ARTICLE IN PRESS
Quaternary Science Reviews 25 (2006) 1110–1126
Millenial-scale climatic and vegetation changes in a northern Cerrado
(Northeast, Brazil) since the Last Glacial Maximum
Marie-Pierre Ledrua,, Gregorio Ceccantinib, Susy E.M. Gouveiac, José Antonio López-Sáezd,
Luiz C.R. Pessendac, Adauto S. Ribeiroc
a
CNPq/IRD, Universidade de São Paulo, Dpto de Geociências/UR 55, rua do Lago 562, 06708-900 São Paulo, SP, Brazil
b
Universidade de São Paulo, Departamento de Botanica, rua do Matão, São Paulo, SP, Brazil
c
Centro Energia Nuclear A Universidade de São Paulo, Piracicaba, SP, Brazil
d
Laboratorio de Arqueobotánica, Departamento de Prehistoria, Instituto de Historia, CSIC, Duque de Medinaceli 6, 28014 Madrid, Spain
Received 21 June 2004; accepted 13 October 2005
Abstract
In the Southern Hemisphere, lacustrine sediments started to be deposited with the beginning of the deglaciation at ca 19,000 cal yr BP.
At this time the region of Lake Cac- o was dominated by sparse and shrubby vegetation with dominance of steppic grasses in a poor sandy
soil. The landscape did not present any ecological characteristics of a modern Cerrado. However single pollen grains of two Cerrado
indicators, Byrsonima and Mimosa, suggest that some Cerrado species were able to survive under the prevailing arid climate, probably as
small shrubs. After 15,500 cal yr BP, a sudden increase in the moisture rates is evidenced with the progressive expansion of rainforest
showing successive dominance of various associations of taxa. The development of the forest stopped abruptly at the end of the
Pleistocene between 12,800 and 11,000 cal yr BP, as attested by strong fires and the expansion of Poaceae. In the early Holocene an open
landscape with a relatively high level of water in the lake preceded the progressive expansion of Cerrado species towards a denser forested
landscape; fires are recorded from then on, resulting in the physiognomy of the Cerrado we know today. Late Pleistocene
paleoenvironmental records from northern Brazil reflect the interplay between insolation forcing of two hemispheres with the local
components represented by the interannual shift of the Inter Tropical Convergence Zone and the influence of seasonal equatorwards
polar air incursions.
r 2005 Elsevier Ltd. All rights reserved.
1. Introduction
Recently published data from Northeastern Brazil
(Nordeste) show strong teleconnections between atmospheric and oceanic circulation that enable us to distinguish two different climatic areas (Jennerjahn et al., 2004;
Ledru et al., 2002; Wang et al., 2004). The first concerns the
eastern coastal area which is subject to a winter rainy
season created by the trajectory of the cold Benguela
Current southward along the Brazilian coast; the second
concerns the inland and northern part of the Nordeste
which is subject to the Inter Tropical Convergence Zone
Corresponding author. Present address. IRD-UR 32, MSE, BP 64501,
34394 Montpellier, France and ISEM-Paléoenvironnements, CC 61, 34095
Montpellier, Cedex 5, France. Tel.: +33 4 67 14 90 32; fax: +33 4 67 14 90 71.
E-mail address: ledru@msem.univ-montp2.fr (M.-P. Ledru).
0277-3791/$ - see front matter r 2005 Elsevier Ltd. All rights reserved.
doi:10.1016/j.quascirev.2005.10.005
(ITCZ) seasonal shift and a summer rainy season (Fig. 1A
and B). Marine (Jennerjahn et al., 2004), lacustrine (Ledru
et al., 2002) and speleothem (Wang et al., 2004) data
highlight differences, often out of phase, in signal expression depending on the location of the records. For instance
a dry Younger Dryas (YD) climatic reversal is observed in
north and inland Nordeste while a wet YD event is
observed on the coast. This observation infers marked
changes in seasonality during this climatic reversal with
differences in signal expression depending on the location
of the study area within the Nordeste region. Seasonal
changes greatly influence the floristic composition of the
tropical forest and also play a role in the dynamics and
evolution of tropical biodiversity. This is why it is
important to characterize the biome we are currently
studying and to define the way it responded to climatic
changes over time.
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M.-P. Ledru et al. / Quaternary Science Reviews 25 (2006) 1110–1126
precipitation mm
500
400
300
200
100
0
jan feb mar apr may jun jul aug sep oct nov dec
27.5
27
26.5
26
25.5
25
24.5
24
23.5
23
temperature °C
São Luis de Maranhão (2,31°S, 44,16°W, 120m a.s.l.)
(A)
(B)
GeoB
Lagoa Caçó
SA
CZ
0°
ITCZ
Tr
20°S
PA
summer DJF
ITCZ
GeoB
0°
Lagoa Caçó
BC
Tr
20°S
PA
winter JAS
Fig. 1. (A) Climatic diagram of the city of São Luiz (21310 S, 441160 W) the
capital of Maranhão State. (B) Map of South America showing the
respective austral winter and summer position of the Inter Tropical
Convergence Zone and the South Atlantic Convergence Zone. Arrows
indicate the trajectories of polar air advections. BC, Benguela Curren; PA,
polar advection; Tr, travertines from Wang et al. (2004), GeoB marine
core from Jennerjahn et al. (2004).
The State of Maranhão in the Nordeste represents the
northern Cerrado area within the six phytogeographic
zones defined by Ratter (Ratter et al., 1996) and also the
northern climatic region that is subject to a climate with
summer rainfall and changes in the amplitude of ITCZ
seasonal shifts. After Amazonia, the Cerrado represents the
second largest biome in Brazil. It is composed of several
mosaics of vegetation that are rich in endemic species. The
surface area originally covered by Cerrado is estimated at 2
million km2, or 22% of the Brazilian territory (OliveiraFilho and Ratter, 2002). The floristic composition of a
given area of Cerrado depends to a large extent on the
1111
main neighboring ecosystem (Ratter et al., 1996; OliveiraFilho and Ratter, 2002).
From rapid botanical inventories consisting in collecting
different species in a delimited area for a period of no more
than 30 mn, these authors were able to define six
phytogeographical zones for the Cerrado biome: south,
southeast, central, centerwest north and some patches of
Cerrado inside the Amazonian rainforest. The mean
annual precipitation, the length of the dry season and the
mean winter temperature appear to be the main factors
that separate these areas. The vegetation is extremely
heterogenous as none of the 534 species identified was
observed in all 96 study sites, and only 28 species were
found at 50% or more of the sites. The Cerrado also has
the highest variety of fruits in South America with regular
production throughout the year. Archeological studies
showed that during the last 12,000 yr BP, the populations
of the central region of the Cerrado were subject to changes
in their environment and consequently had to look for
different kinds of food to survive.
