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Home My WebLink AboutAPA589r SUSITNA HYDRO AQUATIC STUDIES PHASE II FINAL REPORT Volume 2.Adult Anadromous Fish Studies,1982. PART B:APPENDICES A-H ARLIS Alaska Resources Library &Information Services Anchorage,Alaska ..... .- :~ - - .LIST OF APPENDIX FIGURES Appendix Figure 2-A-l.Susitna St~tion with sonar and fishwheel locations defined . .Appendix Figure 2-A-2.Yentna Station ~ith ~onar and fishwheel locations defined. Appendix Figure 2-A-3.Sunshine Station with sonar and fishwheel locations defined. Appendix Figure 2-A-4.Talkeetna Station with sonar and fishwheellocations defined. Appendi x Figure 2-A-5.Curry Station wlth fi shwheel locations defin~d. Appendix Figure 2-8-1.Daily sonar counts of sockeye salmon at Susitna.Yentna.Sunshine and Talkeetna stations. Appendix Figure 2-8-2.Daily sonar counts of pink salmon at Susitna.Yentna,Sunshine and Talkeetna stations. PAGE Al A2 A3 . A4 A5 A6 A7 Appendix Figure 2-B~3. Appendix Figure 2-B-4. Appendix Figure 2-B-5. Daily sonar counts of chum salmon at Susitna,Yentna,Sunshine and Talkeetna stations. Daily sonar counts of coho salmon at Susitna,Yentna,Sunshine and Talkeetna stations. Cumulative percent of sonar counts by species at Susitna,Yentna Sunshine and Talkeetna stations. PAGE A8 A9 AlO Appendix Figure2-B-6.Sector distribution of chinook salmon passing over SSS substrate whe~e daily chinook salmon apportioned sonar counts were equal to or greater than ninety percent of total sonar counts. Appendix Figure 2-B-7.Sector distribution of sockeye and pink salmon passing over SSS substrate .whereda i1y sockeye and pink salmon apportioned sonar counts were equal to or greater than ninety percent of total sonar counts. A53 A54 '""" ft!I!l,. - - - Appendix Figure 2-B-8.Bottom profile at Susitna and Yentna stations 1982 sonar sites. PAGE A55 Appendix Figure 2-8-9.Bottom profile at Sunshine and Talkeetna A56 stations 1982 sonar sites. - - "... Appendix Figure 2-0-1.Lenqth frequencies of chinook salmon sampled from fishwheel catches at Susitna Station. Appendix Figure 2-0-2.Lepgth frequencies of chinook salmon sampled from fishwheel catches at Yentna Station. Appendix Figure 2-0-3.Length frequencies of chinook salmon sampled from fishwheel catches at Sunshine Station. Appendix Figure 2-D-4.Length frequencies of chinook salmon sampled from fishwheel catches at Talkeetna Station. A85 A86 A87 AB8 ..-Appendix Figure 2-D-5.Length frequencies of chinook salmon sampled from fishwheel catches at Curry Stati on. A89 Appendix Figure 2-0-6.Length frequencies of sockeye salmon sampled from fishwheel catches at Susitna Station. PAGE A90 Appendix Figure 2-0-7.Length frequencies of sockeye salmon sampled from fishwheel catches at Yentna Station. A91 Appendix Figute 2-0-8.Length frequencies of sockeye salmon sampled fromfishwheel catches at Sunshine Station. A92 ...... Appendix Figure 2-0-9.Length frequencies of first run sockeye A93 .salmon sampled from fishwheel catches at Sunshine Station. Appendix Figure 2-0-10.Length frequencies of second run sockeye salmon sampled from fishwheel catches at Sunshine Station. Appendi x Fi gure 2-0-11.Length frequenci es of sockeye sa 1mon sampled from fishwheel catches at Talkeetna Station. A94 A95 - - - .- , r- , Appendix Figure 2-0-12.Length frequencies of sockeye salmon .sampled from fishwheel catches at Curry Station. Appendix Figure 2-D-13.Length frequencies of pink salmon sampled from fishwheel catches at Susitna Station. Appendix Figure 2-0-14.Length frequencies of pink salmon sampled from fishwheelcatches at Yentna Station. Appendix Figure 2-0-15.Length frequencies of pink salmon sampled from fishwheel catches at Sunshine Station. Appendix Figure 2-D-16.Length frequenctes of pink salmon sampled from fishwheel catches at Talkeetna Station. Appendix Figure 2-D-17.Length frequencies of pink salmon sampled from fishwheel catches at Curry Station. PAGE A96 A97 A98 A99 A100 AlGI Appendix Figure 2-0-18.Length frequencies of chum salmon sampTedfrom fishwheel catches at Susitna Station. Appendix Figure 2-0-19.Length frequencies of chum salmon sampled from fishwheel catches at Yentna Station. Appendix Figure 2-D-20.Length frequencies of chum salmon sampled from fishwheel catches at Sunshine Station. Appendix Figure 2-0-21.Length frequencies of chum salmon sampled from fishwheel catches at T~lkeetna Station. Appendix Figure 2-0-21.Length frequencies of chum salmon sampled from fishwheel catches at Curry Station. Appendix Figure 2-0-23.Length frequencies of coho salmon sampled from fishwheel catches at Susitna Station. PAGE AI02 AI03 AI04 AI05 AI06 AI07 ~I ~. - -- .... Appendix Figure 2-0-24.Length frequencies of coho salmon sampled from fishwheel catches at Yentna Station . Appendix Figure 2-D-25.Length frequencies of coho salmon sampled from fishwheel catches at Sunshine Station .. Appendix Figure 2-0-26.Length frequencies of coho salmon sampled from fishwheel catches at Talkeetna Station. Appendix Figure 2-0-27.Length frequencies of coho salmon sampled fromfishwheel catches at Curry Station. Appendix Figure 2-0-28.Length frequencies of ~ering cisco sampled from fishwheel catches at Susitna,Yentna,Sunshine and Talkeetna stations. Appendix Figure 2-E-1.Movement of radio tagged chinook salmon 600-2 in the Susitna River drainage during July. PAGE A108 A109 AlIO AlII A1I2 A114 Appendix Figure 2-E-2.Movement of radio tagged chinook salmon 610-2 in the Susitna River drainage during June and July. PAGE A116 AlI8 Appendix Figure 2-E-4.Movement of radio tagged chinook salmon A119 660-1 in the Susitna River drainage during June and July. A121 ~, Appendix Figure 2-E-6.Movement of radio tagged chinook salmon 680-1 in the Susitna River drainage during \June and July. Appendix Figure 2-E-7.Movement of radio tagged chinook salmon 700-1 in the Susitna River drainage during June and Jul y. A123 A125 - ,.,.. ..,.. Appendix Figure 2-E-8.Movement of radio tagged chinook salmon 710-3 in the Susitna River drainage during July. Appendix Figure 2-E-9.Movement of radio tagged chinook salmon 720-1 in the Susitna River drainage during July. Appendix Figure 2-E-I0.Movement of radio tagged chinook salmon 720-3A in the Susitna River drainage during June and July. Appendix Figure 2-E-ll.Movement of radio tagged chinook salmon 720-38 in the Susitna River drainage during July and August. PAGE A126 A128 A129 Al31 Appendix Figure 2-E-12.Movement of radio tagged chinook salmon A133 730-1 in theSusitna River drainage during June and July . ...... ,t""- r"'" Appendix Figure 2-E-13.Movement of radio tagged chinook salmon 730-2 in the Susitna River drainage during June and July. A135 Appendix Figure 2-E~14.Movement of radio tagged chinook salmon 730-3 in the Susitna River drainage during June and July. Appendix Figure 2-E-15.Movement of radio tagged chinook salmon 740-2 in the Susitna River drainage during Ju'neand July. PAGE A136 A138 ~J Appendix Figure 2-E~16.Movement of radio tagqed chinook salmon A139 740-3 in the Susitna River drainage during July.-- Appendix Figure 2-E-17.Movement of radio tagged chum salmon 600-3 in the Susitna River drainage during August. Appendix Figure 2-E-18.Movement of radio tagged chum salmon 610-3 .;n the Susitna River drainage during August. Appendix Figure 2-E~19.~ovement of radio tagged chum salmon 620-2 in the SusitnaRiver drainage during August. A141 A143 A144 ...,. - - PABE Appendix Figure 2-E-20.Movement of radio tagged chum salmon A146 620-3 in the Susitna River drainage during August and September. - r~_-~, I~ Appendix Figure 2-E-21.Movement of radio tagged chum salmon 630-2 in the Susitna RiVer ~rainage during August and September. Appendix Figure 2-E-22.Movement of radio tagged chum salmon 630-3A in the Susitna River drainage during August. Appendix Figure 2-E-23.Movement of radio tagged chum s.almon 630-3B in the Susitna River drainage during August and September. Appendix Figure 2-E-24.I~ovement of radio tagged chum salmon 640-2 in the Susitna River drainage during August. A148 A149 A151 A153 Appendix Figure 2-E-25.Movement of radio tagged chum salmon A154 650-2 in the Susitna River drainage during August. Appendix Figure 2-E-26.Movement of radio tagged chum salmon 66b-l in the Susitna River drainage during August. PAGE A156 Appendix Figure 2-E~27.MONement of radio tagged chum salmon A157 660-2 in the Sus itna Ri ver dra inage duri ng July and August. Appendix Figure 2-E-28.Movement of radio tagged chum salmon AlS9 670-2A in the Susitna River drainage during July and August. Appendix Figure 2':'E.:.29.Movement of radio tagged chum salmon A161 670-2&in the Susitna River drainage during August and September. ~, Appendix Figure ,2-E-30.r~oveiTlent of radio tagged chum salmon 670-3 in the Susitna River drainage during August and September. A162 - Appendi x Fi gure 2-E-31.Movement of radi a tagged chum sal man A164 680-2 in the Susitna River drainage during August and September. PAGE Appendix Figure 2-E-32.Movement of radio tagged chum salmon A165 700-2 in the Susitna River drainage during August and September. - ,- Appendix Figure 2-E-33.Movement of radio tagq~d chum salmon 700-3 in the Susitna River drainage during August and September. Appendix Figure 2-E-34.Movement of radio tagged chum salmon 710-2 in the Susitna River drainage during July,August and September. Appendix Figure 2-E-35.Movement of radio tagged chum salmon 710-3 in the Susitna River drainage during August. Appendix Figure 2-E-36.Movement of radio tagged chum salmon 720-1 in the Susitna River drainage during August and September. Appendix Figure 2-E-37.Movement of radio tagged coho salmon 600-1 in the Susitna River drainage during August and September. A167 A169 A170 A172 A174 Appendix Figure 2-E-38.Movement of radio tagged cohO salmon 600-2 in the Susitna River drainage during .August and September. PAGE A175 - Appendix Figure 2-E-39.'Movement of radio tagged coho salmon A178 610-1 in the Susitna River drainage during August and September. Appendix Figure 2-E-40.Movement of radio tagged coho salmon 610-3 in the Susitna River drainage during August and September. Appendi x Figure 2-E-41.,Movement of radi 0 tagged coho sa 1mon 620-3A in the Susitna River drainage during August and September. Appendix Figure 2-E-42.Movement of radio tagged coho salmon 630-1 in the Susitna River drainage during August and September. Appendix Figure 2-E-43.Movement of radio tagged coho salmon 640~1 in the Susitna River drainage during August. .A179 Al81 Al83 A184 -. ..... .,.... - ""'" Appendix Figure 2-E-44.Movement of radio tagged coho salmon, 640-3 in the Susitna River drainage during August and September.' Appendix Figure 2-E-45.Movement of radio tagged coho salmon 650-1 in the Susitna River drainage during August and September. Appendix Figure 2-E-46.Movement of radio tagged coho salmon 650-3 in the Susitna River drainage during August and September. Appendix Figure 2-E-47.Movement of radio tagged coho salmon 660-3 in the Susitna River drainage du~ing . August and September. Appendix Figure 2-E-48.Movement of radio tagged coho salmon 680-3 in the Susitna River drainage during August and September . Appendix Figure 2-E-49.Movement of radio tagged coho salmon 700-1 in the SusitnaRiver drainage during August and September. PAGE A186 A188 A190 A192 A193 A195 Appendix Figure 2-E-50.Movement of radio tagged coho salmon 710-2 in the Susitna River drainage during August. Appendix Figure 2..E-51.·Movement of radio tagged coho salmon 720-2 in the Susitna River drainage during August. PAGE .A197 A198 """ Appendix Figure 2-G-1.Slough locations and primary streams of the Susitna River from the confluence of th~Talkeetna ~nd Chuljtna rivers to Upper Devil Canyon. A250 ~, Appendix Figure 2~G-2.locatinn of Susitna River streams Cheechako and Chinook creeks above proposed Devil Canyon damsite. A255 - Appendix Figure 2-G-3.Slough B located at RM 126.3 approximately.A256 Appendix Figure2-G-4.Mainstem Susitna River chum salmon spawning A257 ~, area at RM 114.4 approximately.- Appendix Figure 2-G-5.Mainstem Susitna River chum salmon spawning A258 128.6 approximately."""iareaatRM - Appendix Figure 2-G-6..Mainstem Susitna River chum salmon spawning area at RM 129.8 approximately. PAGE A259 Appendix Figure 2-G-7.Mainstem Susitna River chum salmon spawning A260 area at RM 131.3 approximately. Appendix Figure 2-G-8.Mainstem Susitna River chum salmon spawning A261 area at RM 136.0 approximately. - Appendix Figure 2-G-9.Mainstem Susitna River chum salmon spawning area at RM 137.4 and 138.2 approximately. Appendix Figure 2-G-10.Mainstem Susitna River chum salmon spawning area at RM 138.9 approximately. Appendix Figure 2-G-11.Mainstem Susitna River chum salmon spawning area at RM 143.3 approximately. Appendix Figure 2-G-12.Mainstem Susitna River chum salmon spawning area at RM 148.2 approximately. Appendix Figure 2-G-13.Mainstem Susitna River Bering cisco spawning area at RM 76.8 approximately. A262 A263 A264 . A265 A266 Appendix Figure 2-G-14.Mainstem Susitna River Bering cisco spawning A267 area at RM 80.8 approximately. ,.,.. Appendix Table 2-8-1. Appendix Table 2-8-2. LIST OF APPENDIXtABCES Yentna Station north bank daily and cumulative sonar counts by species. Yentna Station south bank daily and cumulative sonar counts by species. PAGE All Al4 Appendix Table 2-8-3.Sunshine Station east bank daily and Al7 cumulative sonar counts by species. p:m., Appendix Table 2-8-4.Sunshine Station west bank daily and A20 ~,""'l!"~..", cumulative sonar counts by species. Appendix Table 2-8-5. Appendix Table 2-8-6. Appendix Table 2-8-7. Appendix Table 2-8-8. Talkeetna Station east bank daily and cumulative sonar counts by species. Talkeetna Station west bank daily and cumulative sonar counts by species. Sector distribution of sonar counts. adjusted for debris.~est\bank. Susitna Station. A23 A26 A29 A32 Appendix Table 2-B-9.Sector distribution of sonar counts, adjusted for debris,north bank, Yentna Station. PAGE A35 Appendix Table 2-B-I0.Sector distribution of sonar counts, adjusted for debris,south bank, Yentna Station. Appendix Table 2~B~11.Sector distribution of sonar counts, adjusted for debris,east bank, Sunshine Station. Appendix Table2-B-12.Sector distribution of sonar counts, adjusted for debris,west bank, Sunshine Station. Appendix Table2-B-13.Sector distribution of sonar counts, adjusted for debris,east bank, Talkeetna Station. Appendix Table 2-8-14.Sector distribution of sonar counts, adjusted for debris,west bank, Talkeetna Station. A38 A41 A44 A47 A50 - -,- ~I """I , I Appendix Table 2-C-l.Susitna Station east bank fishwheels daily and cumulative catch log by species. A57 Appendix Table 2-C-2. Appendix Table 2-C-5. Appendix Table 2-C-6. Appendix Table 2-C-7. Appendix Table 2-C-8. Appendix Table 2-C·9. Susitna Station west bank fishwheels daily and cumulative catch log by species. Sunshine Station east bank fishwheels daily and cumulative catch log by species. Sunshine Station west bank fishwheels daily and cumulative catch log by species. Talkeetna Station east'barlk fishwheels daily and cumulative catch log by species. Talkeetna Station west bank fishwheels daily and cumulative catch log by species. Curry Station east bank fishwheeldaily and cumulative catch log by species. PAGE· A59 A66 A70 A73 A76 A79 PAGE Appendix Table 2-C-IO.Curry station west bank fishwheel daily A82 and cumulative catch log by species. '"'" Appendix Table 2-F-l. Appendix Table 2-F-2. Appendix Table 2-F-3~ Appendix Table 2-G-l. Appendix Table 2-G-2. Appendix Table 2~G~3. Electroshocking summary of mainstem Susitna River. .Summary of mainstem Susitna River sampling usirig gill nets and vis~al inspection. fvaluation of tag loss based on spawning surveys conducted between Sunshine Station and Devil Canyon. Escapement survey counts of Susitna River sloughs between Talkeetna River and Devil Canyon. E~capement survey counts of Susitna River streams between Chulitna River and Upper Devil Canyon. Sockeye salmon spawning ground surveys of selected spawnihg areas and resultant tagged to un tagged ratios. A199 A246 A249 A268 A278 A283 ~, - "'""'I I i -I Appendix Table 2-G-4. Appendix Table 2-G-5. Appendix Table 2-G-6. Pink salmon spawning ground surveys of selected spawning areas and resultant tagged to untagged ratios. Chum salmon spawning ground surveys of selected spawning areas and resultant tagged to untagged ratios. Coho salmon spawning ground surveys of selected spawning areas and resultant tagged to untagged ratios. PAGE A285 A288 A292 - .... ,~ .... Appendix 2-H LIST OF APPENDIX REPORTS STOCK SEPARATION REPORT PAGE A295 - - - .... APPENDIX 2-A SUSITNA AND YENTNA RIVERS SAMPLING STATIONS J --)j j i i -I I '--1 1 -1 i J 1 J 1 J -1 )} "I.• -z ..... 6) Rlvermlle 27 Weat Bank Sonar I July 1-24 "i'/vl!'"-9,---- -.\;'-':-::':l. "-';"'''''' :.":::". ,\..,:..•..,~-' .~,;..;~...,.~.#-...."-~~s U,s/r -1'-<7 .\;.,,.;.;,.,-',•••-":i'~",~,••O~I"_ ."'''.~9:l Ealt Banlt,Fllhwheel ~4:. Ealt aa"ksonar;f ....~.\.~. ~~. ,.0,:,. ";;'"West Bank $onor2 "p~July 2!5~S.pt!5 ~.\).;~ "._4 _~.. ...... ...':...... '...~, .::""r,··.·f~..W..t Bank Fishwheel ~"./...•.:~.....• <.()~·h. "J:1""""~~sus'iT'N'A':': CAMP ~•STATION SUSITNA STATION >..... Appendi X Fi gure 2-A-1.Sus itna StatiOl)with sonar and fi shwheel locations defined,Adult Anadromous Investi gations,Su Hydro Stud;es,1982. > N ..b...z;·.·FJ~"".!;".,,,.-<,''':-'.,•• 1t"tt.._;::;.... YENTNA STATION Appendix Figure 2-A-2.Yentna Station with sonar and fishwheel locations defined,Adult Anadromous Investigations,Su Hydro Studies,1982 . )~J I J J I ) .~ J J J .1 J J \ I I '))i J J )I J J I J -]}1 -J I ] )~ ,1 > (,) -~*pz .,t "\ ,.-...,..-.~-"(,;;.':'" ..u····;...L· S ~,/....:.".-.. .i.S J t •.tt ?).....'t=.-...., SUNSHINE STATION Appendix Figure 2-A-3.Sunshine Station with sonar and fishwheel locations defined,Adult Anadromous Investigations,Su Hydro Studies,1982. » ~ Low.r Eatt Bank Flshwhe.1 ...........-*-----::sz- Upp.r W.st Bank, Flshwh ••1 West Bank't """"';"'01~';Son.Q r,........."."""";i:"~V::'€i''''j-::.,?"j"';',,\.;_.'.~'.....+_..,......"4-4uLowerW••t Bank ~CD Fishwhul .....;;.....~. .....n·..·'''''·",~.___S US I rNA IJ I VEI?____ ED " Rlv.,,,,lle 103 ,r''',,-...III .'•...D .....~.,.•,.".~,\.",.\",•.;_~Ea.t B',.f.·~..,." .""._.,......,S ."",,,,~•.".".....'..CAM P •••,' •"""<".. •"....• U "".,. """"'F'E••'e••'~.I __~..h.h••'...,•.".~,~,".~,..~,.., '::'1' "..~:';...... ._,.~.::'C',:::,,~';'-"':"""':::<)';'<>..••E.i.::.:"'• ....................-: Ig] CABIN TALKEETNA STAT ION Appendix Figure 2-A-4.locations defined,Adult Anadromous 1 ~~J } Talkeetna Station with sonar and fishwheel Investigations,Su Hydro Studies,1982. l .J 1 )J )J J J I J J I \ J J 1 D J -1 -J i .1 I i I 1 J J j J 1 .)Jt)f >01 CURRY STATION ••;'ll_....:;.,,,..:."""•••*'".....,,'1 west Bank ....... Append;x Figure 2-A-5.Curry Station with fi shwheel locations defi ned,Adult Anadromous Inves ti gations, Su Hydro Studies,1982. .- - - rr-, - APPENDIX 2-B SONAR 1.FIGURES OF DAILY SIDE SCAN SONAR COUNTS ,BY SPECIES 2.FIGURE OF CUMULATIVE PERCENT OF SONAR COUNTS BY SPECI ES 3.DAILY SONAR COUNTS BY STATION· 4.SECTOR DISTRIBUTION OF SONAR COUNTS 5.BOTTOM PROFILES OF 1982 SONAR SITES j '~ ? J )-1 I 1 J ·····1 ) J -,j 1 ) j 15,000-) SUSITNA STATION YENTNA STATION 22,500- ~12,000 c: :) o0 9000 _ ...oc:o U'I 6000- 11/16,000- ..- c: :JoU 13,500-...oc:oen 9000- TALKEETNA STATION ,\\J\ 61'20 6/'30 7/10 7/'2.0 7i'30 SYIO SY20 ei'30 9YlO Date 6i'20 6/307/10 7i20 7i30 e,i'10 8720 81'30 9/'10 Date 4500-.I~3000- 6/Z0 6/30 ¥7~2077~e%o 8/309/10 Date » 7500J SUNSHINE STAT I·ON 0)I 300 <Il U IIIC6000~240 :) 0 :J 0 0u... o 4500 ...180 c 0 0 c: U)0en 3000 120 1500 60 EY20 6130 7/10 7/20 7/30 8/10'8120 8/30 9/10 Date Appendix Figure 2~B-l.Daily sonar counts of sockeye salmon at Susitna,Yentna,Sunshine,and Talkeetna stations,Adult Anadromous Investi.gations,Su Hydro Studies,1982. })l "1 ) 1 1 I 'I ) SUS ITNA STATION YENTNA STATION 50,000 ..I -.-- 1 r I I 6/20 6/30 7/10 7/20 7/30 8/10 8/20 8/30 9110 Date TALKEETNA STATION 71~8/10 8/20 8/30 9/10 Do te 12,500 10,000 2 40,000 c: ::3o U ...30,000 oc:o CJ) 20,000 A SUNSHINE STATION fiJ ~.... 13,000 - 50,000- >.~ II)-;_40,000;- o U ;;30,000- c:o en \ ~IO,OOOc: -::3o U ...7500o c:o CJ) 20,000-5000 N 10,000 - ______J\, 6/20 s)'30 7710 7720 7730 8/10 8720 8/30 9110 Date 2500 o 8/30 9110 Appendix Figure 2-B-2.Daily sonar counts of pink salmon at Susitna,Yentna,Sunshine,and Talkeetna stations,Adult Anadromous Investigations,Su Hydro Studies,1982. 1 i1 . SUSITNA STATION YENTNA STATION » Ql) 3750 .3000w-c: :s 0 2250U '"'0c: 0 (/)150P 750 12500 w ~·IOOOO :J 8 ~7500c ~ SOOO SUNSHINE STATION y 4000 !!3200 c:J. 8 ..2400 o ~ laoo 800 ( 2500 2000w...., C :J .<3 150' 6/20·a/?/) TALKEETNA STATION J: \" 1I .~ !J)__1) 6/20 6i'30 i/IO 7120 7130 8110 el208130 Dote Yentna,Sunshine and Talkeetna Hydro Studies,1982. lIOO J• -- __t 6/20 al30 "Q107~7J30 Dote Appendix Figure 2-B-3.Daily sonar counts of chum salmon at Susitna, stations~Adult Anadromous Investigations~Su t .. _J J j ~..! 2S00 JJ 1-,--1 1 " 1 }1 ]J J 'I 1 !J ) t 5000 UI 4000 SUSITNA STATION 6250 5000 YENTNA STATION c :;lo (.)3000 t- oco (f)2000 1000 6/20 UI-;3750 o (.) ....g 2500 ··0en 1250' »SUNSHINE STATION 3250 375 CD 2600 300 UI III --~cc::J:J 0o1950-(.)225 (.)... t-o 0 c ~1300 0 (f)150 if) 650 75 6tlO 6/30 Appendix Figure 2-B~4. TALKEET~STATION 6i'20 6/30 7/10 7/2!J 7/30 a/lo a'l20 a/30 9/10 Date Daily sonar countsnf coho salmon at Susitna,Yentna,Sunshine,and Talkeetna stations,Adult Anadromous Investigations,Su Hydro Studies,1982. Susitno StatiOn--;..- Yentna Station -_. Sunshine Statlon-·.•• Tol\(eetna Station ~.- 7/30 sYJ()S/,20 S'/3{)9YIO Dote PINK I00'TI~~~~-~-:-----==:;::;;:;;;;=<='",!!:::,-=="""'----.-e=?TO I 20 60 67206/'30 ~o Q)60>-.2 :::l.E 40 ='U 7}20 7}'30 e~lo eY20 eY30 9YI0 Dote W20 80 20 IDOl SOCKEYE r //.-./.-.-.1 /' ;' / (' ! I I, / II:iI'.r ) 'I:.I..:-:/ -c =' E 40=' () ~o QI .~60 ~ /,:( .'i :'i..:/ COHO 20 80 -.s::gV"'".I100I.._,.~."/' ,/' / /~o ~60-o =:J . E 40 :::l U ~60 20 100 ,.--;a:c»=i eo 6/'20 6i'30 7/10 7/20 7/30 a/lo 8/20 8/30 9/10 6/'20 6/30 7'110 7/'20 7/30 a/lo a'l20 8/30 9'/10 Date Date Appendix Figure 2-B-5.Cumulative percent of sonar counts by species at Susitna.Yentna.Sunshine and Talkeetna stations.Adult Anadromous Investigations.Su Hydro Studies,1982. .CHUM· ~o .--c =' E 40 .='u >0 -'o )~, I J .J J ))I I ]J j t ..1 ).J l , 1 1 1 j }1 --I 1 J, )) J J 1 1 ,i Appendix Table 2-8-1.Yentna station north bank daily and cumulative sonar counts by species,Adult Anadromous Investigations,Su Hydro Studies,1982. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC. DAILY COUNT DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820628 00008 008 0008 00000 000000 00000 000000 0000 00000 0000 00000 000 0000 820629 00024 024 0032 00000 000000 00000 000000 0000 00000 0000 00000 000 0000 820630 00026 026 0058 00000 000000 00000 000000 0000 00000 0000 00000 000 0000 820701 00074 042 0100 00016 000016 00000 000000 0000 00000 0000 00000 016 0016 820702 00046 026 0126 00010 .000026 00000 000000 0000 00000 0000 00000 010 0026 820703 00093 052 0178 -00021 000047 00000 000000 0000 00000 0000 00000 020 0046 820704 00079 044 0222 00018 000065 00000 000000 0000 00000 0000 00000 017 0063 >-820705 00082 025 0247 00021 000086 00011 000011 0000 00000 0000 00000 025 0088 ~820706 00045 014 0261 000098 00005 000016 0000 00000 0000 00000-a.00012 014 0102 820707 00019 006 0267 00005 000103 00002 000018 0000 00000 0000 00000 006 0108 820708 00012 004 0271 00003 000106 00001 000019 0000 00000 0000 00000 004 0112 820709 00004 002 0273 00001 000107 00000 000019 0000 00000 0000 00000 001 0113 820710 00024 010 0283 00004 000111 00001 000020 -0000 00000 0000 00000 009 0122 - 820711 00036 015 0298 00006 000117 00002 000022 0000 00000 0000 00000 013 0135 820712 00026 011 0309 00005 000122 00001 000023 .0000 00000 0000 00000 009 0144 820713 00015 001 0310 00009 000131 00004 000027 0000 00000 0001 00001 000 0144 820714 00023 002 0312 00012 000143 00006 000033 0000 00000 0002 00003 001 0145 820715 00058 005 0317 00030 00017:3 00015 000048 0000 00000 0005 00008 003 0148 820716 00019 002 0319 00010 000183 00004 000052.0000 00000 0002 00010 001 0149 820717 00100 000 0319 00033 000216 00043 000095 0015 00015 0007 00017 002 0151 820718 00276 000 0319 00091 000307 00117 000212 0043 00058 0019 00036 006 0157 820719 01100 000 0319 00364 000671 00468 ·000680 0169 00227 .0074 00110 025 0182 820720 05008 000 0319 02559 003230 01783 002463 0386 00613 0255 00365 025 ·0207 820721 07906 000.0319 03534 006764 03360 005823 0751 01364 0261 00626 000 0207 820722 03235 000 0319 01074 007838 01686 007509 0281 01645 0194 00820 000 0207 820723 01474 000 0319 00153 007991 01225 008734 0046 01691 0050 .00870 000 0.207 AppendiX Table 2-B-l.Continued. DATE TOTAL CHINOOK SOCKEYE PINK CHillI COHO MIse DAILY COUNT DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820724 00514 000 0319 00053 008044 00415 009149 0026 01717.0020 00890 000 0207 820725 00575 000 0319 00068 008112 00461 009610 0010 01737 0024 00914 002 0209 820726 00301 000 0319 00024 008136 00259 009869 0013 0175,0 0002 00916 004 0213 820727 01224 000 0319 ,00089 008225 01097 010966 0028 01778 0010 00926 000 0213 820728 04314 000 0319 00052 008277 04069 015035 0121 01899 '0082 01008 000 0213 820729 07751 000 0319 00171 '008448 07185 022220 0171 02070 0224 01232 000 0213 820730 '09830 000 0319 00167 008615 09103 031323 0413 02483 0147 01379 000 0213 8207}1 11910 000 0319 00453 '009068 10409 041732 '0893 03376 0155 01534 000 0213 820801 13834 '000 0319 00719 '009787 10666 052398 1785 05161 0664 02198 000 0213 >-820802 11386 000 0319 00204 009991 09872 062270 '0911 06,072,0399 02597 '000 0213..a. I\)820803 07248 000 0319 00080 010071 06393 068663 0580 06652 0188 02785 007 0210 820804 07411 000 0319 00170 010241 0624,0 074903 0778 07430 0208 02993 015 0235 820805 03983 000 ' ,0319 00147 010388 02768 077671 0849 08279 0183 03176 036 0271 ' 820806 01122 000 0319 00021 010409 00753 078424 0220 08499 0113 03289 015 0286 820807 01018 000 0319 00056 010465 00709 079133 0166 08665 0077 '03366 010 0296 820808 01288 002 0321 00041 010506 01061 080194 0111 08776 0063 03429 010 0306 820809 0165~000 0321 00030 010536 01238 081432 0260 09036 0108 03537 023 0329 820810 01323 000 0321 00049 010585 00893 082325 0277 09313 0081 03618 023 0352 820811 01012 000 0321 00110 010695 00583 082908 0168 09481 0120 03738 031 0383 820812 00875 000 0321 00096 010791 00504 083412 0145 09626 0103 03841 021 0410 820813 00787 000 0321 00055 010846 00458 089370 0106 09732 0110 03951 058 0468 820814 00394 000 0321 00028 010874 00229 084099 0053 09785 0055 04006 029 0491 820815 00271 000 0321 00035 010909 00086 084185 0054 09839 0086 04092 010 0501 820816 00308 000 0321 00040 010949 00097 084282 0062 09901 0097 04189 012 0519 820817 00441 000 0321 00057 011006 00140 084422 0088 09989 0139 04328 017 0536 820818 00408 000 0321 00053 011059 00129 084551 0082 10071 0129 04457 016 0552 820819 00344 000 0321 00035 011094 00067 084618 0118 10189 0083 04540 041 0593 l , .,j J J ~J J J ]J 3 I i }j J I I J 1 I I -1 I )J -i )I J 1 J 1 }J ~~ )j Appendix Table 2-B-l.Continued. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC. DAILY COUNT DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820820 00247 000 0321 00025 011119 00048 084666 0085 10274 0060 04600 029 0622 820821 00100 000 0321 00010 011129 00020 0846 86 0034 10308 0024 04Q24 012 0634 820822 00178 000 0321 00018 011147 00035 084721 0061 10369 0043 ·04667 021 0655 820823 00141 000 0321 00016 011163·.00013 084734 0021 10390 0038 04705 053 0708 820824 00135 000 0321 00016 011179 00013 084747 0020 10410 0036 04741 050 0758 >820825 00155 000 0321 00018 011197 00014 084761 0024 10434 0041 04782 058 0816 -a.820826 00239 000 0321 00028 011225 00022 084783 0036 10470 0064 04846 089 0905CU82082700167000032100012011237000000847830031.i0501 0027 04873 097 1002 820828 00165 000 0321 00012 011249 00000 084783 0010 10531 0027 04900 096 .1098 820829 00078 000 0321 00006 011255 00000 084783 001.4 .10545 0013 04913 045 1143820830001350000321.00010 011265 00000 084783 0025 10570 0022 04935 078 1221 820831 00158 000 0321 00007 011272 00000 084783 0029 10599 0079 05-014 043 1264 820901 00101 000 0321 00005 011277 00000 084783 0018 10617 0051 05065 027 129182090200394000032100018011295000000847830072106890197052621071398 820903 00326 000 D321 .00015 011310 00000 084783 0059 10748 0163·05425 089 1487 820904 00164 000 0321 00000 011310 00000 084783 0016 10764 0099 05524 049 1536 Appendix Table 2-8-2.Yentna station south bank daily and cumulative sonar counts by species,Adult Anadromous Investigations,Su Hydro Studies.1982. DATE TOTAL CHINOOK SllCKEYE PINK CHUM COHO MISC. DAILY COUNT DAILY CUM DAILY CUM -DAILY CUM.'DAILY CUM·DAILY CUM DAILY CUM 820627 .00044 029 .0029 00015 000015 00000 000000 0000 00000 0000 00000 000 0000 820628 00064 .043 0072 .00021 000036 00000 000000 0000 00000 0000 -00000 000 0000 820629 00028 019 0091 00009 000045 ..00000 000000'0000 ooobo 0000 00000 000 0000 820630 00008 005 0096 00003'000048 00000 .000000 0000 00000 0000 00000·000 .0000 820701 00020 ..015 0111 00005 000053 00000 000000 0000 00000 0000 00000 '.000 0000 820702 OOC02 001 0112 00001 000054 00000 000000 0000 00000 0000 00000 001·0001 820703 ·00106 078 0190 00027 ·000081 00000.000000 0000 00000 0000 00000 001 0002 820704 00101 .074 0264 00026 000107 .00000 000060 0000 00000 0000 00000 017 0019 »820705 00064 038 .0302 00009 000116 .00000··000000 0000 00000 0000 ooobo·010 .0029 ;..a. 00038....820706 023 0325 00005 000121 00000 000000 0000 00000 0:000 .00000 010 0029 820707 00016 010 0335 00002 000123 ..00000 000000 0000 oooqo 0000 .00000 004 0033 820708 00191 115 0450 00027 000150 .00000 000000 0000 .00000 0000 00000 049 0082 820709 00066 038 0488 .00017 000167 00003 000003 0000 00000 0000 00000 008 0090 820710 00016 009 0497 00004 000171 00001 000004 0000 00000 0000 00000 002 0092 820711 00012 007 0504 00003 000174 00001 000005 0000 00000 0000 00000 001 0093 820712 00020 012 0516 00005 000179 00001 000006 0000 00000 0000 00000 002 0095 820713 .00033 004 0520 00019 000198 00004 000010 0000 00000 0003 00003 003 '0098 820714 00074 009 0529 00044 000242 00009 000019 0000 00000 0005 00008 007 0105 820715 00071 009 0538 00042 000284 00009 000028 0000 00000 0005 00013 006 0111 820716 00154 019 0557 00090 000374 00019 000047 0000 00000 0011 00024 015 0126 820717 01694 014 0571 01257 001631 00203 000250 0080 00080 0127 00151 013 0139 820718 03928 031 0602 02915 004546 00471 000721 0185 00265 0295 00446 031 0170 820719 18288 165 0767 12436 016982 03072 003793 1262 01527 1262 01708 091 0261 820720 21748 000 0767 17225 034207 03349 007142 0609 02136 0500 02208 065 0326 820721 25350 000 0767 18987 053194 04867 012009 1040 03176 0456 02664 000 0326 820722 18261 000 0767 10336 063530 05606 017615 0913 04089 1406 04070 000 0326 820723 13831 027 0794 04163 067693 08755 026370 0277 04366 0609 04679 000 0326 )•\ l J J _I J I I J I J i I J J J .J J 1 I -]J 1 J .1 I J J -B 1 J )-1 1 I 1).~).0;-1" Appendix Table 2-8-2.Continued. Appendix Table 2-B-2.Continued. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC. DAILY COUNT DAILY CUM DAILY CUM DAILY .CUM DAILY CUM DAILY CUM DAILY CUM 820820 00257 000 0872 00067 101535 00033 362305 0076 16387 0076 27423 005 0669· .820821 00089 000 0872 00023·101558 00012 362317 0026 16413 0026 27449 002 0671 820822 .00050 000 0872 00020 .101578 00002 362319'.0009 16422 0016 27465 003 0674 820823'00195 000 0872 00079 1016.57 00006 362325 ,0037 16459 0061 27526 012 0686>-820824 00265 000 0872 00108 101765 00008 362333'0050 16509 0083 27609 016 0702... 00219 000 0872 00089 101854 00007 362340 0041 16550 0069 27678 013 0715en820825 820826 00170 000 0872 00058 101912 00016 362356 0011 16561 0080 .27758 .005 0720 820827 00182 000 0872 00063 101975 00017 .362373 0011 16572 .0085 27843 ".006 0726 820828 00232 000 0872 00080 102055 00022 362395 0014 16586 0109 27952 007 0733 820829 00286 000 0872 00098 102153 00027 362422 0018 16604 0134 28086 009 0742 820830 00222 000 0872 00066 102219 00013 362435 0052 16656 0065 28151 026 0768 820831 00135 000 0872 00040 102259 00008 362443 0032 16688 0040 28191 015 0783 820901 00213 000 0872 00062 102321 00013 362456 0050 16738 0063 28254 025 0808 820902 00294 000 0872 00086 102407 00018 362474 0069 16807 0086 28340 035 0843 820903 00243 000 0872 00051 102458 00000 362474 0103 16910 0089 28429 000 0843 820904 00302 000 0872 00064 102522 00000 362474 0127 17037 0111 28540 000 0843 820905 00069 000 0872 00015 102537 00000 362474 0029 17066 0025 28565 000 0843 •\ J I J J ••J .~,)j ••I J J I J )] )]1 1 1 ]I J ]'I 1 1 J .J )..1 .J 1 J J~.~)} Appendix Table 2-8-3.Sunshine station east bank daily and cumulative sonar counts by species,Adult Anadromous Investigations,Su Hydro Studies.1982. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC DAILY DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820706 00369 362 0362 00003 000003 00000 000000 000003 000003 0000 00000 001 0001 820707 00470 456 0818 00014 000017 00000 000000 000000 000003 0000 00000 000 0001 820708 00434 421 1239 00013 000030 00000 000000 000000 000003 0000 00000 000 0001 820709 00433 420 1659 00005 000035 00004 000004 000004 000007 0000 00000 000 0001 820710 00413 401 2060 00004 000039 00004 OnOO08 000004 000011 0000 00000 000 0001 820711 00216 210 2270 00002 000041 00002 000010 000002 000013 0000 00000 000 0001 820712 00219 213 2483 00002 000043 00002 000df2 000002 000015 0000 00000 000 0001 820713 00116 064 2547 00019 000062 00016 0·00028 000012 000027 0000 00000 005 0006 »820714 00089 049 2596 00014 000076 00013 000041 000009 00C036 0000 00000 004 0010 ,..........820715 00116 064 2660 00019 000095 00016 000057 000012 000048 0000 QOOOO 005 0015 820716 00089 049 2709 00014 000109 00013 000070 000009 000057 0000 00000 004 0019 820717 00060 002 2711 00055 000164 00003 000073 000000 000057 0000 00000 000 0019 820n8 00056 002 2713 00052 000216 00002 000075 000000 000057 0000 00000 000 0019 820719 00222 007 2720 00204 000420 00011 000086 000000 000057 0000 00000 000 0019 820720 01024 023 2743 00788 001208 00161 000247 000049 000106 0000 00000 003 0022 820721 06716 013 2756 05716 006924 00443 000690 000537 000643 0007 00007 000 002282072207408022277805593012517010080016980007700014130015000220000022 820723 11686 000 2778 07000 019517 02980 004678 001659 003072 0046 00068 000 0022 820724 05032 010 2788 04177 023694 00720 005398 000125 003197 -.0000 00000 000 0022 820725 04832 000 2788 03817 027511 00797 006195 000218 003415 0000 00000 000 0022 820726 820727 08643 017 2805 04080 031591 03535 009730.001011 004426 0000 00000 000 0022 820728 12625 000 2805 04217 035808 04027 013757 004356 008782 0025 00093 000 0021. 820729 21596 000 2805 .05680 041488 08639 022396 007191 015973 0086 00179 000 0022 820730 25301 000 2805 04580 046068 16446 038842 004174 020147 0101 ..00280 000 0022 820731 19842 000 2805 03175 049243 14544 053386 002083 022230 0040 00320 000 0022 820801 38510 000 2805 03851 053094 26957 080343 007509 029739 0193 00513 000 ·0022 Appendix Table 2~B-3.Continued. DATE 'rUTAL ..CHINOOK SOCKEYE PINK·CHUM .COHO MISC· DAILY DAILY CUM DAILY CUM DAILY CUM DAILY CUM·DAILY CUM DAILY CUM 820802 53689 000 2805 ·01503 054597 .40911 121254 010953 040692 0322 00835 000 ·0022 820803 57200 000 280S 01316 055913 45302 166556 009781 050473 0801 01636 000 0022 820804 51505 .000 2805.00618 056531 40277 .206833 009632 060105 0978 02,614 000 0022 820805 37138 000 2805 00371 056902 26591 233424 009136 069241 1040 03654 000 0022 820806 39593 000 .2805~00317 057219 25933 259357 011443 080684 1900 05554 ··000 0022 820807 32792 ·000 2805 00262 057481 18692 278049 011444 092128 2394 07948 .000 0022 820808 21372·000 2805 00107 057588 10451 288500 008784 100912 2030 09978 000 0022 820809 14934 000 .2805 ·00119 057707 05421·293921 007930 108842 1464 11442 000 0022. 820810 13422 000 280S .00134 057841 04107 298028 007342 116184 1839 13281 000 0022 »820811 15074 000 280S 00060 057901 04070 302098 008939 125123 2005 15286 000 0022....820812 13042 000 2805 00065 057966 02778 304876 008165 133288 2008 ·17294 026 0048<».820813 0870f 000 2805 00043 058009 01523 306399 005717 139005 1375 18669 043 0091 820814 07851 008 2813 00047 058056 01814 308213 004703 143708 1256 19925 023 0114 820815 02377 004 2817 00036 058092 00378 308591 001198 144906 0761 20686 000 0114 820816 02918 000 2817 00038 058130 00376 308967 001243 146149 1261 21947 000 0114 820817 02510 000 2817 00020 058150 00186 309153 001024 147173 1275 23222 005 0119 820818 01713 000 2817 00022 058172 00154 309307 000655 147828 0882 24104 000 0119 820819 02003 000 2817 00030 058202 00272 309579 000916 148744 078S 24889 000 OU9 820820 01542 000 2817 00006 058208 00171 309750 000884 149628 0463 25352 018 0137 820821 01156 000 2817 00000 058208 00094 309844 000701 150329 0326 25678 035 0172 820822 01001 000 2817 00000 058208 00075 309919 000511 150840 0373 26051 042 0214 820823 01011 000 2817 00000 058208 00076·309995 000516 151356 0377 26428 042 0256 820824 00778 000 2817 00020 058228 00055 310050 000466 151822 0207 26635 030 0286 820825 00680 000 2817 00018 058246 00048 310098 000407 152229 0181 26816 026 0312 820826 00559 000 2817 00006 058252 00015 310113 000394 152623 0086 26902 058 0370 820827 00583 000 2817 00006 058258 00016 310129 000411 153034 0089 26991 061 0431 820828 00438 000 2817 00005 058263 00011 310140 000309 153343 0067 27058 046 0477 ~, J J J J 1 I J J I J J ~)5 J J J !J J ))"1 -~-1 1 J 'll.'J -,]1 1 •jjJ! \)J Appendix Table 2-B-3.Continued. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC DAILY DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820829 00333 000 2817 00004 058267 00006 310146 000253 153596 0033 27091 037 0514 820830 00367 000 2817 00004 058271 00007 310153 000278 153874 0037 27128 041 0555 820831 00235 000 2817 00003 058274 00005 310158 000178 154052 0023 27151 026 0581 820901 00393 000 2817 00005 058279 00007 310165 000298 154350 0039 27190 044 0625 )10 820902 00449 000 2817 00003 058282 00003 310168 000346 154J 96 0026 27216 071 0696......820903 00428 000 2817 00003 058285 00003 310171 000330 155026 0025 27241 067 0763lD8209040022200028170000205828700002310173000171155197.0013 27254 034 0797 820905 00250 000 2817 00002 058289 00002 310175 000192 155389 0015 27269 039 0836 82090n 00336 000 2817 00003 058292 00000 310175 0002.56 155645 0030 27299 047 0883 820907 00334 000 '2817 00003 058295 00000 31017 5 000255 155900 0030 27329 046 0929 820908 00250 000 2817 00002 058297 00000 310175 000191 156091 0023 27352 034 0963 820909 00177 000 2817 00001 058298 00000 310175 000135 156226 0016 27368 025 0988 820910 00132 000 2817 00000 058298 .00000 310175 000074 156300 0005 27373 053 '1041 820911 00127 000 2817 00000 058298 00000 310175 000071 156371 0005 27378 051 1092 820912 00013 000 2817 00000 058298 00000 310175 000007 156378 0001 27379 005 1097 Appendix Table 2-B-4.Sunshine.station west bank daily and cumulative sonar counts by species,Adult Anadromous Investigati ons,Su Hydro Studi es,1982. J -,.J »1 1 1 )I 1 )]I I 1 )JJ. )~J Appendix Table 2-B-4.Continued. DATE TOTAL CHINOOK SOCKEYE PINK .CHUM COHO MISC DAIL'lDAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820802 12069 000 0107 02064 012566 07748 011516 -001654 004466 0603 00927 000 0010 820803 11006 000 0107 01882 014448 07066 018582 001508 005974 0550 01477 000 0010 820804 10584 000 0107 01080 015528 07398 025980 001651 007625 0455 01932 000 0010 820805 09841 000 0107 00650 016178 06239 032219 002057 009682 0895 02827 000 0010 820806 06888 000 0107 00413 016591 04505 036724 001247 010929 0723 03550 000 0010 820807 04902 000 0107 00113 016704.02274 038998 001598 012527 0917 04467 000 0010 8:Z0808 02212 000 0107 00066 016770 00615 039613 000940 013467 .0591·.05058 000 0010 820809 01582 000 0107 00048 016818 00440 040053 000672 014139 0422 ·05480 000 0010 820810 01430 000 0107 00077 .016895 00288 ·040341 000619 014758 0446 05926 .000 0010 >-820811 02022 000 0107 00109 ·017004 00406 040747 000876 01~634 0631 06557 000 0010 N 820812 02452 000 0107 00069 017073 00414 041161 001118 016752 0851 07408 000 0010 .A 820813 02512 000 0107 0181840003001710300236041397001432 0804 08212 010 0020 820814 01729 000 0107 00024 017127 00133 041530 000965 .019149 0598 08810 009 0029 820815 00940 000 0107 00037 017164 00037 041567 000319 01946 8 0547 09357 000 0029 820816 00877 000 0107 00034 017198 00034 041601 000298 019766 0511 09868 000 0029 820817 00929 000 0107 00036 017234 00036 04~637 000316 020082 0541 10409 000 0029 820818 00601 000 0107 00029 017263 00020 041657 000099 020181 0453 10862 000 -'0029 820819 00671 000 0107 00032 017295 .00023 041680 000111 020292 0505 11367 000 0029 820820 00696 000 0107 ·00033 0173.28 00024 041704 ObOII5 020407 0524 ·11891 000 0029 820821 00790 000 0107 00038 017366 00027 041731 000130 020537 0595 12486 000 0029 820822 00546 000 0107 00066 017432 00043 041774 000066 020603 0371 12857 000 0029 820823 00259 000 0107 00031 017463 00021 041795 000031 020634 0176 13033 000 0029 820824 00292 000 0107 00035 017498 00023 041818 .000035 020669 0199 13232 000 0029 820825 00264 000 0107 00032 017530 00021 041839 000032 020701 0179 13411 000 0029 820826 00295 000 0107 00030 017560 .00000 041839 000103 020804 0148 13559 014 ·0043 820827 00230 000 0107 00023 017583 00000 041839 000081 020885 0115 13674 011 0054 820828 00214 000 0107 00021 017604 .00000 041839 000075 020960 0107 13781 011 .0065 Appendi~Table 2-B~4.Continued. