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<br />,'12/~7j92 14;~2 <br /> <br />'&303 945 $799 <br /> <br />COLO RIVER DIST ~~~ USFWS RIP DNVR <br /> <br />Ffsan 2 shoM the peak fioWfrequency ~ (best fit and 95 percent confidence (nl:eMI) fQr <br />the period fmm 1953 to 1990 at the Gr&ilh HlVer gage. Depending on the n wIue used (0.03 or 0.035) <br />;at; the CQII:cnwocd BdtDm reach. the bankfuD timcharge has 8 frequency of 25 to 28 percentwhicb at!: <br />eqUi\laJent to return J:*fods rJ between 4 and 5 years. At Unknown BoUcm. depencrq on the n wlue <br />used (0.03 IX' 0.035). the bankfull dischalge. W a frequenc.y d 14 to 20 per=r4 \'Vhlch ere equIvalent <br />to r-.m pIVIcxIs,af between 5 and10~..Jn contrHt. Figure 3 shews the peak flow hquancy <br />CUN8J (bOstftt One ar1dB5 percent canfic:Ience"intel'M) for U1EI pertxI frcm 1894 to 1Q62. Dependtng <br />OD the ,.n varue.used lO-03 or OJl35) ..th8 CQII:cnwocd Bottom IWCh,If1e IxmkfuIl cflSCharge tw;l <br />frequenGyof 60 to 58 percentwhtch ana equIvalent to . relum pWiocf d ~ 2 years. N.lJnIcnoWn <br />Botkxn the ban1cftJII dTscharges have freqUendes from 36 to 50 percent whlch are equfwlent 10 reIum <br />periods of2 to 3 years. . '.'. <br /> <br />The frequenq and retum pedact. data obviousfy do not "* any allowance for ch9nnel <br />morphdoglc Changes that may ~ tM;Ien ~ by the e$labrsshment of tamarisk (Gear, 1978). If tn <br />fad: Onts 'interpretation is correct, the frequency of overbank flows wauld haVe been loWer priorta 1118 <br />edvent of ~ . . <br /> <br />3) <br /> <br />Haf:lifat UtiIimtian Potential <br /> <br />Hkltorfcal fish catch d:rta Indic:ite that juvenilv. Colorado Squawfi!:h are abuhdant In the lower <br />Greerl RIver (G. Smfth, USFWS Memo. to Channl'1.d Manitat'ing Crew. 1992) which tends to suggest that <br />thel'9 Is adequate fuv;nle ~ In the reacl1. <br /> <br />Since the CoIcndo sqrmwfish'8pilMl all the recessional limb or the ~ hytI~ (Tyus <br />and Karp. 1989). and the larvae are distributed dcwnsb'eam by drift it is poss1b1e that the rnocfification <br />dthe IIowdur.Jtion cwve (seeArfjrews. 1985) has had an Impact an the JaMJ c1rift:distJnce. Squawfi!h <br />are kncwn to $pawn in canyoh-bound reaches of the lower Yam,. River (Tyue end ~, 1989) and in <br />Desolation C'.nyon (E. WICk. pelS. ccmrnunfcation) onthaGreen River. Ifthetimtng oflmwl emergence <br />coincides with the longer duration tn'id-rarlg(;l ft(l'lNt;, the larvae co1Jd in fact be mnied farther <br />downGtI'rmm than wautd have or:.curred picrto flaw regulation.. With a ~cwer channel, 'the flow depth <br />for a ~e of cIIsd14lrge$ foIJCNling larval emero~nce wm: be hIgher 8IU It Is ttlerefore conceivable that <br />there Will be lest sI8ckwat<< h-:lbif4lt fer the Imvae. Because of !he magnitude of the bBnkfuII capacii;y <br />and1he fad thal: sqtJaWlmh 9~. &ft&r' the",enk dJsc:harge.. out-ot'-bank hsbftat will rarely. If ~ be. <br />awiIabIe to larval squawfish Tn the~awerGreen Ftlver. Inaeased pO$l-em<<genc8 release:s from Flaming <br />Gorge reselWlrwBI tend to be courd:erprcduc:Uva with respect to the laval stage of the squawfish. . <br /> <br />. The RazorbJck sucker $pawnsCR the lisihg funb of 1he BMUCIl h)drcgraph (ryus and f<'#rp. <br />1989) and awears to have a f3irly limitl;ld nurn:bm- of spawning loc:aticM on th;I upper Green River and <br />1he IowerYampa Rivet (Tyu!1 and Karp, 1990). laMm ma also disper8ed by a drift mechanism. bUt I <br />flOW$ following 1mvaI emergen~ exceedbanW ~ is a potential for1hem to util~ 1he DUt.m.fmtk <br />habiI3t In ths reach of the Green RIVer ~t is the subject of this report (RM 120 to AM Z8) Uu, <br />frequency of exceedBl1C8 of Um bahJCfuIl <lISdWgc Is lew. If it Is assumed that the bar1;kfuII C3P3clty <br />estimates fer Cottonwccxi Bottom alxI Uriknown Bottom are ~y representative fer the <br />bottomarxls downstream of AM 97 (ccn1Iuenre with San Rafael River) then It is 3Iso reasonab1e to <br />condude that in most yearn Bny Razorback sud~er larvae th3t enter the reach will be passed througtr <br />the reach. If flow releaRlS from Flaming Gorge. reS8fVOir fail to increase the total dischal{le in the river <br />to the point where the I:lankfurr discharge Is ~~ for whatever period Is required for successfU <br />overbank habitat utlizition, the increa:ied 1I0\vs will merely in(:rease the larval drift rate and di$mCL <br /> <br />4) Recommenda(loflS <br /> <br />1. l11e channel cep;cl1y ~ :Jt both Cottonwood and UnknoWI\ Bottoms and 1he flow dunlUor ' . <br />. and Ifooc:I ~ ~ Jndlc:ate that the rawer reaches cI the Green River are unlikely to. btt <br />d great: s1gnific;nce in terms of Aazcnmck. SUcker ~e habitat. Therefore. there doe$ <br />not appear to be rnw;!1 value in futuro cl13nnel ~ - overbank flaw rncnitoring. <br /> <br />5 Re50Urce Consultants & Engineers, Ino. <br /> <br />~007 <br /> <br />.~ <br /> <br />.~ <br /> <br />;~ <br /> <br />:'-- <br /> <br />i <br />