Four different prehistoric periods are evidenced in the
caves of Serranopolis, State of Goias (Schmitz et al., 1989).
The first or Paranaı́ba period, is related to the Itaparica
tradition and dated between 11,000 and 8000 yr BP. Food
remains attest to hunting of different types of animals such
as capivaras, turtles, and fish from the surrounding rivers.
Bones artifacts were mainly made from cervides. The
environment was drier than today. During the second or
Serranópolis period, the populations hunted and collected
snails. This period dated between 8000 and 5500 yr BP and
shows an increase in moisture rates. At the end of the
Serranópolis period a sterile layer with no archeological
content is observed. The third or Jataı́ period related to the
Una tradition starts with layers covering eroded depositions. These layers contain remains of cultivated plants
such as corn, peanut, various legumes and fruits from the
Cerrado and riparian forest, as well as remains from
hunting and snails. The Una tradition extended from the
central Plateau to Rio de Janeiro at 2000 yr BP. The
Tupiguarani tradition is evidenced in the surface layers of
the caves and disappeared with European settlement.
Pollen records from the central region also highlight an
extremely arid event at mid-Holocene (Salgado-Labouriau
et al., 1998). Here we present results obtained from the
examination of lacustrine sediments, botanical surveys and
soil isotopic analyses undertaken to characterize the
evolution of this biome during the Late Quaternary. We
compared our records with records in other Cerrado areas
to discover how this biome responded to major climatic
changes at different latitudes, and how the floristic
composition of a biome can differ from one region to
another depending on local climate changes.
2. Modern settings
Lake Cac- ó is an extended lake 3 km long and 0.5 km
wide that occupies a small closed basin covering an area of
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98-5
LCF150
LCF50
98-4
97-1
LCF200
coring site
Brazil
soil profile
river
1 km
South
Atlantic
Fig. 2. Distribution of the biome Cerrado (in gray) and location of Lake
Cac- o in Brazil. Map of the lake with location of the cores MA 97-1, MA
98-4 and MA 98-5 and of the soil profiles LCF 50, 150 and 200.
about 15 km2 (Fig. 2). The modern-day vegetation in this
area is diverse, from Restinga, the steppe vegetation typical
of the coastal regions of Brazil, to Cerrado, consisting of
woody savanna containing species from the Restinga
growing on eolian sand, and finally gallery (riparian)
forests containing Amazonian rainforest species. Botanical
inventories were undertaken in all the different ecosystems
from the lake to the coast covering a distance of ca 100 km
in November 1998, at the end of the dry season, and in
April 1999, at the end of the rainy season (Fig. 1). Material
is available at the Herbarium of the Botanical Department
of the University Federal of Paraná, in the city of Curitiba,
Brazil. These inventories include the following species: (1)
in the lake, the predominant aquatic species are Nymphaea
sp., Nymphoides sp., Sagittaria, Cabomba and Montrichardia linifera. (2) The lake margins are occupied by
herbaceous plants: Cyperaceae (Eleocharis sp.), Orchidaceae, and Eriocaulaceae, Mauritia flexuosa, a palm that
forms large mixed colonies with Xylopia (Annonaceae) in
seasonally flooded marshland, and trees from the gallery
forest Melastomataceae, Tapirira guianensis (Anacardiaceae), Vochysia tucanorum (Vochysiaceae), Cordia nodosa
(Boraginaceae), Casearia spp. (Flacourtiaceae), Ficus spp.
(Moraceae) and Picramnia spp. (Simaroubaceae). (3) The
Cerrado profiles vary with the density of the trees and
include Stryphnodendron adstringens (Mimosaceae), Parkia
pendula (Mimosaceae), Qualea grandiflora (Vochysiaceae),
and Curatella americana (Dilleniaceae). (4) The coastal
vegetation (Restinga) is observed on the dunes and includes
small trees and shrubs (e.g., Byrsonima spp. (Malpighiaceae), Copaifera spp. (Caesalpiniaceae), Hymenaea sp.
(Fabaceae), Caryocar coriaceum (Caryocaraceae) and
many Bromeliaceae; the dominant herbaceous plant being
Chamaecrysta flexuosa (Fabaceae). (5) The mangrove
association on the coastal stretches is composed of
Rhizophora mangle (Rhizophoraceae), Avicennia nitida
(Verbenaceae), Laguncularia flexuosa (Combretaceae),
and Conocarpus erectus (Combretaceae). The most representative families are Myrtaceae (16 species), Poaceae (10
species) Caesalpiniaceae (8 species), Fabaceae (7 species),
Mimosaceae (7 species), Malpighiaceae (7 species), Annonaceae, Bignoniaceae and Rubiaceae (6 species) Arecaceae,
Cyperaceae and Vochysiaceae (5 species), Asteraceae,
Apocynaceae Clusiaceae and Malvaceae (4 species),
Bromeliaceae, Chrysobalanaceae, Sapotaceae (3 species)
followed by 34 families with 1 or 2 species.
A total of 31.4% of the plant species from this region are
found in Cerrados in Central Brazil, and the correlation
with gallery forest in Central Brazil (27.2%) is higher than
with northern restingas (19.9%), while the correlation with
Amazonian and Atlantic rainforests is low (10% and 14%,
respectively). Manilkara sp. (Sapotaceae) is the dominant
tree of the area and is common to the three types of
vegetation, Cerrado, gallery forest and Restinga. In the
rainforest, trees belonging to Copaifera martii (Caesalpiniaceae), Platonia insignis (Clusiaceae), Anacardium occidentale (Anacardiaceae) Platonia martii (Clusiaceae) and
Eschweilera ovata (Lecythidaceae) grow to a height of 30 m
while in the Lake Cac- ó area they remain treelets (Table 1)
(Ribeiro, 2002; Pessenda et al., 2004).
The area around Lake Cac- ó has a mean annual
precipitation of 1400–1500 mm and a mean annual
temperature of 25 1C. Seasonal climate is controlled by
the position of the ITCZ, or meteorological equator that
divides the year into two main seasons: a rainy and a dry
season (Fig. 1A and B). Variations in the position of the
convergence zone are determined by the temperature
gradient between the pole and the equator. Consequently,
the convergence zone stays in the warmest hemisphere,
i.e. in the northern hemisphere, when the winter temperature gradient between the Antarctic and the equator is the
greatest, from June to September, and in the southern
hemisphere when the winter temperature gradient between
the Arctic and the equator is the greatest between
December and March. This seasonal feature can change
depending on the position of the South Atlantic Convergence Zone (SACZ) at mid-latitudes in Central Brazil.
