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Titlebook: Heavy Metals in Soils; Trace Metals and Met Brian J. Alloway Book 2013Latest edition Springer Science+Business Media Dordrecht 2013 Environ

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樓主: 嚴厲
51#
發(fā)表于 2025-3-30 11:23:39 | 只看該作者
Selenium(0.01–2 mg/kg), but parts of China, India and the USA have toxic soil Se levels. Available soil Se is poorly correlated with total soil Se and is highly variable, both locally and globally. The plant availability of Se in soil depends on the major Se species present and on soil characteristics, incl
52#
發(fā)表于 2025-3-30 13:26:06 | 只看該作者
Zincough atmospheric depositions, fertilization and sewage sludge application. Zinc contaminated soils with negative impact on the soil ecosystem are found around Zn smelters, near Zn mining sites and under galvanized structures. The solubility of Zn in soils is almost invariably controlled by sorption
53#
發(fā)表于 2025-3-30 17:29:50 | 只看該作者
54#
發(fā)表于 2025-3-30 21:28:58 | 只看該作者
55#
發(fā)表于 2025-3-31 04:00:08 | 只看該作者
Sources of Heavy Metals and Metalloids in Soilst and many other non-specific urban sources. Although the heavy metal(loid) composition of agricultural soils tends to be more closely governed by the parent material, inputs from sources such as deposition of long-distance, atmospherically-transported aerosol particles from fossil fuel combustion a
56#
發(fā)表于 2025-3-31 06:09:23 | 只看該作者
57#
發(fā)表于 2025-3-31 10:14:48 | 只看該作者
58#
發(fā)表于 2025-3-31 16:04:40 | 只看該作者
Effects of Heavy Metals and Metalloids on Soil Organismslly result in either population decline due to toxic effects/loss of prey or population growth due to the removal of predators or competition. Populations of different species are affected in different ways, modifying community structure and ecosystems. Organisms found in contaminated soils in which
59#
發(fā)表于 2025-3-31 20:44:46 | 只看該作者
60#
發(fā)表于 2025-4-1 00:00:14 | 只看該作者
Critical Loads of Heavy Metals for Soilsplications are shown. Results are discussed in view of the uncertainty and applicability of the critical load concept for heavy metals in future agreements on the reduction of metal emissions. It is concluded that for policy applications, dynamic models are also needed to estimate the times involved
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