra Flatfish 1 first vertebra 2 other vertebra Eel 20 vertebra Herring 1 first vertebra 15 other vertebra Mackerel 1 vertebra Bull-rout 6 vertebra Unidentified 7 vertebra 134E 135N Culture Layer Trench 3 02July2007 KCR 2 liters 2mm Cod family 1 basioccipital 1 first vertebra (3.6mm) 3 second vertebra 1 third vertebra 13 other vertebra Flatfish 1 vertebra Eel 1 vertebra Herring 1 vertebra Bull-rout 1 vertebra Unidentified 2 vertebra 135E 132N Culture Layer Trench 2 25Jun2007 KCR 2 liters 2mm Cod family 8 vertebra Eel 5 vertebra Bull-rout 1 vertebra Unidentified
2 vertebra 136E 132N Culture Layer Trench 2 24June2007 LRA 2 liters 2mm Cod family 1 fourth vertebra 1 fifth vertebra 11 other vertebra Eel 7 vertebra Herring 2 vertebra Unidentified 3 vertebra 134E 133N Culture Layer Trench 2 25June2007 KCR 2 liters 2mm Cod family 1 second vertebra 6 other vertebra Eel 4 vertebra Herring 5 vertebra Bull-rout 1 vertebra Unidentified 1 vertebra 124E 135N Shell Trench 3 17July2007 KCR 2 liters 4mm Cod family 6 basioccipital 4 first vertebra (5.7, 4.6, 4.4, 4.6mm) 6 second vertebra 6 third vertebra 3 fourth vertebra 4 fifth vertebra 3 sixth vertebra 180 other vertebra 3L 3R otoliths (1 fragment) 4L premaxillary 1 parasphenoid 1L supracleithrum 1L 2R epihyal 3L 2R posttemporal 1L palatine 5L 5R quadrate 4L 2R angular 3L 3R vomer 1R cleithrum Flatfish 6 vertebra Eel 25 vertebra Bull-rout 2 vertebra Gurnard 1 vertebra Unidentified 3 vertebra too dirty 4 other vertebra 46 vertebra fragments 72 other fish fragments 11 fragments mammal/bird 125E 132N Culture Layer Trench 1 22June2007 TLS 2 liters 4mm Cod family 1 first vertebra (3.8mm) 5 second vertebra 2 third vertebra 2 fourth vertebra 1 fifth vertebra 35 other vertebra 1L 2R angular 1L maxillary 2L quadrate 1L premaxillary Eel 2 vertebra Unidentified
16 vertebra fragments 3 other fish fragments 17 fragments mammal 124E 135N Culture Layer Trench 3 06July2007 KCR 2 liters 4mm Cod family 4 basioccipital 6 first vertebra (5.2, 5.0, 5.1, 5.2, 4.8, 7.4mm) 3 second vertebra 5 third vertebra 4 fourth vertebra 5 fifth vertebra 4 sixth vertebra 74 other vertebra 1L 1R posttemporal 2L 1R premaxillary 1L dentary 1L supracleithrum 1R maxillary 2R quadrate 2R hyomandibular 2L 3R angular Flatfish 4 vertebra Eel 17 vertebra Bull-rout 2 vertebra Mackerel 1 vertebra (very small) Unidentified 4 vertebra too dirty 1 small vertebra 33 vertebra fragments 18 other fish fragments 3 fragments mammal 121E 134N Feature A7 Upper Layer Trench 3 18July2007 VLS 2 liters 4mm Cod family 2 basioccipital 1 first vertebra (4.3mm) 6 second vertebra 7 third vertebra 4 fourth vertebra 2 fifth vertebra 1 sixth vertebra 53 other vertebra 2L vomer 1R dentary 1 parasphenoid 2L premaxillary 1L posttemporal 2L quadrate 2L 3R angular 1L hyomandibular Eel 1 vertebra 1 vomer Bull-rout 1 vertebra 1L posttemporal Unidentified 2 vertebra 23 vertebra fragments 17 other fish fragments 27 fragments mammal 136E 132N Culture Layer Trench 2 24June2007 LRA 2 liters 4mm Cod family 2 first vertebra (7.3, 5.6mm) 1 fourth vertebra 4 other vertebra 1R otolith 1L quadrate 1R posttemporal Flatfish 1 vertebra Eel 2 vertebra Unidentified 1 vertebra 3 vertebra fragments 3 other fragments 1 third phalanx (small roe deer?) 135E 132N Culture Layer Trench 2 25June2007 KCR 2 liters 4mm Cod family 5 vertebra 1L maxillary Eel 1 vomer Unidentified
3 fragments fish bone 1 fragment mammal 124E 135N Brown Surface Trench 3 18July2007 KCR 2 liters 4mm Cod family 5 basioccipital 3 first vertebra (7.1, 5.4, 5.1mm) 1 second vertebra 1 third vertebra 3 fourth vertebra 3 fifth vertebra 72 other vertebra 2L & 1 fragment otoliths 1L 1 whole vomer 1R dentary 1 parasphenoid 3L 3R premaxillary 2L angular 1R supracleithrum 1L posttemporal 2L 1R maxillary 2L quadrate Flatfish 3 vertebra Eel 36 vertebra 1R 1(? - dirty) ceratohyal (2.5mm) Bull-rout 1 first vertebra 1 other vertebra 1R preopercle Garfish 1 vertebra Mackerel 3 vertebra Unidentified 11 vertebra too dirty 4 other vertebra 1 quadrate 34 vertebra fragments 102 other fish fragments 5 fragments mammal 134E 135N Culture Layer Trench 3 02July2007 KCR 2 liters 4mm Cod family 1 basioccipital 1 fourth vertebra 17 other vertebra 1 otolith fragment 1L angular 1L premaxillary 1R posttemporal Eel 1 vertebra Unidentified 7 vertebra fragments 2 other fish fragments 134E 133N Culture Layer Trench 2 25June2007 KCR 2 liters 4mm Cod family 1 fifth vertebra 6 other vertebra 1L otolith (eroded) 1L maxillary Bull-rout 1R angular Unidentified 3 other fish fragments 1 fragment mammal 136E 133N Culture Layer Trench 2 25June2007 LRA 2 liters 4mm Cod family 2 first vertebra (5.6mm, no measure) 1 second vertebra 1 fourth vertebra 19 other vertebra 1 vomer 1L supracleithrum 1L angular Eel 1 vertebra Bull-rout 3 vertebra Unidentified 3 vertebra fragments 9 other fish fragments 1 fragment mammal 1 fish scale
125E 135N Shell Trench 3 04July2007 LRA 2 liters 4mm Cod family 2 basioccipital 3 first vertebra (12.4, 6.2, 5.1) 2 second vertebra 1 third vertebra 6 fourth vertebra 2 fifth vertebra 2 sixth vertebra 72 other vertebra 2L 1R otoliths 3L 1R maxillary 2L premaxillary 1R 1 whole vomer 1L dentary 1 parasphenoid 1R supracleithrum 1L 1R quadrate 1L 1R angular 1R cleithrum 3L hyomandibular 1R palatine 1L opercle Flatfish 3 vertebra Eel 5 vertebra Bull-rout 1 vertebra Mackerel 2 vertebra Cyprinid 1 vertebra Unidentified 1 vertebra 19 vertebra fragments 29 other fish fragments 135E 133N Culture Layer Trench 2 29June2007 KCR 5 liters 4mm Cod family 3 basioccipital 2 third vertebra 1 fifth vertebra 42 other vertebra 1L premaxillary 2L dentary 1L 2R vomer 1 parasphenoid 1L 2R posttemporal 1L 2R quadrate 2R maxillary 2L angular 2L 1R supracleithrum Flatfish 2 vertebra 1 os anale Eel 2 vertebra Unidentified 3 vertebra fragments 19 other fish fragments 1 fragment charred nutshell 121E 134N Feature A7 Lower Layer Trench 3 19July2007 VLS 2 liters 4mm Cod family 1 basioccipital 1 first vertebra (4.2mm) 1 third vertebra 3 fourth vertebra 36 other vertebra 1L 1R premaxillary 1L 2R posttemporal 1 parasphenoid 2R angular Flatfish 1 vertebra Eel 2 vertebra Bull-rout 1 vertebra Unidentified 2 vertebra 15 vertebra fragments 12 other fish fragments 11 fragments mammal 125E 133N Culture Layer Trench 1 25June2007 VLS 2 liters 4mm Cod family 2 basioccipital 2 first vertebra (5.6, 4.4mm) 3 second vertebra 1 third vertebra 4 fourth vertebra 2 fifth vertebra 75 other vertebra 1L 1R & 1 fragment otoliths 1L 3R premaxillary
1 parasphenoid 1 vomer 1R hyomandibular 2R quadrate 2R angular 5L 1R maxillary 1R posttemporal Flatfish 2 vertebra Eel 4 vertebra Bull-rout 1 first vertebra 2 other vertebra 1R maxillary Unidentified 3 vertebra too dirty 1 other vertebra 23 vertebra fragments 23 other fish fragments 12 fragments mammal/bird
Bøgebjerg Notes Final 57E 291N Layer 1 Trench 2 23July2003 AR Cod family 1 second vertebra 3 third vertebra 2 other vertebra Flatfish 2 vertebra Unidentified 1 vertebra 2 vertebra fragments 1 other fragment 57E 292N Stratum 1 Kulturlag Trench2 28July2003 Cod family 1 second vertebra 6 other vertebra 2L premaxillary 58E 289N Stratum 1 Cod family 1 fragment vertebra (cf) 1 parasphenoid 58E 296N Layer 5 Trench 2 08August2003 NN Cod family 3 first vertebra (4.9, 8.5, 5.0mm) 1 second vertebra 3 third vertebra 9 other vertebra 1R maxillary Flatfish 5 vertebra Garfish 1 vertebra Unidentified 2 vertebra 9 vertebra fragments (1 burnt) 58E 296N Layer 7 Shell Trench 2 19August2003 NN Cod family 1 first vertebra (6.7mm) 2 other vertebra 1L angular Unidentified 1 vertebra 58E 297N Layer 7 Shell Trench 2 18August2003 LRA Cod family 1 basioccipital 9 first vertebra (6.5, 6.3, 7.5, 5.5, 5.3, 4.6, 4.8, 6.0, 5.3mm) 1 second vertebra 10 third vertebra (1 burnt) 264 other vertebra (3 burnt) 2R premaxillary 1R dentary 1L maxillary 1L quadrate Flatfish 1 basioccipital 5 first vertebra (5.9, 5.5, 4.3mm, 2 no measure) 204 other vertebra (2 burnt) 1L maxillary 1R hyomandibular Eel 6 vertebra Garfish 21 vertebra (2 burnt) Mackerel 3 vertebra Bull-rout 1 first vertebra 13 other vertebra Family Sparidae 1 vertebra
Unidentified 11 vertebra 58E 298N Stratum 5 Trench 2 7August2003 LRA Cod family 1 basioccipital 2 first vertebra (4.7, 5.4mm, 1 burnt) 1 second vertebra 1 third vertebra 75 other vertebra (6 burnt) 1 parasphenoid Flatfish 62 vertebra (4 burnt) 1R maxillary Eel 3 vertebra Mackerel 2 vertebra Spurdog 2 vertebra Garfish 3 vertebra Bull-rout 6 vertebra Unidentified 10 vertebra 58E 298N Stratum 7 Shell Trench 2 19August2003 LRA Cod family 6 basioccipital 5 first vertebra (8.1, 5.0, 5.4, 4.5mm, 1 no measure) 9 second vertebra (1 burnt) 7 third vertebra 265 other vertebra (1 calcined) 1L maxillary 1L 1R hyomandibular 1L premaxillary 1R angular 1 symplectic 1L palatine Flatfish 5 basioccipital 2 first vertebra (4.2, 4.0mm) 285 other vertebra 1R hyomandibular 1R maxillary Eel 3 vertebra Garfish 40 vertebra Herring 2 vertebra (1 calcined) Mackerel 11 vertebra Bull-rout 4 first vertebra 9 vertebra Weever 1 vertebra Spurdog 4 vertebra Unidentified 29 vertebra 58E 299N Layer 7 Shell Trench 2 19August2003 Cod family 1 basioccipital 4 first vertebra (8.1, 7.9, 4.8mm, 1 no measure) 4 second vertebra 4 third vertebra 161 other vertebra 1L premaxillary Flatfish 1 basioccipital 2 first vertebra (4.7, 4.4mm) 169 other vertebra (2 burnt)
1 os anale (in two pieces) 1R posttemporal 1R angular 1 investing bone (flounder) Eel 3 vertebra Spurdog 2 vertebra Mackerel 3 vertebra Garfish 13 vertebra Bull-rout 1 first vertebra 10 other vertebra Weever 2 vertebra Unidentified 6 vertebra 58E 300N Stratum 5 Trench 2 14August2003 LRA Cod family 3 basioccipital 4 first vertebra (4.8, 4.7, 5.7, 5.2mm) 2 second vertebra 1 third vertebra 47 other vertebra (8 burnt) 2L premaxillary 1R angular 1L sphenotic 1L pterotic Flatfish 1 first vertebra (no measure) 46 other vertebra (2 burnt) Eel 3 vertebra (1 burnt) Garfish 4 vertebra (2 burnt) Bull-rout 3 vertebra Weever 1 vertebra Unidentified 3 vertebra 58E 300N Shell lag Trench 2 18August2003 Cod family 3 first vertebra (4.0, 5.8, 4.9mm) 2 second vertebra 1 third vertebra 51 other vertebra Flatfish 1 basioccipital 31 vertebra 1 os anale 1L maxillary 1R pterotic (flounder) Eel 1 vertebra Garfish 10 vertebra Mackerel 1 vertebra Spurdog 3 vertebra (one of these is in two pieces) Weever 1 vertebra Unidentified 3 vertebra 43 vertebra fragments 9 other fragments
58E 300N Lag under skallag Trench 2 20August2003 Cod family 1 third vertebra 21 other vertebra Flatfish 8 vertebra Garfish 1 vertebra Spurdog 2 vertebra Unidentified 5 vertebra fragments 58E 301N Layer 7 Shell Trench 2 15August2003 LRA Cod family 2 basioccipital 1 third vertebra 38 other vertebra 1R supracleithrum Flatfish 15 vertebra Garfish 7 vertebra Spurdog 1 vertebra 1 half vertebra Unidentified 4 vertebra 59E 289N Stratum 1 Trench 3 24July2003 ECS Cod family 1 first vertebra (5.1mm) 3 second vertebra 1 third vertebra 5 other vertebra 1L premaxillary Flatfish 2 vertebra Weever 2 vertebra Unidentified 3 vertebra fragments 59E 289N Layer 1 12August2003 Cod family 1 basioccipital 3 first vertebra (7.0, 4.4, 5.6mm) 11 second vertebra 9 third vertebra 19 other vertebra 1R vomer Flatfish 1 first vertebra (5.6mm) 9 other vertebra (2 burnt) Garfish 1 vertebra Bull-rout 2 vertebra Weever 1 vertebra Unidentified 3 vertebra 10 vertebra fragments 4 other fragments 59E 289N Layer 3 Trench 3 13August2003 Cod family 6 first vertebra (6.7, 5.7, 7.5mm, 3 no measure) 28 second vertebra 32 third vertebra 71 other vertebra (3 burnt) 1L 2R dentary 6L 4R premaxillary (2 fragments) 1L 2R 1 whole vomer 1R supracleithrum
1L 2R posttemporal 1L 4R maxillary (1 burnt) 1 parasphenoid 1 mesethmoid Flatfish 4 first vertebra (5.6, 6,2mm, 2 no measure) 23 other vertebra Garfish 2 vertebra 1 dentary fragment Bull-rout 4 vertebra Weever 4 vertebra Unidentified 12 vertebra (1 calcined, 1 burnt) 60E 289N Layer 1 Trench 3 06August2003 Cod family 4 second vertebra Flatfish 2 vertebra Unidentified 1 vertebra 2 vertebra fragments 60E 289N Stratum 3 Trench 3 08August2003 ECS Cod family 4 first vertebra (8.7, 5.7mm, 2 no measure) 16 second vertebra (1 burnt) 20 third vertebra 57 other vertebra (1 burnt) 12L 11R premaxillary (1 burnt) 1L 4R dentary (1 burnt) 1L vomer 4 parasphenoid 1L 3R maxillary 2L 3R posttemporal (1 burnt) 2L 1R supracleithrum 1R quadrate 1 branchiostegal ray Flatfish 19 vertebra (1 burnt) 1 os anale Eel 1 vertebra Bull-rout 3 vertebra 1L dentary Unidentified 8 vertebra 61E 289N Stratum 2 contact with glacial till 8 Trench 3 29July2003 ECS Cod family 1 second vertebra 69E 282N Kulturlag Cod family 1 second vertebra 69E 282N Lagdelt sand under kulturlag Cod family 1 fourth vertebra 74E 288N Gyttje under skallag Trench 3 2003 Spurdog 1 half vertebra 74E 288N Gyttje under skallag Trench 3 2003 Garfish 6 dentary fragments
74E 288N Gyttje under skallag Trench 3 2003 Garfish 1 dentary fragment Burned nutshell 58E 298N Stratum 5 1 fragment hazelnut 58E 299N Layer 7 Shell 8 fragments hazelnut 60E 289N Stratum 3 2 fragments 58E 300N Stratum 5 7 fragments hazelnut 57E 291N Layer 1 1 fragment hazelnut 59E 289N Stratum 1 1 fragment 58E 300N Lag under skallag 3 fragments 58E 300N Shell lag 2 fragments, 1 fragment acorn 58E 301N Layer 7 Shell 4 fragments 58E 297N Layer 7 Shell 7 fragments hazelnut
Dragsholm Fish Notes
Trench 3 128E 120N Layer 7a Trench 3 16July2003 TLS Garfish 1 dentary 128E 120N Layer 7c Trench 3 16July2003 TLS Weights: 10g bone fragments, 15g charcoal, shell, etc., 3g non-vertebra, 22g cod, 6g flatfish, 7g other vertebra, 2g no ID Cod family 2 basioccipital 4 first vertebra 2 second vertebra 3 third vertebra 181 other vertebra 1L premaxillary 1R quadrate 1L dentary 1L 1R posttemporal 1L maxillary 1L angular 1R prefrontal Flatfish 2 basioccipital 73 other vertebra 1L investing bone Mackerel 2 vertebra Bull-rout 1 vertebra 1R premaxillary Weever 6 vertebra 1R dentary 1L 1R hyomandibular 1L maxillary 1R investing bone 1L opercle 1R posttemporal 1R supracleithrum Garfish 30 vertebra 4 dentary fragments Spurdog 29 vertebra 1 dorsal spine Unidentified 11 vertebra 128E 120N Layer 7d Trench 3 17July2003 TLS Cod family 1 third vertebra 4 other vertebra Flatfish 2 vertebra 1R angular (flounder) Mackerel 1 vertebra Unidentified 1 vertebra 128E 120N Layer 7c/8 Trench 3 21July2003 TLS Cod family 1 second vertebra 11 other vertebra Flatfish 3 vertebra 128E 120N Layer 8 Trench 3 17July2003 TLS Weights: 10g bone fragments, 14g charcoal, shell,, etc, 3g non-vertebra, 13g cod, 1g flatfish, <1g other vertebra Cod family 1 basioccipital 1 first vertebra 8 second vertebra
11 third vertebra 87 other vertebra 1L angular 1R posttemporal 3 parasphenoid 1L 2R premaxillary 1R quadrate 1R cleithrum Flatfish 1 basioccipital 1 first vertebra 23 other vertebra Bull-rout 1 vertebra Garfish 4 vertebra 7 dentary fragments Spurdog 2 vertebra 1 dorsal spine 128E 126N Layer 7c sample Trench 3 23July2003 CF Weights: 12g bone fragments, 4g charcoal, stone and some shell, 3g non-vertebra, 11g cod, 2g flatfish, 1g other vertebra Cod family 1 basioccipital 8 first vertebra 12 second vertebra 11 third vertebra 81 other vertebra 1L 1R supracleithrum 3L 2R premaxillary 2L 1R 2 fragments dentary 3 parasphenoid (2 fragments) 2L 2R maxillary 1R otolith (broken) 1L palatine 2L vomer 1L epihyal 2L 2R posttemporal 1L ceratohyal 4L 4R angular 1L hyomandibular Flatfish 3 first vertebra 33 other vertebra 1 os anale (1 fragment) Weever 2 vertebra Bull-rout 7 vertebra Mackerel 1 vertebra Gurnard 1 dorsal spine Garfish 5 vertebra 1 dentary fragment Unidentified 2 vertebra 128E 126N Layer 7c/8 Trench 3 23July2003 CF Bag 1 Weights: 5 large pieces oyster shell and sand – 28g, 15g bone fragments, 101g cod, 17g flatfish, 6g other vertebra, 1g no ID Cod family 12 basioccipital 36 first vertebra 56 second vertebra 59 third vertebra 741 other vertebra (2 sets of 2 fused) 1, 2, 3, and other vertebra from the same fish – better preserved and chocolate brown color Flatfish 5 basioccipital 12 first vertebra (4.8, 4.7, 4.7, 6.0, 4.7, 4.7, 5.1, 4.6, 4.1, 4.5mm, 2 no measure) 275 other vertebra (3 vertebra turbot) Eel 1 vertebra Garfish 31 vertebra Mackerel 18 vertebra Weever 5 vertebra
