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Last modified
1/26/2010 3:14:42 PM
Creation date
10/12/2006 4:31:58 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8170
Description
Arkansas Basin Water Quality Issues
State
CO
Basin
Arkansas
Water Division
2
Date
9/1/1981
Author
Bureau of Reclamati
Title
Heavy Metals Pollution of the Upper Arkansas River - Colorado - and its Effects on the Distribution of the Aquatic Macrofauna
Water Supply Pro - Doc Type
Report/Study
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<br />0012 <br /> <br />principal anion in fresh waters. It is an important <br />component of sulfhydryl bonding in protoplasm <br />(Cole. 1979 [28J I. In waters of the United <br />States that contain good fish populations. <br />95 percent have sulfate values of less than <br />90 mg/L (Hart et aI., 1945 (711). <br /> <br />Chloride <br /> <br />Chloride (CI) is a constituent of rain and snow <br />throughout the world and is fairly uniform within <br />each locality (Hutchinson, 1957 1811), Other <br />sources of chloride include waters containing <br />chloride leached from igneous rock, releases <br />from chlorinated domestic sewage treatment <br />plants ICole. 1979 (281), and runoff from <br />winter salting of highways (Environmental Pro- <br />tection Agency, 1971 [501 l. Hart et al. (1945) <br />[711 report data which indicates that 95 per- <br />cent of United States waters with good fish <br />populations have chloride concentrations below <br />170 mg/L. Adams (1941) 111 reported that a <br />concentration of 400 mg/L was harmful to <br />trout. <br /> <br />Phosphorus <br /> <br />Phosphorus IPI is an extremely important ele- <br />ment for primary production in streams, and <br />because of sources in rainfall, runoff. and <br />domestic sewage discharges. it is seldom a <br />limiting factor for plant growth in a natural <br />stream IHynes, 1970 [84J and Golterman. <br />1975 (661). Phosphorus is essential to all life <br />in that it is a component of A TP (adenosine tri- <br />phosphate), which is instrumental in providing <br />cellular energy. The inorganic form. orthophos- <br />phate, is highly reactive and can be used im- <br />mediately by autotrophic plants ICole, 1979 <br />[281 I. Phosphorus is highly concentrated in <br />aquatic food chains. A study by Davis et al. <br />119581 [351 found concentrations of the radio- <br />active tracer phosphorus-32 to be 370,000 <br />times higher in the caddisfly larvae. Hydrop- <br />syche. than in the water. <br /> <br />Nitrogen <br /> <br />Nitrogen IN). like phosphorus, is an important <br />component for primary production in aquatic <br />systems. Nitrogen usually exists as ammonia, <br />(NH,), nitrite INO,). nitrate INO,). and organic <br />nitrogen ITKNl. Nitrate is the most available <br />form for plant growth, and this fully oxidized <br />form occurs most often in running water (Hynes. <br /> <br />1970 [841). A variety of sources such as <br />sewage and other forms of pollution, and the <br />abundance of nitrogen in the atmosphere, en- <br />sures that nitrogen seldom limits plants produc. <br />tion in aquatic ecosystems ICole. 1979 [281 l. <br />Hart et al. (1945) [711 report that 95 percent of <br />the waters in the United States that contain <br />good fish fauna have nitrate concentrations of <br />less than 4.2 mg/L. <br /> <br />Heavy Metals <br /> <br />The heavy metals referred to in this review in- <br />clude manganese IMn). iron IFe). copper ICul, <br />zinc IZn), lead IPbl, molybdenum IMo). and cad. <br />mium ICd). Wood (1975) [1731 has classified <br />metals into three categories: 111 noncritical. <br />(2) toxic but very insoluble or rare, and 13) very <br />toxic and relatively abundant. IMetals of atomic <br />number less than 40 are generally abundant and <br />usually cause the greatest concern in relation to <br />aquatic ecosystems.) <br /> <br />Many of these elements are needed in small con- <br />centration for primary production and are there- <br />fore essential for all life IFogg, 1975 [571 I. <br />Toxicity results when these elements reach <br />levels that can no longer be tolerated or avoided <br />by aquatic organisms. <br /> <br />There have been many literature reviews of the <br />toxicity of heavy metals to aquatic organisms <br />(McKee and Wolfe. 1963 [105]; Environmental <br />Protection Agency, 1971 [491; and Becker and <br />Thatcher, 1973 [7J l. Much of the literature <br />deals with acute toxicity levels, with less em- <br />phasis on the study of safe levels for chronic ex- <br />posure. <br /> <br />Concentrations of heavy metals in waters are <br />generally higher in summer than in winter INam- <br />minga and Wilhm. 1977 [1181 I. This is prob- <br />ably due to an increase in microbial activity in <br />the warmer sediments and a corresponding in- <br />crease in metal concentrations I Duke et al.. <br />1966 [411 I. Under conditions of low dissolved <br />oxygen. pH. and oxidation-reduction potential, <br />heavy metals can be released into the water <br />(Sartoris et al., 1977 [133] I. Mathis and Cum- <br />mings (1971) [104J showed that organisms <br />that inhabited the mud-water interface had high <br />levels of metals in their body tissues; however, <br />fishes that were primarily carnivorous or higher <br />in the food chain had the lowest concentrations. <br />In contrast, other studies have shown a high <br /> <br />11 <br />
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