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<br />r,t <br />q, <br />,,'" <br />~.l. <br />~';1' <br />.~.~. <br />~'--~ <br /> <br />1fj <br />~]; <br />~;.:,'J. <br /> <br />'f,::l <br />.;1 <br />iJ <br /> <br />r~ <br />':-.~ <br /> <br />.f~j <br /> <br />..~ <br />h <br />~"~J <br /> <br />i:~'71 <br />i~ <br />~..j <br /> <br />,:.,:.~ <br /> <br />, <br />E~ <br /> <br /><eel <br />,'f..,L <br />t;,:1 <br /> <br />~;;;:;. <br />~. ; <br />:;. _:~ <br />i.2j <br /> <br />;';/,:.' <br />ii~ <br />,'. <br /> <br />f"l <br />~, <br />kJ <br /> <br />p <br />i;,Z1'" <br />''" <br />~' <br /> <br />~~;l <br /> <br />;" <br /> <br />". <br /> <br />Ditch <br />s stem <br />Gran V1ew <br />Crawford Clipper <br />Needle Rock <br />A1 <br />A2 <br />Aspen Canal <br />Aspen Canal <br /> <br />Hydrosalini ty <br /> <br />Reclamation's study of the SSA began in February 1985 with initiation of <br />a monitoring program to define surface inflow and outflow water quality and <br />quantity. To determine the base flow salt loading, a base flow separation <br />technique was applied. <br /> <br />CHAPTER II <br /> <br />Ditch <br />system <br />Grand View <br />Crawford Clipper <br />Needle Rock <br />A1 <br />A2 <br />Aspen Canal <br />Total <br /> <br />PIAN FORMULATIOO <br /> <br />Table 3 <br />Irr~ation system analysis <br />Wi in SSA <br /> <br />outside SSA <br />canal Lateral <br />length length <br />(feet) (feet) <br />48,396 <br />7,734 18,470 <br /> <br />Acres <br />served <br />l67.0 <br />237.9 <br /> <br />Canal <br />length <br />(feet) <br />39,357 <br />21,597 <br />31,900 <br /> <br />Lateral <br />length <br />(feet) <br />35,265 <br />222,488 <br />38,425 <br />7,950 <br />4,605 <br />2,640 <br />311,373 <br /> <br />404.9 <br /> <br />Acres <br />served <br />l,943.8 <br />3,165.l <br />1,193.7 <br />218.5 <br />138.9 <br />N/A <br />6,660.0 <br /> <br />5,900 <br />62,030 l8,470 <br /> <br />30,100 <br />l22,954 <br /> <br />Table 4 <br />Field inventory data <br />Measured Design <br />divefsion size <br />(ft s) (afl30 ac) <br /> <br />Record <br />source <br />Measure <br />Smi th Fork Report <br />Water Right <br />Measured <br />Measured <br />Smi th Fork Report <br />Smi th Fork Report <br /> <br /> <br />, . . <br />3,403.0 157.0 2.74 <br />1,l93.7 41.3 2.06 <br /> 2l8.5 22.0 5.99 <br /> 138.9 9.2 3.94 <br />5,974.3 l25.0 <br />1,l93.7 25.0 1.25 <br /> <br />Seepage losses from off-farm delivery systems were determined from <br />permeability data contained in the smith Fork project Definite plan Report and <br />winter and summer wetted perimeter estimates. <br /> <br />This data resulted in a range of estimated seepage rates of 0.27 to <br />0.41 feet per day, with an average of 0.38 feet per day. Seepage losses from <br />on-farm delivery systems were estimated using SCS data consisting of a 0.47 <br />foot-per-day seepage rate, head and tailwater ditch wetted perimeters, and <br />ditch lengths. <br /> <br />Deep percolation was estimated from SCS data that indicated a possible <br />range of 0.8 to 1.5 acre-feet per acre per year. Infiltrated precipitation <br />estimates developed by the SCS ranging from 9.23 to 12.22 inches per year were <br /> <br />also used to define ground-water inflow. using this data, the maximum <br />possible ground-water inflow to the SSA was determined to be 33,500 acre-feet <br />per year. <br /> <br />12 <br /> <br />00C038 <br />