Climate-induced Late-Holocene ecological changes in Pichavaram estuary, India
Transcript of Climate-induced Late-Holocene ecological changes in Pichavaram estuary, India
ORIGINAL ARTICLE
Climate-induced Late-Holocene ecological changes inPichavaram estuary, IndiaJyoti Srivastava1, Anjum Farooqui1 & Shaik M. Hussain2
1 Birbal Sahni Institute of Palaeobotany, Lucknow, India
2 A.C. College Campus, University of Madras, Chennai, India
Keywords
Climate; Late Holocene; Pichavaram; salinity;
thecamoebians.
Correspondence
Jyoti Srivastava, Birbal Sahni Institute of
Palaeobotany, 53 University Road, Lucknow
226007, U.P., India.
E-mail: [email protected]
Accepted: 11 December 2012
doi: 10.1111/maec.12048
Abstract
Variation in sedimentology as well as freshwater and marine palynomorphs has
been studied in ecological perspective in two 2.5- and 5-m deep sediment cores
deposited since 3440 and 3630 cal BP, respectively in the central part of Pich-
avaram mangrove wetland, Cauvery River delta. The palynological and sedi-
mentological results of the sediments reveal a monsoonal circulation and a
climatic shift from warm and humid with strengthened monsoon (3630–3190 cal BP) to dry and arid (~2750–760 cal BP). Since the last millennium
(~760 cal BP), Pichavaram estuary has been influenced by a similar cyclicity
but with a less wet and humid climate due to weakened monsoon conditions.
These ecological changes in turn affect the relative sea level rise and fall which
is reflected by the variability/extinction of freshwater and marine pal-
ynomorphs. The estuary remained an active water channel between ~3630 and
2750 cal BP, responding to the strengthened monsoon, during which the fresh-
water algal remains with thecamoebians and marine dinoflagellate cysts and
foraminiferal linings both dominated with a ratio of 1.5 for marine/freshwater
forms. After this period, since ~2750 cal BP there has been a dominance of
marine forms with a ratio of 4.5 for marine/freshwater forms, indicating fluvi-
o-marine sediment deposition and suggesting the recent landward intrusion of
seawater during weakened monsoon conditions. Freshwater thecamoebians are
vulnerable to the salinity >3 in the aqueous soil solution of estuarine sediment,
and therefore serve as an excellent proxy for monitoring salinity gradient along
with short-term high resolution palaeoecological fluctuations induced by
climate and relative sea-level changes in an estuarine ecosystem.
Introduction
Estuaries are subjected to frequent salinity changes
depending on the interplay of tidal influx and the fresh-
water input from land. This blending of marine and fresh
water ushers in a change in flora and fauna assemblage
composition and behaviour, suggesting that some agents
such as tidal amplitudes and fluvial discharge can be qual-
itatively monitored through biotic features in estuaries
(Bonetti & Eichler 1997). The river systems of east coast
of India are essentially monsoon-driven and as such the
sediments embedded in their deltas are considered excel-
lent repositories of past monsoon events to which the
biotic forms have responded. The composing organisms,
spores/pollen, thecamoebians, foraminifera and dinofla-
gellates are useful hydrodynamic bioindicators because
their microfaunal composition demonstrate environmen-
tal characteristics such as sedimentological features, cli-
mate and ecological changes (Ellison 1995; Patterson &
Kumar 2002; Lahr et al. 2006). Those studies have been
focused on higher latitudes, whereas few records are from
the tropical zone (Roe & Patterson 2006). There are
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Marine Ecology. ISSN 0173-9565
records of intermittent relative sea-level rise and fall dur-
ing Late Holocene from Pulicat lagoon and other contem-
porary sites along the east coast (Bannerjee 2000;
Farooqui & Vaz 2000).
