Selenium Contamination in Water. Группа авторов

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Selenium Contamination in Water - Группа авторов

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available for plants in loamy than in sandy soil. Besides this, OM facilitates the simulation of microbial activity that changes the oxidation state of Se (VI to ‐II). This may also result in methylation, which facilitates strong binding of Se to OM. The reduced form of Se is sorbed on OM and less mobile. Fungal growth in the presence of OMs affects the mobilization of Se and its availability hindered dramatically from soil to plant. Se concentration in soil also varies along the depth profile of soil. Presence of free calcium carbonate and increased pH (alkaline) reveals toxic seleniferous soils. To evaluate Se contamination understanding related to particulate Se is important, because every species has different bioavailability. The bioavailability of Se in soil follows the following order: selenate (Se6\+) > selenomethionine > selenocysteine > selenite (Se4+) > elemental selenium (Se0) > selenide (Se2−). Remedial treatments are highly desired to overcome the problems related to Se pollution by industrial waste. To this end it has been proposed by the researchers that treatment of industrial discharge is necessary before disposal. On the other hand it can be minimized by reducing the concentration of Se level in the soil by encouraging use of gypsum, OM such as mud, and poultry manure. Besides this, there is also more‐advanced in‐situ bioremediation by different bacterial cultures to reduce or tolerate Se concentrations in soil.

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