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32 MAYLAND ET AL. <br />SELENIUM AS A FERTILIZER <br />Selenium fertilization is briefly discussed to provide information to in- <br />terested agronomists and animal nutritionists. <br />The clay fraction and organic matter content in soil play a major role <br />in the bioavailablilty of Se, especially selenite, which is readily sorbed to these <br />soil constituents. Selenate is less readily sorbed in finer-textured soils or soils <br />with higher organic matter concentrations. Consequently, Selenate is usual- <br />ly absorbed from soils by plants more readily than is selenite (Carter et al., <br />1969). Greater absorption of Selenate may also result from differences in root <br />permeability or that selenite is reduced to elemental Se on the root surface. <br />Although sulfate-S exerts little effect on selenite uptake, it competes with <br />the absorption of selenate (Gissel-Nielsen, 1973; Westermann & Robbins, <br />1974). <br />The development of a safe and effective Se fertilizer must consider the <br />chemical form, its solubility under the range in soil pH and redox poten- <br />tials, and the rate and amount of Se uptake by the plant. The application <br />of lime or companion fertilizer containing phosphate, sulfate, or N can also <br />affect Se concentrations in the herbage (Gissel-Nielsen, 1973; Milchunas et <br />al., 1983). These materials may contain small amounts of Se, or they may <br />stimulate root growth and subsequent uptake of soil Se (Carter et al., 1972; <br />Westermann & Robbins, 1974). Application of these nutrients often stimu- <br />late forage yields, thereby diluting the Se concentration in the forage (H.F. <br />Mayland, 1975 unpublished data). <br />Fertilizers made from rock phosphates may contain as much as 200 mg <br />Se/kg (Rader & Hill, 1935; Robbins & Carter, 1970; Senesi et al., 1979). These <br />concentrations are generally much higher than those measured in fertilizers <br />derived from rock carbonates, synthetic N fertilizers, and even potassium <br />sulfate (Senesi et al., 1979). Thus, some fertilizer materials may contribute <br />Se for use by higher plants. <br />Selenium-deficient soils are often S-deficient, especially for the produc- <br />tion of legumes. The application of sulfate fertilizers can simultaneously <br />stimulate plant growth and compete with soil selenate for absorption sites <br />on the root and transport mechanisms in the plant. Increasing the concen- <br />trations of sulfate-S in the forage also may have detrimental effects on Se <br />availability to the animal (Hintz & Hogue, 1964; Pope et al., 1979). <br />There is some risk associated with the application of selenates to acid <br />and neutral soil because of their high bioavailability (Reuter, 1975). Ex- <br />perience has shown that the use of selenate fertilizer results in much higher <br />levels (sometimes toxic to animals) of Se in the first cut of forages following <br />fertilization (Tables 2-3 and 2-4). Selenium concentrations in the forage, <br />fertilized with a selenate source, usually tend to decrease sharply with each <br />subsequent harvest (Carter et al., 1969; Giessel-Nielsen & Bisbjerg, 1970; <br />Ylaranta, 1983). <br />