Stratigraphic changes in the palynological assemblages
in sediments responding to ecological changes during
Late Holocene induced by external factors such as relative
sea level and climate have been studied from Pichavaram
wetland. Palynomorphs such as the freshwater algal mat-
ter, fungal remains, dinoflagellate cysts, thecamoebians,
foraminifera and loricated tintinid remains are often
completely overlooked while studying the palynological
assemblages retrieved from the Quaternary sediments of
India. Nevertheless, the paucity of spores and pollen
grains in sediments make it necessary to look for alterna-
tive forms for interpretation of palaeoenvironmental con-
ditions. Thus such biotic forms constitute an important
component of the palynological data for palaeoecologial
information. Based on the respective occurrence of terres-
trial and marine palynomorphs, it is possible to assess the
freshwater or marine character of sediments, and thus to
reconstruct climatic changes in the past along with the
relative sea level. In the present study, a combination of
freshwater algal matter, fungal remains, dinoflagellate
cyst, thecamoebian, foraminifera and loricated tintinid
assemblages and abiotic parameters such as sediment tex-
ture and salinity were examined for sediment cores col-
lected from a swampy region and from an exposed land
section of the Pichavaram estuary to identify a deposi-
tional zonation representing hydrodynamic and ecological
patterns that could be applicable to paleoenvironmental
analysis in the Southeast coast of India.
Study area
The Pichavaram mangrove ecosystem (latitude 11º25′ Nand longitude 79º47′ E) is a shallow estuarine complex
sandwiched between two prominent estuaries, Vellar estu-
ary in the north and Coleroon estuary in the south, with a
total area of 1100 ha. The complex has 15 islets ranging in
size from 10 m2 to 2 km2 separated by intricate waterways,
which connect the Vellar estuary in the north and the
Coleroon estuary in the south (Ramanathan 1997). The
Coleroon estuary part is largely dominated by mangroves,
whereas the Vellar estuary is dominated by mud-flats.
Tidal water enters the Pichavaram mangrove through a
small direct connection with the Bay of Bengal at Chinna-
vaikal and estuarine water finds its way through the two
adjacent river systems (Fig. 1). Site P2 is located in the
central part of Pichavaram estuary and is mainly inhabited
by Avicennia officinalis, Avicennia marina and Suaeda sp.,
with fringes of Rhizophora sp. along the backwater channel.
Site T2 is towards the south of Pichavaram close to the
village TS Pettai and is dominated by salt-tolerant Suaeda
sp. with A. marina and A. officinalis occupying the land-
ward zones.
Material and Methods
Two sediment cores, P2 and T2, measuring 2.5 and 5 m
depth, respectively, were obtained using a hand-operated
augur cum piston corer (Eijelkamp, the Netherlands).
Immediately after collection, P2 and T2 cores were sub-
sampled at 2- and 5-cm intervals, respectively. The samples
were stored in air-tight polythene bags without any preser-
vative. In the laboratory, sediment colour was identified
using a Munsell colour chart (Munsell and Farnum, 2004)
and texture was analysed on the basis of the percentage of
sand in the sediment according to the soil density method
(USDA 1992). Salinity was measured in 10 g of an air-
dried soil sample dissolved in 100 ml of deionized water.
Prior to measuring salinity, the aqueous soil solution was
kept overnight after rigorous shaking for an hour. The
samples were homogenized for 30 min before measuring
the salinity using Orion-5 star (Thermo-Orion, Scientific
Equipment, USA) at standardized 25 °C temperature.
For the palynological and thecamoebian study, 10 g of
an air-dried soil sample was treated with 10% potassium
hydroxide (KOH) on a sand bath for 5 min and sieved
through 150-mesh. The filtrate was then acetolysed fol-
lowing Erdtman (1943). The samples were then passed
through 600-mesh and the residue (>10 lm) was col-
lected for palynological slides referring to standard litera-
ture (Ogden & Hedley 1980; Patterson & Kumar 2002).
The palynological spectra represent the percentage of total
300 counts of macrophyte pollen, freshwater algal spores,
fungal remains, thecamoebians, foraminifera and dinofla-
gellate cysts in homogenized 10 ml acetolysed sample.
The ratio of marine and freshwater forms was calculated
to determine the variability in these marine/freshwater
indicators during climatic fluctuations.
