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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />Dissolved Oxvgen <br /> <br />Dissolved oxygen was measured at 10 locations in the Dolores River during Trip 3 and ranged from <br />6.5 to 8.1 mg/L. EPA's standards for non-salmonid waters fisheries are 6.5 mg/L for early life stages <br />and 6.0 mg/L for all other life stages. <br /> <br />4.4 Macroinvertebrates <br /> <br />Results of macroinvertebrate sampling in the Dolores River in 1990 are presented in Tables 33-35. <br />During Trip 1, 86.3% of all macroinvertebrates sampled were Dipterans, mostly from the family <br />Simullidae. Composition from other orders never exceeded 10% of the total sample. Three orders <br />dominated the sample composition from Trip 2; Trichoptera, Ephemeroptera, and Diptera at 39%, <br />30.2% and 22.4% respectively. Dipterans comprised 55.5% of all samples on Trip 3, followed by <br />Trichoptera (22.3%) and Ephemeroptera (12.7%). The composition of macro invertebrates shifted <br />gradually downstream through the sample reaches. Most insects sampled in the lower reaches were <br />of orders Trichoptera (mostly Hydropsychidea), Ephemeroptera and Diptera (mostly Simuliidae), <br />comprising 40.2%,28.7% and 25.6% of the total, respectively at the lower most sampling site (RM <br />1.2) and 26.5%,38% and 28.7% respectively at the next lowest sampling site (RM 59.7). Dipterans <br />dominated samples taken from above this point. Composition of Dipterans as a percentage of the <br />total samples for collections at RM 64.4-64.6 and RM 122.6 were 56.5% and 70% respectively. Over <br />90% of all insects collected in the San Miguel sampling station were Dipterans. <br /> <br />Crayfish (Orconectes virilis) were also abundant in the Dolores River. This cructacean is a potential <br />predator on young fish. Crayfish densities appear to increase in upper portions of the study with very <br />high localized densities. Beck (1989) reported mean catch rates of 31.8 crayfish/trap day near <br />Bradfield Bridge and 3.3 crayfish/trap day immediately below Disappointment Creek in 1989. <br /> <br />5.0. PRELIMINARY FINDINGS <br /> <br />1. Colorado squawfish, humpback chub, bonytail and razorback sucker were not encountered in the <br />Dolores River in 1990. Non-native fish comprised 83.8% of the total catch. Native species comprised <br />13% of the total catch. Red shiner was the most common fish captured. <br /> <br />2. Channel geomorphology appears to provide physical attributes suitable for spawning, adult juvenile <br />habitat and limited nursery habitat. <br /> <br />3. Flow may limit use by Colorado squawfish; McPhee has reduced spring flows but may supplement <br />base flow; reduced spring flows are allowing silt accumulation that may eventually armour the <br />substrate; lack of flushing flows may allow parasites to proliferate. <br /> <br />4. Water quality is unknown, but increased elements during stochastic events indicates toxic <br />substances remain trapped in muds and tributaries. <br /> <br />5. Non-native fishes outnumber native fishes and competition and predation is a problem. <br /> <br />20 <br />