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Environmental monitors onlobster traps (eMOLT):
long-term observations ofNew England’s bottom-water
temperatures
J Manning, Northeast Fisheries Science Center, National Oceanic and Atmospheric
Administration, Woods Hole, Massachusetts, USA
E Pelletier, Gulf of Maine Lobster Foundation, Kennebunk, Maine, USA
Nearly one hundred New England lobstermen have installed temperature sensors on
their traps to record hourly values at fixed locations since 2001. These moorings are
distributed primarily along the shelf edge in the northern Mid-Atlantic Bight and along
the entire western edge of the Gulf of Maine in a range of water depths (1–300m).
Variability associated with tidal, wind, seasonal, and inter-annual processes can be
depicted at nearly all sites. Tidal variation, for example, at certain times of the year in
many locations can be significant (.108C). Wind forcing is shown to significantly modify
the seasonal cycle at many locations such as in Massachusetts Bay where a dramatic
turnover occurs in the Fall. Inter-annual anomalies are derived by removing seasonal
cycles. Comparisons between sites and between years are made. The years 2002 and
2006, for example, are documented as warmer in general than other years at nearly all
sites. While a direct correlation between temperature variability and lobster catch is
difficult to quantify in the data collected thus far, preliminary investigations document the
relationships on a seasonal time scale.
The possibility of incorporating this network of moored sensors into a regional ocean
observing system is addressed and the limitations are discussed. Given the minimum cost
required to deploy the instrumentation and the sustained interest of the fishermen, the
initiative provides a means to collect data continuously and a strategy for monitoring
environmental change on climatic time scales.
AUTHORS’ BIOGRAPHIES
James P Manning has been employed as an oceanographer
for the NOAA’s Northeast Fisheries Science Center for
more than 20 years. After receiving his masters degree in
oceanography from the University of Rhode Island in 1987,
he has been investigating physical processes on New Eng-
land’s shelf and their relationship to fisheries. In addition to
working with local fishermen, he is particularly interested in
providing data to local coastal ocean circulation modellers
to help initialise, assimilate, and validate numerical simula-
tions.
Environmental monitors on lobster traps (eMOLT)
Volume 2 No. 1 2009 Journal of Operational Oceanography 25
Erin Pelletier has worked on eMOLT and a variety of other
collaborative research projects for the last decade. As ex-
ecutive director of the Gulf of Maine Lobster Foundation,
she coordinates, for example, extensive ‘ventless trap’ and
‘rope exchange’ programs with fishermen throughout New
England. Trained in environmental education, she specialises
in outreach to fishermen and helps them sustain their
resource.
INTRODUCTION
Much of the historical record of bottom tempera-
ture in the New England region comes from
NOAA’s Northeast Fisheries Science Center1
and Canada’s Department of Fisheries and
Oceans.2 These observations extend back nearly a hundred
years so that decadal scale variability can be investigated.
Since most of these observations are shipboard casts made
a few times per year, the higher frequency event-scale
variability in temperature is largely missed. Beginning in
2001, the Gulf of Maine Ocean Observing System (Go-
MOOS) deployed moorings at several locations that mea-
sure temperature throughout the water column. These
observations provide greater insight into higher-frequency
temperature variability but only at a limited number of
locations – limited by the cost of mooring operations.
There are several million lobster traps deployed around
the Gulf of Maine. The fishermen who maintain these
moorings could make a significant contribution to the ocean
observing systems of New England. Not only are they on
the water on a near-daily basis for much of the year but
they have a sincere interest in their resource and the envir-
onmental changes that may affect that resource. The Envir-
onmental Monitors on Lobster Traps (eMOLT) project has
collaborated with lobsterman and deployed internally-
recording temperature sensors on lobster traps on a routine
basis since 2001. Each fisherman typically has one or two
probes deployed at a fixed location (fixed depth) that are
recovered on an annual basis to download the hourly time
series. The database of bottom temperature from over 100
locations has now grown to over three million records,
which allows investigation of temperature variability from
tidal to inter-annual time scales. Since shipboard protocol
often calls for randomly-selected station positions, bottom
temperature from fixed locations and depths is rare in the
historical record.
