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Selenium - The Risk Assessment Information System

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2.0 SUMMARY OF ECO-SSLs FOR SELENIUM<br />

<strong>Selenium</strong> is a naturally occurring element found in all environmental media: air, soil, sediment,<br />

and water. In nature it is found in the sulfide ores of heavy metals and predominates in<br />

approximately 40 minerals including clausthalite, naumannite, tiemannite, and berzelianite<br />

(Budavari, 1996; Fishbein, 1991). <strong>Selenium</strong> is also found in volcanic rock, sandstone, shale,<br />

carbonates, bedrock, coal oil, and mineral oil (Kent and Spycher, 1994; Langer, 1993).<br />

<strong>Selenium</strong> may be released to the environment from natural sources such as volcanic eruptions,<br />

leaching and weathering of rocks, and volatilization as a result of biomethylation by plants and<br />

bacteria (ATSDR, 1996). Anthropogenic releases of selenium may result from use in the<br />

manufacture and production of glass, pigments, rubber, metal alloys, textiles, petroleum, medical<br />

therapeutic agents, anti-dandruff shampoos, veterinary medicines, fungicides, gaseous insulators,<br />

and photographic emulsions (USDOI, 1985; ATSDR, 1996). <strong>The</strong> burning of coal, oil and solid<br />

waste may also contribute to selenium in the environment (NRC, 1976; ATSDR, 1996).<br />

Background concentrations<br />

reported for many metals in U.S.<br />

soils are described in Attachment<br />

1-4 of the Eco-SSL guidance<br />

(U.S. EPA, 2003). Typical<br />

background concentrations of<br />

selenium in U.S. soils are plotted<br />

in Figure 2-1 for both eastern and<br />

western U.S. soils.<br />

In soils, the chemical forms of<br />

selenium are largely dependent<br />

on pH and oxidation-reduction<br />

potentials (McNeal and<br />

Balistrieri, 1989). <strong>Selenium</strong> can<br />

exist in the 2-, 0, 4+, and 6+<br />

oxidation states (McNeal and<br />

Balistrieri, 1989). Speciation of<br />

selenium in soils is also<br />

Conc (mg/kg dw)<br />

influenced by the chemical and mineralogical composition of the soil,<br />

microbial intervention, and the nature of the adsorbing surfaces (Neal,<br />

1990). <strong>Selenium</strong> has a sorptive affinity for hydrous metal oxides, clays,<br />

and organic materials. In well-aerated alkaline soils, inorganic selenium<br />

exists primarily as the oxyanions selenite (Se(4+)) and selenate (Se(6+)).<br />

4<br />

3.5<br />

3<br />

2.5<br />

2<br />

1.5<br />

1<br />

0.5<br />

0<br />

East West<br />

Figure 2-1 Typical Background<br />

Concentrations of <strong>Selenium</strong><br />

in U.S. Soils<br />

Maximum<br />

Eco-SSL for <strong>Selenium</strong> 2<br />

July 2007<br />

95th<br />

75th<br />

50th<br />

25th<br />

5th Percentile<br />

Selenite is soluble, but can strongly adsorb to soil minerals and organic material (Tokunaga et al.,<br />

1997), while selenate is the most mobile of selenium compounds because of its high water<br />

solubility and inability to adsorb to soil particles (ATSDR 1996). Alkaline soils formed from<br />

parent materials high in selenium are also high in biologically available selenium (Mayland et al.,<br />

1989). In poorly aerated soils, inorganic Se predominates as the relatively soluble selenide and

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