Selenium is not an essential element for plant growth, but its level in the diet affects
the health of animals and humans. The Food and Nutrition Board of the National
Academy of Sciences, USA (1980) has accepted 5 mg Se
kg_1 diet (dry wt. basis) as the critical
level between toxic and nontoxic feeds. Consumption of Se-rich feed is seriously affecting
the health of animals and human beings in some parts of Punjab (Dhillon and Dhillon,
1997). Soils containing as low as 0.5 mg Se
kg_1 can produce fodder containing toxic levels of
Se (Dhillon et al., 1992). The transfer of Se from soil through plants to food is governed
by many soil-related factors, including the presence of other ions such as S, P or Fe in the
soil solution (Mikkelsen et al., 1989). The classical antagonistic relationship
between sulphate-S and selenate-Se uptake by various plants has been reported by many
research studies (Pratley and McFarlane, 1974; Mikkelsen and Wan, 1990; and Dhillon and
Dhillon, 2000). Although alfalfa (Medicago
sativa) accumulated more Se than western wheat
grass (Pascopyrum smithii), S amendments either as elemental S or gypsum at 1.0 Mg
ha_1 were equally effective in suppressing Se uptake (>60%) in both the forage species
(Mackowiak and Amacher, 2008). Sulfate-S is a structural analog of selenate-Se, resulting in
competitive uptake. Absorption of selenate-Se takes place through high affinity sulfate
transporters, but the transporters favor S over Se in nonaccumulating plants
(Sors et al., 2005). Greater
sulphate/selenate ratios in soil solution may shift the balance toward greater
sulphate uptake, resulting in lower plant Se concentrations.
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