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<br />I <br /> <br />I <br /> <br /> <br />. <br />I <br />- <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I, <br /> <br />I <br /> <br /> <br />I <br />I <br />I <br />I <br />.' <br />. <br /> <br />Impact of Tamarisk Infestation on the <br />Water Resources of Colorado <br />May 3D, 2003 <br /> <br />3.0 Non-Beneficial Water Use <br /> <br />Consumption of water by tamarisk is the unifying issue that brings diverse groups ofpeople to <br />agree that there may be a need to control this invasive plant. Environmental organizations, <br />government agencies, conservation groups, ranchers, landowners, sportsmen, and others who <br />often times have been at odds on other issues seem to be willing to work together because of the <br />non-beneficial use of water by tamarisk. For this study, the term "non-beneficial water use" is <br />defined as the difference in water consumption (evapotranspiration) between tamarisk and the <br />native plants it has replaced. <br /> <br />Water Usage by Different Vegetative Types <br /> <br />Limited evidence indicates that water usage per leaf area of tamarisk and the native <br />cottonwood/willow riparian communities may not be that different. However, because tamarisk <br />grows into extreme thickets, the leaf area per acre may actually be much greater; thus, water <br />consumption would also be greater on an acre basis (Kolb 2001). Probably the most insidious <br />aspect of tamarisk and its consumption of water is that its much deeper root system (up to 100 <br />feet compared to healthy cottonwoods and willows stands at 6 feet (Baum 1978, USDI-BOR <br />1995)) allows tamarisk to grow further back from the river and thus can occupy a larger area and <br />use more water across the floodplain than would be possible by the native phreatophytes. This is <br />especially significant, because the adjacent uplands and floodplain typically occupy a cross- <br />sectional area several times that of the riparian zone. In these areas, less dense areas of mesic <br />plants (such as bunch grasses, sagebrush, rabbit brush, skunk bush, and greasewood) can be <br />replaced by tamarisk resulting in overall water consumption several times that associated with <br />these other plants (DeLoach 2002). <br /> <br />From thirteen different studies conducted between 1972 and 2000 on tamarisk evapotranspiration <br />rates, the average water use reported is approximately 5.3 feet per year (Hart 2003). More recent <br />work performed on the Pecos River in Texas over the last three years indicates water use by <br />tamarisk of 7.7 feet per year (Hart 2003). Recent research by the U.S. Department ofInterior on <br />the middle Rio Grande estimates evapotranspiration rates on the order of 4.3 feet per year <br />(Interior 2003). These studies were performed using different methods of measurement, at <br />different locations, and Dr different densities of infestation. Native cottonwood/willow <br />communities have been estimated to use approximately one foot less per year than tamarisk <br />(Weeks, 1987) while the native shallow-rooted upland plant communities of grasses, sage, etc. <br />use only the moisture received by precipitation. Unpublished research on the Bosque del Apache <br />National Wildlife Re fuge on the middle Rio Grande River in New Mexico indicates that <br />Russian-olive has very similar evapotranspiration rates as tamarisk (Bawazir 2003). <br /> <br />Estimates of Non-Beneficial Water Use in Colorado <br /> <br />Estimates on water consumption by tamarisk vary a great deal depending on location, maturity, <br />density of infestation, and depth to groundwater. This will also be true for the <br /> <br />15 <br />