Laserfiche WebLink
<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />1. Fairly distribute its water resources and the risk ofreduced water availability <br />among its members; <br /> <br />2. Sustain its revenues (even during periods of drought) to meet loan payments; <br />and <br /> <br />3. Develop a well monitoring and control program that insures compliance with <br />mandates that is administratively feasible for LA WMA and acceptable to the <br />Colorado State Engineer. <br /> <br />In general, LA WMA desires an operating structure that is fair, has maximum flexibility <br />for both LA WMA and its members to deal with risk and contingencies, promotes <br />efficient use of water, reduces unnecessary depletions and is administratively feasible. <br /> <br />Pumping vs. Depletion vs. Replacement ~' <br /> <br />Pumping of groundwater by LA WMA members impairs Arkansas River flow, but the <br />relationship between plllTIping and the impact on the river is complex. It is important to <br />note however that replacement water for impaired river-j/ow is the major cost factor for <br />LAWMA. To achieve water efficiency and fairness, pumping by individual members <br />should be directly related to this cost factor. It may not be feasible to rate every well by <br />the amount of replacement water it requires for otfset. As an alternative, we have related <br />assigned depletion factors of wells to the amount of replacement water as follows: <br /> <br />I. Pumping vs. depletion: The amount of depletion is related to pumping by factors that <br />vary among users. LA WMA has four types of agricultural irrigators: tributary, <br />supplemental, sole- flood, and sole-sprinkler. Commercial and municipal water users <br />are excluded from this analysis because they already have their own offsetting water <br />rights. Depletion factors are the fraction of groundwater depletion associated with the <br />level of pumping. Total depletion is estimated at 29,997 afin a normal year and <br />39,992 af in a dry year. <br /> <br />2. Pre-compact plllTIping allowances and other modifications reduces the impact on the <br />river from groundwater depletion. Based on these adjustments, we use a factor that <br />reduces the amOlll1t of depletion to the level necessary to protect senior rights and <br />compact obligations. From analysis by Helton & Williamsen, P.C. the amount of <br />replacement water for a normal year is 18,049 af The replacement factor is calculated <br />as (18,049/29,997= 0.602) in a normal year and as (24,435/38,992 = .627) in 1st and <br />2nd dry years. <br /> <br />3. The adjustment for plllTIping to depletion to replacement is indicated in Table I. 1bis <br />is a table of pumping demands (desired levels) by the different type of irrigators. <br />Associated with desired pumping are the amount of depletion and the amount of <br />required replacement water. Note that in a dry year, pumping demand increases <br />substantially among supplemental users. These users would increase pumping to <br /> <br />EnWater Resource Consultants September 5,1997 Final Report <br /> <br />14 <br />