Gurnard 3 vertebra Bull-rout 9 vertebra Spurdog 4 vertebra Unidentified 23 vertebra 128E 126N Layer 7c/8 Trench 3 23July2003 CF Cod family 3 second vertebra 3 third vertebra 17 other vertebra 1 parasphenoid 1L 1R dentary 1L angular 1R posttemporal 1L ceratohyal Flatfish 1 first vertebra 17 other vertebra Gurnard 1 vertebra Unidentified 1 vertebra 128E 126N Layer 7c/8 Trench 3 23July2003 CF Weights: <1g bone fragments (9 medium-sized pieces), 1 shark tooth Cod family 7 vomer (1 = 2 halves) 4L 6R angular 7L 6R maxillary 1R palatine 11L 7R quadrate 2L 6R posttemporal 17L 21R premaxillary (1 fragment) 2L 4R dentary 1R ceratohyal 1L hyomandibular 1L sphenotic Flatfish 1L angular 1L maxillary 4L 1R quadrate 1R pterotic Spurdog 1 dorsal spine 128E 126N Layer 7c/8 Trench 3 23July2003 CF Weights: 36g bone fragments, 15g vertebra and non-vertebra Cod family 1 first vertebra (very small) 1 second vertebra 8 other vertebra 1 pharyngeal plate 4L 6R premaxillary (1 fragment) 1 pharyngobranchial 7L 2R dentary (1 fragment) 5L 3R angular 1R palatine 2L opercle 2L 6R ceratohyal 1L 2R vomer 3L 1R posttemporal 8L 13R supracleithrum 8L 3R quadrate 5L 5R cleithrum 2L 1R maxillary 2L 4R 2 fragments hyomandibular 13 parasphenoid (8 fragments) 3 epibranchial 1 branchiostegal ray 1L preopercle 2R lower hypohyal 1L epihyal 2L pterotic Flatfish 1 first vertebra 11 other vertebra (2 ultimate) 1 vomer 1L 1R supracleithrum 1R hyomandibular 5 os anale (4 fragments) Eel 1 first vertebra 2 vertebra Garfish 3 dentary fragments Eelpout 1 vertebra Unidentified
1 vertebra
128E 126N Layer 8 sample Trench 3 23July2003 CF Weights: 12g bone fragments, 5g charcoal, stone and shell, 4g non-vertebra, 8g cod, 2g flatfish, <1g other vertebra, 1g no ID Cod family 1 basioccipital 4 first vertebra 5 second vertebra 5 third vertebra 59 other vertebra 1R 1 whole vomer 1L 1R ceratohyal 1R hyomandibular 3 parasphenoid 6L 3R premaxillary 2L 5R dentary 1L palatine 1L 3R posttemporal 2L 2R quadrate 3R supracleithrum 2L angular 1L 5R maxillary 1R cleithrum 1L symplectic 1R epibranchial Flatfish 3 first vertebra 42 other vertebra (1 ultimate, burnt) 2 prootic 1R supracleithrum 1R hyomandibular 1R quadrate Eel 1 first vertebra 3 vertebra 1R ceratohyal (2.6mm) Gurnard 3 vertebra Weever 2 vertebra 1R ceratohyal Mackerel 5 vertebra Garfish 4 vertebra 1 dentary fragment Spurdog 5 vertebra Bull-rout 1R supracleithrum Unidentified 4 vertebra 1-2 non-vertebra Trench 4
140E 130N Layer 8 Trench 4 16July2004 KCR Weights: 24g bone fragments, 9g charcoal, sand and shell, 6g non-vertebra, 32g cod, 8g flatfish, 7g other vertebra Cod family 3 basioccipital 9 first vertebra 9 second vertebra 10 third vertebra 337 other vertebra 8 parasphenoid 3L 3R premaxillary 1L 1R dentary 1R vomer 5L 1R quadrate 1L 3R angular 1L 2R posttemporal 3L 2R supracleithrum 1L ceratohyal 1L preopercle Flatfish 5 first vertebra 121 other vertebra 1R quadrate 1 os anale 1R premaxillary 2 investing bones 1R maxillary Gurnard 7 vertebra Eel 3 vertebra Bull-rout 9 vertebra
Mackerel 4 vertebra Garfish 26 vertebra 3 dentary fragments Spurdog 49 vertebra 3 dorsal spines (use wear?) Unidentified 15 vertebra 140E 130N Layer 8b Trench 4 17July2004 KCR Weights: 39g bone fragments, 10g charcoal, sand and shell, 49g cod, 9g flatfish, 9g other vertebra, 8g non-vertebra, 2g no ID Cod family 3 basioccipital 14 first vertebra 7 second vertebra 13 third vertebra 437 other vertebra 1R vomer 4 parasphenoid 2L 1R dentary 2L 2R premaxillary 3L 2R maxillary 1L 2R quadrate 2L 1R angular 1L 3R posttemporal 3L 2R supracleithrum 3L 2R hyomandibular 2 branchiostegal rays 3L 2R ceratohyal 1L 1R preopercle 1R sphenotic Flatfish 131 vertebra (including 2 ultimate) 1L 1R hyomandibular 1 os anale Gurnard 3 vertebra Trout/salmon 1 vertebra Weever 7 vertebra Garfish 2 first vertebra 30 other vertebra 5 dentary fragments Mackerel 17 vertebra Spurdog 61 vertebra Unidentified 19 vertebra 140E 130N Layer 8k (no shell) Trench 4 18July2004 KCR Weights: 13g bone fragments, 5g sand and charcoal, 15 g cod, 4g flatfish, <1g other vertebra, <1g no ID, 4g non-vertebra Cod family 2 basioccipital 1 first vertebra 4 second vertebra 3 third vertebra 92 other vertebra 2 branchiostegal rays 2L 1R ceratohyal 1R preopercle 1R maxillary 1 parasphenoid 2R dentary 1L posttemporal 1R hyomandibular 1R supracleithrum Flatfish 1 first vertebra 34 other vertebra 1L dentary (flounder) 1R opercle 1L supracleithrum Bull-rout 2 vertebra Mackerel 1 vertebra Herring 1 vertebra Spurdog
5 vertebra Garfish 1 vertebra Unidentified 5 vertebra (4 eroded, 1 other species?) 1 supracleithrum 140E 130N Layer 9 (rust) Trench 4 18July2004 KCR Cod family 2 vertebra Flatfish 2 vertebra Spurdog 1 vertebra Unidentified 1 vertebra (too dirty) Trench 5
121E 115N Layer 8 Trench 5 19August2003 KCR 27L 33R 8 fragments otoliths 121E 115N Layer 8 Trench 5 21August2003 KCR 7L 9R 2 fragments otoliths 124E 115N Layer 7b Trench 5 08August2003 ERS Cod family 2 first vertebra 1 second vertebra 3 third vertebra 20 other vertebra 1L premaxillary 1R maxillary Flatfish 12 vertebra Spurdog 7 vertebra Bull-rout 2 vertebra Unidentified 2 vertebra 124E 115N Layer 7b transition Trench 5 13August2003 ERS Weights: 15g bone fragments, 3g charcoal, sand and stone, 4g non-vertebra, 17g cod, 11g flatfish, 6g other vertebra, 2g no ID Cod family 2 basioccipital 13 first vertebra 12 second vertebra 22 third vertebra 207 other vertebra 1R posttemporal 1L 1R supracleithrum 1R angular 2L 2R quadrate 1L dentary 1 parasphenoid 3L maxillary 4L 2R premaxillary Flatfish 2 basioccipital 7 first vertebra 202 other vertebra 1 vomer 1L quadrate 1R maxillary Eel 1 vertebra 1 ceratohyal (2.5mm) Gurnard 4 vertebra Bull-rout 1 first vertebra 7 other vertebra Spurdog
22 vertebra 1 dorsal spine Mackerel 2 vertebra Garfish 28 vertebra 13 dentary fragments Unidentified 18 vertebra (1 burnt) 124E 115N Layer 7c grey Trench 5 14August2003 CF Weights: 22g bone fragments, 13g charcoal, sand and shell, 4g non-vertebra, 31g cod, 8g flatfish, 3g other vertebra, 2g no ID Cod family 5 basioccipital 13 first vertebra 6 second vertebra 9 third vertebra 263 other vertebra 3L 1R premaxillary 2L 1R supracleithrum 2 parasphenoid 1R vomer 1L hyomandibular 2L ceratohyal 1L 1R maxillary 2L 4R angular 3L 6R quadrate 1 pharyngobranchial Flatfish 1 basioccipital 3 first vertebra 100 other vertebra (2 burnt, 1 calcined) 1 os anale (2 fragments) Spurdog 5 vertebra Eel 2 vertebra Mackerel 6 vertebra (2 burnt) Garfish 10 vertebra 5 dentary fragments Unidentified 4 vertebra 124E 115N Layer 7c shell Trench 5 14August2003 CF Weights: 17g bone fragments, 4g charcoal and sand, 4g non-vertebra, 31g cod, 9g flatfish, 4g other vertebra, 2g no ID Cod family 5 basioccipital 13 first vertebra 6 second vertebra 15 third vertebra 334 other vertebra 1 whole vomer 1L 3R premaxillary 2L 2R dentary 2L posttemporal 1L maxillary 1L 2R angular 1L ceratohyal 1L preopercle 2L quadrate 1L 1R hyomandibular Flatfish 2 basioccipital 1 first vertebra 150 other vertebra 1 os anale Eel 1 vertebra Weever 1 first vertebra 1 other vertebra Spurdog 12 vertebra Bull-rout 2 vertebra Mackerel 8 vertebra Garfish 16 vertebra 5 dentary fragments
Unidentified 7 vertebra 124E 115N Layer 8 Trench 5 20August2003 CF Weights: 40g bone fragments, 29g charcoal, shell and sand, 33g cod, 9g flatfish, 4g other vertebra, 4g non-vertebra, 3g no ID Cod family 8 basioccipital 16 first vertebra 38 second vertebra 31 third vertebra 244 other vertebra 6L 6R premaxillary 1 parasphenoid 2L 2R dentary 1L angular 2L 1R supracleithrum 3L 4R maxillary 1L 3R quadrate 1R palatine 2L 4R posttemporal Flatfish 2 basioccipital 4 first vertebra 156 other vertebra 1 piece ultimate vertebra fan 1R hyomandibular 1L quadrate Eel 1 vertebra Bull-rout 1 first vertebra 13 other vertebra Mackerel 2 vertebra Spurdog 2 vertebra Garfish 24 vertebra 1 dentary fragment Gurnard 1 vertebra Pike 1 vertebra Unidentified 18 vertebra 1 supracleithrum Trench 11
121E 117N Layer 7a Trench 11 15July2004 CF (‘screen test’) Weights: 12g bone fragments, 12g vertebra and non-vertebra Cod family 3 basioccipital 2 first vertebra 17 second vertebra 10 third vertebra 80 other vertebra (1 calcined) 1R dentary 1R vomer 1L 1R supracleithrum 4 parasphenoid 1R angular 1L 2R posttemporal 1L 2R quadrate 6L 6R premaxillary (1 medium to large, all the rest are small) Flatfish 2 first vertebra 51 other vertebra (1 burnt, 1 calcined) 1R hyomandibular 1 os anale Eel 2 vertebra (sent to Anders Fischer June 2007) Herring 1 vertebra Spurdog 3 vertebra Bull-rout 8 vertebra Weever 6 vertebra Gurnard
3 vertebra Garfish 1 dentary fragment Unidentified 8 vertebra 121E 117N Layer 7b (bottom) Trench 11 07July2004 CF 7 bone fragments Cod family 1 vertebra Flatfish 1 first vertebra 121E 117N Layer 7b Trench 11 09July2004 CF 14 bone fragments Cod family 1 second vertebra 3 other vertebra 1R angular 1R maxillary Flatfish 3 vertebra Unidentified 1 vertebra 121E 117N Layer 7c below first 5cm, lighter oxidized Trench 11 CF 1 of 3 (note included: not screened for fishbone. Level 8 panned out in mid-layer so split off 7c top, 7c mid, 7c/8 lower, probably not ideal) Weights: 3g bone fragments, 1g sand and nutshell, 3g non-vertebra, 13g cod, 1g flatfish, <1g other vertebra, <1g no ID Cod family 2 basioccipital 5 first vertebra 1 second vertebra 2 third vertebra 93 other vertebra 4 parasphenoid 1L 1R supracleithrum 1L 1R sphenotic 3L premaxillary (1 fragment) 1L posttemporal 1R maxillary 2L 1R quadrate 2L angular 2L cleithrum Flatfish 1 first vertebra (5.3mm) 14 other vertebra 1L quadrate 1 os anale (3 fragments) Mackerel 1 vertebra Garfish 1 vertebra Spurdog 5 vertebra Unidentified 1 vertebra 121E 117N Layer 7c top 5cm dark above shell Trench 11 14July2004 CF 2 of 3 Weights: ca. 1g total Cod family 1 third vertebra 7 other vertebra Flatfish 1 vertebra Mackerel 1 vertebra Garfish 1 vertebra
121E 117N Layer 7c/8 lower level Trench 11 14July2004 CF 3 of 3 Weights: <1g two fragments burnt nutshell, 2g bone fragments, 1g non-vertebra, 8g cod, 1g flatfish, <1g other vertebra, <1g no ID Cod family 1 basioccipital 3 first vertebra 3 second vertebra 5 third vertebra 44 other vertebra 1L 1R premaxillary 1L supracleithrum 2R maxillary 1R dentary 1L hyomandibular 1L epihyal 1L cleithrum Flatfish 1 first vertebra (5.9mm) 17 other vertebra (1 burnt) Garfish 2 vertebra Unidentified 1 vertebra 122E 117N Layer 6 Trench 11 30June2004 CF Cod family 1 vertebra 122E 117N Layer 7a Trench 11 30June2004 CF Weights: 2g charcoal (mostly hazelnut), 4g bone fragments, 6g vertebra and non-vertebra Cod family 2 third vertebra 33 other vertebra 1L 1R posttemporal 2L angular 1R premaxillary 1L maxillary Flatfish 14 vertebra 2 os anale 1 urohyal Bull-rout 1 vertebra Spurdog 1 dorsal spine Unidentified 1 vertebra (eroded) 122E 117N Layer 7b Trench 11 09July2004 CF Weights: 10g bone fragments, 12g vertebra Cod family 1 basioccipital 3 first vertebra 19 second vertebra 14 third vertebra (1 calcined) 76 other vertebra 9L 7R premaxillary 2L 3R maxillary 1L 1R dentary 1L 1R vomer 1L 1R supracleithrum 2 parasphenoid 1L posttemporal 2R angular 1L quadrate Flatfish 1 basioccipital 3 first vertebra 48 other vertebra 1L quadrate Gurnard 3 vertebra Spurdog 1 vertebra 1 dorsal spine Garfish 1 first vertebra 4 other vertebra Bull-rout 6 vertebra Unidentified 8 vertebra
122E 117N Layer 7c Trench 11 09July2004 CF (‘screen test’) Weights: 29g bone fragments, 18g charcoal and shell, 25g cod, 7g flatfish, 3g other vertebra Cod family 9 basioccipital 30 first vertebra (1 burnt) 43 second vertebra 51 third vertebra 254 other vertebra 5L 5R 2 fragments otolith 26L 20R 2 fragments premaxillary 3L 5R dentary 4L 4R posttemporal 9L 6R angular 3L 7R quadrate 5L 11R supracleithrum 3L 7R maxillary 4L 3R 3 whole vomer 14 parasphenoid 1L hyomandibular 1R ceratohyal 1R preopercle 1 epibranchial Flatfish 8 first vertebra (4.7, 4.5, 3.9, 5.0, 4.1, 3.1mm 2 no measure) 1 basioccipital 131 other vertebra 1 urohyal 1 os anale fragment 1L 1R pterotic (flounder) 1L maxillary 1R supracleithrum 1R dentary 1L quadrate 1L posttemporal Spurdog 8 vertebra 1 dorsal spine Trout/salmon 1 vertebra Garfish 10 vertebra 3 dentary fragments Mackerel 10 vertebra Eel 10 vertebra (9 vertebra, cleithrum and ceratohyal sent to Anders Fischer June 2007) 1R cleithrum (2.1mm) 1L ceratohyal (2.3mm) Bull-rout 1 basioccipital 1 first vertebra 16 other vertebra 2R preopercle Gurnard 4 vertebra 1 dorsal spine plate (grey gurnard) Weever 1 vertebra Cyprinid 1 vertebra Herring 1 prooticum Unidentified 17 vertebra 122E 117N Layer 8 Trench 11 13July2004 CF #1 Weights: 60g bone fragments, 42g charcoal, shell and stone, 17g non-vertebra, 49g cod, 14g flatfish, 4g other vertebra, 2g no ID, 3g otolith Cod family 8 basioccipital 28 first vertebra 62 second vertebra 48 third vertebra 448 other vertebra (1 calcined) 9 parasphenoid (2 fragments) 23L 25R premaxillary (2 fragments) 4L 6R dentary 5L 7R 1 whole vomer 16L 13R quadrate 1 pharyngeal plate 1R epihyal 1R ceratohyal 1R sphenotic 1L preopercle 2 interhyal 3 epibranchial 10L 11R posttemporal 11L 12R supracleithrum 2L hyomandibular 2R cleithrum 1L 1R palatine 8L 9R maxillary 18L 12R angular 1L opercle 13L 14R 6 fragments otoliths Flatfish 7 basioccipital 8 first vertebra (6.3, 5.0, 5.5, 4.0, 4.4, 4.5, 4.4mm, 1 no measure) 218 other vertebra (1 burnt) 2 os anale 1L palatine
1L pterotic (flounder) 1L quadrate 1 pharyngobranchial Herring 2 vertebra Eel 5 vertebra 1 urohyal 1R quadrate Garfish 4 vertebra 5 dentary fragments Spurdog 16 vertebra Mackerel 17 vertebra Bull-rout 1 first vertebra 7 other vertebra Weever 9 vertebra Unidentified 28 vertebra 7 non-vertebra 122E 117N Layer 8 Trench 11 13July2004 CF #2 Weights: 14g bone fragments, 6g charcoal, stone and shell, 9g non-vertebra, 17g cod, 6g flatfish, 3g other vertebra, 2g no ID Cod family 1 basioccipital 10 first vertebra 14 second vertebra 15 third vertebra 109 other vertebra 6 parasphenoid (2 fragments) 6L 4R premaxillary 4L 3R dentary 4L 4R vomer 1 epibranchial 2L 1R angular 1L 1R (in two ½s) cleithrum 1R hyomandibular 1 branchiostegal ray 1R epihyal 1R hypohyal 1R ceratohyal 4L 2R maxillary 1L 2R quadrate 1L 1R supracleithrum 1L 3R posttemporal 1 interhyal Flatfish 3 basioccipital 3 first vertebra (5.1, 4.6, 4.1mm) 65 other vertebra 1 os anale 1L pterotic (flounder) 1L quadrate 2 urohyal 1L angular 1R cleithrum Eel 3 vertebra Spurdog 2 vertebra Garfish 2 vertebra Mackerel 14 vertebra (7 burnt) Herring 1 vertebra Weever 1 vertebra Bull-rout 1 first vertebra 1 other vertebra Unidentified 7 vertebra 2 non-vertebra 122E 117N Layer 8 Trench 11 13July2004 CF #3 Weights: 20g bone fragments, 6g charcoal, stone and sand, 7g non-vertebra, 22g cod, 7g flatfish, 2g other vertebra, 2g no ID Cod family
8 basioccipital 11 first vertebra 20 second vertebra 26 third vertebra 138 other vertebra (2 burnt) 5L 9R premaxillary (2 fragments) 5 parasphenoid 1L 1R ceratohyal 2L 2R dentary 1L hyomandibular 2L 1R quadrate 3L 4R angular 5L 3R supracleithrum 2L 1R vomer 2L 2R maxillary 3L 2R posttemporal Flatfish 3 first vertebra (5.5, 5.3, 5.2mm) 107 other vertebra (3 burnt) Bull-rout 5 vertebra Spurdog 1 vertebra Garfish 3 vertebra Mackerel 3 vertebra Gurnard 1L frontal (grey gurnard) Unidentified 5 vertebra 123E 116N Layer 7a Trench 11 07July2004 BO Weights: 2g charcoal and stone, 3g vertebra and non-vertebra, 3g bone fragments Cod family 1 third vertebra 21 other vertebra 1L premaxillary (very small) 1L vomer Flatfish 1 first vertebra 2 other vertebra Unidentified 1 vertebra (eroded) 123E 116N Layer 7b Trench 11 07July2004 BO Weights: 87g bone fragments, 24g charcoal, sand and stone, 12g non-vertebra, 25g cod, 13g flatfish, 6g other vertebra, 3g no ID Cod family 12 basioccipital 38 first vertebra 48 second vertebra 59 third vertebra 307 other vertebra (2 burnt) 3L 1R supracleithrum 1 parasphenoid 41L 29R premaxillary 1 branchiostegal ray 2L hyomandibular 3L 5R dentary 10L 6R 1 whole vomer 6L 6R quadrate 4L 7R angular 12L 8R maxillary 7L 10R posttemporal 1R epihyal Flatfish 18 first vertebra (4.7, 4.7, 4.6, 5.2, 6.4, 5.5, 5.8, 4.6, 4.3, 4.3, 3.2, 4.3, 5.6mm, 5 no measure) 1 basioccipital 254 other vertebra (5 burnt, 1 calcined) 1 vomer 2 os anale 1L supracleithrum Eel 1 first vertebra 13 vertebra Mackerel 4 vertebra Garfish 1 first vertebra 15 other vertebra 5 dentary fragments Spurdog 8 vertebra Herring 1 vertebra Weever