When the SACZ is present, at around 20731S in latitude,
moisture is transported from the equatorial Atlantic
towards Amazonia with the help of the North-East trade
winds and progressively channeled’ and incorporated into
the SACZ in Central Brazil. When the SACZ is absent, the
warm and moist equatorial air masses remain close to
the coast, and polar advections from the south may be
able to reach these low latitudes and cooler temperatures
and heavy rainfalls occur. The interplay between these
two convergence zones regulates precipitations and seasons
in the northern part of the Nordeste (Fig. 1A and B)
(Ledru et al., 2002).
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Table 1
Main tree species in the Cerrado and riparian forest of Lake Cac- ó with their importance value index (IVI) (see explanation in the text)
Cerrado taxa
Cerrado IVI
Riparian forest taxa
Riparian forest IVI
Plathymenia reticulata
Mimosoidae
Qualea parviflora
Vochysiaceae
Parkia platycephala
Mimosoidae
Caryocar coriaceum
Caryocaraceae
Stryphnodendron
coriaceum
Mimosoidae
Salvertia
convalliaeriodora
Vochysiaceae
35
Manilkara sp.
Sapotaceae
Platonia insignis
Clusiaceae
Anacardium occidentale
Anacardiaceae
Copaifera martii
Caesalpinioidae
Protium sp.
Proteaceae
56.2
Qualea parviflora
Vochysiaceae
15.1
31.8
25.6
24.0
21.4
16.5
3. Material and methods
Three cores were collected in 1997 and 1998 in
aluminium pipes 7 cm in diameter with a Vibracorer
(Martin et al., 1995) at different locations in the lake
and under 12 m of water (Fig. 2). Core 98-4 was located at
the southernmost part of the lake near the entrance of
a stream at a depth of 600 cm. Core 98-5 was drilled in
the middle part of the lake where the seismic profile showed
a sand accumulation at a depth of 810 cm, and core 97-1
in the northern part of the lake at a depth of 345 cm.
Sediment samples were processed following standard
palynological techniques (Faegri and Iversen, 1989). Pollen
and spores were identified by comparison with a reference
pollen collection of 1000 taxa collected from various
herbaria by M.-P. Ledru and published pollen floras
(Colinvaux et al., 1999; Hooghiemstra, 1984; Markgraf
and D’Antoni, 1978; Roubick and Moreno, 1991; SalgadoLabouriau, 1973). Non-pollen palynomorphs were identified according to van Geel (1976). Data are expressed as
percentages of each taxon in relation to the sum of arboreal
pollen (AP), non-arboreal pollen (NAP) and undetermined
pollen grains, while pollen grains from aquatics and spores
were excluded from the pollen sum. The relative percentages of spores and pollen grains from aquatics were
calculated in relation to the total AP and NAP pollen sum.
A pollen concentration diagram (pollen grains/gram of
sediment) was also performed based on the method
described by Cour (1974) which consists in measuring
all the volumes and quantities during pollen extraction
(Fig. 5). A chronologic framework for the sedimentary
sequence was provided by conventional and accelerator
mass spectrometer (AMS) radiocarbon dates (Table 2).
Radiocarbon dates were calibrated into calendar years
before present (Stuiver and Reimer, 1993).
Isotopic analyses of carbon were underaken from soils
in the area of Lake Cac- ó in order to study the changes
in q13C of the humic material. Soil surface values of
35.4
32.0
17.3
15.3
d13C today range between –27.6% and –26.4% and
characterize the vegetation cover of the area. The application of carbon isotopes in studies of vegetation dynamics
is based on the variation in 13C composition of C3 and
C4 plants and its preservation in soil organic matter. 13C
values of C3 plant species range from approximately
32% to 20% PDB, with a mean of 27%. In contrast,
d13C of C4 species range from 17% to 9% with a
mean of 13%. Thus, C3 and C4 plant species have distinct
d13C values and differ from each other by approximately
14% (Boutton, 1996). Botanical surveys have shown that
crassulacean acid metabolism (CAM) plants, mainly
consisted of succulent plants, are absent from the study
area and thus cannot upset the measurement of q13C
(Pessenda et al., 2005).
4. Results
4.1. Lithology of the cores
4.1.1. Core ma 97-1
Core MA 97-1 was drilled at a depth of 345 cm. The
lowest 15 cm (Pollen zone VI in Fig. 4) were possibly
contaminated by modern organic sediment during coring
and were consequently not taken into consideration for this
study. Two sedimentological units were distinguishable
based on the color and the grain size of the sediment. In the
upper 300 cm, the sediment was composed of black organic
clay interbedded with a layer of sand between 238 and
250 cm. The unit from 300 to 310 cm was composed of gray
clay with sand.
4.1.2. Cores ma 98-4 and ma 98-5
Core MA 98-4 was drilled at a depth of 700 cm and
core MA 98-5 at a depth of 500 cm. Core MA 98-4
comprised 3 main units: the upper part was composed
of black organic clay to a depth of 285 cm interbedded
with gray clay and sand in the lowest part just above
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Table 2
Radiocarbon ages of total organic matter from cores MA 97-1, MA 98-4 and MA 98-5
Age (14C yr BP)
Depth (cm)
Lab number
Age rangea (cal yr BP)
q13C (%)
Core MA97-1
3060750
3830760
5090760
5580780
6010750
7660750
9040790
9720750
10,220740
10,170740
10,880750
11,6007120
12,6407135
12,930790
13,5607185
15,4007180
15,870760
18–23
31–32
40–45
48–49
68–70
95–100
118–120
135–140
150–151
158–160
172–174
178–180
200–202
215–218
241–242
259–260
275–277
Beta 110192
AA 32146
Beta 115180
AA 32147
AA33915
Beta 110193
AA 32148
Beta 110194
AA 35584
AA 35585
Beta 110195
AA 32149
AA 32150
Beta 115181
AA 32151
AA 32153
Beta 110196
3370–3080
4410–4000
5980–5660
6520–6200
7010–6820
8540–8370
10,040–9920
11,220–10, 880
12,400–11,740
12,360–11,630
13,130–12, 650
13,910–13, 170
15,750–14, 180
16,040–14, 480
16,920–15, 680
19,130–17, 740
19,570–18, 370
27.7
26.9
30.5
28.1
27.4
28.3
30.3
29.3
29.2
25.5
32
31.9
32.3
31.1
30.1
26.9
22.5
Core MA 98-4
2650740
7190790
8980770
15,3107100
16,2607280
30–32
90–92
200–202
336–338
432–434
AA
AA
AA
AA
AA
41234
41232
41243
41235 (1)
41236 (1)
2890–2790
8230–7840
10,290–9940
18,980–17,790
20,340–18,590
28.6
26.8
29.5
27.3
26.8
Core MA 98-5
5130750
12,010770
11,047770
14,7607170
15,2607110
15,3807110
54–56
154–156
268–270
327–329
406–408
362–364
AA
AA
AA
AA
AA
AA
49422
49423
49424
49425
49426
49427
6040–5800
15,370–13,700
13,230–12,720
18,390–17,100
18,930–17,720
19,070–17,850
28.5
31.7
25
24.2
24.4
24.1
Dates on samples with a (1) were obtained on vegetal remains only.
a
Range at two standard deviations with error multiplier of 1.0.
