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Programa e Resumos - I Congresso Ibérico de Ciência do Solo 2004

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I <strong>Congresso</strong> Ibérico da Ciência <strong>do</strong> <strong>Solo</strong> – 15 a 18 <strong>de</strong> Junho <strong>de</strong> <strong>2004</strong>, Bragança, Portugal<br />

Total Hg content in acid forest soils nearby a coal-fired power-plant in<br />

Galicia (NW Spain).<br />

1 Nóvoa-Muñoz, Juan Carlos; Pontevedra-Pombal, Xabier; Martínez-Cortizas, Antonio &<br />

Eduar<strong>do</strong> García-Ro<strong>de</strong>ja.<br />

1 Dpto. Edafología y Química Agrícola. Fac. Biología. Universidad <strong>de</strong> Santiago <strong>de</strong> Compostela.<br />

Rúa Lope Gómez <strong>de</strong> Marzoa s/n, 15782 Santiago <strong>de</strong> Compostela, Galicia, España.<br />

Resumo<br />

Comunicação: Painel<br />

Total Hg contents were measured in five soil profiles, nearby a coal-fired power plant<br />

located in Galicia (NW Spain), sampled between 1992 and 2001. Previous studies have<br />

shown that lignite burning in the power plant results in the emission of 95% of Hg<br />

contained in the coal. Mercury concentrations were measured in air dried soil samples<br />

using an ALTEC AMA-254 mercury analyzer. The aim of this work is to use natural<br />

soils as geochemical indicators to study the <strong>de</strong>gree of Hg contamination in terrestrial<br />

ecosystems.<br />

The results revealed that surface soil horizons (O, A) have the highest Hg contents, up<br />

to 300 ng g -1 soil, although it was observed a subsurface maximum in Bs horizons (80-<br />

250 ng g -1 ). Mercury enrichment factors, calculated by normalizing to the total Hg<br />

content of the soil parent material, are above 50 in most surface horizons, suggesting a<br />

strong Hg accumulation in the upper part of the soils probably due to the power plant<br />

emissions.<br />

Using a multiple regression analysis, a combination of soil organic matter content<br />

(SOM), pyrophosphate extracted Fe (Fep) and ammonium oxalate Al (Alo) could<br />

explain 88% of the variance of Hg content of these soils. (Hg = 8.2 SOM + 51.1 Fep -<br />

43.8 Alo). Whereas SOM can be regar<strong>de</strong>d as a soil capacity factor to bound Hg, Fep<br />

may indicate a quality factor associated with geochemically active SOM. The negative<br />

load of Alo could be explained through the competition between Al and Hg for SOM<br />

binding sites.<br />

Regarding the temporal trend, Hg contents measured in 1992 were significantly higher<br />

than those measured in the following years. This can be the result of two processes:<br />

losses of soil Hg and a lower Hg <strong>de</strong>position due to recent changes in the coal mixture<br />

burnt in the power plant.<br />

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