1 first vertebra 9 other vertebra Gurnard 6 vertebra Bull-rout 3 first vertebra 36 other vertebra (1 calcined) 1R angular Eelpout 2 vertebra Whitefish 2 vertebra Unidentified 27 vertebra 123E 116N Layer 7c Trench 11 09July2004 BO 3 pieces charcoal, 3 bone fragments Cod family 1 third vertebra 1 other vertebra 1R supracleithrum Flatfish 1 first vertebra 2 other vertebra Unidentified 1 vertebra 123E 116N Layer 7c Trench 11 09July2004 BO 14 bone fragments Cod family 1 basioccipital 1 first vertebra 5 other vertebra 2 parasphenoid 1L 1R premaxillary Spurdog 2 dorsal spines (use wear?) Flatfish 1 os anale 123E 116N Layer 7c Trench 11 09July2004 BO Weights: 116g bone fragments, 94g charcoal, shell and stone, 26g non-vertebra, 95g cod, 28g flatfish, 15g other vertebra, 5g no ID, 2g otolith Cod family 47 basioccipital 101 first vertebra 113 second vertebra 119 third vertebra 1551 other vertebra (1 burnt, 1 calcined) 6L 9R 2 fragments otolith 4 branchiostegal rays 21 parasphenoid (4 fragments) 18L 12R dentary (1 fragment) 63L 65R premaxillary 46L 43R quadrate 38L 49R maxillary 24L 22R angular 12L 11R supracleithrum 15L 22R 2 whole vomer 3L 2R hyomandibular 2L 4R ceratohyal 19L 19R posttemporal 1L 1R epihyal 7 epibranchial 2R sphenotic 2R opercle 1L 1R cleithrum 2L exoccipital 2 mesethmoid Flatfish 23 first vertebra (5.2, 5.1, 3.3, 4.6, 4.7, 4.0, 3.3, 5.8, 4.9, 3.7, 4.4, 3.7, 5.3, 2.8, 4.3, 3.8, 4.1, 4.0mm, 5 no measure) 12 basioccipital 665 other vertebra (6 burnt, 1 calcined) 7 os anale (1 fragment) 2L supracleithrum 3R maxillary 2L 1R quadrate 4 vomer 3 urohyal 2L 1R pterotic (flounder) 1R premaxillary 1 palatine 1 investing bone 2L posttemporal 1R pterotic (not flounder) Mackerel 73 vertebra (2 burnt) Garfish 44 vertebra 3 dentary fragments
Spurdog 76 vertebra 2 dorsal spines (1 fragment) Eel 1 basioccipital 2 first vertebra 56 other vertebra 4L 1R ceratohyal (1.8, 2.1, 2.4, 2.0, 2.1mm) 1L maxillary Herring 16 vertebra 4 prooticum Bull-rout 2 basioccipital 8 first vertebra 103 other vertebra 1R opercle Weever 1 first vertebra 11 other vertebra Gurnard 9 vertebra 2 dorsal plates (grey gurnard) Shad 3 vertebra Eelpout 4 vertebra Pike 1 vertebra Perch 2 vertebra Unidentified 61 vertebra 22 non-vertebra 123E 116N Layer 7c Trench 11 14July2004 BO 8 bone fragments Cod family 2 basioccipital 1R angular 1L dentary 1 parasphenoid 1L premaxillary Flatfish 1 vertebra 123E 116N Layer 7c Trench 11 14July2004 BO Weights: 143g bone fragments, 86 charcoal, shell, sand and stone, 30g non-vertebra, 163g cod, 42g flatfish, 8g other vertebra, 7g otolith, 8g no ID Cod family 57 basioccipital 100 first vertebra 126 second vertebra (1 burnt) 154 third vertebra (2 burnt) 2098 other vertebra (11 burnt) 27L 22R 7 fragments otolith 16 parasphenoid 8L 6R hyomandibular 18L 31R dentary 25L 28R posttemporal 22L 14R supracleithrum 35L 30R quadrate 31L 32R angular 38L 34R maxillary 24L 18R 2 whole vomer 44L 64R 4 fragments premaxillary 6L 5R epihyal 2 mesethmoid 4L 1R ceratohyal 4 branchiostegal rays 1L 1R preopercle 1L 4R palatine 1L 1R opercle 6 epibranchial 1 ceratobranchial 2 pharyngeal plates 1 pharyngobranchial 5L 6R sphenotic 2 basibranchial 1L retroarticular 2R opisthotic 2L 1R 6 fragments cleithrum Flatfish 30 first vertebra (1 burnt) (4.9, 4.7, 5.5, 5.0, 3.9, 4.2, 3.4, 4.8, 4.4, 3.8, 5.8, 4.3, 5.5, 5.4, 4.7, 6.2, 3.3, 4.0, 3.2, 4.0, 3.9, 3.6mm, 8 no measure) 20 basioccipital 927 other vertebra (1 turbot, 3 ultimate, 15 burnt) 4 vomer 2L 3R pterotic (flounder) 2R pterotic 1L 4R maxillary 2L 2R angular 1L 1R quadrate 4L 2R posttemporal 5 os anale (5 fragments) 1L supracleithrum 1L palatine 5 urohyal 1R hyomandibular
1L pharyngobranchial Eel 1 basioccipital 1 first vertebra 65 other vertebra (3 burnt) 1 vomer 1L cleithrum (3.3mm) 1R quadrate Spurdog 48 vertebra 1 dorsal spine (2 fragments) Mackerel 52 vertebra (8 burnt) Herring 2 first vertebra 15 other vertebra 5 prooticum Garfish 2 first vertebra 40 other vertebra 6 dentary fragments Trout/salmon 1 vertebra Pike 1 vertebra Weever 22 vertebra Gurnard 2 first vertebra 18 other vertebra 1 dorsal ray 1L opercle 2 dorsal plates (grey gurnard) Bull-rout 2 basioccipital 1 first vertebra 32 other vertebra 1R maxillary 1R quadrate Eelpout 2 vertebra Perch 2 vertebra Unidentified 83 vertebra 49 non-vertebra 123E 116N Layer 8 Trench 11 13July2004 BO Weights: 28g charcoal, shell and stone, 37g bone fragments, 22g otoliths, 36g cod, 6g other vertebra (including flatfish), 12g non-vertebra Cod family 9 basioccipital 13 first vertebra 43 second vertebra 35 third vertebra 255 other vertebra 80L 90R 24 fragments otolith 5 parasphenoid 15L 18R 3 fragments premaxillary 3L 7R vomer 10L 7R dentary 7L 13R maxillary 9L 8R posttemporal 5L 5R quadrate 8L 9R angular 3L 2R supracleithrum Flatfish 1 first vertebra (no measure) 77 other vertebra 1 vomer 2 os anale 1L premaxillary (flounder) Spurdog 2 vertebra 1 dorsal spine Mackerel 8 vertebra Garfish 4 vertebra Bull-rout 1 vertebra Gurnard 2 vertebra Unidentified 20 vertebra
123E 116N Layer 8 Trench 11 14July2004 CF 11 bone fragments Cod family 1 parasphenoid 1L 1R premaxillary 123E 117N Layer 6 Trench 11 02July2004 BO Cod family 1 parasphenoid 123E 117N Layer 7a Trench 11 02July2004 BO 4 bone fragments, 2 burnt hazelnut shell fragments Flatfish 1 os anale 123E 117N Layer 7a Trench 11 06July2004 BO Weights: 4g bone fragments, 1g charcoal and stone, 7g fishhook in container, 5g vertebra and non-vertebra Cod family 3 basioccipital 2 first vertebra 2 second vertebra 3 third vertebra 41 other vertebra Flatfish 8 vertebra (1 calcined) 1R pharyngobranchial Spurdog 1 vertebra 1 dorsal spine (usewear?) Bull-rout 4 vertebra Unidentified 4 vertebra 123E 117N Layer 7b Trench 11 05July2004 BO 15 pieces charcoal, 4g bone fragments Cod family 2 vertebra 8L 4R premaxillary 1L 1 whole vomer 2L angular 1L quadrate 1L 2R maxillary Flatfish 1 first vertebra 1 other vertebra Garfish 1 dentary fragment 123E 117N Layer 7b Trench 11 05July2004 BO Weights: 55g bone fragments, 14g stone, charcoal and sand, 2g no ID, 25g cod, 11g flatfish, 3g other vertebra, 7g non-vertebra Cod family 6 basioccipital 15 first vertebra 44 second vertebra 46 third vertebra 269 other vertebra 16L 10R premaxillary 9L 4R maxillary 1L 1R supracleithrum 3L 1R dentary 1L 2R 1 whole vomer 2 parasphenoid 2L 3R posttemporal 4L 6R angular 6L 4R quadrate 1R opercle Flatfish 14 first vertebra 190 other vertebra 1L angular 1L quadrate 1 os anale 1 urohyal 1L palatine 1R maxillary Garfish 13 vertebra 1 dentary fragment Eel
2 vertebra Herring 1 vertebra Mackerel 1 vertebra Spurdog 4 vertebra Bull-rout 1 first vertebra 16 other vertebra Gurnard 7 vertebra Unidentified 23 vertebra 123E 117N Layer 7c Trench 11 14July2004 BO 11 pieces burnt hazelnut shell Weights: 3g bone fragments and nutshell, 5g vertebra and non-vertebra Cod family 2 vertebra 6 parasphenoid 2R premaxillary 1L dentary 1R angular Flatfish 2 vertebra 1 urohyal 1 os anale Spurdog 3 dorsal spines Unidentified 1 vertebra (very small) 123E 117N Layer 8 Trench 11 15July2004 LRA 1 bone fragment Cod family 1R maxillary 1 parasphenoid 123E 117N Layer 8 Trench 11 15July2004 LRA Weights: 1g bone fragments, 11g vertebra and non-vertebra Cod family 1 basioccipital 4 first vertebra 2 second vertebra 6 third vertebra 48 other vertebra 1R posttemporal 1R maxillary 1R angular Flatfish 16 vertebra (1 calcined) Garfish 4 vertebra Mackerel 1 vertebra Unidentified 1 vertebra 124E 116N Layer 6 Trench 11 30June2004 LRA Cod family 1 vertebra 124E 116N Layer 7a Trench 11 01July2004 LRA Cod family 2 vertebra Unidentified 2 vertebra (eroded)
124E 116N Layer 7b Trench 11 05July2004 LRA Unidentified 2 vertebra fragments 2 other fragments 124E 116N Layer 7b Trench 11 05July2004 LRA Cod family 1 third vertebra 1 other vertebra 1L premaxillary Flatfish 2 vertebra (1 calcined) Garfish 2 dentary fragments 124E 116N Layer 7b Trench 11 05July2004 LRA Weights: 34g fragments, 20g cod, 12g flatfish, 4g other vertebra Cod family 6 basioccipital 21 first vertebra 27 second vertebra 40 third vertebra 270 other vertebra (2 burnt, 1 calcined) 1 mesethmoid 1 supraoccipital Flatfish 2 basioccipital 7 first vertebra (6.6, 4.8, 3.5, 3.8, 3.5mm, 2 no measure) 250 other vertebra (4 burnt, 1 calcined) Eel 8 vertebra (7 sent to Anders Fischer June 2007) Mackerel 3 vertebra Garfish 2 first vertebra 15 other vertebra Herring 1 first vertebra 2 vertebra 1 prooticum Spurdog 24 vertebra Gurnard 2 first vertebra 12 other vertebra Weever 1 first vertebra Bull-rout 1 first vertebra (broken) 11 vertebra Eelpout 2 vertebra Unidentified 35 vertebra (1 calcined) 124E 116N Layer 7c (top) Trench 11 09July2004 LRA Weights: 24g fragments, 8g non-vertebra, 6g other vertebra, 39g cod, 7g flatfish Cod family 11 basioccipital 15 first vertebra 7 second vertebra 17 third vertebra 354 other vertebra (1 burnt) 1L 1R otolith 1L 1 whole vomer 10L 8R 1 fragment premaxillary 9 parasphenoid 4L supracleithrum 3L 4R dentary 3L 2R posttemporal 1L 6R angular 1L 5R quadrate 1L 1R prefrontal 2R hyomandibular 1L preopercle 1L maxillary 1R cleithrum Flatfish 5 basioccipital 1 first vertebra 122 other vertebra 1L maxillary 3 os anale (4 fragments) 1R hyomandibular
1R investing bone Eel 6 vertebra 1 vomer Mackerel 18 vertebra Garfish 20 vertebra 4 dentary fragments Herring 4 vertebra Spurdog 41 vertebra 5 dorsal spines (2 with usewear?) Gurnard 3 vertebra 1L frontal Shad 2 vertebra Bull-rout 4 vertebra Unidentified 18 vertebra 124E 116N Layer 7c Trench 11 09July2004 LRA Unidentified 1g fragments 124E 116N Layer 8 Trench 11 12July2004 LRA Weights: 3g non-vertebra, 13g cod, 3g flatfish, <1g other vertebra, 13g fragments Cod family 2 basioccipital 8 first vertebra 14 second vertebra 7 third vertebra 110 other vertebra 2L 1R 2 fragments otolith 3L 3R premaxillary 5 parasphenoid 1L 3R angular 2L quadrate 1L 1R maxillary 2L 1R supracleithrum 1L 3R vomer 3L 3R posttemporal 1 epibranchial 1 dentary fragment 1L 1R hyomandibular Flatfish 2 first vertebra 51 other vertebra (1 burnt) 1 fragment os anale Eel 1 vertebra 1 vomer (5.0mm) (sent to Anders Fischer June 2007) 1R dentary Mackerel 1 vertebra Garfish 2 vertebra Pike 1 vertebra Trout/salmon 1 vertebra Bull-rout 3 vertebra Unidentified 9 vertebra 124E 116N Layer 8 Trench 11 12July2004 LRA Cod family 1 vertebra 1L 1R otolith 124E 116N Layer 8
77g otolith 304L 277R 96 fragments 124E 117N Layer 7a Trench 11 01July2004 LRA Weights: 4g bone fragments, 1g charcoal, 4g vertebra and non-vertebra Cod family 1 first vertebra 2 second vertebra 1 third vertebra 24 other vertebra 1R angular Flatfish 4 vertebra Spurdog 2 vertebra 124E 117N Layer 7b Trench 11 02July2004 LRA Weights: 32g cod, 17g flatfish, 32g fragments, 8g non-vertebra, 6g other vertebra, 3g charcoal Cod family 3 basioccipital 30 first vertebra 32 second vertebra 39 third vertebra 397 other vertebra (5 burnt) 14L 11R premaxillary 9L 2R maxillary 2L 4R quadrate 3L 8R angular 2L 2R posttemporal 1R supracleithrum 2L 3R vomer 6 parasphenoid 1L 3R dentary 1R epihyal Flatfish 15 first vertebra (4.3, 5.5, 4.4, 5.3, 4.4, 5.5, 6.8, 4.0, 5.1, 5.2, 3.9mm, 4 no measure) 1 basioccipital 345 other vertebra (3 burnt, 2 calcined) 1 urohyal 2R quadrate Eel 4 vertebra Mackerel 4 vertebra Spurdog 9 vertebra 3 dorsal spines Garfish 42 vertebra 15 dentary fragments Trout/salmon 1 vertebra Gurnard 11 vertebra Bull-rout 1 first vertebra 17 other vertebra (1 burnt, 1 calcined) Cyprinid 1 vertebra Unidentified 37 vertebra (1 burnt) 1 maxillary 1L quadrate 124E 117N Layer 7b Trench 11 02July2004 LRA 2 vertebra fragments 124E 117N Layer 7b Trench 11 02July2004 LRA 9 bone fragments Cod family 1 vertebra 3L premaxillary 1R vomer 1R maxillary 1R angular 1L quadrate Flatfish 1 urohyal 124E 117N Layer 7b Trench 11 05July2004 LRA Flatfish
1 fragment os anale Herring 1 vertebra 124E 117N Layer 7c Trench 11 06July2004 LRA 1 small mammal ulna? Cod family 1 vertebra Flatfish 1 vertebra 124E 117N Layer 7c Trench 11 06July2004 LRA 5 bone fragments Cod family 1 vertebra 1L premaxillary 3 parasphenoid 124E 117N Layer 7c Trench 11 07July2004 LRA Weights: 75g charcoal, shell and stone, 130g fragments, 48g flatfish, 142g cod, 10g other vertebra, 21g non-vertebra Cod family 50 basioccipital 103 first vertebra 94 second vertebra (1 calcined) 144 third vertebra 1615 other vertebra (1 calcined) 15L 16R 4 fragments otolith 1L epibranchial 1L 1R palatine 2L 1? hyomandibular 10L 16R maxillary 10L 5R posttemporal 7L 11R supracleithrum 13L 16R quadrate 26L 17R angular 8L 17R vomer 14 parasphenoid 7L 8R dentary 47L 32R premaxillary 1 interhyal 1 basibranchial Flatfish 7 basioccipital 19 first vertebra 923 other vertebra 2R maxillary 4 vomer 2L 1R quadrate 1 investing bone (flounder) 1L supracleithrum 1L 2R posttemporal 1 urohyal 1R pterotic (flounder) Eel 13 vertebra 1 ceratohyal (1.5mm) 1R cleithrum (2.3mm) 1 vomer Mackerel 49 vertebra Garfish 2 first vertebra 52 other vertebra 7 dentary fragments Spurdog 24 vertebra 3 dorsal spines Herring 2 vertebra Gurnard 5 vertebra Weever 9 vertebra Bull-rout 2 first vertebra 26 other vertebra (1 burnt) 1R maxillary Unidentified 114 vertebra (6 basioccipital) 124E 117N Layer 8 27g otolith 103L 99R 51 fragments 124E 117N Layer 8 Trench 11 08July2004 LRA
Weights: 12g bone fragments, 17g charcoal, shell and stone, 11g all vertebra, 3g non-vertebra Cod family 2 basioccipital 3 first vertebra 10 second vertebra 16 third vertebra 59 other vertebra 1L 1R dentary 2L 2R maxillary 1L 6R premaxillary 1L 1R vomer 2 parasphenoid 2L 1R supracleithrum 3L 3R posttemporal 1L 1R angular 1L 5R 1? quadrate Flatfish 2 first vertebra 42 other vertebra 1L upper hypohyal Spurdog 2 vertebra Garfish 3 vertebra Gurnard 3 vertebra Bull-rout 1 vertebra Unidentified 8 vertebra 1 shark tooth 124E 117N Layer 8 Trench 11 08July2004 LRA Cod family 1 second vertebra Spurdog 1 vertebra 125E 116N Layer 7a Trench 11 01July2004 KCR 1 fragment burnt hazelnut shell 1 bone fragment Cod family 3 vertebra 1R quadrate 1R angular 125E 116N Layer 7b Trench 11 06July2004 KCR Weights: 54g bone fragments, 24g sand, charcoal and stone, 4g non-vertebra, 16g cod, 10g flatfish, 3g other vertebra, 1g no ID Cod family 6 basioccipital 22 first vertebra 13 second vertebra 11 third vertebra 255 other vertebra (2 calcined) 1L 1 whole vomer 1L posttemporal 4L 2R dentary (1 calcined) 4L 1R angular 2L 7R premaxillary 1R supracleithrum 2L 1R hyomandibular 1L 2R quadrate 4 parasphenoid 1R ceratohyal 2L maxillary 1 epibranchial Flatfish 5 basioccipital 8 first vertebra (3.7, 4.7, 5.7, 6.0, 3.6, 3.6mm, 2 no measure) 234 other vertebra (1 ultimate, 2 burnt, 2 calcined) 1L angular Eel 1 basioccipital 4 other vertebra 2 vomer 1L ceratohyal (2.5mm) 1R dentary Mackerel 1 vertebra Garfish 21 vertebra 19 dentary fragments Bull-rout 1 first vertebra 22 other vertebra Herring 2 vertebra Weever
