INCREASED
MERCURY CONCENTRATIONS DURING THE YOUNGER DRYAS RECORDED IN AN OMBROTROPHIC
PEAT BOG
F. Roos, Geological Institute, University of Berne, Baltzerstrasse 1, CH-3012
Berne Switzerland.
Tel: +41 (31)
631 87 73 Fax: +41 (31) 631 48 43 email: fiona.roos@geo.unibe.ch
W. Shotyk, Geological Institute, University of Berne,
Baltzerstrasse 1, CH-3012 Berne, Switzerland
Abstract: Mercury concentrations have been determined in the oldest 1.6m of a peat
core from Etang de la Gručre in the Swiss Jura mountains which dates back over
12,300 radiocarbon years. A significant
Hg peak, more than three times the average “background” value, occurs at a
depth corresponding to the Younger Dryas cold period. The depth of the Younger
Dryas in the peat is indicated both by radiocarbon age dates and soil dust
indicator peaks in a replicate core from the same bog. These results show that
climate change is a significant factor in the natural variability of Hg in the
atmosphere.
Introduction: During the last three decades there has been
increasing interest in Hg as a global pollutant due to its capacity for long
range atmospheric transport, and the bioaccumulation of its toxic methylated
form. Numerous studies using lake
sediments and ice cores suggest that atmospheric Hg deposition has increased
significantly since the onset of the industrial revolution, even in remote
areas.
However, in order to quantify the anthropogenic
component of today’s global Hg budget it is important to understand natural
background levels and their variations. Studies have shown ombrotrophic peat
bogs to be good archives of net atmospheric Hg deposition (Benoit et al 1998,
Shotyk et al, in prep.). Of special
importance to the present study is the finding that there exists a relationship
between net Hg accumulation in the peat and Holocene climate change, with
greater accumulation occurring during cold periods (Martinez-Cortizas et al
1999). Peat formation in the ombrogenic bog “Etang de la Gručre” (EGR) in the
Swiss Jura mountains began 12,370 14C years BP. This offers an
opportunity to reconstruct the complete history of atmospheric Hg deposition
throughout the Holocene, extending as far back as ca. 14,500 calendar years, or
into the Older Dryas (14ka BP) cold event.
Unlike the “Little Ice Age” cold event, the inclusion of the Younger
Dryas (ca. 12,000 to 11,000 cal yr. BP) in the profile allows natural
variations in net mercury accumulation during an extensive cold climate period
in pre-anthropogenic times to be reconstructed. Here we present new measurements of Hg concentrations in the
deepest, oldest layers of EGR, to test the hypothesis that Hg accumulation
rates were elevated during the Younger Dryas cold event.
Methods: The Etang de la Gručre (EGR, co-ordinates
CH 570.525, 232.150) 2A core was used for Hg analysis. EGR lies 1005m above sea level. Annual precipitation at the site is
estimated to be 1500mm. The core was collected using a Livingston
corer and was 734cm long and 8cm in diameter. There is a sharp transition to
clay at 650cm. The core was sliced
frozen into 2cm slices and the individual slices were then stored at -18°C until analysis. Mercury was
analysed from 656 to 490cm. Tests were performed to assess the effect of air
drying on Hg concentration in peat samples compared to the concentration in wet
samples and the effects were found to be negligible. These tests are described
in detail elsewhere (Roos et al, 2000).
Samples measured wet (656-646cm) were allowed to thaw before analysis.
Material from these was extracted using plastic tweezers and analysed using the
Leco AMA 254. Each slice was analysed
in triplicate and the average concentration of each slice is given here. The
drying time (s) for the samples was [0.7 x volume of water], with water volume
calculated from water content and mass of sample. Water content and bulk
density of each slice were determined using peat plugs of known volume. The plugs were obtained from each thawed
slice using a stainless steel tube, of diameter 16mm, with a sharpened end. The
height of these plugs was measured and the volume of each calculated (v = pr2h) in cm3. The plugs were then dried to constant
weight at 105°C and the water content of the slice calculated.
The bulk density was expressed in g cm-3. The dry weight of each
sample analysed for Hg was calculated from its mass and water content. Hg
concentrations for all samples are expressed as ng g-1 dry weight.