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC DAlLY DAlLY CUM DAILY CUN DAlLY CUM DAlLY CUM DAILY CUM DAILY CUM 820829 00232 000 0107 00023 017627 00000 .041839 000081 021041 0116 13897 012 0077 820830 .00282 000 0107 00000 017627 00000 041833 000113 021154 0113 14010 056 0133 820831 00170 .000 0107 00000 017627 00000 041839 000068 021222 .0068 14078 034 0167 820901 00.319 000 0107 00000 017627 00000·.041839 000128 021350 0128·14206 063 0230 820902 00291 000 0107 00000 017627 00000 041839 000116 021466 .0117 14323 058 0288 820903 00094 000 0107 00000 017627 ..00000 041839 000038 021504 ··0050 14373 006 0294 >820904 00342 000 0107 00000 017627 00000 041839 000137 ..021641 0182 1.4555 023 0317 f\)820905 00253 000 0107 00000 017627 00000 041839 000101 021742 0135 14690 017 0334 f\).820906 00239 000 0107 00000 ..017627 00000 041839 000096 021836 0127 14817·016 0350 820907 00175 000 0107 00000 017627 00000 ...041839 .000052 .021890 0053 14870 070 0420 820908 00181 000 0107 00000 017627 00000 041839 000054 021944 0054 14924 073 0493 820909 00117 000 0107 00000 017627 00000 041839 000035 02197.9 0035 14959 047 0540 820910 00102 000 0107 00000 017627 00000 041839 000031 022010 0031 14990 040 0580 820911 00128 000 0107 00000 017627 00000 041839 000038 022048 0038 15028 050 0630 820912 00027 ·000 0107 00000 017627 00000 041839 000008 022056 0008 15036 011 0641 \\ .J ]_..J I 9 J t )j _J ))t J t J !I 1 1 1 1 )i 1 1 1 )»]1 1 1 1 J ] )) Appendix Table 2-B-5.Talkeetna station east bank daily and cumulative sonar counts by species~Adult Anadromous Investigations,Su Hydro Studies,1982. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC. DAILY COUNT DAILY CUM DAILY ·.·CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820704 00075 074 0074 00000 000000 00000 000000 0000 00000 0000 00000 001 0001 820705 00194 191 0265 00000 .oonooo 00000 000000 0000 00000 0000 00000 003 0004 820706 00185 182 0447 00000 000000 00000 000000.0000 00000 0000 00000 003 0007 820707 00187 184 0631 00000 000000 00000 000000 .OOQO·00000 0000 00000 003 0010 820708 00070 066 0697 00000 ·000000 00000 000000 0000 00000 0000 00000 004 0014 820709 00071 067 0764 00000 000000 00000 000000 0000 00000 0000 00000 004 0018 820710 00089 084 0848 00000 000000 00000 000000 0000 00000 0000 00000 005 0023 820711 00050 047 0895 00000 000000 00000 000000 0000 00000 0000 ·.00000 003 0025 >820712 00038 038 0933 00000 000000 00000 000000 0000 00000 0000 00000 000 0025 I\) (,,)820713 00021 021 0954 00000 000000 00000 000000 0000 00000 0000 00000 000 0025 820714·00019 019 0973 00000 000000 00000 000000 0000 00000 0000 00000 000 0025 820715 00010 010 0983 00000 000000 00000 000000 0000 00000 0000 00000 000 0025 820716 00016 013 0996 00001 000001 00002 000002 0000 00000 0000 00000 000 0025 820717 00023 018 1014 00002 000003 .00003 000005 .0000 00000 0000 00000 000 0025 820718 00011 008 1022 00001 000004·00002 000007 0000 OCOOO 0000 00000 000 0025 820719 00017 013 1035 00001 000005 .00003 000010 0000 00000 0000 00000 000 0025 820720 00028 021 1056 00000 000005 00000 000010 0000 00000 0000 00000 007 0032 820721 00022 017 1073 00000 000005 00000 000010 0000 00000 0000 00000 005 0037 820722 00026 020 1093 00000 000005 00000 000010 0000 00000 0000 .00000 006 004:J 820723 00023 017 1110 .00000 ·000005 00000 000010 0000 00000 0000 00000 006 0049 820724 00023 000 1110 00015 000020 00007 000017 0001 00001 0000 00000 000 0049 820725 00021 000 1110 00014 000034 00006 000023 0001 00002 0000 00000 000 0049 820726 00015 000 1110 00010 000044 00004 000017 0001 00003 0000 00000 000 0049 820727 00072 000 1110 00047 000091 00023 000050 0002 00005 0000 00000 000 0049 820728 00082 000 1110 00022 000113 00048 000098 0012 00017 0000 00000 000 0049 820729 00269 000 IUD 00073 000186 00158 000256 0038 00055 0000 00000 000 0049 820730 00338 000 1110 00091 000277 .00199 000455 0048 00103 0000 00000 000 0049 Appendix Table 2-:S-5.Continued. DATE TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC DAILY COUNT DAILY CUM DAILY CUM DAILY CUM DAlLY ·CUM DAILY CUM .DAILY CUM 820731 00248 000 1110 00067 .000344 00146 000601 0035 00138 0000 00000 000 0049 820801'00514.000 1110 00032 .'000376 00400 001001 0081 ·00219 dOOl 00001 000 0049 820802 01853 000 1110 00115 .000491 01441 002444 0291 00510 0004 00005 000 0049 820803 03165.000 1110 .00070 000561 02684 005128 '0386 00896 0025 00030 000 0049· 820804 06705 000·1110 00080 000641 05719 010847 0872 01768 0034 00064 000 0049 82Q805 .04643 000 1110 00009 00065.0 04077 ()14924 0488 02256 0069 00133 000 0049 820806 07272 000 1110 00051 000701 05,868 020792 1273 03529 0080 00213 000 0049 820807 06449 •000 1110 00077 00077 8 04889 025681 1354 04883 0129 00342 000 0049 820808 03202·000 1110 00016 000794 02395 :028076 0737 05620 0054 .00396 000 0049 »000819 01108 029184 0780 ·06400 0150 00546 000 0049f\)820809 02063 000 1110 00025•820810 01469 000 1110 00018 000837 00789 029973 0555 06955 0107 00653 000 0049 820811 01624 000 1110 00015 .()00852 00916 030889 0586 07541 0107 00760 000 0049 820812 01803 000 1110 00033 000885 01078 031967 0593 08134 .0099 00859 000 0049 820813 01939 000 1110 00027 000912 01204 033171 0549 .08683 0159 01018 000 0049 820814 01397 000 1110 00020 000932 00868 034039 0395 09078 .0114 01132 000 0049 820815 00868 000 1110 00037 000969 00306 034345 0405 09483 0120 01252 000 0049 820816 00517 000 1110 00022 000991 00183 034528 0241 09724 0071 01323 000 0049 820817 00708 000 1110 00030 001021 00250 034778 0330 10054 0098 01421 000 0049 820818 00693 000 1110 00029 001050 00245 035023 0323 10377 0096 01517 000 OU49 820819 00563 000 1110 00006 001056 00169 035192 0242 10619 0146 01663 000 0049 820820 00509 000 1110 00005 001061 00153 035345 0219 10838 0132 01795 000 0049 820821 00291 000 1110 00003 001064 00087 035432 0125 10963 0076 01871 000 0049 820822 00262 000 1110 00002 001066 00079 035511 0113 11076 0068 01939 000 0049 820823 00299 000 1110 00009 001075 00055 035566 0163 11239 0063 02002 009 0058 820824 00197 000 1110 00006 001081 00036 035602 0107 11346 0042 02044 006 0064 820825 00131 000 1110 00004 001085 00024 035626 0071 11417 0028 02072 004 0068 820826 00130 000 1110 00004 001089 00024 035650 0071 11488 0027 02099 004 0072,,\jfl J ,J )J J .~j i J )J J ~"- )j J J 1 J T 1 J I J ]J 1 J I J 1 ] ')~)l Appendix Table 2-B~5.Continued. DATE '-'.TOTAL CHINOOK SOCKEYE PINK CHUM COHO MISC. DAILY COUNT DAILY,CUM DAILY CUM 'DAILY CUM,DAILY CUM DAILY CUM DA.ILY CUM 820827 00148 000 1110 00007 001096 00000 035650 0085 11573 0053 02152 003 0075 820828 00215 000 1110 00010 001106 00000 '035650 ,0123 11696 0077 02229 005 0080 820829 00178 000 '1110 00008 001114 00000 035650 0102 11798 0064 01293 004 0084 820830 ,00184 000 l110 00009 001123 00000 035650 0105 11903 0066 '02359 004 0088 820831 00192 000 1110 00000 00U23 00000 035650 0134 '12037 0058 02417 000 0088 820901 00096 000 1110 00000 001123 00000 035650 0067 12104 0029 02446 000 '0088 >820902 00086 000 1110 00000 00U23 '00000 035650 0060 12164 0026 ,02472 000 0088 'f\)820903 000 001123 .... (JI 00122 1110 00000 '00000 035650 0085 12249 0037 '02509 _000 0088 820904 00126 000 1110 00000 001123 00000 035650 0070 12319 0056 02565 000 0088 820905 00107 000 1110 00000 001123 00000 035650 0059'12378 '0048 02613 000 0088 820906 00207 000 1110 00000 001123 00000-0356'50 0115 12493 ,0092 02705 000 0088 820907 00114 000 1110 00000 001123 00000,035650 0063'12556 0051 02756 000 0088 820908 00091 000 1110 00000 001123 00000 035650 0051 12607 '0040 02796 000 0088 820909 00.062 000 1110 00000 001123 00000 035650 00.14 12641 0028 02824,000 0088 820910 ,00076 000 1110 '00000 001123 00000 035650 0042 12683 0034 02858 000 0088 820911 00057 000 1110 00000 001123 00000 035650 0032 12715 0025 02883 000 0088 ' 820912 "00053 '000 1110 00000 '001123 00.000 035650 0000 12715 0000 02883 053 0141 820913 00052 000 1110 00000 001123 00000 035650 0000 12715 0000 02883 052 0193 820914 00000 000 1110 00000 001123 00000 035650 0000 12715 0000 02883 000 0193 AI;ASKA RESOURCES LIBRARX U.S.,DEPT.OE LNTERlOll ' Appendix Table 2-B-6.Talkeetna station west bank daily and cumulative sonar counts by species,Adult Anadromous Investigations,Su Hydro Studies,1982. DATE TOTAL CHINOOK SOCKEYE'PINK CHUM COHO MISC. DAILY COUNT DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAI~Y CUM DAILY CUM '. 820704 00131 130 0130 00000 000000·00000 000000 0000 00000 0000 00000 001 0001 820705 00235 233 0363 00000 000000·'00000 000000 0000 00000 0000 00000 002 0003 820706 00274 272 0635 00000 000000'00000 000000 0000 00000 0000 00000 002 0005 820707 00166 165 0800 00000 000000 00000 000000 0000 00000 0000 00000 001 0006 820708 00191 179 0979 00012 000012 00000 000000 0000 00000 0000 00000 000 6006 820709 .00141 132 1111 00009 000021 00000 000000 0000 00000 0000 00000 000 0006 820710 00080 075 1186 00005 000026'00000 000000 0000 .00000 0000 00000 000 0006 82.0711 00048 045 1231 00003 000029 00000 000000 0000 00000 0000 00000 000 0006 820712 00031 031 1262 00000·000029 00000 000000 0000 00000 0000 00000 000 0006 >-820713 00048 048 1310 '.00000 '000029 00000 000000 ·0000 00000 0000 00000 000 0006l\) 0)820714 00079 079 1389 00000 000029 00000 000000 0000 00000 0000 00000 000 0006. 820715 00113 113 1502 00000 .000029 00000 000000 0000 00000 0000 00000 000 0006' 820716 00044 .037 1539 00003 000032 00002 0,00002 0002 00002 0000 00000 000 0006 820717 00045 038 1577 00003 000035 00002 000004 0002 ·,00004 0000 00000 000 0006 820718 00032 028 1605 00002 000037 00001 000005 0001 00005 0000 00000 000 0006 820719 00032 028 1633 00002 000039 00001 000006 0001 00006 0000 OO()OO 000 0006 820720 00047 017 1650 00011 000050 00018 000024 0001 00007 0000 00000 000 0006 820721 00024 009 1659 00005 000055 00009 000033 0001 .00008 0000 00000 000 0006 820722 00055 020 1679 00012 000067 00021 000054 0002 00010 0000 00000 000 0006 820723 00050 018 1697 OOOU 000078 00019 000073 0002 00012 0000 00000 000 0006 820724 00040 003 1700 00022 000100 00014 000087 .0001 00013 0000 00000 000 0006 820725 00088 006 1706 00048 000148 00032 000119 0002 00015 0000 00000 000 0006 820726 00034 002 1708 00017 000165 00012 000131 0001 00016 0000 00000 000 0006 820727 00108 007 1715 00059 000224 00039 000170 0002 00018 0000 00000 000 0006 820728 00240 003 1718 00101 000325 00113 000283 0022 00040 0000 00000 001 0007 820729 00495 006 1724 00207 000532 00234 000517 0045 00085 0000 00000 003 0010 820730 00579 007 1731 00243 000775 00274 000791 0052 00137 0000 00000 003 0013 ,\ I J I ,I i _J .1 j ,J ))•]J J ) )]J --1 J l J )1 ]))J 1 !1• ))) Appendix Table 2-B-6.Continued. DATE TOTAL CHINOOK SOCKEYE PINK CHilli COHO MISC DAILY COUNT DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM DAILY CUM 820731 00242 003 1734 00033 000808 00173 000964 0033 00170 0000 00000 000 0013 820801 00527 006 1740 00072 000880 00377 001341 0072 00242 0000 00000 000 0013 820802 02570 000 1740 00216 001096 01984 003325 0355 00597 0015 00015 000 0013 820803 05502 000 1740 00170 001266 14655 007980 0622 01219 0055 00070 000 0013 820804 08376 000 1740 00126 001392 07538 015518 0637 01856 0075 00145 000 0013 820805 06813 000 1740·00020 001412 06268 021786 0484 02340 0041 00186 000 0013 820806 08321 000 1740 00075 001487 07106 028892 1007 03347 0133 00319 000 0013 820807 07408 000 1740 00015 001502 05956 034848 1304·04651 0133 00452 000 0013 820808 05297 000 1740 00037 001539 04053 038901 0969 05620 0238 00690 000 0013»041728 0941 06561 0203 00893 000 oouI\)820809 04073 000 1740 00102 001641 02827 ......820810 03190 000 1740 00048 001689 01895 043623 0973 0753.4 0274 01167 000 0013 82.0811 02779 000 1740 00042 001731 01651 045274 0847 08281 ·0239 01406 000 0013 820812 02073 000 1740 00006 001737 00962 046236 0877 09258 0228 01634 000 0013 820813 02672 000 1740 00037 001774 01264 047500 1176 10434 0195 01829 000 0013 820814 02302 000 1740 00016 001790 00495 047995 1542 11976 0249 02078 000 0013 8T0815 01198 000 1740 00023 001813 00405 048400 0671 12647 .0099 02177 000 0013 820816 00580 000 1740 00011 001824 00196 048596 0325 12972 0048 02225 000 0013 820817 .00670 000 1740 00036 001860 00216 048812 0297 13269 0121 02346 000 0013 820818 00681 000 1740 00037 001897 00219 049031 0302 13571 0123 02469 000 0013 820819 00685 000 1740 00008 001905 00196 049227 0355 13926 ··0126 02595 000 0013 820820 00715 000 1740 00008 001913 00205 049432 0370 14296 0132 02727 000 0013 820821 00500 000 1740 00006 001919 00143 049575 0259 14555 0092 02819 000 0013 820822 00420 000 1740 00010 001929 00026 049601 0203 14758 0176 02995 005 0018 820823 00306 000 1740 00008 001937 00019 049620 0147 14905 0128 03123 004 0022 820824 00286 000 1740 00007 001944 00018 049638 0138·15043 0120 03243 003 0025 820825 00260 000 1740 00007 001951 00016 049654 0126 15169 0107 03350 004 0029 820826 00176 000 1740 .00016 001967 00008 049662 0087 15256 0057 03407 008 0037 Appendix Table 2-B.,...6.Continued. DATE TOTAL·CHINOOK SOCKEYE PINK CHUM COHO MISC. DAILY COUNT DAILY CUM DAILY CUM DAILY CUM DAlLY CUM DAILY CUM DAILY CUM 820827 00185 000 1740 00017 ·001984 00009 .049671 0090 15346 0060 03467 ..009 0046 820828 00349 000 1740 00032 002016 00016 049687 ·0171 15517 0114 03581 016 0062 820829 00183 ..000 1740 00017 002033 00009 049695 0089 15606 0059 03640 009 0071 820830 00195 000 .1740 .00017 002050 00008 049704 0085 15691 0085 03725 000 0071 >0 820831 ·00230···000 1740 00020 002070 00010 049714 .0100 15791 0100 03825 oob 0071 . I\)820901 00166 .000 1740 0.0014 002084 00007 049721 .0073 15864 0072 03897 000 0071 . CD 810902 0014·5 000 1740 00013 002097 00006 049727 0063 15927 0063 03960 000 0071 820903 00206 oob 1740 .00013 002110 00000·.049727 0053 15980 0100 04060 040 0111· 820904 00148 000 1740 00010 002120 00000 049727 0038 16018 0071 04131 029 0140 820905 00155 000 1740 00010 .002130 00000 049727 0040 16058 0075 04206 030 0170 820906 00099 000 1740 00006 002136 00000 049727 0026 16084 0048 04254 019 0189 820907 00048 000 1740 00012 002148 00000 049727 0006 16090 0012 04266 018 0207. 820908 00053 000 1740 00013 002161 00000 049727 0007 16097 0013 04279 020 0227 820909 00027 000 1740 00007 002168 00000 049727 0003 16100 0007 04286 010 0237 820910 00026 000 1740 00006 002174 00000 049727 0003 16103 0007 04293 010 0247 820911 00010 000 1740 00000 002174 00000 049727 0001 16104 0002 04295 007 0254 820912 00025 000 1740 00000 002174 00000 049727 0002 16106 0006 04301 017 0271 820913 00021 000 1740 00000 002174 00000 049727 0002 16108 0005 04306 014 0285 )\---I J )),J ~J ),J •I 1 .1 )~, 1 fi I I J i I 1 I J j 1 I J"'\)»1 Appendix Table 2-8-7.Sector distribution of sonar counts,adjusted for debris,east bank,Susitna station, Adult Anadromous Investigations,Su Hydro Studies.1982. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total - July 11 33 25 8 4 2 4 5 10 8 18 17 19 1531 - 2 19 16 20 6 3 5 6 3 11 14 18 15 136 3 40 9 15 15 11 7 14 20 16 38 26 29 240 4 38 25 9 14 5 3 6 8 6 13 20 19 166 5 76 34 19 10 2 3 78 15 4 19 34 35 329 6 63 26 9 7 1 0 3 4 13 15 30 40 211 7 48 35 10 8 5 1 9 2 3 20 60 36 237 8 67 28 18 3 2 1 1 1 10 17 38 58 .244 9 60 33 22 5 3 1 3 6 3 7 35 55 233 10 72 38 19 5 2 2 3 11 5 19 22 17 215 »11 56 37 33 9 4 2 0 2 5 6 32 13 199 l\)12 59 43 15 17 3 2 3 3 8 3 24 7 187 CO 13 51 14 18 7 0 0 6 6 6 16 23 51 198 14 50 22 1 3 2 1 6 8 5 11 23 10 142 15 21 33 16 6 5 1 4 3 10 19 36 36 190 16 32 18 34 12 8 4 14 12 13 30 28 30 235 17 94 80 61 42 60 43 97 91 91 173 145 209 1186 18 122 68 55 79 49 54 74 75 102 150 131 140 1099 19 290 412 333 248 264 277 389 402 365 609 601 716 4906 20 197 162 183 III 114 126 181 222 201 393 423 694 ·3007 21 447 83 123 56 75 101 131 282 317 932 655 ..1382 .4584 ?2 201 III 97 76 94 82 149 215 239 878 800 1243 4185 23 952 389 533 405 32 166 376 454 595 1491 1941 3254 10588 24 2895 1646 2115 1507 1057 235 453 358 337 563 993 842 13001 25 2499 1881 3071 2815 2672 1190 1405 1733 1734 2617 3087 3616 28320 26 9791 7297 7610 3153 .1562 141 597 662 418 1451 1246 860 34788 27 3786 4437·.6923 4490 4332 2078 3919 3830 3393 6082 5057 4349 52676 28 2973 3044 5198 4798 4800 2074 5713 7202 6850 13423 12827 14927 83829 29 1570 2760 4355 3753 2607 1365 5773 6~86 5953 11891 19370 .·8896 74579 30 1511 4384 73i'2 5858·3470 1199 5095 5853 4319 8953 6667 6034 60665 31 5724 8903 9774 6662 3023 779 2334 2804 2524 5703 5234·4990 58454 AUc:just 61371177046275804396819196972093297522915659 4797 42737 2 1058 2758 3445 2812 1451 692 2759 3065 2416 5157 6689 6702 39004 Appendix Tabl~2-B-7.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 .Tota 1 - August 3 781 1660 1996 1803 880 445 1976 .2050 1878 3741 4213 3453 ,24876 4 818 1162 1268 861 312 156 703 568 785 1443 1100 1299 .10475 5 615 511 ..635 322 153 .40 222 229 315 592 477 562 4673 6 5.67 '.484 418 247 87 43 142 172 205 442 354 479 3640 7 488 5'11 472 216 53 24 .172 180 238 414 347 535 3650 8 .274 290 317 159 46 18 96 133 199 312 2~5 451 2530 9 258 184 127 101 50 13 67 75 84 162 114 135 1370 10 .278.209 146 77 32 22 47 60 60 186 121 133 1371 11 .165 112 102 46 32 16 56 55 82 132 153 114 1065 12 ·134 153 101 66 23 17 43 54 54 112 255 165 1177 >13 148 166 190 62 31 20 37 57 53 112 146 92 1114 c,.)14 118 96 58 51 28 20 43 59 64 142 96 101 876 0 15 126 114 89 51 23 17 33 43 .61 114 65 61 797 16 124 117 80 34 21 14 40 41 54 74 .34 41 674 17 66 51 47 32 23 10 32 52 51 82 55.52 553 18 83 67 45 39 19 .10 23 .44 24 50 40 29 473 19 85 53 31 37 15 21 15 41 32 85 33 27 475 20 102 67 41 36 33 11 18 34 27 50 42 33 494 21 60 53 52 38 26 13 29 31 38 37 .39 30 446 22 68 47 30 41 26 14 14 14 18 28 31 38 369 23 60 43 60 .43 31 18 25 37 41 32 59 37 486 24 62 43 48 25 17 15 28 21 33 45 53 37 427 25 53 24 21 26 18 5 24 26 21 22 42 34 316 26 35 33 35 40 25 7 22 16 25 23 33 33 327 27 63 41 36 23 19 17 26 26 15 23 25 28 342 28 38 49 26 49 29 13 26 17 24 41 42 54 407 29 33 44 32 20 21 7 28 20 20 22 23 32 302 30 34 31 23 25 12 12 24 22 27 38 50 47 345 31 40 32 33 10 11 5 16 36 31 40 27 29 310 September 1 40 31 42 24 13 12 32 34 37 59 32 40 396 2 46 37 36 18 30 9 32 18 25 33 44 35 363 , J .1 .~I .~J 1 J J I :1 1 8 J J I ~m J j I ».---1 J 1 )J 1 I j )J Appendix Table 2-8-7.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total -- September 3 23 19 23 14 21 13 34 21 22 28 30 24 272 4 29 31 20 11 8 9 13 28 .14 33 39 24 259 5 30 27 32 22 12 10 23 34 19 33 37 24 303 TOTAL 42609 50070 63980 45633 29819 12432 35859 40971 36947 75172 80955 72429 586876 PERCENT 7.3 8.5 10.9 7.8 5.1 2.1 6.1 7.0 6.3 12.8 13.8 12.3 »-- Co\)y 60 foot substrate deployed.- Appendix Table 2-8-8.Sector distribution of sonar counts,adjusted for debris,west bank,Susitna station, Anadromous Adult Investigations,Su Hydro Studies,1982. ~ - Sector Date 1 2 3 4·5 6 7 8 9 10 11 12 Total - July 11 41 10 1 0 0 0 o·0 a 6 1 0 591 - 2 44 6 2 8 4 1 a 0 0 4 4 7 80 3 23 16 2 4 5 2 2·4 2 2 2 13 77 4 52 8 0 a 0 a 1 a 4 4 0 II 8Q 5 n.22 5 a 0 0 0 a a a 3 4 106 6 43 14 2 0 0 0 a a a 2 2 7 70 7 86 29 4 2 0 ·0 0 a a 0 a 0 121 8 108 19 a a 1 a a a 1 .1 a 0 130 9 73 32 6 5 5 5 0 a a 0 2 1 129 10 41 6 6 7 6 6 a 1 a a 3 2 78 >11 45 5 a a a 0 1 0 a 1 a .2 54 ~12 53 4 1 1 a 0 1.a a 4 0 1 65 I')13 23 2 3 1 ·0 0 0 7 3 0 1 2 42 14 50 11 1 a a 0 2 8 4 6 1 5 88 15 35 12 0 1 0 a a a a 1 0 4 53 16 91 37 2 3 ()a 0 3 7 10 1 3 157 17 305 133 54 46 30 30 29 25 40 64 54 29 839 18 673 334 218 158 83 83 171 186 233 577 547 353 3616 19 5559 2459 1022 505 79 29 228 303 743 1575 1098 763 14363 20 5575 1805 1020 403 63 15 177 170 576 1418 1068 718 13008 21 7607 2207 1635 533 299 269 116 146 242 353 227 17.4 13808 22 10797 2152 787 229 109 3 53 77 36 39 32 75 14389 23 3352 2613 629 141 112 111 121 127 135 241 217 218 8017 24 21 3074 1889 219 49 38 76 3 15 42 35 56 122 5618 25 -180 232 36 6 a a a 4 0 12 18 10 498 26 27 28 29 30 31 August 1 2 .~ ~J J ;1 l J J B ,,I ,I I ) 1 )J j ]~I ]I -I 1 i J I ---J .~J9 J ) Appendix Table 2-B-8.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total August 3 4 3/112 60 39 3 6 1 5 1 6 5 30 124 3925 - 6 242 122 94 11 5 7 11 6 3 14 28 104 647 7 173 111 68 7 4 1 5 2 2 2 7 22 404 8 172 78 73 9 3 2 4 4 2 4 5 11 367 9 36 47 20 11 11 10 2 0 0 1 1 0 139 10 66 31 25 8 10 7 2 2 1 0 6 2 160 11 60 36 39 5 1 2 2 1 0 o ,7 0 153 12 141 57 19 5 0 1 2 1 0 0 1 52 279»13 111 43 26 2 3 1 0 3 3 10 31 27 260 (,I)14 117 51 2 0 0 0 0 2 3 19 16 20 230 (,I)15 65 13 2 1 0 0 0 0 3 1 8 27 120 16 57 12 2 0 0 0 ·0 0 0 4 2 7 87 17 12 10 2 0 0 0 0 0 0 8 12 14 58 18 45 26 ?0 0 0 0 0 0 3 5 4 85 19 49 15 4 0 0 0 0 0 0 2 6 14 90 20 62 24 0 0 0 0 0 0 0 0 0 8 94 21 48 15 1 0 0 0 0 0 0 1 1 5 71 22 53 35 2 0 0 0 0 0 1 0 3 10 104 23 32 30 2 0 0 0 0 0 0 4 5 15 88 24 19 22 4 4 4 4 2 2 3 8 2 8 82 25 38 33 0 0 0 0 0 0 0 0 1 8 80 26 23 29 1 0 0 0 0 0 0 0 0 13 66 27 71 38 5 0 0 0 0 0 0 0 3 7 124 28 42 39 10 0 0 0 0 0 0 0 0 5 96 29 52 22 0 0 0 0 0 0 0 0 1 10 B5 30 36 28 3 0 0 0 0 0 0 0 3 11 81 31 56 33 1 0 0 0 0 0 0 0 0 2 92 September 1 31 19 0 o·0 0 0 0 0 0 0 3 53 2 36 27 0 0 0 0 0 0 0 5 1 5 74 Appendix Table 2-8-8 ..Continued. Date 1 2 3 4 September 3 19 24 0 0 4 33 27 7 0 5 20 35 3 0 >TOTAL.40131 15249 .6111 ·2168 6)PERCENT 49.9 19.0 7.6 2.7 ~ ]j 60 foot substrate deployed. y Eleetronicspulled.at 1200,substrate to be moved. Y New location 1.6 miles downstream. Sector 5 6 7 8 9 10 11-12 Total 0 0 0 0 0 0 4 9 56 0 0 0 o .0 0 0 6 .73 0 0 0 0 0 0 1 .9 68 881 666 940 n03·2095 4446 3527 3086 80403 1.1 0.8 1.2 1.4 2.6 5.5 4.4 3.8 . )~ I __I J ]J .._J I J J I J J J J J I J J 1 J )1 J 1 j 1 1 1 J I 1 )» Appendix Table 2-B-9.Sector distribution of sonar counts,adjusted for debris,north bank,Yentna station, Adult Anadromous Investigations,Su Hydro Studies,1982. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total - June 1/ 1 2 0 0 0 0 0 0 0 4 0 1 828- 29 11 7 0 0 a a a a a a a 4 ?? 30 8 3 2 a a a a 1 2 1 7 1 25 July 1 26 8 3 a a a 1 3 2 7 8 17 75 2 24 10 a a a 0 a 1 1 a 0 11 47 3 23 13 2 0 a a 2 1 a 6 23 31 101 4 15 1 2 1 1 a a '14 a 1 10 30 75 5 19 12 a a a a a 0 a 0 1 34 66»6 2/5 6 a a a a 7 0 8 a 8 1 35 (a)7 -3 1 0 a a a a a a a a 24 28 (JI 9 7 0 0 0 a a a a a a a a 7 10 19 4 1 0 a a a a a a a 7 31 11 19 13 2 1 0 a a a a a a 1 36 12 6 14 1 a 0 a a a 0 2 7.1 26"13 13 2 a a a a a 0 0 0 a 0 15 14 12 3 1 a a a a 0 a a 7 a 23 15 47 7 4 0 0 a a a 0 0 a 0 .58 16 15 2 2 0 a a a 0 a a a a 19 17 71 12 a a a a a a 0 a a 1 84 18 209 54 11 a a a a a a a a 2 276 19 641 250 72 0 a a a a a 2 6 81 105?. 20 3665 1018 148 1 1 a a a 0 a 11 97 4941 21 6182 1478 160 4 0 0 a a a a 1 69 7894 22 2436 645 93 5 a a a a 0 a a 13 319? 23 597 535 192 8 1 a 2 a 1 6 33 97 1472' 24 213 .174 33 a 0 a 0 1 0 1 11 46 479 25 301 126 30 1 a 0 0 a 0 3 28 79 568 26 247 45 0 a a a a a 0 a 1 a 293 27 506 340 254 54 13 10 0 1 0 a 4 38 Ina 28 1775 1176 933 272 46 26 5 1 0 a 2 86 4322 Appendix Table 2-B-9.Continued. Sector Date 1 2 3 4'5 6 7 8 9 10 11 12 Total -- July 432931861285 1457 4?2 102 15 9 6 6 7 31 6569, 30 2193 3217 3084 934 159 35 200 96 24 35 81 49 10107 AUQust i 7508 4050 3737 1626 348 74 258 192 74 50 266 666 13849 2 3366 7750 2846 1081 205 50 165 108 41 22 254 321 16199 3 4385 2041 459 95 15 0 2 0 0 0 14 154 7165 4 3903 182 729 117 7 3 2 1 3 0 81 102 5130 5 2463 967 319 65 4 0 2 0 0 0 28 27.2 4070 6 836 207 47 9 0 0 0 0 0 0 5 18 1122 >7 720 206 70 5 0 0 0 0 0 0 2 6 1009 (,)8 862 239 69 14 0 1 12 5 7 14 34 31 1288c»9 912 188 117 30 3 1 22 27 36 104 103 116 1659 10 699 190 86 24 5 2 13 30 24 72 77 101 1323 11 435 ]63 70 15 4 1 26 32 16 92 47 111 1012 12 510 130 30 4 1 0 16 7 25 54 29 67 873 13 364 111 54 9 2 0 14 19 19 38 87 89 806 14 315 45 5 0 0 0 5 5 3 12 5 9 404 15 164 37 29 1 0 0 5 5 2 1 2 22 268 16 161 65 36 3 0 0 4 4 2 23 10 0 308 17 202 97 38 5 0 0 2 10 6 12 29 40 441 18 168 99 42 5 0 0 1 7 11 14 31 30 408 19 178 82 34 12 0 0 7 4 1 5 7 14 344 20 164 30 18 2 0 0 2 3 0 14 10 10 253 21 115 24 1 0 0 0 0 0 0 0 0 0 140 22 135 21 4 1 0 0 0 0 0 2 11 5 179 23 110 18 0 0 0 0 0 0 0 8 16 4 156 24 86 36 3 0 0 0 2 1 0 0 6 0 134 25 96 38 11 0 0 0 0 1 0 0 '(7 155 26 197 29 9 0 0 0 0 1 (1 0 1 2 239 27 158 2?2 1 0 0 0 0 0 0 1 1 185 28 ]57 17 4 0 0 0 2 0 0 2 1 0 183 29 74 6 3 0 0 0 0 0 1 0 0 0 84 30 109 24 0 0 0 0 0 0 0 0 0 7 135 31 137 26 1 0 0 0 0 0 0 0 0 2 166 ---- •\ ,J J J J J ~l J J .!))I i .~J J .~ 1 1 I ]1 J I i I ~I I 1 J))) Appendix Table 2-8-9.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total September I 78 18 3 1 a a a a a a a a 100 2 237 47 13 0 0 a a 0 0 1 32 113 443 3 :?74 22 10 0 0 a 0 0 0 a 2 46 354 >4 62 18 0 0 0 0 a a 0 1 5 6 92 CAl...,TOTAL 47835 27708 15386 4828 917 236 794 590 315 615 1449 3169 103842 PERCENT 46.1 26.7 14.8 4.6 0.9 0.2 0.8 0.6 0.3 0.6 1.4 3.0 }j 60 foot substrate deployed. ?J Data off due to electronic malfunction from 2300 7/7 to 2000 7/9. Appendix Table 2-8-10.Sector distribution of sonar counts,adjusted for debris,south bank,Yentna station, Adult Anadromous Investigations,Su Hydro Studies,1982. Sector nate 1 2 3 4 5 6 7 8 9 10 11 11'Total - June 1/ 13 2 6 4 3 0 3 0 1 0 1 10 4327- 28 20 13 7 2 2 0 2 6 2 0 1 4 59 29 19 5 0 0 0 0 a 0 0 0 0 0 ~4 30 4 1 1 0 0 0 1 0 1 0 0 0 8 July 1 3 1 1 0 0 0 a 0 5 16 1 3 30 2 2 0 0 0 0 0 a 0 0 a 0 0 7 3 7 1 a 0 a 0 7 3 4 31 14 37 104 4 14 1 0 0 0 0 5 4 8 18 5 46 101 >-5 20 .1 0 0 0 0 4 1 3 7 6 22 64 (,.)6 17 0 0 0 0 0 i 0 2 a 0 19 39 Q)7 27 0 0 1 0 0 a 0 0 0 9 3 40 8 159 25 7 3 0 0 0 0 0 2 0 0 196 9 56 0 3 0 0 0 0 0 0 4 3 0 66 10 16 a 0 0 0 0 0 0 0 0 0 0 16 11 12 0 0 0 0 0 0 0 0 0 0 0 12 12 18 1 0 0 0 0 0 1 0 0 0 0 20 13 19 10 0 1 0 0 1 0 1 a a 1 33 14 42 10 5 0 0 0 0 0 9 0 3 5 74 15 29 18 7 0 2 0 1 4 6 0 2 2 71 16 38 76 15 4 4 1 0 4 2 3 5 2 154 17 459 605 246 96 22 1 50 J9 50 58 41 40 1687 18 1078 1354 633 232 40 2 69 66 80 144 123 107 3928 19 5010 7241 2711 868 199 18 316 285 437 447 448 308 18288 20 7983 9037 2360 fi15 84 8 146 189 235 363 31'5 403 ::>1748 21 12524 10450 1768 299 30 3 39 43 24 79 40 51 25350 22 4291 10797 2305 311 30 1 31 14 18 1'2 17 14 17751 23 1985 8717 2386 350 34 1 57 45 44 70 71 71 13831 24 15937 9232 1673 217 19 1 29 17 22 31 43 16 27237 25 11686 4996 1533 ;>08 21 0 37 46 87 84 68 90 18856 26 10046 6610 1773 125 19 1 32 21 36 74 71 88 18896 27 5371 8766 4535 858 281 65 504 460 506 552 483 526 22907 28 12591 13952 6250 1100 394 107 936 1169 1059 557 483 425 40728 ).~~ D J J 1 ,J ,I ___J ••J __..J I ~J J J :I 1 --1 J J I 1 J 1 ) I J 1 I I ) ) I J Appendix Table 2-8-10.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total July 29 18491 16089 6745 1021 396 133 992 797 876 1278 1228 827 48873 30 23047 14966 5047 526 118 20 248 '186 135 296 283 163 45035 31 13046 16146 6494 544 132 38 184 170 205 335 155 154 37603 August 1 6336 13820 10776 1430 406 136 925 1068 1104 694 481 578 37754 2 7578 12160 7932 1416 455 156 967 890 1062 1285 821 861 35583 3 9416 9419 4026 1212 344 88 555 522 556 910 698 635 28381 4 1562 2119 1107 497 416 219 733 657 461 698 838 1029 10336 5 1584 1556 852 527 273 150 467 457 381 457 541 825 8070 6 825 699 553 267 121 97 350 310 162 207 187 344 4122 »7 757 622 477 233 123 89 292 202 139 83 175 207 3399 8 611 560 465 264 128 71 279 160 112 135 149 237 3171(,A)9 544 377 301 149 86 56 162 103 74 134 121 481 2588CO1026412911851185641115763347672703940 11 421 207 149 59 38 14 31 47 30 18 15 57 1086 12 316 154 103 27 15 11 20 9 7 6 17 11 696 13 390 115 36.19 6 0 11 3 14 25 40 135 794 14 497 102 27 8 2 0 16 21 18 19 53 35 798 15 152 46 25 5 3 0 4 6 5 8 8 32 294 16 137 16 24 0 1 0 4 1 1 1 3 5 193 17 143 31 19 4 3 0 5 4 6 4 6 5 230 18 100 20 25 4 2 0 9 0 3 10 22 3 198 19 130 29 22 6 3 0 10 6 6 11 26 24 273 20 78 68 29 4 0 1 6 10 3 25 10 23 257 21 74 41 9 0 0 0 1 0 0 0 9 4 138 22 37 16 1 1 0 0 1 0 4 1 14 1 76 23 118 30 11 2 1 0 8 5 5 5 5 5 195 24 166 37 29 4 0 0 5 1 2 1 6 14 265 25 118 52 17 4 3 0 1 5 1 5 0 13 219 26 III 13 20 3 1 0 0 0 0 0 0 22 170 27 103 33 2 0 0 0 0 1 5 6 0 32 182 28 157 37 16 3 0 0 1 4 0 0 0 14 232 29 192 19 13 1 0 0 1 0 0 0 1 61 288 30 43 15 3 3 1 0 0 0 0 0 0 157 222 31 67 42 10 1 0 0 0 0 0 0 0 0 120 Appendix Table 2-8-10.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 1-1 12 Total - September 1 175 18 5 I 1 0 0 0 2 2 0 9 213 2 187 35 7 1 0 0 5 0 0 0 8 31 274 3 127 48 19 3 0 0 2 0 0 1 0 47 247 4 101 10 6 3 0 0 1 0 0 2 3 205 331 5 39 11 11 3 0 0 0 2 0 0 0 4 70 >TOTAL 180113 181991 73723 13667 4318 1529 8682 7820 8054 10161 8838 10383 509279 ~PERCENT 35.4 35.7 14.5 2.7 0.9 0.3 1.7 1.5 1.6 2.0 1.7 2.0 0 - 1/60 foot substrate deployed. ),\ .>/ Y J ))J I I 1 )D I ••J J J J J J J 1 1 j J 1 I 1 )1 .~J 1 )) }J )J ) } Appendix Table 2-B-ll.Sector distribution of sonar counts, adjusted for debris,east bank,Sunshine station, Adult ARadromous Investigations,Su Hydro Studies,1982. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total - July 1/ 6 16 31 11 29 26 26 31 9 15 13 9 2226- 7 12 22 42 51 62 72 81 52 25 18 17 8 462 8 21 25 70 52 65 70 54 30 14 14 5 5 425 9 23 32 47 49 72 61 61 35 23 19 5 6 433 10 12 27 60 28 39 59 61 44 34 17 3 13 397 11 14 28 24 11 28 31 36 25 8 6 3 2 216 12 12 14 20 21 19 49 39 22 11 6 3 3 219 13 4 .10 7 10 7 26 12 14 10 4 5 3 112 14 11 11 4 5 2 11 22 10 5 3 3 0 87 15 14 16 18 5 17 12 14 10 6 1 2 1 116>16 13 13 22 5 6 10 6 7 3 4 0 0 89 ".17 17 10 6 8 1 4 3 2 6 0 3 0 60 ~18 12 ·17 11 7 2 1 0 1 1 1 1 2 56 19 15 41 63 32 18 18 11 13 7 4 0 0 222 20 71 210 284 128 80 63 92 32 21 13 7 12 1013 21 994 1313 1316 798 753 545 .349 268 157 105 46 72 6716 22 706 1075 1355 .771 1233 631 593 474 232 198 157 123 7548 23 1831 2221 2473 1266 807 718 645 503 391 379 212 135 11581 24 2486 1001 665 369 118 113 28 57 49 101 28 80 5095 25 2067 466 314 141 385 40 22 28 55 32 22 29 3601 27 4879 383 118 127 5507 28 9432 1299 523 425 11679 29 16326 2676 873 1582 21457 30 20608 2192 580 728 24108 31 14960 922 332 908 17127 August 1 30386 4561 1722 802 37471 2 35156 10513 1650 573 47892 3 47332 7519 2001 341 57193 4 39607 8934 2574 390 51505 5 26551 6782 3045 760 37138 6 26244 7590 3310 2449 39593 Appendix Table 2-8-11.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total - August 7 20069 6353.3481 2861 32764 8 11071 4250 2868 3183 21372 9 7593 3285 1527 2288 14693 10 5104 2221 1431 4962 13718 11 5857 2811 2144 10664 21476 12 6008 2959 2132 1943 13042 13 4308 2645 1198 550 8701 14 4548 1990 840 473 7851 15 1424 450 1213 694 3781 16 1258 795 604 261 2918>17 1149 786 344 236 2515 ~18 804 435 301 115 45 1700 I\)19 1161 464 208 77 93 2003 20 872 346 165 56 65 1504 21 513 307 158 48 108 1134 22 345 405 142 83 25 1000 23 354 378 177 64 38 1011 24 338 229 83 56 72 778 25 353 133 82 34 68 670 26 260 136 73 56 31 556 27 253 123 101 54 47 578 28 161 123 85 47 H!434 29 176 83 59 15 333 30 199 61 40 60 360 31 144 43 7 10 204 September 1 250 60 29 24 363 2 728 121 36 47 932 3 299 91 27 11 428 4 33 36 19 10 98 5 152 63 20 15 250 6 220 76 21 16 333 7 233 52 19 17 321 8 179 49 8 9 245 ), _J I I J )I J ~))J 1 "..1 J J I ]J 1 ....J j ]-1 1 J ...]j 1 I J 1 j •1 ]j \)"it. J } Appendix Table 2-B-11.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total September 9 127 41 5 4 177 10 97 21 1 2 121 11 82 22 4 6 114 12 9 2 2 0 13 >TOTAl 2+3 369953 95887 41262 40114 610 547826 "..PERCENT 67.5 17 .5 7.6 7.3 0.1 (,) y 2/ 3/ 20 foot substrate deployed. Twelve sector counts are adjusted to be compatible with 4 sector counts for percent total calculations. When sonar substrate consists of 5 instead of 4 sectors the distance counted per sector decreases by a factor of 0.2. Appendix Tab1e2-B-12.Sector distribution of sonar counts~adjusted for debris,west bank,Sunshine station, Adult Anadromous Investigations,Su Hydro Studies,1982. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total -- July 1/ 3 2 0 0 0 2 1 1 0 1 0 0 106 - 7 4 .5 0 0 0 0 0 0 0 0 0 2 11 8 3 10 0 1 1 0 0 0 0 0 0 0 15 9 7 4 2 0 0 0 0 0 0 0 0 0 13 10 ·0 0 1 0 a 0 1 0 0 0 0 0 2 11 1 0 1 0 0 0 0 0 0 0 0 0 2 12 1 3 0 0 0 0 0 0 0 0 0 0 4 13 2 a 3 0 0 0 1 2 0 0 0 0 8 14 6 1 0 0 a a 0 0 0 a 0 0 7 15 0 1 3 0 0 0 0 0 0 0 0 a 4 >16 7 6 2 a a 0 0 0 0 0 0 1 16 ,fliI.17 7 3 3 0 a 1 0 0 a 1 0 a 15 ,fliI.18 15 9 3 2 a a 0 0 0 0 0 0 ~9 19 13 14 4 1 a 0 a 0 0 a 0 a 32 20 36 45 22 0 a 0 0 0 a 0 1 1 105 21 64 100 89 17 1 0 2 3 1 1 2 5 285 22 184 252 160 26 8 a 1 3 5 6 0 7 652 23 299 127 266 25 4 0 3 2 2 1 1 3 733 24 331 94 43 1 a a 2 0 0 a 0 0 471 25 2/485 120 15 3 0 0 4 0 a 0 2 a 629 26 - 27 252 4 2 a a 0 a 0 0 0 0 2 260 28 458 243 24 7 2 1 2 1 1 1 3 15 758 29 987 993 325 51 5 0 6 2 2 4 1 11 2387 30 1477 556 128 4 0 0 3 1 1 0 1 18 2189 31 3617 342 80 8 0 0 2 2 0 0 0 1 4052 August 1 2714 973 331 28 3 0 8 4 6 9 2 17 4095 2 6086 3845 1487 234 47 0 63 31 28 63 59 125 1206~ 3 3369 3705 ?J86 355 208 39 207 94 97 142 135 272 11010 4 4791 2551 1358 468 346 110 162 141 86 106 161 415 10695 )•J J J .J J J I ~,I J )]m )I I ) 1 .))OJ -.I 1 J i 1 1 !J 1 1 )]1 )., Appendix Table 2-B-12.Continued. Sector Date 1 2 3 4 5 ·6 7 8 9 10 11 12 Total August 5 4661 2558 1327 273 68 8 175 112 61 85 160 353 9841 6 3057 1888 1046 264 73 5 100 77 65 52 62 157 6846 7 1625 1488 973 225 59 5 96 56 52 61 85 177 4902 B 900 674 392 113 20 0 23 13 8 7 22 41 2213 9 591 451 313 100 18 0 24 18 7 9 18 33 1582 10 512 442 252 80 13 0 20 14 12 14 18 57 1434 11 667 464 353 135 40 2 70 55 32 45 61 102 2026 12 746 398 428 189 81 8 130 111 64 69 94 1'32 2550 13 700 353 295 184 78 9 214 158 90 87 105 256 2529 >14 541 286 213 137 62 4 109 95 68 57 66 92 1730 15 599 200 151 57 9 2 14 8 5 7 6 28 1086~16 243 207 197 64 22 0 38 25 9 9 11 56 881en17310217156732523615916671936 18 164 145 92 51 23 0 39 25 14 9 21 18 601 19 211 145 126 49 24 3 34 14 17 11 15 37 686 20 217 122 98 53 25 3 52 37 18 13 23 33 694 21 243 217 112 68 25 3 ~5 .12 10 13 18 22 798 22 138 144 74 31 23 2 33 20 8 17 12 49 551 23 108 43 30 30 12 3 11 3 2 3 5 9 25g. 24 120 64 24 6 3 1 15 7 10 6 20 13 289 25 129 49 26 13 4 0 11 4 3 6 14 0 259 26 117 40 22 16 20 0 26 10 8 15 11 5 290 27 81 27 15 9 8 0 9 17 9 13 17 28 233 28 117 23 15 14 7 1 7 10 4 8 9 5 220 29 136 20 10 17 7 1 9 12 6 1 4 6 229 30 146 56 37 4 0 0 7 5 3 5 4 3 270 31 146 26 10 5 2 0 0 0 1 0 1 0 191 I September 1 170 72 30 7 4 0 2 9 3 2 1 9 309 2 137 51 19 11 1 0 4 0 1 4 0 2 230 3 78 4 4 2 5 0 0 0 0 1 0 0 94 4 189 33 17 S 8 0 5 5 8 1 2 10 286 5 162 37 72 12 1 0 tl 4 1 4 0 4 251 6 132 45 21 12 2 0 3 1 3 1 16 2 238 7 91 32 21 9 6 0 3 0 2 7 3 1 175 Appendix Table 2-8-12.Continued. Sector -- Date 1 2 3 4 5 6 7 8 9 10 11 12 Tota 1 September - 8 95 60 13 3 2 0 2 3 1 1 0 0 180 9 72 21 19 3 2 0 4 2 0 0 1 4 128 10 73 8 8 2 4 0 0 2 0 0 4 1 102 11 92 16 5 4 2 0 1 4 1 0 0 8 133 12 18 8 0 1 0 0 0 0 0 0 0 0 27 TOTAL 43753 25144 13704 3565 1413 215 1853 1250 844 994 1283 2819 96837>PERCENT 45.2 26.0 14.1 3.7 1.5 0.2 1.9 1.3 0.9 1.0 1.3 2.9 ". 0) 1/40 foot substrate deployed. y No data,electronics pulled due to high water . .~.~ J !J I J )!t J 5 I J J J J I I J ~)1 1 I I 1 J J 1 !1 1 I 1 ]1 ] )) Appendix Table 2-B-13.Sector distribution of sonar counts,adjusted for debrisj east bank,Talkeetna station, Adult Anadromous Investigations,Su Hydro Studies,1982. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Tota 1 J u l y l / 32 8 13 3 0 0 2 3 2 1 3 8 754- 5 80 36 32 6 4 0 10 6 7 4 7 7 194 6 84 35 18 3 6 1 5 7 7 4 -5 10 185 7 70 65 n 9 :1 1 9 3 1 3 0 0 187 8 23 14 13 2 0 1 3 4 3 4 1 1 69 9 36 12 14 2 1 1 2 0 0 1 1 1 71 10 26 25 19 10 1 0 0 1 0 0 0 7 89 11 21 5 10 3 0 0 1 0 0 0 0 4 44 12 18 11 5 3 1 0 0 0 0 0 0 0 38 13 8 0 5 1 0 1 1 1 1 1 1 6 26 >-14 15 2 1 0 1 0 0 0 0 0 0 0 19•15 4 2 4 0 0 0 0 0 0 0 0 0 10....16 11 2 3 0 [)0 0 0 0 0 0 0 16 17 11 2 7 1 0 0 0 2 0 0 0 0 (3 18 7 0 1 1 0 0 0 1 0 1 0 0 11 19 12 4 0 0 0 0 0 1 0 0 0 0 17 20 10 6 6 1 0 2 0 0 0 0 0 0 25 21 17 6 2 1 1 0 0 0 0 1 0 0 28 22 20 2 3 0 0 0 0 1 0 0 0 0 26 23 12 7 2 0 0 0 2 0 0 0 .(J 0 23 24 14 4 1 2 0 0 0 3 0 0 0 0 23 25 9 5 5 0 0 0 0 0 0 0 3 0 22 26 3 7 2 ?0 0 1 0 0 0 0 0 15 27 22 34 9 1 0 0 2 2 1 0 0 1 72 28 16 33 12 11 0 1 1 2 3 2 1 0 82 29 65 105 42 16 5 0 15 7 3 8 2 1 269 30 79 154 50 15 3 3 16 8 2 3 2 1 336 31 72 96 29 0 2 0 12 6 2 0 0 1 220 Auguq 1 166 207 65 14 19 1 25 11 3 3 0 (l 514 ')546 897 2?J 54 ?:1 2 61 11 10 13 3 6 1853I. 3 1136 1375 396 119 (9 8 48 54 21 17 9 3 3165 4 1252 2245 757 712 49 5 35 37 23 14 5 9 4643 Appendix Table 2-B-13.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 It Tota 1· - :August 951841338610062446012645410 7 .12 6705 6 1412 3736 1272 .332 68 13 1?9 82 53 32 12 '(7 7168 7 1025 3509 1312 295 .74 12 91 58 22 15 9 27 6449 8 399 1742 655 208 56 9 61 35 8 9 6 14 3202 9 209 961 398 1t8 37 10 35 28 10 6 6 19 1847 10 157 695 340 135 34 4 46 22 12 3 5 16 1469 11 110 784 448 138 33 a 35 20 8 4 6 17 1603 12 110 756 560 195 37 6 43 23 5 2 8 16 1761 13 312 772 493 151 32 2 46 20 9 9 8 15 1869 14 373 546 228 67 11 1 18 5 3 5 6 11 l?74 »15 218 373 181 34 10 1 10 4 3 0 4 13 851•16 160 195 122 28 3 0 5 0 1 2 0 1 517 03 17 185 306 150 38 7 0 11 3 0 0 2 6 708 18 259 268 127 21 4 0 3 4 1 2 1 3 693 19 161 220 111 37 4 2 10 1 1 1 1 7 556 20 95 211 127 45 6 1 5 3 5 2 0 3 503 21 39 96 92 27 5 0 5 5 0 0 1 1 271 22 57 95 78 26 0 0 3 0 1 0 1 0 ?62 23 71 133 71 12 2 1 3 2 1 0 0 3 299 24 40 83 55 10 0 0 2 0 1 2 2 1 196 25 16 25 39 13 0 0 2 0 0 0 2 1 98 26 33 64 27 2 0 0 2 0 1 1 0 0 130 27 26 70 40 6 2 0 0 2 0 1 0 1 148 28 44 113 42 6 0 1 5 1 0 1 1 0 214 29 30 98 33 10 3 0 1 0 0 0 0 0 175 30 26 103 40 11 1 0 3 0 0 0 0 0 184 31 40 108 29 10 1 0 0 (1 0 0 0 0 ISS September 1 18 25 P.4 0 0 2 0 !)0 0 0 57 2 26 45 9 :;0 0 0 (1 ()0 n 0 82 3 29 60 12 3 1 ?1 [1 0 0 ()0 108 4 50 52 18 5 0 0 1 0 ()0 0 0 126 5 34 48 15 7 0 0 3 0 0 0 0 I)107 6 90 87 14 6 "1 7 0 0 0 0 0 207L 7 45 44 12 8 0 0 3 0 0 0 0 0 112 8 34 31 15 5 2 0 1 0 0 0 1 1 90 )l B )J J J -~J ).B J J J 1 I J I J ]J i --1 )1 )I 1 ].)]]J ]1 j ]1 1 "1;;)j , J Appendix Table 2-8-13.Continued. Appendix Table 2-B-14.Secto~distribution of sonar counts,adjusted for debris,west bank,Talkeetna station, Adult Anadromous Investigations,Su Hydro Studies,1982. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total July 1/ 11 10 5 13 10 20 16 17 12 9 3 5 1314- 5 15 23 ]6 10 26 19 25 29 17 18 18 17 '.133 6 4 14 23 17 52 79 41 37 19 14 9 15 274 7 3 9 5 13 17 19 28 19 24 20 5 4 166 8 8 11 18 23 25 20 17 28 12 10 11 7 190 9 11 6 20 18 21 10 10 13 9 5 1 1 125 10 18 26 12 7 7 1 4 3 0 1 I 0 80 11 4 9 12 9 5 2 1 4 2 0 0 0 48 12 3 14 4 3 4 1 0 1 0 0 1 0 31 13 10 8 10 1 2 10 1 2 1 2 0 1 48»14 12 26 14 11 4 6 2 1 2 1 0 0 79 en 15 32 27 13 8 14 12 1 3 0 1 1 1 113 0 16 8 19 2 2 7 2 3 0 0 1 0 0 44 17 19 11 1 0 5 3 4 2 0 0 0 0 45 18 6 9 6 3 3 2 1 0 0 1 0 1 32 19 14 4 5 1 2 2 .2 0 1 0 0 1 32 20 33 9 4 2 2 0 0 0 0 0 0 0 50 21 8 7 3 1 3 0 1 1 0 0 0 0 24 22 6 19 8 1 2 2 5 0 8 3 0 1 55 23 4 20 13 2 3 6 1 1 0 0 0 0 50 24 2 7 8 12 4 4 2 I 0 0 0 0 40 25 28 18 16 10 4 1 2 4 1 0 0 0 84 26 7 20 12 4 6 0 0 0 0 1 0 0 50 27 29 19 30 15 7 4 3 3 I 0 0 0 111 28 10 61 102 33 9 6 8 7 2 2 0 0 240 29 76 176 133 30 15 22 23 15 2 2 1 0 495 30 70 195 172 74 28 14 II 9 3 0 I 0 577 31 12 51 84 49 1'6 10 2 Ii 2 0 0 0 24? August 1 34 92 228 84 34 17 18 13 5 I'0 0 527 2 603 727 60R ?l'6 1'33 77 38 ~?4 I'0 0 2550J,_ 3 1097 2049 1165 423 410 169 101 45 7 III 14 4 5502 4 1582 3512 1664 673 511 193 96 81 31 14 8 11 8376 5 1026 2316 1872 768 452 156 III 68 19 17 5 3 6813 6 1126 2213 2749 1287 454 232 103 78 38 18 10 13 8371 -_._----- ~, J )I J )!,,J J I I ~I J I I J , )1 I 1 J 1 )J 1 ]1 ]1 ]B J ] ))) Appendix Table 2-B-14.Continued. Sector Date 1 2 3 4 5 6 7 8 9 10 11 12 Total - ...""".." August 7 847 1770 2379 1289 634 242 90 92 35 9 7 14 7408 8 609 1152 1719 919 521 203 60 57 33 14 3 7 5297 9 348 783 1298 706 638 145 64 38 36 11 3 3 4073 10 342 530 974 581 495 140 36 44 24 11 7 6 3190 11 189 395 718 608 531 138 51 68 37 23 12 9 2779 12 110 242 583 433 399 125 65 63 24 10 6 5 2065 13 127 255 594 559 590 211 108 105 64 33 16 10 2672 14 101 258 602 453 490 151 70 85 47 24 11 10 2302 15 66 161 308 244 218 100 42 36 8 12 2 1 1198 16 41 68 185 135 82 26 18 17 4 2 1 1 580»17 39 63 170 152 150 53 20 13 4 6 0 0 670 (h 18 25 64 140 119 116 45 32 20 10 10 4 1 586 -I.19 27 59 140 148 114 37 12 30 8 6 3 1 585 20 20 102 198 129 125 62 30 21 14 9 2 3 715 21 23 84 160 85 74 34 13 17 3 4 2 1 .500 22 50 82 114 64 40 38 13 7 6 4 0 0 418 23 25 47 92 59 28 23 20 .10 2 0 a 0 306 24 51 47 79 37 26 19 10 11 4 2 1 0 287 25 34 43 63 45 .-33 19 6 9 3 1 2 2 260 26 23 35 44 23 21 11 10 6 :::a 0 0 176 ?7 26 21 43 32 23 15 10 10 3 0 1 1 185 28 92 33 61 51 55 30 18 6 3 0 0 a 349 29 26 19 45 46 23 12 8 3 1 0 0 a 183 30 20 46 56 28 12 16 6 8 2 1 a a 195 31 9 29 100 50 23 6 7 5 0 1 a a 230 September 1 16 41 52 23 20 4 5 1 0 0 1 a 163 ?15 36 41 :'5 19 2 2 0 0 1 2 0 143 3 22 39 82 42 14 1 3 1 1 0 a a 205 4 25 27 49 27 11 2 6 0 0 1 0 0 148 5 33 24 38 28 11 13 4 1 ?0 1 0 155 6 11 28 29 16 7 6 1 0 1 a 0 0 99 7 2 6 13 13 5 6 1 J 1 0 a 0 48 8 7 21 19 3 2 1 0 0 0 a a a 53 9 4 6 6 4 2 3 2 0 0 a 0 0 27 10 4 9 4 3 3 0 1 1 1 0 0 0 26 Appendix Table 2-B-14.Continued. Sector Date 1-2 3 4 5 6 7 8_9 10 11 12 Tota 1 September 11 0 0 2 2 1 2 2 1 0 0 0 0 10 12 4 4 3 4 3 2 3 2 0 0 0 0 25 13 2 5 5 2 3 1 2 1 0 0 0 0 21 14 0 0 0 0 0 0 0 0 0 0 0 0 0»en TOTAL 9346 18371 20245 11020 7969 3015 1532 1313 606 357 176 160 74110 I\)PERCENT 12.6 24.8 27.3 14.9 10.7 4.1 2.1 1.8 0.8 0.5 0.2 0.2 Y 20 foot substrate deployed. '),, J )J 5 J __J I J J )J J J 1 J F" I 20 FOOT SUBSTRATE:ON E SECTOR =I.5 FEET 40 FOOT SUBSTRATE :ONE SECTOR =3.0 FEET 60 FOOT SUBSTRATE:ONE SECTOR =4.5 FEET 40 >-oz ~30 owa: lL.2 ~o SUNSHINE EAST 20 FOOT SUBSTRATE 1/6/B2 -7/12/82 n=2374 I 2 3 4 5 6 7 e 9 10 11 12 SECTORS TALKEETNA EAST 40 FOOT SUBSTRATE 7/4/82.