8 vertebra Spurdog 15 vertebra 3 dorsal spines Unidentified 16 vertebra 125E 116N Layer 7c incomplete Trench 11 07July2004 KCR Weights: 27g bone fragments, 14g charcoal, sand and shell, 3g non-vertebra, 12g cod, 9g flatfish, 2g other vertebra, <1g no ID Cod family 4 basioccipital 7 first vertebra 4 second vertebra 12 third vertebra 230 other vertebra (3 burnt) 3L 3R premaxillary 3R dentary 1R supracleithrum 6L 2R maxillary 1L hyomandibular 1L palatine 1L 3R quadrate 2L angular Flatfish 4 basioccipital 8 first vertebra (4.7, 4.2, 4.8, 4.1mm, 4 no measure) 216 other vertebra (3 burnt, 1 calcined, 3 fused) 1R quadrate 1R prootic 1 ceratobranchial Bull-rout 1 first vertebra 21 other vertebra Herring 1 vertebra Eel 10 vertebra (1 calcined) Gurnard 2 vertebra Spurdog 7 vertebra Mackerel 2 vertebra Weever 1 first vertebra 8 other vertebra Garfish 11 vertebra 18 dentary fragments Unidentified 15 vertebra 125E 117N Layer 7a Trench 11 01July2004 KCR Cod family 1 first vertebra 1 third vertebra 9 other vertebra (1 burnt) 1R premaxillary Flatfish 4 vertebra Garfish 1 vertebra Spurdog 1 dorsal spine Unidentified 3 vertebra fragments 125E 117N Layer 7b Trench 11 05July2004 KCR Weights: 71g bone fragments, 32g charcoal, shell, stone and sand, 8g non-vertebra, 19g cod, 14g flatfish, 3g other vertebra, 3g no ID Cod family 1 basioccipital 26 first vertebra 21 second vertebra
24 third vertebra 298 other vertebra (2 burnt) 1 parasphenoid 12L 2R 1 fragment premaxillary 2L 4R vomer 1L 1R dentary 7L 1R angular 3L 1R supracleithrum 5L 2R maxillary 5L 1R posttemporal 4L 5R quadrate 1R palatine 1L 1R ceratohyal 1R hyomandibular 2 epibranchial 1L cleithrum Flatfish 11 first vertebra (4.7, 4.3, 3.8, 4.5, 4.3, 4.5, 4.7, 4.3, 4.7, 4.4mm, 1 no measure) 1 basioccipital 256 other vertebra (6 burnt) 2 os anale 1L 2R quadrate 2L posttemporal 1R dentary Eel 2 first vertebra 6 other vertebra Bull-rout 2 first vertebra 17 other vertebra 1L angular Garfish 12 vertebra 23 dentary fragments Spurdog 14 vertebra 1 dorsal spine Herring 2 vertebra Gurnard 4 vertebra Weever 2 vertebra Unidentified 38 vertebra 125E 117N Layer 7c Trench 11 12July2004 KCR Weights: 88g bone fragments, 37g charcoal, shell and stone, 18g non-vertebra, 73g cod, 41g flatfish, 12g other vertebra, 6g no ID, 3g otolith Cod family 28 basioccipital 41 first vertebra 32 second vertebra (1 calcined) 38 third vertebra 1062 other vertebra (6 burnt, 1 calcined) 11L 5R otolith 10 parasphenoid (3 fragments) 15L 16R premaxillary (3 fragments) 2 branchiostegal rays 9L 7R dentary 9L 11R angular 3L 7R 7 whole vomer 11L 6R posttemporal 2L 6R supracleithrum 6L 5R maxillary 3L ceratohyal 9L 8R quadrate 1R palatine 8L 6R hyomandibular 1R epihyal 2L 1R cleithrum 1L sphenotic 2L 3R preopercle 2L symplectic 1L pharyngeal plate 1R pterotic Flatfish 10 basioccipital 7 first vertebra (5.2, 4.5, 6.5, 4.4, 4.9, 4.4mm, 1 no measure) 759 other vertebra (7 burnt) 2 vomer 1 os anale (1 fragment) 1R dentary 1R premaxillary 1R angular 1L 1R quadrate 2R hyomandibular (flounder) 1L 1R hyomandibular (dab) 1R palatine 1L pterotic (flounder) 1 exoccipital 2L posttemporal Herring 7 vertebra 1 prooticum Eel 1 first vertebra 21 other vertebra 1R ceratohyal (2.0mm) Spurdog 44 vertebra 1 dorsal spine Garfish 53 vertebra 15 dentary fragments Mackerel
48 vertebra (5 burnt) Bull-rout 2 first vertebra 20 other vertebra 1R supracleithrum Weever 14 vertebra Gurnard 7 vertebra 1 basioccipital (grey gurnard) Perch 1 vertebra Whitefish 1 vertebra Unidentified 44 vertebra 28 non-vertebra 125E 117N Layer 7c Trench 11 14July2004 KCR Weights: 109g bone fragments, 109g charcoal, shell and stone, 22g non-vertebra, 84g cod, 36g flatfish, 2g otolith, 7g other vertebra, 8g no ID, 2g otolith Cod family 20 basioccipital 42 first vertebra 46 second vertebra 53 third vertebra 1168 other vertebra (3 burnt) 3L 9R 2 fragments otolith 3L 10R dentary 18L 20R premaxillary 6 parasphenoid 16L 13R maxillary 1L 2R ceratohyal 8L 15R angular 11L 13R posttemporal 15L 16R quadrate 3L 6R supracleithrum 8L 6R vomer 5L 7R hyomandibular 2L 2R 1 fragment cleithrum 7 epibranchial 3L 4R sphenotic 1R epihyal 1R opercle 1R interopercle 2L 1R pterotic 1 pharyngeal plate Flatfish 19 first vertebra (4.9, 4.3, 4.1, 4.1, 4.5, 4.3, 4.4, 3.9, 3.7, 3.9, 4.4, 4.9, 5.0, 5.2, 5.1, 4.2, 5.0, 4.2mm, 1 no measure) 15 basioccipital 859 other vertebra (9 burnt) 2 os anale 6 vomer 2L 1R dentary 3L 1R quadrate 1R supracleithrum 3L 2R angular 2 urohyal 2L 2R hyomandibular 3L palatine 1R upper hypohyal 3R posttemporal 1R premaxillary 1R pterotic (flounder) 1R pterotic (plaice) 1L preopercle Eel 38 vertebra 1 vomer Spurdog 44 vertebra Herring 19 vertebra 2 prooticum Garfish 1 first vertebra 21 other vertebra 1 dentary fragment Mackerel 50 vertebra Trout/salmon 1 vertebra Bull-rout 23 vertebra Weever 13 vertebra Gurnard 6 vertebra Eelpout 1 vertebra
Unidentified 81 vertebra 46 non-vertebra 125E 117N Layer 8 Trench 11 15July2004 KCR Weights: 37g bone fragments, 30g charcoal, shell and stone, 7g non-vertebra, 25g cod, 3g flatfish, 2g other vertebra, 1g otolith, <1g no ID Cod family 3 basioccipital 14 first vertebra 24 second vertebra 30 third vertebra (2 burnt) 182 other vertebra (1 burnt) 3L 3R 6 fragments otolith 3L 2R 1 whole vomer 15L 10R premaxillary 4L 4R dentary 1 branchiostegal ray 6 parasphenoid 1L sphenotic 6L 4R supracleithrum 6L 8R posttemporal 1L 1R palatine 1L 3R maxillary 3L 2R angular 2L ceratohyal 2L 1R hyomandibular 1 epibranchial 5L 5R quadrate 1L cleithrum Flatfish 3 first vertebra (5.0, 4.7mm, 1 no measure) 75 other vertebra (1 burnt) 1 os anale Garfish 1 vertebra Spurdog 1 vertebra Eelpout 2 vertebra Eel 6 vertebra (4 burnt) Weever 1 first vertebra 2 other vertebra Bull-rout 1 first vertebra 7 other vertebra Unidentified 7 vertebra 125E 117N Layer 8 96g otolith 312L 373R 106 fragments 126E 116N Layer 7b/c Trench 11 05July2004 22 pieces charcoal (<1g), 3g bone fragments, 5g vertebra Cod family 2 first vertebra 1 second vertebra 2 third vertebra 32 other vertebra Flatfish 1 first vertebra 29 other vertebra Gurnard 1 vertebra Garfish 2 vertebra Spurdog 3 vertebra Unidentified 3 vertebra 126E 116N Layer 7c Trench 11 08July2004 TB Flatfish 1 os anale
126E 116N Layer 8 Trench 11 13July2004 TLS 6 fragments burnt hazelnut shell, 16 bone fragments (3g) Cod family 7 parasphenoid 1L premaxillary 1L angular 1L maxillary 1L supracleithrum 126E 117N Layer 7b/c Trench 11 05July2004 TB Flatfish 1L hyomandibular Unidentified 1 vertebra 126E 117N Layer 7b/c Trench 11 05July2004 TB 3 bone fragments 126E 117N Layer 7b/c Trench 11 06July2004 TB 27 pieces charcoal (mostly hazelnut shell) Weights: 5g bone and charcoal, 3g vertebra and non-vertebra Cod family 16 other vertebra 1L posttemporal Flatfish 1 first vertebra 17 other vertebra Spurdog 1 dorsal spine Gurnard 1 vertebra Garfish 5 vertebra 126E 117N Layer 7b/c Trench 11 06July2004 TB 10 fragments burnt hazelnut shell, many fragments bone Flatfish 1R cleithrum 126E 117N Layer 7c Trench 11 06July2004 TB 1 bone fragment Cod family 1 parasphenoid 126E 117N Layer 7c Trench 11 06July2004 TB Weights: 56g bone fragments, 44g charcoal, sand and shell, 8g non-vertebra, 54g cod, 30g flatfish, 13g other vertebra, 5g no ID Cod family 7 basioccipital 18 first vertebra 26 second vertebra 32 third vertebra 755 other vertebra 1R otolith (in with non-vertebra) 5L 1R premaxillary (1 fragment) 2L 3R supracleithrum 1L 1R posttemporal 1 pharyngobranchial 1R palatine 1R ceratohyal 2 epibranchial 1 branchiostegal ray 6L 3R quadrate 6L angular 1L 3R maxillary 1L vomer 1R dentary 1 parasphenoid 3L 1R hyomandibular 1L epihyal Flatfish 7 basioccipital 5 first vertebra (5.0, 7.2, 4.5, 5.1mm, 1 no measure) 548 other vertebra (1 calcined) 1 investing bone 1L palatine 1L quadrate 1 vomer 1 os anale 1L posttemporal
Eel 16 vertebra Herring 5 vertebra Garfish 2 first vertebra 42 other vertebra 7 dentary fragments Spurdog 66 vertebra 4 dorsal spines Mackerel 19 vertebra Trout/salmon 1 vertebra Weever 1 first vertebra 10 other vertebra Bull-rout 1 basioccipital 2 first vertebra 23 other vertebra Whitefish 1 vertebra Gurnard 5 vertebra Unidentified 64 vertebra 126E 117N Layer 7c Trench 11 12July2004 TB Weights: 10g bone fragments, shell and charcoal, 7g vertebra and non-vertebra Cod family 1 first vertebra 1 second vertebra 1 third vertebra 50 other vertebra 2L otolith Flatfish 1 first vertebra 16 other vertebra 1R pterotic (flounder) Eel 1 vertebra Gurnard 1 vertebra Spurdog 1 vertebra Garfish 1 vertebra 4 dentary fragments Bull-rout 2 vertebra Unidentified 1 vertebra 126E 117N Layer 8 Trench 11 12July2004 TB 9 pieces charcoal (1 hazelnut), 5 bone fragments Cod family 2 vertebra 1L otolith 126E 117N Layer 8 36g otolith 108L 131R 12 fragments 126E 117N Layer 8 Trench 11 12July2004 TB Weights: 30g bone fragments, 20g charcoal, shell and stone, 2g non-vertebra, 37g cod, 4g flatfish, 1g other vertebra, 1g no ID Cod family 5 basioccipital 21 first vertebra 36 second vertebra
39 third vertebra 254 other vertebra 3R dentary 1R supracleithrum 1L 3R premaxillary 1 branchiostegal ray 1L palatine 1R posttemporal 2L 2R maxillary 5 parasphenoid 1R 1 whole vomer 2L 1R angular Flatfish 4 first vertebra (5.6, 6.3, 5.4mm, 1 no measure) 76 other vertebra 1 os anale 1L quadrate Bull-rout 6 vertebra Mackerel 10 vertebra Garfish 2 vertebra Spurdog 3 vertebra Unidentified 17 vertebra 126E 117N Layer 8 Trench 11 13July2004 TB 4 bone fragments Cod family 1R premaxillary 1R dentary 1 parasphenoid 127E 116N Layer 7a Trench 11 0July2004 TLS Weights: 1g bone fragments, 3g vertebra and non-vertebra Cod family 1 first vertebra 1 second vertebra 2 third vertebra 16 other vertebra Garfish 1 dentary fragment 127E 116N Layer 8 Trench 11 27July2004 KCR (ca. 12 liters) Weights: 9g bone fragments, shell and sand, 11g vertebra, 2g otolith Cod family 5 first vertebra 4 second vertebra 3 third vertebra 70 other vertebra 2L 7R otolith Flatfish 23 vertebra Mackerel 1 vertebra Garfish 1 first vertebra Unidentified 2 vertebra 127E 117N Layer 7a Trench 11 01July2004 TLS Cod family 1 third vertebra 5 other vertebra Unidentified 1 vertebra fragment 127E 117N Layer 7c Trench 11 12July2004 TLS 2g bone fragments Flatfish 1L maxillary (turbot) 1L premaxillary (turbot) 1investing bone (turbot) Unidentified
1 head bone (turbot?) 127E 117N Layer 8 Trench 11 12July2004 TLS 1 fragment burnt hazelnut shell, 1 bone fragment Cod family 2 vertebra 1 parasphenoid 127E 117N Layer 8 Trench 11 12July2004 TLS 3 pieces charcoal (2 hazelnut shell), 13 bone fragments Cod family 2 first vertebra 1 other vertebra 3 parasphenoid 1R premaxillary 1L dentary Dragsholm Geologic Screen Samples Fish Notes
1mm Samples The non-vertebra elements were not systematically analyzed, only some were noted. All the Chenopodium seeds appeared to be charred. Many of the dermal denticles appeared burned or calcined. 122E 116N Layer 7B Trench 11 27July2004 KCR 1mm 11 dermal denticles flounder, several Chenopodium seeds, 3 vertebra cod family (1 calcined), 1 first vertebra eel, 3 other vertebra eel, 1 vertebra eelpout, 2 vertebra no ID (too dirty, eroded), 2 vertebra no ID 122E 116N Layer 7C Trench 11 27July2004 KCR 1mm Many Chenopodium seeds, a few other possible seeds, a few snails, 1R otolith cod family, 2 dermal denticles flounder, 2 teeth spurdog, 1 first vertebra herring, 2 other vertebra herring, 2 first vertebra eel, 2 other vertebra eel, 1 vertebra eelpout, 2 vertebra cod family, 1 vertebra no ID (eroded), 3 vertebra no ID (very small), 1 vertebra no ID 123E 116N Layer 7B Black Sand Trench 11 07July2004 BO 1mm A few Chenopodium seeds, a few other possible seeds, bits of charcoal and bone fragments 67 dermal denticles flounder, 1 basioccipital eel, 7 other vertebra eel, 1 vertebra Gasterosteus, 4 vertebra cod family, 10 vertebra no ID (too dirty, eroded), 2 vertebra no ID 2 dermal denticles, 5 teeth spurdog, 1 basioccipital cod family, 2 other vertebra cod family, 2 vertebra eel, 3 vertebra no ID (eroded) 124E 116N Layer 7B Black Spots Trench 11 05July2004 LRA 1mm Only a few Chenopdium seeds, several other charred seeds, 32 dermal denticles, 5 teeth spurdog, 1L premaxillary torsk, 1 urohyal eel, 9 vertebra eel (2 burned, 2 calcined), 1 first vertebra cod family, 10 other vertebra cod family, 2 vertebra herring, 3 vertebra eelpout, 2 vertebra Gobius, 14 vertebra no ID (too dirty, eroded), 14 vertebra no ID (1 calcined) Several Chenopodium seeds, several other possible seeds, 43 dermal denticles (2 calcined), 8 teeth spurdog, 1 vertebra Sygnathidae, 7 vertebra eelpout, 16 vertebra cod family, 4 vertebra herring (1 calcined), 1 first vertebra eel, 11 other vertebra eel (2 burnt), 1 vertebra flatfish, 2 vertebra Gobius, 6 vertebra no ID (eroded), 12 vertebra no ID (2 calcined) 125E 116N Layer 7B Trench 11 06July2004 KCR 1mm Several Chenopodium seeds, a few other possible seeds, 2 dermal denticles flounder, 1 Gasterosteus dorsal spine, 1 vertebra eelpout, 2 vertebra no ID (eroded) 127E 116N Layer 7A Bottom Trench 11 27July2004 KCR 1mm Several Chenopodium seeds, a couple of other seeds, 1 Gasterosteus dorsal spine 127E 116N Layer 7B Trench 11 27July2004 KCR 1mm Several Chenopodium seeds, 1 vertebra herring, 1 vertebra cf. Gobius (dirty)
127E 116N Layer 7C Trench 11 27July2004 KCR 1mm Several Chenopodium seeds, several small snails, 1 dermal denticle flounder, 1 basioccipital eel, 3 vertebra flatfish, 4 vertebra no ID (too dirty, eroded), 1 vertebra no ID 127E 116N Layer 8 Trench 11 27July2004 KCR 1mm Many Chenopodium seeds, 2 other possible seeds, 1R otolith (cf cod family?), 1 vertebra eel (burnt) 121E 117N Layer 7A Trench 11 15July2004 CF 1mm 3 dermal denticles flounder 123E 117N Layer 7B Black Sand Trench 11 06July2004 BO 1mm A few possible burnt seeds, 81 dermal denticles flounder (3 calcined), 1 ceratohyal eel, 1R premaxillary cod family, 9 teeth spurdog, 2 vertebra Sygnathidae, 1 fragment (<½) vertebra spurdog, 1 basioccipital eel, 5 first vertebra eel (2 calcined), 18 other vertebra eel (1 calcined), 1 vertebra garfish, 1 vertebra Gasterosteus, 16 vertebra cod family, 3 vertebra herring, 3 vertebra eelpout, 13 vertebra no ID (too dirty, eroded), 10 vertebra no ID (1 burnt, bagged separately) 124E 117N Layer 7B Trench 11 02July2004 LRA 1mm 1 dermal denticle flounder, 2 Gasterosteus dorsal spines, 1 vertebra cod family, 2 vertebra herring, 3 vertebra no ID (too dirty, eroded), 1 vertebra no ID (ultimate?) Several Chenopodium seeds, a few other possible seeds, 37 dermal denticles flounder, 2 Gasterosteus dorsal spines, 3 teeth spurdog, 2 first vertebra eel, 11 other vertebra eel (1 calcined, 1 burnt), 4 vertebra cod family, 1 vertebra Gobius, 2 vertebra eelpout, 1 vertebra Sygnathidae, 12 vertebra no ID (too dirty, eroded), 11 vertebra no ID 125E 117N Layer 7B Trench 11 05July2004 KCR 1mm Many Chenopodium seeds, some other possible seeds, 9 dermal denticles flounder, 2 first vertebra eel (1 calcined), 2 other vertebra eel, 1 (<½) vertebra pighaj, 1 vertebra Gasterosteus, 1 vertebra Gobius, 11 vertebra cod family (including 1 basioccipital, 1 burnt), 2 vertebra eelpout, 8 vertebra no ID (too dirty, eroded), 3 vertebra no ID 2mm Samples 122E 116N Layer 7B Trench 11 27July2004 KCR 2mm Cod family 1 first vertebra 8 other vertebra 1L 2R dentary 1L vomer 1L premaxillary 1R interopercle 2 parasphenoid 1L 1R posttemporal 1 epibranchial Flatfish 1 vertebra 1 ectopterygoid 1L quadrate Eel 5 vertebra 2R anguloarticular Herring 3 vertebra Spurdog 1 fragment (<½) vertebra Eelpout 1 vertebra Weever 1 vertebra Unidentified 5 vertebra too dirty, eroded 4 vertebra 122E 116N Layer 7C Trench 11 27July2004 KCR 2mm Cod family
2L otolith (10.5/4.3, 10.7/4.4mm) 2 second vertebra 1 third vertebra 2 other vertebra 1 branchiostegal ray 1L 1R posttemporal 1L palatine 1R dentary 1R maxillary Flatfish 1 vertebra (ultimate) Eel 1 basioccipital 6 vertebra (1 burnt) Herring 1 prooticum Mackerel 1 vertebra Unidentified 4 vertebra 123E 116N Layer 7B Black Sand Trench 11 07July2004 BO 2mm Cod family 1 first vertebra 2 second vertebra 19 other vertebra 1 mesethmoid 1L 3R dentary 1L 1R vomer 2L posttemporal 1R angular 1R opercle 2R quadrate 2L 2R maxillary 1L 1R supracleithrum 2L premaxillary Flatfish 6 vertebra 1 urohyal 2 ectopterygoid 1 os anale Eel 13 vertebra (3 burnt) 1 vomer Herring 2 first vertebra 3 other vertebra Eelpout 4 vertebra Bull-rout 2 vertebra Gurnard 1 vertebra Shad 1 vertebra Unidentified 22 vertebra 124E 116N Layer 7B Black Spots Trench 11 05July2004 LRA 2mm Cod family 1 basioccipital 1 first vertebra 8 second vertebra 2 third vertebra 92 other vertebra (3 burnt) 5R dentary 2L 2R vomer 2R epihyal 1L 1R palatine 1L hyomandibular 1R supracleithrum 1 pharyngeal plate 3 mesethmoid 1L symplectic 2 epibranchial 4L 5R premaxillary 1L 1R angular 2L 3R posttemporal 2L 1R maxillary (1 burnt) 3L 1R quadrate Flatfish 2 first vertebra 22 other vertebra (1 burnt) 1R supracleithrum 1 vomer 1R maxillary 1 ectopterygoid 1R angular Eel 4 first vertebra (1 burnt) 68 vertebra (7 burnt, 2 calcined)1L ceratohyal (1.8mm) 1R epihyal Herring
