Large-scale extraction of metals presents hazardous waste management problems worldwide. Projections show that by the year 2000 mining will hgve directly disturbed about 240,000 km of the Earth's surface (1), an area about the size of Oregon; copper mining alone is projected to totally disrupt about 1600 km2 of land. Milling and smelting presently release an estimated 7 to 70 x 103 metric tons (MT) of metals to the aquatic environment (1,2). Metal production has increased over the last century although the grade of ore has declined (3), and the richest metal reserves are now in less developed countries (4) where legislative protection from environmental damage often is limited.Coping with hazardous waste problems is an immense challenge (5). In the United States, EPA has identified over 31,000 hazardous waste sites (6); about 1200 of these need immediate response, and only a small proportion have been cleaned up (6, 7). The largest complex
Selenium fractionation and speciation in Benton
Lake National Wildlife Refuge (Montana), a wetland
system containing moderate levels of selenium, were
studied to determine the biogeochemical processes of
selenium in wetlands. Results showed that selenate
was a major selenium species of dissolved selenium
in drainage water. It decreased substantially through
the pond system as the relative percentages of organic
selenium and selenite increased. Elemental selenium
and selenium associated with organic materials
were the major fractions in sediments, accounting
for a mean of 46% and 33% of total selenium,
respectively.
Concentrations of soluble selenium and adsorbed
selenium were relatively low, respectively accounting
for a mean of 5% and 13%. Within the soluble and
adsorbed fraction of selenium in sediment, selenate
and organic selenium were the major selenium species. Selenium associated with oxides was very low
(less than 4%). In this wetland environment,
microbial
reduction of selenate to elemental selenium, selenium
uptake by wetland organisms, and incorporation of
these organisms into wetland sediment are the
major processes removing selenium from the water
column; selenium adsorption is relatively less
important.
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