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- Surface And Groundwater Interactions In Coalbed Methane Waters <br />In The Powder River Basin, Wyoming <br />by <br />John D. Stednick <br />(Department of Forest, Rangeland, and Watershed Stewardship, Colorado State University) <br />and <br />William E. Sanford <br />(Department of Geosciences, Colorado State University) <br />Coalbed methane (CBM) gas is formed in confined coal - <br />bed aquifers through biogenic processes and remains <br />trapped in coal fractures by overlying water pressure. <br />Pumping water from the coalbed aquifer decreases the <br />water pressure and allows methane gas to be released, <br />collected and subsequently distributed via pipelines. It <br />is estimated that a single CBM well in the Powder River <br />Basin (PRB) produces from 2 to 40 gallons of water <br />per minute, but varies with the aquifer pumped and the <br />density of wells. Approximately 0.6 trillion gallons of <br />product water eventually will be produced from CBM <br />extraction in Wyoming (DeBruin et al., 2000). <br />The variability of water chemistry produced by CBM <br />wells in the Powder River Basin is not clearly under- <br />stood. In general, the total dissolved solids in CBM dis- <br />charge waters increases <br />from the southeast to the <br />northwest in the Powder <br />River Basin as deeper <br />coal seams produce more <br />saline and alkaline waters <br />(Rice, 2000). CBM ex- <br />traction wells are placed <br />together in a manifold <br />system discharging to a <br />single point and releas- <br />ing often into ephemeral <br />stream channel systems, <br />constructed unlined <br />wellhead downstream in ephemeral stream channels <br />and to examine surface- groundwater interactions. We <br />collected CBM discharge water samples from discharge <br />points and analyzed for pH, major element concentra- <br />tions, and calculated the sodium adsorption ratio (SAR). <br />High SAR levels can increase the soil salinity, increase <br />the soil pH, decrease infiltration rates, and decrease soil <br />productivity. These parameters were analyzed in sur- <br />face and shallow groundwater samples collected down- <br />stream of wellhead discharges to determine changes in <br />CBM discharge water. <br />The coalbed methane discharge waters are generally <br />alkaline, high in sodium (Na) and bicarbonate (HCO3) <br />concentrations (Table 1). The chemical composition <br />of the discharge waters did not vary over time, similar <br />to other PRB studies (McBeth et al., <br />2003). Mean pH increased from 7.4 <br />to 8.8 in the stream from precipitation <br />of calcite, with a decrease in calcium <br />retention ponds and /or, <br />re- injected to the groundwater, or recently treated on site <br />to reduce salinity before discharge. A careful evaluation <br />of CBM chemistry to better determine potential uses of <br />CBM produced water and the ability to maintain state <br />water quality standards is needed. <br />The objective of this study was to examine CBM <br />discharge water chemistry as water moves from the <br />6 <br />and increase in sulfate. The decreased <br />calcium increased the SAR. In gen- <br />eral, the water chemistry of the surface <br />water sampled at different points down- <br />stream did not vary, but differences in <br />groundwater chemistry were observed. <br />Discharge and surface waters are a Na- <br />HCO3 type water. <br />Groundwater chemistry as sampled at <br />2 and 4 foot depths, near the channel, <br />showed significantly higher concentrations of all salts. <br />Sodium concentrations in particular tended to increase <br />with soil depth, and are a Na -SO4 type water. As the <br />wellhead water is discharged into the channel, water <br />soluble salts are being dissolved and leached laterally <br />into the soil. Once the channel discharge decreases or <br />is stopped the soil reservoir of salts will migrate back <br />to the channel. This process has been confirmed when <br />