-7/15/82 n=1007 I 2 3 ·4 5 6 7 8 9 10 II 12 SECTORS >-ozw :::>ow 0:: t.L ~o 4>-0 Z UJ ::l 30 0 W 0: t.L ~20 0 10 SUNSHINE WEST 40 FOOT SUBSTRATE 7/6/82-7/13/82 n=65 I 2 3 4 5 6 7 8 9 10 II 12 SECTORS TALKEETNA WEST 20 FOOT SUBSTRATE 7/4/82 -7/15/82 n:1518 I 2.3 4 5 6 7 B 9 10 II 12 SECTORS Appendix Figure 2-8-6.Sector distributiort of chinook salmon passing over SSS substrate where daily chinook salmon apportioned sonar counts were equal to or greater than ninety percent of total sonar counts,Adult Anadromous Investigations,Su Hydro Studies,1982. AS3' 20 FOOT SUBSTRATE:ONE SECTOR =1.5 FEET 40 FOOT SUBSTRATE:ONE SECTOR =3.0 FEET 60 FOOT SUBSTRATE:ONE SECTOR =4.5 FEET 40 >-uz ~30 o W ex:: l.L 2 ~o ' 40 >-(,) Z w3Q =>o W e:20 ~o 10 PINK YENTNA SOUTH 60 FOOT SUBSTRATE 7/28/82 -7/30/82 n =134,636 I 2 3 4 5 6 7 8 9 10 II 12 SECTORS SOCKEYE SUNSHINE EAST 20 FOOT SUBSTRATE 7/17/82-7/19/82 n"338 >-U Z W=>owa::: l.L ~ 40 >-uz W 30=>ow a::: l.L 20 rf. 10 PI NK YENTNA NORTH 60 FOOT SUBSTRATE 7/28/82-7/29/82 n=10,891 I 2 3 4 5 6 7 8 9 10 "12 SECTORS PIN K TALKEETNA WEST 20 FOOT SUBSTRA,.E 8/4/82 -8/5/82 n=1~.189 - ,2 3 4 5 6 7 e 10 II 12 I 2 3 4 5 6 7 a 9 10 II 12 SECTORS S~CTORS Appendix Figure 2-B-7.Sector distribution pf ~ockeye and pink salmon passing over SSS substrate where daily sockeye and pink salmon apportioned sonar counts were equal to or greater than ninety percent of total sonar counts,Adult Anadromous Investigations,Su Hydro Studies,1982. A54 - 1 ]i J 1 J J i J J ) / J -]j J -J ) o SUS IT NA EAST BANK SONAR SITE o SUSITNA WEST BANK SONAR SITE _3.0 ~ I&. ~6.0n. Ia1o 9.0 12.0 I i I I Iiio102030405060 APPROXIMATE OFFSHORE DISTANCE (FT) ""'"3.0... I&..... X ~6.0 l&l o 9.0 12.0.I ,I ,I ,o 10 20 30 40 50 60 APPROXIMATE OFFSHORE DISTANCE (FT) 60 (FT) YENTNA NORTH BAN K SONAR SIT E 8.0 b 16 2b 3'0 I I I A PPROXI MATE OFFSHOR E 6.0 :I: ~4.0n. l&lo ~2.0 ~ I&. o 12.0 •I I I i I -.o 10 20 30 40 50 60 APPROXIMATE OFFS HORE DISTANCE (FT ) YENTNA SOUTH BANK SONAR SITE o 9.0 x~6.0 n. UJo ""'"3.0 ~ I&. > 01 01 Appendix Figure 2-B-8.Bottom profile at Susitna and Yentna stations 1982 sonar sites,Adult Anadromous Investigations,Su Hydro Studies,1982. a SUNSHINE EAST BANK SONAR SITE o SUNSHINE WEST BANK SONAR SITE ;:I.5 IL. :I:t 3.0 UJ o 4.5 -----"'-----'"-",--..".-- 20 25 30 35 OFFSHORE DISTANCE (FTI 6.0 ,I I I I I io51015202530 APPROXIMATE OFFSHORE DISTANCE (FT I 6.0 I I I I I I Iiia TALKEETNA EAST BANK SONAR SITE » 01 en o ~2.0 l- lL. :I:~4.0 UJo 6.0 o TALKEETNA WEST BANK SONAR SITE ~2_0 ...... IL. :I:t 4.0 UJo 6.0 8.0 I I I Io15:30 45 APPROXI MATE OFFSHORE DiSTANCE (FT) 8.0 I I I I I I Ia510152a25:3 a APPROXIMATE OFFSHORE 01 STANCE (FT) Appendix Figure 2-8-9.Bottom profile at Sunshine and Talkeetna stations 1982 sonar sites,Adult Anadromous Investigations,Su Hydro Studies,1982. ~)\ J J J J I I .J I )I J I J 1 ~,~_I ___J I - ~. - APPENDIX 2-C DAILY FISHWHE£l CATCH DATA I j 1 I I i ~--I 1 1 I 1 J 1 J )) Appendix Table 2-C-1.Susitna Station east bank fishwheels daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. Date tb.of \I1ee1 Ih!e1s fbJrs Olil'lXlk Daily I Cun. Sockeye Daily I Cun. Pink Daily I Cun. 01un Dailv I eun, um Daily I Cun. Mi see11 al100Js Senna. Cisco Other I eun. Total Catdl All ~ies Daily I ClIn. )I- (1l "'001 ,July 7. 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 £:4 25 26 27 28 29 :D 31 2 18 2 27 2 24 2 21.5 2 21 2 24 2 24 2 24 2 24 2 24 2 24 2 24 2 23 2 24 2 24 2 26 2 22 2 24 2 3.5 2 11 2 2.5 2 3.5 2 9 2 4.5 2 11 2 17 2 12 2 7.5 2 4 2 10 o 1 o 1 o o 1o oo o o oo 1oooo o o oo oo 1o 1 o o o 1 1 2 2 2 3 3 3 3 3 3 3 3 4 4 4 4 4 4 4 4 4 4 4 5 5 6 6 6 oo 1 o o o o o 1oo '2 6 2 9 49 70 "JJ7 :D 103 18 16 47 24 34 63 52 27 8 42 oo 1 1 1 1 1 1 2 2 2 4 10 12 21 70 140 447 477 58J 5!E 614 66J 685 719 7fI2 834 fl61 ffi9 911 oo 2 2 o 1 1 2 1 oo 1 7.o 3 7 9 12 1 10o 15 64 41 87 63 319 228 126 281 o o 2 4 4 5 6 8 9 9 9 10 12 12 15 22 31 43 44 54 54 69 133 174 261 324 643 871 '!J7 1278 o o o o oooo ooooo o o 5 4 27o 1 o 1 11 3 4 5 19 6 4 13 o oo o o o ooo oo o oo o 5 9 :Ji 36 37 37 38 49 52 56· 61 00 86 m J03 o oooo oo oo o o 1 1 1 2 3 7 12 4 3 1 1 10 o 5 5 9 26 8 22 ooco c oo o o o o 1 2 2 4 7 14 26 :I) 33 34 35 45 45 50 55 64 9J 93 120 oooo ooooo ooo o oooo ooo o oo oo o o o o o ooo o oo coo ooooooo ooo o oo o o o oo o o o ooo 6 o oo oo oo oo oooo oooo o ooo o o o o o o 1 3 3o 1 2 2 2oo 4 9 3 15 64 90 358 35 117 19 33 132 68 1:1) 137 3'!J 288 Wi 35S o 1 4 7 7 8 10 12 14 14 14 18 27 :I) 45 109 1'!J 557 592 709 728 761 893 ':l)1 1091 1228 lfi117 1915 ?f61 2419 Jlu(JJst -1 2 10.5 0 I 6 22 933 81 1359 13 116 14 134 0 0 0 130 2549 2 2 I.0 IJ.6 23 956 148 1507 14 1:D 25 159 0 0 0 210 2759 3 2 11 0 6 30 ~275 1782 27 157 43 202 0 0 0 375 3134 4 2 9 0 6 13 m 64 1846 6 163 29 231 0 0 0 111 3246 Appendix Table 2-C-l.Continued. Total catch ><.n CD L111rook ~Keye 'plnK VItIIl u:oo r'!1 see I laneoos All ::>Il'!Cles Date tb.of Wheel Berino i I-.hee1s Hoors Daily Cull.Daily o..m.Daily Cull.Daily o..m.Daily Cull.Cisco Ol:tl!r I o..m.Daily Cull. ! JlIJ9Jst [ 5 2 13.5 0 6 18 '1017 32 leal 12 175 28 259 0 0 0 <X)33:Ii 6 2 14 0 6 8 1025 18 1899 10 185 20 279 G 0 0 56 3392 7 2 12.5 0 6 4 1029 18 1917 2 187 9 288 0 0 0 33 3425 8 2 24 0 6 16 lot5 76 1993 3 1$(J 3 291 0 0 0 ~3523 9 2 23.5 1 7 7 1(l)2 32 '2025 4 194 9 :m 0 0 0 53 3576 10 2 21.5 0 7 8 ](({)23 2048 2 1%8 :m 0 0 C 41 3617 11 2 22.5 0 7 5 ]~11 2059 2 ICE 3 311 0 0 0 21 36:J! 12 ?23.5 0 7 5 1070 5 2Oi4 0 ICE 1 312 0 0 0 11 3649 13 2 27 0 7 5 1075 2 2OCl6 0 1!ll 10 322 0 0 0 17 3666 14 2 21.5 0 7 0 1075 2 2OCJ8 3 201 4 326 0 0 0 9 3675 15 2 24 0 7 ]1076 4 2fJ72 0 2fJ1 2 328 0 0 0 7 E' 16 2 24 0 7 3 1079 1 2fJ73 0 2fJ1 1 329 0 0 0 5 ?H37 17 2 24 0 7 1 1(8)0 2073 1 202 2 331 0 0 0 4 3691 ' 18 2 24 0 7 4 1<B4 0 2fJ73 0 202 0 331 0 0 0 4 3695 19 2 26 0 7 3 1007 4 2fJn 0 202 2 333 0 0 0 9 37M 20 2 22 0 7 3 1000 1 2078 1 203 0 333 0 0 0 5 3709 21 2 23.5 0 7 2 1092 0 2fJ78 0 203 1 334 0 0 0 3 3712 22 2 23 0 7 1 1093 2 2(8)0 203 3 337 0 0 0 6 3718 23 2 28 0 7 0 1093 0 2(8)1 204 2 339 0 0 0 3 3m 24 2 17.5 0 7 0 1093 2 2C82 1 2(5 1 340 0 0 0 4 3725 Sept:.aTber 2 2 1'3.5 0 7 0 1093 0 2002 2 207 0 340 1 0 1 3 3728 3 7-26 0 7 0 1093 0 2002 4 211 0 340 3 0 4 7 3735 4 2 22.5 0 7 0 1093 0 2002 1 212 1 341 0 0 4 2 3737 5 ?24 0 7 0 1093 0 2002 0 212 0 341 3 0 7 ~3740 1 j ~J J J I i , J ~__J I J 1 J } )I 1 -1 )I ]1 -"1 1 1 J I ]".J 1 )1• )) Appendix Table 2-C-2.Susitna Station west bank fishwheels daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. Tota1 C.atch All SpeciesfotiscellaneoosCom01unPinkSockeyeOiimok..-~..----J r:ete ~.of I.tlee 1 Bermq \ootee1s fbJrs Daily Cull.Daily 00.Daily Cull.Daily 00.Daily Cull.Cisco Other Cull.Daily Cun. .1Jly 1 2 24 4 4 0 0 2 2 1 1 0 ()0 0 0 7 7 2 7 24 1 5 C 0 3 5 0 1 0 0 0 0 0 4 11 3 7 26.5 2 7 1 1 4 9 0 1 0 0 0 0 0 7 18 4 2 24 1 8 0 1 3 12 0 1 0 0 0 0 0 4 22 5 2 22 1 9 0 1 1 13 0 1 0 0 0 0 0 2 24 6 2 24 0 9 0 1 1 14 0 1 0 0 0 0 0 1 25 7 2 21 0 9 1 2 1 15 0 1 0 0 0 0 0 2 27 8 2 24 1 10 0 2 0 15 0 1 C 0 0 0 0 1 28 9 2 23.5 1 11 0 2 0 15 0 1 0 0 0 0 0 1 29 10 2 24.5 0 11 0 2 1 16 0 1 0 0 0 0 0 1 J) 11 2 23.5 0 11 1 3 3 19 0 1 0 0 0 0 0 4 34 12 2 24 0 11 0 3 0 19 0 1 0 0 0 0 0 0 34 13 2 24 3 14 3 6 0 19 0 1 0 0 o -0 0 6 40 14 2 23.5 1 15 3 9 3 2?0 1 1 1 0 0 0 .8 48 15 2 24.5 0 15 1 10 o -22 0 1 0 1 0 0 0 1 49 16 2 24 2 17 0 10 5 27 0 1 1 2 0 0 0 8 57 17 2 25.5 0 17 12 22 7 34.0 1 2 4 0 0 0 21 78 18 2 23 0 17 14 )i 18 52 6 7 4 8 0 0 0 42 120 19 2 23.5 0 17 32 68 39 91 24 31 9 17 ·0 0 0 104 224 20 2 4 0 17 5 73 3 94 2 33 3 20 0 0 0 13 237 21 2 11 0 17 9 82 8 In?2 35 0 20 0 0 0 19 256 22 2 10 0 17 12 94 22 124 2 37 3 23 o -0 0 39 295 23 2 21 0 17 22 116 133 257 3 40 7 J)0 0 0 165 460 24 2 U.5 0 17 13 129 le6 443 7 47 9 39 0 0 0 215 675 25 2 7 0 17 12 141 16 459 4 51 4 43 0 0 0 36 711 26 2 14 0 17 27 168 IJ)589 7 58 3 46 0 0 0 167 878 27 2 16 0 17 32 200 13 602 3 61 2 48 0 0 0 SO 928 28 2 9.5 0 17 23 223 173 775 6 67 3 51 0 0 0 205 1133 29 2 16/5 1 18 6 m 6SO 1425 5 72 8 59 0 0 0 670 1803 J)7 3.5 0 18 6 235 114 1539 4 76 13 72 0 0 0 137 1940 31 2 17 0 18 12 247 ISO 1689 14 00 17 89 0 0 0 193 2133 i\JgJst 1 2 12 0 18 7 254 177 1866 6 %9 ~0 0 0 199 2332 2 2 12 0 18 1 255 361 2227 11 107 5 103 0 0 0 378 2710 3 2 15 0 18 "257 392 2619 16 123 7 110 0 0 0 417 3127"- 4 2 6 0 18 0 257 124 2743 3 126 3 113 0 0 0 13C 3257 > 01 co Appendix Table 2-C-2.Continued. .Total Catch All Species~Ii see11 anewsW10Qn.1I1PinkSockeyeChirook----~J-- -...~,-,.-~-_.~ Date No.of 1f1ee1 Benng I lh:e1s Hoors ...Daily Gun.Daily Cun.Daily Cun.Dai iy Cun.Daily Gun.Cisco Other Gun.Daily Cun. l\Jl}Jst 5 2 14 0 18 '3 ..260 56 ?7~8 134 1 114 0 0 Q 6B 33?5 6 2 14 0 18 1 261 25 2824 1 135 0 114 0 0 0 27 335? 7 2 12 0 18 3 264 48 2872 9 144 2 116 0 0 0 62 3414 8 2 24.5 0 18 5 269 93 .2965 5 .149 ,117 0 0 0 104 3518• 9 2 23.5 0 18 4 713 42 3007 3 152 3 120 0 0 0 52 3570 10 2 22.5 0 18 0 273 21 lJ28 6 158 3 123 0 0 0 ]):?fiX) 11 2 22;5 0 18 .5 278 32 3060 0 158 2 125 0 0 0 39 3639 12 2 23.5 0 18 4 282 15 ])75 3 161 1 126 0 0 0 23 ~ 13 2 15.5 0 18 2 284 4 3079 1 162 1 127 0 0 0 8 3670 25 2 19.5 0 18 0 2B4 2 nn 0 162 0 127 0 0 0 2 E2 26 2 24 0 18 1 285 0 1131 1 163 0 127 0 0 0 2 3674 27 2 16.5 0 18 0 285 0 nn 3 166 0 127 0 0 0 3 3677 28 2 16 0 18 0 285 0 1131 0 166 0 127 0 0 0 0 3677 29 2 25 0 18 0 285 0 1131 1 167 0 127 0 0 0 1 N8 30 2 26 0 18 0 285 0 1131 0 167 2 129 0 0 0 2 368J 31 2 24 0 18 3 2ffi 0 1131 0 167 0 129 0 0 0 3 l'i83 SeptaIDer 1 2 22.5 0 18 0 2ffi 0 1131 2 169 0 129 1 0 1 3 36lJ) 2 2 20.5 0 18 1 289 1 ll32 1 170 0 12'9 ;I .0 4 6 'JHl 3 2 26 0 18 0 289 0 ll32 0 170 0 129 1 0 5 1 3693 4 2 23 0 18 0 289 0 3002 0 170 0 129 2 0 7 2 :Ji95 5 2 24 0 18 0 289 0 ll32 0 170 0 129 10 0 17 10 37ffi >- Q) o ),\ 1 I ..I J .i J .~.~J I .J J )J ~I J J J 1 I )1 J )]J -]1 ----I ) Appendix Table 2-C-J.Yentna station north bank fishwheel daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. Total Catch All SpeciesMiscellaneooseoroChunPinkSockeyeOlirool<------J ......----_.-- Date rtl.of \<I1ee1 Benng \<I1eel s I-bJrs Daily Clrn.Daily Clrn.Daily Cun.Daily Clrn.Daily Clrn.Cisco Other Clrn.Daily Cun. .lire 27 1 24 1 1 0 0 0 0 0 0 0 0 0 0 0 1 1 28 1 24 1 2 0 0 0 0 0 0 0 0 0 0 0 1 2 29 1 24 0 2 0 0 0 0 0 0 0 0 0 0 0 0 2 JJ 1 24 1 3 1 1 0 0 0 0 0 0 0 0 0 2 <1 e-\Jlv 1 1 24 3 6 0 1 0 0 0 0 0 0 0 0 0 3 7 2 1 24 1 7 1 2 0 0 0 0 0 0 0 0 0 2 9 3 1 24 1 8 0 2 0 0 0 0 0 0 0 1 1 2 11 4 1 24 0 8 1 3 0 0 0 0 0 0 0 3 4 4 15 5 1 24 0 8 3 6 0 0 0 0 0 0 0 1 5 4 19 6 1 24 3 11 3 9 0 0 0 0 0 0 0 2 7 8 27 7 1 24 2 13 0 9 1 1 0 0 0 0 0 6 13 9 36 8 1 24 2 15 0 9 2 3 -0 0 0 0 0 3 16 7 43 9 1 24 5 20 0 9 0 3 0 0 0 0 0 6 22 11 54 10 1 24 2 22 1 10 0 <3 _0 0 0 0 0 2 24 5 .59 11 1 24 0 22 0 10 0 3 0 0 0 0 0 0 24 0 59 12 1 24 0 22 2 12 1 4 0 0 0 0 0 0 24 3 62 13 1 24 0 12 0 4 0 0 0 0 0 0 0 0 24 0 62 14 1 24 0 22 2 14 1 5 0 0 0 0 0 0 24 3 65 15 1 24 2 24 5 19 2 7 0 0 2 2 0 0 24 11 76 16 1 24 0 24 5 24 3 10 0 0 0 2 0 1 25 9 85 17 1 24 0 24 14 33 8 18 2 2 4 6 0 1 26 29 114 18 1 24 0 24 29 67 39 57 15 17 4 10 0 3 29 90 204 19 1 24 0 24 71 133 99 156 36 53 15 25 0 5 34 .226 4JJ 20 1 21 0 24 192 330 134 290 29 82 19 44 0 2 36 376 lUi 21 1 9 0 24 00 410 76 366 17 99 6 50 0 0 36 179 985 22 1 14.5 0 24 00 498 138 504 23 122 16 66 0 0 36 265 1250 23 1 12.5 a 24 40 538 320 824 12 134 13 79 0 0 36 385 1635 7.4 1 9.5 0 24 24 562 100 1012 12 146 9 88 0 0 36 233 1868 7.5 1 12 0 24 44 6lli 295 1307 13 159 ]5 103 0 1 37 36H 2236 26 1 12.5 0 24 20 626 213 1520 11 170 2 105 0 3 40 249 21185 27 ]10 0 24 26 652 317 1837 8 178 3 108 0 0 40 354 2839 28 1 12.5 0 24 10 66?748 2585 22 200 15 123 0 0 40 795 3634 29 1 9 0 24 19 681 792 3377 19 219 25 148 0 0 40 855 4489 1)1 8.5 0 24 8 689 433 3815 20 239 7 155 0 0 40 473 4%2 31 1 9 0 24 21 710 478 4293 41 200 7 162 0 0 40 547 5509 » 0)... Appendix Table 2-.C-3.Continued. Total Catch All SpeciesMisee11aneousCohoamPinkSockeyeChirook------"--.....~._.------ Date No.of htteel Benng Wheels HaJrs Daily Cun.Daily Cun.Daily Cun.Daily Cun.Daily Gun.Cisco Otter Cun.Daily Cun; JllJg.Jst 1 1 10.5 0 24 24 734 356 4649 f£J 340 22 184 0 0 40 462 5971 2 1 10 0 24 9 743 '443 5092 -41 381 18 202 0 0 40 511 6482 3 1 11 0 24 8 751 648 5740 59 440 19 221 0 1 41 735 7217 4 1 12 0 24 9 7f£J 336 f£J72 .42 482 11 232 0 1 42 399 7616 5 1 9 0 24 8 768 150 6226 46 528 10 242 0 3 45 217 7833 6 1 10 0 24 3 771 llli 6332 31 559 16 258 0 2 47 158 7931 7 1 24 0 24 21 792 265 6597 62 621 29 287 0 4 51 381 8372 8 1 24 1 25 14 ro5 356 6953 37 658 21 :m 0 3 54 432 !ro4 9 1 24 0 25 4 810 162 7115 34 692 14 322 0 3 57 217 9021 10 1 24 0 25 6 816 110 7225 34 726 10 332 0 4 61 164 9185 11 1 24 0 25 12 828 92 7317 .22 748 14 346 0 5 66 145 93JJ 12 1 24 0 25 13 841 40 7357 16 764 13 359 0 3 69 85 9415 13 1 24 0 25 2 843 73 7430 16 700 13 372 0 7 76 111 9526 14 1 24 0 25 14 857 f£J 7493 15 7fJ5 19 391 0 13 89 121 ~7 15 1 24 0 25 5 ffi2 18 7500 7 002 22 413 0 6 fJ5 58 97(!i 16 1 24 0 25 5 ffi7 9 7517 1 003 5 418 0 0 95 20 9725 17 1 24 0 25 5 872 17 7534 10 813 9 427 0 1 96 42 9767 18 1 17 0 25 5 877 5 7539 13 826 13 440 0 0 96 36 ~ 19 1 24 9 25 5 P82 8 7547 18 844 10 450 0 3 93 44 0047 20 1 24 0 25 3 ffi5 5 7552 10 854 4 454 0 5 104 27 !l374 21 1 24 0 25 1 836 7 7559 7 861 4 458 1 2 107 22 ~ 22 1 24 0 25 2 888 1 75f£J 2 863 8 466 0 2 109 15 9311 23 1 24 0 25 3 891 3 7563 1 864 4 470 0 4 113 15 9926 24 1 24 0 25 5 896 0 7563 2 866 5 475 0 6 119 18 9944 25 1 24 0 25 1 897 2 7565 4 870 6 481 0 12 131 25 9969 26 1 24 0 25 1 Em 3 7568 6 876 8 489 0 11 142 29 gem 27 1 24 0 25 1 899 0 7568 2 878 5 494 0 14 156 22 10020 28 1 24 0 25 2 <XlI 0 7568 0 878 2 496 0 11 167 15 10035 29 1 24 0 25 1 902 0 7568 3 881 3 493 1 9 177 17 10052 30 1 24 0 25 0 902 0 7568 3 004 1 500 0 0 177 4 10056 31 1 24 0 25 0 <Xl2 0 7568 1 885 3 503 0 2 179 6 1(052 5eptarber 1 1 24 0 25 0 902 0 7568 ?887 2 5(6 0 0 179 4 lWi6 2 1 24 0 25 0 <Xl?0 7568 1 888 6 511 0 5 184 12 10078 3 1 24 0 25 2 904 0 7568 4 892 11 522 1 7 192 25 10103 4 1 24 0 25 0 904 0 7568 1 893 5 527 0 3 1fJ5 9 101121:.1 24 0 25 0 904 0 756R t.0 893 1 528 0 0 195 t 10113 -.w '"'" > 0) I\) J I J __J j J ,I J J I )J .1 ..1 _Z ,I J I 1 J J 1 1 J 1 I } I J 1 1 1 )1 Appendix Table 2-C-4.Yentnastation south bank fishwheel daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. Total Catch » 0> (.t,) Chirml<~Pink Dun UJtX)~"scellaneous All SP ~ies I:8te ~.of IrI-eel Bering IrI-ee Is fh.rrs Daily Cun.l:8ily Cun.Daily Cun.Daily Cun.Daily Cun.Cisco Other Cun.Daily 00. ,U1e ?J 1 24 4 4 5 5 0 0 0 0 0 0 0 0 0 9 9 28 1 24 5 9 2 7 0 0 0 0 0 0 0 0 0 7 16 29 1 24 2 11 0 7 0 0 0 0 0 0 0 0 0 2 18 l)1 24 3 14 0 7 0 0 0 0 0 0 0 0 0 3 21 .Ally 1 1 24 11 25 0 7 0 0 0 0 0 ·0 0 0 0 11 32 2 1 24 7 32 5 12 0 0 0 0 0 0 0 0 0 12 44 3 1 19 3 35 2 14 0 0 0 0 0 0 0 1 1 6 50 4 1 24 8 43 3 17 0 0 0 0 0 0 0 2 3 13 63 5 1 24 6 49 3 20 0 0 0 0 0 0 0 0 0 9 7? 6 1 24 5 54 2 22 0 0 0 0 0 0 0 2 5 9 81 7 1 24 8 62 1 23 0 0 0 0 0 0 0 4 9 13 94 8 1 24 11 73 1 24 0 0 0 0 0 0 0 9 18 21 115 9 1 24 4 77 3 27 1 1 0 0 0 0 0 1 19 9 124 -10 1 24-4 81 0 27 0 1 0 0 0 o -o·1 20 5 129 11 1 24 1 82 1 28 0 1 0 0 0 0 0 0 20 2 131 12 1 24 _5 87 2 l)0 1 0 0 0 0 0 2 22 9 140 13 1 24 1 ffi 1 31 1 2 0 0 0 J 0 1 23 4 144 14 1 24 2 50 1 32 0 2 0 0 0 0 0 2 25 5 149 15 1 24 2 92 7 39 1 3 0 0 2 2 0 2 27 14 163 16 1 24 0 92 15 54 3 6 0 0 1 3 0 1 28 20 183 17 1 24 1 93 56 110 13 19 4 4 8 11 0 1 29 83 266 18 1 24 1 94 123 233 16 35 7 11 10 21 0 4 33 161 427 19 1 24 4 93 295 528 73 100 3)41 3)51 0 2 35 434 861 20 1 21 0 98 459 987 89 197 16 57 13 54 0 2 37 579 1440 21 1 9 0 98 154 1151 42 239 9 66 4 68 0 0 37 219 1659 22 1 14.5 0 98 227 1378 123 362 20 86 31 99 0 0 37 401 2050 23 1 12.5 1 99 151 1529 317 679 10 96 22 121 0 0 37 501 2561 24 1 9.5 0 99 110 1639 436 1115 11 107 15 136 {)0 37 572 3133 25 1 12 0 99 89 1728 554 1669 10 117 16 152 0 0 37 669 3002 26 1 12.5 1 100 211 1939 53)2199 7 124 11 163 0 0 37 760 456? 27 1 10 0 100 llJi 2045 595 2794 6 tIl 12 175 0 0 37 719 5281 28 1 12.5 0 100 Al 2126 1327 4121 3 133 30 205 0 0 37 1441 6722 Appendix Table 2-C-4.Continued. Total catch .....IlIlJUI\.J\..I\.".f\cyc r 11'1\.......~II ~~•.•.."......n-~.-......c-_·_- Date I'b.of \oA1ee1 Bering \oA1eels IbJrs Daily Gun.Daily Ct.Jn.Daily Ct.Jn.Daily Gun.Daily Gun.Cisco Other Gun.Daily Cun.. .\lly 29 1 9 1 101 54 2100 1457 5578 10 143 57 262 0 1 38 1500 an' 1'J 1 8.5 0 101 20 2200 762-6340 10 153 16 278 O'0 38 !nl 9110 31 1 9 o .101 33 2233 320 6660 25 178 15 293 0 0 38 393 .9503 AJc].Jst 1 1 10.5 0 101 29 2262 181 6841 18 196 44 337 0 0 38 272 9775 2 1 10 0 101 15 2277 nJ 7141 15 211 34 371 0 0 38 264 10139 3 1 12.5 0 101 10 '22.87 360 7501 17 '22.8 23 394 0 0 38 410 1(649 4 1 12 0 101 24 2311 405 7tX15 12 240 34 428 0 2 40 477 111l?6 5 1 9 0 101 3 2314 140 8046 8 248 20 448 0 1 41 172 111!ll 6 1 10 0 101 7 2321 75 8121 12 2ffl 19 467 0 1 42 114 11312 7 1 24 0 101 27 2348 223 8344 6 266 34 501 0 3 45 293 116ai 8 1 24 1 102 20 2368 322 8666 12 278 33 534 0 1 46 389 119901 9 1 24 0 102 16 2384 102 8768 14 292 19 553 0 1 47 152 12146 10 1 24 0 102 16 2400 74 8842 10 3J2 17 570 0 3 50 120 12266 11 1 24 0 102 /11 2411 51 8893 6 Dl 12 582 0 3 53 83 12349 12 1 24 0 102 11 2422 36 8929 4 312 6 588,0 1 54 58 12407 13 1 24 0 102 4 2426 74 9003 9 321 13 601 0 0 54 100 12507 14 1 24 0 102 13 2439 33 9036 4 325 8 609 0 0 54 58 12565 15 1 24 0 102 5 2444 7 9043 2 327 3 612 0 1 55 18 12583 16 1 24 0 102 7 2451 3 9046 2 329 4 616 0 0 55 16 12599 17 1 24 0 102 4 2455 2 9048 2 331 6 622 0 0 55 14 12613 18 1 17 0 102 3 2458 1 9049 4 335 3 625 0 0 55 11 12624 19 1 24 0 102 5 2463 4 !XJS3 6 341 6 631 0 1 56 22 12646 20 1 24 0 102 1 2464 1 9054 4 345 3 634 0 1 57 10 12656 21 1 24 0 102 5 2469 1 !XJS5 2 347 4 638 0 1 58 13 1::'669 22 1 24 0 102 5 2474 0 9055 2 349 5 643 0 1 59 13 12682 23 1 24 0 102 2 2476 1 9056 1 350 2 645 0 1 60 7 126fl9 24 1 24 0 102 4 2400 0 9056 ..,352 3 648 0 0 60 9 126!ll'- 25 1 24 0 102 2 2482 0 9056 1 353 0 648 0 0 60 3 12701 26 1 24 0 102 4 2486 0 9056 0 353 3 651 0 0 60 7 12700 27 1 24 0 102 3 2489 1 9057 0 353 4 655 0 1 61 9 12717 28 1 24 0 102 1 2490 2 9059 1 354 5 660 0 1 62 10 12727 29 1 24 0 102 3 2493 0 !XJS9 1 355 3 663 0 0 62 7 12734 :lJ 1 24 0 102 1 2494 0 9059 0 355 0 663 0 1 63 2 12736 31 1 24 0 102 1 2495 0 9059 1 356 0 663 0 0 63 2 1273'l -'"'\ 1 >en ~ m I I J )I J J I t ~I I J ,1 ,, 1 I I 1 )]J .11 1 1 i I D i ]It ))J Appendix Table 2-C-4.Continued. Total Catch 01lIn'n/(SocklChirook ---~---_._------------~-..---r--._- Date ~.of W1eel Bering \tIeels IbJrs Daily a.m.Daily a.m.Daily a.m.Daily a.m.Daily a.m.Cisco Otfer a.m.Daily a.m. SeptarlJer 1 1 24 0 102 0 2495 0 ~9 0 356 2 665 0 0 63 2 12740 2 1 24 0 102 3 2493 0 ~9 4 360 3 ffJ8 1 1 65 12 12752 3 1 24 0 102 2 2500 0 ~9 3 363 2 670 0 1 66 8 12760 4 1 24 0 102 1 2501 0 ~9 2 365 4 674 0 0 66 7 .12767 5 1 24 0 102 1 2502 0 ~9 3 368 1 675 0 0 66 5 12m » C» 01 Appendix Table 2-C-5.Sunshine station east bank fishwheels daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. Total catch All SjE:"MiscellCohoDunPinkSockiChirook---_._-_.----.--.....,_.._..----- Date tb.of Wheel Ilenng l-tJee 1s Hours Daily Cun.Daily Cun.Daily Cun.Daily Cun.Daily Cun.Cisco Ot:.rer Cun.Daily Cun. June ,< 4 1 2.5 0 0 1 1 0 0 0 0 0 0 0 0 0 1 1 5 -2 26 a 0 19 20 0 0 0 0 0 0 0 2 2 21 22 6 2 47 2 2 26 46 0 0 0 0 0 0 0 5 7 33 55 7 2 48 0.2 15 61 0 0 C 0 0 0 0 0 7 15 70 8 2 48 2 4 18 79 0 0 0 0 0 0 0 1 8 21 91 9 2 48 1 5 111 190 0 0 0 0 0 0 0 0 8 112 203 10 2 47 8 13 103 293 0 0 0 0 0 b 0 5 13 116 319 11 2 48 7 20 105 39l 0 0 0 0 0 0 0 1 14 113 432 12 2 48 7 27 113 511 0 0 0 0 0 0 0 1 15 121 553 13 2 48 15 42 143 654 0 0 0 0 0 0 0 4 19 162 715 14 2 47 32 74 155 009 0 0 0 0 0 0 0 7 26 194 lXJ9 15 2 40 25 99 60 869 0 0 0 0 0 0 0 1 27 86 995 16 2 47.5 24 123 92 %1 0 0 0 0 0 0 0 0 27 116 1111 17 2 48 9 132 47 lCXJ3 0 0 0 0 0 0 0 0 27 56 1167 18 2 48 68 200 60 1068 0 0 0 0 0 0 0 0 27 128 1295 19 2 48 50 250 32 1100 0 0 0 0 0 0 0 0 27 82 1377 20 2 48 87 337 16 1116 0 0 0 0 0 0 0 1 28 104 1481 21 2 48 22 359 15 1131 0 0 0 0 0 0 0 1 29 38 1519 22 2 47 74 433 19 1150 0 0 0 0 0 0 0 4 33 97 1616 23 2 48 216 649 15 1165 0 0 0 0 0 0 0 3 36 234 IffiO 24 2 48 3J9 958 8 1173 0 0 2 2 0 0 b 0 36 319 2169 25 2 47 172 113J 5 1178 0 0 0 2 0 0 0 1 37 178 2347 26 2 47 143 1273 2 1100 0 0 0 2 0 0 0 3 40 148 2495 27 2 48 151 1424 1 1181 0 0 0 2 0 0 0 1 41 153 2648 28 2 47.5 352 ln6 1 1182 0 0 0 2 0 0 0 2 43 355 3003 29 2 47.5 497 2273 0 1182 0 0 0 2 0 0 0 1 44 4<E :.HII 3J 2 47 437 2710 0 1182 0 0 2 4 0 0 0 0 44 439 3910 July 1 2 48 234 2944 1 1183 0 0 0 4 0 0 0 0 44 235 4175 2 2 48 259 3203 1 1184 0 0 3 7 0 0 0 1 45 264 4439 3 ?46 359 3562 1 1185 0 0 1 8 0 0 0 0 45 361 48Xl 4 2 48 3Jl ].>,63 2 1187 0 0 1 9 0 0 0 4 49 :IE 5100 5 2 47 43J 4293 1 1100 0 0 2 11 0 0 0 6 55 439 5547 6 2 45.5 243 4536 5 1193 0 0 1 12 0 0 0 1 56 250 5797 7 2 48 141 4677 7 1200 0 0 0 12 0 0 0 0 56 148 5945 » 0> 0> ) J I J J )J J J J J 1 J J -J.1 t , J <~ i i I I }B J )J I J ]D J I J 1 11 i~))) Appendix Table 2-C-5.Continued. Total catch >en..... O1il1lOk SOCI<eye f'ml<UU11 W10 Ml SCP.I I aneous !\II :lIll le5 Date ltJ.of Ih!el BenlY,l If1eels fbJrs Daily Gun.Daily Gun.Daily Gun.Daily Gun.Daily Gun.Cisco Other Gun.Daily Gun. July 8 2 48 116 4793 4 1204 0 0 0 12 0 0 0 0 56 120 fffli 9 2 48 50 4843 1 1205 0 0 1 13 0 0 0 1 57 53 6118 10 2 47.5 73 4916 0 1205 0 0 0 13 0 0 0 0 57 73 6191 11 2 47.5 39 4955 1 12O:i 0 0 0 13 0 0 0 0 57 40 6231 12 2 48 2S 4CJJ)1 1207 1 1 1 14 0 0 0 0 57 28 6259 13 2 48 15 4995 1 1203 0 1 2 16 0 0 0 0 57 18 6177 14 2 48 20 5015 3 1211 0 1 2 18 0 0 0 0 57 25 6312 15 2 42 15 5030 5 1216 3 4 0 18 0 0 0 2 59 25 6327 16 2 48 6 5036 6 1222 10 14 2 20 0 0 0 0 59 24 6351 17 2 48 3 5039 7 1229 5 19 1 21 0 0 0 0 59 16 fJS7 18 2 48 7 5046 11 1240 10 29 0 21 1 1 0 0 59 29 63% 19 2 48 8 5054 261 1501 29 58 0 21 1 2 0 0 59 299 6695 20 2 48 12 5OS6 728 2229 147 205 33 54 1 3 0 2 61 923 7618 21 2 46.5 9 5075 1971 4200 214 419 185 239 2 5 0 1 62 2.l32 lODJ 22 2 46 8 5003 2129 6329 484 ~3 345 584 4 9 0 1 63 2971 12971 23 2 48 1 5004 1037 7366 543 1446 345 929 4 13 0 0 63 1930 14931 24 2 48 1 5005 725 0091 113 1559 30 959 0 13 0 0 63 869 15770 25 2 48 0 5085 652 8743 147 17(}i 34 993 0 13 0 0 63 833 16fil3 26 2 48 0 5085 196 8939 58 1764 8 1001 0 13 0 0 63 262 16ffiS 27 2 48 2 5087 5ffi 9527 200 2044 104 1105 0 13 0 0 63 974 17839 28 2 48 0 r:I137 861 103ffi 614 2658 824 1929 4 17 0 0 63 2303 20142 29 2 42.5 2 5089 1209 11597 1751 4409 1615 3544 19 36 0 0 63 4596 24738 30 2 45 0 5089 1196 12793 2946 7355 r:137 4531 20 56 0 0 63 5149 2fB37 31 2 47 0 5009 872 13665 2962 10317 480 5011 14 70 0 0 63 4328 34215 IUgJst 1 2 38 1 509J 925 145~5771 16008 1548 6559 39 109 0 0 63 8284 42499 2 2 30 0 5CJ<:X)281 14871 4932 21020 1162 7721 46 155 0 0 63 6421 48920 3 2 21 1 5091 136 15007 4710 25730 998 8719 78 233 0 0 63 5923 54843 4 2 21.5 0 5091 74 15081 43~30120 1032 9751 99 332 0 a 63 5595 60438 5 ?29 0 5091 77 15158 3672 33792 1705 11456 148 480 0 a 63 5002 66040 6 2 34 0 5091 61 15219 2865 36657 2016 13472 240 720 a 0 63 5182 71222 7 2 35 0 5091 43 15262 1958 38615 2053 15525 331 1051 0 2 65 4387 7r;n.'f.J 8 2 38 0 5091 15 15277 1125 39740 1783 17D3 278 1329 0 a 65 3201 m310 9 2 39 0 5091 17 15294 629 40369 1383 18691 218 1547 0 0 65 2247 81057 10 2 43 a 5091 29 15323 8XJ 41169 2219 20910 476 2023 0 1 66 3525 84582 Appendix Table 2~C-5.Continued. Toful r..atch All Spec.Cd10Sockl.o0oi<_..-._--......,-..._---_.._--- Date tlo.of I.tJee 1 Ben!'19 W1eels Hoors Dailv ClJl1.Daily Cun.Dailv ClJl1.Daily ClJl1.Daily Cun.CiSco Other Cun.Daily Cun. i\J\1lst 2311?45.5 0 5an 15346 715 41004 2631 23541 553 2576 0 0 66 3922 88504 12 2 45 0 5091 13.15359 479 42363 2345 25006 468 3(»1 -0 5 71 3310 91814 13 2 48 ?5093 15 15374 407 4277.0 2782 20058 638 3682 0 10 81 ~95668 14 2 46.5 1 5094 14 153l:l8 353 431('3 1735 ll403 460 4142 0 4 85 '8i7 ~5 15 2 48 1 5095 13 15401 129 43252 605 310ll 314 4456 0 7.87 100l 99299 16 2 ·48 0 5095 13 15414 118 43370 569 31577 575 5031 0 0 87 1275 100574 17 2 48 0 5095 10 15424 79 43449 574 32151 628 5659 0 2 89 1293 101&57 18 2 48 0 5095 6 15430 52 43501 301 32452 375 6034 0 2 91 736 102603 19 2 45 0 5095 5 15435 47 43548 272 32774 238 6272 0 0 91 562 Iffi165 ;:{)2 48 0 5095 2 15437 46 43594 365 3D39 220 6492 0 3 94 636 103001 21 2 47 0 5095 2 15439 21 43615 247 33336 207 6699 0 7 101 484 104285 22 ?48 0 5095 2 15441 21 43636 183 33519 160 6859 0 5 Ire 371 1()1656 23 2 48 0 5095 0 15441 15 43651 188 33707 119 6978 0 8 114 31)104~ 24 2 48 0 5095 3 15444 15 41566 188 33895 78 7056 0 7.116 286 1<li272 25 2 48 0 5095 5 15449 7 43673 173 3400l 72 7128 0 7 123 264 1ffi536 26 2 48 0 5095 0 15449 4 43677 119 34187 24 7152 0 8 131 155 1(6691 27 2 48 0 5095 2 15451 4 43681 161 34348 34 71&5 0 8 139 209 1<li~ 28 2 4B 0 5095 1 15452 4 43685 lOS 34453 22 7200 0 5 144 137 IlXi037 29 2 48 0 5095 0 15452 1 43686 95 34548 22 721)0 7 151 125 1(6162 lJ 2 4B 0 5095 0 15452 2 43600 89 34637 14 7244 0 2 153 107 1tli269 31 2 48 0 5095 1 15453 0 43688 47 346B4 5 7249 0 1 154 54 1(6323 SepteTtler 1 2 45 0 5095 1 15454 .6 43694 44 34728 7 7?95 0 10 164 68 Iffi391 2 2 36 0 5095 2 15456 1 43695 57 34785 6 7262 5 9 178 80 lOOl71 3 2 42.5 0 5095 1 15457 0 43695 83 34e6B 13 7275 1 14 193 112 l00i83 4 2 33 0 5095 0 15457 0 43695 17 34005 1 7276 5 4 202 27 l0i610 5 2 48 0 5095 1 15458 1 43696 44 34929 6 7282 0 20 m 72 1ffi682 6 2 48 0 5095 1 15459 1 43697 45 34974 11 7293 4 22 248 B4 1(6766 7 2 48 0 5095 0 15459 0 43697 50 35024 5 7'83 5 lQ 272 79 1(6845 8 2 4B 0 5095 0 15459 0 43697 42 3500i 9 7lJ7 5 8 ?R5 64 1069)9 9 2 4B 0 5095 1 15460 1 43698 26 35092 5 7312 7 15 Y.J1 55 lCli964 10 2 4B 0 5095 0 15460 1 4})99 21 35113 7.7314 7 l4 328 45 107009 11 2 46 0 5095 0 15460 0 43699 11 35124 1 7315 13 10 351 35 107044 12 7 33.25 0 5095 0 15460 0 43699 6 35130 ?7317 7 5 363 ?O 107Cli4 13 1 24 0 5095 ?15462 0 43699 6 35136 3 7320 13 6 382 30 107094 > 0) CD \t.~J J I I J i j J )I J ,J ~),1/fl J 1 ].~1 1 1 j J J I)) Appendix Table 2-C-5.Continued. Total catch 1 -•MiscellCohoOunPinkSock,Chiroolc J --:'Ipe les Date ttl.of Il1eel Bering \oA1ee1s lbJrs Daily Cun.Daily Cun.Daily Cun.Daily Cun.Daily Cun.Cisco ~r Cun.oaily Cun. Septe1tler 14 1 24 0 5095 0 15462 0 43699 2 35138 0 7320 7 1 :m 10 107104 15 1 24 0 5095 0 15462 0 43699 4 35142 0 7320 4 0 394 8 107112 16 1 24 0 5095 0 15462 0 43699 1 35143 0 7320 1 0 395 2 107114 17 1 23 0 5095 0 15462 0 43699 0 35143 0 7320 2 0 397 2 107116 18 1 24 0 5095 0 15462 0 43699 0 35143 0 7320 0 0 397 0 107116 19 1 24 0 5095 0 15462 0 43699 0 35143 0 7320 1 0 398 1 107117 20 J 24 0 5095 0 15462 0 43699 2 35145 0 7320 0 0 398 2 107119 21 1 24 0 5095 0 15462 0 43699 0 35145 0 7320 0 1 399 1 107120 22 1 24 0 S095 0 15462 0 43699 0 35145 0 7320 0 0 399 0 107120 23 1 24 0 5095 0 15462 0 43699 0 35145 1 7321 4 1 404 6 107126 24 0 24 0 5095 0 15462 0 43699 0 :35145 0 7321 10 1 415 11 107137 25 1 16 0 5095 0 15462 0 43699 0 35145 0 7321 5 0 420 5 107142 26 1 24 0 5095 0 15462 0 43599 2 35147 0 7321 18 14 452 34 107176 27 1 23 0 5095 0 15462 0 43699 1 35148 0 7321 25 26 503 52 107228 28 1 23 0 5095 0 15462 0 43699 .1 35149 1 7372 3 16 522 21 107249 29 1 23 0 5095 0 15462 0 43699 0 35149 0 7322 11 15 548 26 107275 30 1 23 0 5095 0 15462 0 43699 0 35149 0 7322 2 6 556 8 107283 Octcber 1 1 8.5 0 5095 0 15462 0 43699 0 35149 0 7322 0 0 556 0 107283 > 0> ('D Appendix Table 2-C-6.Sunshine station west bank fishwheels daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. Total Catch >...., o O1irook SockeYe Pink (]un COho Miscellaneoos All So !Cies Date fob.of lot1ee1 Benng If1eels IbJrs Dailv Urn.Daily Cun.Daily Urn.Daily Urn.Daily Urn.Cisco Other Urn.Daily Urn. June 8 1 10 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9~2 33 8 8 1 1 0 0 0 -0 0 0 0 0 0 '9 9 10 2 35 4 12 0 1 0 0 a 0 0 "a .a 0 0 4 13 11 2 48 5 17 0 1 0 a a 0 0 a a 0 0 5 18 12 2 48 14 31 5 6 a 0 a a a a 0 0 0 19 37 13 2 47 25 56 3 9 a a a a a 0 a 0 0 28 65 14 2 32 22 78 0 9 0 0 0 a 0 0 a 0 0 22 87 15 2 44 21 99 a 9 0 a a a a 0 a 0 0 21 100 16 2 24 16 115 a 9 0 a a 0 a a a 0 a 16 124 17 2 40 18 133 a 9 0 0 0 0 0 0 0 1 1 19 143 18 2 48 55 100 1 10 a 0 0 0 0 0 0 0 1 56 199 19 2 46 40 228 2 12 0 0 0 0 0 0 0 1 2 43 242 20 2 44 21 249 a 12 0 0 0 0 0 0 0 0 2 21 263 21 2 44 8 257 1 13 0 0 0 0 0 0 0 0 2 9 '[J2 22 2 42 28 285 1 14 0 0 0 a 0 0 0 0 2 29 :JJ1 23 2 48 :JJ 315 0 14 0 0 a 0 0 0 0 1 3 31 332 24 2 48 '[J 342 0 14 0 a 0 0 0 0 0 0 3 27 359 25 2 45.5 32 374 0 14 0 0 0 0 0 0 0 1 4 33 392 26 2 48'37 411 0 14 0 0 0 0 0 0 0 0 4 37 429 '[J 2 48 19 4:JJ 0 14 0 0 0 0 0 0 0 0 4 19 448 28 2 48 19 449 0 14 0 0 0 0 0 0 0 0 4 19 467 29 2 46 14 463 0 14 0 0 0 0 0 0 0 0 4 14 481 :JJ 2 48 12 475 0 14 0 0 0 0 0 0 0 0 4 12 493 July 1 2 48 6 481 0 14 0 0 0 0 0 0 a 0 4 6 499 2 2 48 7 488 0 14 0 0 0 0 0 0 0 0 4 7 5«i 3 2 48 22 510 0 14 0 0 0 a 0 0 a 0 4 22 528 4 2 48 10 520 0 14 0 0 0 0 0 0 0 0 4 10 5:£ 5 2 46 7 527 1 15 0 a 0 0 0 a 0 0 4 8 546 6 2 48 5 532 0 15 a 0 0 0 a 0 0 0 4 5 551 7 2 48 2 534 0 15 a 0 0 a 0 0 a a 4 2 553 8 2 48 1 535 0 15 a 0 a 0 0 a 0 0 4 1 554 9 2 48 3 538 a 15 a 0 0 0 a 0 0 0 4 3 557 10 2 48 4 542 a 15 a a a a 0 0 a 0 4 4 561 11 2 48 0 542 a 15 0 0 a 0 0 0 0 0 4 0 561 I J j ,J J J )J J I J ~J J J J ~ »......... 1 )I 1 1 J J -)J 1 ]1 1 1 1 j '))) Appendix Table 2-C-6.Continued. Total Catch O1irook Sockeye Pink Dun CdxJ Hi see llaneoos All So!ries Date ttl.of lfJeel Benng \oIa!ls fbJrs Daily Gun.Daily Gun.Daily Gun.Daily Gun.Dailv Gun.Cisco Other Gun •Daily Gun. .Ally 12 2 48 a 542 a 15 a a a a a a a a 4 a 561 13 2 47 2 544 a 15 a a a a a a a a 4 2 563 14 2 48 3 547 1 16 a a a a a a a a 4 4 567 15 2 48 2 549 a 16 a a a a a a a a 4 2 569 16 2 48 2 551 a 16 1 1 a a a a a a 4 3 572 17 2 48 4 555 3 19 a 1 1 1 a a a a 4 8 500 18 2 48 1 556 2 21 a 1 a 1 a a a a 4 3 583 19 2 48 a 556 4 25 a 1 a 1 a a a a 4 4 r:I37 20 2 48 1 557 65 ~7 8 1 2 a a a a 4 74 661 21 2 48 1 5r:I3 112 202 6 14 a 2 a a a 1 5 120 781 22 2 48 a 5r:I3 104 ni 13 27 4 6 a a a 1 6 122 903 23 2 48 a 5r:I3 ~404 4 31 2 8 a a a a 6 104 1007 24 2 41 a 5r:I3 73 4n 7 :?B a 8 1 1 a a 6 81 lOll 25 2 48 a 5r:I3 66 543 5 43 1 9 1 2 a a 6 73 1161 26 1 24 a 5r:I3 4 547 a 43 a 9 a 2 a a 6 4 1165 27 2 ~a 5r:I3 58 6lJS 3 46 1 10 a 2 a a 6 62 1227 28 2 48 a 5r:I3 237 842 15 61 13 23 a 2 a a 6 265 1492 29 2 48 a 5r:I3 562 1404 93 154 43 66 4 6 a a 6 702 2194 lJ 2 48 a 5r:I3 227 1631 35 189 12 78 2 8·a a 6 276 2470 31 2 ~a 558 34 1665 16 2l'E 4 82 1 9 a a 6 55 2525 llu9JS t 1 2 44 a 5r:I3 450 2115 157 362 18 100 8 17 a a 6 633 31r:I3 2 2 46 a 558 352 2467 6:?B 1000 28 128 16 33 a a 6 1034 4192 3 2 35 a 558 321 2788 1357 2357 47 175 38 71 a a 6 1763 5955 4 2 37 a 558 165 2953 699 Xl56 110 285 41 112 a a 6 1015 6970 5 2 37.5 a 558 49 DJ2 361 3417 111 396 52 164 a a 6 573 7543 6 2 41 a 5r:I3 33 lJ35 2lJ 3647 58 454 41 205 a a 6 362 7905 7 2 41 a 558 7 lJ42 124 3771 86 540 50 255 a a 6 ?fi7 8172 8 2 42 0 558 6 lJ48 lJ :rol 24 564 27 282 a a 6 87 8259 9 2 48 a 558 1 D+9 17 3818 49 613 21 303 a a 6 R8 8347 '10 2 48 0 5r:I3 2 3051 14 :?B32 21 634 16 319 a a 6 '53 8400 11 2 46 a 5r:I3 16 n,7 35 3867 78 712 55 374 a a 6 184 8584 12 2 44 a 558 7 3074 39 3906 III 810 75 449 a a 6 219 8003 13 2 47 a 5r:I3 4 3078 28 3934 139 949 78 527 a 1 7 250 9053 Appendix Table 2-C-6.Continued. Total Catch >-.... I\) Chinook Sockeye Pink ChlJTl Coho Miscellartnls All SDe 1es Date No.of Wheel Benng Io.tlee1s Hoors Daily ClJTI.Daily ClJTI.Daily ClJTI.Daily ClJTI.Daily ClJTI.Cisco Other ClJTI.Daily ClJTI. Ilu9Jst 928514248055811ll\9 18 3952 121 1070 81 600 0 1 8 232 15 2 42 0 558 5 ...3:l94 0 3952 2 1072 8 616 0 0 8 15 9Dl 16 2 47 0 .558 1 :n:6 0 3952 2 1074 21 637 0 0 8 -24 9324 17 2 48 0 558 7 3102 7 3959 48 1122 69 7O'i 0 0 8 131 9455 18 2 48 0 558 7 3109 5 3964 13 1135 57 763 0 0 8 82 9537 19 2 48'0 558 8 3117 1 3965 7 1142 36 m 0 0 8 52 9589 *20 2 39.5 0 558 3 3120 ('3967 4 .1146 10 009 0 0 8 19 96CB 21 2 48 0 558 5 3125 1 3968 3 1149 19 828 0 0 8 28 9635 Z2 2 48 0 558 10 3135 3 3971 3 1152 23 851 0 0 8 39 9675 23 2 48 0 558 1 3136 0 3971 3 1155 13 864 0 0 8 17 9692 24 2 48 0 558 1 3137 0 3971 1 1156 4 868 0 0 8 6 96511 25 2 47 0 558 1 31:11 1 3972 3 1159 4 872 0 0 8 9 9707 26 2 46 0 558 1 3139 0 3972 2 1161 3 875 0 0 8 6 9713 27 2 48 0 558 1 3140 0 3972 3 1164 5 !Bl 0 0 8 9 9m 28 2 46 0 558 0 3140 0 3972 4 1168 2 882 0 2 10 8 973J 29 2 48 0 558 1 3141 0 3972 0 1168 1 003 0 0 10 ~2 9732 3J 2 47 0 558 0 3141 0 3972 3 1171 2 B85 0 3 13 8 9740 31 1 24 0 558 0 3141 0 3972 0 1171 0 B85 0 0 13 a 9740 SepteTber 1 2 34 0 558 0 3141 0 3972 0 1171 1 886 0 0 13 1 9741 2 2 48 0 558 0 3141 0 3972 a 1171 1 007 0 1 14 2 9743 3 2 48 a 558 0 3141 a 3972 2 1173 1 ffi8 a 1 15 4 9747 4 2 48 9 558 1 3142 0 3972 4 1177 5 893 0 a 15 10 9757 5 2 48 a 558 0 3142 0 3972 3 1100 4 897 a 0 15 7 9764 6 2 48 0 558 0 3142 0 3972 2 1182 2 899 0 0 15 4 9768 7 2 48 a 558 0 3142 0 3972 3 1185 5 904 a 2 17 10 9778 8 1 24 0 558 0 3142 a 3972 0 1185 0 904 0 0 17 0 9778 9 1 24 0 558 0 3142 0 3972 1 1186 1 905 0 2 19 4 9782 10 1 22 0 558 a 3142 0 3972 0 1186 0 905 0 1 20 1 9783 11 1 24 a 558 0 3142 0 3972 a 1186 0 905 a 0 20 0 9783 12 1 14 0 558 a 3142 0 3972 0 1186 0 905 0 0 20 0 97PJ *LW:!r ~t Bank fisf1..teel nDyed 200 yds dcwJstream to new site. J I •I ,I )I .1 )I _J J )J I j .1 J , 1 j ]1 )j -)J J J ]))~]I ~1))) - Appendix Table 2-C-7.Talkeetna station east bank fishwheels daily and cumulative catch log by species~ Adult Anadromous Investigations,Su Hydro Studies,1982, Total Catch All SpeciesMiscellaneousCohoDlIli1Pin.1(SockeveO'Iioook_.-_.- Date tn.of \ileel !Rerinq lhels Hoors Daily Wn.Daily Wn.Daily Wn.Daily Wn.Daily 00.Cisco Other Cun.Daily Cun. ~\Jn:!I I51240!0 0 0 0 0 0 0 0 a 0 a 0 0 0 6 1 24 0 0 0 0 a a a a a 0 0 2 2 ?? 7 1 24 0 i 0 1 1 0 n 0 a a a a a I 2 1 3 8 1 24 0 a 1 2 0 0 a a a a a 0 2 1 4 9 2 27 0 , 0 2 4 0 a 0 0 a 0 0 a '2 ?6I 10 :'48 0 , 0 (1 4 0 0 0 a 0 0 a 0 2 a Ii, 1"'2 48 a ;a 0 4 a 0 0 0 0 a a a 2 0 6.i 12 2 48 a ,0 0 4 0 a 0 0 0 a 0 1 3 1 7, 13 2 48 1 ,1 1 5 a 0 0 0 a a 0 0 3 2 9 14 2 48 1 i 2 a 5 a a a 0 a 0 a a 3 1 10I 15 2 48 2 I 4 0 5 0 0 a 0 0 a a 0 3 2 12 16 2 48 a 4 a 5 a 0 0 0 a a 0 2 5 2 14 17 2 48 a !4 a 5 0 a 0 0 a a 0 0 5 a 14 18 2 48 1 i 5 1 6 0 0 .0 0 a a a 1 6 3 17 19 2 48 0 5 a 6 a a 0 0 a a a 0 6 a 17 20 2 48 1 i Ii 0 Ii 0 a 0 a a a a 1 7 2 19 21 2 48 2 8 0 6 0 0 0 a 0 0 0 0 7 2 21 22 2 48 1 9 a 6 0 0 a 0 0 a 0 0 I 7 1 22 23 2 46.5 9 18 a 6 0 0 0 0 0 a 0 1 8 10 37 24 2 46 3 21 a 6 a 0 0 0 a .a 0 0 B 3 35 25 2 48 10 31 0 6 0 a a 0 0 0 a 1 9 11 46 26 2 48 3 34 a 6 a 0 a a a a 0 0 9 3 .49 27 2 48 19 53 a 6 a a a a 0 0 0 0 9 19 68 28 ?48 12 65 0 6 0 0 0 a a 0 0 0 9 12 80 29 2 48 15 00 a 6 a 0 0 a 0 0 a 1 10 16 96 l)2 48 34 114 0 Ii 0 a 0 0 0 a a 0 10 34 130 .July 1 2 48 49 163 0 Ii 0 0 0 0 a 0 0 0 10 49 179 2 2 48 :.'9 202 0 6 0 0 0 0 0 0 0 1 11 40 2IQ 3 "48 43 245 0 6 0 0 0 0 0 0 0 I I?44 ?fi3'- 4 2 48 41 286 0 6 0 0 0 I)0 0 0 ~12 41 314 5 ...48 :>8 324 0 6 0 0 0 0 0 0 0 0 17 JP 342( 6 z 48 39 363 r 6 a 0 ()0 0 0 0 4 16 43 J35 7 2 47.5 19 "§3?0 6 0 0 0 0 0 0 0 1 17 20 405 8 ?4E 26 400 0 6 0 0 0 0 a 0 0 ]Hl 27 43? 9 ?48 13 421 0 6 0 0 0 0 0 a 0 0 18 13 445 »..... (,.) Appendix Table 2-C-7.Continued. Total C3teh All Sp=!c"11CohoChunkl""",.........."__.<e 'Ie I'lnK "- ----~.~--.., Date No.of \Ihlee1 Bering Wheels Hoors Daily Gun.Daily Gun.Daily Ct.rn.Daily Gun.Daily Ct.rn.Cisco Other Ct.rn.Daily Urn. July 10 2 48 6 427 0 6 0 0 0 0 0 0 0 0 18 6.451 11 2 48 8 435 0 6 0 0 0 0 0 0 0 0 18 8 459 12 2 48 7 442 0 6 0 0 0 0 0 0 0 0 18 7 466 13 2 48 3 445 0 6 0 0 0 0 0 0 0 1 19 4 470 14 2 47.5 3 448 0 6 0 0 0 0 0 0 0 0 19 3 473 15 2 48 8 456 0 6 0 0 0 0 0 0 0 0 19 8 I 4Rl 16 2 48 3 459 0 6 1 1 0 0 0 0 0 0 19 4 485 17 2 48 2 461 0 6 0 1 0 0 0 0 0 0 19 2 487 18 2 48 10 471 0 6 1 2 0 0 0 0 0 0 19 11 4~ 19 2 48 1 472 1 7 0 2 0 0 0 0 0 0 19 2 500 20 2 48 4 476 0 7 0 2 0 0 0 0 0 2 21 6 5C6 21 2 48 2 478 0 7 0 2 0 0 0 0 0 0 21 2 500 22 2 48 3 481 0 7 8 10 0 0 0 0 0 0 21 11 519 23 2 48 0 481 0 7 2 12 0 0 0 0 0 0 21 2 521 24 2 48 0 481 4 11 15 27 0 0 0 0 0 0 21 19 540 25 2 44 0 481 0 11 0 27 0 0 0 0 0 0 21 0 540 26 2 37 1 482 1 12 1 28 1 1 0 0 0 0 21 4 544 27 2 48 0 482 25 37 11 39 3 4 0 0 0 0 21 39 !ID 28 2 48 1 483 23 60 10 49 5 9 0 0 0 0 21 39 622 29 2 48 2 485 31 91 41 90 6 15 0 0 0 0 21 00 702 ~2 48 1 486 12 103 42 132 14 29 0 0 0 2 23 71 773 31 2 48 1 487 8 11l 74 2(li 9 38 0 0 0 0 23 92 ~ Pti9.1st 1 2 48 0 487 17 128 141 347 26 64 0 0 0 0 23 184 1~9 2 2 48 0 487 18 146 457 004 59 123 1 i 0 0 23 535 1584 3 2 48 0 487 16 162 673 1477 56 179 6 7 0 0 23 751 2335 4 2 48 0 487 13 175 962 2439 B4 263 4 11 0 0 23 1013 :rm 5 2 48 0 487 3 178 ll~3545 71 334 9 20 0 0 23 1189 45R7 6 2 48 0 487 4 182 831 4376 86 420 8 28 0 0 23 929 5516 7 2 48 0 487 12 194 923 5299 1~550 20 48 0 0 23 Iffi5 6601 8 2 48 0 487 9 203 l00i 6~148 6~14 62 0 0 23 1177 777R 9 2 48 0 487 1 204 186 6491 28 726 5 67 0 0 1'2 23)79I:F 10 2 48 0 487 3 207 205 6696 60 7ffi 15 82 0 0 23 283 8281 11 2 48 0 487 4 211 773 6969 99 005 17 99 0 0 23 393 8674 12 2 48 0 487 5 216 197 7166 84 969 15 114 0 0 23 ~1 8975 > ~ ~ , :Y t I i J !j )I J J ~I j I ~I ) , J ~ ....a 01 1 !--1 1 )---1 J 1 -1 1 B J .J J 1 1 1 1 )) Appendix Table 2-C-7.Continued. TotA]Catch Chirool<SOCI<eye 1-'1nJ<uun LOIlO M1SCellarEaJs All SPi les I}tte ttl.of IlEcl Senna ~ls !bJrs I}tily Cun.Daily Cun.Daily Cun.Daily Cun.Daily Cun.Cisco OtTer Cun.Daily Cun. Jlu<vst i3 2 48 0 487 3 219 194 73ffl 34 1003 12 126 0 0 23 243 9?1R 14 2 ~0 487 1 220 105 7465 40 1043 14 140 0 0 23 160 9378 15 2 47 0 487 3 223 52 7517 31 1074 7 147 0 0 23 93 9471 16 2 48 0 487 3 226 8 7525 3 1077 5 152 0 0 23 19 94ro 17 2 48 0 487 ]227 14 7539 16 1093 5 157 0 0 23 36 9526 18 2 48 0 487 1 228 23 7562 13 11ex;8 165 0 0 23 45 9571 19 2 48 0 487 1 229 41 7603 7 1113 6 171 0 0 23 55 9626 20 2 44 0 487 2 231 21 7624 7 1120 10 181 0 0 23 40 9666 21 2 48 0 487 0 231 19 7643 21 1141 10 191 0 0 23 SO 9716 22 2 48 0 487 3 234 4 7647 14 1155 10 201 0 0 23 31 9747 23 2 48 0 487 2 236 5 7652 8 1163 6 207 0 0 23 21 97IB 24 2 48 0 487 0 236 4 7656 13 1176 6 213 0 0 23 23 9791 25 2 48 0 487 0 236 1 7657 1 1177 1 214 0 1 24 4 9795 26 2 47 0 487 1 237 1 7658 2 1179 1 215 0 0 24 5 9aX) 27 2 48 0 487 2 239 1 7659 2 1181 2 217 0 0 24 7 9007 28 2 48 0 487 0 239 0 7659 11 1192 7 224 0 1 25 19 9826 29 2 48 0 487 0 239 0 7659·8 1200 5 229 0 0 25 13 -9839 J)?48 0 487 0 239 0 7659 6 1206 3 232 0 0 25 9 5B'l8 31 2 48 0 487 0 239 0 7659 4 1210 2 234 0 0 25 6 9854 Sept.mt:er 1 2 48 0 487 0 239 0 7659 1 1211·0 234 0 0 25 1 9855 2 2 33 0 487 0 239 0 7659 0 1211 1 235 0 0 25 1 9856 3 2 42 0 487 0 239 0 7659 5 1216 2 237 0 1 26 8 9864 4 2 48 0 487 0 239 0 7659 2 1218 3 240 0 0 26 5 9369 5 2 48 0 487 0 239 0 7659 3 1221 1 241 0 1 27 5 9874 6 2 42 0 487 0 239 0 7659 2 1223 2 243 0 0 27 4 <Jl7R 7 2 48 0 487 0 239 0 7659 0 1223 3 .246 0 0 27 3 9881 8 2 48 0 487 0 239 0 7659 0 1223 0 246 0 0 n 0 ~1 9 2 48 0 487 0 239 0 7659 0 1223 0 246 0 0 27 0 9881 10 2 48 0 487 0 239 0 7659 0 1223 0 246 0 0 27 0 em1 11 2 48 0 487 0 239 0 7659 0 1223 0 246 0 0 27 0 9881 12 2 48 0 487 0 239 0 7659 0 1223 0 246 0 0 27 0 em] 13 2 48 0 487 0 239 0 7659 0 1223 0 246 1 0 ?8 1 QPS2 14 2 16 0 1187 0 239 0 7659 0 1223 0 246 0 0 28 0 em2 Appendix Table 2-C-8.Talkeetna station west bank fishwheels daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. TotalCat.ch »..... 0) CnlllXJl<XlCKeye t"lnK UllllI UJlIU ,""::....,,'C1ltlJlJ::.MtI ~"" Date 1tJ.of \oklee 1 Bering htreels IbJrs Daily ClIn.Daily ClIn..Daily ClIn.Daily ClIn.Daily ClIn.Cisco Other ClIn.Daily eun. June 6 1 3 0 0"0 0 0 0 0 0 0 0 0 0 0 0 0 7 . 1 24 0 d 0 0 0 0 0 .0 0 0 0 0 00 0 8 1 24 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 1 24 1 1 1 1 0 0 0 0 0 0 0 0 0 2 2 10 1 24 0 1 0 1 0 0 0 0 0 0 0 1 1 1 3 11 2 25 0 1 0 1 0 0 0 0 0 0 0 2 3 2 5 12 2 33 0 1 2 3 0 0 0 0 0 0 0 0 3 2 7 13 2 48 0 1 0 3 0 0 00 0 0 0 1 4 1 8 14 2 48 0 1 0 3 0 0 0 0 0 0 0 1 5 l'9 15 2 48 0 1 0 3 0 0 0 0 0 0 0 1 6 1 10 16 2 48 0 1 0 3 0 0 0 0 0 0 0 0 6 0 10 17 2 48 0 1 0 3 0 0 .0 0 0 0 0 0 6 0 10 18 2 48 0 1 0 3 0 0 0 0 . 0 .0 0 0 6 0 10 19 2 48 0 1 0 3 0 0 0 0 0 0 0 0 6 0 10 20 2 48 0 1 0 3 0 0 0 0 0 0 0 0 6 0 10 21 2 48 0 1 0 3 0 0 0 0 0 0 0 0 6 0 10 22 2 48 0 10 3 0 0 0 0 0 0 0 0 6 0 10 23 2 46 4 5 0 3 0 0 0 0 .0 0 0 (l 6 4 14 24 2 45 2 7 0 3 0 0 0 0 0 0 0 0 6 2 16 25 2 48 3 10 0 3 0 0 0 0 . 0 0 0 0 6 3 19 26 2 48 6 16 0 3 boo 0 0 0 0 0 6 6 ?5 ?J 2 48 9 25 0 3 0 0 0 0 0 0 0 0 6 9 34 28 2 47 8 33 0 3 0 0 0 0 0 0 0 0 6 8 42 29 2 48 18 51 0 3 0 0 0 0 0 0 a 0 6 18 60 30 2 48 16 67 0 3 0 0 0 0 a 0 0 0 6 16 76 July 1 2 48 36 103 0 3 0 0 0 0 0 0 0 0 6 36 112 2 2 48 34 137 0 3 0 0 0 0 0 0 0 C 6 34 146 3 2 48 33 170 0 3 0 0 0 0 0 0 0 0 6 33 179 4 2 48 31 201 0 3 0 0 0 0 0 0 0 (\6 31 210 5 2 48 31 232 0 3 0 0 0 0 0 0 0 1 7 32 742 6 2 48 36 2ffl 0 3 0 0 0 0 0 0 0 0 7 36 278 7 2 48 30 298 0 3 0 0 0 0 0 0 0 1 8 31 309 8 2 48 12 310 1 4 0 0 0 0 0 0 0 0 8 13 322 9 2 48 8 318 0 4 0 0 0 0 0 0 0 0 8 8 3,,1:1 -.\ !J J .1 D I ,.