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<br />The order of decreasing ease of reduction of the <br />most important heavy metals is: manganese, <br />zinc. iron, cadmium. lead, and copper. However. <br />this order is a function of all the constituent ele- <br />ments and their chemical environments and is <br />only a general indication of mobility under reduc- <br />ing conditions (Mortimer. 1942 1114]). Zinc, <br />being highly toxic and relatively easily reduced. <br />would likely be the most severe heavy metal pol- <br />lution problem in the upper Arkansas River. Cad- <br />mium may also be a serious problem due to its <br />greater toxicity to aquatic organisms. <br /> <br />California Gulch and AR-3 contain visible evi- <br />dence of a precipitated iron layer. Hutchinson <br />(1957) 181] and Cole (1979) 1281 consider <br />this oxidized (ferric) iron layer an effective bar- <br />rier to the diffusion of reduced substances from <br />the deeper layers into the overlying water. <br />Reduction of this oxidized layer to ferrous com- <br />pounds allows other reduced metals in the sedi- <br />ment to move into the water. An E, value of <br />100 mV or below would indicate reduction of <br />sulfate to sulfide, and ferrous sulfide and other <br />heavy metal sulfides are generally insoluble and <br />tend to precipitate (Sartoris et aI., 1977 <br />11331 ). This phenomenon, however, may only <br />occur under anaerobic conditions. Reducing en- <br />vironments also favor slower degradation of <br />organics and the formation of structurally com- <br />plex, large-molecular-weight molecules which <br />are effective in binding metals (Gambrell et al.. <br />1976 f60/ ). These electrochemical factors and <br />the uncertainty of which elements are in ionic or <br />labile forms make precise heavy metals toxicity <br />predictions difficult. <br /> <br />Current <br /> <br />Water velocities determined by discharge meas- <br />urements are questionable in correlations with <br />suitable habitat for macroinvertebrate because <br />the velocity adjacent to the substrate is normally <br />much slower than the calculated average stream <br />velocity (Cummins. 1962 131) I. It was ob- <br />vious. however, that velocities were high <br />enough to suspend sediments and some degree <br />of benthic scour had occurred during the spring <br />runoff. Concentrations of metals generally were <br />higher downstream of AR-3, indicating that <br />sediments were suspended in the areas of the <br />Leadville Drain and California Gulch and carried <br />downstream. and higher metal loads were enter- <br />ing the river through increasing inflows. <br /> <br />Total numbers of benthic organisms were <br />generally lower at all stations, except EF-1, dur- <br />ing spring runoff. This may have been due to dif- <br />ficulty in sampling during high flows, or the <br />emergence of aquatic insects; however. <br />Bogatov (1978) 1121 found a sharp depletion of <br />benthos in riverbeds following a flood period. An <br />increase in Saetis abundance at AR-3 following <br />spring runoff indicates that metal-laden sedi- <br />ments were scoured from the streambed and <br />that the habitat improved for a time. <br /> <br />Substrate <br /> <br />The substrate sampled was relatively uniform <br />throughout the study area. Slightly larger stones <br />were present at the downstream stations. as <br />were deeper channels and pools. The larger sub- <br />strate at AR-8, particularly, was likely the reason <br />for a reduction in the mean d for macroinverte- <br />brates at this station. This substrate was not as <br />preferred. sampling was more difficult, or both. <br />Riffle-type habitat and riparian vegetation <br />dominated in the upper section of the river and <br />became less abundant in the lower reaches. <br /> <br />Ephemeropterans were more abundant in the <br />areas of shallow riffles and trichopterans were <br />more abundant in deeper channel sections. The <br />abundance of trichoptemns in the river below <br />the Lake Fork inflow may reflect an increase in <br />food supply being released from the upstream <br />reservoir (Muller. 1955, 1956 [116. 117]). <br />Dipterans were usually found associated with <br />organic debris during the winter and late sum- <br />mer. The genera of macroinvertebrates found on <br />this substrate indicated that the upper Arkansas <br />River contained rocks and had a moderate-to- <br />fast streamflow (Hart and Fuller, 1974 1701 ). <br />This accurately describes the river in the study <br />area. <br /> <br />Water Chemistry <br /> <br />The major ion properties of the water in the <br />study section of the Arkansas River are similar to <br />most high mountain streams in Colorado. The <br />concentration of any particular element or com- <br />pound usually increases below pollution sources <br />and decreases below freshening inflows <br />(LaBounty et al., 1975 1941 ). <br /> <br />34 <br />