Results
Radiocarbon dates and age-depth models
The age of the oldest sediment in core P2 (�250 cm) is
3440 cal BP, at �138 cm the age of the sediment is
2430 cal BP, and at �65 cm the sediment is 590 cal BP
old. Similarly, the age of the oldest sediment in core T2
(�500 cm) is 3630 cal BP, at �85 cm the sediment is
2750 cal BP, and at �25 cm the sediment dates back to
760 cal BP. Plots of these calibrated dates against depth
are presented for both the sites with age-depth models
proposed to provide means for estimating sample ages
and sedimentation rates (SR) for the sequences.
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Srivastava, Farooqui & Hussain Ecological changes in Pichavaram estuary, India
The gradient of segments of the age-model for core P2
is shown in Fig. 2A. The lowermost segment (P2s-1a)
contains two dates with the deposition of heterogeneous
sediment. Estimated SR for the initial phase of infilling
prior to 2430 cal BP is higher (0.11 cm�year�1). After c.
2430 cal BP, estimated SR decreases to 0.03 cm�year�1
(P2s-1b), and again rises to 0.11 cm�year�1 for the per-
iod from c. 590 cal BP until present (P2s-2). As the
radiocarbon ages fall some distance from the sediment
zone boundaries, changes in SR occurring at zone
boundaries cannot be determined. However, the broad
contrast in SR is demonstrated between sediment zones
P2s-1a and P2s-2 (high average SR) and P2s-1b (reduced
SR).
As with core T2, estimated SR for the first phase of
infilling prior to c. 2750 cal BP is high (0.47 cm�year�1).
For the period between c. 2750 and 760 cal BP, esti-
mated SR falls to 0.03 cm�year�1. After 760 cal BP, esti-
mated SR remains reduced, suggesting long-term average
SR until present, around 0.03 cm�year�1. Lithostrati-
graphical zones are plotted next to the age model
(Fig. 2B). Zones T2s-1 and T2s-2 are characterized by
overall high average SR of around 0.5 cm�year�1. How-
ever, given that changes in lithological characteristics are
likely to be allied with the changes in deposition time,
sedimentation rates across the heterogeneous zones are
unlikely to have been uniform. Rather, sedimentation is
likely to have been episodic, alternating between periods
of comparatively slow accumulation of clay sediments
and rapid to instantaneous deposition of sands. Never-
theless, the total deposition time for T2s-1 and T2s-2
overall appears to have been short, on the order of
800 years.
Fig. 1. Map showing the study area in Pichavaram Mangrove (India).
The core locations are in the estuarine part of the study area from
the backwater channel. P2 is named for Pichavaram estuary as it is
retrieved from the central part of the estuary. Core T2 is named for
Tspettai because it is close to the village Tspettai towards the South
of Pichavaram.
A
B
Fig. 2. (A) Age-depth model, P2, based on linear interpolation. Solid
dots show the median calibrated ages. (B) Age-depth model, T2,
based on linear interpolation. Solid dots show the median calibrated
ages.
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Ecological changes in Pichavaram estuary, India Srivastava, Farooqui & Hussain
Sedimentology and salinity
Core P2
The following lithological zones are distinguished from
base to the top:
P2s-1a: 250–120 cm: This zone contains predominantly
fine-grained sandy clay sediments with intermittent bands
of sand (5Y4/2). The zone shows a heterogeneous
sediment composition with medium to fine sandy layers
interspersed in a sandy clay composition which is pre-
dominantly fine-grained with a greater proportion of silt/
clay and fine sand.
P2s-1b: 120–85 cm: This zone contains sediment domi-
nated by sand (5Y4/2) with a relatively low percentage of
finer fractions of the sediment (silt and clay).
P2s-2: 85–0 cm: The uppermost zone is a clay-rich soil
(5Y2/2) with a homogeneous composition.
Salinity (P2): Values for salinity gradient are presented in
Fig. 3. Zone P2s-1a constitutes fine sand and clay with a
dominance of clay showing higher salinity with an aver-
age of 3.0 maximum going up to 4.4 in the intermittent
clayey layer and a minimum of 1.9. The values of salinity
in zone P2s-1b comprised sand as the main fraction with
an average salinity of 2.2 with a maximum of 2.4 and a
minimum of 2.1. Zone P2s-2 was dominated by fine clay
sediment fractions as compared with the other zones and
shows an average salinity of 4.0 with a maximum of 5.4–4.3 and a minimum of 2.1–3.6.
