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FATE OF MERCURY IN THE ARCTIC Michael Evan ... - COGCI

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to recover ca. 2 cm 3 plugs from every cm down to 40 cm, and every 2 nd cm below 40 cm; these<br />

were air-dried overnight at room temperature in a Class 100 laminar flow clean air cabinet.<br />

Mercury concentrations were measured in these plugs using solid sample atomic absorption<br />

spectroscopy (Salvato and Pirola, 1996) with a LECO AMA 254 as described in detail elsewhere<br />

(Roos-Barraclough et al., 2002). The instrument was calibrated using liquid Hg working<br />

standards prepared from a Merck 1000 mg/l Hg standard solution. Every 12th measurement was<br />

a certified reference material, either NIST 1515 (Apple Leaves) or NIST 1547 (Peach Leaves).<br />

The average measured values were 45.0 ± 0.7 ng/g (n=11) for NIST 1515 (certified value 44 ±<br />

4 ng/g) and 32.1 ± 1.4 ng/g (n=15) for NIST 1547 (certified value 31 ± 7 ng/g). The Hg<br />

concentration profiles presented here (analyst: F. R-B.) are in excellent agreement with those<br />

reported previously (analyst: M.E.G.) for selected samples from the same cores (Goodsite, 2000).<br />

As an independent check on the data which are presented here, Hg concentrations were<br />

also measured in a complete set of subsamples at the Department of Arctic Environment, Danish<br />

National Environmental Research Institute (analyst: G.A.). Approximately 1 g fresh sample and<br />

4 ml concentrated Merck Suprapur nitric acid were added to Teflon bombs with stainless steel<br />

caps, which were then heated for 12 hours at 150/C. After cooling the dissolved samples were<br />

left uncovered until the majority of the nitrous oxides had evaporated. Before analysing for Hg,<br />

potassium permanganate solution was added until a permanent pink colour was obtained in order<br />

to maintain an oxidising environment and to prevent loss of Hg. The samples were then diluted<br />

with 18 MS water to approximately 25 g in polyethylene bottles. Mercury concentrations were<br />

determined following reduction with sodium borohydride in a flow injection AAS system<br />

(Perkin Elmer FIMS). The data set obtained using this procedure is in good agreement with the<br />

data which is presented in this paper, obtained using the LECO AMA 254 (on average, within<br />

15%, r 2 = 0.727, n=65).<br />

11

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