285 cm; the second unit was composed of gray clay with
sand interbedded with several layers of sand between 285
and 432 cm; the lowest unit was composed of sand with
organic clay and vegetal fragments to a depth of 570 cm.
From 570 to 700 cm sand was recovered from the dunes
with no organic content.
Core MA 98-5 comprised 3 main units: the upper unit
was composed of black organic clay to a depth of 156 cm;
the mid unit was composed of gray clay with sand between
409 and 156 cm, interbedded with sand layers, the thickest
layer between 275 and 303 cm, and the lowest unit, between
409 and 500 cm, was composed of sand with organic clay.
Samples were collected at 2 cm intervals for pollen and
non-pollen palynomorph analysis. The whole MA 97-1
core was analysed every 2 cm. In core MA 98-4, only the
lower lithological units were analyzed every 4 cm to detail
the end of the glaciation and the reinstallation of the
vegetation after the Last Glacial Maximum (LGM) in this
area. In core MA 98-5 we analyzed 41 samples every 4 cm
to check if the vegetation changes detected in cores MA971 and MA 98-4 reflected a regional dynamic (Fig. 3).
4.2. Pollen and non-pollen palynomorphs
4.2.1. Ma 97-1
Based on changes in the proportions of AP we
recognized 5 pollen zones in the simplified diagram
numbered from V (the oldest) to I (the youngest) (see
Fig. 4).
Pollen zone V extends from 310 to 250 cm with an
estimated age of 20,000–17,000 cal yr BP and is characterized by low percentages of AP ranging from 18% to 50%
with a peak of 85% at a depth of 258 cm. Among the main
arboreal taxa we distinguished Mimosaceae (ranging from
2% to 12%) Myrtaceae (2–11%) followed by Melastomataceae/Combretaceae (0–2%) and Byrsonima (0.5–4%).
Myrtaceae include taxa characteristic of forest regeneration
and re-humidification of soils on lake margins (Marchant
et al., 2002) that generally occur after a dry climatic event,
while the three other taxa characterize Cerrado today.
However the presence of Richardia (0.5–5%) together with
the Cucurbitaceae Ceratosanthes (single pollen grain)
evidence a dry prevailing climate at that time and AP
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Core MA 98-5
Core MA 98-4
cal yr B.P.
Core MA 97-1
2500
5000
10,000
cal yr B.P.
cal yr B.P.
7500
12,500
15,000
17,500
20,000
0
50 100
0
0
50 100
50 100
Arboreal Pollen (%)
Fig. 3. Arboreal pollen frequency curves of cores MA 97-1, MA 98-4 ad
MA 98-5. Percentages are expressed in calendar ages along a linear time
scale.
could represent treelets or bushes in a steppic environment.
This dry environment was confirmed by the presence of
Borreria (4–21%) and halophytic taxa (an association of
two chenopods Alternanthera and Gomphrena that are
herbaceous saline marsh plants) (1–12%). These taxa attest
to fluctuating water levels in the lake while Myriophyllum
(single grains in each sample) and Botryococcus (3–40%)
attest to shallow waters and cool temperatures. The peak of
85% AP at a depth of 258–260 cm and an estimated age of
17,500 cal yr BP are due to a sharp increase in the
percentage of Melastomataceae/Combretaceae (30%),
Moraceae/Urticaceae (22%), Myrsine (6%) and Didymopanax (3.5%) together with a decrease in halophytes
(0.5%) and Borreria (0.3%), which we interpreted to reflect
an abrupt increase in both moisture rates and temperature.
Among the non-pollen palynomorphs (Fig. 6), a high
percentage of Pleospora sp., the presence of Pediastrum,
low percentages of Spirogyra and Mougeotia and a peak of
Gieysztoria virgulifera (Neorhabdocoela oocytes) are observed followed by the disappearance of Pleospora sp. at
the end of this zone. At a depth of 280 cm the percentage of
Anthostomella fuegiana reaches maximum together with
high percentages of the algae Botryococcus and Zygnemataceae (Spirogyra) and some Neorhabdocoela such as
Micodalyellia armigera. At a depth of 270 cm the disappearance of Anthostomella fuegiana, low rates of Botryococcus, a peak of Pleospora sp., two maxima for Spirogyra
and the presence of Mougeotia are observed. Pleospora sp.
1115
grows on dead plant remains and is linked with a dry
environment; it is considered to be a good indicator for
some Cyperaceae in the local vegetation (van Geel, 1976).
As the two taxa Pleospora sp. and Anthostomella fuegiana
are out of phase, we considered the latter to characterize
moist edaphic conditions with the development of hygrophilous vegetation. Consequently, an increase in Anthostomella fuegiana at 280 cm is interpreted to indicate the
presence of higher moisture rates in a meso-eutrophic
environment (Haas, 1996). This change in local ecological
conditions is also apparent in the pollen concentration
diagram (Fig. 5) where an abrupt increase in the pollen
concentration of up to 54,300 grains/g, attests to the
dominance of Poaceae, Mimosaceae and Myrtaceae. In
addition, high rates of Pleospora sp. (at 270 cm) are
interpreted as indicating a shallow lake with eutrophic
waters, while Pleospora sp. disappears and a more humid
climate develops in this region (Haas, 1996; López Sáez
et al., 1998).
The end of the glaciation and the beginning of the
deglaciation are characterized by a steppic landscape with
low levels of water in the lake and cool temperatures.
Several abrupt changes in edaphic conditions indicate
unstable local climatic conditions during this period.