Core T2
The following lithological zones are distinguished from
base to the top:
T2s-1: 500–215 cm: Basal deposits of T2 sedimentary fill
are composed of sandy sediment (5Y4/2) with intermit-
tent bands of clay (5Y4/2). The zone shows a heteroge-
neous sediment composition with medium to find sand
Fig. 3. Diagram showing the radiocarbon dates, textural composition, salinity gradient for cores P2 and T2 from Pichavaram, India. The
lithostratigraphical zones are delimited on the basis of results of sediment analysis. The zones are prefixed with the site code and the letter’s’ to
distinguish them from independent biostratigraphical zones defined on the basis palynomorph data.
Marine Ecology 34 (2013) 474–483 ª 2013 Blackwell Verlag GmbH 477
Srivastava, Farooqui & Hussain Ecological changes in Pichavaram estuary, India
A
B
Fig. 4. (A) Palynological diagram showing the percentage count of the most frequent freshwater and marine forms and the total marine/
freshwater ratio calculated for Core P2 of Pichavaram Estuary, India This figure also includes three radiocarbon dates. (B) Palynological diagram
showing the percentage count of the most frequent freshwater and marine forms and the total marin/freshwater ratio calculated for Core T2 of
Pichavaram Estuary, India This figure also includes three radiocarbon dates.
478 Marine Ecology 34 (2013) 474–483 ª 2013 Blackwell Verlag GmbH
Ecological changes in Pichavaram estuary, India Srivastava, Farooqui & Hussain
interspersed by thin to broad bands of fine grained
clay.
T2s-2: 215–0 cm: Zone T2s-2 contains predominantly fine-
grained compact clay (5Y3/2) sediment overlying the
fluctuating sand zone. A thin band of sand and clay is
noted at 20 cm from the surface.
Salinity (T2): Values for the salinity gradient are presented
in Fig. 3. The topmost zone T2s-2 constituting fine clay
sediment fractions shows the highest salinity status with
an average of 3.6, a maximum value going up to 10.4
and a minimum of 1.9. The values of salinity in zone
T2s-2 constituting fine sand with intermittent clay bands
show intermediate salinity with an average of 1.8, maxi-
mum going up to 4.2 in the intermittent clayey layer and
a minimum of 0.8.
Palynomorph assemblage
On the basis of palynomorph succession, four climatic
phases are identified.
Core P2
Phase P2-I (250–200 cm): Macrophytes – freshwater algal
remains – thecamoebian assemblage – dinoflagellate cyst –
foraminiferal linings: Signatures of both freshwater and
marine forms mark this phase constituting freshwater
algae Botryococcus, Coelastrum, Pediastrum boryanum,
Pediastrum simplex, macrophytes such as Eichhornia and
Typha, thecamoebians such as Cyclopyxis, Nebela and
Arcella along with marine dinoflagellate cysts such as Spi-
niferites and Operculodinium, Scolecodont and brackish
water foraminiferal chitinous linings of Ammonia and
Cornuspira (Plate 1). The marine/freshwater forms ratio
for the present phase is calculated as 1.3 with an overall
abundance of both groups of palynomorphs (Fig. 4A).
Phase P2-II (200–75 cm): Freshwater algal remains –
thecamoebian assemblage – dinoflagellate cyst – foraminiferal
linings: This phase is characterized by overall reduced val-
ues for freshwater algae such as Pediastrum boryanum
and Pediastrum simplex and a relatively good percentage
of thecamoebians such as Arcella, Cyclopyxis and Nebela,
along with the abundance of marine forms such as dino-
flagellate cysts, and foraminiferal linings such as Ammo-
nia and Cornuspira. The ratio of marine and freshwater
form curve shows high to low peaks throughout the
phase, with an average ratio of 2.3 due to higher pro-
portion of foraminiferal linings, with Cornuspira and
dinoflagellate cysts in the uppermost section of the
phase.
