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Relations of Main -Stem Reservoir Operations and Specific Conductance <br />in the Lower Arkansas River, Southeastern Colorado <br />INTRODUCTION <br />Two main -stem reservoirs on the <br />lower Arkansas River, Pueblo Reservoir <br />and John Martin Reservoir, are used to reg- <br />ulate and manage streamflow for irrigation <br />and domestic water supplies, flood control, <br />and recreation. Water storage and release <br />operations for these reservoirs can affect <br />streamflow and water quality of the down- <br />stream river. One water - quality property <br />that can be affected is specific conductance. <br />In 1996, the U.S. Geological Survey com- <br />pleted a study of the effects of Pueblo <br />Reservoir and John Martin Reservoir opera- <br />tions on specific conductance at five sites <br />located on the Arkansas River between <br />Pueblo Reservoir and Lamar (fig. 1). <br />This fact sheet presents an overview of <br />the study findings. A detailed discussion of <br />the study results is presented in Lewis and <br />Brendle (1998). <br />Specific Conductance <br />and Dissolved Solids <br />Specific conductance, in microsie- <br />mens per centimeter at 25 degrees Celsius <br />(gS /cm), is a property of water that is <br />attributable to salinity, or dissolved solids, <br />which is a measure of salts such as sodium <br />chloride or calcium bicarbonate. Pure water <br />has a very low specific conductance —a few <br />hundredths of a microsiemen per centime- <br />ter. As the dissolved - solids concentration <br />of water increases, the specific conductance <br />increases (fig. 2). <br />I.eadville 104° <br />105° <br />Granite <br />�1as° <br />103° <br />COLORADO <br />DENVER <br />i <br />1 <br />Study area <br />Colorado <br />Springs o f <br />ndy l` <br />Bue� • . �" <br />Vista <br />P <br />t Salida <br />CC tyn 102° <br />\ Pciala d S'Q.P Avondale n <br />John Martin Reserva' , <br />R� vofr Pueblo <br />�� e a <br />38 �orles Rl �� Nepesta Lam <br />S, Las Animas <br />La Junta <br />EXPLANATION <br />WATER - QUALITY <br />SAMPLING SITE <br />-- -L -1 -- <br />NEW MEXICO OKLAHOMA <br />25 50 75 MILES <br />0 25 50 75 KILOMETERS <br />Rgure 1. Location of study area. <br />U.S. Department of the Interior <br />U.S. Geological Survey <br />I <br />I <br />I <br />Specific Conductance <br />Can Affect Water <br />Suitability <br />High specific conductance indicates <br />high dissolved - solids concentration; <br />dissolved solids can affect the suitability <br />of water for domestic, industrial,,and agri- <br />cultural uses. The secondary maximum <br />contaminant level for dissolved solids in <br />drinking water is 500 milligra�rls per liter <br />(mg/L) (U.S. Environmental lfirotection <br />Agency, 1986). In the lower Arkansas <br />River, 500 mg/L of dissolved solids is <br />equivalent to a specific conductance of <br />about 700 to 800 gS /cm (Cain, 1987). <br />At higher levels, drinking water may have <br />an unpleasant taste or odor or may even <br />cause gastrointestinal distress. Additionally, <br />high dissolved - solids concentration can <br />cause deterioration of plumbing fixtures <br />and appliances. Relatively expensive <br />water - treatment processes, such as reverse <br />osmosis, are needed to remove excessive <br />dissolved solids from water. <br />Agriculture also can be adversely <br />affected by high- specific- conductance <br />water. Depending on the crop, agricultural <br />losses might occur when salinity reaches <br />700 to 850 mg/L (U.S. Department of the <br />Interior, 1994), which is equivalent to <br />a specific conductance of about 950 to <br />1,200 gS /cm in the Arkansas River (Cain, <br />1987). The salinity hazard of irrigation <br />water is a relation developed by the <br />U.S. Salinity Laboratory (Richards, <br />1954) that describes the qualitative effect <br />of saline water on irrigated crops. The <br />hazard is based on the specific conductance <br />of the water and is divided into four classes <br />of salinity hazard ranging from low (less <br />than 250 gS /cm) to very high (greater than <br />2,250 g6/cm). As specific conductance <br />increases, special agricultural management <br />practices may be needed, and crops having <br />a substantial salinity tolerance may need <br />to be grown. Generally, crops with a <br />higher salinity tolerance have a lower <br />market value than more salt- sensitive <br />crops (Miles, 1977). <br />USGS Fact Sheet 166 -97 <br />July 1998 <br />