~I 1 ]1 ))J J J j J )10...,..., 1 I I I l ~)~J .)J J 1 J 1 1 1 1 ., ) Appendix Table 2-C-8.Continued. Total Catc:n DlillJd(Sockeye Pink.Dun COho Miscellaneous All SO!ies Date /b.or \fleel Benng \oI1eels lturs IBHy Cull.IBHv Cull.Dailv CtIll.l:8ily Cull.1:811y Cull.Cfsco Other Cull.Daily Cull. .ltly 10 2 48 8 326 1 5 0 0 0 0 0 0 0 0 8 9 339 11 2 48 4 III 0 5 0 0 0 0 0 0 0 0 8 4 343 12 2 48 2 332 0 5 0 0 0 0 0 0 0 0 8 2 345 13 2 48 3 335 0 5 0 0 0 0 0 0 0 0 8 3 :m 14 2 48 7 342 0 5 0 0 0 0 0 0 0 0 8 7 355 15 2 48 7 349 0 5 0 0 0 0 0 0 0 0 8 7 lJ2 16 2 48 10 359 0 5 0 0 0 0 0 0 0 0 8 10 372 17 2 48 7 366 2 7 0 0 1 1 0 0 0 0 8 10 112 18 2 48 4 370 0 7 1 1 0 1 0 0 0 0 8 5 ~ 19 2 48 5 375 0 7 0 1 0 1 0 0 0 0 8 5 392 20 2 48 2 377 0 7 1 2 0 1 0 0 0 0 8 3 395 21 2 48 2 379 1 8 1 3 0 1 0 0 0 0 8 4 3J9 22 2 48 4 :m 1 9 6 9 0 1 0 0 0 0 8 11 410 23 2 48 4 :fJ7 5 14 4 13 1 2 0 0 0 0 8 14 ~4 24 2 48 -1 :Jl8 0 14 4 17 0 2 0 0 0 0 8 5 429 25 2 46 1 :fJ9 5 19 3 20 0 2 0 0 0 0 8 9 4]3 26 2 35 1 39J 3 22 2 22 0 2 0 0 0 0 8 6 444 27 2 48 0 39J 16 38 7 29 1 3 0 0 0 0 8 24 a68 28 2 48 1 391 18 56 8 37 1 4 0 0 0 0 8 28 4% 29 2 48 0 391 :34 9)24 61 8 12 0 0 0 0 8 66 $2 3)2 48 1 392 18 100 47 100 6 18 0 0 0 0 8 72 634 31 2 48 1 392 3 111 26 134 4 22 0 0 0 0 8 33 ffi7 PugJst 1 2 48 2 394 24 135 117 251 23 45 0 0 0 0 8 166 833 2 2 48 0 394 26 161 240 491 43 ffi 2 2 0 0 8 311 1144 3 2 48 0 394 29 1~786 1277 105 193 9 11 0 0 8 929 2073 4 2 48 0 394 16 206 975 2252 82 275 10 21 0 0 8 1003 3156 5 2 48 0 394 1 207 324 2576 25 l))2 23 0 0 8 352 3500 6 2 48 0 394 13 220 1246 3822 176 476 24 47 0 0 B 1459 4%7 7 2 48 0 394 3 223 911 4733 199 675 20 67 0 0 8 1133 6100 8 2 48 0 394 5 228 561 5294 134 009 33 100 0 0 8 733 6833 9 2 48 0 394 4 232 11l 5405 37 846 8 100 0 0 8 160 6993 10 2 48 0 394 1 233 81 5486 34 8PD 10 118 0 0 8 126 7119 11 2 48 0 394 5 238 153 5639 86 966 24 142 .0 0 8 268 7387 12 2 48 0 394 1 239 135 5774 123 1009 32 174 0 0 8 291 7678 Appendix Table 2-C-8.Continued. Total Catch All ~iesMiscellaneooseoroQ1lJnPinkSockeyeChirook--_.._"--~--- Date No.of Wheel I:lenrKl Wfleels Hoors G:lily Gun.G:lilv Gun.G:lilv Gun.G:lilv Gun.G:lilv Gun.Cisco Other Gun.rEily Gun. : PilgJst 13 2 48-0 394 4 243 129 5~120 1209 20 194 0 0 8 273 7951 14 2 48 0 394 2 245 flJ 5~3 187 13~30 224 0 0 8 279 -82JJ 15 2 48 0 394 3 248 37 fill)68 1464 8 232 0 0 8 116 ·8346 16 2 48 0 394 0 248 16 W16 20 1484 5 237 0 0 8 41 8:E7 17 2 48 ·0 394 2 250 21 6037 27 1511·8 245 0 0 8 58 8445 18 2 48 0 394 6 256 27 ro54 39 1550 19 264 0 0 8 91 B536 19 2 48 0 394 0 256 38 6102 41 1591 18 282 0 0 8 97 8633 20 2 40 0 394 2 258 9 6111 25 1616 8 &l 0 a 8 44 f£l7 21 2 48 a 394 a 258 3 6114 24 1640 6 ~0 a 8 33 8710 22 2 48 a 394 0 258 2 6116 16 1656 13 m a 0 8 31 8741 23 2 48 0 394 2 260 2 6118 11 1667 11 320 0 0 8 26 ·8767 24 2 48 0 394 a 260 1 6119 6 1673 7 327 0 1 9 15 8782 25 2 48 0 394 0 260 0 6119 5 1678 2 329 -0 0 9 7 8789 26 2 48 0 394 0 260 0 6119 3 1681 2 331 0 0 9 5 8794 27 2 48 0 394 1 261 0 6119.4 1685 2 333 0 1 10 8 8002 28 2 44 0 394 1 262 2 6121 9 1694 3 336 0 1 11 16 0018 29 2 48 0 394 2 264 0 6121 5 1699 7 343 0 0 11 14 8832 ~2 48 0 394 1 265 1 6122 4 1703 2 345 0 0 11 8 ffi40 31 2 45 0 394 0 265 0 6122 4 1707 2 347 0 0 11 6 8846 5eptaIDer 1 2 48 0 394 0 265 0 6122 1 1700 1 348 0 0 11 2 8848 2 2 45 0 394 1 266 0 6122 1 1709 5 353 0 0 11 7 IE55 3 2 48 0 394 0 266 0 6122 2 1711 4 357 0 3 14 9 8ffi4 4 2 48 a 394 0 266 0 6122 2 1713 5 362 0 2 16 9 0073 5 2 48 0 394 1 267 0 6122 2 1715 3 365 0 4 20 10 8003 6 2 48 0 394 1 268 0 6122 2 1717.3 368 0 0 20 6 lIB9 7 2 48 0 394 1 269 0 6122 0 1717 0 368 0 0 20 1 8!ro 8 2 48 0 394 0 269 0 6122 0 1717 1 369 0 1 21 2 0092 9 2 48 0 394 1 -270 0 6122 0 171T 1 370 0 0 21 2 8894 10 2 48 0 })4 0 ··270 0 6122 1 l7I8 0 370 0 ;>23 3 f£97 11 2 48 0 394 0 270 0 6122 0 1718 0 370 0 1 24 1 IHlI 12 2 48 0 394 0 270 0 6122 0 l7l8 1 371 0 4 28 5 8!ID 13 2 48 0 394 0 270 0 6122 1 1719 ?373 0 4 32 7 8910 14 2 22 0 394 0 270 0 6122 0 l7l9 0 373 0 0 32 0 8910 »..... CD J \ I j J ]~J J »l J m J )I )~m ! -~i J 1 1 J j J j 1 1 1 j J .'\.1 )).' Appendix Table 2-C-9.Curry station east bank fishwheel daily and cumulative catch log by species, Adult Anadromous Investigations,Su Hydro Studies,1982. Total Catd1 All ~esMiscellaneoJsCohoDunPinkSockeyeOIil'lrt -''J---, Date ftI.of \<otlee1 Benng htleels Hrurs Daily Cun.Daily Cun.Daily Cun.Daily Cun.DailY Cull.Cisco Other Cun.Daily (u:r. June 11 1 11 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 12 1 24 0 0 0 0 0 0 0 0 0 0 0 2 2 2 2 13 1 24 0 0 0 0 0 0 0 0 0 0 0 9 11 9'11 14 1 23.5 0 0 0 0 0 0 0 0 0 0 0 1 12 1 12 15 1 24 1 1 0 0 '0 0 0 0 0 0 0 0 12 1 13 16 1 23.5 0 1 0 0 0 0 0 0 0 0 0 0 12 0 13 17 1 24 0 1 0 0 0 {)0 0 0 0 0 8 20 8 21 18 1 24 0 1 0 0 0 0 0 0 0 0 0 1 21 1 22 19 1 24 0 1 0 0 0 0 0 0 0 0 0 4 25 4 ?'5 20 1 24 2 3 0 0 0 0 0 0 0 0 0 7 32 9 35 21 1 24 1 4 0 0 0 0 0 0 0 0 0 1 33 2 37 22 1 24 0 4 0 0 {)0 0 0 0 0 0 5 38 5 ~2 23 1 23.5 3 7 0 0 0 0 0 0 0 0 0 1 39 4 to 24 1 21 10 17 0 0 0 0 0 0 0 0 0 1 40 11 57 25 1 23 10 27 0 0 b 0 0 0 0 0 0 2 42 I?69 26 1 24 28 55 0 0 0 ·0 0 0 0 0 0 1 43 29 ..~ 27 1 24 21 76 0 0 0 0 0 0 0 0 0 0 43 21 119 28 1 22 13 89 0 0 0 0 0 0 0 0 0 1 44 14 133 29 1 23 16 lOS 0 0 0 0 a a a 0 a 2 46 18 151 30 1 23 27 132 a 0 a 0 a a 0 0 0 2 48 29 100 July 1 1 24 24 156 0 0 a a a 0 a 0 a 0 48 24 2()1 2 1 24 28 184 0 0 a 0 a 0 a a 0 0 48 28 232 3 1 24 31 215 .0 0 0 a a a a a 0 a 48 31 263 4 1 24 32 247 a 0 0 0 a a 0 a a 0 48 32 295 5 1 24 28 275 0 a a a a 0 a a 0 1 49 29 324 6 1 24 19 294 0 0 a 0 a a a 0 0 4 53 23 347 7 1 24 20 314 0 0 a 0 0 a a 0 0 2 55 22 369 8 1 24 16 31.1 0 0 0 a 0 0 0 a a 0 55 16 :Fj 9 1 23 15 345 0 0 a a 0 a 0 0 a 3 58 18 403 10 1 24 10 355 0 0 0 a 0 0 a 0 0 2 60 12 415 11 1 24 4 359 0 0 0 0 a 0 0 a 0 0 60 4 419 12 1 24 4 363 0 0 a 0 a a 0 0 a 0 60 4 .47.3 13 1 24 12 375 0 0 a 0 0 0 a 0 0 0 60 12 435 » ...... CD Appendix Table 2~C-9.Continued. Total Catch All SpeciesHisee11areoosCohoQlllnPinkSockeyeChirook_...--~~--.'..-. Date ~b.of btleel Berino . \oI1eels Halrs Daily ClIlt.Daily ClIlt.Daily ClI!1.Daily Cun.D.;il.y ClJl1.Cisco OtJer :Cun.Dailv Cull. .lily 384,14 1 "4 9 0 0 0 0 0 0 0 0 0 0 60 9 444 15 1 24 7 391 0 0 0 0 0 0 0 0 0 0 60 7 451 16 1 24 8 399 1 .1 a .0,0 0 0 0 0 0 60 9'460 17 1 24 3 402 0 1 0 0 0 0 0 0 .I)0 60 3 463 18 1 ?4 7 409 1 2 0 0 0 0 0 0 0 1 61 9 472 19 1 24 6 4).5 1 3 0 0 0 0 0 0 0 0 61 7 479 20 1 24 6 421 1 4 0 (l 0 0 0 0 0 0 61 7 486 21 1 24 5 426 0 4 0 0 D 0 0 0 0 2 63 7 493 2?1 74 0 426 0 4 1 1 0 0 0 0 0 0 63 1 494 ;13 1 24 1 4?J 0 4 1 2 0 0 0 0 0 0 63 2 4% 24 1 24 1 428 2 6 0 2 0 0 0 0 0 0 63 3 499 25 1 24 2 430 1 7 0 2 1 1 0 0 0 0 63 4 503 26 1 24 0 430 1 8 2 4 1 2 0 0 0 0 63 4 ~7 27 I 24 0 430 7 IS 6 10 I 3 0 0 0 0 63 14 521 28 I 24 4 434 0 15 7 17 0 3 0 0 0 0 63 II 532 29 I 24 I 435 7 22 17 34 3 6 0 0 0 I 64 29 561 30 1 23.5 0 435 6 28 II 45 12 18 0 0 0 0 64 29 590 31 I 24 0 435 4 32 36 81 6 24 0 0 0 1 65 47 637 I\JgJst I 1 24 I 436 3 35 39 120 12 36 0 0 0 0 65 55 692 2 I 24 0 436 4 39 132 252 23 59 I 1 0 1 66 161 853 3 1 23.5 0 436 5 44 262 514 29 !?8 3 4 0 1 67 :m II53 4 1 24 0 436 12 56 564 1078 76 164 3 7 0 0 67 655 urn 5 I 24 0 436 16 72 721 1799 98 262 3 10 0 2 69 840 2648 6 I 24 0 436 4 76 559 2358 86 348 3 13 0 0 69 652 3D) 7 1 24 0 436 4 00 324 2682 ~:Nl 4 17 0 0 69 3!l2 3682 8 1 24 0 436 0 00 226 2~81 479 5 22 0 2 71 314 3996 9 1 23 0 436 I 81 195 3103 95 574 4 26 0 0 71 2%4291 10 1 24 0 436 2 83 142 3245 56 630 3 29 0 1 77 204 4495 II 1 74 0 436 ?85 8?3327 77 707 I 30 0 0 72 162 4657 12 I 21 0 436 1 86 46 3373 81 700 4 34 0 0 72 132 4789 13 I 24 0 436 (l 86 51 3424 134 922 5 39 0 0 7?190 4979 14 1 24 0 436 1 87 4?3466 73 995 4 43 (l 1 73 I?1 5100 15 1 24 0 436 3 CXJ 29 3495 45 1040 6 49 0 1 74 84 5184 » 0). o ~ I -.J ---~)I .1 B )I ~J 1 J J I I J J I »»J J J 1 J I i I J I .j I 1 J J I )t J Appendix Table 2-C-9.Continued. Chil100k Sockeve Pink Chun Com tii see11 ilneo.JS Total Catch All Srecies >- (X) ~ Oilte ~b.of \<Ilee1 -Herinq \oI"ee 1s IbJrs Daily CLrn.Daily Cun.Dailv Cun.Dailv Cun.Daily Cun.Cisco Other Cun.Daily Gun. ;\Jws~.- 16 1 24 0 436 2 92 12 3r:IJ7 24 100l 3 5<a 1 75 42 5~ 17 1 24 0 a36 1 93 8 3515 7 1071 4 56 0 (1 75 20 246 18 ,24 0 436 4 97 16 3531 IlO 1001 9 65 0 0 75 49 5295 19 1 24 0 436 2 99 17 3548 2?1113 1 66 0 3 78 45 5340 20 1 24 0 436 3 102 11 3559 50 1162 7 73 0 1 79 72 5412 ?1 1 24 0 436 3 lOS 10 3569 45 1200 5 78 0 1 80 64 5475 22 ,24 0 436 6 111 6 3575 32 1240 3 81 0 0 80 47 5523"23 ,24 0 436 2 113 4 3579 10 1250 3 84 (l J 81 20 5543J. 25 1 24 0 436 2 115 0 3579 19 1269 2 86 0 2 83 25 5568 25 1 24 0 436 2 117 3 3582 12 1281 3 89 0 1 84 21 5589 71:;1 24 0 436 0 117 2 3584 11 1292 2 91 0 0 84 15 5601 27 1 23 0 436 4 121 0 3584 9 Ull 2 93 0 0 84 15 5619 28 1 24 0 436 1 122 0 3584 7 1])3 1 94 0 ?86 11 5630 29 1 24 0 436 1 123 0 3584 11 1319 3 97 0 1 87 16 5646 )).1 24 0 436 0 123 0 3584 13 1332 1 ~0 1 88 15 5661 31 1 24 0 436 1 124 .0 3584 7 1339 4 102 0 0 88 12 5673 5eptaTber 1.1 .24 0 436 0 124 0 3584 0 1339 1 103 0 0 88 1 5674 2 1 24 0 436 2 126 0 3584 1 1340 2 lOS 0 3 91 8 5682 3 1 24 0 436 0 126 0 3584 1 1341 0 105 0 4 .95 5 5687 4 1 24 {)436 1 127 0 3584 0 1341 0 lOS 0 0 95 1 56B8 5 1 24 0 436 0 127 0 3584 0 1341 0 105 0 1 96 I 5689 6 1 24 0 436 0 127 0 3584 0 1341 0 lOS 0 0 96 0 5689 7 1 24 0 436 0 IV 0 3584 0 1341 0 lOS 0 1 97 1 5693 8 1 24 0 436 0 127 0 3584 1 1342 0 lOS 0 0 97 1 5691 9 1 24 0 4313 (l 127 0 3584 0 1342 0 lOS (1 0 97 0 5691 10 1 24 0 436 0 127 0 3584 0 1342 I Iffi 0 1 98 ;>5693 11 I 24 0 436 0 127 0 3584 2 1344 1 107 0 1 99 4 5697 12 1 24 0 436 0 127 0 3584 0 1344 o '.107 0 1 100 1 5698 13 1 ?4 0 436 0 127 0 3584 0 1344 0 107 0 0 100 0 5693 14 1 24 0 436 0 127 0 3584 1 1345 {)107 0 ?1O?3 5701 15 1 ?4 0 436 (1 127 0 3584 0 1345 0 107 ()1 103 1 5702 10 1 24 0 436 0 I?7 0 3584 0 1345 0 107 0 0 103 0 5702 J7 I 24 0 436 0 127 0 3584 0 1345 0 107 0 0 103 0 5702 18 1 16 0 436 1 1?8 0 3584 0 1345 0 107 0 1 104 ?5704 _._.- Appendix Table 2-(-10.Curry station west bank ftshwheel daily and cumulative catch log by species. Adult Anadromous Investigations.Su Hydro Studies.1982. Total catct) All SpeciesMisee11areooseoroDunPinkSock~Chirook - - --.f ....~ Date No.of Wheel ,Benng W1eels IbJrs Daily Cun.Daily Cun.Daily a.m.Daily Cun.Daily Cun.Cisco Other Cun.Daily Cun. June 9 1 11 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 10 1 24 0 0 0 0 0 0 0 0 0 0 0 0 1 0 .1 11 1 24 0 0 0 0 0 0 0 0 0 0 0 1 2 1 7. 12 .1 24 o .0 0 0 0 0 -0 0 0 0 0 2 4 2 4 13 1 23 0 0 0 0 0 0 {)0 0 i 0 0 1 I 5 1 5I 14 1 24 0 0 0 0 0 0 0 0 0 ,0 0 0 5 0 5 ,I 15 1 24 0 0 0 0 0 0 0 0 0 0 0 1 I 6 1 6 16 1 24 0 0 0 0 0 0 0 0 0 0 0 0 I 6 0 fi 17 1 24 0 0 0 0 0 {)0 0 0 I 0 0 1 7 1 7 18 1 24 0 0 0 0 0 0 0 0 0 0 0 0 7 0 7 19 1 24 1 1 0 0 0 0 0 0 0 0 0 1 8 2 9 20 1 24 0 1 0 0 0 0 0 0 0 0 0 0 8 0 9 21 1 24 1 2 0 0 0 0 0 0 0 I 0 0 0 8 1 10 22 1 22 2 4 0 0 0 0 0 0 0 0 0 0 8 2 12 23 1 24 2 6 0 0 0 0 0 0 0 ;0 0 0 8 2 14 24 1 24 7 13 0 0 0 0 0 0 0 0 0 2 10 9 23 25 1 24 10 23 0 0 0 0 .-0 0 0 0 0 0 10 10 33 26 1 24 18 41 0 0 0 0 0 0 0 0 0 0 10 18 51 27 1 24 15 56 0 0 0 0 0 0 0 0 0 0 10 15 66 28 1 24 33 89 0 0 0 0 0 0 0 0 0 0 10 33 99 29 1 24 29 118 0 0 0 0 0 0 0 0 0 0 10 29 128 30 1 24 24 142 0 0 0 0 0 0 0 0 0 1 11 25 153 July 1 1 24 31 173 0 0 0 0 0 0 0 !0 0 1 12 32 I 185 2 1 24 25 19'1 0 0 0 0 0 0 0 I 0 0 0 12 25 I 210, 3 1 24 12 210 0 0 0 0 0 I 0 0 0 0 0 12 12 !m 4 1 24 23 233 0 0 0 0 0 0 0 0 0 0 12 23 i 245I! 5 1 24 15 248 0 0 0 0 0 I 0 0 0 0 3 15 18 I 263I 6 1 24 9 257 0 0 0 0 0 !0 0 0 0 2 17 n I 274 7 1 24 16 273 b 0 0 0 0 I 0 0 0 0 2 19 18 292 8 1 23 14 487 0 0 0 0 0 0 0 0 0 0 19 14 I n; 9 1 24 10 497 0 !0 0 0 0 0 0 0 0 0 19 10 316 10 1 24 6 :m 0 i 0 0 0 0 0 0 0 0 0 19 6 ~ 11 1 24 6 309 0 I 0 0 0 0 0 0 0 0 1 20 7 329 12 1 24 5 314 0 0 0 0 0 0 0 0 0 0 20 5 334 I > CD I\) .t .~ I 1 )J J J J J t J I J J ).~I ] J )1 J J .,1 i ) 1 Appendix Table 2-C-10.Continued. Total Catch » Q) (A) Ot1rook ~~Plnk U1lIll WlO Mlscellaneoos All SP '.!Cies Date ttl.of \hel I Bering \th!els IWrs lRlily Cun.Daily Cun.lRlily Cun.lRlily Cun.ll1ilv Cull.Cisco Other Cun•Daily Cull. .lily 13 1 24 6 320 0 0 0 0 0 0 0 0 0 0 20 6 340 14 1 24 6 326 0 0 0 0 0 0 0 0 0 0 20 6 346 15 1 24 4 I 330 0 0 0 0 0 0 0 ()0 0 20 4 350 16 1 24 2 I 332 1 1 0 0 0 0 0 0 0 1 21 4 :f)4 17 1 24 3 335 0 1 0 0 0 0 0 0 0 0 21 3 357 18 1 24 5 340 0 1 0 0 0 0 0 0 0 0 21 5 :Jill 19 1 24 5 345 0 1 0 O·0 0 0 0 0 0 21 5 E 20 1 24 2 347 0 1 0 0 0 0 0 0 0 1 22 3 370 21 1 24 2 349 0 1 0 0 0 0 0 0 0 0 22 2 372 22 1 24 0 349 0 1 1 1 0 I 0 0 0 0 1 23 2 374 23 1 24 1 350 0 1 2 3 0 I 0 0 0 0 0 23 3 In 24 1 24 0 350 0 1 0 3 0 0 0 0 0 0 23 0 3n 25 1 11 0 350 0 1 0 3 0 0 0 0 0 0 23 0 In 26 1 6 0 350 0 1 0 3 0 0 0 0 0 0 23 0 In 27 1 24 0 350 0 1 1 4 0 0 0 0 0 0 23 1 378 2R 1 24 2 352 1 2 3 7 0 o·0 0 0 0 23 6 Jl4 29 1 24 1 353 2 4 7 14 1 1 0 0<0 0 23 11 395 lJ 1 24 0 .<353 -1 5 20 34 3 4 0 0 0 0 23 24 419 31 1 16.5 0 353 0 5 9 43 2 6 0 0 0 0 23 11 4lJ - .Pu}Jst 1 1 24 0 353 0 5 3 46 1 7 O·0 0 0 23 4 434 2 1 23.5 0 I 353 1 6 67 113 1 I 8 0 0<0 0 23 69 503 3 1 24 1 354 1 7 266 379 7 I 15 1 i 0 0 23 276 779 4 1 22 0 354 3 10 397 776 13 I 28 2 3 0 0 23 415 1194 5 1 24 0 354 0 10 478 1254 12 40 2 5 0 0 23 492 16ffi 6 1 24 1 355 2 12 600 1862 18 58 6 11 0 0 23 635 2321 7 1 24 0 355 1 13 461 2323 34 I 92 2 13 0 0 23 4~2819 8 1 24 0 I 355 1 14 474 2797 19 I 111 5 18 0 1)23 499 3318 9 1 24 0 355 0 14 231 lJ28 12 I 123 2 20 0 0 23 245 3563 10 1 24 0 355 1 15 1~3226 10 133 2 22 0 0 23 211 3n4 11 1 24 0 355 1 16 155 3381 20 j 153 3 25 0 0 23 179 3953 12 .<1 24 0 355 0 16 133 3514 19 172 4 29 0 0 23 156 4109 13 1 24 0 355 0 I 16 94 3603 34 I 2C6 4 33 0 1 24 133 4242 14 1 24 0 355 1 17 36 3644 45 251 5 38 0 0 24 87 4329 15 1 24 0 355 3 20 17 3661 24 275 5 43 0 1 25 50 4379 16 1 24 0 355 2 22 16 3677 13 2ffi 9 52 0 0 25 40 4419 Appendix Table 2-C-10.Continued. Total Catch All SpeciesMisee11aneousCOOoOUJnPinkSockeveChirool<~.J , Date No.of \oh:el <:Un. Bering I-.t1eels Hours Dailv Cull.Daily Cull.Daily Daily Cull.Daily Cull.Cisco Otter Cull.Dailv Cull. h1glst 25 i 44281712403554264368102ffi1530 0 9 18 1 24 0 355 1 27 9 3600 12 .:m 4 57 0 0 25 26 4454 19 1 24 0 355 3 l)10 3700 14 314 14 71 0 1 26 42 44% 20 1 22 0 355 0 l)5 3705 8 322 4 75 0 0 26 17 4513 21 1 23 0 355 0 l)4 3700 8 nJ 3 78 0 0 26 15 4528 22 1 23.5 0 355 0 l)3 3712 15 345 -3 81 0 0 26 21 4549 23 1 24 0 355 0 Xl 2 3714 8 353 8 89 0 0 26 18 4567 24 1 24 0 355 0 l)2 3716 4 357 1 00 0 0 26 7 4574 25 1 23.5 0 355 0 I Xl 1 3717 1 358 5 95 0 0 26 ~7 4581 26 1 24 0 355 0 l)1 3718 4 362 7 III'0 1 27 13 4594 'll 1 23 0 355 1 31 0 3718 8 370 1 103 0 0 27 10 46Qil 28 1 24 0 355 0 31 0 3718 4 374 3 1~0 1 28 8 4612 29 1 24 0 355 1 32 0 3718 6 3lIJ 1 107 0 0 28 8 4620 l)1 24 0 355 0 32 0 3718 7 'Y37 5 112 0 0 28 12 4632 31 1 24 0 355 1 33 0 3718 2 'Y39 2 114 0 0 28 5 4637 Septe!ltJer 1 1 24 0 355 0 33 0 3718 0 'Y39 1 115 0 0 28 1 4638 2 1 24 0 35S 0 33 0 3718 2 391 2 117 0 0 28 4 4642 3 1 24 0 355 0 33 0 3718 0 391 3 120 0 0 28 3 4645 4 1 24 0 355 0 33 0 3718 0 391 0 120 0 0 28 0 4645 5 1 24 0 35S 0 33 0 3718 0 391 0 120 0 0 28 0 4645 6 1 24 0 35S 0 33 0 3718 0 391 1 121 0 0 28 1 4646 7 1 24 0 355 0 33 0 3718 0 391 1 122 0 1 29 2 4648 8 1 24 0 355 0 33 0 3718 0 391 0 122 0 0 29 0 4648 9 1 24 0 355 0 33 0 371B 0 391 0 122 0 0 29 0 4648 10 1 24 0 355 0 33 0 3718 0 391 0 1ZZ 0 0 29 0 I 4601fI 11 1 24 (1 355 0 33 0 3718 0 391 0 122 0 0 29 0 4648 12 1 24 0 355 0 33 0 3718 0 391 0 1?2 0 0 29 0 4648 13 1 24 0 355 0 33 0 371fl (1 391 0 127 0 1 30 1 4649 14 1 24 0 355 0 33 0 3718 0 391 0 122 0 0 30 0 4649 15 1 19.5 0 355 0 33 0 3718 0 391 0 122 0 ()30 0 4649 16 1 5 0 355 0 33 0 3718 0 391 0 122 0 0 30 0 I 4649 17 1 16 0 355 0 33 0 3718 0 391 0 17.2 0 0 30 0 4649 j > ('D• J ) I I .1 •• )I J J __J J J .~]J ~J , 1 1 F'" I I I'!'" I' ': i APPENDIX 2-D LENGTH FREQUENCIES OF CHINOOK,SOCKEYE,PINK,CHUM AND COHO SALMON AND BERING CISCO ,I 25 20 MAL.ES n =10 i =468 >-u Z 15W :::>ow (k:lla 1.L 5 I 200 I 416 I 632 I 848 I I 1064 1280 20 16 >- U ~12 :::>ow 0=8 1.L FEMALES n =11 X =629 I 200 o <b) I I I I 416 632 848 1064 1280 LENGTH (mm) Appendix Figure 2-D-1.Length frequencies of chinook salmon sampled from fishwheel catches at Susitna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. ASS -MALES n -87 X =473 15 12 >- U Z 9W::> 0w ~8IJ.. ~ 3 0 n~~n~~ I I I I I I (a)200 418 832 848 1084 1280 25 20 >- U Z 15W::>ow Ck:t 0lL. 5 o FEMALES n -39 X =603 ,~ Cb) I 200 I I I I 416 632 848 1064 1280 LENGTH <mm) Appendix Figure 2-0-2.Length frequencies of chinook salmon sampled from fishwheel catches at Yentna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. ABS -I I .A87 n I I 1064 1280 I 848 I 632 I 416 ! 20121 121 "'"'1 -"1121 MALES n ==497 i =5778 >- U Z 6W ~::> 0 W Ck:4 ~1L. ~ 2 l!!!!'iifP\ Appendix Figure 2-0-4.Length frequencies of chinook salmon sampled from fishwheel catches at Talkeetna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. - FEMALES n ==2e2 x -801 n I I II 4 I 6 632 848 I 12164 1280 LENGTH (mm) I 209 2 Ie o A88 8 >-W Z 6W :Jaw Ct:4~ <b) HALES n ...370 X =650 Ie 8 >- U ~\Z 8W ::J 0 I.&J ~41L. ~ """2 -nfa I I I I I I (0)200 418 632 848 1064 1280 FEMALES n ...263 X =831 10,~ 8 >-U Z 8W ::J 0 Wa::41L. ~ 2 - e 11 I I I I Cb)200 416 632 848 1064 1289 LENGTH (mm) Appendix Figure 2-D-5.Length frequencies of chinook salmon sampled from fishwheel catches at Curry Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A89 ~, 15 12 MALES n ...51 I i =539 >-u Z 9W ~I :> 0w ~6u.. ~ 3 0 j"l,n 1n .1 1 I I I 1 (0)290 308 416 524 632 740 20 16 >-u Z 12W :>awn::8 LL FEMALES n =5.08 i =547 - I I I 398 416 524 632 LENGTH (mm) 4 e (b) I 200 nn I1n I 740 Appendix Figure 2-0-6.Length frequencies of sockeye salmon sampled from fishwheel catches at Susitna Station,Adult Anadromous Investigations,Su Hydro Studies,1982.~,~ AgO -- ",...,10 MALES n ::598-8 X ==532 >-u Z 8W :J 0 W et=4lL. ~ !"'"" 2 F }\ 0 n n I I I I 1 I (0)200 308 416 524 -632 740- 15 12 >-U Z 9W :J .....0 W et=6lL. ~ 3 p;sm 0 n n n n r I I I I Cb)200 308 416 524 632 749 LENGTH (mm) FEMALES n =293 X =533 Appendix Figure 2-D-7.Length frequencies of sockeye salmon sampled from fishwheel catches at Yentna Station.Adult Anadromous Investigations.Su Hydro Studies,1982. A91 - I 7-40 nri I 632 I 524 I 418 I 308 n(1, I 200 ~ 15 --MALES 540 .... n = i =55312 """: ~ U Z 9W::> 0w ~61.L...... ~ """: I 7-40 I I I 308 426 524 632 LENGTH <mm) n I 200 o - 25 FEMALES ,,-- n =694 X =53812 ->-U Z 9W ::> 0w ~61.L. ~ 3 - Cb) Appendix Figure 2-D-8.length frequencies of sockeye salmon sampled from fishwheel catches at Sunshine Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A92 nn~n I I I 364 458 552 646 LENGTH (mm). - 20 16 >-u . ~12 :::> Q W ~8 l1.. 4 fa (0) 20 16 >- U Z 12W :::> Q W ~8l1.. 4 o <b) I 270 I 270 n I 364 I 458 I 552 I 646 n I .. 740 I 740 MALES n =f60 X :.549 FEMALES n >=269 i =527 ""'" I"- ! ! Appendix Figure 2~D-9.Length frequencies of first run sockeye salmon sampled from fishwheel catches at Sunshine Station, Adult Anadromous Investigations,Su Hydro Studies, 1982. A93 ~ 15 ,-"MALES n :or 380 X =55512 -, >- Uz 9W :J ~ 0 W ~6l.L. ~ 3 ~ 0 n(l,,...,n ~, I I I I I I (a)a'e 364 458 552 646 740 ~I IS FEMALES --- n -425 X =545 ..... >.-uz 9 ~4J :J 0 W ~6h. ~ 3 n)~ ~n r-. I I t I I Cb)270 364 458 552 646 740 LENGTH <mm) Appendix Figure 2-D-10.Length frequencies of second run sockeye salmon sampl ed from fi shwhee 1 catches at Suns hi,ne Sta ti on, Adult Anadromous Investigations,Su Hydro Studies, 1982.- A94 - 29 16 ~u Z 12IJ.J ..::> "IJ.J 0:::8l.L 4 9 (0) 20 16 n I 200 I 308 f 416 I 524 I 632 I 749 MALES n =243 X =544 FEMALES n =171 X =553 .~ U ~12 :J "W (k:8 l.L 4 o <b) I 2.0.0 n I I I 398 416 524 632 LENGTH (mm) I 74a Appendix Figure 2-D-11.Length frequencies of sockeye salmon sampled from fishwheel catches at Talkeetna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. AS5 - MALES n -83 X =4378 f0 >-u Z 8lLJ::> 0 lLJ ~4 -'':\l:ilLL ~ 2 n~~ 0 ~ I I I t I I (0)zea 30'8 416 524 832 740 16 12 FEMALES n -38 X =530 t 7<4.0 I I f 308 416 524 632 LENGTH <mm) I2ae 8 9 >-U Z """lLJ 9 ::> 0w t:t.6h. ~ (b) Appendix Figure 2-0-12.Length frequencies of sockeye salmon sampled from fishwheel catches at Curry Station~Adul t Anadromous Investigations,Su Hydro Studies,1982. A96 I e1e I $32 I 454 I 376 I 298 I 220 o P'" ~", IS MALES n -130 ""'"12 i =.432. >- ~U Z 9W:> 0w Ct:e4- ~ 3 20 16 >-U ~12 :>ow ct 84- 4 o Cb) I 220 n I I I 298 378 454 532 LENGTH (mm) .I 810 FEMALES n =137 i'=412 ,..... i i Appendix Figure 2-D-13.length frequencies of pink salmon sampled from fishwheel catches at Susitna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A97 - 1"*'15 MALES -n -838 12 X ==433 >-uz gw::>aw ~6I.&.. ~ 3 ~ 0 r"1 I I I I I I (0)220 ~8 376 45<4 532 e10 < 16 FEMALES n -632 X =422 I I I 298 376 454 532 LENGTH Cmm) >-u @12 ::>ow ~. La...8 o Cb) .... I 220 ... I 610 Appendix Figure 2-0-14.Length frequencies of pink salmon sampled from fishwheel catches at Yentna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A98 ...., I 610 n I 532 I 454 I 376 I 298 I 220 o <a) <~~ """ 15 HALES n =618 .....12 X =441 >-u Z QW ::Jaw ~elJ.. ~ 3 20 "'"16 >- ~u Z 12W ::Ja....w ~8lL. [@I~~ 4 o (b) I 220 nn,......, I I I 298 376 454 532 LENGTH (mm) I 610 FEMALES ·n ==342 X =423 Appendix Figure 2-0-15.·Length frequendes of pink salmon sampled from fishwheel catches at Sunshine Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A99 - MALES n ...587 i ::a 425 I 810 ,.,,..I1 I S32 J 464 I 378 I 298 I 22" >-0 Z 9W ~::> 0w~eu... ~ IS 12 3 20 16 FEMALES n -3e1 x =428 I I I 298 376 454 532 LENGTH <mm) M I 6t0 .Mnn I 220 >-U Z 12W::>ow..~8 1.L.. <b) Appendix Figure 2-0-16-.Length frequencies of pink salmon sampled from fishwheel catches at Talkeetna Station,Adult Anadromous Investigations.Su Hydro Studies,1982. A100 4_ 15 MALES n -483 .f'!!lIiIlIIJIli 12 X =417 >-u Z 9~ 0 W....~eIL. )It ~ S F'"' e n n I I I I I I (0)229 298 378 454 S32 e19 >-u Q 12 ::>ow ~8lL. ~ Cb) I 229 I I I 298 376 454 532 LENGTH (mm) I 610 FEMALES n -322 X =421 Appendix Figure 2-0-17.Length frequencies of pink salmon sampled from fishwheel catches at Curry Station,Adult Anadromous Investigations,Su Hydro Studies,1982. Al01 HALES n -1....0 X =604 I 730 I 66121 l 59121 I 52a n I 4Sa J 380 3 >-u Z 9W ~ :J 0 W C!6 .....tL.., ~ (a) 20 16 >-um12 :Jo W a::81.L. 4 o Cb) I 38a n n I I I 4Sa520 ··590 6S0 LENGTH Cmm) J 730 FEMALES n co 2BS it =595 ~, Appendix Figure 2-0-18.Length frequencies of chum salmon sampled from fishwheel catches at Susitna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A102 n n9 Ca) I 380 I 450 I 520 I 590 I 680 I 730 n FEMALES n -302 X =586 I 730 I I I 450 520 590 660 LENGTH (mm) I 380 16 20 4 fa >u ~12 ::>ow 0::81L. Cb) - - Appendix Figure 2-0-19.Length frequencies of chum salmon sampled from fishwheel catches at Yentna Station,Adult Anadromous Investigations,Su HYdro Studies,1982. A103 I 739 I ese I 591a I 520 I 459 .I 380 o ~ 15 ,..-. MALES ~ n -501 12 i ..613 !'I!IlP >-U Z 91JJ :J 0 l.U ~8u..--I ~ 3 P\Im!l (0) FEMALES n ....532 ~=599 I 730 I I , 459 529 590 660 LENGTH (mm) ..,n n I 380 12 3 15 o >-wm 9 :Jo W Ct::6u.. Cb) Appendix Figure 2-0-20.Length frequencies of chum salmon sampled from fishwheel catches at Sunshine Station~Adult Anadromous Investigations,Su Hydro Studies,1982. A104 ",,-,. 20 18 >- U ~12 :::>ow 0::.8 tL. 4 I 38e t 458 I 520 I 590 I 880 I 738 MALES n -415 X =613 20 te >-o ~12 :::> (] LlJ ~8tL. e Cb) I 380 I'I450520590660 LENGTH <mm) I 7S0 FEMALES n -2t 1 i =601 Appendix Figure 2-D-21.Length frequencies of chum salmon sampled from fishwheel catches at Talkeetna Station.Adult Anadromous Investigations.Su Hydro Studies.1982. A105 20 '6 >-u ~'2 ::>ow (k:8 1J.. 4 o (a) I 380 I 450 I 520 I 590 I 660 I 730 MALES n -283 X =607 - 20 '6 >-U ~'2 ::>ow O!:8 1J.. FEMALES n =255 X =599 ~, ..... I 730 n n I I I 450 520 590 660 LENGTH (mm) n I 380 4 o Cb) Appendix Figure 2-D-22.Length frequencies of chum salmon sampled from fishwheel catches at Curry Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A106 ,..... ~" IS MALES n -146 12 i =550 >-u Z 9W :J C ~W ~eLt.. ~ 3 n~0 n 11 I I I I I I ~(0)27e 3S6 442 528 614 7ee FEMALES n :I 266 i =536 16 12 >- U Z 9W :J 0 W ~6Lt.. ~ 3 .0 n ~n I I I I I (b)279 356 442 528 614 799 LENGTH (mm) .- Appendix Figure 2-0-23.Length frequencies of coho salmon sampled from fishwheel catches at Susitna Station,Adult Anadromous Investigations,Su Hydro Studies,1982. A107 19 8 >-uz ew::> 0w ~<44- ~ 2 o [ 270 1sse r 442 I Isae.tU4 I 700 MALES n -497 X =546 - ~, FEMALES n •229 X =539 I 700 n I I I I 356 442 528 614 LENGTH Cmm) I 270 e 3 IS. 12 >-uzW 9 :::>ow ~6 . ....~ Cb) Appendix Figure 2-D~24.Length frequencies,of,coho salmon sampled from ~ fishwheel catches at Yentna Station~Adult Anadromous Investigations,Su Hydro Studies,1982. A108 15 12 FEMALES n -283 X =546 I 700 n I 614 r,n I I 356 442 528 LENGTH (mm) n n I 270 o 3 >-u Z 9W::>ow ~6 <b) - .... Appendix Figure 2-0-25.Length frequencies of coho salmon sampled from fishwheel catches at Sunshine Station,Adult Anadromous Investigations,Su ~dro Studies,1982. A109 MALES n -2se x =5508 10 >-u Z 6W '""":::> 0w ~4 ~1.L. .)t 2 ~"'ili 9 n n ~, I I I I .I I (a)279 356 442 528 614 700 ,.... IS FEMALES ~..- n -151 X ==55112 >-U Z 9W :J 0 W Ck:6tL. ~ ~ 3 1~fll ~- 0 I I I I I Cb)270 356 442 528 614 700 -LENGTHCmm) Appendix Figure 2-0-26.Length frequencies of coho salmon sampled from fishwheel catches Qt Talkeetna Station,Adult Anadromous I nves t iga t ions,Su Hydro Studies,1982. A 11 0 15 12,.. W Z 9W :J 0 Wa::81J.. ~ ~3 ~nrflll0 I I I I I I (a)270 356 442 528 '814 '700 ~ MALES n =94 X ::;521 FEMALES n -72 i ..54316 4 20 :>0- W ~12 :Jo Wa::81J.. 0 nnM ~ I I I I I Cb)270 356 442 528 614 709 LENGTH (mm) .- .... Appendix Figure 2-0-27.Length frequencies of coho salmon sampled from fishwheel catches at Curry Station,Adult Anadromous Investigations,Su Hydro Studies.1982. A111 20 ~i - I 420 I I I 260 300 340 380 LENGTH <mm) I 220 4 n -218 X =338 >-U Z 12W ::>ow ~8 lL. ~- Appendix Figure 2-0-28.Length frequencies of Bering cisco sampled from .fi shwheel catches at Sus itna,Yentna,Sunshine and Talkeetna stations,Adult Anadromous Investigations,Su Hydro Studies,1982. A112 APPENDIX 2-£ RADIO TELEMETRY TRACKING REPORTS FOR CHINOOK,CHUM AND COHO SALMON -Chinook Salmon,Radio Transmitter 600-2 Chinook salmon 600-2 was tagged and released at Talkeetna Station (RM 103) July 2,1982.Seven hours after being released fish 600-2 had ascended 0.2 miles to RM 103.2.On July 3~fish 600-2 was located 3.9 miles downstream at RM 99.3.It remafned within 0.3 miles of this location through July 7. Between July 7 and 8,fish 600-2 ascended to RM108.3.The next day,it was downstream in the Chulitna River (RM 98.5).On July 11,15,and 18,fish 600-2 was upstream 9.7,20.0,and 22.0 miles respectively in the Chulitna -River.Fish 600-2 was last detected July 18 at the mouth of Troublesome Creek,22.0 miles upstream in the Chulitna River (RM 98.5). A graphic presentation of the movements of chinook salmon 600-2 is provided in Appendix Figure 2-E-l. Chinook Salmon,Radio Transmitter 610-2 Chinook salmon 610-2 was tagged and releilsed at Curry Station (RH 120)June 23,1982.The fi sh mi grated upstream after bei ng rel eased and was off the mouth of Portage Creek (RM 148.9)June 26.The average migrational rate of fish 610-2 between RM 103 and 148.8 was in excess of 8.4 mpd,and the maximum rate recorded was 16.6 mpd in a 24 hour period .. Between June 26 and July 14,fish 610-2 twice departed Portage Creek confluence at RM 148.9 and entered lower Devil Canyon in the reach from RM 150.5 to 151.5.Fish 610-2 first entered lower Devil Canyon to RM 150.5 A 113 155 CH1NOOK SALMON 600-2 145 '\.Fi8h entered Chulitna River between 1510h 8 July and 0920h 9 July Troublesome 20;--Confluence ~.~ 16-1Q:; 24 135 UJ ...J- ~ a::125 UJ >-a:: »<t 115....Z....~ -I:loo -(/) :::> (/) 105 . Talkeetna Station Chulitna River Confluence, 95 24 26 28 302224 26 28 30 2 4 6 8 10 12 14 16 18 20 JUNE JULY Appendix Figure 2-E-1.Movement of radio tagged chinook salmon 600-2 in the Susitna River drainage during July,Adult Anadromous Investigations,Su Hydro Studies,1982. }~!~~!J J ,t !)J I j ~J J ,J B 'i ;;! ,"" ..- ..- between June 26 and 29.It remained at RM 150.5 from June 29 through July 1. On July 2 and 3,fish 610-2 was downstream at RM 149~8 and 148.8, respectively. From July 15 through 24,fish 610-2 was in Portage Creek as fa~upstream as 11.0 miles.Fish 610-2 departed Portage Creek (RM 148.9)between July 24 and 31 and was at RM 139.8 July 21.The fish carcass descended to RM 138.6 where it remained from August 4 to 19.The carcass and functional radio transmitter from this fish were recovered at RM 138.6 August 19. A graphic presentation of the movements of chinook salmon 610-2 is provided in Appendix Figure 2-E-2 . Chinook Salmon,Radio Transmitter 620-1 Chinook salmon 620-1 was tagged and released at Curry Station (RM 120)June 30,1982.Fish 620-1 ascended directly to RM 138~6 after being released at an average migrational rate of 10.4 mpd.It remained at the mouth of Indian River at RM 138.6 from July 2 through 8. A 115 Fish departed Devj I Canyon between 1530 h 2 July and 095!5h 3 July \ ~--\Fhh departed Devt!Canyon and re-entered Portage Creek lometlme \ between 1555h 14 July and 0942h 15 July Fish re -entered Devil Canyon between 0955 h a July and 2135h 5 Ju I Y Fish entered Devil Canyon between 1740h 26 June and 1240 h 29 June 155 145 w 135 ..J-::!: crw ~125 cr «>z ~.... ~en 115 0);:) en 105 95 CH INOOK SALMON 610-2 22 24 26 28 JUNE 2 4 6 8 I 2 14 16 18 20 22 24 JULY Appendix Figure 2-E-2. J I J )j J Movement of radio tagged chinook salmon 610-2 in the Susitna River drainage during June and July,Adult Anadromous Investigations,Su Hydro Studies,1982. )) J I J J ~J I J _I ]_J , ,~ ,~ ..... Fish 620-1 entered Indian River (RM138.6)July 8ar 9.It was located on the latter date 1.5 miles upstream and July 11,13,15 and 18,5.1,9.2,13.0 and 16.2 miles upstream in Indian River,respectively.Fish 620-1 was located July 24,17.2 miles upstream in Indian ~iver and presumably spawned in this stream.The carcass of this fish entered theSusitna River on or about August 3. A graphic presentation of the mov~ments of chinook salmon 620-2 is provided in Appendix Figure 2-E-3. Chinook Salmon,Radio Transmitter 660-1 Chinook salmon 660-1 was tagged and released at Talkeetna Station (RM 103) June 28,1982.After being released fish 660-1 migrated upstream at a migrational rate not less than 6.5 mpd.Fish 660-1 was in lower Devil Canyon July 5 and 7 atR~1 150.4 and 151.3,respectively.Sometime between July 7 and 9,fish 660-1 departed Devil Canyon and moved downstream.It was last detected at RM 97.8 July 9. The fastest upstream migrational rate recorded on fish 660-1 between RM 103 and 150.4 was 14.6 mpd. Agraphic presentation of the movements of chinook salmon 660-1 is provided in Appendix Figure 2-E-4. A117 Fish departed Indian River between 0940h 31 July and 1510 h 3 Auqust ~ --15e ~12 ~ct 9 .~6 'l) ~...,....~.......... "Fish entered Indion River between 1230 h 8 July and 1031 h 9 July 155 145 J I n dian River I Confluence 135 w -.J- :E a::125w >-a::l'E--Curry Stotlon)I- ~<! .-Z 115 (J)~-en ~ (J) 105 95 CHINOOK SALMON 620-1 22 24 26 28 30 2 4 JUNE 6 8 10 12 14 16 18 20 22 24 26 28 30 I 3 J UL Y AUGUST Appendix Figure 2-E-3.Movement of radio tagged chinook salmon 620-1 in the Susitna River drainage during June,July and August,Adult Anadromous Investigations,Su Hydro Studies,1982. \~ J I j j ~J W J J J ~~~I .J I ..J ,j .~ I s J 1 1 1 1 )) ) ]B 1 ~1 B Devil Canyon Fish entered Devil Canyon between IOOOh 3 July and 1030h 5 Ju Iy Talkeetna Sta tion 145 135 155 l.LI ...J ~125 0:: l.LI > 0:: 115c:rz I- 00 :::> 00 105 »........ co 95 Fish departed Devil Canyon between 1030h 5 July and 1030h 7 July CHINOOK SALMON 660-1 22 24 26 28 JUNE Appendix Figure 2-£-4. 30 2 4 6 8 10 12 14 16 18 20 22 24'26 28 30 I 3 5 JULY AUGUST Movement of radio tagged chinook salmon 660~1 in the Susitna River drainage during June and July,Adult Anadromous Investigations,Su Hydro Studies,1982. Chinook Salmon,Radio Transmitter 670-1 Chinook salmon 670-1 was tagged and released at Curry Station (RM 120) June 24,1982.The following day fish 670-1 was at RM 125.3.It reached the mouth of Indian River at RM 138.6 on or about June 30. Fish 670-1 migrated between RM 120 and 135.5 at rates exceeding 5.5 mpd and from RM 135.5 to 138.3 at speeds consistently less than 1.7 mpd. Fish 670-1 remained at,or within 0.2 miles,of Indian River (RM 138.6)from llune 30 to July 8.Between July 8 and 9,fish 670-1 entered Indian River and ~, ~ I I was last detected 2.8 miles upstream in the river July 24.Fish 670-1 presumably spawned in Indian River in the third and fourth week of July.~- A graphic presentation of the movements of chinook salmon 670-1 is provided in Appendix Figure 2-E-5. Chinook Salmon,Radio Transmitter 680-1 ~\ Chinook salmon 680-1 was tagged and released June 25,1982 at Talkeetna Station (RM 103).The following day,fish 680-1 was 5.8 miles downstream at RM 97.2.Fish 680-1 remained between RM 96.0 and 99.7 from June 28 through July 3. •Between July 3 and 5,fish 680-1 entered the Talkeetna River (RM 97.0),where it was located six miles upstream July 5.It was at the same location July 7 A120 )1 1 j )1 1 1 1 J J .]t 1 ··1 J i")),J 155 145 135 w ...J-~ 0::125 w >- >0::.. I\) <t 115..z t--(/) => (/)105 95 ~.... I: It: g 6,»4 ~2 \FISh entered Indian River between 1230h 8 July and 1032h 9 July CHINOOK SALMON 670~1 Appendix Figure Movement of radio tagged chinook salmon 670-1 in the Susitna River drainage during June and July,Adult Anadromous Investiga ti ons,Su Hydro Studi es,1982. and ,July 9 was last located nine miles upstream in Chunilna Creek,a Talkeetna River tributary. A graphic presentation of the movements of chinook salmon 680-1 is provided in Appendix Figure 2-E-6. Chinook Salmon,Radio Transmitter 700-1 Chinook salmon 700-1 waS tagged and released at Talkeetna Station (RM 103.0) June 22,1982.It ascended by June 26 to within 0.4 miles of the Indian River confluence at RM 138.6. Fish 700-1 ascended from RM 103.3 to 138.2 at migrational rates ranging from 5.3 mpd to 9.4 mpd. Fish 700-1 occupied various positions in the Susitna River within 0.4 miles of the mouth of Indian River{RM 138.6),including the mouth of Slough 17 (RM 138.8),for several days prior to entering that tributary. On July 3,fish 700-1 was 2.2 miles upstream in the Indian River (RM 138.6) as detected by an aeri al survey on that date.The fish presumably ascended the Indian River (RM138.6)June 30 or July 1,evident by failure to locate fish 700-1 by waterbourne telemetry surveys in the mainstem Susitna River July 1 and 2. Fish 700-1 progressively moved upstream in the Indian River (RM 138.6)from A122 - - - J 1 1 ~1 i 1 D 1 j ~]i I J i ]).))\} 155 CHINOOK SALMON 680-1 145 .............Fish ent~red Chunllna Creek between 0947h 7 July and 1I12h 9 July '"Fish entered Tal keetna River between 0850h 3 July and 2103h 5 July 95 135 UJ ....J- :E 125 a:: UJ >-a::> «1/5.... zI'.) ~~- (J) ::::> (J) \(\1;,....J TalkHtna Station Appendix Figure 2-E-6.Movement of radio tagged chinook salmon 680-1 in the Susitna River drainage during June and July~Adult Anadromous Investigations~Su Hydro Studies~1982. July 3 to 11.It was last detected 8.8 miles upstream in the Indian River July 11. A graphic presentation of the movements of chinook salmon 700-1 is provided in Appendix Figure 2-E-7. Chinook Salmon,Radio Transmitter 710-3 Chinook salmon 710-3 was tagged and released at Talkeetna Station (RM 103) July 7,1982.Fish 710-3 moved upstream and reached RM 122.9 July 14 which represents an average migrational rate of 2.9 mpd. Between July 14 and 15,fish 710-3 descended from RM 122.9 to 101.6 where it was located July 16.Its downstream movement from RM 119.5 to 105.6 was at the rate of 24 mpd. Aerial surveys in the Talkeetna River (RM 97.0)drainage,lower 15 miles of the Chulitna River (RM 98.5)and the Susitna River from RM 152 to 77.0 failed to detect this fish from its previous known location at RM 101.6 July 16. A graphic presentation of the movements of chinook salmon 710-3 is provided in Ap~endix Figure 2-E~8 .. Chinook Salmon,Radio Transmitter 720-1 Chinook salmon 720-1 was taqged and released at Curry Station (RM 120)July 8,1982.It migrated upstream to the mouth of Indian River (RM 138.6)within A124 -.1 1 -~-i 1 1 -)I ]j J -j ~I I 1 c J 1 ) Tal keetna Station Fish detected at Indian River Confluence 28.29 and 30 June / ~ "12e ~8c: b ~4 A ••~1~FiSh departed Indian River Confluence and ascended Indian River between 30 June and 3 July Indian River Confluence 155 105 145 W ...J :IE a:125 lL/ > a: 135 «"5 Z I- CJ) ::J en ~ I\) en » 95 CHI NOOK SALMON 700-1 14 16 18 20 22 24 26 2~ JULY 22 24 26 28 30 2 4 6 8 JUNE Appendix Figure 2-E-7.Movement of radio tagged-chinook salmon 700-1 in the Susi'tna River drainage during June and July,Adult Anadromous,Investigations,Susitna Hydro Studies,1982. 155 145 UJ -I ~ >.... N 0) a:: UJ > 0:: <115 Z t- en ;:) (J) 95 To Ik••tna Station CHINOOK SALMON 710-3 22 24 26 28 30 2 4 6 JUNE Appendix Figure 2-E-8.Movement of radio tagged chinook salmon 710-3 in the Susitna River drainage during July,Adult Anadromous Investigations,Su Hydro Studies,1982. ) J .~~.J J J j ;I I J J J j J I ~ 1 ) five days of release.The average migrational rate of fish 720-1 in this five day period was 3.6 mpd;the fastest speed recqrded on this fish during an 11.3 hour period was 4.7 mpd. Between .July 13 and 14,fish 720-1 entered Indian River (RM 138.6)where it was detected 0.3 miles upstream July 14~Fish 720-1 was last located 8.1 miles upstream in Indian River Juli 24. A graphic presentation of the movements of chinook salmon 720-1 is provided in Appendix Figure 2-E-9. Chinook Salmon,Radio Transmitter 720-3A Chinook salmon 720-3Awas tagged and released at Talkeetna Station (RM 103) June 24,1982.It was detected 2.7 miles downstream of RM 103 at RM 97.1 June 26 and was within 0.2 miles of this location June 28 and 30. Between June 30 and July 3,fish 720 ....3A entered the Talkeetna River (RM 97.0).On July 3,fish 720-3A was 0.7 miles upstream in the Talkeetna River and July 7 was 13.3 miles further upstream in the river.On July 9,fish 720-3A was last located 21.9 miles upstream in the Talkeetna River. A graphic presentation of the movements of chinook salmon 720-3A is provided in Appendix Figure 2-E-10. A127 15!S 145 13!S W ...J ~12!S a::: w > 0:»......«115 I\)Z (X)..... en ::>en 105 ge Indlon River Confluence Curry Station Fish entered I ndlan River bet.un 113eh 13 July and 14eOh 14 July CHINOOK SALMON 720-1 22 24 26 28 30 2 4 JUNE 6 8 10 12 14 16 18 20 22 24 26 28 30 JULY I 3 5 AUGUST Appendix Figure 2-E-9.Movement of radio tagged chinook salmon 720-1 in the Susitna River drainage during July,Adult Anadromous Investigations,Su Hydro Studies,1982. ) I I J I J .~J J ~I I ~~]I !J ) ~, I i J I J I )j ))I J ~!1 1 ) ~~~ ) 155 CHINOOK SALMON 720-3A 145 135 Fish departed RM 97.0 Susitna RIver and entered Talk.etno River between 0930h June and 0940 h 3 Ju 11 24 Talkeetna Stat ion Talkeetna RIver Confluence95 105 115 lJJ ...Ji 125 > 0:: ~ lJJ I\) >- co 0:: <f Z.... (/) :) (f) 22 24 2628 30 2 46 8 1~12 14 16 18 20 22 24 JUNE JULY Appendix Figure 2-E-10.Movement of radio tagged chinook salmon 720-3A in the Susitna River drainage during June and July,Adult Anadromous Investigations,Su Hydro Studies,1982. Chinook Salmon,Radio Transmitter 720-3B . Chinook salmon 720-38 was tagged and released at Curry Station (RM 120)July 9,1982.Four days later it was 1.3 miles upstream in Portage Creek (RM 148.9).Enroute to Portage Creek,fish 720-3 displayed relatively consistent upstream migrational rates.Migrational rates for periods of time,between successive telemetry locations less than and greater than five hours ranged from 5.8 to 10.3 mpd.and 8.6 to 11.3 mpd,respectively.Aerial surveys July 15 and 18 establ ished fish 720-3B in Portage Creek (R~1 148.9)4.5 and 6.2 miles upstream,respectively. Between July 18 and 24,fish 720-3B departed Portag~·Creek (RM 148.9), descended to RM 138.6 and entered Indian River.Fish 720-38 was 3.2,3.3, and 2.8 miles upstream in Indian River,respectively July 24 and 31 and August 11 and presumably spawned in this river. A graphic presentation of the movements of chinook salmon 720-3B is provided in Appendix Figure 2-E~11. Chinook Salmon,Radio Transmitter 730-1 Chinook salmon 730-1 was tagged and released at Talkeetna Station (RM 103) June 24,1982.Fish 730-1 moved downstream upon release and remained between RM 95.0 and 97.7 from June 26 through July 3.On July 5 fi sh 730-1 was located 2.7 miles upstream in the Chulitna River (RM 98.5)and remained in the Chulitna River through July 9.Its furthest movement upstream in the Chulitna River was 11.4 miles. A130 JliIMl., 1 ..1 1 j )I B ~I )1 J 1~J ))) » -I. CA) -I. 11515 1415 135 iLl ..J :E a:: iLl Il5> a:: c{z ....1115 CI) ::::) CI) 105 915 Portage Creek Confluence Indian Rivlr Confluenci \ Fish deported Portage Creek and enterld Indian River b.t.een IOOOh 18 J III,and 1122h 24 Jul, Fish .ntared Portage Creek bet.lln 17221\12 July and 1154h 13 July CHINOOK SALMON 720-38 22 24 26 28 30 2 4 6 8 10 12 14 16 .18 20 22 24 26 28 30 I 3 15 JUNE JULY AUGUST Appendix Figure 2-E-ll.Movement of radio tagged chinook salmon 720~3B in the Susitna River drainage during July and August.Adult Anadromous Investigations.Su Hydro Studies,1982. Fish 730-1 departed the Chulitna River (RM 98.5)between July 9 and 11 ascended the Susitna River and eventually reached the Indian River (RM 138.6) July 17 or 18.On July 11,fish 730-1 was at RM 117.9,19.4 miles upstream from the mouth of the Chulitna River.It progressed upstream and .was at RM 123.8 and 131.1 July 12 and 13,respectively.However,fish 730-1 was next downstream at RM 120.8 July 15.The following day fish 730-1 was 9.6 miles upstream at RM 130.4,and by July 17 it was located at RM 138.5 immediately downstream of the mouth of Indian River (RM 138.6).On July 18,fish 730-1 was 4.2 and 9.2 miles upstream,respectively,in Indian River (RM 138.6).It remained in Indian River through August where it presumably spawned. A graphic presentation of the movements of chinook salmon 730-1 is provided in Appendix Figure 2-E-12. Chinook Salmon,Radio Transmitter 730-2 ""'" - ~, - Chinook salmon 730-2 was tagged and released at Curry Station (RM 120)June 29,1982.The following day it was encountered 1.8 miles upstream at RM 121.3.Fish 730-2 was subsequently detected upstream at RM 138.5,0.1 miles downstream of the Indian River confluence (RM 138.6),July 3.~ The two fastest mi grati ona 1 rates recorded on fi sh 730:"2 between RM 120 and 138.4 were 9.4 and 18.0 mpd,respectively,over a 18.6 hour and 1.2 hour period. Between July 3 and 5,fish 730-2 ascended Indian River (RM 138.6),where it was detected 2.1 miles upstream July 5.It was later detected at the same A132 J i 1 1 1 J 1 J I 1 I J i D J ·1 i )) 155 CHINOOK SALMON 730-1 ~iSh exited Chlf Iitno Rive'_.pnd mia.rated ugstream Susitna River between 0945h 9 July and IZ32h II July -Fish entered Indian Rlyer between 1600h 17 July and lOO5h 18 July ~12.... Ii: Q:;8 c: .t3~4 ~ \ \1 Fish deported Susitna Ri"er ascended Chulitna RiY8r between 0930h 3 July and 2138h 5 July Indian Riyer Confluence Fourth of July Cr.Confluence 95 145 135 W ...J ::!:125 a::w > a:: 115ex:z J- (/) ;:) (/)·105 --» (,,) .