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<br />~> <br />(" <br />~~. <br /> <br /> <br />~,"!, <br />",., <br />" <br />;,. <br /> <br />~'J <br />;i.;..j <br />;',. <br />~.l <br /> <br />P <br />.,J <br /> <br />.~ <br />}.1. <br /> <br />tJ <br /> <br />t',~ <br />~"l <br />i~ <br /> <br />~l <br /> <br />~~) <br />r1 <br /> <br />f:'l <br />q <br />t~ <br /> <br />f>l <br />'"'' <br />l;..;j <br />~;j <br /> <br />,1.'^.e.l <br />q <br />~:J <br /> <br />1'1 <br />li'" <br />I>:i <br /> <br />~ <br />~~-~ <br />"3 <br /> <br />~,~ <br /> <br />CHAPTER II <br /> <br />PIAN FORMULATIOO <br /> <br />Water quality samples collected over the period March 1976 to <br />October 1983 from four natural drainages wi thin this reach were used to <br />conduct the analysis. These drainages are Alkali Creek, an unnamed gulch <br />1/4 mile west of Dieter Gulch, Dieter Gulch, and Dry gulch. To estimate the <br />base flow concentration associated with these drainages, water quality samples <br />taken during the nonirrigation season of November through March were evaluated <br />to determine average TOS values. <br /> <br />The samples from Alkafi Creek were taken during periods of low flow <br />ranging from 0.1 to 0.3 ft Is and exhibited an average TOS value of <br />approximately 4,200 mg/L. This quality is considered to be representative of <br />the drainage's natural base flow condition. <br /> <br />A wide range of flows from 0.1 to 17.7 fe Is occurred in the unnamed <br />gulch durin~ the collection period. However, for periods where flow was less <br />than 1.0 ft Is the water quality values ranged from 2,940 to 5,960 mg/L. <br />These qualities are likely to be representative of this drainage's base flow <br />condition. <br /> <br />The flow weighted TOS of 2,917 ~/L for Dieter Gulch is based on a narrow <br />range of low flows from 0.2 to 0.4 ft Is. This value is based on a narrow <br />range of samples but appears to be significantly lower than the concentrations <br />for the other drainages in the reach. <br /> <br />The flow weighted TOS of 5,377 ~ for Dry Gulch is based on samples <br />taken within a range of O.l to 1.5 ft Is range from 2,100 to 10,900 mg/L and <br />are the highest observed for the four sampling locations in this reach. <br /> <br />None of the Alkali Creek drainage area, and only small portions of the <br />area in unnamed gulch, Dieter Gulch, and Dry Gulch are located below the canal <br />systems. Therefore, observed TDS concentrations are likely to be indicative <br />of natural salt loading conditions and not salt loading due to canal seepage. <br /> <br />The SCS soils map shows that the majority of the land above the North <br /> <br />Delta Canal is located on soils classified as Badlands. Badlands soils <br />consist of nearly barren outcrops of gypsiferous and saline shale with some <br />soil material. The mapping also shows that the majority of irrigated land <br />occurs on Billings silty clay loam which is deep, well drained, and moderately <br />fine textured. The Billings soil is a grassland type formed on alluvial fans <br />washed from adjacent exposures of gray and olive shale and siltstone. This <br />distribution of soils appears to support the assumption that the observed TOS <br />in this reach of the Gunnison River are due primarily to natural loading <br />conditions. Therefore, North Delta canal and lateral lining was dropped from <br />further consideration. <br /> <br />Colona area winter water replacement <br /> <br />Area Description <br /> <br />The Colona area is located approximately 3 miles south of the city of <br />Montrose, in Montrose and ouray Counties. Irrigation and winter stockwater <br />deliveries are provided by ten private ditch systems. The systems serve <br />approximately 6,600 acres of irrigated land. The ditches are the Heiland, <br /> <br />15 <br /> <br />001"941 <br />