4 first vertebra 24 other vertebra Spurdog 1 vertebra (and two fragments <½) 1 dorsal spine Stickleback 1 dorsal spine Garfish 1 dentary fragment Mackerel 2 vertebra Bull-rout 9 vertebra Eelpout 3 vertebra Shad 3 vertebra Weever 1 first vertebra 1 other vertebra Goby 2 vertebra Unidentified 17 vertebra too dirty, eroded 45 vertebra 125E 116N Layer 7B Trench 11 06July2004 KCR 2mm Cod family 6 vertebra 1L 1R posttemporal 1R hypohyal Flatfish 1 basioccipital 1 other vertebra Eel 2 vertebra Herring 1 vertebra Spurdog 1 vertebra Unidentified 4 vertebra 127E 116N Layer 7A Bottom Trench 11 27July2004 KCR 2mm Cod family 1 vertebra Unidentified 1 vertebra 127E 116N Layer 7B Trench 11 27July2004 KCR 2mm Cod family 1 vertebra Eel 1 vertebra Spurdog 2 fragments (<½) vertebra 127E 116N Layer 7C Trench 11 27July2004 KCR 2mm Cod family 3 vertebra 1R posttemporal 1L opisthotic 1R quadrate Eel 1 vertebra
Herring 1 vertebra Unidentified 1 vertebra 127E 116N Layer 8 Trench 11 27July2004 KCR 2mm Cod family 2 vertebra Unidentified 1 vertebra too dirty 1 vertebra no ID 121E 117N Layer 7A Trench 11 15July2004 CF 2mm Cod family 2 vertebra (1 very small second) Flatfish 1 vertebra Eel 1 vertebra Bull-rout 1 vertebra Unidentified 2 vertebra 123E 117N Layer 7B Black Sand Trench 11 06July2004 BO 2mm Cod family 1 first vertebra (burnt) 4 second vertebra 2 third vertebra 47 other vertebra 2L 1R dentary 2L 1R posttemporal 4L 1R premaxillary 2L 2R quadrate (1 fragment) 3L supracleithrum 1 parasphenoid 1R opercle 1L interhyal 1L sphenotic 1L epihyal 1 pharyngeal plate Flatfish 12 vertebra 1R quadrate 1 vomer Eel 32 vertebra (1 burnt, 1 calcined) 1 urohyal 1L anguloarticular Herring 1 first vertebra 22 other vertebra Bull-rout 1 vertebra 1 parasphenoid Weever 1 vertebra Eelpout 2 vertebra Unidentified 9 vertebra too dirty, eroded 13 vertebra 124E 117N Layer 7B Trench 11 02July2004 LRA 2mm Cod family 1 first vertebra 4 second vertebra 2 third vertebra 41 other vertebra (1 burnt) 1L 1R palatine 1R posttemporal 1R symplectic 1L dentary 1L retroarticular 2R vomer 1R premaxillary Flatfish 11 vertebra 1L posttemporal Eel 1 basioccipital 13 other vertebra
Herring 1 first vertebra 4 other vertebra Stickleback 1 dorsal spine Bull-rout 6 vertebra Eelpout 4 vertebra Unidentified 17 vertebra too dirty, eroded 11 vertebra 125E 117N Layer 7B Trench 11 05July2004 KCR 2mm Cod family 1 basioccipital 2 first vertebra (4.1mm and no measure) 1 third vertebra 27 other vertebra 1 branchiostegal ray 1 mesethmoid 2L 1R dentary 3L supracleithrum 1R quadrate 1R symplectic 1L opercle 2L 3R posttemporal 1R vomer 2R maxillary (1 fragment) 1R sphenotic Flatfish 13 vertebra (1 burnt) 1L 1R posttemporal 1L supracleithrum Eel 10 vertebra (1 burnt) Herring 9 vertebra (1 burnt) 1 prooticum Spurdog 1 fragment (<½) vertebra Bull-rout 4 vertebra (1 burnt) Gurnard 1 vertebra Unidentified 16 vertebra 4mm Samples 122E 116N Layer 7B Trench 11 27July2004 KCR 4mm Cod family 2 first vertebra (5.0mm, no measure) 2 second vertebra 1 other vertebra 1R premaxillary Flatfish 1 basioccipital 3 other vertebra Unidentified 18 fragments 122E 116N Layer 7C Trench 11 27July2004 KCR 4mm Cod family 1 basioccipital 2 second vertebra 2 third vertebra 6 other vertebra Flatfish 2 vertebra Unidentified 1 vertebra 23 fragments 123E 116N Layer 7B Black Sand Trench 11 07July2004 BO 4mm Cod family
1 first vertebra 1 third vertebra 6 other vertebra 1 epibranchial Flatfish 6 vertebra 1L angular Spurdog 1 vertebra Bull-rout 1 vertebra Garfish 1 dentary fragment Gurnard 1 vertebra Unidentified 3 vertebra 39 fragments 124E 116N Layer 7B Black Spots Trench 11 05July2004 LRA 4mm Cod family 1 basioccipital 1 first vertebra 4 second vertebra 6 third vertebra 70 other vertebra 1L symplectic 1 branchiostegal ray 1 mesethmoid 2L dentary 5L 3R premaxillary 1R supracleithrum 1L posttemporal 1 epibranchial 1L vomer 1L quadrate 1R opisthotic Flatfish 8 first vertebra (4.9, 4.0, 4.1, 3.8, 4 no measure) 52 other vertebra (1 burnt) 1 urohyal Eel 2 vertebra 1L ceratohyal (1.9mm) Spurdog 2 fragments (<½) vertebra Garfish 2 vertebra 2 dentary fragments Mackerel 2 vertebra Weever 1 vertebra (burnt) Gurnard 1 vertebra Bull-rout 2 vertebra Unidentified 26 vertebra 229 fragments 125E 116N Layer 7B Trench 11 06July2004 KCR 4mm Cod family 8 vertebra Flatfish 1 first vertebra 2 other vertebra Garfish 2 vertebra Mackerel 1 vertebra Unidentified 4 vertebra 15 fragments 127E 116N Layer 7A Bottom Trench 11 27July2004 KCR 4mm
Flatfish 1 vertebra Unidentified 6 fragments (plus 1 stone and 1 charcoal) 127E 116N Layer 7B Trench 11 27July2004 KCR 4mm Unidentified 4 fragments 127E 116N Layer 7C Trench 11 27July2004 KCR 4mm Cod family 2 basioccipital 11 other vertebra 1 parasphenoid 1L sphenotic Flatfish 5 vertebra 1 os anale Garfish 1 vertebra Unidentified 3 vertebra 26 fragments 127E 116N Layer 8 Trench 11 27July2004 KCR 4mm Cod family 10 vertebra Flatfish 3 vertebra Unidentified 3 vertebra 18 fragments (mostly/all vertebra, fairly eroded and broken) 121E 117N Layer 7A Trench 11 15July2004 CF 4mm Cod family 1 vertebra 1R posttemporal Flatfish 1 vertebra Unidentified 8 fragments 123E 117N Layer 7B Black Sand Trench 11 06July2004 BO 4mm Cod family 1 basioccipital 1 first vertebra 1 second vertebra 2 third vertebra 10 other vertebra 1 branchiostegal ray 1L 3R vomer 1L premaxillary Flatfish 1 basioccipital 1 first vertebra 15 other vertebra (1 burnt) Mackerel 1 vertebra Garfish 1 vertebra Gurnard 3 vertebra (including 1 ultimate) Unidentified 4 vertebra 56 fragments 124E 117N Layer 7B Trench 11 02July2004 LRA 4mm Cod family 1 second vertebra 1 third vertebra 15 other vertebra (2 burnt) 1L supracleithrum 1R quadrate 1R premaxillary (burnt)
Flatfish 2 vertebra Bull-rout 1 first vertebra Garfish 2 dentary fragments Gurnard 1 dorsal spine Spurdog 1 fragment (<½) vertebra Unidentified 5 vertebra 34 fragments 125E 117N Layer 7B Trench 11 05July2004 KCR 4mm Cod family 1 basioccipital 2 first vertebra (4.1mm, no measure) 2 second vertebra 1 third vertebra 17 other vertebra 2R vomer 2L premaxillary 1R maxillary 1L quadrate 2R angular 1L sphenotic Flatfish 1 first vertebra 30 other vertebra Eel 1 basioccipital Spurdog 1 vertebra 2 fragments (<½) vertebra Mackerel 1 vertebra (1 fragment) Bull-rout 3 vertebra (1 burnt) Garfish 4 dentary fragments Unidentified 8 vertebra 80 fragments
Fårevejle Fish Notes Final
140E 107N Layer 3 Trench 1 27July2004 TB 2 non-vertebra fragments, probably not fish bone 141E 107N Layer 4 Trench 1 12August2004 TB Cod family 1 vertebra 141E 107N Layer 5 Trench 1 12August2004 TB Cod family 1 vertebra Flatfish 2 vertebra Unidentified 1 vertebra fragment 141E 107N Layer 5 Trench 1 13August2004 TB Cod family 2 vertebra Flatfish 2 vertebra Unidentified 1 vertebra 3 vertebra fragments 8 non-vertebra fragments 141E 107N Layer 6 Trench 1 17August2004 TB Cod family 1 second vertebra 140E 108N Layer 5 Trench 1 14July2005 CF Cod family 1 third vertebra 11 vertebra 1R dentary 1L quadrate Flatfish 1 first vertebra (5.9mm) 9 other vertebra 1R posttemporal 1 os anale Eel 2 vertebra (?) 1L cleithrum (2.5mm) 140E 108N Layer 5-6B Trench 1 15July2005 CF Cod family 1 first vertebra (5.7mm) 1 other vertebra 1 parasphenoid 1 vomer Flatfish 2 vertebra Garfish 1 vertebra 140E 108N Layer 6B Trench 1 15July2005 CF Cod family 2 third vertebra 5 other vertebra 1R premaxillary Flatfish 3 vertebra
Unidentified 1 vertebra 140E 108N Layer 6C Trench 1 15July2005 TLS Cod family 2 vertebra 1L retroarticular 1R maxillary 2L 1R premaxillary Flatfish 1 vertebra Trout/salmon 1 vertebra 140E 108N Layer 6A1 Trench 1 18July2005 CF Cod family 3 vertebra Flatfish 1 vertebra 140E 108N Layer 6A2 Trench 1 18July2005 CF Cod family 3 vertebra Flatfish 3 vertebra 140E 108N Layer 6C2 Trench 1 19July2005 CF Unidentified Several fragments 140E 108N Layer 7 Oyster Trench 1 20July2005 CF Cod family 1 basioccipital 1 third vertebra 1 other vertebra Flatfish 1 vertebra 140E 108N Layer 7 Trench 1 21July2005 CF Cod family 1 vertebra 1 parasphenoid Unidentified 1 vertebra 140E 108N Layer 7(B?) Trench 1 22July2005 CF Cod family 1L otolith Flatfish 1 vertebra Eel 1 vertebra 140E 108N Layer 8 Trench 1 22July2005 CF Flatfish 1 vertebra 141E 108N Layer 5 Trench 1 14July2005 TLS Cod family 2 vertebra 1R maxillary Flatfish 6 vertebra
Garfish 1 vertebra Unidentified 1 vertebra 141E 108N Layer 6D Trench 1 15July2005 TLS Cod family 3 vertebra Flatfish 1 vertebra 141E 108N Layer 7 Trench 1 20July2005 TLS Cod family 13 vertebra 1R dentary 2R angular Flatfish 6 vertebra 141E 108N Layer 7B Trench 1 21July2005 TLS Cod family 1 third vertebra 3 other vertebra Below Midden Trench 1 01August2005 CF Cod family 1 vertebra 140E 109N Layer 4 Trench 1 13July2005 KCR Cod family 1 second vertebra 4 other vertebra Flatfish 3 vertebra 140E 109N Layer 5B Trench 1 18July2005 KCR Cod family 1 second vertebra 23 other vertebra 1R posttemporal 2L angular 1L 1R quadrate 1 symplectic 1R ectopterygoid Flatfish 1 basioccipital 1 first vertebra (5.2mm) 47 other vertebra 1L hyomandibular 2L 1R quadrate 1 vomer (turbot/brill) 1L hypohyal Eel 2 vertebra 1L quadrate 1R ceratohyal (4.6mm) Cyprinid 1 first (?) vertebra 1 other vertebra Unidentified 2 vertebra (eroded) 140E 109N Layer 6 arbitrary Trench 1 15July2005 KCR Cod family 1 first vertebra (no measure) 2 second vertebra 2 third vertebra 11 other vertebra 1L 1R dentary 1L vomer 1R otolith 1L 2R angular 1R supracleithrum Flatfish 2 first vertebra (4.2mm, 1 no measure) 27 other vertebra (1 turbot) 1R hyomandibular 1 vomer Eel
1 basioccipital 1 other vertebra 1R cleithrum (2.0mm) Herring 1 vertebra 140E 109N Layer 6F Trench 1 20July2005 KCR Cod family 1 vertebra 1 parasphenoid 140E 109N Layer 6F Trench 1 20July2005 KCR Weights: 7g fragments, 9g identified Cod family 1 basioccipital (>3kg fish) 1 first vertebra (7.4mm) 1 second vertebra 3 third vertebra 34 other vertebra 1R angular 1L 1R dentary 1R quadrate 1L 2R premaxillary 5 parasphenoid 2R vomer 1R cleithrum 1R ceratohyal 1 symplectic Flatfish 1 first vertebra (4.9mm) 45 other vertebra 4 os anale 1 urohyal Eel 1 vertebra 1 vomer Garfish 2 vertebra 140E 109N Layer 7 Trench 1 20July2005 KCR Cod family 1L otolith (broken, >½) 140E 109N Layer 8 Trench 1 22July2005 KCR Cod family 1 second vertebra 2 third vertebra 7 other vertebra 3L 2R otolith Flatfish 6 vertebra Unidentified 1 vertebra 141E 109N Layer 4 Trench 1 12July2005 LRA Flatfish 2 vertebra 141E 109N Layer 5 Trench 1 15July2005 LRA Cod family 1 first vertebra (in 2 pieces) 1 second vertebra 1 third vertebra 44 other vertebra 4L 4R otoliths 1L 1R maxillary 4L 2R premaxillary 1L dentary 2R quadrate 2 symplectic 2R vomer 1R cleithrum 1 epibranchial Flatfish 3 first vertebra (4.9, 4.7, 3.9mm) 84 other vertebra 1L maxillary 2 vomer 2 urohyal 1 parasphenoid 1L posttemporal 1R epihyal 1 ectopterygoid 1 os anale 1R supracleithrum 1L 1R hyomandibular 2L quadrate Eel 6 vertebra
Garfish 2 vertebra Pike 1 vertebra Unidentified 1 vertebra (eroded) 2 non-vertebra 141E 109N Layer 6E Trench 1 18July2005 LRA Cod family 3 basioccipital 4 first vertebra (9.2, 9.6, 6.9, 5.3mm) 106 other vertebra 2L dentary 2 parasphenoid 3L 4R premaxillary 4L 2R maxillary 1L 1R supracleithrum 2L vomer 2L 1R posttemporal 1L ceratohyal 1R hyomandibular 4L 1R angular 1L 1R quadrate 2L 1R cleithrum 1R hypohyal 1L palatine Flatfish 95 vertebra (1 turbot) 3 urohyal 3L 1R supracleithrum 1 vomer 1R angular 3L pterotic (flounder) 1R epihyal Eel 9 vertebra 1L quadrate 1L 1R hyomandibular Herring 2 vertebra Garfish 2 vertebra Bull-rout 1 vertebra Mackerel/Horse mackerel(?) 2 vertebra Pike 1 tooth Cyprinid 2 vertebra Unidentified 3 vertebra 141E 109N Layer 6F Trench 1 20July2005 LRA Cod family 2 basioccipital 2 first vertebra (7.0, 6.1mm) 1 second vertebra 3 third vertebra 103 other vertebra (2 fused) 5L 4R premaxillary 1L dentary 3L 3R maxillary (2 fragments) 1L supracleithrum 3L angular 1R posttemporal 1L 1R quadrate 1R palatine 1 symplectic 2 postcleithrum 1R cleithrum 1L ceratohyal Flatfish 50 vertebra (1 turbot) 1L premaxillary (flounder?) 2 os anale 1L hyomandibular 1L posttemporal Eel 4 vertebra Herring 3 vertebra Garfish 1 vertebra 141E 109N Layer 6F Trench 1 20July2005 LRA Cod family
1R maxillary Flatfish 1 vertebra 141E 109N Layer 7 Trench 1 21July2005 LRA Cod family 12 vertebra 1R maxillary 1 parasphenoid Flatfish 7 vertebra Eel 1 vertebra 1 vomer (very large) 141E 109N Layer 7 Trench 1 21July2005 LRA (2
nd bag)
Cod family 1 vertebra 141E 109N Layer 7 Trench 1 22July2005 LRA Bag #2 Cod family 4 vertebra 1 parasphenoid 1R premaxillary 1L quadrate 140E 110N Layer 6 Trench 1 09August2004 TLS Cod family 1 second vertebra 5 other vertebra Unidentified 1 vertebra fragment 140E 110N Layer 7 Trench 1 10August2004 TLS Cod family 3 second vertebra 1 other vertebra Flatfish 1 vertebra (turbot) 141E 110N Layer 4 Trench 1 23July2004 TLS Weights: 1g fragments, <1g no ID, 7g cod family, 1g flatfish, 1g non-vertebra Cod family 2 first vertebra (7.1, 5.6mm) 2 second vertebra 3 third vertebra 61 other vertebra 1R otolith 1R maxillary 1R angular 1L ectopterygoid Flatfish 22 vertebra 1L dentary Eel 1L 1R cleithrum 1R epihyal Unidentified 1 vertebra (eroded) 141E 110N Layer 5 Trench 1 26July2004 TLS Cod family 2 first vertebra (5.8, 5.2mm) 2 second vertebra 3 third vertebra 99 other vertebra 3R premaxillary 2R quadrate 1L cleithrum 1L angular 3L 1R maxillary Flatfish 1 first vertebra (3.4mm) 54 other vertebra Eel 1 vertebra Garfish
3 vertebra Cyprinid 1 vertebra (Rutilus?) Unidentified 2 vertebra (eroded) 18 vertebra fragments 140E 111N Layer 6 Trench 1 09August2004 CF Weights: 2g fragments, 6g cod family, 2g flatfish, <1g other, 1g non-vertebra Cod family 6 second vertebra 1 third vertebra 71 other vertebra 1L quadrate 2R premaxillary 1R posttemporal 1R dentary 1 epibranchial 1L pharyngeal plate Flatfish 26 vertebra 1 os anale Eel 3 vertebra 1L cleithrum (2.0mm) Garfish 1 vertebra 140E 111N Layer 8 Trench 1 10August2004 CF Cod family 1 third vertebra 2 other vertebra Unidentified 2 non-vertebra fragments 141E 111N Layer 2 Trench 1 20July2004 CF Cod family 3 vertebra 1R premaxillary Unidentified 7 vertebra fragments 1 non-vertebra fragment 141E 111N Layer 3 Trench 1 29July2004 CF Cod family 1R premaxillary 141E 111N Layer 4 Trench 1 26July2004 CF Flatfish 3 vertebra 1 os anale Unidentified 1 vertebra fragment 5 non-vertebra fragments 141E 111N Layer 4 Trench 1 28July2004 CF Cod family 1 third vertebra 3 other vertebra Flatfish 12 vertebra Unidentified 1 vertebra 3 vertebra fragments 141E 111N Layer 5 Trench 1 28July2004 CF Cod family 1 first vertebra (no measure) 2 second vertebra 1 third vertebra 63 other vertebra 1L 1R supracleithrum 2L 3R premaxillary (1 fragment) 1L 1R posttemporal 1L 1R cleithrum 1R otolith Flatfish 2 first vertebra (5.0, 4.6mm) 129 other vertebra (1 turbot) 4 os anale (2 fragments)