Pollen zone IV extends between 251 and 173 cm with an
estimated age of 17,000–12,800 cal yr BP. This pollen zone
is characterized by high percentages of AP ranging from
75% to 90% attesting to marked changes in the environment. The detailed succession of the different dominant
tree species is described in Ledru et al. (2001). Successive
ecological associations are observed in this zone: first
Didymopanax and Byrsonima, followed by Melastomataceae/Combretaceae and Myrsine and finally an increase in
Moraceae, Cecropia and Podocarpus. These are lighttolerant, pioneer taxa and attest to the progressive
installation of a dense forest around the lake. After the
peak of Podocarpus, Myrtaceae becomes dominant while
Podocarpus disappears. Two abrupt and brief changes in
vegetation towards forest regression are recorded: the first
at a depth of 222–224 cm, 15,000 cal yr, shows 35% AP,
and the second at 184–186 cm, 13,500 cal yr, shows 52%
AP. Both changes in arboreal cover are characterized by an
increase in Mimosaceae (2%) Borreria (10% at 184 cm),
Poaceae (35% at 222 cm, 41% at 184 cm) and Botryococcus
(45% at 222 cm) and the appearance of a new taxon
Rhizophora (6% at 184 cm). At 184–186 cm, during the
second abrupt change, pollen concentration values (Fig. 5)
increase sharply and are characterized by the presence of
Mauritia, Rhizophora and Mimosaceae taxa; at the same
time, the presence of the non-pollen palynomorphs (Fig. 6)
Coniochaeta cf. ligniaria, type 359 and Ustulina deusta,
indicators of stumps and dead roots of deciduous trees that
form their usual habitat (López Sáez et al., 1998; van Geel,
1976; van Geel et al., 1981), confirm the drastic regression
of the forest. The continuous presence of Rivularia type, a
cyanobacteria indicator of deep running waters in a mesoto oligotrophic environment, of Spirogyra, Mougeotia and
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Fig. 4. Pollen percentage diagram of core MA 97-1 showing selected taxa. The pollen sum includes arboreal and non-arboreal pollen taxa. Values smaller than 1% are represented by the ‘‘+’’ sign.
Core MA 97-1
3060±50
3830±60
5090±60
5580±80
6010±50
50
7660±50
100
9040±90
9720±50
150
10,880±50
11,605±120
12,640±135 200
12,930±90
300
13,560±185
15,400±180 250
15,870±60
Depth cm
1
5
1
type 90
type 173A
cf. Scopinella barbata
type 351
1
Bactrodesmium type
5
type 55
5
Spermatophores cf Copepoda
1
animal hairs
10 0.5 1
Rivularia type
Aphanizomenon cf. gracile
Alona rustica
Others
1 0.5 1 0.5
type 757
type 76
Mauritia
Mimosaceae
500 0 1500 0 500 0 500
2
%
type 359
Cecropia
103 0 100 0
pollen/g
10 0.5 0.5 1
Fungi
3
cf. Spadicoides bina
Coniochaeta cf. ligniaria
Byrsonima
Myrtaceae
Podocarpus
Rhizophora
Charcoal particles
type 527
type 972
I
II
III
1
1
Micodalyellia armigera
2
Strongylostoma radiatum
Pollen zones
Turbellaires
5
Gyratrix hermaphroditus
Gieysztoria virgulifera
IV
V
1
Mesostoma lingua
I
II
III
IV
V
Pollen zones
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5
Ustulina deusta
Poaceae
103 0 500 0
1
type 19
Total
M.-P. Ledru et al. / Quaternary Science Reviews 25 (2006) 1110–1126
10
Anthostomella fuegiana
Coniochaeta xylariispora
0
20
1
Pleospora sp.
0 20 103 0
5
Mougeotia
Tetraedron minimum
40
60
80
100
120
140
160
180
200
220
5
Spirogyra
Depth cm
240
260
280
300
1
Pediastrum
Lithology
Fig. 5. Pollen concentration diagram of core MA 97-1 showing selected taxa.
Botryococcus
Algae
50
Fig. 6. Diagram of core MA 97-1 showing records of non-pollen palynomorphs. Values are percentages of the pollen sum.
Age (14C yr B.P.)
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Pediastrum, and more discontinuously of Botryococcus, are
recorded throughout this zone.
The Lateglacial is characterized by the installation and
the development of a dense moist forest with high water
levels in the lake. Two regression phases towards open
landscape are recorded during this period.
Pollen zone III extends between 172 and 154 cm with an
estimated age of 12,800–11,000 cal yr BP and is characterized by the disappearance of the forest. The step
corresponding to the decreasing concentration of 14C in
the atmosphere at that time is clearly visible in the
radiocarbon dates with four dates between 11,600 and
10,220 14C yr BP within a 30 cm sediment deposition (Table
2) (Stuiver and Reimer, 1993). For a detailed description of
this environmental change see Ledru et al. (2002). A sharp
decline in the total percentage of AP (from 75% to 35%
within a 100 yr time period) occurs and is replaced by an
increase in Moraceae (from 2% to 23%) and Cecropia
(from 0.5% to 23%) two pioneer species that provide
evidence for the abrupt degradation of the previous dense
moist forest. Micro particles of charcoal (Fig. 5) are also
observed for the first time in the sediments of zone III
attesting to frequent fires in the area. Among non-pollen
palynomorphs (Fig. 6) we observe a decrease in the
percentage of Botryococcus, Spirogyra and an even greater
decrease in the Pediastrum and Rivularia type, as well as the
presence of type 55 and Coniochaeta cf. ligniaria. This
association is related to a locally meso-euthrophic environment with low water levels in the lake. Coniochaeta
xylariispora and Coniochaeta cf. ligniaria, high percentages
of cf. Spadicoides bina, type 359 and Bactrodesmium type
are associated with strong fires; high percentages of
Ustulina deusta, a non-pollen palynomorph common on
stump butts and dead roots of deciduous trees deposited
after forest burning are also apparent; Type 527 reflects a
clay sedimentation environment (van Geel, 1976, van Geel
et al., 1981, 1983a, 1986).
A drastic, short term but complete replacement of the
dense moist forest by Cecropia and grasses associated with
frequent fires characterize the general conditions of this
period.
Pollen zone II extends from 153 to 105 cm with an
estimated age of 11,000–8500 cal yr BP and is characterized
by a stable percentage of AP of between 41% and 63%.
The percentage of Cecropia is still high (0–11% with a
mean value of 4%) and Poaceae becomes a dominant
taxon (30–52%). New taxa such as Mauritia (single pollen
grains) and Rhizophora (3–15%) appear. They attest to
environmental conditions that are different from previous
zones. Mauritia is a common palm tree of the Cerrado
linked with seasonally inundated patches in the Cerrado
and Rhizophora is a component of mangrove vegetation.
The percentage (15%) of this species corresponds to the
distance between the lake and the coast, i.e. ca 80 km, as
the percentage of Rhizophora can reach more than 90% in
modern samples collected on the surface of the mangrove
(Behling, 1997). An abrupt change is apparent at 136 cm,
10,500 cal yr BP characterized by lower percentages of
Poaceae (7%) and Rhizophora (0%) and an increase in
Myrtaceae (28%) and Mimosaceae (11%). We interpreted
this as a short-term development of a dense riparian forest.
The percentage of Botryococcus, Pediastrum and Spirogyra
algae increase, and for the first time Spermatophores of
Copepoda are observed in the sequence, suggesting the
presence of open water (van Geel, 1976; van Geel and
Middeldorp, 1988). Rivularia type increase and the
appearance of the Neorhabdocoela oocytes (Mesostoma
lingua, Gyratrix hermaphroditus, Micodalyellia armigera,
Gieysztoria virgulifera and Strongylostoma radiatum) suggests the presence of locally moister soils than before, as
non-pollen palynomorphs that are characteristic of a dryenvironment are not recorded (e.g. type 55). The high
values detected for Neorhabdocoela could be the result of a
rise in lake productivity due to inorganic and organogenic
input to the lake, as attested by the subsequent blooming of
Pediastrum species, Botryococcus species and Zygnemataceae (Spirogyra) (Haas, 1996).
