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<br />UUUI n <br /> <br />The 1974 estimales bv Ffolliotl and Thorud are <br />based on low and high trealment options in three <br />vegetation types. Treatment in the mixed conifer <br />forests would convert to grass one-third to h.\'o- <br />thirds of Ihe area next lo stream channels. The low <br />option projection of 1.2 inches of increased water <br />yield from converting one-third of the area appears <br />consistent \vith the current estimate of 3 to 4 inches <br />from complete conversion, since response in this <br />vegetation Iype appears proportional to area <br />treated. However. the high option projection of 6 <br />inches from converting only two-thirds of the <br />forest appears overly optimistic. Treatment op- <br />tions in the chaparral would convert 40% and 60% <br />of the area to grass for increases of 1.2 and 2.4 <br />inches. These projections fall within the range of <br />current estimates of 1 to 5 inches for an area fullv <br />treated (the average on favorable sites is 3.8 inch';s <br />adinsted to 2.4 inches for onsite and offsile losses). <br />In ponderosa pine. the low option would clear <br />one-third in strip cuts for 1.2 inches increase, and <br />the high option would clear Iwo-thirds in strip cuts <br />for 2.4 inches increase. Th"se are slightly higher <br />estimates but not necessarily incompatible with <br />ClIffent unadjusted estimates. However. since the <br />ClIffent adjusted estimate of 0.1 to 1 inch is con- <br />sidered more realistic from a management <br />standpoint. Ihe water yield potential in ponderosa <br />pine is believed to be much less Ihan estimated for <br />the Lower Basin by the FfoIliott- Thorud study. <br />Further. the acreages considered suitable for <br />treatment in the F'foIliott-Thorud study may not be <br />available. since much of the ponderusi::t pine is in <br />poorly stocked condition. <br /> <br />Assessment <br /> <br />Amount of Additional Water <br /> <br />The amount of additional water that can be pro- <br />duced within a multiple use management concept <br />needs to be delermined. II can be theorized that the <br />maximum increase possible could be eslimaled by <br />multiplying tolal acreage times the unadjusted av- <br />erage increase for each vegetation type (tables 1 <br />and 2). If this were done in this study. some 4 <br />million acre-feel would be indicated for the Upper <br />Basin and about 2 million acre-feet for Ihe Lower <br />Basin. <br />However. this type of estimate ignores several <br />basic problems that cause aclual yield increases to <br />fall short of Ihe maximum potential. <br /> <br />1. Only a portion of each vegelation type could <br />be treated economically for water yield in- <br /> <br />creases. The amount depends on the demand <br />for water and ils value in the markel place. <br />2. Consideration of other resource values and <br />desires of the public tend to reduce both the <br />area that can be treated and the effectiveness of <br />treatments below that which could be ob- <br />tained if water yield was the main objective of <br />management. <br />3. The time frame required for water yield im- <br />provement practices to become fu lIy opera- <br />tional is probably in the order of several dec- <br />ades for commercial forests with timber har- <br />vest rotation ages of up to 120 years. However, <br />less time would be required for noncommer- <br />cial types. such as chaparral. <br /> <br />Thus. the amount of water that can be produced <br />hy vegelation management can best be quantified <br />in terms of a range of alternative management op- <br />tions that would include consideration of all fac- <br />tors above. <br />Another approach 10 assessing water yield po- <br />tential is to determine how much treatment would <br />be required to meet certain water augmentation <br />goals. For example. the proposed Yuma Desalting <br />Plant' on the lower Colorado River will produce up <br />to 42.000 acre-feet per year of highly concentrated <br />reject water. which would not be suitable for agri- <br />cultural. municipal. or industrial uses. The Lower <br />Basin states are unwilling to lose any water <br />through a desalting plant reject stream because of <br />anticipated future shortages. Therefore. the need <br />arises to augment the existing supply by 42.UUO <br />acre-feet to make up the difference. Although veg- <br />etation management may not be the appropriate <br />way to get the extra water. it is used here as an <br />example to illustrate the role that vegelation man- <br />agement could play in augmentation of the surface <br />waler supply. <br />The 42.000 acre-feet could be obtained by plac- <br />ing 250.000 acres of subalpine forests in Ihe Upper <br />Basin under management designed for water yield <br />improvement as a major objective. Or. the 42.000 <br />acre-feet could be obtained by converling 210.000 <br />acres of brush to grass in the Lower Basin. Larger <br />acreages in each case might need to be treated. if <br />water yield improvement practices should require <br />modification to adequately accommodate other re- <br />source values. <br />As a second example, suppose it became neces- <br />sary to augment the water supply of the Colorado <br />River by 750.000 acre-feet per year on the average. <br />with no restriction on where in the basin the water <br />should be generated. Since the Upper Basin yields <br /> <br />7Re/eet stream replacement study status report, January 1978, <br />102 P USDf Bureau of Reclamation. Lower Colorado Region, <br />Boulder City. Nevada. <br /> <br />22 <br />