Elevated Mercury
Concentrations in Southern Patagonian Peat Bogs – An Anthropogenic Signal ?
Institute of Environmental
Geochemistry, INF 236, 69120 Heidelberg, Germany
Dept. of Geology, University
of Freiburg, Albertstr. 1b, 79104 Freiburg, Germany
*corresponding author:
hbiester@ugc.uni-heidelberg.de
Mercury was analysed
in two peat cores from an ombrogenic peat bog in the southernmost Andes/Chile.
Mercury concentrations range between 40 and 80 µg/kg in pre-industrial times
and show a sharp increase to 160 µg/kg in modern times. The high Hg levels in
the upper part of the cores were attributed to the strong increase of Hg
emissions from anthropogenic sources in the past 100 yr. Sources of Hg others
than atmospheric deposition could be excluded in the study area. It is assumed
that the comparatively high accumulation of Hg in this remote area is mainly
due to the high precipitation rates reaching up to 10.000 mmm per year. This
suggests that Hg emitted from anthropogenic sources is dispersed all over the
atmosphere and even accumulated in remote sub-antarctic areas.
Numerous studies in
the past two decades confirm an increase of Hg concentrations in the atmosphere
due to modern anthropogenic emissions. Fluxes of Hg from industrial sources
such as coal fired plants, ore smelters or chlor alkali plants are comparable
in magnitude to natural fluxes (Nriagu, 1989). The biogeochemical cycle of Hg
is characterized by distribution of the metal all over the planet due to its
unique property of being volatile. Therefore, the atmosphere is the main
pathway for the distribution of mercury at the Earth‘s surface. The residence
time of Hg in the atmosphere is estimated to be about one year. The dominant
atmospheric Hg species is elemental Hg which could be partly oxidized. Both Hg
species reach the Earth‘s surface through wet or dry deposition. In recent
years increasing attention has been given to atmospheric deposition of Hg in
remote areas especially in arctic regions. Increased Hg levels found in several
natural archives such as snow and ice, lake sediments and ombothrophic peat
bogs confirm increased fluxes of anthropogenic Hg from mid lattitudes to the
arctic. Here, deposition of Hg, derived from mid latitudes was found to be
mainly due to a gernerally increased deposition of gaseous compounds at low
temperatures (cold condensation). The impact becomes clear regarding the high
Hg levels in arctic mammals. However, up to now little is known about the fate
of Hg in the southern hemisphere especially in higher latidues. While ice core
records from Antarctica have provided excellent chronological records of
atmospheric lead, little is reported about past and present deposition of Hg.
Vandal et al. (1993) investigated
mercury deposition in Antarctica ice cores and found that variability of
pre-anthropogenic Hg levels is due to variations of productivity in the
oceans. It is still unknown, if anthropogenic Hg emission on the northern
hemisphere also cause increased Hg deposition in high latitudes of the southern
hemisphere.
In our study we have
investigated the record of atmospheric Hg deposition in peat bogs located in
the southernmost Andes/Chile. Several studies have shown that ombothrophic peat
bogs are excellent archives for records of atmospheric Hg deposition (e.g.
Pheiffer-Madsen, 1981; Benoit et al.,
1994). The southernmost Andes are characterized by narrow succession of
climatic zones which are characterized by heavy rains and strong westerly winds
driven by the antarctic circum polar vortex on the west side and dryness on the
east side. The sampling area is located in the area of maximum anual
precipitation reaching up to 10.000 mm . Vegetation in the area is characterized
by a mixture of magellanic moorland and subarctic forests.
Two peat cores were
taken from an ombrogenic raised bog (GC1) located on the alluvial plain of the
Gran Campo Nevado glacier (52° S). The cores were taken by means of a 2 m
stainless steel Wardenaar corer. Length of the both peat monolith was about 150
cm, respectively. The cores were immediately cut into 2 cm slices (10 x 10 cm)
using a serrated stainless steel bread knife and packed into polyethelen bags.
All samples were stored deep frozen. Bulk density was determined from 3
subsamples, which were cut in the field from the fresh peat slices using an
apple corer. Before analysis approximately half of each slice was freeze dried
and milled. Mercury concentrations were determined by atomic absorption
spectroscopy after thermal combustion of the freeze dried samples and Hg
preconcentration on a gold trap. SRM (apple leaves, rye grass and olive
leaves) were used for quality control of Hg analysis. RSD was in the range of
1.5 - 2.1 % (n = 4). About 3 g of the dried and milled peat of the uppermost 15
cm were dated using 210Pb age. Trace-metal free protocols were
employed during all stages of collection and analysis. The ash content was
determined after combustion of approximately 1 g of dried peat at 550 °C.
Both profiles are
marked by an about 12 cm thick, coarse grained tephra layer at about 100 cm
depth, which was identified as a big Mt. Burney eruption dated to 8500 B.P.
(Stern, 1992). The cores are assumed to cover about 13.000 yr. The Hg records
in both profiles are very similar in shape indicating that the variation of Hg
concentrations in corresponding sections within the bog is low. Both cores show
high Hg levels of about 100 µg/kg in the deepest
20 cm which probably indicate Hg fluxes from the basement. At about 120 – 130
cm Hg levels drop to about 40 µg/kg. Above the tephra layer Hg concentrations
increase from about 40 µg/kg to values between 80 and 100 µg/kg in the section
from 50 to 15 cm. In the uppermost 15 cm of the profiles Hg concentrations increase
drastically to maximum values of 160 µg/kg.
A.
B. 
Fig. 1: Records of Hg in two
cores from a peat bog taken in southernmost Patagonia/Chile
A: Record of Hg and ash
content in core 1 B: Hg record and Hg record corrected for density in core 2.
As the upper 15 cm
are within the 210Pb excess activity it is most reasonable that this
peak indicates increased anthropogenic emissions of Hg in the last 150 yr.
Those Hg concentrations are at the same levels as those found in Greenland peat
for the same period of time (Shotyk et al.
2000). The enrichment factor of Hg in modern times is about 2 - 4 compared to
the variability of pre-industrial levels (40 – 100 µg/kg). The reasons for the
generally increase of Hg from about 40 to 100 µg/kg in pre-industrial times is
unknown and might be related to climatic factors as indicated in other studies (Martinez-Cortizas et
al., 1999).
Figure 1a shows the
Hg record of one of the peat cores and records of ash content. It seems that in
the ombrogenic part Hg concentration are independend from the ash content which
is different for other trace metals (analysed in ongoing studies). Figure 2b
shows the record of Hg in the second core and the shape of the curve if Hg is
corrected for density. It was found that the variation of the density of the
peat is low and the shape of the Hg record changed only little if corrected for
density.
The Hg record in
ombothrophic peat from the south Patagonian bog shows a clear signal of
increased anthropogenic Hg emission within the last 150 yr. The signal found in
peat of which has not yet been reported from Antarctic ice cores is concluded
to be related to the high precipitation rates in the study area which cause a
strong washout of Hg from the atomsphere.
These results
confirm the long term transport of Hg and its accumulation even in
sub-antarctic areas.
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