After the destruction of the forest observed during the
previous period, the composition of the vegetation did not
reverse to a dense moist forest. Open vegetation, strong
fires and the presence of some Cerrado species such as
Mauritia attest to the establishment of a relatively seasonal
climate with high water levels during this period.
Pollen zone I extends between 104 and 0 cm with an
estimated age of 8500 cal yr BP to modern. AP progressively increases throughout zone I, with 48% at the base
and 62% at the top. Byrsonima (1.5–5%), Cecropia
(1–6%) Melastomataceae (1–6%) Myrtaceae (1–6%)
Rhizophora (4.5–12%) and Swartzia (0–5%) represent a
constant trend throughout the zone, while Mimosaceae
increase progressively (2.5–17%). At the top of this
zone, the percentages of Mauritia (5%), halophytes (4%)
and Botryoccocus (73%) increase and Moraceae (0.5–2%),
Myrtaceae (3–6%), Borreria (1–3%) remain relatively
high. Maxima of algae Pediastrum, Botryococcus, Spirogyra, Mougeotia, type 55, Coniochaeta cf. ligniaria and
Neorhabdocoela, the presence of Pleospora sp., type 90,
Anthostomella fuegiana, type 173A and Aphanizomenon cf.
gracile are observed in the upper part of the zone (Fig. 6).
Between 15 and 50 cm, spermatophores of Copepoda
Alonsa rustica, Tetraedron minimum are also observed.
These taxa are characteristic of lakes with a low pH and
high water levels and indicate eu- to mesotrophic
conditions of open fresh water (Bakker and van Smeerdijk,
1982; van Geel, 1976; van Geel et al., 1983b). Aphanizomenon cf. gracile are akinetes of cyanobacteria and are able
to form dense populations (referred to as water blooms)
under warm temperature conditions. They are considered
as good indicators for meso- to eutrophic environments
and are linked to the increased input of phosphates into the
lake by man in modern times (van Geel et al., 1994; López
Sáez et al., 2000). Types 19, 52, 757, 972 also show maxima
in this zone but their ecological significance is not known
yet (Fig. 6).
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The wide range of non-pollen palynomorphs is characteristic of a euthrophic environment, with more organicrich and shallower water than during the previous period.
The Cerrado that started to develop in zone II now
develops fully. Warm temperatures and an increase in
moisture rates during the last centuries are modern
features.
4.2.2. Core ma 98-4
Radiocarbon dates (Table 2) indicate that core MA 98-4
represents a more detailed post LGM recovery of the
vegetation than in the other records. Consequently we
analyzed the lowest 300 cm of sediment deposition between
ca 21,000 and 17,000 cal yr BP. This section is characterized
by low percentages of AP, between 5% and 20% (Fig. 7).
Among the trees, we identified Byrsonima (0–5%), Mimosa
(0–11%), Myrtaceae (0–9%), Solanum (0–4%), Triplaris
(0–7.5%) and Melastomataceae (0–4%). Dominant herbs
are Borreria (0–37.5%) and Poaceae (17–58%). A change
in the aquatic taxa is evidenced at 427 cm by an increase in
Myriophyllum (0–4%), the disappearance of Alismataceae
(13–0%), and a decrease in Cyperaceae (from over 15% to
less than 10%), while Botryococcus increase sharply
up to 133%. Between 350 and 335 cm depth Borreria
increase (33%) and Richardia (less than 1%) and Botryococcus (1.5%) decrease due to a drop in the previous
water level.
The landscape was open with fewer trees and probably
more bushes in a dry herbaceous vegetation cover. There is
evidence of fluctuations in water levels from low to shallow
(succession of aquatics and algae) and for a progressive
increase in edaphic moisture (Myrtaceae).
4.2.3. Core ma 98-5
This core drilled at a depth of 439 cm was analyzed
between 122 cm and the bottom of the core to check if the
regional characteristics of the environmental changes
detected in both cores 97-1 and 98-4 during the
past 20,000 yr BP are also apparent in another part of the
lake.
Two main zones could be distinguished separated by a
sterile sand layer with no pollen content (Fig. 8). In the first
zone, between 450 and 315 cm, the arboreal content is
characterized by low percentages (13–30%) mainly comprising Byrsonima (0–4%) and Myrtaceae (1–7.5%). NAPs
are mainly Asteraceae (0–6%), Borreria (7–55%), Poaceae
(20–63%), Gomphrena (0–4.5%).
In the second zone, between 275 and 122 cm, after a brief
fluctuation in the percentage of AP from 26% to 87%, the
diversity and frequency of taxa increase: Byrsonima
(0–7%), Didymopanax (0–10%), Ilex (0–6.5%), Melastomataceae (0–33%), Moraceae (0–22%), Myrsine (0–9,5%),
Myrtaceae (6–25%), Podocarpus (0–6.5%). The peak of
6.5% of Podocarpus at 194 cm allows us to ignore the date
of 11,000 14C yr BP obtained at ca 260 cm since a similar a
peak was dated at ca 12,000 14C yr BP in core 97-1. The
succession of the following tree taxa is observed: Didymo-
1119
panax and Byrsonima, Melastomataceae/Combretaceae
and Myrsine followed by an increase in Moraceae and
Cecropia and Podocarpus. Botryococcus decrease attesting
to an increase in the depth of the lake. The same pattern is
observed in 97-1 between 17,000 and 12,800 cal yr BP
(Ledru et al., 2001).
The first zone attests to an open landscape under dry
environmental conditions and corresponds to zone V in
core MA 97-1. The second zone confirms the progressive
development of a dense moist forest during the lateglacial
and corresponds to zone IV of the MA 97-1 pollen
diagram.
The results obtained in the three cores MA 97-1, 98-4,
and 98-5 show the same evolution of the environment
during the last 20,000 yr and confirm the regional feature of
the changes observed in percentages of pollen in the
lacustrine sediments.
4.3. Changes in @13C
Three profiles were analyzed 50 m from the edge of the
lake (LCF 50), at 150 m (LCF 150) and at 200 m (LCF 200)
to the south (Figs. 1 and 9). The soil profile 50 m from the
edge of the lake does not show any changes in isotopic
values while the two other profiles show a change at
180–190 cm depth with values of q13C of 21.5% in LCF
150 and of 21% at 140–150 cm depth in LCF200. We
interpreted this as the presence of more open vegetation
with the dominance of C4 plants at the time of this isotopic
event. This change is estimated to have ocurred between
9000 and ca 4000–3000 cal yr BP according to five 14C dates
obtained in LCF 200. The presence of charcoals is
attributed to fires during the same time interval (Fig. 5)
(Pessenda et al., 2004, 2005).