The primary objective of the eMOLT system, like many
ocean observing systems, is to provide numerical circulation
modellers the data they need to properly initialise, assimi-
late, and validate their simulations. Given the multiple-
scales of variability in both temperature and salinity, it is
increasingly clear that model runs need data to provide
realistic fields.3 While tremendous advancements have been
made in recent decades in Gulf of Maine circulation model
accuracy4,5,6,7 success is limited by the difficulty in properly
resolving the fine-scale baroclinicity of the density fields.
After a brief description of the eMOLT data and the
methods used to process the data, the patterns in the data
are described according to time scale. An analysis of the
inter-annual variability is followed by the tidal variability,
and finally the event-scale process of ‘turnovers’ is pre-
sented. In some cases, the GoMOOS data is used and com-
pared with the eMOLT data. Since much of the results are
presented in the way of examples and since it is often
necessary to focus an analysis in specific regions much
smaller than the entire Gulf of Maine, the Massachusetts
Bay area is chosen as a sub-region, although the same type
of analysis can be conducted throughout the study area.
While not the focus of the report, the biological impli-
cations of bottom temperature change are presented in the
discussion. The eMOLT project has also attempted to docu-
ment the relationship of lobster catch to both the absolute
temperatures and the variation of temperature over time. A
small portion of the eMOLT participants contributed to this
aspect of the study by providing catch data along with their
temperature records. While this aspect is not the focus here,
examples of the analysis are presented and discussed in
relation to other studies of a similar nature.8,9,10
DATA/METHODSWhile the protocol has evolved over the years since the
project inception, the general procedure is simple and now
involves the steps outlined in Table 1.
The primary sensors used in the study thus far are the
ONSET Tidbit and the VEMCO Minilog which both have
resolution and accuracy better than 0.28C. Depending on
the range of temperatures expected in some regions, some
probes are specifically engineered for smaller ranges and
can therefore resolve temperatures near 0.18C. In some
cases, the LOTEK LTD-1100 and SEABIRD Microcats
were used.
A few years into the eMOLT project, lobster catch data
was recorded by several of the participants on the Thistle
electronic log books but, after a year or two of successful
operation, the company that sold the unit dissolved. While
• The fishermen attach the sensor to the lobster trap for the entire duration of the fishing season
• The science party mails a self-addressed-stamped envelope to the fishermen near the end of the year asking for:
a) probes to be returned
b) documentation on any changes in mooring location/depth
c) catch for traps with probes attached (optional)
• The data is downloaded, cleaned, filtered (for occasional spikes associated with hauling), plotted, archived, and posted on the web
• Probes are immersed in a controlled ice-bath to check on biases and calibrations
• The science party reinitialises the temperature sensor at hourly sample rate and mails it back to participants along with hard copy plots of
the data.
Table 1: eMOLT Procedures
26 Journal of Operational Oceanography Volume 2 No. 1 2009
Environmental monitors on lobster traps (eMOLT)
there has been some effort by the scientific community to
continue the use of these loggers, most participants reverted
to hand-written logs. Since the data collection was con-
ducted on a voluntary basis, only a few dozen participants
provided catch records. Some documented in detail the
numbers of legals, shorts, and eggers, while others recorded
legals only. More than a thousand hauls have been recorded
to date and, while this phase of the eMOLT project is no
longer funded, several participants continue to submit their
catch records.
Each temperature time series is processed by truncating
the records for ‘in-water’ periods and subjecting the rest to
a range and delta check. The range and delta check criteria
varies depending on the region and a visual inspection of
the raw data. Beginning with a conservative test of all
temperatures between �6.6–26.78C and any changes of
0.88C/h, the tests are iteratively performed with a graphical
inspection at each stage until only those spikes likely asso-
ciated with hauling the instrument are removed. Plots of
raw, filtered, and daily averages are plotted for each record
and posted on the web. Processed data is served with Open-
Source Network Data Access Protocol Standards at http://
emolt.org.