Phase P2-III (75–25 cm): Marine foraminiferal linings: Phase
P2-III shows the dominance of marine forms with mainly
foraminiferal linings of Ammonia and Cornuspira along
with Scolecodont fragments with a reduction in the fresh-
water thecamoebians Cyclopyxis, Arcella and Nebela. The
ratio of marine and freshwater forms towards the marine
side also goes up to 7.0, increasing the prominence of
these forms.
Phase P2-IV (25–0 cm): Thecamoebian – marine foraminiferal
linings – dinoflagellate cyst: A low abundance of freshwater
algae Pediastrum boryanum and thecamoebians such as
Cyclopyxis and Nebela along with a good percentage of chi-
tinous linings of Ammonia and dinoflagellate cyst has been
recorded. The ratio of marine/freshwater forms is calculated
as 3.5, showing the abundance of marine indicators along
with a lower proportion of freshwater forms.
Core T2
Phase T2-I (500–280 cm): Macrophytes – freshwater algae –
thecamoebians – marine dinoflagellate cysts – foraminiferal
linings: The presence of macrophyte Typha, the abundance
of freshwater algae such as Botryococcus, Pediastrum borya-
num and Pediastrum simplex, and the dominance of thec-
amoebians such as Cyclopyxis and Arcella along with a
relatively low percentage of marine dinoflagellate cysts and
a good percentage of foraminiferal lining of Ammonia is
marked in this phase. Fungal spores, VAM fungi and Tet-
raploa are also well represented. The ratio of marine and
freshwater indicators comes out to 1.1, with an equal pro-
portion of both marine and freshwater forms (Fig. 4B).
Phase T2-II (280–100 cm): Macrophytes – freshwater taxa –
thecamoebians – marine dinoflagellate cysts – foraminiferal
lining assemblage: Phase T2-II is characterized by the pres-
ence of macrophytes such as Eichhornia, Typha and algae
such as Pediastrum boryanum, Pediastrum simplex and a
dominance of thecamoebians such as Arcella, Cyclopyxis
and Nebela along with the presence of dinoflagellate cysts
such as Spiniferites, Operculodinium and foraminiferal lin-
ings such as Ammonia. The ratio of marine/freshwater is
1.6, indicating a slightly higher abundance of marine
forms.
Phase T2-III (100–30 cm): Thecamoebians – marine
foraminiferal linings: Phase T2-III displays evidence of
dinoflagellate cysts, Spiniferites and Operculodinium and
foraminiferal linings such as Ammonia along with Scolec-
odont fragments, with a decline in thecamoebians such as
Cyclopyxis and Arcella. The marine/freshwater forms is
calculated as 5.4, indicating the prominence of marine
forms.
Marine Ecology 34 (2013) 474–483 ª 2013 Blackwell Verlag GmbH 479
Srivastava, Farooqui & Hussain Ecological changes in Pichavaram estuary, India
Plate 1. 1.Typha; 2. Myriophyllum; 3. Nebela; 4. Cyclopyxis intermedia; 5. Botryococcus; 6, 7. Pediastrum boryanum; 8. Pediastrum simplex; 9,
13. Centropyxis aculeata; 10. Arcella spp.; 11, 14. Arcella artocrea; 12.Centropyxis corona; 15. Cornuspira; 16, 17. Foraminiferal linings; 18, 19.
Spiniferites; 20. Operculodinium; 21, 22. Tintinid lorica remains.
480 Marine Ecology 34 (2013) 474–483 ª 2013 Blackwell Verlag GmbH
Ecological changes in Pichavaram estuary, India Srivastava, Farooqui & Hussain
Phase T2-IV (30–0 cm): Thecamoebian – marine foraminiferal
linings – dinoflagellate cysts: A relatively low percentage of
the freshwater palynomorphs compared with Phase T2-I
such as Pediastrum boryanum and thecamoebians such as
Cyclopyxis, Nebela and Arcella in the surface and sub-
surface sediment has been encountered. On the other
hand, an abundance of estuarine to marginal marine
palynomorphs such as dinoflagellate cysts, foraminiferal
linings such as Ammonia, Scolecodont fragments and
Tintinids has been recorded. The ratio of marine and
freshwater forms goes down to 2.3 due to an overall
dominance of marine forms with a low abundance of
freshwater indicators.
