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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.

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