The most important protocol that has been stressed
throughout the programme is maintaining fixed sites. Since
it is often impossible for lobstermen to land the traps on
exactly the same bottom with each haul, we expect ‘fixed’
sites are those which vary by ‘no more than one mile and,
most importantly, no more than 5% of the water column
depth’. Given the vertical stratification in many locations, it
is important to maintain this protocol. In some locations
such as the edge of the continental shelf, this is particularly
important. In most of these shelf edge locations, fishermen
are supplied with a pressure sensor along with the tempera-
ture sensor (VEMCO Minilog-TDR) so that a rough esti-
mate of water depth becomes part of the data stream at
these ‘fixed’ locations. These pressure sensors are accurate
enough to register changes greater than 5% of the water
column. Errors associated with trap movement to multiple
depths are addressed further in the discussion.
While each fisherman typically installs temperature
probes only on the trap at the bottom, several have also
attached a sensor 1m below the surface buoy as well. In
these cases therefore, a continuous record of thermal strati-
fication is available.
The organisation and outreach for the project is
provided by the various lobstermen associations in New
England. The four largest groups (Atlantic Offshore, Massa-
chusetts, Maine, and Downeast) have all had at least several
participants involved from the start of the project. They
provide updates and reminders to the participants via near-
monthly meetings, newsletters, and annual forums. An up-
date on the project is presented at all the annual forums. An
eMOLT newsletter is mailed to all participants a few times
per year with plots of the most interesting findings.
Temperature probes, administered by the eMOLT pro-
gramme, are now being deployed on a set of projects
around the Gulf of Maine including multiple ‘ventless trap’
programmes and a ‘lobster settlement’ programme. In both
cases, biological data is kept in a systematic way so that
correlations with temperature may be possible in the near
future. These parallel studies are conducted by both federal
and state agencies in the US and by the Fishermen and
Scientist Research Society (FSRS) in Canada. Beginning in
2006, several eMOLT probes have been deployed by Nova
Scotian fishermen. Temperature records from various pro-
jects are stored in the same database and served at http://
emolt.org.
RESULTSThe geographic distribution of eMOLT sites, presented in
Fig 1, covers the majority of the Northeast US Continental
Shelf but is limited to those areas where lobstermen fish.
Fig 2 depicts the distribution of eMOLT records as a func-
tion of water depth where approximately a third of the sites
are in depths of 90 fathoms (165m) or more with a large
portion near the 45 fathom (82m) depth. The distribution of
eMOLT temperature records over time is presented in Fig 3.
While the majority of sites have short records, over 100
sites span multiple years.
Interannual variability
Given several years of data from various depth zones off
the coast, it is now possible to quantify seasonal cycles and
calculate typical deviations. The range of temperatures ob-
served in 2006, for example, versus those observed through-
out the eMOLT record (2000-present) is presented in Fig 4.
The time series of the anomaly (seasonal cycle removed) is
depicted in Fig 5 for four distinct sites. For the first time,
we now have an objective measure of continuous bottom
temperature relative to other years in various depth zones.
A traditional shipboard observation in October of 2006
would have registered 2006 as being a normal year while
one in late November would register it as a very warm year.
We know from the continuous record, the anomaly changed
sign within a few weeks time. Extracting the monthly
Fig 1: Multi-year eMOLT bottom temperature mooring
locations
Volume 2 No. 1 2009 Journal of Operational Oceanography 27
Environmental monitors on lobster traps (eMOLT)
means, it is possible to look at a simple time series of the
interannual progression (Fig 5). It is still too early to claim
specific long term trends in the eMOLT records but we
have noted that 2002 and 2006 as being, in general, the
warm years.
Tidal variability
Hourly observations adequately resolve a semi-diurnal tide
in nearly all the eMOLT records. In a few cases, the ampli-
tude of the tidal signal is equal or greater than the seasonal
or wind-driven signals. In some locations, the sensors are
evidently placed in the vicinity of the seasonal thermocline.
Fig 6, for example, comes from Alex Brown who fishes the
inside of Cape Cod. Here the tidal oscillations can exceed
108C during the passage of a front and quickly drop to near
zero variance within the time scale of an upwelling/down-
welling cycle. The vertical stratification as observed by
Billy Anderson off Lubec Maine can vary as a function of
the lunar cycle by as much as a few degrees (Fig 7). Two
days subsequent to the timing of each full moon during the
summer of 2007, the increased tidal velocities were appar-
ently sufficient to mix the entire water column in that area.