(") 22 24 26 28 30 ~4 6 8 10 12 14 JUNE 18 20 JULY Ap~endix Figure 2-E-12.Movement of radio tagged chinook salmon 730-1 in the Susitna River drainage during June and July,Adult Anadromous Inv~stigations,Su Hydro Studies,1982.. location July 7.Fish 730-2 was last located July 24,9.7 miles upstream in Indian River and presumab1y'spawned in the river. Chinook Salmon,Radio Transmitter 730-3 Chinook salmon 730-3 was tagged and released at Curry Station (RM 120)June 25,1982.Within five hours it h~d ascended 0.7 miles upstream to RM 120.2 and by June 30 was at the mouth of Portage Creek (RM 148.9).The overall upstream migrational rate of fish 730-3 from time of release to detection at Portage Creek was 7.4 mpd.Fish 730-3 demonstrated faster movement when it progressed 12.2 miles from RM 120.2 to 132.4,within 24.5 hours which was equivalent toa speed of 12.0mpd. Fish 730-3 remained ~t the mouth of Portage Creek (RM 148.9)for several days prior to entering that stream.It was located by telemetry gear at RM 148.9 from June 30 to July 3.Fish 730-3 ascended Portage Creek between July 3 and 5.On July 5,the fi sh was 9.5 mi 1es upstream and was 1ast detected in Portage Creek at that same location July 15. A graphic presentation of the movements of chinook salmon 730-3 is provided in Appendix Figure 2-E-14. .A134 .... 1 j ) ---I )) "-FiSh entered Indian River between 1000h 3 July and 2200h 5 July 155 I ..-I~j .... ~ ~ Indian River.Confluence 13S UJ .J-~ ci::125 w >-i+--Curry Station>a:: ~ ~«liS 01 Z ~-(J) :J (J) 105 9S CHINOOK SALMON 730-2 22 24 26 28 30 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 1 ;, JUNE JULY AUGUST Appendix Figure 2-E-13.Movement of radio tagged chinook salmon 730-2 in the Susitna River drainage during June and July,Adult Anadromous Investigations,Su Hydro Studies,1982. ~ ~~ ,-:10 (.)8 ~: ce 2:1(\.'.... Fish entered Portage Creek between 1030h 3 July and 2139h 5 July Portage Creek Confluence 145 155 135 I.Ll ..J-:!: c:::125 I.Ll >-1..&-Curryc::: Station >~115 .....r- CA)-enm::> en 105 95 CHINOOK SALMON 730-3 22 24 26 28 30 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 I 3 5 Appendix Figure 2-E-14. 1I \') jJ AUGUST •~ ,0J,J JULY ) )I~ Movement of radio tagged chinook salmon 730-3 in the Susitna River drainage during June and July,Adult Anadromous Investigations,Su Hydro Studies,1982. It JUNE ,, tI r Chinook Salmon,Radio Transmitter 740-2 Chinook salmon 740-2 was tagged and released at Curry Station (RM 120)June 28,1982.Two days later the fish was at RM 123.1 ..Between July 1 and 3, fish 740-2 ascended from RM 123.1 to 148.9 (Portage Creek)in approximately 2.4 days at an average speed nf 9.9 mpd. On July 5,fi sh 740-2 was located 1.4 mi 1es upstream in Portage Creek (RM 148.9).Fish 740-2 was last detected July 24,2.1 miles upstream in Portage Creek where it presumably spawned. A graphic presentation of the movements of chinook salmon 740-2 is provided in Appendix Figure 2-E-15. Chinook Salmon,Radio Transmitter 740-3 Chinook salmon 740-3 was tagged and released at Curry Station (RM 120)July 6,1982.Two days 1ater it was upstream at RM 121.8.On July 12,fi sh 740-3 was 0.2 miles upstream in Portage Creek (RM 148.9).The fastest migrational rate recorded between RM 120 and 148.9 was 9.6 mpd in 16.2 hours of observation. Fish 740-3 was last located July 24,8.3 miles upstream in Portage Creek (RM 148.9)and presumably spawned in this stream. A graphic presentation of the movements of chinook salmon 740-3 ;s provided in Appendix Figure 2-E-16. A137 "'-FiSh entered Portage Creek between I030h 3 July and 2138 h 5 July Portage Creell. Conflu.nc. 145 155 135 IJJ -J-~ a::125 IJJ > a::r--currt » Stat on ....«115 CA) z ...... (X)-CJ) :;) CJ) 105 95 CHINOOK SALMON 740-2 22 24 26 28 !O 2 4 JUNE JULY AUGUST Appendix Figure 2-E-15.Movement of radio tagged chinook salmon 740-2 in the Susitna River dralnage during June and July,Adult Anadromous Investigations,Su Hydro Studies,1982. \J ) .~,J )J I I I J 1 I I ~]J ).1 .~~ \FiSh re-entered Portage Creek between 093Bh 15 July and IOl2h 18 July \ \Fi8h depa rted Portage Creek between 1156h 13 July and 1545h 14 Ju Iy Fish entered Portage Creek between 1158h II July and 1748 12 July Portage Creek Confluence 95 155 145 1 J 1 1 J J J -j "j J.I J I J 1 I 1'\~ ))J CHINOOK SALMON 740-3 22 24 26 2830 JUNE 2 4 6 8 10 12 14 16 18 JULY 20 22 24 26 28 30 I 3 5 AUGUST Appendix Figure 2-E-16.Movement of radio tagged chinook salmon 740-3 in the Susitna River drainage during July,Adult AnadromouS Investigations,Su Hydro Studies,1982.·. Chum Salmon,Radio Transmitter 600-3 Chum salmon 600-3 was tagged and released at Talkeetna Station (RM103) August 9,1982.Approximately eight hours after being released it was detected 0.6 miles downstream at RM 102.4.Fish 600-3 remained within 0.2 miles of this location until August 11,when it began ascending.It was detected at RMl 02.6 at 0850 h August 11 and later the same day was at RM 102.7 and 103.8 at 1500 and 2010 h.respectively.It was last located at RM 103.8 August 11.However,September 4 the Petersen disc of this fish was recovered in Slough 21 (RM 140.0).Presumedly,the transmitter failed on or about August 11 and fish 600-3 spawned in Slough 21. A graphic presentation of the movements of chum salmon 600-3 is provided in Appendix Figure 2-E-17. Chum Salmon,Radio Transmitter 610-3 Chum salmon 610-3 was tagged and released at Curry Station (RM 120)August 19,1982.Within 6.4 hours of release it moved downriver 1.0 miles.Fish 610-3 migrated upstream the following two days and was at the Indian River confluence (RM 138.6)August 21.The maximum upstream migration rates recorded between Augu·st 19 and 21 was 18.5 mpd and 17.3 mpd for monitoring periods equal to or less than.and greater than 10 hours,respectively. ~- - Within 13.5 hours after being located at the Indian River confluence (RM - 138.6).fish 610-3 had descended 39.5 Miles downstream to RM 98.6.It A"""'\ A140 J 1 }1 1 I I ]I 1 1 ))) >• .fl- • 155 145 135 W ...J ~125 0:: w> 0:: et 115 z l- (/) ~ rn CHUM SALMON 600-3 105 95 Talkeetna Station •Fish la't detected on ..--.II AUQust at RM 103.8 Appendix Figure 2-E-17.Movement of radio tagged chum salmon 600-3 in the Susitna River drainage during August,Adult AnadromoU5 Investigations,Su Hydro Studies,1982. remained at RM -98.6 through August 26 and was last monitored at RM 96.0 August 27. A graphic presentation of the movements of chum salmon 610-3 is provided in Appendix Figure 2-E-l8. Chum Salmon,Radio Transmitter 620-2 Chum salmon 620-2 was tagged and released at Talkeetna Station (RM l03) August 2,1982.Within 20.5 hours of release it was 10.6 miles upstream at RM 113.6.Fish 620-2 was next Jocated August 5 at RM 132.0. Between August 2 and 5,fish 620-2 migrated at rates ranging from 7.7 to 21.6 mpd. By August 6,fish 620-2 moved downstream 12.5 miles to RM 117.5.It remained undetected by telemetry water-bourne and aerial surveys from RM 96.0 to 150.4 and occasional overflights of the Talkeetna River drainage until August 14, when it was detected 14.2 miles upstream in the Talkeetna River.Fish 620-2 was located last in the Susitna River at RM 97.9 a month later. A graphic presentation of the movements of chum salmon 620-2 is provided in Appendix Figure 2-E-19. Chum Salmon,Radio Transmitter 620-3 Chum salmon 620-3 was tagged and released at Curry Station (RM 120)August 9, A142 --- ~, ~, --1 -1-1 ) 155 145 135 ~Indian River Confluence }) CHUM SALMON 610-3 W ...J -12~ »a:: Curry StationwicC-">""-a::~U5 «z l- en ::::> en 105 Fish deport.d Indian Rlv.r Confluence and / mOV.d ~ownstream to RM 98.6 ••tw ••',930b 21 A••••'••"0930b 22 A....' 95 30 I 3 5 7 9 11 -13 15 JULY Appendix Figure 2-£-18.Movement of radio tagged chum salmon 610-3 in the Susitna River drainage during August,Adult Anadromous Investigations,Su Hydro Studies,1982. 155 CHUM SALMON 620-2 145 135 rRMI3~.O w -1-125 :E >cr UJ ~> ~cr ~115 <! Z.--en ::> en 105 I Talkeetna Station 1 95 Fish moved downstream fromRM 132.0 to 117.5 between /0917h 5 AUO\llt and 1700h 6 A\loust Fish departed SusitnaRiver and entered Talkedna River .........between 6 August and 14 August;last detected at ~mouth Sheep River 14 August )~ J ))I J i I J J J »J ~ •.~J! Appendix Figure 2-E~19.Movement of radio tagged chum salmon 620-2 in the Susitna River drainage during August,Adult Anadromous Investigations,Su Hydro Studies,1982. \:l j) r 1982.Two days after release it was located 5.9 miles upstream at RM 126.4. On August 14 and 18,it was at the mouth of Portage Creek (RM 148.9). The rate of upstream movement of fish 620-3 from time of release to first detection at the mouth of Portage Creek (RM148.9)was 6.2 mpd.The fish was capable,however,of moving substantially faster.For example,August 11 it moved 3.6 miles upstream in 7.4 hours which is equivalent to a speed of 11.7 mpd.Later the same day,fish 620-3 moved 0.8 miles upstream in 65 minutes, equivalent to a speed of 17.7 mpd. Fi sh 620-3 ascended from the confl uence of Portage Creek (RM 148.9)to RM 150.3 in lower Devil Canyon between August 18 and 22.By August 26,it had moved back downstream and was 2.1 miles upstream in Portage Creek (RM 148.9). r-Between August 26 and 31,fish 620-3 descended to the confluence of Portage Creek (RM 148.9)and subsequently moved downstream and occupied Slough 21, ~ where it was detected spawning September 8 and 9. A graphic presentation of the movernentsof chum salmon 620-3 is provided in Appendix Figure 2-E-20. Chum Salmon,Radio Transmitter 630-2 Chum salmon 630-2 was tagged and released at Talkeetna Station (Rr1 103) August 4,1982.Seven hours after being released it was 1.4 miles downstream at RM 101.6.On August 5 fish 630-2 had re-ascended to RM 103 and by August 13 was at the Portage Creek confluence (RM 148.9). A145 Fish detected inS lough 21 on 8 and 9 September CHUM SALMON 620-3 Filh moved downstream from Devil canyon and ./entered Portage creek.between 1I00h 22 ,,/"Augult and 18Mh 26 Augult Fish occupied Portage Creek . \ --...J ~Confluence 1650h 31 Augult Fish detected in Devil Canyon (RM 150.3)0840h and JlOOh 22 Augult Filh located at Portatjle Creek Confluence I040h 18 Autjlust J(Slough 21 Confluence ~Devil Canyon ~Portage Creek Confluence 95 135 155 145 UJ ..Ji 125 > ~0:: ~UJ '""k---Curry Station> 0)-0:: 115 <rz I--en :J en 105 30 JULY 3 5 7 9 II 13 15 17 19 21 23 25 27 29 31 2 4 6 8 AUGUST SEPTEMBER Appendix Figure 2-E-20.Movement of radio tagged chum salmon 620-3 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982.) J D J ,~)}B J I I J J ;J J )j J ~ Between August 4 and 5,maximum recorded upstream migrational rates of fish 630-2 were 10.6 mpd and 19.4 mpd,respectively,for periods of time greater than,and equal or less than 10 hours between consecutive observations. Fish 630-2 was first detected in Portage Creek (RM 148.9)August 14,1.8 mi 1es upstream.It was next located 11.2 mi 1es upstream in Portage Creek August 27 and was at the same location when last encountered September 10. A graphic presentation of the movements of chum salmon 630-2 is provided in Appendix Figure 2-E-21. I' I Chum Salmon,Radio Transmitter 630-3A Chum salmon 630-3A was tagged and released at Talkeetna Station (RM 103) August 15,.1982.On August 21,fi sh 630-3A was detected in Slough 9 (RM 129.0)which would represent an average upstream migration rate of 4.3 mpd. Fish 630-3A remained in Slough 9 (RM 129.0);the carcass was recovered there and necropsied August 27.It was found to be partially spent. A graphic presentation of the movements of chum salmon 630-3A is provided in Appendix Figure 2-E-22. Chum Salmon,Radio Transmitter 630-3B Chum salmon 630-3B was tagged and released August 28.1982 at Talkeetna Station (RM l03).It was next located August 31,7.6 miles upstream in the A147 155 k Portage Cre.k Confluence "T-_Fish entered Portag.Creek between 1840 h 13 August and 0951 h 14 August 95 145 135 I.Ll ..J- ~125 a:: LLJ >-a::» 4:115.... ~Z I-CD -(f) :::> (f) 105 Talke.tna Station CHUM SALMON 630-2 30 1 3 5 JULY Appendix Figure 2-E-21. 7 9 II 13 15 f7 19 21 23 25 27 29 3 I AUGUST Movement of radio tagged chum salmon 630-2 in during August and September,Adult Anadromous Studi es,1982 ~ 2 4 6 8 10 12 SEPTEMBER the Susitna River drainage Investigations,Su Hydro ))) J J j ..~1 J •;J J I I .~,J .~;.~1 j )1 l 1 )1 -cl 1 J ~----,~~~~))) 155 145 95 135 ~/FI••lint d.t.ct.d ;.Slo••'9 21 Auoust SlouOh 9 r "-~125 i Carcass recovered In partially srent condition at SlouOh 9 .27 Auous >a:::w....> .flo,- CO lr 115 <iz.... (J) :::> (J)105 To I k.e tna Stat ion CHUM SALMON 630-3A 30 I 3 5 JULY Appendix Figure 2-E-22. 7 9 II 13 15 17 19 21 23 25 27 29 31 2 4 6 8 10 12 AUGUST SEPTEMBER Movement of radio tagged chum salmon 630-3A in the Susitna River drainage during August,Adult Anadromous Investigations,Su Hydro Studies,1982. Talkeetna River (RM 97.0).Indirect evidence suggests that fish 630-3B entered the Tal keetna River sometime before 1700 h August 29,when a water- bourne telemetry survey from RM 96.0 to 150.6 August 29 did not locate this fish. Fish 630-3B was next located 9.0 miles upstream in the Talkeetna River (RM 97.0)September 1.It was last found 9.2 miles upstream in the Talkeetna River September 5. A graphic presentation of the movements of chum salmon 630-38 is provided in Appendix Figure 2-E-23. Chum Salmon,Radio Transmitter 640-2 Chum salmon 640-2 was tagged and released at Talkeetna Station (RM 103) August 7,1982 and was detected 22.2 hours later August 8,18.8 miles upstream at RM 121.8.This represents an upstream migrational speed of 20.3 rnpd. Indirect evidence suggests that fish 640-2 descended and entered the Talkeetna River (R~'97 .0)during a 24.5 hour period between 1200 h August 8 and 1230 h August.9.Fish 640-2 was detected 4.2 mil es upstream in the Talkeetna River (97.0)August 11 but was not detected by telemetry in a waterbourne survey from RM 96.0 to RM 139.0 August 10.It was last detected at the previous mentioned Talkeetna River location August 11 despite sUbsequent telemetry surveys in the Talkeetna River drainage including Chunilna (Clear)Creek,Iron Creek,Oiappointment Creek,and Sheep River. A150 - """'. ]-i ]l 1 I J 1 '1 i )) 155 145 135 CHUM SALMON 630-38 1.Ll ..J i 1"25 a:::>l.L/ -a.>-01 0:: -a.115 <{ Z I--en ::> en 105. Talk••tna StatJon Talkeetna Ri".r Confluence J 95 ~e Q:" I:l<:: "-'b:10....~e 6 4 ~FiSh first detected In Talkeetna River 3\August 30 JULY 3 5 1 9 11 13 15 11 19 2 I AUGUST Appendix Figure 2-E-23.Movement of radio tagged chum,salmon 630-3B in the SusitnaRiver drainage during August and September,Adult Anadromous Investigations,SuHydro Studies,1982. - A graphic presentation of the movements of chum salmon 640-2 is provided in Appendix Figure 2-E-24. Chum Salmon,Radio Transmitter 650-2 Chum salmon 650-2 was tagged and released at Curry Station (RM 120)August 9, 1982.Augustll,fish 650-2 was at RM 131.1.Four hours later the same day I it was last detected 20.5 miles downstream at RM 110.6. .~ A graphic presentation of the movements of chum salmon 650-2 is provided in ""'" Appendix Figure 2-E-25. Chum Salmon,Radio Transmitter 660-1 Chum salmon 660-1 was tagged and released at Talkeetna Station (RM 103)- August 13,1982.About eight hours after being released it was 1.9 miles downstream at RM 10T.l.Thirteen hours later August 14,fish 660-1 was located an additional 2.9 miles downstream at RM 9R.l. Between August 14 and 18,fish 660-1 entered and was 14.2 miles upstream in ~ the Talkeetna River (RM 97.0)in the Sheep Creek tributary.On August 22, fish 660-1 was downstream in the Talkeetna River approximately 12 miles from its previous location.On August 26,it was 33.6 miles upstream in the Talkeetna River and was last located downstream approximately 31 miles from the previous location. A152 1 ]J I ]j ]~l!)J 1 J "~~!,I "" 155 CHUM SALMON 640-2 145 T(1lk~Sfn(1 R;ysr mileIFishmoved'downstream from RM 121.8 and entered Talkeetna /River between 1I12n 8 August and 1130 h II August Appendix Figure 2-E-24.Movement of radio tagged chum salmon 640-2 in the SusitnaRiver drainage during August.Adult Anadromous Investigations,Su Hydro Studies,1982. 155 14~ 13~ w }-RM 131.1 .Ji 125 >a:: .....IJJ 01·>l+--Curry Station- .~a:: 115«z I--(fJ ::;) (fJ 105 Fish moved downstream from RM 131.1 to 110.6 /between 10lSh and 1~45hon II August 95 CHUM SALMON 650-2 4 6 S 10 12 SEPTEMBER II 13 15 17 19 2\23 25 27 29 3\2 AUGUST 7 9 Movement of radio tagged chum salmon 650-2 in the Susitna River drainage during August,Adult Anadromous Investigations,Su Hydro Studies,19B? ~\ )J ,J J J )J J ~J~ 3 S J) 30 JULY Appendix Figure 2-E-25. 1J r A graphic presentation of the movements of chum salmon 660-1 is provided in Appendix Figure 2-E-?6. Chum salmon,Radio Transmitter 660-2 Chum salmon 660-2 was tagged and released at Talkeetna Station (RM 103)July 30,1982.The following day,it was at RM 102.1,and the next day,fish 660-2 was further downstream at.RM 101.6. On August I,fish 660-2 had entered the Talkeetna River (RM 97.0)and was 3.4 miles upstream in the river.The fish was located next 4.2 miles upstream in the Talkeet.na River August 5.By Auqust 8,fish 660-2 had ascended -,approximately 26 miles in the Talkeetna River to within 1.8 miles of Iron Creek.Between August 8 and 18,fish 660-2 had moved downstream approximately seven miles to a point 1.5 miles above the Sheep Creek confluence.August 18 was the last date this fish was located with radio telemetry gear.It presumably 'spawned in the Talkeetna River drainage. A graphic presentation of the movements of chum salmon 660-2 is provided in--Appendix Figure 2-E-27. Chum Salmon,Radio Transmitter 670-2A Chum salmon 670-2A was tagged and released at Talkeetna Station (RM 103)July 31,1982.It ascended and was at RM 113.6 August.1 and RM 127.1 August 3. A155 lee 14e CHUM SALMON 660-1 13e Fish exited Susitna River and entered Talkeetna River b.t.ween OS42hl4AuQustand 0956 h IS August;located IS August at mouth Sheep River,RM 14.2 'Talkeetna River .UJ ..J -125~ a: >lLJ >~-t21 01 a:II e '""0)«,.~16, z ~ t-~12en.... =>"Cf)loe "s~ Talk..tna Station ,b~4 L Talk ••tna River Confluence,. 95 30 JULY 3 e 7 9 II 13 15 17 19 21 23 25 27 29 31 AUGUST 2 4 6 8 10 12 SEPTEMBER Appendix Figure 2-E-26. .J 1 ~!I ~ Movement of radio tagged chum'salmon 660-1 in the S~sitna River drainage during August,Adult ~qadromous Investigations,Su Hydro Studies,1982., ,v J I I II 1 I )I !I I J 1 1 I 1 )i i J ~-]~~ 155 CHUM SALMON 660-2 -Fish located at mouth Sheep River,RM 14.2 Talkeetna River,5 Auoust Fish deported Susltna River and entered Talkeetna River Vbetween 1410h 31 July and 2027h 1 A",oust 145 135 1JJ ...J i 125 28 a:::-!.~ >llJ E!24 >-a.-\" 01 a::::20 .....,oct 115 .~ It: z C)16 I-'=-.... C/)ll2::> CI) .... 105 ~e 95 Talkeetna River Confluence 30 JULY 3 5 7 9 II 13 1.5'17 19 21.23 Z5 27 29 31 AUGUST 2 4 6 8 10 SEPTEMBER Appendix Figure 2-E-27.Movement of radio tagged chum -salmon 660-2 in the Susitna River drainage during July and August,Adult Anadromous Investigations,Su HydroStudies, 1982. Between August 3 and 4,fish 670-2A descended to RM l18.4 t and August 5 it was located at RM 117.8.Fish 670-2A then ascended to RM 123.7 and entered Fifth of July Creek (Rt1 123.7)where it was located August 6.Later that same day,fish 670-2A exited Fifth of ~lul'y Creek and held at the confluence of the stream with the Susitna River at RM 123.7. On August 8,fish 670-2A was at the confluence of Fourth of July Creek (RM 131.1).It remained at this location through 1600 h,August 13.At 1940 h t August 13,fish 670-2A was downstream at RM 124.3.The fish and transmitter were recovered at RM 124.3 August 23.Examination of the carcass revealed that it was spent.The fish presumedly spawned at the Fourth of July Creek confluence (RM 131.1)between August 6 and 13. A graphic presentation of the movements of chum salmon 670-2A is provided in Appendix Figure 2-E-28. Chum Salmon,Radio Transmitter 670-2B Chum salmon 670-2B was tagged and released at Curry Station (RM 120)August 26,1982.Twenty-eight hours after being released it was at RM 130.3,this ~epresents an upstream migration rate of 9.4 mpd. Fish 670-2B moved downstream between August 27 and 29 to RM 117.8.Two days later it was located upstream at RM 123.8.It entered Slough 8A (RM 125.7) between September 2 and 6,where it spawned.A necropsy conducted September 13 established that it was spent. A158 """ )]J j )J )i I ..]]1 J ]~D .~~)•l J 131.1 ) Fish deported Fifth of July Creek Confluence between 6 and 8 A uoust \ \Fi.h ••••"••F••rth .f J.ly C••tI •••••(RM between 1620h and 1940h 13 Auoust . Fish detected In Fifth of July Creek at 1500h 6 Augustj later detected same day at confluence of Fifth of July Creek 95 155 145 I ~ 135...l ~~........Q~ c:'- UJ ~~ ...J ii:~ -:E 125 >-a: ~ UJ (JI >- CO a:: «115 z....-CI) :::> CI)105 CHUM SALMON 670-2A 30 JULY Appendix Figure 2-E-28. 12 SEPTEMBER Movement of radio tagged chum salmon 670-2A in the Susitna River drainage during July and August,Adult Anadromous Investigations,Su Hydro Studies, 1982. A graphic presentation of the movements of chum salmon 670-28 is provided in Appendix Figure 2-E-29. Chum salmon,Radio Transmitter 670-3 Chum salmon 670-3 was tagged and released August 22,1982 in lower Devil Canyon (RM 150A).Fish 670-3 moved downstream of RM 150.4 and entered Portage Creek (R~1 148.9)within four days.Between August 26 and September 5,fish 670-3 outmigrated from Portage Cr~ek.On September 5 it was located at RM 130.8.Fish 670-3 was subsequently at RM 123.0 September 12 and was last detected September 24 at RM92.0 A graphic presentation of the movements of chum salmon 670-3 is provided in Appendix Figure 2-E-30. Chum Salmon,Radio Transmitter 680-2 Chum salmon 680-2 was tagged and released at Curry Station (RM 120)August 2, 1982.Twenty-two'point seven hours later it was at RM 130.7 which represents an upstream migr~tion rate of approximately 11.5 mpdi Between August 3 and 4~fish 680-2 began moving downstream.On August 4,it ~was located at RM 113.2 an~aboutsiKhours later the same day,was 3.9 miles further downstream at RM 109.3. August 5,fish 680-2 was 5.9 miles upstream in the Talkeetna River(RM 97.0), and by August 8 was an additional 27.5 miles upstream in the river.Fish A160 ..- .... 1 1 ]1 J J -1 1 ) 150 \ ",\.,....,.....'.d i •••••, .condition 13 Siptemtier~,fl ••d.t••t.d I.s,....8A "om 6 to 13 Septemblr .Fish moved downstream from RM /30.3 to 117.8 ~tween leOOh 27 AU\1ust and 1655 h 29 AU\1~st CHUM SALMON 610-2B tagged chum salmon 670-28 in the Su~itna River drainage September,'Adult Anadromous Investigations,Su Hydro Appendix Figure 2-E-29. 7 9 II 13 15 17 19 21 23 25 27 29 AUGUST Movement of radio during August and Studies,1982. 31 2 4 6 8 10 12 14 16 SEPTEMBER Fish entered Portage Creek between /1315h 22 August and 1854h 26 August 95 JC---Devil Canyon Portage Creek Confluence 155 145 135 j "1LJ Fish exited Portage Creek between---- ..J 26 August and 5 September .- :E 125 >-0::: ......1LJ 0)>-I\)0::: 115« Zr-- (J) :::> (J)105 CHUM SALMON 670-3 30 I 3 5 JULY Appendix Figure 2-E-30. 'I J ~!I J 7 9 II 13 15 17 19 21 23 25 27 29 31 2 4 6 8 10 12 AUGUST SEPTEMBER Movement of radio tagged chum salmon 670-3 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982.~ III J I I))J J ~ I r r- i ..... ..... 680~2 then descended 27.5 miles and entered Chunilna (Clear)Creek sometime between August 8 and 22.On August 22 and September 14,fish 680-2 was approximately 18 miles upstream in Chunilna Creek. A graphic presentation of the movements of chum salmon 680-2 is provided in Appendix Figure 2-E-31. Chum Salmon,Radio Transmitter 700-2 Chum salmon 700-2 was tagged and released at Curry Station (RM 120)August 4, 1982.By August 6,fish 700-2 had entered and was 0.35 miles upstream in the Indian River (RM 138.6).The movement from Curry Station to Indian River represents a migration rate of approximately nine mpd . Fish 700-2 continued to ascend Indian Riijei through August 26,evident by its position 1.8,4.0, 4.5,6.2,7.5 and 10.1.miles upstream in the river, respectively August 8,11,14,18,22,and 26.On September 9 and 14,fish 700-2 was 2.6 miles downstream from its former position and presumedly was in a spawned out condition. A graphic presentation of the movements of chum salmon 700-2 is provided in Appendix Figure 2-E-32. Chum Salmon,Radio Transmitter 700-3 Churn salmon 700-3 was tagged and released in lower Devil Canyon (RM 150.4) August 22,1982.Four days later,it was in Portage Creek (RM 148.9);On A163 155 145 CHUM SALMON 680-2 Fish moved downstream Talkeetna Rlver from RM 26andjon,.".Ch.niln.(CI ••'I C,••·RM 5.9 '.'WHn 8 .n.22A.O.II • '4~FiSh departed Susltna River and entered Talkeetna River between 2000 h 4 August 0 nd 1055 h 5 August 135 w ~ -.J .... F:-\"::E125 ~r 28...a::Curry ~)10 w ~~24>Stat Ion c:...a.....-..0)a::r20~-c:{115 ~ z !--en ::::) en 105 95 JI during 1982. \ 2 4 6 SEPTEMBER Movement of radio tagged chum Sa1ITKln 680-2 in the Susitna River drainage August and September,Adult Anadromous Investigations,Su Hydro Studies, \ J J J 11 I_I .1 JJ~I) 30 JULY Appendix Figure 2-E-31. ) .~ 1 J J 1 B J -j 1 I 1 ]---1 1 -J --.11 ))) 155 145 1 I_d .._0.,.,-7~I 01,,,botw.._ Confluence Fish entered In~at935h 6 August 0914h 5 Augus1351 lLJ ...J- :!:125 a::: lLJ iE---curry»>Station-~a:::0) 115c.n ct Z....-(fl ~ en 105 95 CHUM SALMON 700-2 JULY Appendix Figure 2-E-32.Movement of radio tagged chum salmon 700-2 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. September 5,fish 700-3 was at the confluence of Indian River and the Susitna River (RM 138.6).Fish 700-3 was last located September 9 approximately one mile upstream in Indian River. A graphic presentation of the movements of chum salmon 700-3 is provided in - Appendix Figure 2-E-33. Chum Salmon,Radio Transmitter 710-2 Chum salmon 710-2 was tagged and released at Curry Station (RM 120)July 30,_ 1982.It was subsequently locat.ed at RM120.6 July 21 and August 3 at RM 147.3,which represents a travel rate of approximately seven mpd. --Indirect evi dence i ndi cates that fi sh 710-2 moved downriver and entered Indian River (RM 138.6)between August 3 and 4.Fish 710-2 was not located August 4,during a thorough search by waterbourne craft from RM 96.0 to 150.4.However,during a telemetry overflight the following day the fish was located 5.2 miles upstream in Indian River (RM 138.6).Fish 710-2 apparently entered the Indian River (RM 138.6)sometime between August 3 and 4 and occupied a position.in the stream not detectable by telemetry equipment operated from the Susitna River mainstem. An aerial survey August 8 established the position of fish 710-2,2.2 miles upstream in Indian River (RM 138.6).It was thereafter located between 1.0 and 1.6 miles upstream in Indian River from August 11 thro.ugh September 9. A166 1 I .~1 l 1 1 ) ) I ··-1 )J ~, 155 145 W .-J -125:::E »a::w->0)- a::115 ...., <tz I-- (1) :::> (1)105 If--Devil Canyon 'k--Portage Creek Confluence Indian River Confluence ~Fish exited Deyll Canyon and ascended Portage Creek between 22 and 26 Auqult / Fish departed Portage Creek and moved downstream to Indian River Confluence between 26 AUQust and 5 September .95 CHUM SALMON 700-3 30 I 3 5 JULY Appendix Figure 2-E-33. 7 9 1\13 15 17 19 2.1 AUGUST Movement of radio tagged chum salmon 700-3 in theSusitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. A graphic presentation of the movements of chum salmon 710-2 is provided in Appendix Figure 2-E-34. .... Chum Salmon.Radio Transmitter 710-3 Chum salmon 710-3 was tagged and released at Talkeetna ,Station (RM 103) August 16.1982.It moved downstream and remained at the Talkeetna River confluence (RM 97.0)from August 17 to 19. Fish 710-3 was last located four miles upstream in the Talkeetna River (RM 97.0)August 22. ·~i A graphic presentation of the movements of chum salmon 710-3 is provided in Appendix Figure 2-E-35. Chum Salmon.Radio Transmitter 720-1 Chum salmon 720-1 was tagged and released at Curry Station (RM 120)August 7, 1982.Two days after being tagged it was located 3.0 miles upstream at RM 122.5.On August 11,fish 720-1 was at RM 132.3.The fish continued moving upstream.and August 13 was detected at the mouth of Slough 17 (RM 137.9). Two hours later it was upstream at the mouth of the Indian River (RM 138.6) where it remained through August 14. - - Between August 14 and 17,fish 720-1 descended to RM 123.8.Later it moved - downstream to RM 122.0 where it remained from August 19 to 22.On August 23 fish 720-1 was detected upstream in Moose Slough (RM 123.4).Later.August A168 1 ) )1 ])1 1 1 1 ) I 1 1 .j \J >-.... 0) CD 155 145 135 I.LI ~125 ::!: c::: ILl > a::U5 «z.- (I) ::l (I)105 95 Fi8h moved downstrea m from RM 147.3 and entered Indian /River between 1510h 3 Auou8t and 1030h 5 Auoust _Curry Station CHUM SALMON 710 - 2 30 I 3 5 JULY Appendix Figure 2-E-34. 7 9 II 13 15 17 19 AUGUST Movement of radio tagged during July,August~and Hydro Studies,1982. 21 23 25 27 29 31 2 4 6 8 10 12 SEPTEMBER chum salmon 710-2 in the Susitna River drainage September,Adult Anadromous Investigations,Su 155 CHUM SALMON 710-3 145 135 )l- •..... o IJJ -I :E 125 0:: IJJ > 0:: 115 ~ Z I-:' (() ::l en 105 95 Talkeetna Station Talkeetna River Confluence ~..... ~ Q:; ~/Filh entered li \E I G between 19 a~Jk~e2tna River .-.:4 AUQult ....~2 ~, during ) SEPTEMBERAUGUST Movement of radio tagged chum salmon 710-3 in the Susitna River drainage August,Adult Anadromo"~~Investigations,Su Hydro Studies,1982. JU J J J !~i j I DJs) 30 I 3 5 7 9 II JULY Appendix Figure 2-E-35. ,·~ r .- -I [ 26 and 28 the fish was at RM 121.6 and 122.2,respectively.From August 31 to September 14,fish 720-1 was in Slo~gh Be at RM 121.9. Between September 14 and 18,fish 720-1 exited Slough Be (RM 121.9)and from September 18 through October 4 remained at RM 121.5.Fish 720-1.presumedly spawned in Slough Be between August 31 and September 14. A graphic presentation of the movements of chum salmon 720-1 is provided in Appendix Figure 2-E-36 • A171 155 ..Fish detected durIng .13 one!14 August /at confluence of 1nCllo n RIver CHUM SALMON 720-1 Fish detected at RM 123.S at 1955h 17 August / ..Fish located in Slough Se from ./31 August to 13 September .""\"" ".........""""". Fish lQ.cated in Moose Slough (RM 123.4) at 1630h 23 August 95 145 I Indian River Confluence I 135 W ...J- :E 125 a:: W»>-r Curry.....a::.....Station I\)ex:115 Z I--en ~en 7 9 II 13 Appendix Figure 2-E-36. 15 17 19 21 23 AUGUST Movement of radio during August and Studies,1982. 25 27 29 31 2 4 6 8 10 12 14 16 18 20 SEPTEMBER tagged chum salmon 720-1 in the Susitna River drainage September,Adult Anadromous Investigations,Su Hydro l l !J )J J .~;1 )J .J J ))!J t J )~ Coho Salmon,Radio Transmitter 600-1 . Coho salmon 600-1 was tagged and released at Talkeetna Station (RM 103) August 29,1982.It was last located 10.4 miles downstream August 31. A graphic presentation of the movements of coho salmon 600-1 is provi ded in Appendix Figure 2-E-37. Coho Salmon,Radio Transmitter 600-2 Coho salmon 600-2 was tagged and re1e.ased at Talkeetna Station (RM 103) August 27,1982.Sixteen and one-half hours after being released fish 600-2 __was 2.1 miles downstream at RM 100.9.It was next encountered August 31 1.9 miles upstream in the Talkeetna River (RM 97.0).Fish 600-2 continued to ascend the Talkeetna River through September 9 When it was last located 15.5 miles upstream on that date. ,....A graphic presentation of the movements of coho salmon 600-2 is provided in Appendix Figure 2-E-38. Coho Salmon,Radio Transmitter 600-3 .... .... Coho salmon 600-3 was tagged and released at C,urry Station (RM 120)August 25,1982.It moved 0.2 miles downstream within 1.0 hours after release and was located the following day at RM 121.3 and thereafter at RM 121.0.Fish 600-3,without its radio transmitter was captured 11.2 miles upstream in A173 155 145 lLJ 135 ..J-:::!: a::w >J25 a:: >eX: Z.....~-......(f)II 5.,.~ (f) 105 95 I"",Tal keetna Stat Ion 18 20 22 24 26 28 30 AUGUST 357 COHO SALMON 600-1 Appendix Figure 2-E-37.Movement of radio tagged coho salmon 600-1 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. .~\I j j I I J ))J I !.1 I §J B I 1 -J 1 J J 1 ]I i -1 i ~~~))) 155 COHO SALMON 600-2 145 135 >........, 01 LLJ ...J ::E 0:::125 LLI > a::: <t 115Z ~ en :::J Ul 105 95 To Ikeetna Stat Ion Talkeetna River Confluence "---Fish entered Talkeetna River between 28 and 31 AUQuat 18 20 Appendix Figure 22 24 26 28 30 I 3 AUGUST 2-E-3B.Movement of radio during August and Studies,1982. 5 7 9 II 13 15 17 19 21 23 25 27 SEPTEMBER tagged coho salmon 600-2 in the Susitna River drainage September,Adult Anadromous Investigations,Su Hydro Portage Creek (RM 148.8}September 24.The fish apparently regurgitated the radio transmitter September 21 or 28 at RM 121.0. Coho Salmon,Radio Transmitter 610-1 Coho salmon 610-1 was tagged at Curry Station (RM 120)August 22,1982. About 22 hours after being released it was 3.2 miles downstream at RM 116.3 August 23.It was next monitored 13.3 m'iles upstream at RM 129.6 August 26. About 24 hours later,August 27 fish 610-1 was encountered 0.6 miles upstream at RM 130.2 and had reached Slough 11 (RM 135.8)August 28.This coho salmon,while enroute to RM l35~8,ascended at an average migrational rate of 5.5 mpd. Between August 28 and 29,fish 610-1 moved downstream to,and remained at,or near Fourth of July Creek confluence{RM l31.l}from August 29 to September 7.By September 8,it had moved further downstream to RM 126.4.It then re-ascended to RM 131.1 where it was located September 9 and 10. Between September 10 and .13,fish 610-1 departed the Fourth of July Creek confluence (RM 131.1)and migrated to the mouth of Slough 15 (RM 137.3)where it was locatpd September 13. Coho salmon 610-1 was detected later September 14,upstream at the Indian River confluence (RM 138.6).Between September 14 and 18,fish 610-1 ascended Indian River {~M138.6}.Aerial surveys September 18 and 22 located the fish 2.4 miles upstream in Indian River (RM 138.6)•.The fish was last detected in the Indian River September 22,1982. A176 - -A graphic presentation of the movements of coho salmon 610-1 is provided in Appendix Figure 2-E-39. Coho Salmon,Radio Transmitter 610-3 Coho salmon 610-3 was tagged at Talkeetna Station (Rt·1103)August 28,1982. Three days later it was located 14.8 miles downstream at the Birch Creek confluence (RM 88.4).It next was detected there September 14.Despite subsequent telemetric overflights the fis~was not located again. A graphic presentation of the movements of coho salmon 610-3 is provided in Appendix Figure 2-E-40. Coho Salmon,Radio Transmitter 620-3A Coho salmon 620-3A was tagged August 26 at Talkeetna Station (RM 103).It was detected for the following two days 1.5 miles downstream at RM 101.5.On August 29,fish 620-3A descended another 0.3 miles to RM 101.2;it then ascended to RM 106.9 to the confluence of Chase Creek where it remained from August 21 to September 2.Fish 620-3A exited the confluence of Chase Creek (RM 106.6)and moved upstream to Slough 5 (RM 107.6)between September 2 and 3.It remained at this location through September 6. Sometime between September 6 and 7,coho salmon 620-3A departed Slough 5 and 1 migrated upstream to where it was located at RM 109.2 September 7.Fish.-620-3A then ascended to RM 110.9 September 9 and to 111.4 September 10 where it remained through September 14. "1 I A177 155 ~e ~e ~ '~4__~J\ Fish entered Indian Riyer between 14 and 18 SePtember ~Fish detected at Fourth of July Creek .'Confluence from 29 August to II September Curry Station Fourth of July Creek Confluence Indian Riyer Cont'luence 145 135 w ...J- ::!:.125 a: UJ>. »-a: ...Ao....,<[115 (X)z I-- (J) ::J (J) 10 95 COHO SALMON 610-1 18 20 22 24 2628 30 I AUGUST 3 5 9 II 13 15 17 19 21 23 25 27 SEPTEMBER Appendix Figure 2-E-39.Movement of radio tagged coho salmon 610-1 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. \~;/ ]J '~~cJ ,I J _ct ~1 .~~,B I .~ ~ ~1 ~-1 ]J I 1 j J 1 J ~'~))! 14 COHO SALMON 610-3 > -.I....., CO 135 W -l ~125 a::: w > a::: <t 115 z I- U) ::> U) 10 Talkeetna Station Birch Creek Confluence 18 20 22 24 26·28 30 AUGUST 3 5 7 9 I I 13 15 17 19 21 23 25 SEPTEM BER Appendix Figure 2-E-40.Movement of radio tagged coho salmon 610-3 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. September 15,fish 620-3A was located first at the confluence of Slough 5 (RM 107.6)and approximately three hours later it descended to the confluence of Chase Creek at RM 106.9.Fish 620-3A was next located September 18 at the confluence of Little Gash Creek (RM 111.4). Evidence indicates that fish 620-3A ascended Gash Creek (RM 111.6)sometime between September 18 and 21.The fish was not detected telemetrically with boat mounted equipment between RM96~0 and 122.0 September 2.However,it was detected during an aerial overflight 0.5 miles upstream in Gash Creek (RM 111.6)September 23.Fish 620-3A was observed spawning in Gash Creek September 25 and 27;the fish was captured the latter date and found to be partially spent. A graphic presentation of the movements of coho salmon 620-3A is provided in Appendix Figure 2-E-41. Coho Salmon,Radio Transmitter 630-1 Coho salmon 630-1 was tagged August 28 at Talkeetna Station (RM 103).It was detected the following day at RM 101.2,and thereafter within 0.4 miles of this location from August 31 to September 5. Indirect evidence suggests that fish 630-1 entered Whiskers Creek (RM 101.2) between September 5 and 6.Fish 630-1 was not detected telemetrically by boating round-trip from RM 96.0 to 126.0 September 6 •.However,a September 9 overflight located the fish 1.9 miles upstream in Whiskers Creek (RM 101.2). Fish 630-1 was probably in Whiskers Creek (RM 101.2)September 6 beyond the A180 ..... ------i ~-I 1 J J ......1 }JJ~.. {~)} 155 COHO SALMON 620-3 145 Fish monitored at Slough 5 Con f luence on 3,5 and 6 September \ t Little Gosh"detected a on 10,12, FISh k conflue~C:tember~..erer4 and \8 e13, --,...eo../ _..0,11011, red a live p streamF"sh recove leased tos~ent and re Slough 5 Confluence Gosh Creek Confluence Little Gosh Creek Confluence Talkeetna Station 135 UJ -'- :!:125 a::: UJ >-a::: 115octz I--en ::> en >..... Q)..... 18 20 22 24 26.28 30 I 3 5 7 9 II 13 15 17 19 21 23 25 27 29 AUGUST SEPTEMBER Appendix Figure 2-E-41.Movement of radio tagged coho salmon 620-3A in the Susitna River drainage during August and September,Adult Anadromous Investigations.Su Hydro Studies.1982.. range of boat mounted telemetry gear and therefore was not located.Fish 630-1 was repeatedly located in Whiskers Creek 1.5 and 1.9 miles upstream from September 9·through September 25 when the last aerial survey was conducted. A graphic presentation of the movements of coho salmon 630-1 is provided in Appendix Figure 2-E-42. Coho Salmon,Radio Transmitter 640-1 Coho salmon 640-1 was tagged and released August 18 at Talkeetna Station (RM 103.0).The following day the fish was monitored 4.3 miles upstream at RM 107.3.Between August 19 and 20,)fish 640-1 ascended to the confluence of Chase Creek (RM 106.9).It remained within 0.3 miles of this location through August 23. Between August 23 and 25,ftsh 640-1 exited the confluence of Chase Creek (RM 106.9)and ascended to the confluence of Lane Creek at RM 113.6.The following day,fish 640-1 was located one mile downstream at RM 112.6.It remained at this location through August 27.Fish 640-1 was last located 7.0 miles downstream at RM 105.6 August 28. A graphic presentation of the movements of coho salmon 640-1 is provided in Appendix Figure 2-E-43. A182 ,..,.,.. ~- ~...... i ~.~-==,~--J I J 1 j J }]--.~ )} COHO SALMON 630-1 ~.... ~ ~~Fish entered Whisker1t Creek ~:l /b'tw,..5 .0'9 So,tomb" .....~,._--,---..----.~----•••••r •• 155 145 135 W ...J- :!:125 0:: ILl >»-a:::....... Q)115 <t(,,)Z....-(J) ::> (J)105 Tal keetnaStation Whisker's Creek Confluence I 95 1 3 5 7 9 1\13 15 17 19 2-1 SEPTEM BER Movement of radio tagged coho salmon 630-1 in the Susitna River drainage during August and September,Adult Anadromous Investig,ations,Su Hydro Studies,1982. 18 20 22 24 26 28 30 AUGUST Appendix Figure 2-E-42. 155 145 135 lU -J ~ 125 ».... (» ~ a::w > a:: <l Z I- en :> (J)10 To Ike'tna Station I COHO SALMON 640-\ 3 5 7 9 II 13 15 17 19 21 23 25 27 SEPTEMBER Movement of radio tagged coho salmon 640-1 in the Susitna River drainage during August,Adult Anadromous Investigations,Su Hydro Studies,1982. IS 20 22 24 26 28 &> AUGUST Appendix Figure 2-E-43. )"i J ~.~I .~I •~1 I J J !j J I I f!,!i!IM, Coho Sa1mon t Radio Transmitter 640-3 Coho salmon 640-3 was tagged and released at Talkeetna Station (RM 103) August 25 t 1982.It descended to RM 98.3 approximately four hours after its release.On August 26 and 27 t fish 640-3 was in the Susitna River at the confluence of Wiggle Slough at RM 98.0.It then ascended upstream to RM 99.6 where it was located August 28. Between August 28 and 21 t fish 640-3 descended from RM 99.6 and entered the Talkeetna River (RM 97.0)where it was detected 2.2 miles upstream in the river August 31 and September 1,Fish 640-3 then descended the Talkeetna River to a point with 0.3 miles from its confluence with the Susitna River at RM 97.0. Between September 2 and 3,fish 640-:3 exited Talkeetna River (RM 97.0)and migrated upstream to the confluence of Wiggle Slough with the Susitna River at RM 98.0.Next this fish was located in the Chulitna River (Rt1 98.6) September 9.By September 13 it had returned,to.the Susitna River.Fish 640-3 advanced upstream to RM 100.9 and RM 101.2 September 14 and 18, respectively. Between September 18 and 25,fish 640-3 entered.Whiskers Creek (Rt1 101.2). It remained in Whiskers Creek through September 27,the last date of observation. A graphic presentation of the movements of coho salmon 640-3 is provided in Appendix Figure 2-E-44. A185 COHO SALMON 640-3 Fish entered Talkeetn a River between 28 and 31 August .......... l..u ~.. ~ -=4.... ~~2 1..--- "-Fish exited Chulitna River between 9 and 13 September Fish en tered Chulit no River between 5 andIOS.PI ...bo, ••__--le..-------l'\ Fish entered Whisker's Creek between 18 ondZ5 September ~ l Q:: l:) t::....::::4::. (32 \ .!! "'E: ~ Whi~ker'8 Stough Confluence Talkeetna Station 135 lJ.l ...J-:.:E a::125 iLl >-a: <t Z....