5. Discussion
5.1. Evolution of the Cerrado at Lake Cac- o
Pollen, algae, spore and isotope contents of the cores and
profiles analyzed from Lake Cac- o and surroundings attest
to important changes in the floristic composition of the
Cerrado. In the southern hemisphere warming started at ca
19,000 yr BP leading that of northern hemisphere by about
2000 yr (Clark et al., 2004; Grootes et al., 2001; Jouzel
et al., 1995; Steig et al., 1999). The region of Lake Cac- o
showed sparse and shrubby vegetation with dominance of
steppic grasses and absence of trees in a poor sandy soil
(Jacob et al., 2004) with numerous short-term fluctuations.
This landscape does not present the characteristics of a
Cerrado but indicates dry climatic conditions. However,
single pollen grains of Byrsonima and Mimosa attest to
their presence in this region and that they could survive
under arid climates, most likely as shrubs. At the end of the
LGM and the beginning of deglaciation, when sedimentation started in the lake, the vegetation was sparse and
rare and mainly composed of dry herbs, Gomphrena,
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Fig. 7. Pollen percentage diagram of core MA 98-4 showing selected taxa. The pollen sum includes arboreal and non-arboreal pollen taxa. Values smaller than 1% are represented by the ‘‘+’’ sign.
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Fig. 8. Pollen percentage diagram of core MA 98-5 showing selected taxa. The pollen sum includes arboreal and non-arboreal pollen taxa. Values smaller than 1% are represented by the ‘‘+’’ sign.
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0
1890±60
2560±60
3870±70
Depth (cm)
100
4580±70
200
8970±80
LCF 50
LCF 150
LCF 200
300
-28
-26
-24
-22
∂13C ()
Fig. 9. q13C curves of the profiles LCF 50, LCF 150, LCF 200 and
radiocarbon dates obtained from charcoals collected in LCF 200 trench,
adapted from Pessenda et al. (2004).
Cyperaceae and Alismataceae, and shrubs such as Ceratosanthes (Cucurbitaceae), Richardia, indicators of poor
sandy soils in a dry climate. Cerrado was absent from the
area although some of the main Cerrado taxa (Byrsonima,
Mimosa) are represented by single pollen grains indicating
that Cerrado taxa continued to be present in the form of
some individual shrubs. Important taxa to consider are
Manilkara and Copaifera, both trees common to the three
vegetation types present today in the region of Lake Cac- o,
Cerrado, Restinga and riparian forest. They are observed
at Lake Cac- o since the beginnning of the record, although
in small numbers.
In Amazonia, at the same latitude as Lake Cac- o, the
record of Carajas (61S) shows that an expansion of
Byrsonima occurred at least two times during the Last
Glacial, which was interpreted as an indicator of a drier
and more open landscape (Absy et al., 1991). However, this
expansion of Byrsonima into Amazonia is not related to
any of the three phases of the decrease in the percentage of
AP (LGM, Lateglacial and mid Holocene for the latter)
recorded in the pollen diagram (Ledru, 2002). Thus, we
cannot infer an expansion of the Cerrado towards
Amazonia during glacial times. However we can infer the
facility of Byrsonima and some other Cerrado taxa, such as
Myrsine, to grow in association with other non-Cerrado
species revealing the importance of this taxon when
vegetation changes occur.
In northern Brazil, when humidity progressively increased after 17,000 cal yr BP, the percentage of AP starts
to increase mainly with an increase in Byrsonima, Mimosa,
Myrtaceae and the presence of Copaifera and Hymenea, an
assemblage of taxa that is characteristic of a Restinga. The
percentage of Myrtaceae, an indicator for poorly drained
soil, often increases when conditions suddenly become
moister after a dry event. Botryococcus, which is observed
at the base of all three cores, is associated with the presence
of a shallow lake. Beside these local features, a major
regional change is evidenced by the spread of the forest.
This forest evolved from a forest dominated by pioneerspecies towards a dense rain forest rich in Podocarpus, a
conifer of the cloud forest (Podocarpus lambertii) that is
widespread in southern Brazil today and is also found in
refugia in northern Brazil (P. sellowii). This increase in
Podocarpus is also evidenced in other records from
northern Brazil thereby attesting to the spread of this
species under favorable climatic conditions (Ledru et al.,
2001). The development of a dense moist forest represents
the main difference from the evolution of vegetation
in Central Brazil, considered to be the main area for
Cerrado today. In this region no forest installation was
recorded during the Lateglacial (Barberi et al., 2000). Here
the forest evolved from a forest with dominant-pioneer
species to a dense rain forest and ended abruptly at the end
of the Pleistocene.
The presence of Rhizophora since the beginning of the
Holocene attests to the installation of the mangrove on the
coast in the state of Maranhão after a rise in sea level. Its
relatively low percentage (20%) compared to the 90%
observed in records located inside the mangrove (Behling,
1997), attest to wind transportation from the coast to the
lake, which corresponds to the direction the trade winds
blow today.
During the early Holocene, summer insolation reached
its lowest value in the southern hemisphere with warmer
winters, colder summers and less precipitation than today
(Martin et al 1997), ENSO was also weaker or absent
(Rodbell et al., 1999). An open landscape expanded nearly
throughout the southern tropics showing some hiatus
in sedimentation (Ledru et al., 1998). At Lake Cac- o, all the
Cerrado taxa are recorded since the beginning of the
Holocene but at low rates. Mauritia, the main component
of the swamp forest in the Cerrado, can be observed since
the beginning of the Holocene attesting to an increase in
available soil moisture. The high water level of the lake
identified by sedimentological analysis (Sifeddine et al.,
2003) that is reflected in the higher soil moisture
availability in the region could be related to the rise in
sea level that started at the beginning of the Holocene and
continued until 7000 yr BP (Milne et al., 2005). Fully
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developed Cerrado is observed after 8000 yr BP when
Byrsonima and Mimosa are widespread along with
Poaceae. A sharp increase in Botryococcus, an alga that
is an indicator of shallow lakes, followed by repeated
changes in abundance attest to fluctuations in the level of
the lake during the late Holocene due to a more seasonal
climate. This is a general pattern observed in all
neotropical savanna areas, Llanos in Colombia and
Cerrados in Brazil, which became fully established after
7000 yr BP (Behling and Hooghiemstra, 2001).
Fires in the Cerrado are characterized as surface fires
that consume the fuel represented by the herbaceous layer.