Discussion
Sediment analysis along with palynology has been under-
taken in the present study with a view to the character-
ization of the hydrodynamic environment of deposition.
The interpretation of textural data was only possible
within the framework of a general understanding of nat-
ure of sedimentation in the estuarine environment. Sedi-
ment transport within an estuary depends on several
factors, including river discharge, tidal circulation pat-
terns and salinity (Dyer 1979). Salt in the soil is best
washed away by freshwater but clay and silt are relatively
impermeable, hence the filtration process called leaching
is slow. In some relatively dry zones, salt already accumu-
lates on the surface and becomes crystallized. As a result
the salinity problems may persist for a long period unless
checked and measures are taken to remove the salts by
flushing or leaching (Sparks 1995). Palynomorph data for
freshwater algal forms, thecamoebians, foraminiferal lin-
ings and dinoflagellates also support important observa-
tions for the interpretation of hydrological condition of
the estuary. The dinoflagellates observed in the sample
suggest at least some tidal influence during the period of
infilling (Jennings et al. 1993). However, it is recognized
that biological indicators of brackish or marine condi-
tions may occur well upstream of sedimentary tidal influ-
ence, relating to periods of reduced river discharge (Frey
& Howard 1986). Pediastrum is considered an indicator
of freshwater conditions (Round 1965). The freshwater
protozoans that form agglutinated or autogenous tests are
the thecamoebians. They are also called Arcellaceans
because their tests resist dissolution in low pH environ-
ments, unlike those of other freshwater organisms such as
molluscs and ostracods (McCarthy et al. 1995; Dalby
et al. 2000). The mechanism of encystment enables these
organisms to populate dry areas and remain dormant
until water brings them back to active life. They are read-
ily transported over a long distance by a variety of agents.
Hence, they are found in freshwater to slightly brackish
environments, including freshwater lakes, estuarine envi-
ronment, salt and freshwater marshes, soil peat, moss
under tree bark, ponds and standing water (Medioli &
Scott 1983; Patterson et al. 1985). Foraminiferal linings
generally categorize hypo-saline lagoons and estuaries,
which may also be found in intertidal and shallow water
in coastal areas. Their frequent occurrence in palynologi-
cal preparations suggests an exclusively marine condition.
The radiocarbon data, sedimentological and palynolog-
ical records from the present study reveal four climatic
and ecological phases in Pichavaram estuary since Late
Holocene. First, a stabilized estuarine ecosystem as Phase
I (~3630–3190 cal BP), showing mixed conditions in the
water column with a relatively high fluvial energy due to
more freshwater input to the estuary, indicating strength-
ened monsoon conditions as evidenced by a higher sedi-
mentation rate, heterogeneous sediment composition, and
the presence of both freshwater (macrophyte, algae, thec-
amoebians) and marine forms (foraminifera and dinofla-
gellates). The freshwater and marine forms encountered
in this study include macrophyte pollen such as Typha
and Eichhornia, freshwater algal remains such as Botryo-
coccus and Pediastrum, freshwater thecamoebians such as
Cyclopyxis and Arcella, which reveal a lacustrine environ-
ment and are indicators of hydrological changes (fresh
water input). In contrast, dinoflagellate cysts (Spiniferites
and Operculodinium) and foraminiferal linings such as
Ammonia and Cornuspira in sediment indicate an estua-
rine to marginal marine depositional environment and
are an excellent marker for marine incursion during
lower hydrological input. There are also records of maxi-
mum winter precipitation in Northwestern India during
the Indus Culture period of 5000–3500 years BP (Singh
et al. 1974; Vishnu-Mittre & Sharma 1975).
