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<br />OOf\71? <br /> <br />soils. Thctl\'erallaverage is 1 inch or slightly more: <br />the lower. drier sill's produu'! very Iillle. while the <br />well est sites ma~' yield 3 or"\ inches. <br />The putential for increasing stte<imno\\' by type <br />conversion of chaparral is guud on favorable sihtS <br />where precipitation averages 20 inches or more <br />(Hibbert et 011. HI74). Thl'! key to increasin~ waler <br />yield is the replacement uf dt!ep-rooted shruhs <br />with shallo\\'+toolt!d grasses and forb!'! that use less <br />waler. The ollsite inCft!8ses determined from ex- <br />perimentallype conversions on small watersheds <br />range from Ipss than 1 inch to mtire than 5 inches <br />lfig. 1 ~)). The i1\"erage is 3.8 inches at 22 inches <br />precipitation. Some discounting is in orriN hcfoft' <br />extrapolating the ftlsearch results to larger areas <br />where cunversion ma\" not be as intensive, con- <br />tinuous, or as well maintained as on the experi- <br />mental watersheds. Moreover. some of the in- <br />creased llow may be lost to riparian \'egetation <br />downstream before it reaches storage or points of <br />use. Therefore. the a\'erage increase expected <br />downstream from type cOl1\'ersion is estimated to <br />be about hvo-thirds of the onsite increase, or 2.4 <br />inches where precipilation is 22 inches (con- <br />sidered average for treatahle chaparral). Other con- <br />siderations will limit tht~ amount of type com'cr- <br />sian to a fraction of the tolal acreaKe. <br />Of the 1.8 million acres of chaparral on National <br />Forest lands. more than 200,UOO acres are in wil- <br />dt~rness and other special use areas. where conver- <br />sion is not compatible \'vith pft~sent land use pol- <br />icy. A much larger portion. nearly 40% of the re- <br />maining chap<-lrral. is considered too dry and open <br />(crown COVHr less than 30'''0) to be a KOOtI risk for <br />waler vield impron~menl. Also. much of the <br />chapar~al is nil excessi\'ely steep slopes. In a sludy <br />of chaparral con\'ersion potential on National <br />Forest lands in the Salt-Verde Basin above <br />Phoenix. Ariz. IT. Brown et al. 1974). about 10% of <br />otherwise treatable chaparral was on slopes <br />steeper than fiO'....... which was the upper limit con- <br />!'iitiered safe for conversion. Ilowever. some land <br />managers fed that the 60% !'ilope criterion is too <br />steep for practical field application, and that the <br />upper limit should be 50%, or t!\'en ..HJ%. Sinct! <br />approximately 40% of the chaparral is on slope!'i <br />between 40U" and 60%. the steepness at which <br />conversion call be safely accomplished is ex- <br />tremel\' important. Approximately 20% less area <br />would 'bt' available for conversion if the maximum <br />operable slOlH' is lowered from 6001;, to 50%. and <br />another 20% of acrt'agl' would he lost belween 50% <br />and ..0% slope. A]so. substantial acrea!,:es may be <br />excluded for treatment. or gi\'en low priority. be- <br />cause of opt'rational rt'striclions or ~l.'{)graphic ]0- <br />cation. such as chaparral on !'ilopc!'i of isolated <br />mountain ranges. wht.rt~ an increast' in waler <br /> <br />8 <br /> <br /> <br />. <br />}' <br />u <br />= 6 <br />. <br />E <br /> <br />T fealed <br /> <br />E <br />0 . <br />. 38 inch <br />;;; <br /><; lncr~$e <br />, <br />< <br />< 2 <br />0 <br />< <br />0 <br />. Natural <br />~ <br /> 0 26 <br /> 16 18 20 22 2' <br /> Mean annuat precipitation (Inches) <br /> <br /> <br />Figure 19.-Average water yIeld from naluraland converted <br />Chaparral Is a function of precipitation. Difference be- <br />Iween lines Is aUribUled 10 Ireatmen! (Hibbert el al. <br />1915). <br />wou]d he of questionable value. Therefore. buth <br />the t acre in 5 estimate for treatable chaparral and <br />the 2.4-inch water yield increase projp.clion proba- <br />bly would be cunsidered th!t most optimistic po- <br />tentials allainable by large-scale management ef- <br />forts ill the chaparral. <br />Further. use of the arithmetic a\'erage to dl>scrihe <br />annual water yield potential can he misleading, <br />bl~r:ause this vahlt' (2.4 indws in this casl~) will not <br />hI! equalled or p.xcet~ded 511% of the years as would <br />occur if precipitation and rUIloff were normalJ~' <br />distributed. In Ihe chaparral of C(mtral Arizona, <br />precipitation is less than averagl' about 58"/0 of the <br />\lears. Since runoff increases exponentially with <br />im:cipitation. yearly runoff amounts are skewed <br />ever farther to the tir... side of the distribution <br />curve. Wet years tend t~ yielti many tinws as much <br />water as dr\' unes. Thus. l!\'en though precipitation <br />Hxceeds th~ mean in nnl\' aboul4 \lears in 10. more <br />than 80% of the water vield increases are produr:ed <br />in these weller tha'n aVl!ragn :'.'ears. Storage <br />facilities are imperative to get full benefit of in- <br />creastld water \lields in wet vears. To the extent that <br />downstream s-Iorage capacity is exclleded {which <br />happened 7 times in lhe past 50 years in the Salt- <br />Verde Basin above Phoenix) and willt'r is spilled. <br />runoff increases from conversion would b(~ lost to <br />the full extent of the release, assuming no further <br />beneficial use could be made of the water down~ <br />stream. <br /> <br />~ <br /> <br />~1ountain Brush <br /> <br />~lountain brush lands (fig. 201 are exh'nsi\'e only <br />in the Upper Basin. where they are found on about <br /> <br />15 <br />