1R maxillary (turbot) 1 ectopterygoid 1L 1R supracleithrum 2 parasphenoid Eel 4 vertebra 1R dentary Garfish 1 vertebra 2 dentary fragments Cyprinid 1 vertebra Unidentified 6 vertebra (eroded) 141E 111N Layer 5 Trench 1 28July2004 CF Cod family 2 vertebra 1R premaxillary Flatfish 1 first vertebra (5.6mm) 37 other vertebra 1 os anale 2R hyomandibular Unidentified 1 vertebra (eroded) 141E 111N Layer 6 Trench 1 29July2004 CF Weights: 1g fragments, <1g no ID, 1g cod family, 1g flatfish, <1g non-vertebra Cod family 1 third vertebra 5 other vertebra Flatfish 1 first vertebra (5.2mm) 17 other vertebra 1 opercle 1 os anale (1 fragment) Unidentified 1 vertebra (eroded) 7 vertebra fragments 141E 111N Layer 7 Trench 1 29July2004 CF Cod family 1 first vertebra (no measure) 1 other vertebra Flatfish 2 vertebra Eel 1R ceratohyal (2.3mm) Unidentified 1 vertebra 2 vertebra fragments 3 non-vertebra fragments 141E 111N Layer 8 Trench 1 30July2004 CF Cod family 2 vertebra Flatfish 1 vertebra Unidentified 1 vertebra fragment 1 non-vertebra fragment 132E 112N Layer 2 Trench 2 20July2005 PN Cod family 1L posttemporal Flatfish 1 vertebra 132E 112N Layer 2 Trench 2 21July2005 PN Cod family
1 first vertebra (5.8mm) 1 third vertebra 3 other vertebra 1R premaxillary Flatfish 2 vertebra Unidentified 1 vertebra (gurnard/weever?) 132E 112N Oyster Trench 2 03August2005 CF Unidentified 1 fragment vertebra (cf. cod family) 133E 112N Last Oysters to Floor Trench 2 04August2005 CF Cod family 1 vertebra 140E 112N Layer 3 Trench 1 11August2004 BO Cod family 2 vertebra Flatfish 1 basioccipital 3 other vertebra Unidentified 3 vertebra fragments 140E 112N Layer 4 Trench 1 11August2004 BO Cod family 14 vertebra 1L vomer 1 pharyngobranchial 1 interhyal 1L cleithrum 1L otolith Flatfish 2 vertebra 1R hyomandibular Eel 1 vertebra Cyprinid 1 first vertebra 140E 112N Layer 4 Trench 1 11August2004 BO Cod family 1 basioccipital 2 first vertebra (8.2, 8.6mm) 2 third vertebra 46 other vertebra 1 pharyngobranchial 1 postcleithrum 1R cleithrum 1L ceratohyal 2L premaxillary 2L 1R maxillary 1L 1R posttemporal 1R quadrate 1R supracleithrum 1 vomer 1R epihyal Flatfish 1 first vertebra (4.8mm) 29 other vertebra 1R angular 1 parasphenoid Eel 5 vertebra 1 parasphenoid 1L ceratohyal (2.0mm) 140E 112N Layer 6 Trench 1 12August2004 BO Cod family 7 vertebra 1 parasphenoid 1L premaxillary 1L vomer 1L angular 1R ceratohyal Flatfish 1 vertebra Eel 1 parasphenoid 1R ceratohyal (2.1mm) Unidentified
8 vertebra fragments 4 non-vertebra fragments 140E 112N Layer 7 Trench 1 13August2004 BO Weights: 6g fragments, <1g no ID, 7g cod family, 1g flatfish, <1g other vertebra, 3g non-vertebra Cod family 3 basioccipital 4 third vertebra 65 other vertebra 3L 1R otolith 4L 3R premaxillary 1L dentary 2 parasphenoid (1 fragment) 2L maxillary 1R quadrate 1L 1R supracleithrum Flatfish 3 first vertebra (4.5, 4.5mm, no measure) 14 other vertebra (1 turbot) 5 os anale (2 fragments) Eel 1 first vertebra 1 other vertebra 1R dentary 1L ceratohyal (3.1mm) Herring 2 vertebra Bull-rout 1 vertebra Unidentified 3 vertebra 140E 112N Layer 8 Trench 1 13August2004 BO Cod family 2 first vertebra (9.2, 8.2mm) 2 second vertebra 7 other vertebra 1R otolith Flatfish 1 vertebra 141E 112N Layer 3 Trench1 23July2004 BO Weights: 3g fragments, 5g cod family, Cod family 2 basioccipital 2 first vertebra (8.6mm, no measure) 2 second vertebra 1 third vertebra 46 other vertebra (2 fused) 3L 1R otolith 3L premaxillary (2 fragments) 1L 3R vomer 1L angular 3R quadrate 1L posttemporal 1L maxillary Flatfish 48 vertebra Eel 1L dentary Garfish 1 vertebra Unidentified 3 vertebra 52 vertebra fragments 141E 112N Layer 4 Trench 1 28July2004 BO Cod family 1 second vertebra 27 other vertebra 1R 1 whole vomer 2L 1R premaxillary 2 parasphenoid 1R posttemporal 1R cleithrum 1L hyomandibular Flatfish 3 first vertebra (5.2, 4.9, 4.2mm) 39 other vertebra 1L 1R cleithrum Eel 2 vertebra 1 parasphenoid Pike
1 vertebra Unidentified 2 vertebra (broken, worn) 141E 112N Layer 4 Trench 1 27July2004 BO Cod family 1 vertebra (small) 1 otolith fragment Flatfish 1 os anale 1 cleithrum Unidentified 5 non-vertebra fragments 141E 112N Layer 5 Trench 1 29July2004 BO Eel 1 parasphenoid Unidentified 2 non-vertebra fragments 141E 112N Layer 5 Trench 1 29July2005 BO Cod family 1 third vertebra 6 other vertebra 1R dentary Flatfish 1 first vertebra (no measure) 21 other vertebra (1 burnt) 1 cleithrum 2R posttemporal Eel 1 parasphenoid 1L cleithrum (1.3mm) 141E 112N Layer 6 Trench 1 30July2004 BO Cod family 2 vertebra Flatfish 2 vertebra 141E 112N Layer 7 Trench 1 30July2004 BO Cod family 1 vertebra 141E 112N Layer 8 Trench 1 30July2004 BO Unidentified 2 non-vertebra fragments 132E 113N 410/404 Trench 2 26July2005 PP(?) Flatfish 1 vertebra 133E 113N Crushed Shell Above Oysters Trench 2 05August2005 CF/TLS Cod family 1 vertebra 2 vertebra fragments 133E 113N Midden Bottom of Pit to N Trench 2 09August2005 KCR(?) Cod family 1 vertebra 140E 113N Layer 5 Trench 1 10August2004 KCR Cod family 3 first vertebra (9.4, 8.2, 6.7mm) 4 second vertebra 5 third vertebra
83 other vertebra 1L 3R premaxillary 1R dentary 1L 1R posttemporal 1R maxillary 2L angular 1R supracleithrum 2L otoliths Flatfish 30 vertebra (2 turbot) 1R quadrate Eel 1R quadrate Spurdog 1 dorsal spine Unidentified 2 vertebra (eroded) 140E 113N Layer 6 Trench 1 11August2004 KCR Cod family 2 first vertebra (6.7, 6.2mm) 1 second vertebra 72 other vertebra 2R otolith 2L 2R premaxillary 1 parasphenoid 1 vomer 1L 2R angular 1L 1R quadrate 1L 1R maxillary Flatfish 11 vertebra 1 urohyal Eel 1 vertebra 140E 113N Layer 6 Trench 1 11August2004 KCR Cod family 1 vertebra 1L quadrate 1R dentary 1R vomer Flatfish 1R quadrate (turbot) Unidentified 1 vertebra fragment 8 non-vertebra fragments 140E 113N Layer 7 Trench 1 12August2004 KCR Cod family 1 third vertebra 7 other vertebra 1R maxillary Flatfish 4 vertebra 141E 113N Layer 4 Trench 1 26July2004 KCR Weights: <1g fragments and no ID, 1g cod family, 1g flatfish Cod family 2 second vertebra 5 other vertebra 1R otolith Flatfish 11 other vertebra (1 turbot) Unidentified 3 vertebra 3 vertebra fragments 2 non-vertebra fragments 141E 113N Layer 5 Trench 1 29July2004 KCR Cod family 1 first vertebra (9.8mm) 2 other vertebra Flatfish 3 vertebra 141E 113N Layer 6 Trench 1 30July2004 KCR Cod family 2 vertebra
Flatfish 2 vertebra 1L cleithrum Unidentified 1 non-vertebra fragment 132E 114N Broken Crushed Shell Trench 2 04August2005 LRA Cod family 3 vertebra 1 parasphenoid (1 fragment) Flatfish 1 vertebra 132E 114N Sand Above Moraine Trench 2 05August2005 TLS Cod family 1 third vertebra Flatfish 1 vertebra 133E 114N Broken Shell Top Layer Trench 2 20July2005 MJ Cod family 1L otolith 133E 114N Broken Crushed Shell Trench 2 04August2005 LRA Cod family 1 second vertebra 1 other vertebra 133E 114N Dark Layer Below A36 Trench 2 04August2005 LRA Cod family 1 vertebra 141E 114N Layer 6 (A7) Trench 1 18August2004 KCR Cod family 1L otolith 132E 115N Top Broken Shell Layer Trench 2 20July2005 MJ Cod family 3R otoliths 132N 116E Top Shell Layer Trench 2 11July2005 MJ Cod family 1 third vertebra 132E 117N Top Shell Layer Trench 2 15July2005 MJ Cod family 2 vertebra 132E 117N Top Shell Layer Trench 2 15July2005 MJ Unidentified 2 vertebra fragments (<½) 132E 117N Oyster Shell Heap #2 Trench 2 25July2005 MJ Cod family 1 second vertebra 5 third vertebra 12 other vertebra 1R dentary 1L 1R vomer 2L quadrate Unidentified 3 vertebra 1 ceratohyal/epihyal
132E 118N Oyster Shell Heap #2 Trench 2 26July2005 MJ 2 bags Unidentifed 1 vertebra 132E 118N Oyster Shell Heap #2 Trench 2 26July2005 MJ Cod family 1 vertebra Feature A35 Trench 1 01August2005 Cod family 1L otolith 141E Under Midden Mottled Sand Trench 1 02August2005 CF Unidentified 1 vertebra
Havnø 4014 101/98 MHF Nothing identified 102/94 NE FOH 1 os anale flatfish 1 Left 1 Right cleithrum eel 11 vertebra eel 1 vertebra herring 89/100 SE 231- HWD Nothing identified 92/100 SE 210-217 HZS Nothing identified 89/100 NE 196-212 HRR Nothing identified 89/100 NW 194-210 HRQ 2 vertebra eel 1 vertebra flatfish 100/99 SE LDY Nothing identified 93/100 SE 208-213 HZW 1 vertebra salmon/trout 99/98 SW LTT 1 vertebra flatfish 98/102 SE 149-161 MOM 1 vertebra eel 1 R ceratohyal eel 92/100 NW 180-188 HNW 1 L epihyal eel 2 parasphenoid eel 1 frontal eel 2 L ceratohyal eel 1 L cleithrum eel 8 vertebra eel 98/102 SE 135-139 MEO Nothing identified 92/100 NE 173-180 HLV 5 vertebra eel 1 L opercle eel 92/100 SW 180-188 HNY 1 vertebra eel
89/100 SE 220- HTU Nothing identified 102/94 SW FOL 4 vertebra eel 1 first vertebra flatfish 1 vertebra no ID 1 R ceratohyal eel 1 L 1 R cleithrum eel 98/101 SE JRN Nothing identified 102/93 NE FOM 2 vertebra eel 1 vertebra herring 2 vertebra salmon/trout 2 vertebra no ID 1 L quadrate eel 100/98 SE MGQ Nothing identified 102/93 NE 219-232 MNJ 1 vertebra weever 100/98 NE MBR Nothing identified 93/100 NW 202-210 HZT Nothing identified 92/100 SW 175-180 HLW 1 first vertebra eel 2 vertebra eel 1 R angular eel 98/101 SE 136-138 MEF 1 vertebra no ID 93/100 SW 178-189 HOC 2 vertebra eel 1 L hyomandibular eel 93/100 SW 205-214 HZV 1 first vertebra eel 4 vertebra eel 1 vertebra herring 1 vertebra eelpout 5 vertebra no ID (too dirty) 1 L cleithrum eel 89/100 NE 224- HWB 2 vertebra eel
99/102 SE MOQ Nothing identified 93/100 NW 174-180 HLY 2 vertebra eel 100/98 MHK 1 vertebra eel 99/99 SW 146-154 LJF Nothing identified 92/100 NW 173-180 HLU 4 vertebra eel 102/91 NW JNY 1 L dentary eel 1 L ceratohyal eel 102/96 NW Nothing identified 88/100 SE 196-216 HNQ 1 parasphenoid eel 1 vertebra salmon/trout 4 vertebra flatfish 1 vertebra no ID 3 vertebra garfish 102/93 NW FON 2 vertebra eel 2 vertebra herring 89/100 SE 184-204 HNU 7 vertebra eel 1 vertebra gadid 1 vertebra weever 1 R hyomandibular eel 1 L post-temporal gadid 99/98 NW LFR 1 vertebra garfish 99/102 NE 142-150 JSB Nothing identified 88/100 NE 191-212 HNO 1 vertebra eel 1 vertebra herring 1 vertebra flatfish 1 os anale flatfish 100/101 NGE Nothing identified
100/99 LDJ 1 vertebra flatfish 102/92 SE JOC Nothing identified 88/100 SW 241- HVY Nothing identified 88/100 SW 196-216 HNP Nothing identified 100/99 LRT 1 vertebra flatfish 93/100 SW 188- HUS 2 vertebra eel 1 R ceratohyal eel 102/92 NE JBM Nothing identified 89/100 SE 204- HRT 2 vertebra eel 1 vertebra flatfish 1 vertebra no ID 1 R angular flatfish 102/94 SW MNY Nothing identified 98/102 NE 145-162 MOO 1 vertebra eel 89/100 SW 183-203 HNT 4 vertebra eel 1 vertebra gadid 92/100 NE 208-217 HZQ 8 vertebra eel 88/100 237- HVW Nothing identified 102/96 SW APX 2 vertebra eel 93/100 NE 155- HCB Nothing identified 90/100 NE 180-199 HAG 1 vertebra gadid 102/94 SE FOK 3 vertebra eel 2 vertebra herring
1 vertebra flatfish 89/100 NW 175-194 HNR 1 L dentary weever 1 first vertebra eel 21 vertebra eel 5 vertebra weever 89/100 NE 178-196 HNS 4 vertebra gadid 1 vertebra eel 1 vertebra no ID 92/100 NW 208-218 HZP 2 vertebra eel OAC 3 vertebra eel 1 R cleithrum eel 1 R ceratohyal eel 1 R quadrate eel 1 vertebra no ID 88/100 NW 191-211 HNN 2 vertebra eel 1 vertebra weever 102/94 SE 220-228 MLM Nothing identified 100/98 SW MGR Nothing identified 100/98 SE MGQ Nothing identified 89/100 NW 222- HWA Nothing identified 88/100 NW 211-225 HRM 3 vertebra eel 87/100 SE 261-269 HKJ 1 vertebra probably weever 100/102 SW JUD 2 snail shells 93/100 NW 180-189 HOA 1 vertebra eel 1 L ceratohyal eel 88/100 SW 230- HTP 1 vertebra eel
100/99 NE LPL 1 R maxillary flatfish 92/100 SE 179-188 HNZ 1 L dentary eel 1 L angular eel 1 R hyomandibular eel 89/100 SV 220- HTT 1 vertebra garfish 93/100 NE 188- HUR 1 vertebra eel 91/100 SE 173-199 HAD 3 vertebra eel 92/100 NE 154- HBX 3 vertebra + 2 fragments gadid 88/100 NE 226- HTO 1 R angular eel 102/93 SW MLO 1 vertebra flatfish 1 vertebra eel 1 basioccipital eel 90/100 NW 178-198 HAF 1 basioccipital eel 6 vertebra eel 1 vomer eel 1 L 1 R ceratohyal eel 1 R angular eel 1 vertebra eelpout 93/100 SE 181-189 HOD 1 vertebra eel 1 frontal eel 102/93 SE FOO 1 basioccipital weever 1 first vertebra eel 1 vertebra eel 1 vertebra herring 6 vertebra salmon/trout 1 vertebra flatfish 1 R quadrate eel 93/100 SE 173-181 HMB 3 vertebra eel
1 L opercle eel 98/101 NE JRP 2 vertebra eel 88/100 NE 212-226 HRN 1 vertebra eel 1 vertebra weever 6 vertebra garfish 101/98 SW MGV Nothing identified 100/101 NE MJF Nothing identified 101/98 SE MGU Nothing identified 88/100 SW 216-230 HRO 2 vertebra flatfish 1 os anale flatfish 1 L palatine flatfish 102/97 NW L/4 BGS 4 vertebra eel 2 vomer eel 1 L epihyal eel 1 L cleithrum eel 1 frontal eel 92/100 SE 153- HBZ 1 vomer eel 1 R dentary eel 89/100 SW 203-220 HRS 1 vertebra eel 102/94 NW (FOF?) 3 vertebra eel 4 vertebra weever 1 basioccipital gadid 1 L ceratohyal eel 1 L cleithrum eel 89/100 NE 212- HTS 2 vertebra flatfish 1 R dentary species? 92-93/100 NW OAD (fyldskifte OAB) 1 vertebra eel 102/91 SE JNZ Nothing identified (vertebra fragments)
92/100 NE 180-188 HNX 7 vertebra eel Rodent mandible L 1 L 2 R cleithrum eel 88/100 SE 216-230 HRP 1 small vertebra no ID 1 R cleithrum eel 93/100 SE HUT 1 R hyomandibular eel 100/99 SW LSE Nothing identified 93/100 NE 175-180 HLZ 8 vertebra eel 102/94 NE 216-229 MLK 1 vertebra flatfish 1 vertebra salmon/trout 102/93 SE 218-231 MMQ 2 vertebra eel 1 L opercle eel 88/100 NW 225- HTN 1 L angular eel 93/100 SW 173-178 HMA 1 vertebra eel 1 frontal eel 93/100 NW 188- HUQ 1 vertebra eel 102/92 NE JOA 1 vertebra eel 1 R dentary eel 1 basioccipital eel? (dirty) 1 R angular eel 2 L 1 R cleithrum eel 100/101 SW MJJ 2 vertebra eel 91/100 NW 171-196 HAC 1 vertebra eel 2 vertebra gadid 98/102 MZP 1 basioccipital eel 2 vertebra eel 100/99 SE LPJ 1 vertebra bull-rout
LHL 1 vertebra flatfish 1 cleithrum eel 93/100 SE 201-204 2 vertebra eel Totals 179 vertebra eel 20 vertebra flatfish 15 vertebra weever 13 vertebra gadid 11 vertebra salmon/trout 11 vertebra garfish 9 vertebra herring 2 vertebra eelpout 1 vertebra bull-rout 14 vertebra no ID 275 vertebra (261 identified) 69 non-vertebra specimens 344 total specimens (330 identified)
DJM 2050 Jesholm There were: 47 vertebrae, of which, 18 were not identified (mostly because of eroded features or clinging matrix that obscured features) 11 non-vertebra elements, including 2 otoliths 12 miscellaneous fragments, not identified Identified vertebrae include: 14 weever 5 flatfish (plaice/dab/flounder) 3 eel 3 spurdog 2 gadid 1 bull-rout 1 herring From 10 liter matrix samples: E036 N811 Orange sand 28February2008 Trench 6 10 liter 1 right opercle weever 1 basipterygium gurnard 2 vertebra flatfish 4 vertebra weever 4 vertebra too dirty for identification (probably weever) 1 vertebra not identified E038 N811 Shell layer L.1 29February2008 Trench 6 10 liter 1 vertebra spurdog E042 N813 Shell layer 04March2008 Trench 6 10 liter 1 vertebra weever 2 vertebra not identified (very eroded) 1 left cleithrum eel E044 N811 Shell layer L.1 04March2008 Trench 6 10 liter 1 fragment 1 vertebra eel 1 vertebra weever E038 N811 Orange sand 03March2008 Trench 6 10 liter 1 vertebra flatfish 2 vertebra not identified (eroded and with matrix encrustations) E040 N811 Orange sand 27February2008 Trench 6 10 liter 1 partial vertebra not identified (eroded) 1 vertebra not identified (also eroded, possibly gadid) E040 N811 Orange sand 28February2008 Trench 6 10 liter 1 vertebra flatfish 2 very small vertebra not identified 1 fragment E043 N813 Shell layer 07March2008 Trench 6 10 liter
1 ultimate vertebra flatfish 1 second vertebra gadid-familie (3,5mm anterior face) 1 vertebra not identified 1 epihyal flatfish E041 N816 Shell layer 04March2008 Trench 6 10 liter 2 fragments 2 vertebra eel 1 vertebra bull-rout 1 vertebra weever 2 vertebra not identified (eroded) E040 N811 Shell layer 26February2008 Trench 6 10 liter 1 left preopercle weever 1 half vertebra spurdog 1 vertebra herring 1 vertebra gadid (small) 5 vertebra weever 1 vertebra not identified (eroded, possibly weever) E041 N811 Shell layer L. 1 27February2008 Trench 6 10 liter 1 fragment 1 half vertebra spurdog 1 partial vertebra not identified 2 vertebra weever 1 left and 1 right otolith species? Not from 10 liter samples: E044 N812 Shell layer 06March2008 Trench 6 1 left opercle weever 1 right preopercle weever E043 N812 Shell layer 06March2008 Trench 6 1 right opercle weever 1 fragment E042 N813 Shell layer 04March2008 Trench 6 3 fragments 1 left maxillary gadid?
