Agricultural (Ap, Ap-horizon, 0–20 cm) and grazing land soil samples (Gr, 0–10 cm) were collected from a large part of Europe (33 countries, 5.6 million km2) at an average density of 1 sample site/2500 km2. The resulting more than 2 2000 soil samples were air dried, sieved to <2 mm and analysed for their Hg concentrations following an aqua regia extraction. Median concentrations for Hg are 0.030 mg/kg (range: <0.003–1.56 mg/kg) for the Ap samples and 0.035 mg/kg (range: <0.003–3.12 mg/kg) for the Gr samples. Only 5 Ap and 10 Gr samples returned Hg concentrations above 1 mg/kg. In the geochemical maps the continental-scale distribution of the element is clearly dominated by geology. Climate exerts an important influence. Mercury accumulates in those areas of northern Europe where a wet and cold climate favours the build-up of soil organic material. Typical anthropogenic sources like coal-fired power plants, waste incinerators, chlor-alkali plants, metal smelters and urban agglomerations are hardly visible at continental scales but can have a major impact at the local-scale.

Mercury in European agricultural and grazing land soils / R. T., Ottesen; M., Birke; T. E., Finne; M., Gosar; J., Locutura; C., Reimann; T., Tarvainen; Albanese, Stefano; M., Andersson; A., Arnoldussen; M. J., Batista; A., Bel lan; D., Cicchella; A., Demetriades; E., Dinelli; DE VIVO, Benedetto; W., De Vos; M., Duris; A., Dusza; O. A., Eggen; M., Eklund; V., Ernstsen; P., Filzmoser; D., Flight; M., Fuchs; U., Fugedi; A., Gilucis; V., Gregorauskiene; A., Gulan; J., Halamic; E., Haslinger; P., Hayoz; R., Hoffmann; J., Hoogewerff; H., Hrvatovic; S., Husnjak; C. C., Johnson; G., Jordan; L., Kaste; B., Keilert; J., Kivisilla; V., Klos; F., Krone; P., Kwecko; L., Kuti; A., Ladenberger; Lima, Annamaria; D. P., Lucivjansky; D., Mackovych; B. I., Malyuk; R., Maquil; P., Mcdonnell; R. G., Meuli; N., Miosic; G., Mol; P., Négrel; P., O’Connor; A., Pasieczna; W., Petersell; M., Ponavic; S., Pramuka; C., Prazeres; U., Rauch; H., Reitner; M., Sadeghi; I., Salpeteur; N., Samardzic; A., Schedl; A., Scheib; I., Schoeters; P., Sefcik; F., Skopljak; I., Slaninka; A., Šorša; T., Stafilov; E., Sellersjö; V., Trendavilov; P., Valera; V., Verougstraete; D., Vidojevic; Z. Z. o. m. e. n., I.. - In: APPLIED GEOCHEMISTRY. - ISSN 0883-2927. - 33:(2013), pp. 1-12. [10.1016/j.apgeochem.2012.12.013]

Mercury in European agricultural and grazing land soils

ALBANESE, STEFANO;DE VIVO, BENEDETTO;LIMA, ANNAMARIA;
2013

Abstract

Agricultural (Ap, Ap-horizon, 0–20 cm) and grazing land soil samples (Gr, 0–10 cm) were collected from a large part of Europe (33 countries, 5.6 million km2) at an average density of 1 sample site/2500 km2. The resulting more than 2 2000 soil samples were air dried, sieved to <2 mm and analysed for their Hg concentrations following an aqua regia extraction. Median concentrations for Hg are 0.030 mg/kg (range: <0.003–1.56 mg/kg) for the Ap samples and 0.035 mg/kg (range: <0.003–3.12 mg/kg) for the Gr samples. Only 5 Ap and 10 Gr samples returned Hg concentrations above 1 mg/kg. In the geochemical maps the continental-scale distribution of the element is clearly dominated by geology. Climate exerts an important influence. Mercury accumulates in those areas of northern Europe where a wet and cold climate favours the build-up of soil organic material. Typical anthropogenic sources like coal-fired power plants, waste incinerators, chlor-alkali plants, metal smelters and urban agglomerations are hardly visible at continental scales but can have a major impact at the local-scale.
2013
Mercury in European agricultural and grazing land soils / R. T., Ottesen; M., Birke; T. E., Finne; M., Gosar; J., Locutura; C., Reimann; T., Tarvainen; Albanese, Stefano; M., Andersson; A., Arnoldussen; M. J., Batista; A., Bel lan; D., Cicchella; A., Demetriades; E., Dinelli; DE VIVO, Benedetto; W., De Vos; M., Duris; A., Dusza; O. A., Eggen; M., Eklund; V., Ernstsen; P., Filzmoser; D., Flight; M., Fuchs; U., Fugedi; A., Gilucis; V., Gregorauskiene; A., Gulan; J., Halamic; E., Haslinger; P., Hayoz; R., Hoffmann; J., Hoogewerff; H., Hrvatovic; S., Husnjak; C. C., Johnson; G., Jordan; L., Kaste; B., Keilert; J., Kivisilla; V., Klos; F., Krone; P., Kwecko; L., Kuti; A., Ladenberger; Lima, Annamaria; D. P., Lucivjansky; D., Mackovych; B. I., Malyuk; R., Maquil; P., Mcdonnell; R. G., Meuli; N., Miosic; G., Mol; P., Négrel; P., O’Connor; A., Pasieczna; W., Petersell; M., Ponavic; S., Pramuka; C., Prazeres; U., Rauch; H., Reitner; M., Sadeghi; I., Salpeteur; N., Samardzic; A., Schedl; A., Scheib; I., Schoeters; P., Sefcik; F., Skopljak; I., Slaninka; A., Šorša; T., Stafilov; E., Sellersjö; V., Trendavilov; P., Valera; V., Verougstraete; D., Vidojevic; Z. Z. o. m. e. n., I.. - In: APPLIED GEOCHEMISTRY. - ISSN 0883-2927. - 33:(2013), pp. 1-12. [10.1016/j.apgeochem.2012.12.013]
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Utilizza questo identificativo per citare o creare un link a questo documento: https://hdl.handle.net/11588/568298
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