In Phase II, an unstable depositional environment is
evident from the heterogeneous sediment constituting
medium to fine sand embedded with occasional bands of
fine sticky clay, perhaps due to occasional high tidal
influx and freshwater input from land during the
strengthened monsoon conditions in the early part of
Late Holocene (~3190 years BP). Variation in the salinity
gradient for Phase I and II also reflects this heterogeneous
sediment composition, showing finer clay particles with
greater affinity for salts in comparison with their coarser
counterparts. The clay particles are flexible and plastic
because of their lattice-like design and have a large sur-
face area which is chemically reactive, attracting and
holding positively charged nutrient ions (Hiller 2003).
Wide fluctuations in the dominance of freshwater thec-
amoebians, mainly Cyclopyxis and marine forms such as
dinoflagellate cysts and foraminiferal linings, along with
the salinity suggest climatic amelioration from warm and
humid to dry and arid (3190–2430 years BP). Records
Marine Ecology 34 (2013) 474–483 ª 2013 Blackwell Verlag GmbH 481
Srivastava, Farooqui & Hussain Ecological changes in Pichavaram estuary, India
using mixed proxies from Asia and Africa show a severe
and lasting drought during Middle-Late Holocene
(Kaniewski et al. 2008). A steady weakening of the Asian
summer monsoon between 3700 cal years BP and
1500 cal years BP has been reported from low and middle
latitudes in India and China (Selvaraj et al. 2008; Liu
et al. 2009), and is generally understood to be a response
to decreasing summer insolation (Overpeck et al. 1996).
The dominance of marine forms such as foraminif-
era and dinoflagellates with a decline in freshwater
thecamoebians in Phase III (2430–760 years BP) indicates
marine incursion with low freshwater input from land,
supporting a dry and arid climate due to weakened mon-
soon conditions. Low salinity recorded in the present
phase suggests deposition of a coarser sediment fraction
with a high proportion of sand with larger inter-particle
pore sizes causing vertical translocation of salts to deeper
layers. The study of lacustrine sediments of Southwestern
Ghats, India, also explains the reduction in rainfall and
arid climatic conditions in the beginning of Late
Holocene which slowly ameliorated to warm and humid
conditions until 780 years BP (Bera & Farooqui 2000).
The climate in Phase IV (since ~760 years BP) was less
warm and humid than Phase I due to weakened mon-
soons and comparatively stable low energy intertidal estu-
arine setting, favouring the deposition of fine grain
sediment and leading to an increase in salinity. In the
beginning of the last millennium (Phase IV) the climate
ameliorated from dry and arid to warm and humid but
with weakened monsoon conditions, which is evidenced
by a moderate percentage of freshwater thecamoebians
along with the estuarine to marginal marine pal-
ynomorphs such as dinoflagellate cysts of Spiniferites and
foraminiferal linings of Ammonia. This indicates a lower
hydrological input during the recent decades leading to
the deposition of fine grained clay sediment with higher
accumulation of salts. The precipitation of salt through
capillary action during dry months in exposed land is
common in the coastal wetlands (Farooqui 2010). These
changes drastically affected the diversity and dominance
of freshwater thecamoebians, which serve as a suitable
proxy for monitoring the magnitude of salinity fluctua-
tions in the river mouth.
Conclusion
On the basis of proxy records, two major phases of cli-
mate and ecological changes are inferred. The ratio of
marine and freshwater forms is low between the third
and second millennia (Phase I), as indicated by a high
percentage of thecamoebian and algal forms, which
suggests strengthened monsoon conditions. A higher
ratio of marine and freshwater forms since the last
millennium (Phase II) indicates seawater incursion due
to low freshwater input from land as evidenced by a
decline in freshwater thecamoebians, which reveals weak-
ened monsoon conditions. The freshwater thecamoebians
serve as an excellent proxy for monitoring salinity gradi-
ent in coastal wetlands. The recent changes in the
strength of freshwater flux leading to landward intrusion
of seawater could be attributed to the geomorphological
and hydrological changes in the estuary influenced by
climatic deterioration.
Acknowledgements
The authors are grateful to Director BSIP for granting
permission and providing necessary facilities to accom-
plish this work. J.S. thanks the Department of Science
and Technology, New Delhi for providing financial
support as Junior Research Fellowship in a DST spon-
sored Project No. SR/S4/ES-264/2007.
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