Lollikhuse Fish Notes 9/88 358/504 10-20cm Cod family 8 vertebra (3 sent to Anders Fischer June 2007) Flatfish 2 first vertebra 123 other vertebra 1 os anale Eel 6 vertebra (5 sent to Anders Fischer June 2007) Herring 3 vertebra Garfish 1 vertebra Unidentified 4 vertebra 16 vertebra fragments 5 other fragments MFG 9/88 x667 358/504 30-40cm Cod family 1L premaxillary MFG 9/88 x665 358/504 30-40cm Cod family 1R quadrate MFG 9/88 x610 358/504 30-40cm Cod family 1R supracleithrum 9/88 358/504 30-40cm Cod family 1 first vertebra 1 second vertebra 6 third vertebra 7 fourth vertebra 6 fifth vertebra 2 sixth vertebra 54 other vertebra 1 parasphenoid 1 vomer 1R angular Flatfish 6 first vertebra 222 other vertebra 2 os anale Eel 6 vertebra 2 cleithrum Mackerel 1 vertebra Herring 2 vertebra Garfish 22 vertebra Unidentified 23 vertebra too dirty (cf 10 flatfish) 18 vertebra 81 vertebra fragments 5 other fragments 6 fragments non-fish MFG 9/88 358/504 30-40cm Cod family 2 first vertebra 1 third vertebra 1 fifth vertebra 1 other vertebra 1 vomer 1L premaxillary 1L posttemporal 3L angular Flatfish
22 vertebra 8 os anale 1 urohyal Garfish 1 vertebra Unidentified 1 vertebra too dirty 19 vertebra fragments 24 other fragments MFG 9/88 358/504 40-50cm Cod family 10 vertebra 1R premaxillary (large fish) Flatfish 1 basioccipital 1 first vertebra 36 other vertebra Eel 1 vertebra Unidentified 6 vertebra too dirty (cf 3 flatfish, 1 garfish) 1 vertebra 10 vertebra fragments 4 other fragments MFG 9/88 x527 358/504 40-50cm Cod family 1R angular MFG 9/88 359/504 0-10cm Flatfish 7 vertebra Unidentified 1 vertebra 9/88 359/504 10-20cm Flatfish 15 vertebra Garfish 1 vertebra Unidentified 1 vertebra 11 vertebra fragments MFG 9/88 359/504 20-30cm Cod family 3 vertebra Flatfish 30 vertebra Garfish 4 vertebra Spurdog 1 dorsal spine Unidentified 8 vertebra too dirty 11 vertebra fragments 9/88 359/504 30-40cm Cod family 1 first vertebra 1 second vertebra 3 fourth vertebra 18 other vertebra (2 vertebra sent to Anders Fischer June 2007) 1L supracleithrum 1R maxillary Flatfish 13 first vertebra 655 other vertebra 1 urohyal 19 os anale Eel
16 vertebra (4 vertebra sent to Anders Fischer June 2007) 3L 1R cleithrum (3.2, 2.1, 3.3, 3.5mm) Herring 6 vertebra Garfish 34 vertebra Gurnard 1 vertebra Unidentified 30 vertebra too dirty 11 vertebra 184 vertebra fragments 55 other fragments 5 mammal/bird fragments MFG 9/88 x516 359/504 40-50cm Flatfish 1 os anale MFG 9/88 359/504 40-50cm Flatfish 2 vertebra 9/88 359/504 40-50cm Cod family 9 vertebra 2R premaxillary Flatfish 4 first vertebra 173 other vertebra 2 os anale Eel 10 vertebra 1L 1R cleithrum (3.4, 2.5mm) 2L 1R ceratohyal (3.6, 3.0, 3.0mm) Mackerel 2 vertebra Garfish 4 vertebra Unidentified 7 vertebra too dirty 8 vertebra 60 vertebra fragments 33 other fragments 5 non-fish fragments MFG 9/88 359/504 50cm-bund Cod family 2 vertebra Flatfish 9 vertebra Unidentified 1 vertebra too dirty 1 vertebra 1 vertebra fragment MFG 9/88 360/504 Afrens af grøft Flatfish 2 vertebra Herring 1 vertebra Unidentified 1 vertebra too dirty MFG 9/88 360/504 Oprens af grøft Flatfish 1 vertebra MFG 9/88 363/504 0-10cm Flatfish
1 vertebra MFG 9/88 363/504 10-20cm Flatfish 2 vertebra 9/88 363/504 30-40cm Cod family 2 vertebra Flatfish 1 first vertebra 31 other vertebra Eel 2 vertebra Garfish 11 vertebra Unidentified 5 vertebra too dirty 4 vertebra 31 vertebra fragments 4 other fragments MFG 9/88 364/504 20-30cm Flatfish 1 vertebra 9/88 364/504 40-50cm Cod family 1 first vertebra (no measure) 1 second vertebra 2 third vertebra 2 fourth vertebra 4 fifth vertebra 1 sixth vertebra 27 other vertebra 1L premaxillary 1L maxillary Flatfish 5 vertebra Garfish 6 vertebra Unidentified 7 vertebra too dirty (cf 2 flatfish, 1 eel) 1 vertebra 8 vertebra fragments 8 other fragments MFG 9/88 364/504 40-50cm Cod family 2 vertebra 1L maxillary MFG 9/88 365/502 0-15cm Flatfish 1 vertebra Unidentified 1 vertebra too dirty MFG 9/88 365/504 40-50cm Unidentified 1 vertebra too dirty (cf cod family) 9/88 366/502 10-15cm Flatfish 1 vertebra MFG 9/88 366/504 20-30cm Flatfish
1 vertebra MFG 9/88 366/504 40-50cm Cod family 1 vertebra Unidentified 1 vertebra too dirty MFG 9/88 366/505 30-40cm Cod family 1 second vertebra Flatfish 2 vertebra Garfish 1 vertebra MFG 9/88 366/505 40-50cm Cod family 1 first vertebra (9.4mm) Flatfish 2 vertebra Unidentified 1 vertebra too dirty 1 vertebra fragment MFG 9/88 366/505 50-60cm Cod family 1 vertebra Flatfish 1 vertebra Unidentified 1 vertebra fragment MFG 9/88 367/504 50-60cm Flatfish 1 vertebra MFG 9/88 367/504 60-70cm Flatfish 3 vertebra MFG 9/88 367/505 40-50cm Unidentified 1 vertebra too dirty MFG 9/88 367/505 50-60cm Unidentified 2 vertebra fragments MFG 9/88 367/505 60-70cm Cod family 1 second vertebra 2 third vertebra Flatfish 2 first vertebra 5 other vertebra Eel 1 first vertebra Garfish
2 vertebra Unidentified 2 vertebra fragments 9/88 367/505 80-90cm Cod family 1 vertebra Unidentified 1 vertebra MFG 9/88 367/505 90cm-bund Cod family 1 fourth vertebra 1 other vertebra Flatfish 1 vertebra Mackerel 1 vertebra MFG 9/88 369/510 Lag 1 40-50cm Cod family 1R posttemporal Unidentified 2 other fragments MFG 9/88 369/510 Lag 1 Garfish 1 vertebra MFG 9/88 369/510 Lag 2 Flatfish 1 vertebra Unidentified 1 vertebra too dirty 1 vertebra fragment MFG 9/88 369/510 Lag 2 Flatfish 6 vertebra Garfish 2 vertebra Unidentified 1 vertebra too dirty 1 vertebra fragment MFG 9/88 369/510 Lag 2 Cod family 1 third vertebra 2 other vertebra Flatfish 6 vertebra Mackerel 1 vertebra Garfish 3 vertebra Unidentified 1 vertebra fragment MFG 9/88 369/510 Lag 3 Flatfish
1 vertebra MFG 9/88 369/510 Lag 3 Cod family 1 vertebra Flatfish 7 vertebra Eel 1 vertebra Mackerel 1 vertebra Unidentified 2 vertebra fragments 3 other fragments MFG 9/88 369/510 Lag 4 Cod family 1 sixth vertebra MFG 9/88 369/511 Lag 1 under Lag 4 Cod family 1 other vertebra Flatfish 1 first vertebra 4 other vertebra Unidentified 1 vertebra MFG 9/88 369/511 Lag 4 Cod family 1 vertebra Flatfish 1 vertebra Unidentified 1 vertebra too dirty 1 vertebra MFG 9/88 369/511 Lag 4 Cod family 1 basioccipital 1 fourth vertebra 1 sixth vertebra 3 other vertebra Flatfish 7 vertebra Eel 1 vertebra Garfish 3 vertebra Unidentified 2 vertebra fragments 1 other fragment MFG 9/88 369/511 Lag 5 Cod family 2 third vertebra 1 fourth vertebra 1 sixth vertebra 3 other vertebra Flatfish 3 first vertebra 24 other vertebra Eel 1 first vertebra 1 other vertebra Mackerel
6 vertebra Herring 1 vertebra Garfish 10 vertebra Unidentified 1 vertebra too dirty 1 vertebra 16 vertebra fragments MFG 9/88 369/511 Lag 5 Cod family 3 vertebra Flatfish 24 vertebra Garfish 23 vertebra Unidentified 3 vertebra 12 vertebra fragments MFG 9/88 369/511 Lag 7 Flatfish 1 vertebra MFG 9/88 369/511 Lag 8 Cod family 1 vertebra Flatfish 1 vertebra MFG 9/88 369/512 Lag 3 Cod family 1 first vertebra (7.6mm) 1 other vertebra Flatfish 10 vertebra Mackerel 3 vertebra Garfish 3 vertebra Unidentified 2 vertebra 2 vertebra fragments 2 other fragments MFG 9/88 369/512 Lag 4 Unidentified 2 vertebra fragments MFG 9/88 369/512 Lag 4 Cod family 1 second vertebra 1 third vertebra Flatfish 18 vertebra Eel 1 vertebra Unidentified 5 vertebra too dirty 1 vertebra 6 vertebra fragments MFG 9/88 369/512 Lag 5 Cod family
1 third vertebra 1 other vertebra Flatfish 4 vertebra 1 os anale Eel 1 vertebra Garfish 10 vertebra Unidentified 1 vertebra too dirty 1 vertebra 10 vertebra fragments MFG 9/88 369/512 Lag 6 Cod family 2 basioccipital 2 third vertebra 1 fourth vertebra 1 fifth vertebra 2 sixth vertebra 11 other vertebra 1L 1R premaxillary Flatfish 2 first vertebra 34 other vertebra Mackerel 3 vertebra Garfish 17 vertebra Unidentified 5 vertebra 37 vertebra fragments 4 other fragments MFG 9/88 369/512 Lag 6 Cod family 3 vertebra Flatfish 15 vertebra Garfish 1 first vertebra 19 vertebra Spurdog 1 dorsal spine Unidentified 2 vertebra 10 vertebra fragments MFG 9/88 369/512 Lag 6 Garfish 1 vertebra MFG 9/88 369/512 Lag 6 Cod family 1 basioccipital 2 first vertebra 1 second vertebra 1 third vertebra 1 fourth vertebra 1 fifth vertebra 17 other vertebra Flatfish 1 first vertebra 8 other vertebra 1 os anale Garfish 4 vertebra Unidentified 5 vertebra too dirty 2 vertebra 13 vertebra fragments 9/88 370/504 50-60cm Cod family 1 third vertebra 1 fourth vertebra 1R angular Flatfish
2 vertebra Unidentified 1 vertebra too dirty 3 vertebra fragments 9/88 370/504 70-73cm Cod family 1 second vertebra 1 fifth vertebra 1 other vertebra 1R supracleithrum Flatfish 2 vertebra Unidentified 1 vertebra too dirty 3 vertebra fragments 1 other fragment 9/88 371/504 50-60cm Cod family 1 fourth vertebra 9/88 372/504 40-50cm Cod family 3 vertebra (1 very large) Flatfish 5 vertebra Unidentified 1 vertebra (cf cod family) 2 vertebra fragments 9/88 374/504 30-40cm Flatfish 1 vertebra 9/88 374/504 40-50cm Cod family 1 first vertebra 2 other vertebra Unidentified 3 vertebra too dirty (cf flatfish) 1 vertebra fragment 9/88 374/504 50-60cm (1) Flatfish 2 vertebra Mackerel 1 vertebra 9/88 374/504 60-70cm Cod family 1 vertebra Flatfish 1 os anale 1 fragment vertebra Garfish 1 vertebra 9/88 375/504 20-30cm Cod family 2 vertebra Unidentified 1 vertebra fragment 9/88 375/504 50-60cm
Cod family 1 second vertebra Garfish 1 vertebra 9/88 376/504 40-50cm Flatfish 1 os anale 9/88 376/504 40-50cm Cod family 1 third vertebra 1 other vertebra Flatfish 1 first vertebra 1 urohyal Unidentified 1 vertebra fragment 9/88 376/504 50-60cm Cod family 1 third vertebra Flatfish 2 vertebra 9/88 376/504 50-60cm Flatfish 9 vertebra 1 os anale Garfish 1 first vertebra 1 other vertebra Mackerel 1 vertebra Unidentified 1 vertebra fragment 9/88 376/504 60-70cm pose 1 Flatfish 1 first vertebra 18 other vertebra 1 os anale Eel 1 vertebra Garfish 1 vertebra Unidentified 2 vertebra too dirty 3 vertebra 10 vertebra fragments 9/88 376/504 60-70cm pose 2 Flatfish 10 vertebra 1 os anale Mackerel 1 vertebra Unidentified 2 vertebra too dirty 2 vertebra fragments 9/88 377/504 60-70cm Flatfish 1 vertebra Garfish 2 vertebra
Unidentified 1 vertebra fragments 2 other fragments 9/88 378/504 0-10cm Unidentified 1 vertebra too dirty 1 other fragment 9/88 378/504 40-50cm Flatfish 2 vertebra Unidentified 3 vertebra fragments 2 other fragments 9/88 378/504 60-70cm Flatfish 1 vertebra 9/88 379/504 30-40cm Flatfish 1 vertebra Unidentified 1 vertebra too dirty (cf flatfish) 9/88 379/504 40-50cm Cod family 1L premaxillary Flatfish 1 vertebra Unidentified 2 vertebra too dirty 2 vertebra fragments 9/88 379/504 50-60cm Cod family 1 vertebra Flatfish 3 vertebra Unidentified 2 vertebra fragments 1 other fragment 9/88 379/504 60cm-bund Flatfish 1 first vertebra 4 other vertebra Unidentified 1 vertebra fragment 9/88 380/504 20-30cm Flatfish 1 vertebra Garfish 1 vertebra Unidentified 1 vertebra fragment 9/88 380/504 30-40cm Cod family 2 second vertebra 1 third vertebra 11 other vertebra
1L premaxillary 1R maxillary Flatfish 1 first vertebra 16 other vertebra 1 os anale Eel 4 vertebra Garfish 9 vertebra Unidentified 3 vertebra too dirty 10 vertebra fragments 9/88 380/504 40-50cm Cod family 7 vertebra Flatfish 16 vertebra Eel 1 vertebra Mackerel 2 vertebra Garfish 11 vertebra Unidentified 3 vertebra too dirty 10 vertebra fragments 1 other fragment 9/88 380/504 50-60cm Cod family 2 vertebra 1L premaxillary Flatfish 8 vertebra Eel 1 cleithrum Unidentified 2 vertebra too dirty (herring?) 2 vertebra fragments 9/88 380/504 60-70cm Cod family 1R maxillary Flatfish 1 vertebra Unidentified 1 other fragment MFG 9/88 381/503 20-30cm Cod family 3 vertebra 1R premaxillary Flatfish 8 vertebra Unidentified 3 vertebra too dirty 1 vertebra 1 vertebra fragment MFG 9/88 381/503 30-40cm Cod family 1 third vertebra 1 fifth vertebra 4 other vertebra 1L dentary (cod, from a large fish) Flatfish 64 other vertebra 3 os anale
Eel 6 vertebra Mackerel 1 vertebra Garfish 1 first vertebra 35 vertebra Unidentified 10 vertebra too dirty 2 vertebra 24 vertebra fragments MFG 9/88 381/503 Lag 4 Cod family 5 vertebra Flatfish 2 vertebra Unidentified 1 vertebra 1 other fragment 9/88 381/504 0-10cm Cod family 1 vertebra Flatfish 1 vertebra 9/88 381/504 10-20cm Cod family 3 vertebra Flatfish 3 vertebra Garfish 2 vertebra Spurdog 1 dorsal spine Unidentified 1 vertebra too dirty (cf cod family) 1 vertebra 2 vertebra fragments 9/88 381/504 20-30cm Cod family 1 second vertebra 2 third vertebra 6 other vertebra 1R premaxillary (sent to Anders Fischer June2007) Flatfish 29 vertebra Eel 4 vertebra Garfish 6 vertebra Unidentified 1 vertebra 31 vertebra too dirty 32 vertebra fragments 3 other fragments 9/88 381/504 40-50cm Cod family 3 vertebra Flatfish 14 vertebra Eel 4 vertebra
Garfish 1 vertebra Unidentified 10 vertebra too dirty 10 vertebra fragments 9/88 381/504 50-60cm Unidentified 1 vertebra 1 vertebra fragment 1 other fragment 9/88 381/504 60cm-bund Cod family 2 vertebra Garfish 1 vertebra MFG 9/88 383/504 Lag 4 30-40cm Unidentified 1 vertebra too dirty 1 vertebra fragment MFG 9/88 386/504 0-10cm Cod family 2 vertebra MFG 9/88 387/504 Øverste lag 0-10cm Cod family 1 first vertebra 3 third vertebra 1 fifth vertebra 5 other vertebra Flatfish 1 first vertebra 12 other vertebra Garfish 3 vertebra Unidentified 9 vertebra too dirty 2 vertebra 13 vertebra fragments MFG 9/88 388/504 Cod family 1 fifth vertebra 9 other vertebra Flatfish 1 first vertebra 21 other vertebra Garfish 2 vertebra Unidentified 1 vertebra 14 vertebra fragments 1 other fragment MFG 9/88 389/504 Cod family 1 vertebra Unidentified 1 vertebra MFG 9/88 390/505 Østerlag Cod family 1 third vertebra 2 other vertebra Flatfish 1 first vertebra 2 other vertebra Unidentified
2 vertebra too dirty 1 vertebra fragment MFG 9/88 391/506 Skallag Cod family 1 first vertebra (no measure) 3 other vertebra Unidentified 1 vertebra too dirty 4 vertebra fragments MFG 9/88 391/507 Lag 2 Garfish 1 vertebra Unidentified 2 vertebra fragments MFG 9/88 393/507 Lag 6 Garfish 1 vertebra Unidentified 1 vertebra too dirty
Nederst Fish Notes X9483 søldeprøve Cod family 1 second vertebra 1 third vertebra 1 fourth vertebra 37 vertebra A 30 vertebra B 51 vertebra C 1R premaxillary (2 fragments, 1 fragment burned) 1L supracleithrum 1L quadrate 3L 1R otolith (1 fragment) 1L 1R vomer 3L 2R palatine 3L 1R posttemporal 1L angular 5L 2R maxillary 1L 1R opercle 1 branchiostegal ray 1 parasphenoid 2L 1R epihyal (1 burnt) Flatfish 13 basioccipital 35 first vertebra (4.6, 4.2, 4.1, 4.1, 3.5, 4.4, 4.1, 2.6, 4.2, 4.2, 4.0, 3.6, 3.9, 4.2, 4.0, 4.7, 3.5, 4.9, 5.0, 4.2, 4.0, 4.4, 4.8, 3.6, 4.3, 3.7mm, 9 no measure) 110 vertebra A (1 burnt) 190 vertebra B 874 vertebra C (8 turbot) 8L 5R premaxillary 3L 3R supracleithrum 11L 4R quadrate 7 os anale 14 urohyal 13 vomer 8L palatine 1L 1R posttemporal 3R angular 7L 13R maxillary 2 pharyngobranchial 1L 1R ceratohyal Eel 2 first vertebra 2 vertebra A 9 vertebra B 84 vertebra C 1L 1R cleithrum 1L ceratohyal (1.8mm) 1L anguloarticular Weever 3 vertebra B 8 vertebra C 1R quadrate Eelpout 3 vertebra B 15 vertebra C Trout/salmon 4 vertebra C Stickleback 1 vertebra Herring 11 vertebra C Unidentified 38 vertebra B (1 calcined) 47 vertebra C X9394 Cod family 1 first vertebra (6.2mm) 1 second vertebra 4 third vertebra 2 fourth vertebra 1 vertebra A 3 vertebra B 15 vertebra C 1 parasphenoid 1L maxillary 2L otolith 1R dentary 1R supracleithrum Flatfish 12 basioccipital 36 first vertebra (3.8, 5.4, 3.9, 3.6, 5.1, 4.8, 4.4, 5.2, 4.4, 4.5, 4.2, 3.6, 4.5, 5.0, 4.8, 3.5, 4.5, 4.4, 5.5, 3.7, 4.3, 5.4, 4.5, 4.0, 5.2, 4.3, 4.0, 3.7, 4.3mm, 7 no measure) 111 vertebra B (1 burnt) 1227 vertebra C (2 burned, minimum 1 turbot) 69 vertebra A 1L 3R angular 7L 13R maxillary 24 os anale (6 fragments) 8 urohyal 10 vomer 1 otolith 1L 1R dentary 1L 2R premaxillary 6L 5R quadrate 10L 5R supracleithrum 8L 1R palatine 3 pharyngobranchial 1R cleithrum 5R hyomandibular 13 ectopterygoid 4L 3R epihyal 2R hypohyal 4R posttemporal Eel
