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SELENIUM IN SELENIFEROUS ENVIRONMENTS 41 <br />tus officinallis (L.) Pall.], grown on fly ash containing 5.3 mg Se/kg, was <br />formulated at 35% of a diet fed to hamsters (Mesocricetus auratus) and guinea <br />pigs (Cavia porcellus) for 90 d (Furr et al., 1975). Sheep and goats (Capra <br />hircus) were fed a pelleted diet containing seleniferous white sweet clover <br />(Melilotus alba Medik.) harvested from a fly ash disposal area. The sweet <br />clover contained 66 mg Se/kg, but as prepared contained only 15.5 mg Se/kg, <br />which was fed for 173 d. In yet another study, wheat grain containing 5.7 <br />mg Se/kg, was fed to Japanese quail (Coturnix coturnix japonica). The wheat <br />had been grown on fly ash containing 21 mg Se/kg (Stoewsand et al., 1978). <br />Feed consumption and weight gains in each of these studies were not ad- <br />versely affected by the seleniferous diets. Although body tissues from animals <br />fed the seleniferous diets contained elevated levels of Se, outward signs of <br />selenosis were not evident. <br />SELENIUM IN MUNICIPAL SEWAGE SLUDGE <br />Municipal sewage sludge represents a major portion of the national solid- <br />waste disposal problem with an estimated 4.5 x 1010 kg produced in 1968 <br />(Furr et al., 1976b). Furr et al. (1976c) measured the elemental concentra- <br />tions in sludges collected from 16 U.S. cities and reported that the spectrum <br />and concentration of heavy metals in the sludge was generally a function <br />of the industry in the area. Selenium concentrations in the 16 sludges ranged <br />from 1.7 to 8.7 mg Se/kg, with an average of 3.2 mg Se/kg. <br />The bioavailability of the Se (and other metals) becomes an important <br />factor in the disposal of sewage sludges. Aheat-treated, waste-activated sludge <br />from the city of Milwaukee, WI, has been marketed commercially as Milor- <br />ganite, asoil conditioner for application on lawns and gardens. The product <br />contains 1.8 mg Se/kg. Furr et al. (1976b) grew a variety of garden crops <br />in pots with soil containing 10% Milorganite by weight. At harvest, the edible <br />portions of these crops had significantly greater concentrations of Se than <br />for those plants grown on the control soil, but the increase may not have <br />been biologically significant. <br />Waste from feed lots, poultry houses, and municipal sewage treatment <br />plants have also been evaluated as a supplemental feed for livestock. The <br />manures tested by Capar et al. (1978) contained 0.5 to 0.7 mg Se/kg, whereas <br />the Denver municipal sludge contained 5.4 mg/kg total Se. Feeding the Den- <br />ver sludge as 0, 4, or 12% of diet to 340 kg steers provided diets containing <br />0.16, 0.35, or 0.72 mg Se/kg (Kienholz et al., 1979). The sludge provided <br />very little metabolizable energy, and animal weight gains were less compared <br />with control animals. There was a trend (P > 0.05) for increasing Se con- <br />centrations in liver; 1.3, 1.7, and 4.2 mg Se/kg (dry basis) for the three treat- <br />ments, respectively. Selenium concentrations in dried blood were 1.3 and 1.7 <br />mg Se/kg in the basal and 12% diet, respectively (P < 0.05). <br />In another study (Boyer et al., 1981), steers were fed a basal or basal <br />diet containing 12% Fort Collins anaerobically digested sewage sludge. The <br />sludge contained 16 mg Se/kg but, after dilution with the rest of the ration, <br />