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UCREFRP
UCREFRP Catalog Number
8153
Author
Jacobs, e. L. W.
Title
Editor
USFW Year
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USFW - Doc Type
1989
Copyright Material
YES
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SELENIUM IN SELENIFEROUS ENVIRONMENTS 29 <br />of Se tolerance. Selenium absorbed by the nonaccumulator plants is con- <br />verted into Se metabolites, which act as analogues of essential S compounds <br />and interfere with cellular biochemical reactions. <br />SELENIUM IN ANIMALS <br />Selenium toxicosis in aquatic and terrestrial animals has been well <br />described in several reviews (NAS-NRC, 1983; Sorensen, 1986; Chapter 8 <br />of this publication). Selenite, selenate, and organic Se sources produce simi- <br />lar toxicological effects (Moxon &Rhian, 1943; unpublished data by L.F. <br />James et al., 1986). Absorption rates vary between chemical forms. Mini- <br />mum lethal doses maybe 1.5 to 3.0 mg Se/kg body weight as selenate (Moxon <br />& Rhian, 1943), although tolerance levels differ between and within animal <br />species and nutritional conditions (Volcani et al., 1957). <br />Chronic toxicity studies have indicated that diets providing 4 to 5 mg <br />Se/kg body weight or more of Se daily result in chronic toxicity in laborato- <br />ry animals (NAS-NRC, 1983). The Food and Nutrition Board of the Na- <br />tional Academy of Sciences (1980) has accepted 5 mg Se/kg diet as the critical <br />level between toxic and nontoxic feeds. <br />In general, Se as selenomethionine is more readily absorbed when in- <br />gested by animals than is Selenite, selenate, or selenocystine (NAS-NRC, <br />1983). Nearly one-half of the Se in wheat grain is present as selenomethio- <br />nine (Olson et al., 1970), so the Se in wheat is more readily available to animals <br />than is the Se in selenocystine, Astragalus, or fish meal. Generally, Se from <br />plant forms is more available to animals than Se from animal forms. <br />As in plants, Se in animals interacts with other trace elements. Frank <br />et al. (1986) found 20% lower liver Cu concentrations in cattle (Bos taurus) <br />supplemented with 0.58 mg Se/kg diet compared with 0.18 mg Se/kg in the <br />control diet over a 7- to 8-month period. Koh and Judson (1987) evaluated <br />the efficacies of oxidized Cu particles and Se bullets on the production <br />responses in young cattle marginally deficient in both elements. The Se bullets <br />exerted an antagonistic effect on the availability of Cu from the Cu0 parti- <br />cles, as indicated by reduced Cu concentrations in the whole blood, plasma, <br />blood cells, and liver. Animal weight gains were significantly increased when <br />both Cu and Se were supplemented, but not when provided individually. This <br />has practical applications because Cu deficiency has been reported in areas <br />where cattle and sheep (Ovis arees) are often supplemented with Se (H.F. <br />Mayland, 1986, personal observation). <br />Sulfate S is another anion that interferes with Se absorption and <br />metabolism. Halverson et al. (1962) reported that the addition of sodium <br />sulfate to rat (Rattus rattus) diets reduced the toxicity of 10 mg Se as selenate <br />per kilogram diet. However, adding the sulfate salt to diets containing Selenite <br />or seleniferous wheat was ineffective in reducing the toxicity. Thus, increas- <br />ing the sulfate-S levels in diets that are marginally adequate in Se could be <br />expected to increase the clinical incidence of white muscle disease (Hintz & <br />Hogue, 1964). Pope et al. (1979) also found that blood-Se levels in sheep <br />were inversely related to dietary S levels, but this effect could be countered <br />by increasing the dietary intake of Se. <br />
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