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Last modified
7/14/2009 5:02:30 PM
Creation date
5/17/2009 11:16:55 PM
Metadata
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UCREFRP
UCREFRP Catalog Number
7729
Author
Valdez, R. A., W. J. Masslich and A. Wasowicz.
Title
Annual Summary Report - 1990\
USFW Year
1991.
Copyright Material
NO
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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 />In addition to water quality samples for laboratory analysis, field measurements were taken for <br />conductivity, salinity, pH, alkalinity and dissolved oxygen. Water quality data collected afield are <br />presented in Table 29. <br /> <br />Alkalinity <br /> <br />Alkalinity is a measure of the buffering capacity of water. Buffering capacity is important to water <br />quality (EP A 1986) since pH has a direct effect on organisms as well as an indirect effect on the <br />toxicity of certain other pollutants. Alkalinity in the Dolores River was moderate, ranging from 92.1 <br />on Trip 3 to 165.5 mg CaCOJL on Trip 1. Overall, alkalinity was slightly higher on the first trip than <br />the following two trips, probably due to base flow conditions. Samples from individual trips showed <br />little difference between study reaches. Historically, alkalinity levels in the Dolores River near Slick <br />Rock in 1960 were similar to levels found in 1990 (United States Public Health Service 1961). <br />Alkalinity levels in the San Miguel River just above the Dolores River confluence are slightly higher <br />than in 1960. The EP A Criteria for freshwater aquatic life for alkalinity is a minimum of 20 mg <br />CaCOJL except where natural concentrations are less. <br /> <br />Hardness <br /> <br />Water hardness varied from 138.5 to 912 mg CaC03/L, both values taken from Trip 2. Although <br />hardness varied substantially between reaches, no distinct trend was apparent. High values during <br />Trip 2 may reflect a high noncarbonate hardness fraction, since alkalinity levels were relatively low <br />for the same samples. Values did not differ greatly between trips although, again, the variance was <br />large. Dolores River water is classified as moderately hard to very hard based on the classification <br />used by Sawyer (1960). In 1960, water hardness ranged from 760 - 2200 mg/L around the Slick Rock <br />area, and went as high as 2,360 mg/L above the mouth of the San Miguel River (USPHS 1961). <br />Water hardness in the San Miguel just above the confluence decreased from 900 mg CaC03/L in 1960 <br />to 528 mg/L on Trip 3 in 1990. The effects of hardness on freshwater fish and other aquatic life <br />appear to be related to the ions causing the hardness rather than the hardness itself, therefore no <br />EPA criteria exists (EPA 1986). <br /> <br />pH Units <br /> <br />Values for pH varied only slightly, from 7.67 on Trip 2 to 8.45 on Trip 3, with most values close to <br />8.3. No distinct trends or differences were apparent between trips or study reaches. In 1960, <br />measurements of pH levels in the Slick Rock area and around Gateway never exceeded 8.0 and went <br />as low as 7.5 (USPHS 1%1). The pH of the San Miguel River near the confluence was 8.45 in 1990, <br />compared to 7.6 in 1960 and pH values as low as 4.3 were measured in the main channel several <br />miles below Uravan. Effluent with a pH as low as 2.3 was being discharged into the San Miguel <br />River from a Uravan uranium mill in 1960. A review of the effects of pH on freshwater fish by the <br />European Inland Fisheries Advisory Commission (1969) found the pH ranges (5 - 9) not directly <br />lethal to fish. However, the toxicity of several common pollutants is markedly affected by pH changes <br />within this range, and increasing acidity or alkalinity may make these poisons more toxic (EP A 1986). <br />The EP A criteria is set at 6.5 - 9.0 for freshwater aquatic life. <br /> <br />16 <br />
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