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<br />onn? 41 <br /> <br />452 CM, Tate and J,S, Heiny <br /> <br />Mountain ecoregion, Clear Creek at Golden had the <br />lowest Shannon diversity index value, number of <br />taxa and invertebrate density compared with other <br />mountain sites and was the only site affected by <br />mining. Differences in invertebrate communities <br />among forest, range, and built-up land use in the <br />mountain sites were not as distinct as compared with <br />different invertebrate communities found in plains <br />sites, In the Western High Plains ecoregion, geomor- <br />phology and land use affected invertebrate distribu- <br />tion as defined by DCA analyses, Land use was an <br />important factor affecting nutrient concentrations and <br />invertebrate communities, Sites in the plains/tributary <br />group were located in urban or a mixture of agricul- <br />ture/urban land use, These sites had higher nitrile, <br />ammonia, and total phosphorus concentrations than <br />sites in the plains/braided channel; higher nutrient <br />concentrations probably represent urban affects on <br />stream-water chemistry, The plains/braided channels <br />were wider and shallower than other plains sites and <br />land use primarily was agriculture or built-up, and <br />nutrient concentrations were lower than other plains <br />sites. Invertebrate density and total number of taxa <br />were greater and functional-feeding group composi- <br />tion was different in the plains/braided channel sites <br />compared with other plains sites. The land use at the <br />plains/ downstream from point-source sites was mixed <br />agriculrure/urban; however, these sites were below <br />the major municipal discharges into the South Platte <br />River Basin (Dennehy et ai" 1993) and nutrient concen- <br />trations were high, Organic pollution from point <br />sources, such as waste-water effluent, generally <br />decreases the number of insect species (Hynes, 1960) <br />as was shown in this srudy. In addition, community <br />composition was altered at these sites (Le. absence of <br />Trichoptera, greater proportion of non-insect taxa) <br />compared with plains/ tributary and plains/braided <br />channel sites, The plains/ downstream from point- <br />source sites were located in a rich algal zone (Table I) <br />where OIigochaeta dominated and oxygen concentra- <br />tions were high, This region is characterized by having <br />increased numbers of snails and an abundance of <br />Chironomidae (Wiederholm, 1984)_ The presence of <br />OIigochaeta, Physel/a sp" Simulium sp" and dominance <br />of Chironomidae genera and the absence of Trichop- <br />tera are characteristic of a stream reach effected by <br />organic pollution (Wiederholm, 1984), Similarly, Quinn <br />& Hickey (1990) reported that gross organic pollution <br />and runoff were important affects on community <br /> <br />composition at some sites in New Zealand streams. <br />Although spatial assemblages of invertebrate commu- <br />nities appear to be related to land-use patterns, specific <br />cause and effect relations cannot be addressed in the <br />present study, <br /> <br />Environmental factors affecting invertebrates <br /> <br />As noted in other large basin-scale studies, a combina- <br />tion of environmental factors affected the invertebrate <br />distribution and abundance within the South Platte <br />River Basin. Differences in invertebrate communities <br />occurred between mountains and plains and were <br />most highly correlated with differences in stream <br />slope, specific conductance, water temperature <br />(Table 3) and surface water organic nitrogen + ammo- <br />nia and total phosphorus concentrations and to a <br />lesser extent to factors such as drainage area, altirude, <br />sinuosity, stream order, mean substrate size, and <br />ammonia, nitrite, and nitrate + nitrate concentrations. <br />As previously discussed, differences in invertebrate <br />communities among sites within the plains region <br />varied according to geomorphology and land-use <br />affects on nutrient concentrations. With the exception <br />of nitrate + nitrite concentrations, nutrient concentra- <br />tions in the hyporheic waters were not related to <br />the invertebrate community, McMahon et at, (1994) <br />reported that groundwater effects on surface-water <br />nutrient concentrations were related to a combination <br />of factors such as redox conditions of groundwater, <br />land use and proximity of site to sources of nutrients <br />in the South Platte River Basin, In British streams, <br />different environmental factors were useful in describ- <br />ing invertebrate communities depending on the spatial <br />scale examined (Furse et ai" 1984; Wright et aI., 1984), <br />For instance, substrarum characteristics, alkalinity, <br />total oxidized nitrogen (Le, nitrate + nitrite) were use- <br />ful in distinguishing invertebrate communities among. <br />rivers in Great Britain, whereas discharge, distance <br />from source, width, and depth were useful in distin- <br />guishing within river sites and slope and altitude were <br />useful in distinguishing within and between sites in <br />rivers, Quinn & Hickey (1990) reported that silty and <br />sandy substrates and recent severe flooding caused <br />low biomass and taxonomic richness; whereas catch- <br />ment development and related environmental factors <br />(Le, increased periphyton, increased water temper- <br />ature) had the most widespread important effect on <br />community composition, Corkum (1989) determined <br /> <br />" <br /> <br />'J <br /> <br />@ 1995 Blackwell Science Ltd, Freshwater Biology, 33, 439--454 <br />