FATE OF MERCURY IN THE ARCTIC Michael Evan ... - COGCI
FATE OF MERCURY IN THE ARCTIC Michael Evan ... - COGCI
FATE OF MERCURY IN THE ARCTIC Michael Evan ... - COGCI
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138 F. Roos-Barraclough et al. / The Science of the Total Environment 292 (2002) 129–139<br />
species or between mosses growing within different<br />
microclimates on the surface of a bog could<br />
be inconsistent (Norton et al., 1997).Mercury<br />
concentrations within one small horizontal section<br />
of peat may be uneven.Several subsamples should<br />
be taken from each peat slice in order to obtain a<br />
representative Hg concentration for the whole<br />
slice.Because large fluctuations in bulk density<br />
values can occur throughout a peat core, bulk<br />
density should be determined in each slice to allow<br />
Hg flux rates to be calculated accurately.<br />
Finally, mixing together the moss component of<br />
the subsamples increases the homogeneity of the<br />
material to be analysed.Here, grinding in a coffee<br />
mill resulted in a slight loss of Hg.However,<br />
simple hand mixing of the dried samples held in<br />
a plastic bag resulted in low standard deviation of<br />
duplicate pairs.<br />
5. Conclusions<br />
The following protocol is proposed for the<br />
determination of mercury concentrations in solid<br />
peat samples:<br />
Cores should be transported frozen from the<br />
field to the laboratory, if possible, to avoid unnecessary<br />
compaction and losses of water or Hg.The<br />
peat should be kept in clean (wrapped airtight in<br />
plastic), cool conditions until analysis.The edge<br />
of the core should be removed prior to analysis in<br />
case of contamination (by smearing) during core<br />
collection.Several subsamples should be analysed<br />
from each peat slice in order to obtain a representative<br />
value.These subsamples can be air-dried at<br />
room temperature in a clean environment, such as<br />
a Class 100 laminar flow cabinet, without significant<br />
loss of mercury.During this period, the<br />
cabinet should be darkened to avoid light-enhanced<br />
evasion of mercury from the samples (Gustin and<br />
Maxey, 1998).Dried subsamples can be homogenised<br />
by crushing air-dried plugs of peat together<br />
into a powder and mixing; this can be done by<br />
hand, with the samples in a sealed plastic bag.<br />
One or more subsamples from each slice should<br />
be used for bulk density determination, which is<br />
required to allow mercury deposition fluxes to be<br />
calculated.Bulk density can be determined from<br />
the dry weight of a peat subsample of known<br />
volume.Air drying this subsample with the subsamples<br />
to be used for mercury analysis (of the<br />
same shape and volume) before drying it in a<br />
drying oven to constant weight allows the water<br />
content of the air-dry samples to be accurately<br />
estimated; this information can be used to correct<br />
the masses of the samples analysed for Hg to their<br />
true dry weights.<br />
Suggested times for a Leco AMA 254 air-dry<br />
peat analysis program are: 30 s (drying), 125 s<br />
(decomposition) and 45 s (waiting for emission<br />
of waste gases before Hg content determination by<br />
AAS).<br />
Acknowledgments<br />
Financial support for this work, including graduate<br />
student assistantships to F.R. and N.G., was<br />
provided by the Swiss National Science Foundation<br />
(grants 21-55669.98 and 21-061688.00) to<br />
W.S. Peat core collection in the High Arctic of<br />
Canada was made possible by a research grant to<br />
W.S., Heinfried Scholer ¨ (University of Heidelberg)<br />
and Stephen Norton (University of Maine) by the<br />
International Arctic Research Centre, Fairbanks,<br />
Alaska.Many thanks to Drs W.O.Van der Knaap,<br />
E.Feldmeyer, A.Gruenig and A.Holzer for plant<br />
identification and B.Eilrich for considerable field<br />
assistance.<br />
References<br />
Aaby B, Digerfeldt G.Handbook of Holocene Paleoecology<br />
and Paleohydrology.Sampling techniques for lakes and bogs<br />
New York: John Wiley and Sons, 1986.p.181 –194.<br />
Benoit JM, Fitzgerald WF, Damman AWH.The biogeochemistry<br />
of an ombrotrophic peat bog: evaluation of use as an<br />
archive of atmospheric mercury deposition.Environ Res<br />
Sect A 1998;78:118 –133.<br />
Burgess, N., Beauchamp,S., Brun, G., Clair, T., Roberts, C.,<br />
Rutherford, L., Tordon, R.,Vaidya,O. Mercury in Atlantic<br />
Canada A Progress Report, Environment Canada, Atlantic<br />
Region.Environment Canada Report, 1998.<br />
Environmental Protection Agency.EPA method 7473:Mercury<br />
in solids and solutions by thermal decomposition, amalgamation,<br />
and atomic absorption spectrophotometry.1998.<br />
Gustin MS, Maxey R.Mechanisms influencing the volatile<br />
loss of mercury from soil.Proceedings of Air and Waste<br />
Management Association: Measurement of toxic and related<br />
air pollutants.Carty, NC Sept.1–3, 1998.