-(f) :::> (f) ...A. CD 0). » Fish departed Tal.eerna River and occupied Whi~k.r s Slaugh 18 20 22 24 26 28 30 I 3 5 7 9 \I 13.15 17 19 21 AUGUST SEPTEMBER Appendix Figu r e2-E-44.Movement of radio tagged coho salmon 640-3 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. I )J .B a J J J )}J ,J J J ~ ) J -' - l Coho Salmon,Radio Transmitter 650-1 Coho salmon 650-1 was tagged August 17,1982 at Talkeetna Station (RM 103). On August 18 and 19,fish 650-1 was detected downstream of RM 103 at RM 99.5 and 99.2 respectively.Fish 650-1 then descended an additional 1.2 miles to the confluence of Wiggle Slough (RM 98.0)where it remained at or near the position from August 21 through 27. Fish 650-1 was next monitored 1.4 miles downstream at RM 96.6 August 31 and then later September 9,was located 1.8 miles upstream in Whiskers Creek (RM 101.2).From September 9 through September 18,fish 650-1 occupied various locations between 1.8 and 2.5 miles upstream in Whiskers Creek.This fish was last detected September 18,2.5 miles upstream in Whiskers Creek. A graphic presentation of the movements of coho salmon 650-1 is provided in Appendix Figure 2-E-45. Coho Salmon,Radio Transmitter 650-4 Coho salmon 650-4 was tagged at Curry Station (RM 120)August 19,1982.The fish was encountered 7.7 miles downstream at RM 112.8 about 8.4 hours after being released.It was next located August ?O an additional 12.3 miles downstream at RM 100.5.On August 21,fish 650-4 was located at RM 101.4. It then descended and remained at the Talkeetna River confluence (RM 97.0) from August 22 through 23. A187 1~5 COHO SALMON 650-1 ~Fish moved upstream SusUna River and entered Whisker's Cruk between 31 August and 9 September 140 135 w ...J-~12~ a:: »1LI >.....-II~~~Q)a::.... Q)~ oCtz l- en ~en 105 _ -Ta"lkeetna Station _Whisker',Creek Confluence ~,:11!~~eh r 85 18 20 22 24 26 28 30 AUGUST 3 5 7 9 "13 15 SEPTEMBER 19 21 Appendix Figure 2-£-45.Movement of radio tagged coho salmon 650-1 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. \)) J-J J J J I J !__J m J J J j I J J J J ] Between August 23 and 26,fish 650-3 entered the Talkeetna River (RM 97.0). On August 26 it was located 3.2 miles upstream in the Talkeetna River where it remained within 0.1 miles from August 31 throug~September 5.Fish 650-3 was last monitored September 9,6.0 miles upstream in the Talkeetna River (RM 97.0). A graphic presentation of the movements of coho salmon 650-3 is provided in Appendix Figure 2-E-46. -Coho Salmon,Radio Transmitter 660-3 Coho salmon 660-3 was tagged and released at Curry Station (RM 120)August -25,1982.Fish 660-3 descended to RM 118.9,118.0 and 117.8 one,19.2 and 23.7 hours after being released,respectively. By August 27,fish 660-3 had ascended to RM 122.3.It was next encountered upstream at RM 130.8, 135.8,138.9 on August 28,29 and 30,respectively. r1aximum (upstream)migrational rates displayed by fish 660-3 from August 27 to 30,were 18.2 mpd and 8.6 mpd respectively for an interval less than and greater than 4.0 hours.Between August 30 and September 3,fish 660-3 descended to,and remained in,Slough 15 (RM 137.3)through September 8. By September 9,coho salmon 660-3 had departed Slough 15(RM 137.3)and was 1.0 miles upstream in Indian River (RM 138.6).The following day fish 660-3 :1 was 0.5 miles further upstream in Indian River. 1 A189 I~ COHO SALMON 650-3 145 >-.... tDo UJ ..J :E a::: LLI> a::: «zr (I) => (I) III..... ".. Talkeetna·~I R.Conf luence Fish entered Talkeetna River between /"'00 23 A•••"and 19270 26 A••••I 18 20 22 24 26 28 30 I 3 5 7 9 II 13 15 17 19 21 AUGUST SEPTEMBER Appendix Figure 2-E-46.Movement of radio tagged coho salmon 650-3 in the Susitna River drainage during August and September~Adult Anadromous Investigations~Su Hydro Studi es,1982. \-)J ~).~)I I J I I ])I ~J I Sometime between September 10 and 13,fish 660-3 exited Indian River (RM 138.6)and descended to RM 128.9.On September 14 the fish/carcass moved downstream from RM 103.0 to RM 94.5 in 1.7 hours.Fish 660-3 was not encountered thereafter despite several tel emetry overfl i ghts extendi ng to the confluence of Montana Creek (RM 77.0). The movement out of the Indian River {RM 138.6}and relatively rapid downstream movement in the Susitna River indicates that fish 660-3 spawned in Indian (RM 138.6)sometime prior to September 13. A graphic presentation of the movements of coho salmon 660-3 is provided in Appendix Figure 2-E-47. Coho Salmon,Radio Transmitter 680-3 Coho salmon 680-3 was tagged at Talkeetna Station (RM 103)August 28.1982. Three days later it was detected at 2.9 miles upstream in the Talkeetna River (RM 97.0).Fish 680-3 was next encountered at Birch Creek Slough (RM 88.4) September 14.Aerial overflights September 18 and 25 established the fish at the same location.Fish 680-3 was last encountered October 4,0.7 miles downstream at RM87.7. A graphic presentation of the movements of cohQ salmon 680-3 is provided in Appendix Figure 2-E-48. A191 155 _Filh exited Indian River between 10 and 13 September Filh departed Slough 15 and entered Indian River between 1030h 8 September and 1030h 9 September / Filh detected at Slough 15 Con f I uence-'3,5 a n-d B . September . 145 J Indian River Confluence .Slough I~Confluence 1'35 ILl ...J-~ 0::125 UJ >~Curry Station-»0::.. CO «115 N Z t--(J) ~ (I)105 9~ COHO SALMON 660-3 5 7 9 "13 15 17 19 21 23 25 SEPTEMBER tagged coho salmon 660-3 in the Susitna River drainage September,Adult Anadromous Investigations,Su Hydro 18 20 22 24 26 28 30 1 3 AUGUST Appendix Figure 2-E-47.Movement of radio during August and Studies~1982., J j J I ~.~l J ~.!J ,!~J ~..~ , )l --------=t ) --1 ) ]i 1 ,1 9 155 COHO SALMON 680-3 145 Fish departed Talke.tna River and entered Birch Creek Slough between 31 August and /14 Se.lem 'e, Fish entered Talks.tno River /,e,.een2.and 31 AUO'" 135 IIJ ..J-~125 0::: w >>-......0::: 115CO«(A)z.--(/) :::> C/)105 Ta Ikeetna Station Talkeetna River 951 Confluence Birch Creek Slough Confluence 27 Appendix Figure 2-E-48.Movement of radio tagged coho salmon 680-3 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. - Coho Salmon,Radio Transmitter 700-1 Coho salmon 700-1 was tagged and released at Curry Station (RM 120)August _ 17,1982.Sixteen hours'following release it was encourlter'ed 1.8 miles upstream at RM 121.3.Fish 700-1 continued migrating upstream and was at the Indian River confluence (RM 138.6)August 21.It remained there through the fo 11 owi ng day.Enroute to the Indian River (RM 138.6)fish 700-1 moved,\ upstream·at varying speeds.The (upstream)migrational rates between consecutive telemetric pos'itions less than and greater than five hours were 11.5 mpd and 7.4 mpd,respectively. ."-,,- The relatively rapid down~tream movement of coho salmon 700-1 from Portage Creek at RM 148.8 to RM 111.5 indicates that the fish probably spawned in Portage Creek prior to September 15. A graphicpre~~ntation of the movements of coho salmon 700-1 is provided in Appendix Figure 2-E-49. Coho Salmon,Radio Transmitter 710-2 Coho salmon 710-2 was tagged at Talkeetna Station (RM 103)August 19,1982. A194 ~. ,~ :J ----J ~~~\\~---,~-j I )...))J )f ]j~ ))) Fish exited.Portage Creek between 1040h/14 S....m..'.nd ,.200 .5 S.•t.mb.,\FiSh entered ~rtaoe Creek between 1835h 26 August and 1230h 29 August "FiSh monitored at Indian River Confluence Portoge Creek Confluence ""'\(~Curry Station 155 145 135 1LI ...J-~125 lr UJ >-»0: .....ct· CD z (JI l- 00 ~ 00 95 COHO SALMON 700-1 ra to 2"2 24 2""6 28 30 AUGUST Appendix Figure 2-E-49.Movement of radio tagged coho salmon 700-1 in the Susitna River drainage during August and September,Adult Anadromous Investigations,Su Hydro Studies,1982. A week later it was·last detected at 4.5 miles upstream in the Talkeetna River (RM 97.0)~Numerous aerial flights of the Talkeetna River drainage did not detect this fish after August 26. A graphic presentation of the movements of coho salmon 710-2 is provided in Appendix Figure 2-E-50. Coho Salmon,Radio Transmitter 720-2 Coho salmon 720-2 was tagged August 21,1983 at Talkeetna Station (RM 103). About 21 hours after being released.the fish was encountered 6.0 miles downstream at the Talkeetna River confluence (RM 97.0). Fish 720~2 ascended the Talkeetna River (RM 97.0)between AIJgust 22 and 26. It was next monitored 3.1 miles upstream in the Talkeetna River (RM 97.0) August 26;fi ve days 1ater it was detected 2.2.mil es downstream from its former position.Aerial overflights established the fish at 1.6,1.9 and 2.5 miles upstream in the Talkeetna River September 1,5,and 9,respectively. Fish 720-2 was c?nsist~ntly encountered 2.5 miles upstream in the Talkeetna River (RM 97.0)during aerial overflights September 10,14,18 and 25. A graphic presentation of the movements of coho salmon 720-2 is provided in Appendix Figure 2-E-51. A196 ~, - - I 1 ]----J ~---------J -----i ------j ~-1 ))1 ))1 J, ))} 155 COHO SALMON 7[0-2 145 135 )It..... co...., ILl ..J :E 125 a:::: ILl > a:::: ex:z ~ (f) ::::>en •::: ~ Cl: Talkee1na River COnfluence Fish entered Talkee1na River /be1ween 190nd 26 Augus1 IS 11 19 21 SEPTEMBER Movement of radio tagged coho salmon 710-2 in the Susitna River drainage during August!Adult Anadromous Investigations!Su Hydro Studies!1982. W~Ma~~1 AUGUST Appendix Figure 2-E-50. --~--._-~...".--....-lr 155 COHO SALMON 720-2 /45 135 UJ ...J- :E /25 a::: UJ >.... 0:: /15»c:r.....zCDI--en en ::> en 10: ~... ll! Q£ tl 8 Fish entered Talkeetna River :r.Ik••,..~~b".".22 ••d 2.A.O'" S,.tI••\•~4a • • Talkeetna "•••• River Confluence II 13 /5 17 SEPTEMBER Movement of radio tagged coho salmon 720-2 in the Susitna River drainage during August,Adult Anadromous Investigations,Su Hydro Studies,1982. 18 20 22 24 26 28 30 AUGUST Appendix Figure 2-E-51. )~\ J ] .~j :t i J J ~J •• j I ,j J I ~~ APPENDIX 2-F MAINSTEM SPAWNING SURVEYS 1.ELECTROSHOCKING SUMMARY 2.VISUAL AND GILL NET SUMMARY 3.EVALUATION OF TAG LOSS \ ~D 1 ___cc-:)---'--1 ~-~J ]1 1 j J J J J ]\ )), ApP2ndix Table 2-F-1.E1 ectroshocki ng summary of mainstem Sus itna Ri ver.Adult Anadromous Inves tigati ons. Su Hydro Studies.1982. --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M 0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK -SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 7.2 S15N07W28ADA 820907 50 0 0 0 0 0 0 ------- 7.5 S15N07W27AAC 820907 100 0 0 0 0 0 0 ------ 7.6 S15N07W27 AAB 820803 20 0 0 2 0 0 0 ------ 9.5 S15N07W07 CDC 820828 40 0 0 0 0 0 0 ------- 9.8 S15N07W10DDB 820824 60 0 0 0 0 0 0 ------- 9.9 S15N07W07 ABB 820809 60 0 0 0 0 1 0 ------- 12.7 S15N07W12BBC 820824 150 0 0 0 0 0 0 ------- 13 .0 S16N07W32CDC 820829 50 0 0 0 0 0 0 ------- )I-13 .1 S15N07W01CDC 820824 25 0 0 0 0 0 0 ---------13.3 S15N07W01CBD 820824 50 0 0 0 0 0 0 -------«>13 .5 SlSN07W01BBC 820803 150 0 1 1 0 0 0CD ------- 13_.5 S15N07W01BBC 820824 30 0 0 0 0 0 1 -------- 13.7 SlSN07W01CBA 820912 100 0 0 0 0 0 1 ------- 14.5 SlflN07W35DDC 820907 --20 0 0 0 0 0 0 ------- 14.8 S16N07W35cAC 820907 30 0 0 0 0 0 0 ------- 14.9 S16N07W35BDD 820912 200 0 0 0 0 0 0 ------ 15.5 S16N07W28DDD 820809 20 0 0 0 0 0 0 ------- 15.7 S16N07W27BCC 820912 50 0 0 0 0 0 0 _._----- 16.1 S16N07W22CCD 820912 70 0 0 0 0 0 0 ------- 16.9 S16N07W22BCC 820829 30 0 0 0 0 0 0 ------- 17.0 S16N07W22ADA 820907 150 0 0 0 0 0 0 ------- 17.1 S16N07W21AAD 820912 150 0 0 0 0 0 0 ------- 17.7 S16N07W14CCC 820907 50 0 0 0 0 0 0 ------- 17 .7 S16N07Wi5DCD 820818 50 0 0 0 0 0 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. ---------------------------------------------------~---------------------------------------~-------------------"CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)·CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------~------ 17 .7 S16N07W22AAB 820803 ., 100 0 0 0 ·0 0 0 ------- 17.9 S16N07W22BCD 820809 100 0 0 .0 0 0 -o -------- 19.0 S16N07W16DAD .820907 ··..400 -0 0 0 0 0 3 ------- 19.0 S16N07W16DAD 820912 300 0 0 0 0 0 0 ------- 20.0 S16N07W16AAA 820818 50 0 0 0 '0 0 0 ------- 20.4 S16N07W05DCD •820803 200 0 0 2 0 0 0 ------- »20.7 S16N07W08DAC ,820829 80 0 0 0 0 0 1 ------- I'\)21.4 S16N07W09ACA '820907 150 0 0 0 0 0 5 ------- 0 21.5 S16N07W08ABB 820912 150 0 0 0 0 0 0 ----- 0 22.1 S16N07W04CAB 820907 100 0 0 0 O·0 0 ------- 22.4 S17N07W33DCB 820818 50 0 0 0 0 1 0 ------- 22.7 S17N07W32DDA 820912 200 0 ·0 0 0 0 0 ------ 22.8 S17N07W32DAD 820824 350 0 0 0 0 0 0 ------ 23.5 S17N07W33BBB 820829 300 0 0 0 0 0 0 ------- 23.8 S17N07W28CCC 820912 150 0 0 0 0 0 0 ------ 23.8 S17N07W29DDA 820818 75 0 0 0 0 0 0 ------- 23.8 S17N07W29DDC 820809 20 0 0 1 0 2 0 ------- 23.8 S17N07W29DDC 820818 20 0 0 0 0 0 0 ------- 23.8 S17N07W29DDD 820829 60 0 0 0 0 0 0 ------ 23 .9 S17N07W29DDC 820809 150 0 0 0 0 1 0 ------ 23.9 S17N07W29DDD 820802 300 0 5 25 0 7 0 ------ 24.1 Sl1N07W28CBC 820912 30 0 0 0 0 0 0 ------ 24.8 S17N07W27BCB 820818 250 0 0 0 1 1 0 ------- 24.9 S17N07W27BAC 820826 100 0 0 0 0 0 0 ------- --------------------------------------------------------------------------------------------------------------- '~.~\l m I J J I )~.~I ~J ~II .~1 J ,J 1.~ ~I ) .~~1 J '::::-1 ~~-l ]--1 ]J J 1 1 ) / Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YD5)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------~------------------------------------------------------ 24.9 517 N07 W27 BBD 820906 -150 0 0 0 0 0 2 ------- 25.0 S17N07W27BBA 820818 80 0 0 0 0 0 0 ------- 25.0 S17N07 W27 BBA 820824 200 0 0 0 0 0 4 ------- 25.0 -S17N07W27BBB 820906 150 0 0 0 0 0 0 ------- 25.1 S17N07W22CCA 820826 200 0 0 0 0 0 0 ------- 25.1 -S17N07W22CCA 820912 60 0 0 0 0 0 0 ------- >25.3 S17N07W22CDA 820906 50 0 0 0 0 0 3 ------- N 25.4 S17N07W22CAD 820826 40 0 0 0 0 0 0 ------- 0 25.4 S17N07W22CDA 820906 -20 0 0 0 0 0 0 --_._---....26.1 S17N07W23BCB 820826 20 0 0 0 0 0 0 ------- 26.9 S17N07W23AAC 820818 200 0 0 0 0 0 0 ------- 26.9 S17N07W23ADB 820803 20 0 2 --__0 0 0 0 ------- 27.0 S17N07W23AAC 820826 100 -0 <r 0 0 0 0 --------.- _27.1 _S17N07W14DCC 820909 100 0 0 0 0 0 1 ------- 27.2 S17N07W14DCC 820826 100 0 0 0 ()0 1 ------- 27.7 S17N07W13DCB 820818 50 0 0 0 0 0 0 ------- 27.8 S17N07W13DBC 820818 20 0 0 0 0 0 0 ------- 27.8 S17N07W13DCC 820804 -150 0 0 2 0 6 0 ------- 28.0 S17N07W13CBB 820826 20 0 0 0 0 0 0 ------- 28.1 S17N05W13BDA 820826 75 0 0 0 0 0 0 ------- 28.3 S17N07W13ABC 820826 75 0 0 Oc 0 0 0 ------- 28.5 S19N07W13ACA 820904 40 0 0 0 0 0 0 ------- 29.0 S17N06W18BBD 820804 200 0 0 1 0 1 0 ------ 29.1 S17N06W07CCC 820904 200 0 0 0 0 0 4 ------- --------------~------------------------------------------------------------------------------------------------ Appendix Table 2-F-1.Conti nued. ------------------------------------------------------------~-----~---------------------------------------~----CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE bATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------~------------------------------------------ 29.2 S17N06W07CDD 820804 20 0 0 0 ()4 0 ------- 29.2 S17N06W18BAB·820904 20 .0 0 0 0 0 0 --.-'-- 29.3 S17N06W07CDC 820904 75 0 0 0 0 0 0 ------ 29.5 S17N06W07DCD·820804 250 0 0 1 0 2 0 ------- 29.7 S17.N06W07DCA 820904 50 0 0 0 0 0 1 ----~-- 30.3 S17N06W08BCD 820819 100 0 0 0 0 0 0 '------- 30.3 S17N06W08BCD 820904 50 0 0 0 0 0 1 ------ >31.0 S17N06W05CAB 820825 100 0 0 0 O.0 0 ----- N 31.0 S17 N06WO 5CAC 820825 50 0 0 0 0 0 0 ------ 0 31.0 S17N06W08AAB 820904 200 0 0 0 0 0 0 ------N 31.1 S17N06W05CAB 820817 150 0 0 0 0 1 0 ------- 31.1 S17N06W05CAB 820822 250 0 0 0 0 0 2 ------ 31.1 S17N06W05CAB 820825 200 0 O.0 0 1 1 ----- 31.1 S17N06W05CAB 820826 250 0 O·0 0 0 3 ------ 31.1 S17N06W05CAB 820905 150 0 0 0 1 0 12 ---- 31.1 S17N06W05CBA 820804 150 0 0 30 0 10 0 ------- 31.1 .S17N06W05CBA 820913 50 0 0 0 0 0 4 ---- 31.2 S17N06W05CAB 820905 50 0 0 0 ()0 4 ------- 31.2 S18N07W36CBB 820722 400 0 0 3 0 6 0 ----- 31.3 S17N06W05ACB 820905 20 0 0 0 0 0 0 ---- 31.3 S17N06WOSBDD 820913 20 0 0 0 0 0 ;0 ------ 31.4 S17N06W05DDA 820909 20 0 0 0 0 0 .0 ---- 31.5 S17N06W05ACD 820817 60 0 0 0 0 0 0 ------ 31.5 S17N06W05ACD 820909 50 0 0 0 0 0 2 ----- --------------------------------------------------------------------------------------------------------------- ))..~ J j J t ~1 I J ,J J .1 )J ~]1 .) ~~-J 1 j t )1 j 1 1 j 1 )), J Appendix Table 2-F-l.Continued. -----~-----------------------------.-------------------------------------------------------~--------------CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED --------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK.CHUM COHO CISCO OBSERVED --------------------------------------------------~------------------------------------------------------------ 31.6 S17N06W05ACD 820825 20 0 0 0 0 0 0 ------- 31.7 S17N06W04CAC 820904 25 0 0 0 0 0 0 ------- 31.7 S17N06W05ADB 820909 30 ->0 0 0 0 0 0 ------- 31.8 S17N06W04CAA 820727 400 0 0 150 0 0 0 ------- 31.8 S17 N06 W04CAB 820808 50 0 0 1 0 0 0 ------- 31.8 S17N06 W04CAB 820819 300 0 0 0 4 3 0 ------- >31.8 S17N06W04CAB 820825 200 0 0 0 1 0 0 ------- N 31.8 S17N06W04CAB 820904 75 0 0 0 0 0 0 ------- 0 31.9 S17N06W04DBB 820825 150 0 0 0 0 0 0 ------- CA)31.9 S18N06W32DCA 820817 150 0 0 0 0 0 0 ------- 32.2 S17N06W32DDA 820822 30 ·0 0 0 0 0 0 ------- 32.2 S18N06 W3 2DAC 820913 30 0 0 0 0 0 0 ------- 32.2 S18N06W32DCA 820905 100 0 0 0 0 0 0 ------- 32.3 S18N06W32DDA 820905 20 0 0 0 0 0 0 ------ 32.6 S18N06W33DCD 820819 100 0 0 0 0 1 0 ------- 32.7 S18N06W32BDD 820901 75 0 0 0 0 0 0 ------- 32.7 SI8N06W33DCD 820904 75 0 0 0 0 0 0 ------- 32.8 S18N06W33BBC 820913 60 0 0 0 0 0 1 ------- 32.8 S18N06W33DCA 820819 25 0 0 0 0 0 0 ------- 33.0 S18N06W33BCA 820819 20 0 0 0 0 0 0 ------- 33.1 S18N06W33ACA 820909 150 0 0 0 0 0 3 ------- 33.2 S18N06W33ABB 820819 30 0 0 0 0 0 0 ------- 33.2 S18N06 W3 3ABC 821004 200 0 0 0 0 0 1 ------- 33.5 S18N06W33ABB 820905 150 0 0 0 1 0 1 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. -----------~------------------------------------------------------------~--------------------------------------CAT C H ----------------------------------------------~--DISTANCE A D U L T S A LM 0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CI5GO OBSERVED -----------------------------------~--------------~--------------------------~----------~--~-------------------. 33.6 S18N06W28CAC 821004 150 0 0 0 0 O'2 ------- 33.7 .S18N06W28CDC 820825 150 0 0 0 0 0 0 ------- 33.8 S18N06W28CDC 820819 30 0 0 1 0 0 0 ------- 33.8 S18N06W28CDC 820822 80 0 0 0 0 0 1 ------- 33.9 S18N06W28CCD 820804 20 0 0 2 0 0 0 ------- 34.0 S18N06W28BDA 821004 300 0 0 0 0 0 15 ------- >34.0 S18N06W28CDA 820825 75 0 0 0 0 0 0 ------- N 34.1 S18N06W28BAD 821006 100 0 0 0 0 0 1 ------- 0 34.2 S18N06W28BDD 820819 50 0 0 0 0 1 0 ------- -I:l-34.2 S18N06W28BDD 820909 70 0 0 0 0 0 2 ------- 34.5 S18N06W28DBB 820819 30 0 0 0 0 0 0 ------- 34.9 S18N06W20DDA 820804 100 0 0 1 0 0 0 _._----- 34.9 SI8N06W28ABC 820819 30 0 0 0 0 1 0 ------- 35.0 S18N06W22CBC 820904 250 0 0 0 0 O.0 ------- 35.0 S18N06W27BCB 820805 100 0 0 0 1 1 0 ------- 35.1 S18N06 W21DBB 820822 150 0 0 0 0 0 0 ------ 35.1 S18N06W28ABC 820805 400 0 0 0 0 3 0 ------ 35.2 S18N07W13DBA 820722 600 0 0 0 0 0 0 ------- 35.3 S18N06W21CBD 820904 50 0 0 0 0 0 0 ------ 35.3 S18N06W21DCB 820904 175 0 0 0 0 0 2 ------- 35.3 S18N06W22DCC 820805 20 0 0 0 0 0 0 ------ 35.4 S18N06W20ADA 820804 200 0 0 2 0 3 0 ------ 35.4 S18N06W21CBA 820913 200 0 0 0 0 0 0 ------- 35.4 S18N06W31CBA 820909 150 0 0 0 0 0 0 ------ ------------------------------------------~---------------------------------------------------------------- )) J ~)J J .I j j I ..~R .1 J ~I J I f ,J --~1 1 ]J J 1 j I 1 I)J I J Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED -------------------------------------------------~---------------------------------~-------------------------- 35.5 S18N06W21BCB 820822 200 0 0 0 0 0 0 ------- 35.5 S18N06w21DBA 820805 300 0 0 1 1 4 0 ------- 35.7 S18N06W21ADB 820904 200 0 0 0 0 1 3 ------- 36.0 S18N06w22BBB 820_819 50 0 0 0 1 0 0 ------- 36.1 S18N06W22BBB 820805 30 0 0 1 1 0 0 ------- 36.1 S18N06W22BBB 820821 60 0 0 0 0 0 0 ------- 36.1 S18N06w22BBB 820904 150 0 0 0 0 1 1 ------- 36.2 S18N06W16CDA 820909 100 0 0 0 0 0 0 ------- »36.3 S18N06W16BBG 820722 500 0 0 0 0 0 0 ------- I\)36.5 S18N06W15CBA 820805 75 0 0 1 2 3 0 ------- 0 36.5 S18N06 W15CBC 820901 100 0 0 0 0 0 0 ------- 01 36.8 S18N06W09CDA 820722 150 0 0 0 0 0 0 ------- 37.0 S18Nlr6W15BBA 820909 100 0 0 -0 0 0 0 ------- 37.1 S18N06W15BAB 820821 40 Q 0 0 1 0 1 ------- 37.2 S18N06 W11AAB 820804 100 0 0 4 0 0 0 ------- 37.5 S18N06W10DBD 820821 20 0 0 0 0 0 0 ------- 37.6 S18N06W10DDC 820905 100 0 0 0 0 0 0 ------- 37.8 S19N06W10DAB 820908 30 0 0 0 0 0 0 ------- 38.1 S18N06W10ADD 820722 350 0 0 0 0 0 0 ------- 38.2 S18N06WllBDC 820821 30 0 0 0 0 1 0 ------- 38.3 S18N06Q11CBD 820905 100 0 0 0 0 0 2 ------- 38.3 S18N06W03DCB 820804 30 0 0 0 0 0 0 ------- 38.3 S18N06WI1BDC 820722 200 0 3 50 0 5 0 ------- 38.4 S18N06 WO 3DDB 820804 50 0 0 0 0 0 0 ------- ----------------------------------~---------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. -----------------------------------------~----------------------~-----------------------------------------.-~-CAT C R ------------------------------------------------- DI'STANCE A D U L T SAL M 0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (Y1>5)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 38.4 S18N06 W11BDC 820805 too 0 0 2 2 5 0 ----.- 38.5.S18N06W09DBD 820722 600 0 0 0 0 0 0 ------- 39.0 S18B06 W11AAB 820722 500 0 0 0 0 0 0 ------- 39.0 S18N06W11AAB 820727 200 0 ·0.25 0 0 0 ------ 39.0 S18N06 W11AAB 820805 300 0 0 10 0 0 o .------- 39.1 S18N06W02DCA 820905 100 0 0 0 0 0 2 ------- »39.2 S18N06W02DCB 820806 250 0 0 0 0 1 0 ------- I\)39.3 S18N06W02DBA 820905 50 0 0 0 0 0 0 ------- 0 39.3 S18N06W02DBD 820905 200 0 0 0 0 0 5 -------0)39.4 S18N06W02DAC 820821 120 0 0 0 0 1 0 -----...- 40.0 S18N06W02AB 820722 1000 0 2 5 0 0 0 ------_. 40.0 S19N06W35DBB 820905 200 0 0 0 0 0 O'------- 40.1 S18N06W02AAB 820822 300 0 0 0 0 0 0 ------ 40.5 S19N06W35DAB 821005 200 0 0 0 0 0 1 ------ 40.6 S19N06W11CCB 820728 900 0 0 0 0 1 0 ------ 40.6 S19N06W35BDA 820722 500 0 5 20 0 5 0 ------ 40.6 S19N06W35BDA 820728 600 O'0 30 0 6 0 ----- 41.1 S19N06W26DBA 820905 0 ..0 0 0 0 0 ----- 41.2 S19N06 W35AAD 820905 200 0 0 0 0 1 4 ------ 42.1 S19N06W25ABC 820905 150 0 0 0 0 0 1 ------ 42.5 S19N06W25ABB 820806 300 0 0 3 6 12 0 ---- 42.5 S19N06W25ABB 820822 60 0 0 0 1 0 0 ---- 42.6 S19N06W25ABB 820821 85 0 0 0 0 1 0 ------ 43.0 S19N06W24CAA 820908 75 .0 0 0 0 0 0 ----- --------------------------------------------------------------------------------------------------------------- ,.~ J !j m m ~)J J 1 J J !~~~).~ Appendix Table 2-F-1.Continued. -~1-j ) 1 1-..)1 J -1 ) ------------------------------------------------------------------------------------------------------------ CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 43.2 S19N06W24DDA 820821 30 0 0 0 0 0 0 ------- 43.2 S19N06W24DDA 820911 300 0 0 0 0 0 0 ------- 43.4 S19N06W24BAD 820806 120 0 0 0 0 0 0 ------- 43.4 S19N06W24BCA 820908 20 0 0 0 0 0 0 ------ 43.5 S18N05W20CAC 820923 150 0 0 0 0 0 0 ------- 43.5 S19N05W19CCA 820821 15 0 0 0 0 0 1 ------- 43.5 S19N05W19CDC 820805 300 0 0 1 0 2 0 -------)I-43.5 S19N06W24BAD 820822 90 0 0 0 0 0 0 -------f\)43.5 S19N06W24BDB 820908 60 0 0 0 0 0 00 ------- .....,43.6 S19N06W24BAC 820908 100 0 0 0 0 0 0 ------- 43.7 S19N05W19DBA 820821 500 0 0 0 0 0 0 ------- 43.9 S19N06W19CAC 820911 150 0 0 0 0 0 0 ------- 44.0 S19N05W13DCB 820908 -30 0 0 0 0 0 0 ------- 44.0 S19N06W19DBA 820911 100 0 0 0 0 0 0 ------- 44.2 S19N05W20DBC 820805 300 0 0 4 2 4 0 ------- 44.3 S19N06W20DBB 820911 100 0 0 0 0 0 0 ------- 44.4 S19N05W19ABA 820901 70 0 0 0 0 0 0 ------- 44.5 S19N05W09DDC 820821 150 0 0 0 0 0 0 ------- 44.5 S19N06W13ACB 820822 90 0 0 0 0 0 0 ------- 44.7 S19N05W20ADB 820923 200 0 0 0 0 0 0 ------- 44.8 S19N05W21BDC 820727 325 0 1 2 0 0 0 ------- 44.8 S19N06W12DBC 820806 100 0 0 0 2 0 0 ------- 45.0 S19N05W12DBD 820908 40 0 0 0 0 0 0 ------- 45.0 S19N05W21BCB 820831 50 0 0 0 0 0 0 ------- ---------------------.----------------------------------------------------------------------------------------- Appendix Table 2-F-1.Continued. --------------------------------------~----------------------------------------------~---------------~---------CAT C H --------------------~----------------------------DISTANCE A D U L T SAL }of 0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 45.0 S19N06W12DAC 820822 ·250 0 0 0 3 .1 0 ----- 45.2 S19NQ5W17DDD 820805 200 0 0 0 2 0 0 --,.,----- 45.3 S19N05W20ADC 820831 100 0 6 1 0 0 0 --~----. 45.4 S19N05W12DAA 820908 100 0 0 0 0 0 3 ------- 45.5 S19N05Wl2ADD 820908 60 0 0 0 1 0 0 ------- 45.5 S19N06W12DBD 820808 40 0 0 0 0 1 0 ------ 45.7 S19N05W17DAD 820831 100 0 0 0 0 0 1 ------- )I-45.8 Si9N05W07BAB 820908 100 0 0 0 0 0 1 -------'"45.8·S19NO 5W17 BAB 820901 30 0 0 0 0 0 0 ------0 OJ 45.8 S19N06WOIDDD 820806 75 0 0 0 0 0 0 ------- 45.8 S19N06W01DDD 820808 75 0 0 0 0 23 0 ------- 46.0 S19N05W04DDB 820821 20 0 0 0 0 0 0 ------ 46.1 S19N05W16ACD 820911 20 0 0 0 0 0 0 ------ 46 .2 S19N05W16ACB 820911 20 0 0 0 0 0 0 ------ 46 .3 S19N05W16BCA 820805 30 0 0 2 0 0 0 ------ 46 .3 S20N05W32ABA 820908 30 0 0 0 0 0 0 ------- 46 .5 S19N05W06CAB 820808 250 0 0 0 1 5 0 ------- 46 .6 S19N05W07BAC 821005 200 0 0 0 0 0 4 ----- 46 .8 S19N05W09DAB 820911 50 0 0 0 0 0 0 ----- 46.9 S19N05W03BCB 820831 100 0 0 0 0 0 0 ------ 47.0 S19N05W06ADB 820808 25 0 0 0 2 1 0 ------- 47.1 S19N05W04DDB 820911 40.0 0 0 0 0 0 ------- 47.1 S19N05W06ABC 820908 50 0 0 0 0 0 0 ------ 47.3 S19N05W05DAA 820901 30 0 0 0 0 0 0 ----- --------------------------------------------------------------------------------------------------------------- l \ i ~j I ~J J .~)J .,]J J J J 1 J J j CCJ -)--------J '--=-I "-~~~1 1 J -~1 1• )) Appendix Table 2-F-l.Continued. -----------~---~-----------------------------------------------------------------------------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE .DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 47.4 S19N06W06ABA 820806 20 0 0 0 0 0 0 ------- 47.5 S19N05w04DDB 820805 100 0 0 1 1 0 0 ------- 47.7 S19N05W05BBA 820822 75 0 0 0 0 0 0 ------- 47.8 S20N05W32CCC 820808 100 0 0 0 0 2 0 ------- 47.9 S20N05W32CCA 820908 300 0 0 0 1 0 1 ------- 48.2 S20N05W32BCA 820828 60 0 0 0 0 0 0 ------- 48.3 S20N05W32BAD 820822 100 0 0 0 3 0 0 ------ »48.5 S20N05W34CCD 820806 50 0 0 0 0 0 0 ------ I\)48.7 S2ONO 5W3 2ABC 820908 40 0 0 0 0 0 1 ------- 0 49.0 S20N05w29DCD 820806 40 0 0 0 0 0 0 ------- CO 49.0 S20N05W33BDD 820901 100 0 0 0 0 0 0 ------- 49.0 ·S20N05W34CCA 820911 150 0 0 0 0 0 0 ------- 49.2 S20N05W28CGB 820902 75 0 0 0 0 0 0 ------- 49.2 S20N05W29DDD 820808 100 0 0 1 0 0 0 ------- 49.2 S20N05W33DAB 820911 80 0 0 0 0 0 0 ------- 49.3 S20N05W28CBC 820823 50 0 0 0 0 0 0 ------- 49.7 S20N05W28CBD 820806 100 0 0 0 1 0 0 ------- 49.8 S20N05W28BDC 820823 20 0 0 0 0 0 0 ------- 50.1 S20N05W27DCD 820806 100 0 0 2 0 0 0 ------- 50.2 S20N05W28ADB 820911 200 0 0 0 0 0 1 ------- 50.4 S20N05W21DDC 820901 75 0 0 0 0 0 0 ------- 50.5 S20N05W20ADA 820728 400 0 1 4 0 1 0 ------- 50.5 S20N05W23BCD 820727 250 0 0 30 0 0 0 ------- 50.5 S20N05W26AAD 820625 400 12 0 0 0 0 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-f-l.Continued. --------------------------------------------------------------------------------~----~~------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M0 N BEltING RIVER SHOCKED ----------------------------------~----BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ----------------------------~-----------------------------------------------------------------~---------------- 50.5 S20N05W27AAD 820727 170 0 0 0 0 0 0 ------- 50.5 S20N05W27ADD..820806 30 0 0 0 0 0 0 ------- 51.0 S20N05W21BBC·820823 150 0 0 0 0 0 0 -,------"--- 51.0 S20N05W27DCD 820806 100 0 0 50 10 0 0 --~~--- 51.5 S20N05W21ABA 820823 20 0 0 0 0 0 0 ------- 52.1 S20N05W14BCC 820923 200 0 0 0 0 0 0 ------- 52.1 S20N05W16ABA 820823 30 0 0 0 0 0 0 ------->52.2 S20N05W22ABB 820901 100 0 0 0 0 0 1 -------N 52.3 S20N05W16BDD 820911 30 0 0 0 0 0 0 -------.... 0 52.6 S20N05W16ACD 820902 100 0 0 0 0 0 0 ------- 52.7 S20N05W15DDD 820901 100 0 0 0 0 0 0 ------- 52.7 S20N05W16BAA 820902 40 0 0 0 0 0 0 ------- 52.9 S20N05W14CCA 820727 120 0 3 0 0 0 0 ------- 53.0 S20N05W14BCC 820901 30 0 0 0 0 0 0,------- 53.0 S20N05W16ABA 820902 0 0 0 0 0 0 ------ 53.1 S20N05W09CDA 820902 150 0 0 0 0 0 0 ------ 53.1 S20N05W09DCC 820808 400 0 0 3 7 5 0 ------ 53.1 S20N05W11CAD 820923 150 0 0 0 0 0 0 ------- 53.3 S20N05W09CDA 820902 30 0 0 0 0 0 0 ------- 53.3 S20N05W09DCB 820823 150 0 0 0 0 1 3 ------- 53.3 S20N05WllACC 820923 200 0 0 0 0 0 0 ------- 53.7 S20N05W09BDD 820902 100 0 0 0 0 0 0 ------- 53.9 S20N05W09ADB 820823 50 0 0 0 2 0 0 ------ 53.9 S20N05W14BBC 820901 50 0 0 0 0 0 0 ------- ----------------------------------------------------------------------------------------~---------------------- )~ t i -. )J .1 J J J JjIJJJIIBIJ --~1 1 --------i ----;---1 ~-~i I I J --J I -1 J j J ] )} Appendix Table 2-F-l.Continued. ----------------------------------------------------------------------------------~----------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 54.0 S20N05W09ABA 820823 90 0 0 0 2 1 0 ------- 54.0 S20N05wllCDD 820901 0 0 0 0 0 0 ------- 54.1 S20N05w03CCD 820823 80 -0 0 0 1 0 0 ------- 54.3 S20N05w03CAC 820823 150 0 0 0 0 0 0 ------- 54.5 S20N05W03CAD 820902 200 0 0 0 0 0 0 ------- 54.9 S20N05W03CAC 820902 0 0 0 0 0 0 ------- 55.0 S20N05W03BCB 820902 50 0 0 0 0 0 0 -------»55.9 S21N05w34DDA 820902 30 0 0 0 0 0 ·0 ------- I\)56.0 S21N05W340BB 820828 80 0 0 0 0 0 0 ------- ~56.2 S21N05W34DAC 821005 200 0 0 0 0 0 1 -------~56.2 4000S21N05W34DCC820808 0 0 6 6 2 0 ------- 56.5 S21N05W35BBC 820828 150 0 0 0 0 0 1 ------- 57.0 .S21N05W26CBD 820828 30 0 0 0 0 0 0 ------- 57.0 S21N05W36BDC 820727 0 0 0 0 0 0 ------- 57.1 S21N05W36BDC 820625 3696 27 0 0 0 0 0 ------- 57.4 S21N05W27DBD 820728 350 0 0 50 0 30 0 ------ 57.5 S17N05W26BDB 820828 30 0 0 0 0 0 0 ------- 57.9 S17NOSW26BAA 820828 60 0 0 0 0 0 0 ------- 58.0 S21NOSW26ACD 820808 20 0 0 0 0 1 0 ------- 58.5 S21N05W23CCB 820828 200 0 O·0 0 0 0 ------- 59.0 S21NOSW23CBC 820828 30 0 0 0 0 0 0 ------- 59.5 S21NOSW13ACA 820602 250 0 0 0 0 0 0 ------- 59.5 S21N05w23ADB 820828 20 0 0 0 0 0 0 ------- 59.5 S21NOSW24DBA 820625 440 1 0 0 0 0 0 -----_.- ---~---------------------------------------------------------------------------------------------~------------ Appendix Table 2-F-l.Continued. ------------------------------------------------------------------------------------------.-------------~------CAT C H ------------------------------------------------~DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK.CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 59.5 S21N05W24DBA 820727 100 0 0 0 0 0 0 ------- 59~6 S21N05W23AAD 820828 100 0 0 0 1 0 0 ------- 59.7 S21N05W23ABB ..820828 80 0 0 0 0 0 0 ------- 59.8 .S21N05W14CDA 820828 0 0 0 0 0 0 ------- 59.8 S21N05W24BAB 820828 20 0 0 0 0 0 0 -----~- 59.9 S21N05W24BAC ·820808 250 0 0 1 2 1 0 ------- »60.0 S21N05W14DDA 820828 150 0 0 0 0 0 0 ------- I\)60.0 S21N05W14DDB 820828 80 0 0 0 0 0 0 ------ ~60.1 S21N05W13CAC 821005 200 0 0 0 0 0 0 ------ I\)60.1 S21N05W13CCA 820828 30 0 0 0 0 0 0 ------- 60~3 S21N05W13BDD 820828 20 0 0 0 0 0 0 ------ 60.5 S21N05W13ACA 820524 1000 1 0 0 0 0 0 .------ 60.6 S21N05W13CAB 820828 50 0 0 0 0 1 0 ------- 61.0 S21N05W13AAA 820602 100 0 0 0 0 0 0 ------- 61.0 S21N05W13AAA 820803 50 0 0 0 0 0 0 ------- 61.3 S21N05W12DCA 820920 500 0 0 0 0 0 0 ------- 61.3 S21N05W12DCC 820810 400 0 0 3 29 5 0 ------ 61.4 S21N05W12DCC 821002 350 0 0 0 0 0 1 ------ 61.5 S21N05W12DBB 820904 400 0 0 0 2 1 0 ------ 61.5 S21N05W12DBD 820824 350 0 0 0 1 0 0 ----- 61.8 S21N05W12BAA 820821 1000 0 0 0 2 3 0 ------ 62.0 S21N05Wl2AAB 820904 300 0 0 0 0 0 0 ------ 62.0 S21N05W12DBD 820907 600 0 0 0 0 0 2 ------ 62.0 S21N05W12DBD 820920 400 0 0 0 0 0 0 ----- -------------------------------------------------------------------------------------------------------------- \\,~J ~]J I J I ]I I J ]J )~1 ~ ---J ------1 ~--)-D ] ) I -1 J 1 1 Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H -------------------------------------~-----------DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YD5)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ------------------------------------------------------------------------------------------------------------ 62.0 S21N05W12DBD 820925 600 0 0 0 0 0 0 ------- 62.0 521N05W12DBD 821002 300 0 0 0 0 0 1 ------- 62.0 S21N05W12DBD 821008 500 0 0 0 0 0 0 ------- 62.3 S21N05W12DAB 821002 350 0 0 0 0 0 2 ------- 62.8 S21N04W06CAB 820904 150 0 0 0 1 0 0 ------- 62.8 521N05WOICDD 820811 750 0 0 1 1 3 0 ------- »62.8 S21N05WOICDD 820821 200 0 0 0 0 1 0 ------- I\)62.8 S21NOSWOICDD 820824 400 0 0 0 1 3 0 -------...63.0 S21N04W06BDC 820907 300 0 0 0 0 4 0 ------- (.)63.1 S21N05W06BDB 820823 200 0 0 0 0 3 0 ------- 63.2 S21NOSW02ADB 820920 400 0 0 0 0 0 0 ------- 63.2 S22NOSW36DC 820811 350 0 0 0 5 0 0 ------- 63.2 S22NOSW36DC 820821 250 0 0 0 1 0 ()------- 63.2 S22N05W36DC 820824 250 0 0 0 1 1 0 ------- 63.3 S21NOSWOIBAB 820903 600 0 0 0 0 0 0 ------- 63.4 S22NOSW36CDC 820920 200 0 0 0 0 0 0 ------- 63.4 S22NOSW36CDC 820927 200 0 0 0 0 0 0 ------- 63.4 S22N05W36CDC 821008 250 0 0 0 0 0 2 ------- 64~0 S21NOSWOIBAB 820824 200 0 0 0 4 1 0 ------- 64.0 S22NOSW35CAD 820811 250 0 0 0 0 0 0 ------- 64.5 S21N04W31CCC 821002 250 0 0 0 0 0 0 ------- 64.7 S22N05W35BDA 820903 300 0 0 0 0 0 0 ------- 64.7 S22NOsw35BDA 820926 300 0 0 0 0 0 0 ------- 64.9 S22N05W3SABB 820920 350 0 0 0 0 0 0 ------- -------------------------------------------~------------------------------------------------------------------- Appendix Table 2-F-l.Continued. ----------------------------------------------------------------------------~----------------------------------CAT C H ------------------------------------------------- DISTANCE·A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE.(YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 65.0 S21N05W35BBA 820821 250 0 0 0 0 1 0 ------- 65.0 S22NO'SW26 CDC 821002 400 0 0 0 0 0 2 ------- 65.0 S22N05W35BAB 820804 4000 0 0 130 72 13 0 ------- 65.6 S22N05W26CBB 820920 450 0 0 0 0 1 0 ------- 65.6 S22N05W26CBB 821008 200 0 0 0 0 0 0 ------- 65.6 S22N05W27ADC 820712 600 0 0 0 0 0 0 ------- 65.6 S22N05W27ADC 820804 400 0 0 5 0 4 0 ------->65.6 S22N05W27ADC 820811 500 0 0 0 0 0 0 ------- r-,)65.6 S22N05W27ADC 820821 300 0 0 0 0 0 0 -------.....65.8 S22N04W30BCC 820803 300 0 200 30~1 0 0 ------- 65.8 S22N04w30BCC 820925 300 0 0 0 0 0 0 ------- 65.8 S22N05W25ADB 820907 700 0 0 0 0 0 0 ------- 66.1 S22N04W3 OBAB 820712 600 0 0 0 0 0 0 ------ 66.1 S22N04W30BAB 820802 250 0 0 999 200 0 0 ------- 66.1 S22N04W30BAB 820810 200 0 0 250 250 0 0 ------- 66.1 S22N04W30BAB 820823 150 0 0 0 200 50 0 ------- 66.1 S22N04W30BAB 820925 250 0 0 0 0 0 0 ------- 66.1 S22N05w22DAB 820811 1200 0 0 0 0 4 0 ------- 66.1 S22N05W22DAB 820821 800 0 0 0 0 0 0 ------- 66.3 S22N05W23CCD 820903 300 0 0 0 0 0 0 ------- 66.4 S22N05W26ACC 820903 250 0 0 0 1 0 0 ------- 66.4 S22N05W26BAA 820824 700 0 0 0 4 5 0 ------ 66.5 S22N05W23DBA 820920 200 0 0 0 0 0 0 ------- 66.6 S22N05W24DAA 820803 200 0 0 5 20 1 0 ------- ------------------------------------------------------~-------------------------------------------------------- .~) J ~.~J j I I J J ~.~}~1 J ••~~ ---I 1 1 ) ]1 )1 1 .J 1 ) ) Appendix Table 2-F-l.Continued. ----------------------------------------------------------------------------------------~---------------------- CAT C H ------------------------------------------------- DISTANCE A D UL T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE.PINK CHUM COHO CISCO OBSERVED -------------------------------------------------------------------------------------------------------~------- 66.6 S22N05W24DAA 820925 200 0 0 0 0 0 0 ------- 66.7 S22N05W23DBA 820920 400 0 0 0 0 0 0 ------- 66.7 S22N05W23DBA 821008 300 0 0 0 0 0 0 ------- 66.8 S22N05W24DAA 820823 350 0 0 0 1 0 0 ------- 67.0 S22N05W23BAB 820811 250 0 0 0 0 0 0 ------- 67.2 S22N05W13ADB 820920 200 0 0 0 0 0 0 ------- 67.2 S22N05W23ADB 820824 700 0 0 0 0 0 0 -_._---- ):10 67.3 S22N05W23AAA 820821 350 0 0 0 1 0 0 -------I\)67.5 S22N05W24ABA 821002 250 0 0 0 0 0 0 -------~ 01 67.7 S22N05W13CCC 821008 150 0 0 0 0 0 0 ------- 68.2 S22N05W23DCD 820904 600 0 0 0 0 0 0 ------- 68.4 S22N05W14BCA 820712 150 0 0 0 0 0 0 ------- 68.4 S22N05W14BCA 820804'2000 0 0 110 15 8 0 ------- 68~5 S22N05W11DCC 820811 250 0 0 0 0 0 0 ------- 68.5 S22N05W12DAB 820904 1500 0 0 0 1 0 ·0 ------- 68.5 S22N05W12DCB 820823 350 0 0 0 3 0 0 ------- 68.5 S22N05W12DCD 820712 200 0 0 0 0 0 0 ------- 68.5 S22N05W12DCD 820810 100 0 0 0 4 3 0 ------- 68.5 S22N05W13DBD 820904 350 0 0 0 0 0 0 ------- 68.5 S22N05W13DBD 820907 500 0 0 0 0 0 0 ------- 68.5 S22N05W13DBD 820918 900 0 0 0 0 0 0 ------- 68.6 S22N05W14ADA 820803 450 0 0 40 1 1 0 ------- 68.6 S22N05W14ADA 820810 500 0 0 0 2 1 0 ------- 68.6 S22N05W14ADA 820821 400 0 0 0 0 0 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H -----------~---------------~------~--------------DISTANCE ADULT SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM CORD CISCO OBSERVED -----------------------------------~-------------------------------------------------------------------------- 68.6 S22N05W14ADA 820824 600 0 0 0 0 1 0 ------- 68.7 S22N05W14ADA 820903 850 0 0 0 0 0 0 ------'. 68.7 S22NOSW14ADA 820920 800 0 0 0 0 0 0 ------- 68.7 S22N05W14ADA 820926 350 0 0 0 0 0 0 ------- 68.8 S22N05W13DBA 821002 200 0 0 0 0 0 0 ------- >69.0 S22N05W12DAB 820819 300 0 0 0 2 .0 0 -----_.... f\)69.1 S22N05W12DAB 820803 350 0 0 30 103 1 0 -------.....69.1 S22N05W12DAB 820810 500 0 0 4 15 1 0 ------- 0)69.1 S22N05W12DAB 820925 350 0 0 0 0 0 0 ------- 69.4 S22N05WI2ADB 820810 400 0 0 0 2 0 0 ------- 69.5 S22N05W01DDC 820819 1000 0 0 0 0 1 0 ------- 70.0 S22N05WOIDAD 820823 1000 0 0 0 0 1 0 ------- 70.2 S22N05W01CDA 820821 600 0 0 0 1 1 0 ------ 70.2 S22N05WOIDDA 821002 1800 0 0 0 0 0 0 ------- 70.7 S22N05W01DAA 820824 750 0 0 0 1 2 0 ---...._-- 71.0 S22N05W01ADD.820907 1250 0 0 0 0 0 0 ------ 71.0 S23N05W36CAC 820804 2000 0 2 220 165 8 0 ------- 71.0 S23N05W36CCB 821002 300 0 0 0 0 0 0 ----- 71.3 S23N04W30CCB 820810 2000 0 0 2 9 1 0 ---- 71.3 S23N05W36BAD 820821 700 0 0 0 22 11 0 ----- 71.3 S23N05W36CCD 820904 1000 0 0 0 1 0 0 ---- 71.3 S23N05W36CCD 820920 500 0 0 0 0 0 0 ---- 71.3 S23N05W36CCD 820926 1000 0 0 0 0 0 0 ---- 71.3 S23N05W36CCD 820927 1000 0 0 0 0 0 2 ------ -----------------------------------------------~--------------------------------------------~------------------ , ••J i I J ~~;1 ~J ]I t .1 J D .~.~~ -----'I ---~.------j --------J ~~~S 1 i 1 J .J 1 J )-----. ))) Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 71.4 S23N05W35DCC 820824 400 0 0 0 0 0 0 ------- 71.5 S23N04W30CCB 820918 1800 0 0 0 0 0 0 ------- 71.5 S23N04W31BCC 820904 500 0 0 0 1 1 0 -~----- 71.5 S23N04W31BCC 820913 350 0 0 0 0 0 0 ------- 71.5 S23N05W25DBC 821008 600 0 0 0 0 0 1 -------»71.8 S23N04W30CCB 820823 800 0 0 2 1 ..0 0 ------- I\)71.8 S23N04W3 OCCB 820907 1200 0 1 0 1 0 0 -------..72.0 S23N04W30CC 820609 880 0 0 0 0 0 0.....------- 72.0 S23N04W31 BBC 820609 340 0 0 0 0 0 0 ------- 72.0 S23N04W31BBC 820819 1700 0 0 2 12 1 0 ------- 72.0 S23N05W35DBC 820803 20 0 0 50 0 0 0 ------- 72.0 S23N05W35DBC 820811 60 0 0 8 0 1 0 ------- 72.0 S23N05W35DBC 820824 600 0 0 0 0 0 0 ------- 72.0 S23N05W35DBC 820927 100 0 0 0 0 2 0 ------- 72.5 S22N05W25CDC 820821 300 0 0 0 0 0 0 ------- 72.5 S23N05W25AAA 820803 5984 0 2 150 100 0 0 ------- 72.5 S23N05W25AAA 820810 300 0 0 2 1 0 0 ------- 72.5 S23N05W25AAA 820823 500 0 0 1 0 0 0 ------- 72.5 S23N05W25AAA 820904 900 0 0 0 0 0 0 ------- 72.5 S23N05W25AAA 820907 800 0 0 0 1 0 0 ------- 72.5 S23N05W25AAA 820914 1800 0 0 0 1 O·0 ------- 72.5 S23N05W25AAA 820925 2000 0 0 0 0 0 0 ------- 72.5 S23N05W25ACB 820920 800 0 0 0 1 0 0 ------- 72.5 S23N05W25CBB 820811 700 0 0 3 25 14 0 ------- -----------------------------------------------------------------------------------------~--------------------- Appendix Table 2-F-l.Continued. ----------------~---------------------~------------------------------------------------------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DAtE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED· ----.-------------------------------------------~-------------------------------------------~-----------------~ 72.5 S21N05W25CBB 820821 300 0 ·0 0 1 0 0 ------- 72.6 S23N04W30BBC 821002 ·1600 0 0 0 0 0 0 ----~- 72.7 S23N05W26AAD 821008 400 0 0 0 0 0 3 ------- 72.8 S23N05W25CCD 820903 500 0 0 0 0 0 0 ------- 72.8 S23N05W25CCD 820926 500 0 0 0 0 0 0 ------- 72.9 S23N04W30BCB ·820712 30 3 0 0 0 0 0 ------- 73.0 S23N04W30BBB 820821 250 0 0 0 10 0 0 ------->-73.0 S23N04W30BCB 820904 150 0 0 0 0 0 0 ------I\)73.0 S23N05W25BBD 820821 600 0 0 1 0 0 0 -------.. CXJ 73.1 S23N04W30BBB 820609 740 0 0 0 0 0 0 ------- 73.1 S23N04W30BBB 820712 400 12 0 0 0 0 0 ------ 73.1 S23N04W30BBB 820803 240 0 0 40 12 0 0 ----- 73.1 S23N04W30BBB 820819 100 0 0 3 206 3 0 ----- 73.1 S23N04W3 OBBB 820904 100 0 0 0 0 0 0 ------- 73.1 S23N04W30BBB 820925 240 0 0 0 0 0 0 ------ 73.2 S23N04W30BBB 820810 200 0 0 1 3 1 0 ------- 73.2 S23N04W30BBB 820819 200 0 0 0 4 3 0 ------- 73.2 S23 N04W3 OBBB 820918 350 0 0 0 0 0 0 ------ 73.2 S23N05W25ABC 820927 300 0 0 0 0 0 2 ------- 73.4 S23N05W25BBA 820824 700 0 0 0 1 3 0 --- 73.7 S23N05W24CCC 820821 400 0 0 0 1 0 0 ------ 73.8 S23N04W19CCC 820904 200 0 0 0 2 0 0 ------- 73 .8 S23N04W19CCC 820914 250 0 0 0 0 0 0 ----- 73.8 S23N05W24CBD 820920 600 0 0 0 0 0 0 ----- --------------------------------------------------------------------------------------------------------------- \~ I J J ,.1 J ]J ,J J I ~I J J J J ) i -----'I ---j --------1 -------j ----,-J ---l J J J 1 1 J 1 1 1 ) Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK.CHUM COHO CISCO OBSERVED ------------------------------------------------------------------------------------------------------------- 73.8 S23N05w24CBD 821008 200 0 0 0 0 0 0 ------- 74.2 5 23N05W24ABB 820811 400 0 0 0 6 2 0 ------- 74.2 S23N05W24ABB 820819 200 0 0 0 0 0 0 ------- 74.2 S23N05W24ABB 820926 400 0 0 0 0 0 0 ------- 74.2 S23N05W24CCB 821002 200 0 0 0 0 0 5 ------ 74.2 S24N05W24ABC 820821 300 0 0 0 2 4 0 ------- 74.3 S23N05W24ABB 820903 1400 0 0 0 0 0 0 -------»74.3 S23N05W24BAD 820824 500 0 0 0 1 9 0 ------- I\)74.4 S23N05W13CCD 820609 340 0 0 0 0 0 0 --------"74.4 S23N05W13CCD 820712 400 0 0 0 0 0 0co ------- 74.4 S23N05W13CCD 820811 300 0 0 0 4 4 0 ------- 74.4 S23N05W13CCD 820819 500 0 0 0 0 3 0 -------- 74.4 S23N05W13CCD 820823 300 0 0 0 0 0 0 ------- 74.4 S23N05w13CCD 820903 350 0 0 0 1 0 0 ---~--- 74.4 S23N05W13CCD 820906 200 0 0 0 C 0 0 ------- 74.7 S23N05W13DCD 820810 350 0 0 0 0 1 0 ------- 74.7 S23N05W13DCD 820907 600 0 0 0 0 0 0 ------- 74.7 S23N05W13DCD 820920 700 0 0 0 0 0 0 ------- 74.7 S23N05W13DCD 820926 350 0 0 0 0 0 0 ------- 74.8 S23N05W13BBA 820609 880 0 2 0 0 0 0 ------- 74.8 S23N05W13DCD 820904 250 0 0 0 0 0 0 ------- 74.8 S23N05W13DCD 820913 400 0 0 0 1 0 3 ------- 74.9 S23N05W13BD 820914 1200 0 0 0 1 0 4 ------- 75.0 S23N05W13DCC 820918 300 0 0 0 0 0 0 ------- ----------~---------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE AD U L T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 75.0 S23N05w13DCC 821002 450 0 0 0 0 0 5 ------- 75.0 S23N05W13DCD 820927 1500 0 0 0 0 0 0 -----. 