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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
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