Massachusetts Bay turnovers
Sensors at the bottom of Mass Bay for the last several years
have documented a dramatic turnover each fall. The records
from 2005 (Fig 8), for example, show the degree to which
the water column can mix a very stratified water column
the matter of a few days. A wind event that occurs in early
October 2005 was sustained from the north for multiple
days and was able to mix the entire bay to within a few
degrees C. Sensors in shallow water and near the surface
recorded cooling temperatures while the deeper sensors
recorded a warming event. In the case of fishermen in deep
waters, Dave Kandrick (DK) and Rob Martin (RM) for
example, the bottom temperature increased by nearly 58C
during the event. Those fishing in relatively shallower
waters closer to shore like Bill Doherty (BD), saw tempera-
Fig 2: Distribution of eMOLT sites relative to water depth
Fig 3: Distribution of eMOLT records over time
Fig 4: Example comparing 2006 (solid line) to long-term
mean (dashed) and min/max (gray) for the case of the 26
eMOLT sites off the coast of Central Maine in the depth
zone (0–20m)
28 Journal of Operational Oceanography Volume 2 No. 1 2009
Environmental monitors on lobster traps (eMOLT)
ture rise several degrees in the matter of one tidal period.
This difference indicates a downwelling scenario rather than
a direct wind mixing event. It is interesting to note that
these turnover events due to particular storms register at
many sites all along the coast. The effect of the storms is
often depicted at nearly all regions as shown, for example,
in the Fall of 2006 at multiple sites (Fig 9).
DISCUSSIONThere is a variety of limitations associated with collabora-
tive research with fishermen. As noted in the methods
section above, there is uncertainty in the mooring location
and depth. Since the trap movement often happens without
clear documentation, the temperature time series is often
affected and the scientific investigator is required to take
this uncertainty into account. With enough moorings in the
region of interest however these errors can be detected and
filtered from the dataset. In other words, since temperature
time series at nearby locations are often coherent, one can
determine artificial ‘events’ associated with trap movement
from real events associated with wind, tide, and river run-
off.
Another difficulty in working with New England fisher-
men is the fact that they typically work non-scientific units.
Their positions are most often reported in ‘Loran’, depth in
Fig 5: Four examples of
anomalous temperature
time series after having
removed the seasonal
cycle
Volume 2 No. 1 2009 Journal of Operational Oceanography 29
Environmental monitors on lobster traps (eMOLT)
‘fathoms’, time in ‘local’, and temperature in ‘Fahrenheit’.
The investigator needs to take care in properly converting
to more scientific standards but, at the same time, be
prepared to deliver the results back to the fishermen in their
terms. The majority of eMOLT graphical results therefore
are presented in the units requested by fishermen, the pri-
mary stakeholders.
While there is plenty of anecdotal information about the
affect of temperature on lobster catch, very little has been
quantified. Given multiple years of data, we can now begin
to investigate the relationship. In Fig 10, for example, it
appears that the seasonal catch curve is similar although
slightly lagging that of temperature. However, the tempera-
ture vs catch relationship evidently depends on the time
scale, the season, and the location. Where we find catch
still increasing with decreasing temperatures in the fall,
Drinkwater et al10 found the opposite in the spring. Their
results pertained to shallower waters far to the north of our
study area. When Worden et al8 used eMOLT data to
investigate the changes in haul-to-haul catch, no significant
relationship with temperature was found in this less-than-
seasonal time scale. The ventless-trap studies now have a
growing database of catch from several years. Given their
more-controlled data collection system, it is hoped that
these catch vs temperature relationships can be refined in
the near future. In the preliminary correlations of eMOLT
catch data with temperature, the relationship for legal-sized
adults vs that for ‘shorts’ and ‘eggers’ may be different.
The investigator needs to distinguish between the various
life stages.