75.0 S23N05W13DCD 821008 300 0 0 0 0 0 4 ----- 75.0 S23N05W24ABB 820804 4000 0 0 450 225 10 0 ------ 75.0 S23N05W24ABB 820811 450 0 0 1 17 12 0 ------- 75.0 S23N05W24ABB 820823 300 0 0 0 2 0 0 ------- 75.0 S23N05W24ABB 820903 500 0 0 0 2 0 0 ------ 75.0 S23N05W24ABB 820907 600 0 0 0 1 0 0 ----- >75.0 S23N05W24ABB 820914 250 0 0 0 0 0 0 ------ I\)75.0 S23N05W24ABB 821013 1500 0 0 0 0 0 4 ----- I\)75.1 S23N05W13CDA 820804 400 0 0 0 0 0 0 ---- 0 75.3 S23N04W07DCB 820906 200 0 0 0 0 0 0 ----- 75.4 S23N05W13ACC 820811 500 0 0 1 4 2 0 ---- 75.4 S23N05W13ACC 820819 450 0 0 0 0 5 0 75.4 S23N05W13ACC 820823 350 0 0 0 0 1 0 ---- 75.5 S23N04W18BDB 820920 400 0 0 0 0 0 0 ---- 75.5 S23N04W18BDB 821002 300 0 0 0 0 0 5 ---- 75.5 S23N04W18BDB 821005 200 0 ·0 0 0 0 2 ---75.5 S23N04W18BDB 821008 250 0 0 0 0 0 5 75.5 S23N04W18BDB 821013 300 0 ·0 0 0 0 15 --- 75.5 S23N05W24ABB 820819 600 0 0 0 0 6 0 --- 75.7 S23N04W07CB 820810 400 0 0 2 30 12 0 75.7 S23N04W07CB 820819 125 0 0 0 0 0 0 ---75.7 S23N04W07CB 820823 300 0 0 0 1 0 0 --- --------------------------------------------------------------------------------------------------------------- )\ J j J I ,J !I I 8 I J ~)g J ,i ] J I )))D J 1 1 ,;!]i J 1)... \).I Appendix Table 2-F-l.Continued. -------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED -----------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------~-------------------------------------~-----------------------~---------------------------------- 75.7 S23N04W07CB 820903 350 0 0 0 2 0 0 ------ 75.7 S23N04W07CB 820906 250 0 0 0 0 0 0 ---- 75.7 S23N04W07CB 820914 350 0 0 0 0 0 0 ------ 17 .0 S23N04W06CD 820906 700 0 0 0 2 1 0 ------- 17 .0 S23N04W07ABA 820525 200 0 0 0 0 0 0 ------- 77.0 S23N04W07ABA 820609 450 0 0 0 0 0 0 ------- 17 .0 S23N04W07ABA 820903 300 0 0 0 1 0 0 ------ >17.0 S23NOSW13ACC 820918 1500 0 0 0 0 0 0 ______E' f\)17 .0 S23NOSW13ACC 820921 400 0 0 0 0 0 0 ------- f\)17.6 S23N04W06CDB 820918 SOO 0 0 0 0 0 0 -------.....77.6 S23N04W06CDB 820921 800 0 0 0 0 0 1 ------- 17 .6 S23N04W06CDB 820925 600 0 0 0 0 0 0 ------- 77.6 S23N04W06CDB 820927 1100 0 0 0 0 0 0 ------ 17 .6 S23N04W06CDB 820930 900 0 0 0 0 0 12 15 -20 17 .6 S23N04W06CDB 821002 250 0 0 0 0 0 5 ------- 17 .6 S23N04W06CDB 821013 800 0 0 0 0 0 0 20 -25 77.6 S24N04W06CDB 821008 SOO 0 0 0 0 0 25 ------ 78.0 S23N04W01DA 820819 500 0 0 0 12 12 0 ------ 78.0 S23N04W06BD 820823 400 0 0 0 3 2 0 ------- 78.0 S23N04W06CD 820525 1760 0 0 0 0 0 0 ------ 78.0 S23N04W06CD 820609 2640 0 1 0 0 0 0 ------ 78.0 S23N04W06CD 820712 700 2 0 0 0 0 0 ------ 78.0 S23N04W06CD 820802 600 0 0 100 12 0 0 ------- 78.0 S23N04W06CD 820810 600 0 0 9 36 0 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. ---------------------------------------------~---------------~-------------------------------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE·(YDS)CHINOOK.SOCKEYE PINK CHUM COHO CISCO OBSERVED .-.-...-. ---------------------------~-----~----------------------------------------------------------------------------- 78-.0 S23N04W06CD 820819 700 0 0 0 5 2 0 ------ 78_.0.S23N04W06CD 820823 600 0 0 0 4 2 0 ------- 78.0 S23N04W06CD 820903···800 0 0 0 0 0 0 -"!"'"------ 78.0 S23N05W01ADA 820906 300 0 0 0 1 0 0 ------- 78.0 S24NOSW36CD 820913 850 0 0 0 3 0 0 ------- 78.5 S23NOSWOIBBC 820609 300 1 0 0 0 0 0 ------ 78.5 S23NOSWOIBBC 820711 400 0 0 0 0 0 0 ------- >78.5 S23NOSWOIBBC 820802 300 0 0 IS 0 1 0 ------- l\)..78.5 S23NOSWOIBBC 820819 250 0 0 0 0 1 0 ------- 1\)78.5 S23N05WOIBBC 820904 200 0 0 0 0 0 0 ------1\)79.0 S24NOSW36CD 820525 880 0 0 0 0 0 0 ------- 79.0 S24NOSW36CD 820609 880 0 4 0 0 0 0 ------ 79.0 S24NOSW36CD 820711 500 0 0 0 0 0 0 ------- 79.0 S24NOSW36CD 820802 400 0 0 40 50 0 0 ------ 79.0 S24N05W36CD 820810 500 0 0 3 52 10 0 ------- 79.0 S24N05W36CD 820820 500 0 0 0 12 21 0 ------- 79.0 S24NOSW36CD 820823 600 0 0 0 7 11 0 ------ 79.0 S24N05W36CD 820903 30b 0 0 0 12 4 1 ------ 79.0 S24N05W36CD 820906 600 0 0 0 3 0 0 ----- 79.0 S24N05W36CD 820915 600 0 0 0 1 1 ,0 ------ 79.0 S24NOSW36CDA 820927 800 0 0 0 1 0 0 ----- 79.0 S24N05W36CDA 821003 400 0 ·0 0 0 0 0 ----- 79.2 S24N05W36CAD 821003 500 0 0 0 0 0 6 -------- 79.4 S24N05W36BCC 820921 1500 0 0 0 0 0 0 ------ --------------------------------------------------------------------------------------------------------------- )~\ B ~I J 1 _J .~I j~)I t .1 I ~m I I J Appendix Table 2-F-l.Continued. J j .~ ,---------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 79.4 S24N05W36BCC 820925 400 0 0 0 0 0 0 ------ 79.4 S24N05W36BCC 820930 450 0 0 0 0 0 3 ------- 79.4 S24N05W36BCC 821003 900 0 0 0 0 0 11 ------ 79.4 S24N05W36BCC 821013 500 0 0 0 0 0 2 ------- 79.S S24NOSW26 CD 820609 1000 0 1 0 0 0 0 ------- 79.S S24N05W36AD 820711 8S0 0 0 0 0 0 0 ------ 79.5 S24N05W36AD 820819 550 0 0 0 0 0 0 ------- 80.0 S24N05W25BDC 820906 400 0 0 0 0 0 0 ------->80 .0 S24NOSW2SCAB 820921 150 0 0 0 0 0 0 -------I\)80.5 S24NOSW25BAB 820921 700 0 0 0 0 0 0 --------I\) (,)80 .S S24N05W25BAB 820930 300 0 0 0 0 0 2 ------- 80.S S24N05W25BDA 820930 200 0 0 0 0 0 0 ------- 80.8 S24N05W2SBAD 820831 250 0 0 0 0 0 0 ------ 81.0 S24N05W2SBCD 820820 900 0 0 4 4 5 0 ------- 81.0 S24N05W26MB 820824 300 0 0 0 7 3 0 ------- 81.0 S24NO 5W26 BAA 820906 100 0 0 1 0 0 0 ------- 81.1 S24NOSW26ABB 820930 350 0 0 0 0 0 0 ------- 81.2 S24N05w26ABA 821013 300 0 0 0 0 0 0 IS -20 81.3 S24N05W23CDA 820921 200 0 0 0 ·2 0 0 ------- 81.5 S24NOSW23CDA 820921 400 0 0 0 1 0 0 ------- 81.5 S24NOSW23CDA 820930 400 0 0 0 0 0 0 15 -20 81.5 S24N05W26ABD 821013 300 0 0 0 0 0 0 ------- 82.0 S24N05W22ADC 820802 700 0 15 30 30 0 0 ------- 82.0 S24N05W22ADC 820825 0 0 0 2 16 0 ------- ~-------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. ----------------------------------------------------------------------------------~--------------.--~----------CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING .RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ------------------------------------------------~----------------------------------------~--------------------- 82.0 S24N05W22ADC 820831 500 '0 0 0 .1 0 0 ------- 82.0 S24N05W23CBC 820921 300 0 0 0 0 0 0 ------- 82.6 S24N05V22DAB 820812 800 0 0 6 45 12 0 ------_.-. 82.6 S24N05V22DAB 820906 700 0 0 0 2 1 o .------- 83.1 S24N05W15CBD 820812 300 ,0 0 0 3 1 0 ------- 83.1 S24N05W15CBD 820825 400 0 0 0 0 1 0 ------- 83.1 S24N05W15CBD 820831 350 0 0 0 0 0 0 ------ )I-83.1 S24N05W15CDB 820906 300 0 0 0 0 0 0 ------ I\)83.1 S24N05W16AAC 820525 200 0 0 0 0 0 0 -------I\)83.1 S24N05W16AAC 820711 800 1 0 0 0 0 0~------- 83.1 S24N05W16AAC 820713 700 0 0 0 0 0 0 ------ 83.1 S24N05V16DAA 820802 450 0 0 6 0 0 0 ------- 83.1 S24N05W16DAA 820812 400 0 0 2 0 1 0 -------- 83.1 S24N05W16DAA 820820 200 0 0 0 0 8 0 ------- 83.1 S24N05W16DAA 820825 250 0 0 0 0 0 0 ------ 83.1 S24N05W16DAA 820901 300 0 0 0 0 0 0 ------ 83.1 S24N05w16DAA 820906 300 0 0 0 0 0 0 ------ 83.2 S24N05V15CBD 821003 400 0 0 0 0 0 0 ------- 83.3 S24N05W15BDB 821003 500 0 0 0 0 0 0 ------- 83.4 S24N05W15BAB 820906 500 0 0 0 0 0 0 ----- 83.4 S24N05W15BCC 820921 1500 0 0 0 0 0 0 ------ 83.4 S24NOSW15BCC 821006 900 0 0 0 0 0 8 ------- 83.4 S24N05W15BDB 820820 350 0 0 0 0 2 0 ------ 83.4 S24N05W15CBD 820820 400 0 0 0 4 10 0 ----- ~---------------~------------------------------------------------------~-------------------------------------- .~\ -:--1 ) ~J ) J 1 )-J J ) Appendix Table 2-F-l.Continued. --------------------------~---~------------------------------------------------------------------------ CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ---------------------------------------------------------------------------------------------------~----------- 83.5 S24N05W15BCB 820915 150 0 0 0 0 0 0 ------ 83.7 S24N05W15BBA 820915 350 0 0 0 0 0 0 ------- 83.8 S24N05W15BAD 820825 250 0 0 0 0 2 0 ------- 84.1 S24N05W10CDA 821003 300 0 0 0 0 0 0 ------- 84.1 S24N05W10CDA 821006 500 0 0 0 0 0 0 ------- 84.1 S24N05W10CDB 820921 700 0 0 0 1 O·0 ------- 84.4 S24N05W14AAB 820813 400 0 0 0 11 0 0 ------- >84.5 S24N05W10ADC 820930 250 0 0 0 0 0 0 ------- I\)85.0 S24N05W11BAA 820812 700 0 0 1 35 11 0 ------- I\)85.0 S24N05W11BAA 820831 400 0 0 0 0 5 0 ------- C1I 85.0 S24N05W11BAA 820914 300 0 0 0 2 0 0 ------- 85.0 S24N05W11BAA 821003 1100 0 0 0 0 0 1 ------- 85.1 S24N05W11BAC 820825 900 0 0 1 o ·0'7 0 ------- 85.2 S24N05W11ABB 820921 1200 0 0 0 0 0 0 ------- 85.2 S24N05W11ABB 820930 800 0 0 0 0 0 J ------- 85.2 S24N05W11ABB 821006 1200 0 0 0 0 0 0 30 -40 85.2 S24N05W11ABB 821013 800 0 0 0 0 0 10 ------- 85.5 S24N05W02CC 820820 150 0 0 1 0 1 0 ------- 85.7 S24N05W14AAB 820525 300 0 0 0 0 0 0 ------- .85.7 S24N05W14AAB 820610 500 0 4 0 0 0 0 ------- 85.7 S24N05W14AAB 820713 500 2 0 0 0 0 0 ------- 85.7 S24N05W14AAB 820802 120 0 1 75 0 0 0 ------- 85.7 S24N05W14AAB 820813 350 0 0 8 0 7 0 ------- 85.7 S24N05W14AAB 820820 300 0 0 16 0 ()0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M 0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 85.7 S24N05W14AAB 82082'5 1000 0 0 1 0 4 0 ------ 85.7 S24N05W14AAB 820831 250 0 0 2 0 0 0 ------" 85.7 S24N05W14AAB 820908 350 0 0 0 4 200 0 ------- 86.0 S24N05W01BCD 820820 400 0 0 0 1 8 0 --._--- 86.0 S24N05W01BDD 820820 500 0 0 2 2 9 0 -------. 86 .2 S24N05W01CBC 820921 200 0 0 0 0 0 0 ------ 86 .2 S24N05W12BAD 820802 300 0 1 30 50 0 0 ------- 86 .3 S24N05wl2ABB 820610 600 0 0 0 0 0 0 ------->86 .3 S24N05WI2ABB 820713 350 0 0 0 .0 0 0 -------I\)86.3 S24N05Wl2ABB 820802 800 0 1 0 0 0 0I\)------- 0)86 .3 S24N05Wl2ABB 820813 150 0 0 0 0 0 0 ------- 86 .3 S24N05Wl2ABB 820820 300 0 0 1 0 12 0 -------- 86.3 S24N05Wl2ABB 820901 1500 0 0 1 2 1 0 ------- 86 .3 S24N05Wl2ABB 820908 1000 0 0 2 5 1 0 ----_.- 86.4 S24N05W01BB 820825 700 0 0 0 0 0 0 ------ 86 .4 S24N05W01BCC 820812 300 0 0 0 2 0 0 ------- 86 .4 S24N05WOIBCC 821003 300 0 0 0 0 0 0 60 -70 86 .4 S24N05W01BCC 821006 350 0 0 0 0 0 7 ----- 86 .7 S24N05W01BBD 820921 200 0 0 0 0 0 0 ----- 86.7 S24N05W01BBD 821003 200 0 0 0 0 0 1 ----- 87.0 S24N05W01AB 820610 1760 0 0 0 0 0 0 ------ 87.0 S24N05W01AB 820813 1400 0 0 7 9 6 0 ------ 87.0 S24N05W01AB 820825 2200 .0 0 0 1 11 0 ------- 87.0 S24N05WOIBDD 820802 4400 0 5 250 50 0 0 ------- --------------------------------------------------------------------------------------------------------------- ~l ..~ f J I .___I I .1 ~J J J j ])1 ~I 1 ! ~i ~ Appendix Table 2-F-l.Continued. ~1 ) 1 1 1 1 ) ~ ---------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M 0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ------------------------------------------------------------------------------------------------------------~-- 87.0 S24N05W01BDD 820908 800 0 0 0 0 1 0 ------- 87.0 S24N05W01BDD 820915 1000 0 0 0 0 0 0 ------- 87.3 S24N05W01ACD 820813 550 0 0 2 3 4 0 ------- 87.3 S24N05W01ACD 820820 1600 0 0 2 4 7 0 ------- 87.5 S24N05W01ACD 820915 700 0 0 0 1 0 0 ------- 87.5 S25N05W36ACD 820713 1100 1 0 0 0 0 0 ------- >87.5 S25N05W36CAB 820921 500 0 0 0 0 0 0 ------- I\)88.0 S25N05W36BAA 821006 250 0 0 0 0 0 1 ------- I\)86.4 S25N05W25DCC 820525 200 0 0 0 0 0 0 ------- .....88.4 S25N05W25DCC 820605 200 1 0 0 0 0 0 ------- 88.4 S25N05W25DCC 820610 950 5 10 0 0 0 0 ------- 88.4 S25N05W25DCC 820713 300 5 0 0 0 0 0 ------- 88.4 S25N05W25DCC 820805 350 5 10 4 0 0 0 ------- 88.4 S25N05W25DCC 820817 300 0 4 ·.40 24 999 0 ------- 88.4 S25N05W25DCC 820901 350 0 0 15 13 40 0 ------- 89.0 S25N05W25BAA 821006 350 0 0 0 0 0 0 ------- 89.2 S25N05W26DAA 821006 300 0 0 0 0 0 1 ------- 89.2 S25N05W26DBA 820812 300 0 0 0 0 0 0 ------- 89.3 S25N05W26ABB 820812 600 0 0 2 7 0 0 ------- 89.3 S25N05W26ABB 820901 900 0 0 0 0 0 0 ------- 89.3 S25N05W26ABB 820908 800 0 0 0 2 0 0 ------ 89.4 S25N05W26ABB 820820 400 0 0 0 1 1 0 ------- 90.9.S25N05W23CAB 821001 200 0 0 0 0 0 0 ------- 91.0 S25N05W23ACC 821001 .300 0 0 0 0 0 0 8 -10 ---------------------------~--~-~---------------------------------------------'------------------------------~-- Appendix Table 2-F-l.Continued. ---------------------------------------~-----------------------------------------------------------------------CATCH ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------_.~---------------------------------------------------------------- 91.5 S25N05w15DBA 820605 250 6 0 0 0 0 0 ------ 91.5 S25N05W15DBA 820610 320 2 0 0 0 0 0 ------- 91.5 S25N05W15DBA 820710 250 2 0 0 0 0 0 ------- 91.5 S25N05W15DBA 820805 250 0 0 48 1 2 0 ------ 91.5 S25N05W15DBA 820817 400 0 0 10 0 200 0 -----"-- 91.5 S25N05w15DBA 820901 500 0 0 0 0 4 0 ------- 91.5 S25N05W15DBD 820812 500 0 0 14 0 14 .0 -_._---- >91.5 S25N05W15DBD 820817 250 0 0 1 0 15 0 ------- I\)92.0 S25N05w14BAD 820822 300 0 0 0 0 3 0 ------- I\)92.2 S25N05W13BCC 820812 150 0 0 0 0 0 0 ------CO 92.2 S25N05W'13BCC 820817 250 0 0 1 3 14 0 ------ 92.2 S25N05W13BCC 820902 300 0 0 0 0 1 0 ------ 92.8 S25N05W12BDC 820812 300 0 0 0 7 0 0 ------- 92.8 S25N05W12BDC 820817 250 0 0 0 6 3 0 ------- 92.8 S25N05W12BDC 820905 300 0 0 0 1 0 0 ------ 92.9 S25N05W12BAA 821010 1500 0 0 0 O.0 0 15 -20 93.0 S25N05W12CB 820605 1760 0 0 0 0 0 0 ------ 93.0 S25N05W12CB 820805 1760 0 0 95 40 0 0 ------ 93.6 S25N05WOICAA 820812 400 0 0 9 19 1 0 ------ 93.6 S25N05W12BA 820710 1100 2 0 o·0 0 0 ------ 93.6 S25N05W12BA 820805 450 0 0 47 25 1 0 ------ 93.6 S25N05W12BA 820902 300 0 0 0 1 0 0 ------ 93.6 S25N05W12BA 820905 500 0 1 0 1 0 0 ------ 93.8 S25N05WOIDCB 821001 400 0 0 0 0 0 0 ------- --------------------------------------------------------------------------~---~--------------------------------. l , t o~I .1 I J ~J ]J I J J I J J 1 ~J ~---=--:~l ) Appendix Table 2-F-l.Continued. J 1 J --1 ]]I 1 )) --------------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED -------------------~-------------~--------------------------------------------------------------------- 94.2 S25N05W01ACA 820805 220 0 0 3 12 0 0 ------- 94.5 S25N05W01DBB 821010 800 0 0 0 0 0 4 ------- 95.1 S26N05W36DBD 821010 250 0 0 0 0 0 5 ------- 95.2 S26N05W24CDA 820902 500 0 0 0 1 5 0 ------- 95.2 S26NOSW24CDA 820905 200 0 0 0 5 0 0 ------- 95.2 S26N05W36ACD 820710 600 1 0 0 0 0 0 ------- 95.2 S26N05W36ACD 820805 700 0 0 400 60 0 0 --_..--->95.2 S26N05W36ACD 820812 250 0 0 0 0 1 0 -------I\) I\)95.5 S26N05W35ADC 820605 200 0 0 0 0 U 0 ------- CO 95.5 S26N05W35ADC 820709 450 1 0 0 0 0 0 ------- 95.7 S26N05W36CBB 820605 100 0 0 0 0 0 0 ------- 96.2 S26N05W25CAB 821010 150 0 0 0 0 0 3 ------- 96.2 S26N05W25CBC 821001 500 0 0 0 0 0 0 ------- ·97.0 S26N05W24CDA 820604 1200 1 0 0 0 0 0 ------- 97.0 S26N05W24CDA 820605 225 1 0 0 0 0 0 ------- 97.0 S26N05W24CDA 820608 1200 0 0 0 0 0 0 ------- 97.0 S26N05W24CDA 820709 500 0 0 0 0 0 0 ------- 97.0 S26N05W24CDA 820805 200 0 3 130 25 0 0 ------- 97.0 S26N05W24CDA 820816 400 0 0 1 1 2 O·------- 97.0 S26N05W24CDA 820902 350 0 0 0 0 0 0 ------- 97.0 S26N05W24COA 820922 350 0 0 0 0 0 0 ------- 97.5 S26N05W23DBA 821001 500 0 0 0 0 0 0 ------- 97.7 S26 N05W23ACA 820905 400 0 0 0 0 0 0 ------- 97.7 S26N05W23ACA 820922 400 0 0 0 0 0 0 ------- ~-------------------------------------------------------------------------------------------------------------- Appendix Table2-F-l.Continued. --------------------------------------------------~-----------------------------------~------------------------C AT C H ------------------------------------------------- DISTANCE AD U L T SAL M 0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED -----------------------------------------------------~--------~------------------------------------------------ 97.8 S26N05W23ADA .820902··300 0 0 0 1 0 0 ------- 97.9 S26N05S23AAD 820816 300 .0 0 0 0 2 0 ------ 97.9 S26N05W23AJJ>820709 700 ·0 0 0 0 0 0 ------- 97.9 S26N05W23AAD 820809 100 0 0 0 1 2 0 ------ 97.9 S26N05W23ADA 820922 300 0 0 0 0 0 0 ------- 97.9 S26W05W23AAD 820806 70 0 0 4 0 0 0 _._----- 99.3 S26N05W11DDA 820902 300 0 0 0 0 0 0 ------->99.4 S26 NO 5WllDCD 820809 800 0 0 9 8 1 0 ------- r\)99.4 .S26N05WllDCD 820816 500 0 0 0 0 0 0 -------~99.4 S26N05WllDCD 820822 300 0 0 0 0 0 00 ------- 99.5 S26N05W14ABB 821001 900 0 0 0 0 0 0 ------- 99.6 826N05WllDDA 820709 800 0 0 0 0 0 0 ------- 99.6 S26N05WllDDA 820805 75 0 0 0 0 0 0 ------ 99.6 S26N05W11DDA 820816 100 0 0 0 0 0 0 ------- 99.6 826 N05W11DDA 820822 200 0 0 1 0 8 0 ------ 99.7 826N05WllDB 820805 120 0 0 1 1 0 0 ------- 99.7 S26N05WllDBC 820902 600 0 0 0 3 1 0 ------ 99.7 S26N05W11DBC 820922 600 0 0 0 0 0 0 ---- 99.8 S26N05WllDB 820605 704 0 0 0 0 0 0 ------ 99.8 S26 NO 5W11DB 820805 200 0 0 20 4 0 0 ------ 99.8 S26N05WllDB 820816 500 0 0 0 6 14 0 --- 99.8 S26N05WllDDA 820805 220 1 0 35 5 0 0 ------ 99.8 S26 NO 5WllDDA 820809 1000 0 0 17 7 2 0 ------ 100.0 S26N05WllBDC 820905 350 0 0 0 0 0 0 ----- -----------------------------------------------------------------------------------------------------------~--- l \~ ~!]t )J J B j j J ~}~I J I .~ ~-I J ]-]1 i }))1)) Appendix Table 2-F-l.Continued. -------------------------------------------.--------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING. RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ------------------------------------------._------------------------------------------------------------------ 100.0 S26N05WllBDC 820922 350 0 0 0 0 0 0 ------- 100.4 S26N05W02CDD 820805 150 0 0 0 0 0 0 ------- 100.5 S26N05W02CC 820604 1936 0 0 0 0 0 0 ------- 100.5 S26N05W02CC 820822 700 0 O·0 0 0 0 ------- 100.5 S26N05W02CC 820905 1000 0 0 0 4 0 0 ------- 100.5 S26N05W02CDD 820902 150 0 0 0 0 2 0 ------- 100.5 S26N05W02CDD 820922 150 0 0 0 0 0 0 ------- 100.5 S26N05W02DBC .820816 250 0 0 0 0 6 0 -------»100.5 S26N05W11BDB .820922 1000 0 0 0 0 ')0 -------I\) (a)100.5 S26N05WllBDB 821001 400 0 0 0 0 0 0 ------- .-101.0 S26N05W02BCC 820922 300 0 0 0 0 0 0 ------- 101.1 S26N05W03DDD 820709 700 0 0 0 0 0 0 ------- 101.2 S26N05W03ADB 820526 300 0 0 0 0 0 0 ------- 101.2 S26N05W03ADB 820604 320 0 0 0 0 0 0 ------- 101.2 "S26N05W03ADB 820608 340 0 0 0 0 0 0 ------- 101.2 S26N05W03ADB 820709 250 0 0 0 0 0 0 ------- 101.2 S26N05W03ADB 820710 300 2 0 0 0 0 0 ------- 101.2 S26N05W03ADB 820805 0 0 20 1 0 0 ------- 101.2 S26N05W03ADB 820806 50 0 0 4 0 0 0 ------- 101.2 S26N05W03ADB 820809 220 0 0 12 0 2 0 ------- 101.2 S26N05W03ADB 820816 150 0 0 3 0 1 0 ------- 101.2 S26N05W03ADB 820825 175 0 0 0 0 150 0 ------- 101.2 S26N05W03ADB 820902 250 0 0 0 0 3 0 ------- 101.2 S26N05W03ADB 820905 350 0 0 0 0 1 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. -------------------------------------------------------------------~-------------------------------------------CAT C H --______________________r --------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE .DATE (YDS)CHINOOK SOCKEYE PINK.CHUM COHO CISCO OBSERVED ---------------------------------------------------------------------~----------------------------------------- 101.2 S26N05W03ADB 820916 200 0 0 0 0 0 0 ------ 101.2 S26N05W03ADB 820922 250 0 0 0 0 0 0 ------- 101.2 S26N05W03ADB 821001 300 0 0 0 0 0 0 ------- 101.2 S27N05W02BB .820822 600 0 0 3 0 12 0 .-..----- 101.4 S26N05W03AAC 820608 266 0 0 0 0 0 0 ------- 101.4 S26N05W03AAC 820916 150 0 0 0 0 0 0 ------- 101.6 ·S26NOsW02BCC 820902 300 0 0 0 0 0 0 ------- >101.6 S26NOSW3sCCA 820922 1000 0 0 0 0 0 0 ------ I\)101.6 S27NOsW35CCC 820604 400 0 0 0 0 0 0 ------- (,,)101.6 S27NOsW3SCCC 820805 150 0 0 18 0 0 0 -------I\)101.6 S27NOsW3sCCC 820822 300 0 0 0 2 15 0 ------- 101.6 S27NOSW35CCC 820902 1000 0 0 0 0 4 0 ------- 101.8 S27N05W35CAD 820816 BOO 0 0 2 1 41 0 ------- 101.9 S26NOsW35CAD 821001 1500 0 0 0 0 0 1 ------- 101.9 S27NOSW35ACB 820905 900 0 0 0 0 0 0 ------- 101.9 S27NOsW3sCAD 820922 900 0 0 0 0 0 0 ----- 102.5 S26NOsW35ADD 821001 600 0 0 0 0 0 0 ------ 102.6 S27N05W35ADA .820922 BOO 0 0 0 0 0 0 ------ 102.6 S27N05W35ADD 820709 800 8 0 0 0 0 0 ------ 102.6 S27N05W35ADD 820809 1000 0 0 27 11 0 0 ------ 102.6 S27N05W35ADD 820816 500 0 0 2 2 0 0 ------ 102.6 S27N05W35ADD 820822 900 0 0 0 7 11 0 ------- 102.6 S27N05W35ADD 820825 150 0 0 0 0 0 0 ------ 102.6 S27N05W35ADD 820902 700 0 0 0 0 1 0 ------- ------------------------------------------------------------------------------------------------------------- )~~_//! J j I !)!.1 )B I J ]J 1 !]J I J -~"J 1 -~-i I ) I I J 1 -,).1 1 ) Appendix Table 2-F-l.Continued. ---------------------------------------------------------------------------------------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 102.6 S27NOS.W35ADD 820905 800 0 0 0 1 0 0 ------- 102.6 S27N05W35ADD 820922 700 0 0 0 0 0 0 ------- 102.6 S27N05W35ADD 821.010 1700 0 0 0 0 0 0 ------- 102.7 S27N05W35DB 820604 200 0 0 0 0 0 0 -----_... 102.8 S26N05W35ADA 821001 200 0 0 0 0 0 0 ------- 102.8 S27N05W35ADB 820825 150 0 0 0 1 0 0 ------- 102.8 S27N05W35ADB 820901 75 0 0 0 2 0 0 ------- 104.0 S27N05W25BBD 820901 200 0 0 0 0 0 0 ------- >104.4 S27N05w24CBD 820823 0 0 0 0 Q 0 ------- I\)104.4 S27N05W24CBD 820901 250 0 0 0 0 0 0 ------- CN 105.1 S27N05W24BCA 820823 650 0 0 0 1 3 0 ------- CN 105.1 S27N05W24BCA 820901 350 0 0 0 1 0 0 ------- 105.3 S27N05W24BBD 820823 400 0 0 1 0 12 0 ------- 105.3 S27N05W24BBD 820901 950 0 0 0 0 1 0 ------- 105.8 S27N05W13BCC 820823 450 0 0 0 2 0 0 ------- 106.2 S27N05W13BBB 820823 100 0 0 0 0 0 0 ------- 106.2 S27N05W14AAA 820823 300 0 0 0 0 2 0 ------- 106.2 S27N05W14AAA 820901 800 0 0 0 0 ·0 0 ------- 106.9 S27N05W12BCC 820825 70 0 0 0 0 20 0 ------- 106.9 S27N05W12BCC 820901 1760 0 0 0 0 26 0 ------- 107.4 S27N05W12BBA 820708 600 2 0 0 0 0 0 ------- 107.5 S27N05W12BBA 820823·500 0 0 0 2 7 0 ------- 107.5 S27N05W12BBA 820901 500 0 0 0 1 1 0 ------- 108.2 S27N05WOIABC 820901 900 0 0 0 0 0 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.CQntinued. ----------------------------~----------------------------------~---------------------------------~-------------CAT C H ------------------------------------------------- DISTANCE A D U L TS A L MO N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 108.8 S22N05W36DCA 820901 300 0 0 0 0 0 0 ------ 820824 -108.8 S28N05W36DCA 450 0 0 0 0 3 0 ------ 109.4 S28N05W36~D ..820901 150 0 0 0 0 0 0 ------- 109.7 S28N04W30CCC 820901 150 0 0 0 0 0 0 ------- 109.8 S28N04W30CCD 820822 200 0 0 0 0 0 0 ------ 110.0 S28N04W30CBC 820708 500 4 0 0 0 0 0 ------ 110.1 .S28N04W30CBA 820822 60 0 0 0 0 1 0 ----- 110.1 .S28N04W30CBB 820822 40 0 0 0 0 0 0 ----- >110.3 S28N04W30BBB 820824 1760 0 0 0 1 3 0 ----- I\)110.3 S28N04W30BBB 820901 300 0 0 0 1 0 0 ---- (,.)111.0 S28N05W24DAD 820822 200 0 0 0 0 0 0 ---- ~111.0 S28N05W24DD 820606 4400 0 0 0 0 0 0 111.1 S28N05W24DAA 820822 120 0 0 0 0 0 0 ----- 111.9 S28N05W13DCC 820708 1000 1 0 0 0 0 0 ------ 111.9 S28N05W24ABD 820822 175 0 0 0 0 0 0 ----- 112.1 S28N05W13DCC 820822 20 0 0 0 0 0 0 ----- 112.3 S28N05W13CAC 820606 300 0 0 0 0 0 0 --- 112.3 S28N05W13CAC 820708 800 0 0 0 0 0 0 112.3 S28N05W13CAC 820916 450 0 0 0 0 0 0 --- 113.1 S28N05W12DAA 820822 20 0 0 1 0 3 0 113.5 S28N05W12DBA 820708 950 5 0 0 0 0 0 --- 113.6 S28N05Wl2ADD 820606 450 0 0 0 0 0 0 --- 113.6 S28N05W12ADD 820630 500 2 0 0 0 0 0 --- 113.6 S28N05Wl2ADD 820708 600 12 0 0 0 0 0 --- ---------------------------------------------------------------------------------------------------- )\ ~__I ,;I J ~t 1 i J I J J fi J ~J I )~_....'1 ·••·1 ~I J I I J J iJ-- ))-i, Appendix Table 2-F-l.Continued. ,-----~-----------------------------------------------------------------------------------------------C AT C H ------------------------------------------------- DISTANCE AD U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED -------------------------------------------------------------------------------------------------------- 113.6 S28N05Wl2ADD 820728 200 0 0 0 0 0 0 ------- 113.6 S28N05Wl2ADD 820813 500 1 0 350 25 0 0 ------- 113.6 S28N05Wl2ADD 820822 250 0 0 999 -999 2 0 ------- 113.6 S28N05Wl2ADD 820902 300 0 0 0 0 30 0 ------_. 113.6 S28N05Wl2ADD 820914 300 0 0 0 1 8 0 ------- 113.6 S28N05Wl2ADD 820918 400 0 0 0 0 0 0 ------- 113.6 S28N05W12DBA 820908 250 0 0 0 0 4 0 ------- >114.2 S28N04W06CCC 820822 400 0 0 0 1 0 0 ------ I\)114.4 S28N04W06CAB 820606 600 0 0 0 0 J 0 -------Co!)114.4 S28N04W06CAB 820708 400 0 0 0 0 0 0 -------en 114.4 S28N04W06CAB 820822 40 0 0 0 3 0 ·0 ------- 114.4 S28N04W06CAB 820902 200 0 0 0 8 1 0 ------- 114.6 S28N04W06CBB 820822 100 0 0 0 0 0 0 ------- 115.4 S29N04W31DBD 820822 90 0 0 0 0 0 0 ------- 115.9 S29N04w31DBA 820914 300 0 1 0 0 0 0 ------- 115.9 S29N04W31DBD 820902 1700 0 0 0 1 11 0 ------- 115.9 S29N04W31DBD 820914 300 0 0 0 0 0 0 ------- 116.0 S29N04W32BCA 820822 300 0 0 0 6 0 0 ------- 116.2 S29N04W32BDC 820822 50 0 0 0 1 6 0 ------- 116.2 S29N04W32BDD 820902 30 0 0 0 0 5 0 ------- 116.7 S29N04W32ABB 820630 240 0 0 0 0 0 0 ------- 116.7 S29N04W32ABB 820728 100 2 0 0 0 0 0 ------- 116.7 S29N04W32ABB 820902 450 0 0 0 0 0 0 ------- 116.7 S29N04W32ABB 820918 400 0 0 0 0 1 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2~F~1.Continued. --------------------------------------------------------------------------------------------------------------- CAT C R ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO· MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 116.9 S29N04W29DBA 820821 450 0 0 0 1 0 0 ------- 117.2 S29N04W29DBB 820902 150 0 0 0 0 0 0 ------.... 111.6 S29N04W29AAA 820821 150 0 0 0 0 0 0 ------ 117.8 S29N04W21CCB 820914 150 0 0 0 0 0 0 ------- 118.1 S29N04W21CCB 820902 350 0 0 0 0 0 0 ----- 118.9 S29N04W21BAD 820902 450 0 0 0 0 0 0 ------- 119.0 S29N04W16DCC 820918 200 0 0 0 0 0 0 ------ >119.0 S29N04W21BAC 820821 300 0 0 0 3 0 0 ------- I\)119.7 S29N04W16DBA 820821 175 0 0 0 4 0 0 ------- (,I)119.7 S29N04W16DBA .820902 300 0 0 0 0 0 0 ----- 0)119.8 S29N04W16ABB 820821 800 0 0 0 5 0 0 __-.--a_ 119.8 S29N04W16DAB 820821 0 0 0 0 0 0 ---- 120.0 S29N04W09DCC 820902 900 0 0 0 0 1 0 ------- 120.3 S29N04W16AAC 820902 200 0 0 0 0 0 0 ----- 120.4 S29N04W16AAc 820821 350 0 0 1 1 0 0 ---- 120.7 S29N04W10BCD 820630 75 1 0 0 0 0 0 ---_.- 120.7 S29N04W10BCD 820726 50 0 0 0 0 0 0 ------ 120.9 S29N04W10BCD 820821 100 0 0 0 0 0 0 ----- 121.0 S29N04W10BDA 820821 250 0 0 0 4 0 0 ---- 121.0 S29N04W10BDB 820902 250 0 0 0 0 0 0 ------- 121.4 S29N04W10ABA 820821 150 0 0 1 5 0 0 ----- 121.7 S29N04W03DCD 820821 90 0 0 0 1 0 0 ----..-- 121.8 S29N04W02CCA 820630 100 0 0 0 0 0 0 ------ 121.8 S29N04W02CCA 820728 125 0 0 0 0 0 0 ----- --------------------------------------------------------------------------------------------------------------- I J ).J!I J ,t ,),)I B ])J , ~}I :~--1 ~-.1 ) j 1 I 1 ) I 1 Appendix Table 2-F-l.Continued. ------------~-----------------~---------------------------------------------~----------~-----------------CAT C H ---------------------------------------------- DISTANCE A D U L T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO HILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ,--------------------------------------------------------------------------------------------------~---- 121.9 S29N04W03DDB 820821 250 0 0 1 2 0 0 ------- 122.2 S30N03W09DCB 820630 250 1 0 0 0 0 0 ------- 122.2 S30N03W09DCB 820728 150 0 0 0 0 0 0 ------- 123 .0 S30N04W35DBD 820821 350 0 0 0 1 0 0 ------- 123 .3 S30N04W35ACD 820821 200 0 0 0 8 2 0 ------- 123 .5 S30N04W35DBA 820820 150 0 2 0 6 0 0 ------- 123 .6 S30N04W35DBA 820813 150 0 0 2 5 0'0 ------- »123.7,S13N04W26DDC 820907 250 0 0 0 0 1 0 ------- I\)123.7 S30N04W26DDC 820630 120 0 0 0 0 u 0 ------- ('A)123.7 S30N04W26DDC 820726 50 1 0 0 0 0 0 -------......123.7 S30N04W26DDC 820812 200 0 0 18 0 0 0 -------- 123.7 S30N04W26DDC ,820820 200 0 0 10 0 0 0 ------- 123.8 S13N04W35DBA 820907 100 0 0 0 0 1 0 ------ 123 .8 S30N04W35ACA 820820 350 0 0 0 21 0 0 ------- ~124.1 S30N04W35ABD 820820 400 0 0 0 3 0 0 ------- 124.4 S30N04W35AAA 820820 800 0 0 0 9 1 0 ------- 124.7 S13N04W25DBC 820907 500 0 0 0 2 0 0 ------- 124.7 S30N04W25DBC 820629 450 0 0 0 0 0 0 ------- 124.7 S30N04W25DBC 820726 150 0 0 0 0 0 0 ------- 124.7 S30N04W25DBC 820812 200 0 0 18 0 0 0 ------- 124.7 S30N04W25DBC 820819 300 0 0 1 14 0 0 ------- 124.7 S30N04W25DBC 820920 150 0 0 0 0 1 0 ------- 125.3 S30N03W30BCD 820629 400 0 0 0 0 0 0 ------- 125.3 S30N03W30BCD 820726 150 0 0 0 0 0 0 ---._--- ---------------~-----------------------------------------------~----------------------------------------------- Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CAT C H --------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 125.3 -S30N03W30BCD 820812 200 :0 60 -24 5 0 0 ------. 125.3 S30N03W30BCD 820819 200 0 15 2 18 1 0 ------- 125.3 /S30N03W30BCD 820907 100 0 4 0 6 7 0 ---- 125.3 S30N03W30BCD 820920 200 0 0 0 0 0 0 ------- 125.6 S30N03W19CCD 820819 300 0 0 0 0 0 0 ------ 126.3 S30N03W19DAC 820819 125 0 2 0 25 1 0 ------- 126.5 S30N03W20BCC 820819 250 0 0 0 24 0 0 ----~--»-126.5 S30N03W20BCC 820907 200 0 0 0 0 0 0 ----- N 126.7 S30N03W20BCD 820819 250 0 0 0 2 0 0 ----- Col)127.0 S13N03W20BDB 820907 350 0 0 0 0 0 0 ------- CJ)127.1 S30N03W20BDB 820819 150 0 0 0 0 0 0 ------ 127.5 S30N03W20ACD 820819 75 0 0 0 0 0 0 ----- 127.6 .S30N03W20AA 820812 450 0 0 2 4 0 0 ------ 127.8 S30N03W20AAD 820819 150 0 0 0 0 0 0 ------ 128.3 S30N03W16AcB 820726 200 0 0 0 0 0 0 ------- 128.5 S30N03W16BBC 820819 250 0 0 0 0 1 0 ------ 128.6 S31N03W16BCA 820907 0 0 0 0 0 0 ------ 129.1 S30N03W16BAA 820629 850 0 0 0 0 0 0 ------ 129.2 S30N03W09CCA 820819 200 .0 0 2 15 0 0 ---- 129.3 S30N03W09CA 820629 250 0 0 0 0 0 0 ------ 129.4 S30N03W09CDB 820819 400 0 0 1 2 0 0 ----- 129.4 S30N03W09CDB 820907 250 0 0 0 1 0 0 ------- 129.8 S30N03W09DAB 820914 0 0 0 0 0 0 ------ 130.0 S30N03W09ABD 820629 270 0 0 0 0 0 0 ------- --------------------------------------------------------------------------------------------------------------- ")\,4' 11 J j I J J I ~I I I I ,I J J J ~J 11 --1 I ]1 »1 1 -Jj ))) Appendix Table 2-F-l.Continued. ------------------------------------------------------------------------------------------------------- CAT C H ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------- 130.1 S30N03W04DDD 820819 350 0 0 0 2 0 0 ------ 130.1 S30N03W04DDD 820907 150 0 0 0 1 0 0 ------- 130.4 S30NQ3W09AC 820812 350 0 0 20 26 0 0 ------- 130.8 S30N03w03DCC 820629 200 0 0 0 0 0 0 ------- 130.8 S30N03W03DCC 820728 100 0 0 0 0 0 0 ------- 130.8 S30N03W03DCC 820810 75 0 0 4 3 0 0 ------ 130.8 S30N03W03DCC 820812 75 0 0 0 2 0 0 ------- »130.8 S30N03W03DCC 820817 100 0 0 2 1 0 0 ------- I\)130.8 S30N03W03DCC 820907 150 0 0 0 0 iJ 0 ------- (A)131.1 S30N03W03DAA 820820 80 0 0 0 3 0 0 ------ CO 131.1 S30N03W03DAC 820628 400 1 0 0 0 0 0 ---...--- 131.1 S30N03W03DAC 820629 220 1 0 0 0 0 .0 ------- 131.1 S30N03W03DAC 820726 200 1 0 0 0 0 0 ------- 131.1 S30N03W03DAC 820812 300 1 0 48 56 1 0 ------ 131.1 S30N03W03DAC 820817 200 0 0 0 60 0 0 ------- 131.1 S30N03W03DAC 820908 400 0 0 0 25 8 0 ------- 131.1 S30N03W03DAC 820917 400 0 0 0 0 0 0 ----_._- 131.1 S30N03W03DAD 820817 250 0 0 2 50 0 0 ------- 131.3 S30N03W03DAD 820819 80 0 0 0 3 0 0 ------- 131.3 S30N03W03DAD 820904 200 0 0 0 4 0 0 ------- 131.8 S30N03W02CAB 820817 550 0 0 3 15 1 0 ------- 132.3 S30N03W01BAA 820904 100 0 0 0 1 0 0 ------- 132.3 S30N03W02CAA 820812 500 0 0 5 19 1 0 ------- 132.6 S30N03W01BBD 820817 150 0 0 0 2 0 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2~F-l.Continued. -------------------------------~-----------------------------------~----.--------------------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO ctsco OBSERVED ---------------------------------------------------------------------------~----------------------------------- 133.3 S31N03W36DBC 820817 350 0 -0 -2 6 0 0 ------ 133.3 S31N03W36DBD 820817 200 0 0 2 3 0 0------- 133.3 S31N03W36DBD 820904 450 0 0 0 0 1 .0 ---...._- 133.6 S30N03W36DAA 820629 100 0 0 0 0 0 0------- 133.8 S31N03W36AAC 820628 480 0 0 0 0 0 0 ------- 133.8 S31N03W36AAC 820810 75 0 0 1 0 0 0 ------- 133.8 S31N03W36AAC 820817 50 0 0 0 2 0 0 ------->133.8 S31N03W36AAC 820917 100 0 0 0 0 0 0 ------- (\)134.2 S31N03W30DCD 820812 250 0 0 19 17 2 0 -----~134.2 S31N03W30DCD 820817 250 0 0 2 6 2 00 ------ 134.2 S31N03W30DCD 820904 50 0 0 0 0 0 0 ------ 135.0 S31N03W30ACB 820628 220 0 0 0 0 0 0 ------ 135.1 S31N03W30AAB 820628 1760 3 0 0 0 0 0 ------ 135.1 S31N03W30AAB 820904 500 0 0 0 0 0 0 ------ 135.2 S31N02W19DDB 820817 800 0 0 0 4 1 0 ---- 135.2 S31N02W19DDB 820919 100 0 0 0 0 0 0 ------ 135.2 S31N02W30ABB 820812 500 0 0 8 20 0 0 ----- 135.3 S31N02W19DDD 820628 300 0 0 0 0 -0 0 --- 135.3 S31N02W19DDD 820124 100 0 0 0 0 0 0 ----- 135.3 S31N02W19DDD 820904 150 0 0 -0 35 0 0 --- 135.4 S13N02W19DCA 820124 50 0 0 0 0 0 0 ---- 135.1 S31N02W19DAB 820811 350 0 0 5 3 0 0 135.7 S31N02W19DCD 820124 15 0 0 0 0 0 0 --- 135.1 S31N02W19DCD 820812 80 0 0 0 0 0 0 ----- ----------------------------------------------------------------------------------------~--------------------- l .~,i J J .J I j I I :1 I !J I J ~J J 1 ) i J J "1 -I ) .I Appendix Table 2-F-l.Continued. --------------------------------------------------------------------------------------------------------------- CATCH ------------------------------------------------- DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ,-------------------------------------------------------------------------------------------------------- 135.9 S31N02W19ACA 820628 140 1 0 0 0 0 0 ------ 135.9 S31N02W19ACA 820724 100 1 0 0 0 0 0 ------- ,136.0 S31N02W19AD 820629 3500 1 0 0 0 0 0 ------- 136.0 S31N02W19AD 820812 400 0 0 20 14 4 0 ------ 136.0 S31N02W19AD 820904 150 1 0 '0 50 0 0 ------- 136.2 S31N02W20BBC 820817 300 0 0 1 50 1 0 ------- 136.6 S31N02W20BBD 820817 300 0 0 0 25 0 0 ------- 136.7 S31N02W20ABB 820816 50 0 0 0 8 0 0 ------->136.9 S31N02W17DCC 820819 200 0 0 0 25 0 0 -------I\) -I=ioo 137.2 S13N02W17BDC 820905 150 0 0 0 0 3 0 ------- .....137.2 S31N02W17BDC 820628 350 1 0 0 0 0 0 ------- 137.2 S31N02W17BDC 820724 175 0 0 0 0 0 0 ------- 137.2 S31N02W17BDC 820811 250 1 0 50 13 0 0 .------- 137.2 S31N02W17 BDC 820816 50 0 0 3 20 1 0 ------- .137.2 S31N02Wi7BDC 820915 200 0 0 ~O 0 0 0 -----_.- 137.4 S31N02W17DBB 820906 0 0 0 2 0 0 ------- 137.7 S31N02W17ABD 820628 400 0 1 0 0 0 0 ------- 137.7 S31N02W17ABD 820727 50 0 0 0 0 0 0 ------- 137.7 S31N02W17BDD 820912 350 0 0 0 0 0 0 ------- 138.3 S31N02W16BBA 820627 250 0 0 0 0 0 0 ------- 138.3 S31N02W16BBA 820811 200 0 0 8 6 1 0 ------- 138.3 S31N02W16BBD 820819 250 0 0 2 50 0 0 ------- 138.6 S13N02W09CDA 820905 200 0 0 0 100 5 0 ------- 138.6 S31N02W09CDA 820628 650 8 0 0 0 0 0 ------- --------------------------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. -----------------------------------------~-------,----~---------------------------~----------------------------CAT C H ------------------------------------------------- DISTANCE A D U L T S A LM 0 N BERING RIVER SHOCKED ---'-,-------'------------_.------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED ----~---------------------------------------------------------------------------------------------------------- 138.6 S31N02W09CDA 820724 350 1 0 0 0 0 0 ------ 138.6 S31N02W09CDA 820810 250 1 0 65 33 0 0 ------- 138.6 S31N02W09CDA 820816 250 0 0 100 300 2 0 ------ 138.6 S31N02W09CDA 820817 20 0 0 20 30 0 0 ------- 138.6 S31N02W09CDA 820917 400 0 0 0 0 0 0 ------ 138.6 S31N02W09CDA 820918 800 0 0 0 1 0 0 ------- 138.6 S31N02W09CDA 820919 600 0 0 0 1 6 0 -------»138.6 .S31N02W09CDA 820920 150 0 0 0 0 0 0 -------J\)138.6 S31N02W09CDA 820921 350 0 0 0 0 0 0oil-------- J\)138.9 S31N02W09DBD 820627 340 0 0 0 0 0 0 ------- 138.9 S31N02W09DBD 820727 75 0 0 0 0 0 0 ------- 138.9 S31N02W09DBD 820906 0 0 0 0 0 0 ------- 138.9 S31N02W09DBD 820918 100 0 0 0 0 0 0 ------- 139.3 S31N02W01DDB 820906 200 0 1 0 0 1 0 ------- 139.3 S31N02W10CBC 820819 350 0 0 0 60 0 0 ------- 139.3 S31N02W10CBC 820906 150 0 0 0 0 0 0 ------- 139.5 S31N02W10DDA 820906 150 0 0 0 0 0 0 ------- 139.5 S31N02W10DDA 820907 200 0 0 0 1 0 0 ------- 139.5 S31N02W10DDA 820918 .120 0 0 0 0 0 0 ------- 139.7 S31N02W10DBD 820627 150 0 0 0 0 0 0 ------- 140.0 S31N02W10DCA 820819 75 0 0 0 0 0 0 ------- 140.1 S31N02W10ACD 820819 150 0 0 2 2 0 0 ------ 140.1 S31N02W11BBC 820727 50 0 0 0 0 0 0 ------- 140.1 S31N02W11BBC 820811 250 0 0 21 15 0 0 ------- --------------------------------------------------~------------------------------------------------------------,\ I J I J I J ~,~"I J 1 )]J J II J t 1 J j J 1 J .~ ))(I " Appendix Table 2-F-l.Continued. ~------------------------------------------------------------------------------------------------------ CAT C H --------------------------~---------------------DISTANCE A D U L T SALMON BERING RIVER SHOCKED ---------------------~--------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO .CISCO OBSERVED ----------------.--------------------------------------------------------------------------------- 140.1 S31N02W11BBC 820818 200 0 0 0 10 0 0 ------- 140.1 S31N02WllBBC 820905 200 0 0 0 4 1 0 ------- 140.1 S31N02W11BBC 820919 400 0 0 0 0 0 0 ------- 140.5 S31N02W01ADB 820818 400 0 0 4 20 0 0 ------- 140.5 S31N02W02ABB 820811 250 0 0 1 3 0 0 ------- 141.4 S31N02W02ABB 820627 200 0 0 0 0 0 0 ------- 141.8 S21N02W02AAB 820905 250 0 0 0 1 0 0 ------- 141.8 S31N02W02AAB 820818 350 0 0 5 300 1 0 ------- >141.8 S31N02W02AAB 820923 100 0 0 0 0 fJ 0 ------- I\)142.0 S31N02W02AAA 820627 200 0 0 0 0 0 0 ------- -I:lo 142.0 S31N02W02AAA 820727 150 0 0 0 0 0 0 ------- Ca)142.0 S32N02W35DDC 820818 350 0 0 5 17 0 0 ------- 142.2 S32N02W36CBD 820905 350 0 0 0 0 0 0 ------- 142.5 S32N02W31CBA 820818 200 0 0 0 25 1 0 ------- 142.7 S32N02W31BCA 820818 300 0 0 0 7 0 0 ------- 143.0 S32N02W36ADD 820811 400 0 0 6 17 0 0 ------- 143.0 S32N02W36DAA 820905 230 0 0 0 1 0 0 ------- 143.1 S32N02W36ADA 820627 150 2 0 0 0 0 0 ------- 143.5 S32NOIW31BCA 820811 150 0 0 1 2 0 0 ------- 143.5 S32NOIW31BCA 820905 250 0 0 0 0 0 0 --._--- 143.8 S23N01W32BDB 820923 150 0 0 0 0 0 0 ------- 144.3 S32N01W32BBC 820923 300 0 0 0 0 0 0 ------- 144.5 S32N01W32ACA 820727 1200 2 0 0 0 0 0 ------- 144.5 S32N01W32ACA 820811 250 2 0 14 6 3 0 ------- -------------------~------------------------------------------------------------------------------------------- Appendix Table 2-F-l.Continued. ---~-----------------------------------------------------------------------------------------~-------~--------CAT C H ------------------------------------------------- DISTANCE AD U L T SAL M0 N BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO CISCO OBSERVED --------------------------------------------------------------------------------------------------------------- 144.5 S32N01W32ACA 820818 450 .0 0 4 15 30 0 ------- 144.5 S32NOIW32ACA 820905 300 0 1 0 1 10 0 ------- 144.5 S32NOIW3-2ACA 820919 400 0 0 0 ~0 0 0 ------ 145.0 S32N01W32ADB 820627 500 0 0 0 0 0 0 ------ 145.0 S32N01W32ADB 820811 600 0 0 4 12 ·0 0 ------ 145.2 S32N01W33BBD 820818 200 0 0 0 0 0 0 ------ 145.4 S32N01W32ADB 820905 400 0 0 0 0 0 0 ------ >147.2 S32N01W27DAC 820905 300 0 0 0 0 1 0 ------- I\,)147.2 S32N01W27DAC 820923 250 0 0 0 0 0 0 ------ ~147.6 S32N01W26BDC 820818 225 0 3 2 25 0 0 ----- ~147.6 S32N01W26CB 820627 440 1 0 0 0 0 0 ---- 147.6 S3 2NO 1W26 CB 820811 175 0 0 10 3 0 0 ----- 147.6 S32NOIW26CB 820818 800 0 0 2 30 0 -0 ---- 147.6 S32NOIW26CBA 820905 150 0 0 0 3 0 0 ----- 148.0 S32N01W26DCB 820818 75 0 0 1 35 0 0 ----- 148.2 S32N01W26DCA 820818 125 0 0 0 400 0 0 --- 148.2 S32N01W26 DCA 820905 100 0 1 0 4 ·1 0 ----- 148.2 S32N01W26DCB 820923 40 0 0 0 0 0 0 ----- 148.8 S32NOIW25CBD 820727 350 10 0 0 0 0 0 ---- 148.8 S32N01W25CBD 820905 450 0 0 0 10 5 0 ---- 148.8 S32N01W25CDB 820627 440 2 0 0 0 0 0 --- 148.8 S32N01W25CDB 820811 450 3 0 40 30 1 0 ---- 148.8 S32N01W25CDB 820818 500 0 0 0 78 3 0 ---- 148.8 S32NOIW25CDB 820921 400 0 0 0 0 0 0 ------ ----------------------------------------------------~---------------~---------------------------------------- ~tI.1 •t j .