4 vertebra B 41 vertebra C 1L opercle 2Lceratohyal (2.4, 1.8mm) Weever 1 basioccipital 12 vertebra C 2L 1R quadrate Herring 4 first vertebra 8 vertebra B 62 vertebra C Eelpout 1 vertebra C Unidentified 38 vertebra B 17 vertebra C X4915 Cod family 1 basioccipital 2 first vertebra (7.0, 5.5mm) 6 second vertebra (1 burnt) 5 third vertebra 5 fourth vertebra (1 burnt) 4 fifth vertebra 43 vertebra A (6 burnt) 39 vertebra B (4 burnt, 1 calcined) 135 vertebra C (3 burnt, 2 calcined) 4L 3R otolith (3 fragments) 5L 3R premaxillary (3 burnt) 2L 5R dentary (2 burnt) 3L 5R quadrate (1 burnt) 3L 4R maxillary (1 burnt) 2L angular 3L 1 whole vomer 4 parasphenoid 1 pharyngobranchial 2L 1R supracleithrum 1L 2R posttemporal 1L 4R palatine 2L 2R epihyal 2 branchiostegal rays (1 burnt) 1R opercle 2 mesethmoid Flatfish 5 basioccipital 10 first vertebra (3.7, 5.3, 3.8, 3.3, 3.5, 3.6, 2.7, 3.8, 4.4, 4.3mm) 21 vertebra A (1 burnt) 50 vertebra B (1 burnt) 427 vertebra C (7 burnt) 1L premaxillary 2L 1R quadrate 1L maxillary 2R angular 1 vomer 6 urohyal 2 pharyngobranchial 2L 2R supracleithrum 2L palatine 5 os anale 4 ectopterygoid 1L pterotic (flounder) Eel 7 basioccipital (1 burnt) 4 first vertebra 24 vertebra A (2 burnt) 52 vertebra B (7 burnt, 4 calcined) 356 vertebra C (41 burnt, 7 calcined) 7L 2R ceratohyal (3.5, 1.9, 2.1, 1.6, 2.1, 1.4, 1.7, 1.0, 1.1mm) 1L 2R dentary 1R quadrate 1 parasphenoid 3 vomer 1L 2R cleithrum 1L opercle 1R frontal Mackerel 10 vertebra A (1 burnt) 4 vertebra C (1 burnt) Herring 13 first vertebra (6 burnt, 6 calcined) 14 vertebra A (8 burnt, 3 calcined) 166 vertebra B (102 burnt, 52 calcined) 189 vertebra C (86 burnt, 62 calcined) 15 prooticum (13 burnt, 2 calcined) Eelpout 5 vertebra C (1 burnt) Weever 3 basioccipital 2 first vertebra 8 vertebra B (2 burnt) 111 vertebra C (6 burnt, 3 calcined) 1L dentary 1R premaxillary 1R quadrate 1R maxillary 1L 2R opercle 1R hyomandibular Unidentified 29 vertebra B (6 burnt, 2 calcined) 39 vertebra C (4 burnt, 1 calcined) X108 Cod family 3 second vertebra 4 third vertebra (1 calcined) 1 fourth vertebra 10 vertebra A 37 vertebra B (1 burnt) 40 vertebra C 1L 2R otoliths (4 fragments) 1 parasphenoid 1L palatine
1R cleithrum 3L 3R premaxillary 1L dentary 1L 1R vomer 1R angular 1L 1R quadrate 2R maxillary 2L 1R posttemporal 1L 1R supracleithrum 1R hypohyal Flatfish 3 basioccipital 1 first vertebra (no measure) 6 vertebra A 38 vertebra B 119 vertebra C 1R supracleithrum 2 os anale 1 urohyal 2 ectopterygoid 1L palatine 1L pterotic (flounder) 1 interhyal 1R quadrate Eel 5 basioccipital 2 first vertebra 25 vertebra A 51 vertebra B (1 calcined) 266 vertebra C 2L 1R dentary (1 fragment) 3 vomer 4L 6R ceratohyal (1.7, 2.0, 1.5, 2.0, 1.9, 2.1, 1.7, 1.3, 1.4, 1.2mm) 3L 3R 1? cleithrum 1R anguloarticular 1L 1R epihyal 1L hyomandibular 2L 1R quadrate Mackerel 2 vertebra A 5 vertebra B 6 vertebra C Herring 1 first vertebra 3 vertebra B 13 vertebra C Sitckleback 1 vertebra Eelpout 2 vertebra B 6 vertebra C Weever 3 basioccipital 3 first vertebra 4 vertebra A 17 vertebra B 150 vertebra C (3 burnt) 1L dentary 1R premaxillary 1L 1R angular 1L maxillary 1L posttemporal 1L 1R supracleithrum Bull-rout 1 vertebra C Unidentified 24 vertebra B 13 vertebra C X9110 (#2) Cod family 1 basioccipital 1 first vertebra (no measure) 3 second vertebra 2 third vertebra 2 fourth vertebra 1 fifth vertebra 11 vertebra A 16 vertebra B 41 vertebra C 1R otolith 1 parasphenoid 1R supracleithrum 1R quadrate 1R hyomandibular 1L 1R premaxillary 1R angular Flatfish 1 basioccipital 9 first vertebra (3 no measure, 4.6, 4.2, 4.2, 3.9, 3.5, 2.2mm) 16 vertebra A 34 vertebra B 110 vertebra C 2 vomer 5 ectopterygoid 3 os anale 4 urohyal 2 hypohyal 1 epihyal 1L palatine 4L 5R supracleithrum 1R cleithrum 3 interhyal 2 pharyngobranchial 3L 1R hyomandibular 4L 5R premaxillary 1L maxillary 1L angular Eel 5 basioccipital 7 first vertebra 37 vertebra A 84 vertebra B (1 calcined) 219 vertebra C (1 calcined) 1L dentary 7 vomer 1 parasphenoid 2L 3R quadrate 1L 2R hyomandibular 4L 4R anguloarticular 4R epihyal 1L 1R frontal 2L 2R cleithrum
5L 8R ceratohyal (2.7, 3.2, 2.4, 1.6, 1.7, 1.3, 1.1, 1.5, 1.4, 1.8, 1.2, 1.1, 1.1mm) Herring 1 first vertebra 13 vertebra B 50 vertebra C Eelpout 1 first vertebra 4 vertebra A 10 vertebra B 127 vertebra C Trout/salmon 1 vertebra A 3 vertebra B 5 vertebra C Weever 14 basioccipital 21 first vertebra 8 vertebra A 59 vertebra B 557 vertebra C 3L 5R palatine 8 parasphenoid 1L 1R cleithrum 2L 2R angular 1L 1R epihyal 8L 5R quadrate 1R hyomandibular 4L 6R posttemporal 14 vomer 1L 2R dentary 2 (mes)ethmoid 4L 6R opercle 5L 4R premaxillary 7L 6R maxillary Bull-rout 1 first vertebra 9 vertebra C Spurdog 12 vertebra A Unidentified 48 vertebra B 29 vertebra C X4915 Cod family 7 basioccipital (1 burnt, 1 calcined) 8 first vertebra (4 no measure, 7.3, 6.6, 5.6, 5.2mm) 12 second vertebra (3 burnt, 2 calcined) 10 third vertebra (2 burnt, 1 calcined) 10 fourth vertebra (2 burnt, 1 calcined) 16 fifth vertebra (2 burnt) 3 sixth vertebra 102 vertebra A (28 burnt, 13 calcined) 114 vertebra B (34 burnt, 16 calcined) 191 vertebra C (31 burnt, 7 calcined) 9L 6R otoliths (1 fragment) 5L 5R quadrate (2 burnt) 3L 2R vomer 10L 6R angular (3 burnt, 2 calcined) 12L 8R maxillary (4 burnt) 7L 8R dentary (4 burnt) 8L 9R premaxillary (6 fragments, 4 burnt, 3 calcined) 2L 2R posttemporal (3 burnt) 8 branchiostegal rays 9 parasphenoid (1 fragment, 3 burnt) 7L 3R supracleithrum (3 burnt) 1R hyomandibular 5L 4R palatine (3 burnt) 2R interopercle 2L epihyal 1R ceratohyal 5 pharyngeal plates 1R postcleithrum 2L 2R symplectic 1L 2R opercle 4L 3R sphenotic (1 burnt) 2L 2R cleithrum 4 epibranchial 1L ectopterygoid Flatfish 5 basioccipital 27 vertebra A (1 burnt, 1 calcined) 11 first vertebra (9.1, 4.3, 4.2, 3.5, 2.7, 3.5, 2.9, 2.3, 3.8, 5.3mm, 1 no measure, 1 burnt) 55 vertebra B (1 burnt) 398 vertebra C (14 burnt, 3 calcined, 2 turbot) 5 vomer 1L otolith 3L 2R angular 4L 2R maxillary 12 urohyal 7 ectopterygoid 3 os anale (5 fragments) 3L 1R premaxillary 1L 1R dentary 2L 1R posttemporal 1L 1R supracleithrum 1L hyomandibular 3L palatine 1L 1R epihyal 1 pharyngobranchial 2L quadrate Eel 5 basioccipital (1 burnt) 1 first vertebra 20 vertebra A 58 vertebra B (3 burnt) 206 vertebra C (6 burnt, 3 calcined) 1L 2R quadrate 2L 1R anguloarticular 1R dentary 1L frontal 1L 1R epihyal 3L 2R cleithrum 2L 2R ceratohyal (1.3, 2.2, 1.0, 1.0mm) 1 parasphenoid 1L hyomandibular 1L opercle
Herring 5 first vertebra (2 burnt) 2 vertebra A (1 burnt, 1 calcined) 18 vertebra B (9 burnt, 4 calcined) 39 vertebra C (7 burnt, 7 calcined) 3 prooticum (2 burnt) Mackerel 2 vertebra A (1 burnt) 3 vertebra C Eelpout 5 vertebra C Spurdog 1 vertebra A Trout/salmon 1 vertebra C Weever 6 basioccipital (1 burnt) 11 first vertebra (5 burnt, 2 calcined) 5 vertebra A (3 burnt, 2 calcined) 17 vertebra B (7 burnt, 4 calcined) 218 vertebra C (30 burnt, 24 calcined) 4L 2R quadrate 1 vomer 1 (mes)ethmoid 2L angular 3L maxillary 2L premaxillary 2L 2R dentary (1 burnt) 4L 3R posttemporal 4L 2R hyomandibular (1 burnt) 1R palatine (burnt) 1L 1R epihyal 1L 1R ceratohyal 2L 4R opercle (1 burnt, 2 calcined) Unidentified 29 vertebra B (6 burnt, 4 calcined) 21 vertebra C (5 burnt) X8594 grøft Cod family 1R vomer 1L maxillary Flatfish 1 first vertebra (no measure) 2 vertebra B 5 vertebra C Eel 1 vertebra B 2 vertebra C Weever 5 vertebra B 16 vertebra C Unidentified 2 vertebra B 2 vertebra C (too dirty) X8594 fint Cod family 1 first vertebra (3.7mm) 1 second vertebra 1 third vertebra 3 vertebra B 5 vertebra C 1L 1R otoliths (1 fragment) 1L premaxillary 1R maxillary Flatfish 4 first vertebra (2 no measure, 3.4, 4.7mm) 5 vertebra B 21 vertebra C (2 burnt) 1R pterotic (flounder) 1R premaxillary 1R angular 1 urohyal 1R quadrate Eel 6 first vertebra 13 vertebra B (2 burnt, 1 calcined) 42 vertebra C (5 burnt, 1 calcined) 1 vomer 2L 1R ceratohyal (2.2, 1.9, 1.6mm) 1 dentary Weever 6 first vertebra 18 vertebra B (1 burnt) 82 vertebra C (5 burnt) 1R quadrate 2R opercle 1L 1R premaxillary Herring 2 vertebra B 5 vertebra C (1 burnt) 1 prooticum Eelpout 1 first vertebra 2 vertebra C (1 burnt) Unidentified
25 vertebra B (1 calcined) 17 vertebra C (1 burnt) X8502 <fint – not labeled> 1 bead, removed Cod family 1 fifth vertebra 3 vertebra C (1 burnt) 1 branchiostegal ray 1R maxillary 1L angular 1 fragment otolith Flatfish 1 basioccipital 1 vertebra B 4 vertebra C 1 urohyal Eel 2 basioccipital 2 vertebra A 4 vertebra B 16 vertebra C (5 burnt) 1 dentary 1L ceratohyal (2.6mm) Trout/salmon 1 vertebra C (calcined) Weever 1 first vertebra 7 vertebra C (1 burnt) Unidentified 5 vertebra B 7 vertebra C X8492 fint Cod family 1 third vertebra 1 vertebra A 2 vertebra B (1 calcined) 3 vertebra C 1L premaxillary 1R supracleithrum 1R hyomandibular Flatfish 1 vertebra B 5 vertebra C Eel 1 first vertebra 3 vertebra A (1 burnt) 5 vertebra B (1 burnt) 20 vertebra C (4 burnt, 2 calcined) Weever 3 vertebra B 14 vertebra C (2 burnt) 1L opercle Bull-rout 4 vertebra C (1 calcined) Unidentified 3 vertebra B 7 vertebra C (1 burnt) X8566 <fint> Cod family 1 second vertebra 1 vertebra B 2 vertebra C (1 burnt) 1L vomer Flatfish 2 vertebra A 2 vertebra B 10 vertebra C Eel 2 vertebra A 7 vertebra C 1R cleithrum 1 epihyal Weever 2 vertebra B 23 vertebra C Herring 2 vertebra C Salmon/trout 1 vertebra C Bull-rout 4 vertebra C Unidentified 5 vertebra B 1 vertebra C
X8769 grøft Cod family 1 first vertebra (7.1mm) 1 second vertebra 1 third vertebra 1 fifth vertebra 3 vertebra B 6 vertebra C 1 parasphenoid Flatfish 1 vertebra B 23 vertebra C 1 os anale 2L supracleithrum Eel 1 basioccipital 1R epihyal Weever 1R frontal (investing bone) 1L angular Unidentified 1 vertebra B 1 vertebra C X8813 fint Flatfish 4 vertebra A 3 vertebra B 14 vertebra C Eel 1 basioccipital 3 vertebra B 6 vertebra C Weever 2 vertebra C (1 calcined) Unidentified 4 vertebra B 1 vertebra C X8813 grøft Flatfish 2 vertebra B 5 vertebra C 1R supracleithrum Eel 1L cleithrum X9110 grøft excellent preservation Cod family 1 vertebra C 1R otolith 1L premaxillary 1 parasphenoid Flatfish 1 first vertebra (4.7mm) 7 vertebra B 42 vertebra C 1R angular 1R supracleithrum 2 os anale 1L pterotic (flounder) 1L posttemporal 1R cleithrum Eel 1 basioccipital 1 vertebra A 1 vertebra B 7 vertebra C 1 vomer Eelpout 3 vertebra C Weever 1 basioccipital 1 first vertebra 1 vertebra B 117 vertebra C 1L premaxillary 1L maxillary 3R cleithrum 1R subopercle 5L 1R opercle 6L 3R hyomandibular 1L 1R angular 1L dentary 2L 3R posttemporal 1R frontal (investing bone) 1L ceratohyal 1 parasphenoid Trout/salmon 4 vertebra C Herring 1 vertebra B Unidentified
1 vertebra B 3 vertebra C X9110 grøft Cod family 2 vertebra C 1R supracleithrum Flatfish 1 basioccipital 1 first vertebra (4.1mm) 6 vertebra B 51 vertebra C 3 os anale 2 urohyal 1L quadrate 1R dentary 1R maxillary 1L hyomandibular Eel 1 basioccipital 1 first vertebra 4 vertebra B 15 vertebra C 3 vomer 1R cleithrum 2L ceratohyal 1L hyomandibular Weever 2 basioccipital 1 first vertebra 5 vertebra B 112 vertebra C 1L maxillary 1L angular 2L 2R opercle 1R frontal (investing bone) 1L 1R cleithrum 2L 1R supracleithrum 2L posttemporal 2L 2R ceratohyal & epihyal 1L quadrate 1L dentary 2 parasphenoid 3L 2R hyomandibular Herring 1 first vertebra Eelpout 1 basioccipital 9 vertebra C Unidentified 1 vertebra B 2 vertebra C X9347 grøft Cod family 1 first vertebra (5.0mm) 2 second vertebra 4 third vertebra 3 fourth vertebra 2 fifth vertebra 17 vertebra A 23 vertebra B 40 vertebra C 2L 1R otoliths 1R quadrate 1L supracleithrum 1R cleithrum 2L maxillary 2L 1R angular 1R vomer 1L hyomandibular 1R posttemporal 1 branchiostegal ray 4L 3R premaxillary 2L epihyal 1L hypohyal 1L dentary Flatfish 1 basioccipital 2 first vertebra (4.3, 5.7mm) 9 vertebra A 7 vertebra B 123 vertebra C 1 os anale (2 fragments) 1L supracleithrum 1 urohyal 1 vomer 1L 1R quadrate 1L palatine Eel 9 vertebra C 1 vomer Weever 1 vertebra B 29 vertebra C 1L opercle 1L 2R angular 1L dentary 1L quadrate Herring 1 first vertebra 2 vertebra C Eelpout 1 vertebra C Unidentified 5 vertebra B 3 vertebra C X9347 fint
Cod family 1 second vertebra 30 vertebra A 19 vertebra B 23 vertebra C 2R otoliths (1 fragment) 1L supracleithrum 1L quadrate 1 parasphenoid Flatfish 1 basioccipital 1 first vertebra (2.7mm) 21 vertebra A 27 vertebra B 70 vertebra C (1 calcined) 1 vomer 1R premaxillary 2R angular 1L palatine Eel 1 basioccipital 1 vertebra A 5 vertebra B 38 vertebra C Weever 3 basioccipital 2 first vertebra 1 vertebra A 2 vertebra B 55 vertebra C (1 burnt) 1 vomer 1R premaxillary 1R quadrate 1 parasphenoid 1 (mes)ethmoid Mackerel 1 vertebra B Herring 1 first vertebra 3 vertebra C Bull-rout 1 vertebra C Eelpout 4 vertebra C Stickleback 2 vertebra C Unidentified 11 vertebra B 18 vertebra C X9469 grøft Cod family 1 basioccipital 1 first vertebra (6.8mm) 3 second vertebra 5 third vertebra 1 fourth vertebra 1 fifth vertebra 14 vertebra A 14 vertebra B 30 vertebra C 3L 2R otoliths (2 fragments) 2R hyomandibular 1 pharyngobranchial 1R vomer 1L dentary 3L 3R premaxillary 1L supracleithrum 1 parasphenoid 2L 2R maxillary 1R angular Flatfish 2 basioccipital 2 first vertebra (1 no measure, 3.9mm) 7 vertebra A 17 vertebra B 149 vertebra C 6 os anale (1 fragment) 1 vomer 1L premaxillary 1L supracleithrum 4 urohyal Eel 2 basioccipital 1 vertebra A 1 vertebra B 8 vertebra C 1 vomer 1L 1R cleithrum 1L ceratohyal (1.6mm) Weever 20 vertebra C 1R angular Mackerel 1 vertebra C Herring 1 vertebra C Eelpout 3 vertebra C Unidentified
9 vertebra B X8484 grøft Cod family 1 vertebra A 4 vertebra C 1L otolith 2L posttemporal 1L 1R supracleithrum 1L angular Flatfish 1 vertebra A 1 vertebra B 4 vertebra C (1 burnt) 1R supracleithrum Eel 6 vertebra C (4 burnt) Weever 1 first vertebra 1 vertebra A 4 vertebra C Eelpout 1 vertebra C (burnt) Unidentified 1 vertebra C (burnt) X8484 fint Cod family 2 vertebra A 1L otolith 1 mesethmoid 1R posttemporal Flatfish 1 first vertebra (4.2mm) 4 vertebra A 4 vertebra C Eel 5 vertebra A (1 burnt) 6 vertebra B (1 burnt) 28 vertebra C (6 burnt) 1L ceratohyal (2.2mm) Weever 1 vertebra B 2 vertebra C Herring 1 vertebra C (burnt) Eelpout 2 vertebra C Unidentified 5 vertebra B (1 calcined) 2 vertebra C (1 burnt) X9469 fint Cod family 30 vertebra A 22 vertebra B 21 vertebra C 1L 2R otolith (1 fragment) 1L angular 2L supracleithrum 1R maxillary 1L quadrate 1L dentary Flatfish 3 basioccipital 15 first vertebra (6 no measure, 3.6, 2.6, 2.3, 2.3, 4.1, 4.2, 4.4, 3.8, 2.3) 40 vertebra A 67 vertebra B 253 vertebra C 3 os anale 4 urohyal 5 vomer 2R angular 2L 5R maxillary 1L 1R posttemporal 1L palatine 1L hyomandibular 3L 1R supracleithrum 2L 2R quadrate Eel 3 basioccipital 1 first vertebra 13 vertebra A 23 vertebra B 108 vertebra C 1 vomer 1L 1R ceratohyal (1.1, 1.3mm) 1L cleithrum Trout/salmon 1 vertebra A Weever 3 first vertebra 6 vertebra B 45 vertebra C
1L quadrate Herring 5 vertebra B 12 vertebra C Mackerel 1 vertebra B Eelpout 16 vertebra C Bull-rout 2 vertebra C Unidentified 39 vertebra B 28 vertebra C X5110 grøft Cod family 1 basioccipital 1 first vertebra (no measure) 2 second vertebra 3 third vertebra 1 fourth vertebra 4 fifth vertebra 33 vertebra A (1 burnt) 55 vertebra B (1 burnt) 89 vertebra C (1 burnt) 5L 4R otoliths (4 fragments) 1L angular 3L premaxillary (1 fragment) 3R dentary 2L 3R posttemporal 3L 1R maxillary 1R quadrate 3L 4R supracleithrum 1L 2R 1 whole vomer 1 pharyngobranchial 1 parasphenoid 1 branchiostegal ray 1L 1R cleithrum 3R epihyal 1L opercle 1L palatine Flatfish 10 basioccipital 28 first vertebra (8 no measure, 3.3, 3.7, 4.2, 3.9, 1.9, 3.6, 3.5, 3.4, 2.8, 3.7, 4.5, 4.6, 3.4, 2.8, 3.6, 4.3, 3.5, 3.7, 5.0, 2.5mm) 37 vertebra A (1 burnt) 82 vertebra B (1 burnt) 561 vertebra C (5 burnt, 1 calcined) 9 os anale 9 urohyal 2L 2R premaxillary 2L 4R hyomandibular 2L 7R maxillary 3L 2R quadrate 3L 2R supracleithrum 5L palatine 2 pharyngobranchial 7 vomer 1 parasphenoid Eel 5 basioccipital 5 first vertebra (1 burnt) 30 vertebra A (3 burnt) 73 vertebra B (2 burnt) 512 vertebra C (5 burnt) 1L 1R anguloarticular 1L 2R hyomandibular 5 vomer 2L dentary 5L 5R ceratohyal (2.1, 2.2, 2.6, 1.3, 1.4, 0.9, 1.8, 1.3, 1.4, 1.1mm) 3R epihyal 6L 3R cleithrum 2 parasphenoid 2L 1R frontal 1L 1R opercle Herring 5 first vertebra 26 vertebra B (2 burnt) 154 vertebra C (2 burnt) 2 prooticum Mackerel 4 vertebra B 5 vertebra C Weever 5 basioccipital 8 first vertebra 13 vertebra B (1 burnt) 198 vertebra C (7 burnt, 4 calcined) 1R angular 1L dentary 1L 4R posttemporal 3L 1R hyomandibular 4L 3R opercle 1 vomer 3 parasphenoid 1 investing bone 1L ceratohyal 2L 1R supracleithrum Eelpout 3 vertebra C Salmon/trout 1 vertebra A 2 vertebra C Unidentified 46 vertebra B (2 burnt) 42 vertebra C (1 burnt)