Slices 644-594cm were air dried overnight in a
class 100 clean air cabinet. The wet weight of each slice to be air-dried was
recorded. After air drying one peat
plug was removed from each slice. Water content and bulk density of these plugs
was determined as described above. Material was extracted from the samples as
above and analysed for Hg. Each slice was again analysed in triplicate.
Slices 592-490cm were thawed and four plugs were
taken from each slice and air dried as above. One plug from each slice was
treated as above to determine water content and bulk density. The remaining
three plugs from each slice were placed in sealed plastic bags and crushed to a
fine powder by hand. This was done to
homogenise the samples and to allow as much sample as possible to fit into the
sample vessels. These samples were
analysed in duplicate. The average relative standard deviation of Hg
concentration per slice in wet samples 656-646 was 8.9% (3 samples per slice, 6
slices) and in air-died samples 592-490 was 3% (2 samples per slice, 53
slices).
Results and Discussion:
The results of the Hg analyses are shown (Figure
1).
Correspondence of Hg Peak to Younger Dryas Cold
Period
A pronounced peak in Hg concentration appears at
550cm. In a corresponding core from the same bog (core EGR 2P, collected
22.6.1993) (Shotyk et al, in review), the
slice at 555cm depth was dated at 10,590±60 radiocarbon years BP, which corresponds
to 10,572 calendar years BC. The Younger Dryas occurred from 11.5-12.8 calendar
years BP (Alley et al, 1993), which corresponds to 9,550-10,850 calendar years
BC. Thus, the Hg peak in the core EGR
2A corresponds to the Younger Dryas period.
The EGR 2P core has also been analysed for soil dust indicators such as
Zr, Ti and Hf by XRF analysis. These elements show pronounced concentration
peaks (ten times background values) at 550cm depth in the 2P core (Figure
2). During cold periods precipitation
decreases, wind strength increases and vegetation recedes (Holmgren et al,
1998). These factors all lead to an
increase in soil dust in the atmosphere.
Therefore increases in soil dust indicator values in the peat profile
indicate cold, dry periods such as the Younger Dryas. The Hg peak and the soil dust peak in the two profiles occur at
the same depth (550cm), indicating that Hg concentrations were clearly elevated
during the YD compared to deeper, older peat layers.
Possible Causes of Hg Peak During theYounger Dryas
The Hg peak corresponds to an increase in soil
dust and it is possible that the Hg increase is directly due to an increase in
weathering and atmospheric transport of Hg-containing minerals; this would have
caused an increase in particulate mercury in the atmosphere. However, particulate mercury (Hgp)
in non-industrial regions makes up only 0.3-0.9% of total atmospheric mercury
(Slemr et al, 1985), the major component being gaseous Hg(0). It is unlikely,
therefore, that enhanced rates of soil dust deposition caused the elevated Hg
concentrations. Also, the bog is unaffected by any major regional natural
Hg-containing mineral sources. It is assumed therefore that the major sources
of Hg to the bog are wet deposition of Hg (II), oxidised from gaseous
atmospheric Hg(0) in water droplets in the atmosphere (Lin et al 1999) and
direct dry deposition of Hg(0) to the bog surface. An increase in Hg deposition
would therefore require either greater atmospheric Hg concentrations, greater
dry deposition rates and/or a decrease in revolatilisation once deposition has
occurred. A decrease in temperature would reduce the volatility of Hg(0) and
therefore could increase the net rate of accumulation, both by increasing the
rate of dry deposition and also by decreasing the likelihood of revolatilisation.
Implications
It is clear from the results shown here that
climate dependency makes natural net Hg accumulation rates very variable. Also,
climate dependency of net Hg deposition could mean that regions of colder
climate today such as polar and Alpine environments could act as natural sinks
of Hg in the environment, with more condensation and less revolatilisation of
Hg(0). Further studies of long-term
records of Hg accumulation in colder regions and studies to determine the
relative importance of wet and dry deposition are required.

Figure 1: Large squares
represent sediment samples, diamonds represent peat samples.

Figure 2 (Shotyk et al, in review)
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