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<br />i-' <br />C'() <br />C) <br />OJ <br /> <br /> <br />To control turbidity problems, the Illinois project targeted natric soils with <br />2 percent slop~, fine particle size ,and high erodibility, and non-natric soils <br />with 5 percent slope, high erodibility, and proximity to the stream system. <br />The Louisialila RCWP addressed turbidity, sedimentation, and pesticide' <br />problems by tatgetlng cropland adjacent to the water body. Cotton growing <br />on silty solis h/ld highest priority because the fields are close to water- ' <br />bodies, Intensiyely cultivated, and require pesticides and nutrients. This <br />project also offbred high cost-share rates (gO percent) to farmers located <br />adjacent to Bayou Bonne Idee to increase participation in the critical area. <br />In addressln,g eutrophication problems in St. Albans Bay, the Vermont <br />RCWP targeted areas nearest major water courses or the bay where major. <br />rionpolnt sourc&s of phosphorus were present. The project has also used' <br />SCS computer: models to estimate the total phosphorus and sediment <br />loads from altemative management scenarios. The portion of the total load <br />that needs to bb controlled by agricultural BMPs, is designated as critical, <br />. and progressii; then evaluated in terms of the amount of critical load <br />treated with BM,Ps. <br />Water qualitY problems in the Oregon RCWP result from high fecal <br />coliform levels ,and sediment loading to Tillamook Bay. This project tar- <br />geted land with, high priority dairies. Priority levels were based on a point <br />system that considers distance to open water course, manure manage- <br />ment practices:number of animals, and location. <br /> <br />. A project's t!meframe should Include a pre-Implementation assess- <br />ment period: 1\1 addition to identifying the water use impairments, the as- <br />sessment should (1) identify and quantify all pollutants, and their major <br />sources; (2) asbertain the surface and ground-water hydrologic regimes; <br />(3) identify, quatltify, and target critical areas; (4) establish a list of suitable <br />BMPs; and (5) petermine the benefits from improving or maintaining the <br />water quality. Such an assessment will help ensure that project funds are <br />used efficiently. <br />Some RCWP projects with insufficient assessment Information had to <br />redefine their otiginal critical area two to three years after the program <br />began. Minnesota, for example, changed its focus from surface water to <br /> <br />OJ' <br />:1 <br /> <br />fi <br /> <br />Testing the soli is key to Its nutrient <br />management. <br /> <br />J <br />j <br />, <br />. <br />':j <br /> <br />:1 <br />., <br />" <br />-:~ <br />'J; <br />'j <br /> <br />" <br />.j <br />, <br /> <br />'" <br />. :~ <br /> <br />,) <br />. <br />" <br /> <br />'~ <br /> <br />.--i <br />--"j <br />J <br />..j <br />",:: <br /> <br />, <br />, <br />',1 <br />; <br />, <br /> <br />. <br /> <br />I <br />, <br />, <br />::: <br />., <br />~ <br /> <br />Targeting Criteria <br /> <br />Criteria to use In ranking critical . <br />area treatment needs: <br />(1) the magnitude of the pollutant <br />source; <br />(2) distance to the water resource; <br />(3) location, type, and severity of <br />the water resource Impainnent or threat; <br />(4) the type of pollutant; <br /> <br />(5) present conservati9n status;:and <br />(6) on-site evaluation. <br /> <br />., <br />, <br />1{ <br /> <br /> <br />. ,(j <br />. <br /> <br />J <br /> <br />o <br /> <br />,'I <br /> <br />:~- <br />;'i <br />, <br /> <br />1 <br />, <br /> <br />7 <br /> <br />-f <br />f <br /> <br />, <br />, <br />il <br />