The vegetation comprising the herbaceous layer represents
94% of the fuel consumed during the fires and Byrsonima
is fire resistant (Miranda et al., 2002). In northern Brazil,
fires are evidenced after 12,000 yr BP when the herbaceous
layer was fully established and Cerrado taxa started to
expand.
5.2. Paleoclimatic inferences and comparison with other
records
Late Pleistocene paleoenvironmental records from
northern Brazil reflect the interplay between insolation
forcing and local components represented by the interannual shift of the convergence zones (ITCZ and SACZ)
and the influence of equatorwards polar air incursions
during winter. At the time of the LGM, ice cores show that
both southern and northern hemispheres had minima in
temperatures. Consequently strong pole-equator temperature gradients on both sides of the equator were able to
prevent large seasonal shifts of a weakened ITCZ. A dry
climate and sparse open vegetation is observed at low
latitudes. Further south, the diameter of the atmospheric
circumpolar vortex increased and induced an increase in
the intensity of the circulation: mid-latitude westerlies were
able to extend northwards because of a weakened ITCZ
and consequently the subtropical high shifted equatorward
inducing changes in seasonal precipitation (Markgraf et al.,
1992; Wainer et al., 2005). During the deglaciation,
changes in insolation in Antarctica and Greenland resulted
in the reorganization of the thermohaline circulation
(Knorr and Lohmann, 2003) and rapid equatorward
displacement of the polar air masses (Garreaud, 1999;
Marengo et al., 1997). Two regional effects of changes in
the global atmospheric circulation are recorded at Lake
Cac- o during the Lateglacial. Both are characterized by a
decrease in temperature although they express differences
in signal expression. When the first abrupt climatic change
occurred between 15,000 and 13,500 cal yr BP, it was
related to the Antarctic cold reversal (ACR) when the
southern hemisphere was cooler than the northern hemisphere. This event is also well recorded in ice cores from
Antarctica and from the Andes (Blunier and Brook, 2001;
Thompson et al., 1998). Today strong and frequent polar
advections are able to reach low latitudes and influence the
distribution of precipitation (Kousky, 1979). We infer the
1123
same mechanism to explain the consequence of the ACR
near the equator when semi-permanent atmospheric
moisture enabled a forest of Podocarpus to expand
instantly from its refugia while the ITCZ was maintained
in a northern position in the warmest hemisphere. During
the second abrupt climatic change that corresponds to the
YD climatic reversal, temperatures in Greenland were
lower than in the Antarctic (Blunier and Brook, 2001) and
the northern hemisphere was consequently colder than the
southern hemisphere. Polar advections were stronger in the
northern hemisphere, reached tropical latitudes and prevented the seasonal northward shift of the ITCZ which was
maintained in a southern position. This induced a drier and
cooler climate in the tropics until 171S in latitude (Ledru et
al., 2002) and high moisture rates in northern Chile on the
Pacific side (Nuñez et al., 2002) as well as the absence of a
YD event further south in southern Patagonia (Markgraf,
1991). This short dry event drastically destroyed the moist
forest and strong fires are evidenced at this time. This
succession of abrupt climatic changes contributed to the
expansion of the species of the Cerrado in this region which
culminated during the Holocene. These abrupt changes
reflect modifications in the thermal gradient between the
pole and the equator that enable rapid shifts of polar air
masses to low latitudes and changes in the seasonal shifts
of the ITCZ and SACZ (Ledru, 2002; Ledru et al., 2001,
2002; Rind, 1998).
The precessional low that occurred at the beginning of
the Holocene in the tropics is reflected in the out of phase
response of the Central and South American lake levels.
Precipitation maxima/minima are recorded on either side
of a band located quite near the equator. South of this
band lake levels reflect dry conditions associated with the
early Holocene decrease in summer insolation, while north
of the band the ITCZ remained stationary for some time
and high moisture rates are evidenced (Haug et al., 2001;
Mourguiart et al., 1998; Seltzer et al., 2000). At Lake Cac- o,
the situation seems to lie between the two, as neither an
increase in moisture rates nor an increase in aridity after
the YD event is apparent. The expansion of the woody
vegetation seems rather to be related to an increase in
available soil moisture due to a rise in sea level. No major
changes in vegetation cover are evidenced during the late
Holocene while modern climatic conditions display a
strong seasonal contrast.
6. Conclusion
The records obtained at Lake Cac- o provide evidence for
important environmental changes since the beginning of
deglaciation at low latitudes. These changes caused the
installation of the Cerrado physiognomy and floristic
composition that can be observed today. In addition, some
Cerrado species, such as Byrsonima and Myrsine, are able
to grow under different climatic conditions and different
floristic associations which enable this biome to adapt to
local environmental changes. This ability could be the
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reason for the six different types of Cerrado defined by
Ratter in 1996. Marked differences in the evolution of the
climate within the six zones, e.g. between Central Brazil
and Maranhão during the Lateglacial, are also assumed to
explain these ecological differences.
Late Pleistocene paleoenvironmental records from
northern Brazil reflect the interplay between insolation
forcing of both hemispheres with the local components
represented by the interannual shift of the ITCZ and the
influence of equatorwards polar air incursions. Numerous
abrupt and short climatic changes are recorded by the
vegetation. One main change occurred between 15,000 and
13,500 yr BP and is characterized by forest expansion, and
the second occurred between 12,800 and 11,000 yr BP and,
is characterized by forest regression. The Holocene shows a
markedly different evolution and is divided into two main
periods: a relatively moist early Holocene due to a weak
seasonal contrast during the low precession signal and the
installation of a seasonally contrasted climate during the
second half of the Holocene. This is different from the
Central region of Brazil between 10 and 151S, where
marked mid Holocene aridity is evidenced by both pollen
and archeological records. The absence of typical ENSO
variations that are clearly apparent in other Holocene
records from tropical South America (Martin et al., 1993;
Rodbell et al., 1999; Stott et al., 2002) is attributed to the
natural adaptation of the biome Cerrado to a contrasted
seasonal climate, commonly a dry season lasting 5–6
months. This adaptation of the vegetation to long dry
seasons and fires prevented the regional lacustrine sedimentation from being affected by interdecadal or interannual climatic changes at a time resolution of 50–70 yr per
sample.
Acknowledgments
This research benefited from a CNPq (Brazil)–IRD
(France) convention and is part of Paléotropique UR 55 at
IRD. MPL greatly thanks Denis-Didier Rousseau and all
the people of the Paléoenvironnements at ISEM for
welcoming her in their group and for constant stimulation
and discussions. We thank Louis Martin, José Maria
Landim Dominguez, Abdelfettah Sifeddine and Bruno
Turcq for coring and leading the CNPq–IRD project at
Lagoa Cac- o and Evelyne Aliphat, Murielle Pariset, Brigitte
Le Roux for pollen samples treatment at IRD-Bondy.
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