While we have focused here on the first phase of
eMOLT project (temperature and, to a lesser degree, lobster
catch), it should be noted that the eMOLT project has
evolved to also include observations of salinity and cur-
rents. Several lobstermen have deployed Seabird Micro-
cats11 (Fig 11) and satellite-tracked drifters.12 In eMOLT
Phase VI, some are deploying a recently-developed bottom
current meter. As described at http://www.emolt.org, the
Fig 6: Example of tidal
and wind-driven
variability in Cape Cod
Bay over two-week
period
30 Journal of Operational Oceanography Volume 2 No. 1 2009
Environmental monitors on lobster traps (eMOLT)
project continues to evolve as new instrumentation is devel-
oped that will allow telemetered real-time observations by
satellite, radio, and cell phone. It is hoped that the eMOLT
concept can be incorporated into the regional coastal ocean
observing system both in the Northeast US (ie, NERA-
COOS) as well as other regions of the world. The primary
step in ‘integrating’ the eMOLT system with others in the
region, providing data via a distributed server, has already
been accomplished. As suggested by labs participating in
the Gulf of Maine Ocean Data Partnership, the eMOLT data
is served.
SUMMARYResults to-date demonstrate a variety of processes that were
previously difficult to document given the limited number
of moored and shipboard observations. Tidal variability, for
example, has been shown to be significant in many loca-
tions where the amplitude of the signal can be greater than
several degrees Celsius. The dramatic effect of winds and
the ‘turnover’ event that occurs each Fall in places like
Massachusetts Bay is better defined. Lobstermen can, for
the first time, say for certain just how warm or cold it is
relative to the previous years of observations. The years
2002 and 2006, for example, were documented as 2–38C
warmer than other years.
While a definite relationship between temperature and
lobster catch is still difficult to parameterise, records show
an obvious coherence in the seasonal cycle of both variables
with catch lagging the temperature in many cases. The
highest catches apparently occur days-to-weeks after the
water begins to cool in the Fall.
Dozens of New England lobstermen have been monitor-
ing bottom temperature on their lobster traps since 2001.
This dataset provides time series for investigating the ef-
fects of tides, wind, seasonal heating, and offshore influx in
a variety of locations ranging from the Hudson Shelf Valley
to the Nova Scotia. In the future, as the programme con-
Fig 7: Example of variability related to the lunar cycle
Fig 8: Example of wind-
induced ‘turnover’ in
Massachusetts Bay in
2005
Volume 2 No. 1 2009 Journal of Operational Oceanography 31
Environmental monitors on lobster traps (eMOLT)
tinues, it will provide a long-term record for documenting
decadal scale climate variability. Given the low-cost instru-
mentation and the interest and involvement of the fisher-
men, it is hoped that the programme will be sustained and
be merged into whatever observing system develops in the
Northeast US.
ACKNOWLEDGEMENTSThe authors thank the Northeast Consortium for several
years of collaborative research funding. They also appreci-
ate the help of Bonnie Spinazzola from the Atlantic Off-
shore Lobstermen Association, Jeremy Cates and Clare
Grindal from the Downeast Lobstermen Association, Patrice
McCarron from the Maine Lobstermen Association, and
Dave Casoni from the Massachusetts Lobstermen Associa-
tion for making eMOLT work, and, of course, the dozens of
New England lobstermen for providing their time, insight,
and effort.
REFERENCES1. Mountain DG and Jessen PF. 1987. Bottom waters of
the Gulf of Maine, 1978–1983, Jour. of Mar. Res., 45:319–
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2. Petrie B, Drinkwater K, Gregory D, Pettipas R and
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3. Pringle J. 2006. Sources of variability in Gulf of
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Fig 9: Example of coastwide effects of moving storm affecting
Massachusetts Bay to Eastern Nova Scotia. The Nova Scotian
sites are not shown in Fig 1 since they are not part of the
multi-year eMOLT set
Fig 10: Example time series of temperature and catch
Fig 11: Seabird Microcat mounted inside a lobster trap.
[Photo by Norbert Lemeiux, lobsterman from Cutler Maine]
32 Journal of Operational Oceanography Volume 2 No. 1 2009
Environmental monitors on lobster traps (eMOLT)
4. Lynch DR, Ip JTC, Naimie CE and Werner FE. 1996.
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Volume 2 No. 1 2009 Journal of Operational Oceanography 33
Environmental monitors on lobster traps (eMOLT)