~cl I ~J i I J J J J ~J j~ Appendix Table 2-F-l.Continued. --J )•] CAT C H J I J 1 I \} ------------------------------------------------- DISTANCE AD U L T SALMON BERING RIVER SHOCKED ---------------------------------------BERING CISCO MILE GEOCODE DATE (YDS)CHINOOK SOCKEYE PINK CHUM COHO ·CISCO OBSERVED -------------------------------------------------------------------------------------------------------- 150.1 S32NOIE31CBD 820627 340 0 0 0 0 0 0 ------- 150.1 S32NOIE31CBD 820921 50 0 0 0 0 0 0 ------- 150.4 S32NOIE31DCB 820811 150 0 0 2 5 0 0 ------- 150.4 S32NOIE31DCB 820818 200 0 0 1 12 0 0 ------- 150.4 S32NOIE31DCB 820905 200 0 0 0 0 1 0 ------- 150.4 S32NOIE31DCB 820923 100 0 0 0 0 0 0 ------- »----------------------------------------------------------------------------------~~--------------------------- ~ ~ ~ Appendix Table 2-F-2.Summary of mainstem Susitna River sampling using gill nets and visual inspection, Adult Anadromous Investigations,Su Hydro Studies,1982 Catch River Method 1/Oi stance Y Ch i nook Adu 1t Sa'man Bering Mile Legal Date Sockeye Pink Chum Coho Cisco 8.5 S15N07W18ACB 820809 VI 100+0 0 0 0 0 0 17.7 S16N07W22AAB 820811 SN 4 min.0 0 0 1 0 0 17.9 S16N05W150CO 820811 ON 250 0 0 0 0 0 0 20.0 S16N07W090AC 820811 SN 8 min.0 0 0 0 0 0 23.8 S17N07W33ACB 820811 ON 50 0 0 0 0 0 0 24.8 S17N07W27BCC 820811 ON 60 0 0 0 2 0 0 27.1 S17N07W23AAA 820811 SN 6 min.0 0 0 0 0 0 27.8 S17N07~Jl30CC 820811 SN 3 min.0 0 0 0 ~0 0 29.0 S17N07,W13AAA 820811 ON 400 0 0 0 0 0 0 29.6 S17N06W070CB 820811 ON 30 0 0 0 0 0 0 30.9 S17N06W08AAB 820811 ON 75 a 0 0 0 0 0 31.1 S17N06W05CBA 820810 SN 15 min.0 0 0 0 2 0 31.1 S17N06W05CBA 820812 SN 10 min.0 0 1 0 1 0 31.2 S17N06W05CAO 820812 ON 20 0 0 0 0 0 0 »31.5 S17N06W05ACO 820812 ON 15 0 0 O.0 0 0 I\)31.7 S17N06W04CBC 820811 ON 100 0 a 0 0 a 0 ~31.8 S17N06W04CAB 820814 ON 80 0 0 0 0 0 0 0)32.0 S18N06W320CA 820812 SN 15 min.D 0 0 0 0 0 33.1 S18N06W33ABB 820812 ON 75 0 a 0 0 0 0 33.1 S18N06W34BBA 820814 ON 40 0 0 0 0 0 0 33.5 S18N06W28COO 820812 ON 70 0 0 0 0 a 0 34.1 S18N06W34BBA 820812 ON 50 0 0 0 0 0 0 34.5 S18N06W27BCC 820814 ON 40 0 0 0 0 0 0 35.0 S18N06W27BBA 820814 ON 20 0 0 0 0 0 0 36.0 S18N06W22BBB 820814 ON 50 0 0 0 0 0 0 36.2 S18N06W16000 820814 ON 90 0 0 0 2 a a 37.1 S18N06W15BAO 820814 ON 40 0 0 a a a 0 37.1 S18N06W15BAA 820814 ON 45 0 0 0 0 0 0 38.3 S18N06Wll BOA 820814 ON 55 a 0 0 0 2 a 40.0 S18N06W02ABO 820810 ON 250 a 0 0 0 1 0 40.0 S18N06W02AAB 820814 ON 100 0 0 0 0 0 0 ·42.0 S19N06W25BOA 820810 ON 200 0 0 0 0 1 0 51.0 S20N05W21BCB 820815 SN 10 min.0 0 0 0 5 0 l \ ,I j I I )J ,~.1 J I J ]~J J ,I J J ~y ~-~1 ~--I j 1 ~l 1 1 1 J 1 1 1 1 J )) Appendix Table 2-F-2.Continued. Catch River Method 11 Distance ~Chinook Adult Salmon Bering Mile Legal Date Sockeye Pink Chum Coho Cisco 53.1 S20N05W09DCC 820810 ON 65 a a a 5 a a 56.2 S21 N051434DCC 820810 ON 60 a 0 a a a a 59.3 S21N05W23BCB 820815 ON 30 a a a a a 0 60.0 S21N05W14DDB 820815 ON 45 a a a a 1 a 106.3 S27N05W12CCC 820823 VI 400 a a a a 0 0 107.5 S27N05W12BBA 820823 VI 600 a a a a a a 107.5 S27N05W12BBA 820901 VI 600 a a a a a a 109.8 S28N04W30CCD 820911 VI 400 a a a a a 0 11 0.1 S28N04W30CBB 820901 VI 900 a a a 0 a 0 110.1 S28N04W30CBB 820911 VI 900 a a a a a a 111 .6 S28N05W24ADB 820822 ON 200 a a a a a a 114.3 S28N04W06CCB 820927 VI 800 a a a a a a 114.4 S28N041406CAB 820902 VI 700 a a a 10 a 0 117.2 S29N04W29DBB 820902 VI 150 a a a a a a 117.7 S29N04W28BBD 820813 VI 200 a a 12 15 a a >117.7 S29N04W28BBO 821002 VI 200 a a a a 8 a I\)117.8 S29N04W29AAB 820902 VI 500 a a a 0 a a ~117.8 S29N04W29AAB 820924 VI 600 0 a a a a O·....125.2 S30N04W25AD-820928 VI 1000 a a a a a a 125.6 S30N03W30BAD 820924 VI 400 a a a /a a a 125.9 S30N03Wl9CDO 820912 VI 300 a a a a a a 125.9 S30N03~!l9CDD 820920 ON 100 a a a a a a 125.9 S30N031419CDD 820928 VI 300 a a 0 a a a 126.8 S30N03W20BAC 820928 VI 150 a a a a a a 127.8 S30N03W20AAB 820912 VI 200 a 0 a a a a 127.8 S30N03W20AAB 820920 VI 200 a a a a a a 128.6 S30N03~Jl6BCA 820905 VI 200 a a a 10 a 0 128.6 S30N03W16BCA 820907 VI 200 a a a 7 a a 128.8 S30N03W16BBA 820920 ON 150 a a a a a a 129.8 S30N03W09DAB 820912 VI 800 a a a 5 a a 130.1 S30N03W04DDD 820912 VI 100 a a 0 a 0 a 130.1 S30N03W04DDO 820912 SN 20 min.a a 0 a a a 130.1 S30N03W04DDD 820919 ON 200 a a a a a a 130.1 S30N03Wl0BCA 820920 ON 100 a a a a a a Appendix Table 2-F-2.Continued. -----Catch River Method 11 Distance ~Chinook Adult Salmon Bering Mile Lega 1 Date Sockeye Pink Chum Coho'Cisco 130.1 S30N03Wl0BCA .820928 VI 500 0 0 0 0 0 (J 131 .3 S30N03W03DA-820904 VI 100 0 0 0 12 0 0 131.3 S30N03W03DA-820904 SN 45 min.0 0 0 5 0 0 131 .3 S30N03W03DA-820919 ON 120 .0 0 0 0 0 0 131 .5 S30N03W03DAA 820919 VI 500 a 0 0 0 0 0 132.8 S30N03W02B--820912 VI 1500 ,0 0 0 0 0 0 .134.2 S31N03W30DCD 820919 DN 100 0 0 0 1 0 0 135.0 S31N02W30DBB 820904 VI 150 0 0 0 0 0 0 135.2 .S31N02W30BAA .'820902 VI 200 0 0 0 0 0 0 136.0 S31N02W19AD-820904 VI 150 0 0 0 50 0 0 137.4 S31N02W17DBB 820828 VI 150 0 0 0 1 0 0 137.4 .S31 N02W17DBB 820903 VI 150 0 0 0 4 0 0 137.4 S31N02W17DBB 820905 VI 150 0 0 0 14 0 0 >137.4 S31N02W17DBB 820913 VI 100 0 0 0 0 0 0 138.2 S31N02W16BBB 820927 VI 200 0 0 0 0 0 0I\)138.9 S31N02W09DBD 820904 VI 200 0 0 0 16 0 0~ (X)138.9 S31N02W09DBD 820906 VI 200 ·0 0 0 14 0 0 138.9 S31N02W09DBD 820907 VI 200 0 0 0 17 0 0 139.4 S31N02Wl0CAB 820927 VI 300 0 0 0 0 0 0 139.5 S31N02Wl0DDA 820906 VI 250 0 0 0 0 0 0 139.5 S31N02Wl0DDA 820913 SN 30 min.0 0 0 0 0 0 139.~S31N02W10DDA 821002 VI 400 0 0 0 0 0 0 141.8 S31N02W02AAB 820906 SN 20 min.0 0 0 0 0 0 142.5 S32N02W31CBA 820923 VI 400 0 0 0 0 0 0 143.1 S32N02W36ADA 820923 VI 100 O'0 0 0 0 0 143.3 S32N01W31BCB 820904 VI 100 0 0 0 22 0 0 143.3 S32N01W31BCB 820905.VI 100 0 0 0 15 0 0 143.3 S32N01W31BCB 820923 .VI 100 0 0 0 0 0 0 143.9 S32N01W31ACB 820923 VI 300 0 0 0 0 0 0 144.0 S32N01W31ACD 820923 VI 100 0 0 0 0 0 0 144.7 S32N01W32BDC 820923 VI 100 0 0 0 0 0 0 1/Methods Noted:·VI =Visual Inspection SN =Set Gill Net ON =Drift Gill Net ~',Distance recorded in yards unless otherwise indir)ted., J J 1 ,t j ,J J I J )I J J I ~I J, ~.Appendix Table 2-F-3.Evaluation of tag loss based on spawning surveys conducted between Sunshine Station and Devil Canyon, Adult Anadromous Investigations,Su Hydro Studies, 1982. No.Tagged Total Percent Tag Type Taggin,g Fish No.Tags No.Tag Station Examined Shed Tags Retention FT-4/Spaghetti Sunshine 331 28 359 92.2 FT-4/Spaghetti Talkeetna 386 26 412 93.7 Petersen Disc Curry 325 3 328 99.1 A249 l. 2. 3. r 4. 5. ~6. APPENDIX 2-G SLOUGH AND STREAM LOCATIONS FROM R~1 98.6 TO 161.2 LOCATION OF CHEECHAKO AND CHINOOK CREEKS MAP OF SLOUGH B MAINSTEM SUSITNA RIVER SPAWNING SIiE MAPS ESCAPEMENT SURVEYS OF SLOUGHS AND STREAMS TAGGEDjUNTAGGED RATIOS FROM SPAWNING GROUND SURVEYS (•-River Mile I ......TALKEETNA STATION Whiskers Creek ~~~(l Appendix Figure 2-G-1.Slough locations and 'primary streams of the Susitna River from the confluence of the Talkeetna and Chulitna rivers to Upper Devil Canyon,Adult Anadromous Investigations,Su Hydro Studies,1982. A250 ~lough BC ....:Slough 8D ,.-River Mile I Mckenzie Creek Lower Mckenzie Creek Deadhorse Creek RM 120 -0(Moose Slough Filth of July Creek 110 Cnase Creek Oxbow Slougn 5 ~ 115 Lane Creek A Appendix Figure 2-G-l.Continued. Siougn 6A ~ ,~ ...., .-. .- - A251 RM 130 c Appendix o Sherman Creek Slough A252 AM RM 12 L!..-Rivor 11liJiJ Slougl1 9A -- """ ~, E .~Slough 21 Long Creek Portage Creek I •-River Mile I Devil Canyon Appendix Figure 2-G-l.Continued. A253 """ I--RIVER MILE) Appendix Figure 2-G-l. F Continued. _PROPOSED DEVIL CANYON DAMSITE RM 150 A254 - TALKEETNA I--5 River Mlle.l Appendix Figure 2-G-2.Location of Susitna River streams Cheechako and Chinook creeks above proposed Devil Canyon damsite, Adult Anadromous Investigations.SuHydro Studies, 1982. A255 > I\) en m EB River Iilfle 126 ----..:-.SUS /J""4',., '.':0::'• ..••-~"<.,.,,,..''''~"".""....~.,,.'..".•;:·,;,c.."'.'__,,<" "P/i-'/!""/i' .---- ",\):':'10· :":'_"""'~~1-".'~...~;0::._".'.~".......~~...J" o SOO I I I FEET 121 Appendix Figure 2-G-3.Slough B located at RM 126.3 approximately~Adult Anadromous Investigations, Su Hydro Studies,1982. l \ t ~I J •I j g J ~j J J 1 I m )J ~ J I I I I I 1 1 -1 1 1 J .~J )) o 500 I I I FEET "::.......:.~,..:~';~..;~_:::~:-:::~_....!..•:,........,..........-.... E9 Rlv.r mil. /' "f:~~\ t'l~ \'t /5 05> I\) c.n...., Appendix Figure 2-G-4.Mainstem Susitna River chum salmon spawning area at RM 114.4 approximately,Adult Anadromous Investigations,Su Hydro Studies.1982. Appendix Figure 2~G-5. J » I\) (1J CD ~ ~ J !l o 500 I I I FEET Mainstem Susitna River chum salmon spawning area at RM 128.6 approximately,Adult Anadromous Investigations,Su Hydro Studies,1982. ~\ ~l 1 ~D I ),1 J J ~,~ I I 1 j I )J J I 'I J -.I 1 I 1 ), » f\) en co .,,',_.." _,<.,,,.,,:,,.;""..".,"..".,,1"'''/' ~. ~. ~~ Co ~ "~ o 500 I • I FEET Appendix Figure 2-G-6.Mainstem Susitna River chum salmon spawning area at RM 129.8 approximately,Adult Anadromous Investigations,Su Hydro Studies,1982. >- I\) 0>o ,,~~ "~- ........~G-<~ '.'"'" SPAWNING AREA ~"':"_.~::,,4 ;,··..··:'~·r:·-:-._......'.;:.~::t ,:,,'.'"i ..-_'~..''_...... o 500 I I I FEET Appendix Figure ,J '~ I ~ 2-G-7.Mainstem Susitna River chum salmon spawning area at RM 131.3 approximately,Adult Anadromous Investi gations,Su Hydro Studi es,1982. )\ ~J t ,JI I Dig I J J l J 1 .i I J I 1 1 J J J 1 I ]...,1 5lJ))} o 500 I •I FEET Ii Ii 4 X en « ...J .4 ~';:':":: '";0"::;.... "_"c'-"",",.';.,c"!:.,~':",<,0'.' ·x":,' .f .. :." ~f(.')':~~.~ ~..., ~ IT'/Vc"p ------ '--.•'.'•',.".,',,":,"••,-~,':.;,.,-.'0 '",,:._-,.;_"'i'".'"_'".,.,~;'c .,,:-'•.c';, ~SU5ITNA .... » I\) 0> Appendix Figure 2-G-8.Mainstem Susitna River chum salmon spawning area at RM 136.0 approximately,Adult Anadromous Investigations,Su Hydro Studi es,1982.. EBRiver 11'111.138 »- N 0) N SIr N A S U R (V£R ~ ~;~.:.?:~':':.;0':'::::,::"'';',;:,:';;~'-"~i';:;.~~:'·/.:·,~t:.··:;,;::_:::":~':•• .':. .::~,..:~);'.."i"-"-:,;.:.~?,:.o;;;:'I;"~·,:.'.;-<:,:i'.:.",..'j';':.',::':-';:;':',:'; o 500 I I I FEET Appendix Figure 2-G-9. j1 '\ i1lI]I) River chum salmon spawning area at RM 137.4 and 138.2 approximately, Investigations,Su Hydro Studies,1982. ) ~IJJ Mainstem Susitna Adult Anadromous ) ..... !J!i 1 1 -,I J 1 1 I i 1 J i i i J )} '~.~".:-;.~;;:'.-l.'·:1 :,- RIVER.,SUSlrNA .....'.'";,"".~."."..",.,",,..'"''.........,:~,.......;;:;...;';i.:JI&,,,.,:~i<"'\'''''.."'",.,...""..".".. .'":fJi'• ••••",-••,....•,,,,..'.".".' _..,.d.8:-sL ~ ..:',:...~ » I\) 0) (,) $Rive'mile 139 o 500 I I I FEET Appendix Figure 2-G-1O.Mainstem Susitna River chum salmon spawning area at RM 138.9 approximately,Adult Anadromous Investigations,Su Hydro Studies,1982. » N 0'> ~ o 500 I I I FEET \ u '. ~a Sus /;>- /V-<1, "'P"t- ~"'P ~ .:0).:,. Appendix Figure 2-G-11.RM 143.3 approximately,Adult ~J i J 1 Mainstem Susitna River chum salmon spawning area at Anadromous Investigations,Su Hydro Studies,1982. } J ~J I I J ~J J J ]] , !) ,I I '.1 ~-l 1 I )))1 J ]j )) RIV ER -~SUSITNA ";:::~..:::.::,~ •,',r•.-'::.:_'j""",'j ':f';;'-''::'''~:''F''''.".<,~,~\,:,~,.;~"j'f~'":#.'.\:,'1';r .•,••':,'.;:;,;,.....,'.,~.,;;::. ,,,,,,.<",'.'f?'3''':,.",".",.,,,", _A '...... EBRI ..,mil.148 .~.~.. \~.:..:..I':r ··:i\. » I\) 0) 01 o 250 I •I FEET Appendix Figure 2-G-12.Mainstem Susitna River chum salmon spawning area at RM 148.2 approximately.Adult Anadromous Investigations.Su Hydro Studies.1982. ....:01.'• •.•j.:;;••::....••:.;•.:......,.::~,:~:.'.~ ., ::-~'''''.-.".. -'-~'.~'!;''':;.,![.i .......~;..:!.....:.;J':::;.;; '.~... EB Rive,mil.77/·..·.., BERING CISCO SPAWNI NG AREA !;":i;j:";".~;.:,,,,••:,.:;j._A ~~:,;.w. ~ \ '''";'' ":"::::":';'1:..,•.:..",.:•....."""'?,.~...,~ "9/J- ~""P S'vs /?'...-v- ~ , ---*---",..- o 500 I I I FEET » I\) 0) 0) Appendix Figure 2-G-13.spawning area at RM 76.8 approximately, Studies,1982.,J j ~J Mainstem Susitna River Bering cisco Anadromous Investigations,C:')Hydro I J i J I J J 1 J J ) Adult ._~ )1 ~ 1 J 'I 1 1 J 1 J 1 ]J J 1 i)~)j; .':.,. ';.:, o 500 I I FEET .'. ~'.':~-...:--" ":'...:- ..... .-=:"'.... "'.. ." .'"'.:.,~.. RIVER •~• "••'C'• •'.<":.-'•••:••".:'~":~:•• ..'".,'~:':}~<:.<:~'\.::}:~(7:;;'·<;:::',.~' ..~.~.:..-. .>••••~. '''<''\\''~;'"""";.-:;,~,:'":,,,,,,,,,,-.....-,••.••.•. SU S /?, 1%/4 I;.~/;{J.g:;(;;i;l;'·~j(\i';:!:"2;)~;·:;?i?/ ~ (..~ P;"• ..;":::;",:;;.~,--,~:;;:', "'(~':":; ....-:-,...~~ •.1::,.i. ,-=*,...,_,.•..,.J"!':J".~~:·~.'i;'1(;"-:';'i;-J·:r"·:":-1·,·.-."",;;~';';·":~;"'··'··jt:-::;s'.·.·yz;,·.,;· > I\) <»...., Appendix Figure 2-G-14.Mainstem Susitna River Bering cisco spawning area at RM 80.8 approximately,Adult Anadromous Investigations,Su Hydro Studies,1982. Appendix Table 2-G-l.Escapement survey counts of Susitna River sloughs between Talkeetna River and Devil Canyon,Adult Anadromous Investigations,Su Hydro Studies,1982. ROUll :lalmon Tnumerated _. River Survey Percent Chinook Sockeye Pink Chum Coho Slough Mile Date Conditions Surveyed Live Dead Iota 1 Live Dead Total Live Dead Total ,Live Dead Total Live Dead Total Slough 1 99.6 8/8 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 a 0 a a 8/13 Excell ent 100 a 0 a a a a a a 0 0 a a 0 a a 8/20 Good 100 0 a a 0 0 a 0 0 0 0 0 a a a a 8/26 Good 100 '0 a a a a a 0 0 a a 0 a 0 a .0 9/1 Good 100 0 0 0 0 a 0 a a 0 0 0 a I 0 a 0 9/29 Excellent 100 0 0 '0 0 0 a a a 0 a 0 0 a 0 c 10/25 Good 100 0 a a 0 a 0 0 a 0 a a 0 a a 0, Slough 2 100.2 8/8 Poor 100 I a a a a 0 0 0 0 a 0 a a a 0 0 8/13 Poor 100 a a 0 0 0 a a 0 0 I 0 0 a 0 a 0I 8/20 Good 100 a a 0 a 0 a a 0 0 [a a a a a 0 8/26 Good 100 0 a a a 0 0 0 a a a 0 0 a 0 0 9/1 Good 100 a a a a 0 0 0 0 a a a 0 a 0 a 9/29 Excellent 100 a a a a a 0 0 a 0 i 0 0 a 0 a a 10/25 Fair 100 a a a a a 0 a 0 0 ,a 0 a a 0 ai Slough 38 101.4 8/8 Excellent 100 0 a a 0 a 0 0 0 0 0 0 0 a 0 0 8/13 Poor 100 a a 0 '0 0 0 a 0 a 0 a a a a 0 8/23 Good 100 a a a 0 0 0 a a a a 0 0 0 0 0 9/1 Good 100 0 a a a a 0 a 0 a 0 a a 0 0 a 9/7 Excellent 100 0 a a a a a 0 0 a 0 a 0 0 0 0 9/21 Good 100 0 0 0 0 0 0 0 0 0 0 0 0 a 0 0 9/29 Excellent 100 a a a 0 a a 0 a a 0 a a 0 0 a 10/25 Good 100 a a 0 0 0 o .'a 0 a a a 0 0 0 a '. Slough 3A 101.9 8/8 Excellent 100 a a a 0 a 0 0 a 0 I 0 a 0 0 0 0 8/13 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/20 Good 100 0 0 0 0 0 0 0 0 a 0 0 0 0 0 0 9/1 Good 100 0 0 0 0 0 0 a a 0 I 0 0 0 0 0 aI 9/7 Excellent 100 a a a 0 0 0 0 0 0 I 0 0 0 0 0 0 9/21 Good 100 0 0 0 0 0 0 a 0 0 I 0 0 a 0 0 0 10/25 Good 100 a a a a 0 0 0 0 0 I a a 0 0 0 0I Slough 4 105.2 8/13 Poor 100 0 0 0 0 0 0 0 0 o I 0 a 0 I 0 0 0 8/19 Poor 100 0 0 0 0 0 0 0 0-0 0 0 0 a 0 0 8/26 Poor 100 0 0 0 0 0 0 0 0 0 I 0 0 0 0 0 0 9/1 Poor 100 0 0 0 0 a a a a a 0 a 0 0 0 0 \"i- > I') Q) CD 1 J J )J ,I l )~1 t J )j\~~ J j 1 J I 1 I I I l 1 l i j 1 I 1 J 1 J )) Appendix Table 2-G-l.Continued. >- N 0), co AO Ult 5almon tnumerated River Survey Percent Chinook Sockeye P,nk Chum Coho Slouqh Mile Date Conditions SurveYed ive Dead Total Live Dead Total Live Dead Total Live Dead Total Live Dead Total Slough 4 9/7 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/21 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/29 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10/25 Good 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Slough 5 107.6 8/7 Good 100 0 0 0 0 0 0 0 0 0 2 0 2 0 0 0 8/13 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/19 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/26 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/1 Good 100 0 a 0 a a 0 a a a a a a a a a 9/7 Good 100 a 0 a a a a a 0 a 0 a a a a a 9/21 Good 100 a a a 0 a 0 a a a 0 0 0 a a a 10/25 Poor 100 0 0 0 a a a a a a a a a a 0 a Slough 6 108.2 8/13 Poor 100 a 0 a 0 a 0 0 a a 0 0 a 0 a a 8/19 Good 100 0 0 0 0 a 0 0 a 0 a 0 0 0 a a 8/26 Good 100 a 0 0 0 G 0 0 0 0 a a 0 0 0 a 9/1 Good 100 0 0 0 a a 0 0 0 0 0 0 a 0 a 0 9/7 Good 100 0 0 a a a 0 a a 0 a a 0 0 0 0 9/21 Good 100 0 0 0 a a a 0 0 a 0 0 0 a a 0 10/25 Fair -100 0 0 0 0 a 0 0 a a 0 a 0 0 0 0 Slough 6A 112.3 8/7 Poor 100 0 0 0 0 o ,0 35 0 35 a 0 0 a a 0 8/13 Excellent 100 0 0 a 0 0 0 0 a a 0 a a 0 0 a 8/19 Excellent 100 0 a 0 0 0 0 0 0 0 a 0 0 35 0 35 8/25 Excellent 100 0 0 a a 0 0 0 1 1 1 1 2 29 1 30 8/31 Excellent 100 0 0 0 a a a 0 a 0 0 0 0 0 a a 9/7 Excellent 100 0 a 0 0 0 0 0 a 0 a 0 0 0 a 0 9/14 Excellent 100 0 0 0 0 0 0 0 0 a 1 a 1 a 0 0 9/21 Excellent 100 0 0 0 0 a 0 0 0 0 a 0 0 a a 0 9/27 Excellent 100 0 a 0 a a a 0 a 0 a a a a a a 10/25 Good 100 0 0 a 0 0 0 0 a a 0 0 0 a 0 0 Slough 7 113.2 8/8 Excellent 100 a a 0 0 0 a a 0 0 a 0 0 0 0 a 8/13 Excell ent 100 0 0 0 0 0 0 a 0 0 0 0 0 a 0 0 8/19 Excellent 100 0 a 0 0 0 0 0 a a 0 0 0 0 0 0 8/25 Good 100 0 0 0 0 a 0 0 0 0 0 0 a 0 0 0 » I\)..... o '"' Appendix Table 2-G-l.Continued. Adult Salmon Enumerated River Su rvey Percent Chinook Sockeye Pink Chum Coho Slouoh Mile Date Conditions SurveYed Live Dead Total Live Dead Total Live Dead Total Live Dead Total live Dead Total Slough 7 8/31 Good 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/7 Poor 100 0 0 0 0 0 0 0 C 0 0 0 0 0 0 0 9/21 Good 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/27 Good 100 0 0 0 0 0 0 0 0 C 0 0 0 0 0 0 10/25 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 O.0 0 0 Slough 8 113.7 7/28 Fa ir 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/2 Fair 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/7 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/13 Excellent 100 0 0 0 0 0 0 0 C 0 0 0 0 0 0 0 8/19 Excellent 100 0 0 0 0 0 0 0-0 0 0 0 0 0 0 0 8/25 Excellent 100 0 0 0 0 0 0 0 0 a 0 0 0 0 0 0 8/31 Good 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/6 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/14 Excellent 100 0 0 0 0 0 0 0 0 0 a 0 0 0 0 0 9/21 Fa ir 100 0 0 0 0 0 0 0 C 0 0 a 0 0 0 0 10/25 Excellent 100 0 0 a 0 0 0 0 0 0 0 0 a 0 0 0 Slough 80 121.8 8/6 Excellent 100 O·0 0 0 0 a 0 0 a a 0 0 0 0 a 8/15 Excellent 100 0 0 a 0 a a a 0 a 0 a 0 a 0 0 ·8/22 Excellent 100 0 0 0 0 0 a 0 0 0 0 a 0 0 0 0 8/29 Excellent 100 0 0 0 0 0 0 0 a c 0 a 0 0 0 0 9/12 Excellent 50 0 a a 0 0 0 0 0 a a 0 a 0 0 0 9/14 Excellent 100 a a 0 a 0 0 0 a 0 0 0 0 0 0 0 9/20 Poor 100 0 0 0 -0 G a 0 0 a 0 a a 0 0 0 9/25 Excellent 100 a 0 a a a 0 0 0 0 11 12 23 0 0 0 10/25 Poor 100 0 0 0 0 0 0 0 a 0 0 a a 0 0 a Slough 8C 121.9 8/6 Excellent 100 0 a a 0 0 0 0 a a a 0 0 0 0 a 8/15 Excellent 100 0 0 0 0 0 a a 0 0 0 a 0 0 a 0 8/29 Excellent 100 0 0 0 0 0 0 0 0 0 23 a 23 0 a 0 9/12 Excellent 100 0 0 a 2 0 2 0 0 0 43 5 48 0 0 0 9/14 Exce 11 ent 100 0 0 0 1 G 1 0 0 0 20 11 31 0 0 0 9/20 Poor 100 0 0 a 0 0 a 0 0 0 a a 0 0 0 0 9/25 Excellent 100 0 0 0 0 0 a 0 0 a 0 0 a 0 0 0 10/25 Poor 100 0 a a 0 0 a a 0 0 a a 0 0 0 0 )\ J J ~.~J ~I J i j ~,,I I ~.~~~., 1 1 1 J 1 )I )1 J 1 1 1 J J )1 )) Appendix Table 2-G-l.Continued. » N ........ Adult Salmon Enumerated River Survey Percent Chinook Sockeye Pink Chum Coho Slouqh Mile Date Conditions Surveyed Live Dead Total Live Dead Total Live Dead Total Live Dead Total Live Dead Total Slough 88 122.2 8/6 Excellent 100 0 0 C 0 0 0 0 0 0 0 0 0 0 0 0 8/19 Excellent 100 0 0 0 0 0 0 0 0 0 2 0 2 0 0 0 8/22 Excellent 100 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 8/29 Excellent 10C 0 0 0 0 0 0 0 0 0 a 0 0 0 0 0 8/31 Excellent 100 {)0 0 5 0 5 0 0 0 21 2 23 0 0 0 9/6 Excellent 100 0 0 0 2 0 2 0 0 0 66 14 80 o .0 0 9/12 Excellent 50 0 0 0 2 0 2 0 0 0 27 19 46 0 0 0 9/14 Excellent 100 0 0 0 1 0 1 0 0 0 20 11 31 0 0 0 9/20 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/25 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10/25 Good 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Moose Slough 123.5 8/6 Fair 100 1 0 1 0 0 0 8 0 8 2 0 2 0 0 0 8/12 Excellent 100 0 0 0 0 0 0 6 0 6 7 0 7 0 0 0 8/19 Excellent 100 0 0 0 7 1 8 0 1 1 9 0 9 0 0 0.8/25 Good 100 0 0 0 0 0 0 0 0 O·9 0 9 0 0 0 8/31 Excellent 100 0 0 0 5 0 5 0 0 0 21 ..2 23 0 0 0 9/6 Excellent 100 0 0 0 0 0 0 0 0 0 11 3 14 0 0 0 9/20 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 C 9/25 Excellent 100 0 0 0 0 0 0 0 0 0 11 12 23 0 0 0 10/25 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 124.6 7/29 .Excellent 100 0 0 0 0 0 0SloughA00 0 0 0 0 0 0 0 8/6 .Excellent 100 0 0 b 0 0 0 0 0 0 0 0 0 0 0 0 8/12 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/19 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/23 Excellent 100 0 0 0 0 0 0 0 0 0 O·0 0 0 0 0 8/31 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/6 Good 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/13 Exce 11 ent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/19 Poor 100 0 0 0 0 0 0 0 0 {)0 0 0 0 0 0 10/25 Poor 100 0 0 0 0 0 0 0 0 0 0 0 {)0 0 0 Slough A 124.7 7/29 Excellent 100 o ,.0 0 0 0 0 0 0 0 O·0 {)0 0 0 8/6 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/12 Exce 11 ent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/17 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/23 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Appendix Table 2-G-l.Continued. Adult Salmon tnumerated Slouqh River Mile Date Survey Percent I Chinook I S"ockeye I Plnk I Chum ~Coho Conditions Surveyed Live Dead Total Live Dead Total Live Dead Total Live Dead ~1~~De~a~d~T-ot~a~l Slough A 8/31 9/6 9/13 9/19 10/25 Excellent Good Excellent Poor Poor 100 100 100 100 100 o o o oo oo o oo o o o oo o o o oo o o o oo o oooo o oo co o o o o o o 0 o 0o0 o 0o0 o o o o o o o o o o 000 o 0 0 00 0o..00 o 0 .0 o 0 o 68 o .62o23o27 5 35 3 17 o 20 o 15 C 2 o 0 I o oo o o o o oo o oa o oo o o 3 3 4 o o o o oo o o o oo o o o o oo o oo ·2o o o o ooo G 3 3 2 o o oooo oooo o 1 11 47 25 58 22 o oo o o 1 2 2 22 20 o oo o o 1o80 o 190 1 308 63 336 100 305 168 230 8 25 5 13 o 1o0 1 10 45 23 36 2 o oo o 3oo o oo o o 32 o 12 o oo ooo o o i • 28 II 80 5 190 307 273 205 62 17 8 1o o o 3 o oo oo o o o oo 1oo ooo oo o 28 5 2ooo o oo o 32 o 9 o oo oooo o 2 1o 8 6ooo o o o oo 1o o oo o o 2 1o 7 6 o oo o o 68 62 23 27 30 14 20 15 2o o oooo oo oo o o o ooooooo oo ooooo oooo o oo o ooooo o oo o oo o o ooo o o oo oo doooo o o 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 Excellent Fair Good Excellent Excellent Excellent Excellent Excellent Excellent Excellent Fair Exce1ient Excellent Excellent Excellent Excellent Excellent Exce 11 ent Excellent Excellent Poor 8/12 8/19 8/23 8/31 9/5 9/13 9/20 9/25 10/2 10/25 8/6 8/12 8/17 8/23 8/31 9/6 9/13 9/20 9/25 10/2 10/25 126.3 125.1 Slough B 510ugh 8A » I\) ...... I\) Slough 9 128.3 8/6 8/17 8/23 8/30 9/5 9/13 9/19 9/25 10/25 Excellent Excellent Excellent Excellent Excellent Excellent Poor Excellent Fair 100 100 100 100 100 100 100 100 100 o oooo o o o o o oooooo o o o oooo oo o o o o 1 1 3 3 o o o o oo 4 oo o oo o o 1 5 3 3o oo o 10 9 2o oo oo o o 3o o o o o o o 1 10 21 12 45 2 195o242 o 109o0 o 0 o 0 o 1 o 21 2 47 16 211 58 300 186 295o0 o 0 o 0 o o o oo o o o o o oo o ooo o o o ooo o o o o o J J ) ],,J D I ~ ) 1 .~J )..!.1 J \ }J 1 1 1 1 B )1 J ~]]'1 J j J ), Appendix Table 2-G-l.Continued. I U U u ·1 en 0.).).)::J I u . ~~IL.-..I I : flOUI~;)alr:lon tnumera eo River Survey Percent Chlnook Sockeye I Plnk Chum Totalll1ve Coho Slough Mile Date Conditi ons Surveyed Llve Dead lotal Live Dead Total III ve Deao Iota I Live Dead Dead Total Slouqh 9B 129.2 8/30 Excellent 100 0 0 0 0 0 0 I 0 0 0 0 0 0 I 0 0 0 9/19 Excellent 100 0 0 0 1 0 1 I 0 0 0 4 1 5 0 0 0 9/25 Excellent 100 0 0 0 0 0 0 I 0 0 0 0 0 0 !0 0 0 10/25 Fair 100 0 0 0 0 0 0 I 0 0 0 a 0 0 0 0 0I! III! Slough 9A 133.8 8/6 Poor 100 I ~0 0 0 0 0 0 0 0 0 a a 0 0 0 8 11 ?Poor 100 0 0 0 a a a 0 0 a a a a a 01>- 8/17 Poor 100 0 0 0 0 0 a 0 0 0 a a a a a 0 8/23 Good 100 0 0 0 0 0 0 a 0 0 25 0 25 0 0 0 8/30 Poor 100 0 0 0 0 0 a a a a a a a 0 0 0 9/5 Poor 100 a 0 0 a 0 a a 0 0 a a a 0 0 0 9/6 Excellent .100 a 0 0 0 a 0 a a a 107 11 118 0 0 0 9113 Poor 100 0 0 0 0 a a a a a a 0 a a 0 0 9/19 Excellent 100 10 0 0 1 a 1 a a a 2 0 2 0 0 0 9/25 Poor 100 10 0 0 a a a a a a a 0 0 0 a 0 10/1 Excellent 100 I~0 0 a a a 0 0 0 a 0 a a 0 0 10/25 Good 100 0 0 a a a a a 0 0 a 0 0 0 a -I Slough 10 133.8 8/6 Excellent 100 0 0 a 0 0 0 0 0 0 0 0 0 0 0 0 -8112 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/17 Excellent 100 0 0 0 0 0 0 0 0 0 2 0 2 0 0 0 8/23 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/30 Excellent 100 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 9/5 Excellent 100 0 0 a a 0 0 0 a a a 0 a 0 0 a 9/13 Excellent 100 0 0 a a a 0 a a 0 a 0 0 0 0 0 9119 Excellent 100 0 0 0 a a 0 a a a 0 0 0 0 0 a 9/25 Excellent 100 0 0 0 0 a 0 a a a a 0 0 0 0 a 10/25 Excellent 100 0 0 0 a a a a a a a a 0 a 0 0 I I !0510ugh11135.3 8/2 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/6 Excellent 100 0 0 0 I 40 0 40 0 0 0 I 10 0 10 0 0 0 8/11 Fair 100 0 0 0 116 0 116 39 0 39 I 20 0 20 0 0 0 8117 Excellent 100 0 0 0 196 0 196 131 0 131 43 0 43 0 0 0 8/23 Exce 11 ent 100 0 0 0 299 0 299 10?11 113 164 1 165 0 0 0 8/30 Excellent 100 0 0 0 455 1 456 41 46 87 395 16 411 0 0 0 9/5 Excellent 100 0 0 0 0 0 279 98 377 0 0 0 9113 Excellent 100 0 0 0 0 0 141 318 459 0 0 0 9119 Excellent 100 ~~~I 0 0 66 157 223 0 0 0 > f\) ..... (,) > I\)..... ~ Appendix Table 2-G-l.Continued. Adult Salmon EnlH'1eratel1 River Survey Percent Chinook Sockeye Plnk Chum Coho Slough Mil e Date Conditions Surveyed LlVe Dead Total LlVe Dead Total [lVe nead Total Live Dead Total LlVe Dead Total Slough 11 9/25 Excellent 100 0 0 0 142 63 205 0 0 0 17 113 130 0 0 a 10/1 Excellent 100 0 0 0 60 108 168 0 0 0 3 65 68 0 0 0 10/5 Excellerit 100 0 0 0 26 85 111 0 0 (:G 12 12 0 0 0 10/25 Excellent 100 0 0 0 0 0 a a 0 0 a 0 a a a 0 , Slough 12 135.4 8/2 Exce 11 ent 100 a a a a a a 0 0 0 0 0 0 0 a a 8/6 Excellent 100 a 0 0 C 0 0 a 0 0 a a a 0 a a 8/11 Excellent 100 a 0 a 0 0 0 0 0 0 0 0 a 0 a 0 8/17 Excellent 100 a 0 ,0 a 0 a a a 0 a a a a a a 8/23 Excellent 100 a a c 0 a a a a a a a 0 a a a 8/30 Excellent 100 a a 0 0 a 0 0 0 0 a 0 0 0 a a 9/5 Excellent 100 0 0 0 0 0 a 0 0 0 a 0 a a a a 9/13 Excellent 100 0 0 0 0 0 0 a 0 0 0 0 0 0 a a 9/19 Excellent 100 a 0 0 0 0 a 0 0 0 0 C 0 a a 0 9/25 Excellent 100 a a 0 0 a 0 0 0 a 0 0 a a a a 10/25 Fai r 100 0 a 0 0 a 0 0 a 0 a a a 0 a 0 Slough 13 135.9 8/6 Excellent 100 0 0 0 a 0 a 0 0 a a 0 0 0 a a 8/11 Excellent 100 a 0 a 0 a a 0 a a c 0 a 0 0 0 8/17 Excellent 100 a a a a a a a 0 G 0 0 a a 0 a 8/22 Excellent 100 0 a a a a a a 0 a a 0 0 0 a a 8/23 Excellent 100 a a a 0 a a a a a 0 a a a 0 a 8/30 Excellent 100 0 0 a 0 a a a a 0 a a a 0 0 0 9/5 Excellent 100 a 0 0 a a 0 0 0 a 0 0 a 0 0 0 9/13 Excellent 100 0 0 0 a a a a a a 0 a 0 a a a 9/19 Excellent 100 0 0 0 0 a a a 0 0 0 a a 0 0 a 9/25 Excellent 100 0 0 0 0 0 a 0 0 a 0 a a 0 0 a 10/25 Fai r 100 a 0 a a a a 0 0 a 0 0 a 0 a 0 SlouQh 14 135.9 8/6 Excellent 100 a a a 0 a a a a 0 a 0 0 0 a O· 8/11 EXcellent 100 a a a a a a a a a a 0 a a a a 8/17 Excellent 100 a a 0 a 0 a a 0 0 0 0 0 a a 0 8/22 Excellent 100 a a a a 0 a a a a I 0 (l 0 a a a 8/23 Excellent 100 0 0 0 a a 0 a a 0 a 0 0 0 ,0 a 8/30 Excellent 100 0 0 0 a a 0 a 0 0 I a 0 0 0 0 0 9/5 Excellent 100 a a a 0 0 a 0 0 a I a f)0 0 a a 9/13 Exce"ent 100 0 a a 0 0 a 0 0 a 0 l'a 0 0 0 9/19 Excellent 100 a a a 0 a 0 a G 0 0 0 0 0 a 0 9/25 Excellent 100 a 0 d a a 0 a a 0 0 0 0 a a a 10/25 Fair 100 0 a 0 a a 0 0 a a 0 a 0 0 0 a ""\ J 1 J ~~J J ~J ,)J J J ~J ~~] > I\)..., 01 1 1 )1 J i ))..~i J 1 1 J )i ! Appendix Table 2-G-l.Continued. A<lu I t ~a lmon !:.numerated River Survey Percent Chinook Sockeye Pink Chum Coho Slouoh ~lil e Date Conditions Surveyed Live Dead Total live Dead Total Live Dead Total live Dead Total live Dead Total Slough 15 137.2 8/4 Fair 100 0 0 0 0 0 0 24 0 24 0 0 0 0 0 0 8/11 Excellent 100 0 0 0 a 0 a 131 1 132 a 0 0 14 a 14 8/17 Excellent 100 a a 0 0 a a 2 0 2 1 0 1 5 0 5 8/23 Excellent 100 a a a a a 0 0 0 a a a 0 0 0 0 8/30 Excellent 100 0 0 0 0 a a 0 0 0 0 0 0 a c 0 9/4 Excellent 100 0 a 0 0 a 0 a a 0 0 a a a a 0 9/12 Excellent 100 a a a a 0 a a a a a a 0 a 0 0 9/18 Excellent'100 a 0 a a a 0 0 0 a a 0 0 0 0 0 9/25 Excellent 100 0 a a 0 0 0 0 0 a 0 0 0 0 0 0 10/25 Poor 100 0 0 0 0 0 0 0 0 0 0 a 0 0 0 0 Slough 16 137.3 8/4 Good 100 0 0 0 0 0 C 0 0 0 0 0 0 0 0 C 8/11 Excellent 100 0 0 0 a 0 0 I G 0 0 0 0 a 0 0 C 8/17 Excellent 100 0 0 0 0 a 0 0 0 0 a 0 0 0 0 C 8/23 Excellent 100 0 0 0 0 0 0 0 C 0 0 0 0 0 0 0 8/30 Excellent 100 0 0 0 0 0 0 I 0 0 0 0 0 0 0 0 O. 9/4 Excellent 100 0 0 a 0 0 0 I 0 0 0 a 0 0 0 ·0 0 9/12 Excellent 100 0 0 0 0 ·0 a a 0 0 0 0 a 0 0 0 9/18 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/25 Excellent 100 0 0 0 0 0 0 0 0 0 0 a 0 0 0 0 10/25 Good 100 a '·0 0 0 0 0 0 0 0 0 0 a 0 0 0 .. Slough 17 138.9 8/4 Good 100 a 0 0 0 0 0 C 0 0 0 0 0 0 0 0 8/11 Exce 11 ent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 a 0 8/16 Excellent 100 0 0 0 0 0 a 0 0 0 0 0 0 0 0 0 8/22 Excellent 100 0 0 0 0 0 0 0 a a 0 a a a a a 8/30 Excellent 100 a a a a a a a a a 4 a 4 a a 0 9/4 Excellent 100 0 a a a a 0 a a a a 2 2 a 0 a 9/12 Excellent 100 a a a a 0 a a 0 a a a 0 a a a 9/18 Exce 11 ent 100 a 0 a a a a 0 a a 2 a 2 a a a 9/23 Exce 11 ent 100 a a a 0 a a 0 0 0 17 4 21 0 0 0 9/30 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 a 0 10/25 Excellent 100 0 0 0 0 0 a 0 0 0 a 0 (}0 0 0 Slough 18 139.1 8/4 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 {}0 0 0 8/11 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 Q 0 0 0 8/16 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/22 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 > I\) ..... 0) Appendix Table 2-G-l.Continued. ------------------------------,,-----------Adult Sa 1montnumera ted River Survey Percent Chinook I Sockeye Pink Chum Coho Slough Mile Date Conditions Surveyed Live Dead Total 'Live-Dead Total LlVe Dead Total Live Dead Total Live Dead Total Slough 18 8/30 Excellent 100 0 0 0 I 0 0 0 0 0 0 0 0 0 0 0I0 9/4 EXcellent 100 0 0 0 I 0 0 0 0 0 0 0 0 0 0 0 0 9/14 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 .0 9/18 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/23 ~xcellent 100 o·0 0 0 0 0 0 0 0 .0 0 0 0 ci 0 9/30 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10/25 Fair 100 [0 0 0 0 o.0 0 0 0 0 0 0 0 0 0 Slough 19 139.7 8/4 Excellent 100 0 0 0 0 0 0 1 0 1 0 0 0 0 0 0 8/11 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/16 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/22 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/30 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/4 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/12 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/18 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/23 Excellent 100 .0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/30 Exce 11 ent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10/25 Fai r 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Slough 20 140.0 8/4 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/11 Excellent 100 0 0 0 0 0 0 51 .0 51 0 0 0 0 0 0 8/16 Excellent 100 0 0 0 0 0 0 64 0 64 0 0 0 0 0 0 8/22 Excellent 100 0 0 0 0 0 0 37 13 50 3 0 3 0 0 0 8/30 Excellent 100 0 0 0 0 0 0 2 6 8 3 0 3 0 0 0 9/4 Excellent 100 0 0 0 0 0 0 0 0 0 23 7 30 0 0 0 9/12 Excellent 100 0 0 0 0 0 0 0 0 0 2 7 9 0 0 0 9/18 Poor 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/23 Excellent 100 0 0 0 0 0 0 0 0 0 0 2 2 0 0 0 9/30 Excellent 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10/25 Fair 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ! Slough 21 141.1 8/4 Excellent 100 0 0 0 0 0 0 0 0 0 I 0 0 0 0 0 0 8/11 Good 100 0 0 0 0 0 0 0 0 0 7 0 7 0 0 0 8/16 Excellent 100 0 0 0 0 0 0 64 0 64 i 0 0 0 0 0 0 8/22 Excellent 100 0 0 0 10 0 10 7 0 7 231 4 235 0 0 0 8/29 Good 100 0 0 0 115 0 15 3 3 6 568 45 613 0 0 0 9/4 Excellent 100 0 0 0 1 43 1 44 0 0 0 615 121 736 0 0 0 )\ J J 1 J I l J ))J I .~J J m J I ).~ I I J 1 j I ._)J I j J 1 j )~j )J Appendix Table 2-G-l.Continued. » '"...., ...... AClUlt ~almon tnumera eo River Survey Percent Chinook Sockeye 1'101<Chum Coho Slough Mile DatE'Conditions Surveyed L1ve Ueao Iota I [we Dead Total [lve Dead Total [we Dead Total Live Dead Total Slough 21 9/12 Excellent 100 0 0 0 43 10 53 0 0 0 341 167 508 0 0 0 9/18 Good 25 0 0 0 30 2 32 0 a 0 28 8 36 a 0 0 9/23 Excellent 100 0 0 a 18 1 19 0 0 0 17 14 31 0 a 0 9/30 Excellent 100 a 0 0 4 1 5 I 0 0 0 2 1 3 0 0 0 10/25 Fair 100 a a 0 0 0 0 a a 0 0 a 0 0 0 0 Slough 21A 144.3 8/4 Excellent 100 a 0 0 a 0 0 0 a 0 0 0 0 0 0 0 8/9 Excellent 100 0 0 0 ! 0 0 0 a 0 0 a 0 0 0 0 0 8/22 Excellent 100 a a 0 0 a 0 0 a 0 a a a 0 a 0 9/23 Excellent 100 0 0 a I 0 0 0 a a 0 0 0 0 0 a 0 10/25 Fair 100 0 0 0 I 0 0 0 0 0 a a 0 0 0 0 a Appendix Table 2-G-2.Escapement survey counts of Susitna River tributary streams between Chulitna River and Upper Devil Canyon,Adult Anadromous Investi ga ti ons,Su Hydro Stud i es,1982. ,,Survey Adult Salmon Enumerated River Survey Distance Chlnook Sockeye Plnk Chum ,Coho," Stream Mile Date Conditions ~1i1 es Llve Dead Total Live Dead Total [lYe Dead Total [lYe Dead Total IL 1 ve ueM lota I Whi skers Creek 101.4 B/8 Excellent 0.5 0 0 0 0 0 0 73 0 73 0 0 0 5 0 5 8/13 Excellent 0.5 0 0 0 0 0 0 27 0 27 0 0 0 39 0 39 8/18 Poor 0.25 0 0 0 0 0 0 31 16 47 0 0 0 82 0 82 8/23 Excellent 0.25 0 0 0 0 0 0 39 99 138 0 0 0 172 4 ]76 9/21 Poor 0.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/24 Good 10.0 0 0 0 0 0 0 0 0 0 0 0 0 39 0 39 10/25 Good 0.8 -0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Chase Creek 106.9 8/8 Excellent 0.75 0 0 0 0 0 0 4 0 4 0 0 0 0 0 0 8/11 Good 1.0 8 7 15 0 0 0 95 1 96 0 0 0 0 0 0 8/20 Excellent 1.0 0 2 2 0 0 0 91 16 107 0 0 0 0 0 0 8/28 Excellent 1.0 0 2 2 0 0 0 4 58 62 0 0 0 0 0 0 9/6 Good 0.25 0 0 0 0 0 0 0 4 4 0 0 0 0 0 0 9/17 Good 0.25 0 0 0 0 0 0 0 0 0 0 0 0 1 0 1 9/21 Excellent 0.75 0 0 0 0 0 0 0 0 0 0 0 0 1 2 3 9/27 Excellent 0.25 0 0 0 0 0 0 0 0 0 0 0 0 30 6 36 10/25 Fair 0.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Slash Creek 111.2 9/21 Excellent 0.75 0 0 0 0 0 0 0 0 0 0 0 0 6 0 6 10/25 Good 0.1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Gash Creek 111.6 8/7 Excellent 0.25 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8/19 Excellent 0.25 0 0 0 0 0 0 0 0 0 0 b 0 0 0 0 9/1 Excellent 0.25 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/7 Excellent 0.25 0 0 0 0 0 0 0 0 a 0 0 0 0 0 0 9/23 Excellent 1.0 0 0 0 0 0 0 0 0 0 0 0 0 74 0 74 9/27 Excellent 1.0 0 0 0 0 0 0 0 0 0 0 0 0 65 2 67 10/2 Excellent 1.0 0 0 0 0 0 0 0 0 0 0 0 0 22 0 22 10/25 Good 0.25 0 0 0 0 0 0 0 0 0 o '0 0 0 0 0 Lane Creek 113.6 7/12 Excellent 0.7 47 0 47 0 0 0 0 0 0 0 0 0 0 0 0 7/28 Fair 2.5 40 1 41 0 0 0 0 0 0 0 0 0 0 0 0 8/2 Fai r 0.25 1 0 1 0 0 0 0 0 0 1 0 1 0 0 0 8/7 Excellent 0.5 1 0 1 0 0 0 504 0 504 1 0 1 0 0 0 8/13 Excellent 0.5 0 0 0 0 0 0 632 8 640 1 0 1 1 0 1 8/19 Excellent 0.5 0 a 0 0 0 0 512 65 577 3 1 4 0 0 0 8/25 Excellent 0.5 0 0 0 0 0 0 240 336 576 9 2 11 0 0 0 8/31 Good 0.5 0 0"0 0 0 0 4 74 78 10 1 11 O·0 0)\ > I\) ..... (J) J ~J ,I J ~~I )I J t J .~~ » I\)....., CO J j 1 1 J )j J )j ~1 I ti J 1 J ) Appendix Table 2-G-2.Continued. Survey Adult Salmon Enumerated River Survey Distance Chlnook Sockeye Plnl<Chum Coho Stream Mile Date Conditions Miles LlYe Dead Total LlYe Dead Total Live Dead Total LlYe Dead Iota 1 Live Dead Total Lane Creek 9/6 Excellent 0.25 a a 0 0 0 a a a a 1 4 5 1 a 1 9/14 Excellent 0.5 a 0 a 0 0 0 0 a a 1 0 1 5 a 5 9/21 Fair 0.5 a 0 a a a a 0 a a 0 0 a 1 0 1 10/25 Excellent 0.25 a 0 a a a 0 a a a 0 0 0 a a 0 Lower McKenzie 116.2 8/7 Excell ent 0.25 a a 0 0 a 0 a a a 0 a 0 a a a Creek 8/13 Excellent 0.25 0 0 a a a a a 0 a 0 a a 0 a a 8/19 Excellent 0.25 a a 0 a 0 0 15 8 23 0 a 0 a a a 8/25 Excellent 0.25 a a a 0 0 a 6 0 6 a a a a 0 a 8/31 Excellent 0.25 a 0 a a a 0 a a 0 a a a 0 0 a 9/6 Excellent 0.25 0 a a 0 a a 0 0 0 a a a a a a 9/14 Excellent 1.5 a 0 a a a a 0 0 a 0 a a 132 1 ..133 9/21 Good 1.5 a a a a 0 a 0 a a a a a 102 1 103 9/27 Excellent 1.0 a a a a a 0 0 0 a 0 0 0 84 6 90 10/2 Excellent 1.0 a a 0 a a 0 a 0 a a a 0 30 4 34 10/25 Excellent 0.25 a 0 a a a a a a a a a a ·0 0 0 McKenzie Creek 116.7 8/7 Excellent 0.25 a 0 a a a a a a 0 a 0 0 a a a 8/13 Excellent.0.25 0 0 a 0 0 0 a a 0 a 0 0 a a a 8/19 Excellent 0.25 0 0 a a a a 13 4 17 0 0 a a 0 0 8/25 Exce I lent 0.25 0 a 0 a a 0 a 7 7 0 a 0 a a a 8/31 Excellent 0.25 0 0 a a 0 a a a a a a ,0 a a a 9/6 Excellent 0.25 0 a a 0 a a a a a 0 a a a a a 9/14 Excellent 0.25 a 0 a a a 0 O·0 a 0 a a a a a 9/21 Good 0.25 a a a a a 0 a a a a 0 a a a a 9/22 Good 0.25 a a a a a a a a a a a a a a 0 10/2 Excellent 0.25 0 a a 0 a a a a a a 0 a 0 a 0 10/25 Fair 0.1 a a a a a a a a a a a a a 0 0 Little Portilge 117.7 8/7 Excellent 0.25 a 0 0 a a a 40 a 40 a 0 a a a 0 Creek 8/13 Excellent 0.5 a a a a a a 138 2 140 0 a a a a 0 8/19 Excell ent 0.25 a a a a a a 46 28 74 a 0 a a a a 8/25 Excellent 0.25 a ()a a 0 0 15 46 61 25 6 31 a a 0 8/31 Excellent 0.25 a a a a a 0 a 9 9 5 0 5 a a 0 9/6 Excellent 0.25 0 a a a 0 a a a a 18 7 25 a a 0 9/14 Excellent 0.25 a a a a a a a a a a a 0 a a a 9/21 Good 0.25 a a a 0 0 a a a a a a a 5 1 6 9/27 Excellent 0.25 a a a a a a a a a a a a 8 0 8 10/2 Excell ent 0.25 0 a a a a a a a a a a a 8 a 8 10/25 Good 0.1 a a 0 0 a 0 a a 0 a a a a a a » I\) Q) o Appendix Table 2-G-~.Continued. ,Survey Ad Ult :>almon Enumeratea River Survey Distance Chlnool<Sockeye f'lnl<Chul11 Coho Stream Mile Date Conditions Miles Live Dead Total Live Dead ,Total Live Dead Total Live Dead Total Live Dead Total 5th of July 123.7 8/6 Excellent 0.5 3 0 3 0 0 0 17 0 17 1 0 1 0 o '0 Creek 8/12 Excellent 0.25 0 0 0 0 0 0 61 0 61 0 0 0 0 0 0 8/19 Excellent 0.25 0 0 0 0 0 0 113 a 113 0 0 0 0 0 0 8/25 Excellent 0.25 0 0 0 0,0 0 15 14 29 0 0 0 0 0 0 8/31 'Good 0.25 0 0 0 o '0 0 0 0 0 0 0 0 0 0 0' 9/6 Excellent 0.25 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/14 Good 0.25 0 0 0 0 0 0 0 0 0 0 0 '0 0 0 o· 9/20 Good 0.25 I ~0 0 0 0 0 0 0 0 0 0 '0 0 0 0 10/25 Fair 0.2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 , Skull Creek 124.7 8/6 Excellent 0.25 0 0 0 0 0 0 0 0 0 0 0 0 I 0 0 I 0 8/12 Exce 11 ent 0.5 0 0 0 0 0 0 12 0 12 0 0 0 0 0 0 8/17 Excellent 0.5 0 0 0 0 0 0 12 0 12 0 0 0 0 0 0 8/23 Exce 11 ent 0.25 I ~0 0 0 0 0 6 5 11 C 0 0 0 0 0 8/31 Good 0.25 0 0 0 0 0 0 0 0 1 0 1 0 0 0 9/6 Excellent 0.25 0 0 0 a a 0 a 0 0 0 0 0 0 0 9/13 Excellent 0.25 ' 0 0 0 0 0 0 0 a 0 0 0 0 0 0 0 9/19 Fair 0.25 I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 I 10/25 Excellent 0.1 I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 I Shennan Creek 130.8 8/6 Excellent 0.25 J 3 0 3 0 0 0 5 0 5 0 0 0 0 0 0 8/12 Exce 11 ent 0.25 ,0 0 0 0 0 0 23 1 24 0 0 0 0 0 0 8/17 Excellent 0.25 I 0 0 0 0 0 0 4 1 5 0 0 0 0 0 0 8/23 Excellent 0.25 i 0 0 0 0 0 0 0 3 3 0 0 0 0 0 0 9/5 Exce 11 ent 0.25 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9/13 Poor 0.25 0 0 0 0 0 a 0 0 0 0 0 0 0 0 0 9/25 Good 0.25 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10/1 Good 0.25 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10/25 Excellent 0.1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4th of July 131.0 7/28 Good 2.0 55 1 56 0 0 0 0 0 0 a 0 0 0 0 0 Creek 8/6 Excellent 0.25 8 0 8 0 0 0 63 0 63 C 0 0 0 0 0 8/12 Good 0.5 5 0 5 0 0 0 508 3 511 8 0 8 0 0 0 8/17 Excellent 0.25 0 0 0 0 0 0 465 129 594 78 1 79 0 0 0 8/23 Excellent 0.25 0 0 0 0 0 0 177 525 702 152 16 168 0 0 0 8/30 Good 0.25 0 0 0 0 0 0 0 125 125 136 52 188 0 0 0 9/5 Good 0.25 0 0 0 0 0 0 0 0 0 125 66 191 0 0 0 9/13 Fair 0.25 0 0 0 0 0 0 I 0 0 0 4 46 50 1 0 1 )"'\,1 ,~~t t ~J J ~J J .1 I 1 )J ~ )1 J J 1 J I 1 J I J I J J ]I ) Appendix Table 2-G-2.Continued. ~urvey Adult Salmon Enunerated > I\) Q) ..,A. ej Chi nook Socl<eye I'lnk Chum Coho ........_.....-...---._..-.__j ti ve Deaa Iota I L we nead Tota I l1ve Dead Total [we Dead Total LlVe Dean Total 4th of July 9/19 Good 0.25 0 0 C 0 0 0 0 0 0 38 5 43 C'0 0 Creek 9/25 Excellent 0.25 0 0 0 0 0 0 0 0 0 18 10 28 4 0 4 10/1 Excellent 0.25 0 0 0 0 0 0 0 0 0 4 2 6 1 1 2 10/7.5 Poor 0.2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 I 8'-Excellent 4.0 I 20 21 0 0 0 C C 0 0 0 0 0 0GoldCreek136.7 /j I 1 0 8111 Good 0.5 0 2 2 0 0 0 11 0 11 0 0 0 0 0 0 8/19 Excellent 0.25 1 0 0 0 0 a 0 0 0 0 0 0 0 0 0 0 8/23 Excellent 0.25 0 0 C 0 0 0 1 1 2 0 0 l'1 0 1 8/30 Poor 0.25 I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 le/25 Fair 0.2 i 0 0 0 0 0 0 0 0 0 0 0 0 0 (I 0 I I Indian River 138.6 7/21 Excellent 15.0 /1049 4 1053 0 0 0 0 C 0 0 0 0 0 0 0 811 Excellent 6.0 105 5 110 0 0 0 0 0 0 C o .0 0 0 0 8/3 Excellent 2.0 .122 20 142 0 0 0 24 0 24 0 0 0 0 0 0 8/5 Good 4.0 89 40 ·129 0 0 0 202 1 203 16 0 16 0 0 0 8/11 Excellent 1.0 11 19 30 0 0 0 735 3 738 134 0 134 0 0 0 8/16 Excellent 1.0 2 13 15 0 0 0 537 22 559 362 5 367 9 0 9 -8/23 Excellent 1.0 0 2 2 0 0 238 329·567 Hl4 15 199 0 o.0 8/29 Good 1.0 0 8 8 0 0 0 8 339 347 120 48 168 IS 0 18 9/4 Excellent 2.0 0 0 0 0 0 0 0 98 .98 886 460 1346 24 0 24 9/12 Exce 11 ent 2.0 0 0 0 0 0 0 ('0 0 149 1028 1177 36 1 37 9/18 Excellent 2.0 0 0 0 0 0 0 0 0 0 32 42 74 36 0 36 9/24 Excellent 15.0 0 0 0 0 0 0 0 0 0 0 0 a 101 0 101 9/30 Excellent 2.0 0 0 0 0 0 0 0 0 0 2 0 2 32 0 32 10/25 Good 1.0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Jack Long Creek 144.5 8/4 Excellent 0.25 2 0 7.0 0 0 0 0 0 0 0 0 0 0 0 Olll Excellent 0.25 7.0 ')0 0 0 15 0 15 0 0 0 0 0 0 ~/1Ii Excellent 0.25 0 0 (J 0 0 0 21 0 21 0 ()0 0 0 0 R/2'2 Fxcellent 0.25 0 0 0 0 0 0 <;3 R 0 ()0 0 0 0 P,/30 Good 0.25 0 0 0 0 f!0 0 0 0 2 1 :1 ]a 1 Q/IJ Excellent 0.25 i o .0 0 0 0 0 0 0 0 0 1 1 0 0 0 911?r;ood 0.25 0 0 0 0 [)0 0 0 0 0 0 0 0 ()0 9/18 Poor 0.25 0 0 (I n 0 0 0 0 0 0 0 0 0 0 0 9/3r;Excellent 0.25 0 0 0 0 0 0 0 0 0 0 0 0 ()1 I 10/25 Poor 0.3 0 0 0 ()0 0 0 0 0 0 0 0 O·0 0 Appendix Table 2-G-2.Continued. Su rvey ~'__---,.~--.---_.---_____,.,.,__,_...,..".__:_: River Survey Pi stanceSt~am Mile Date CoodiHons Miles ~~~~~~~~~'~~~~~~~Tl~~~~~~~~I~~~~~~~~~~~~~~~" » I\) CD I\) Portage Creek Cheechako Creek 148.9 152.5 7/21 8/3 8/9 8/16 8/22 8/29 9/3 g ""',?Ih ~/18 9/23 .9/24 9/30 10/25 8/5 8/6 8/11 8/18 8/22 8/28 9/8 9/24 10/25 Excellent Excellent Exce llent .Excellent .Exce11 ent Good . Excellent Good' Poor Fa;r Excellent Excellent Excellent Excellent Exce 11 ent Good Exce11 ent hood Excellent Good Excellent Good 15.0 955 15.0 198 0.5 ?2 0.25 1 0.25 0 0.25 0 0.25 0 0.25 0 0.25 0 0.25 0 15.0 0 0.25 0 1.0 0 0.75 11 3.0 16 1.0 6 1.0 0 1.5 1 1.0 0 0.5 0 ).,5 0 0.1 0 o 955 55 1253 3 25 3 a 2 2 4 ao() o 0 o 0o(] o 0o co0 o 11o16 o 6 o 0 o 1 o 0 o 0o0 o 0 o ooo o a oo o o o c () o o o o o o o o o o o oo o o oo o o o oo o oo o o o oo o o 0 (](]0 o 0 eGO·o 146 0 146 ?5 o 166 3 169 71 o III 0 III lC3 4 15 F6 l412lo0(]0 6 '0 0 C (j 0 00 r;(}G o 0 0 0 0o0Q02oQ00 0o0 0 0 0 o 0 COO o 0 0 0 0 OeD 0 0 o 0 0 0 0 o 000 0 o 0 000 o 0 000 o 0 0 C 0 00000 o 0 o 0 o 25 o 71 10 153 7 28 1 7 o 0 o 0 o 0 ?5 o 0 o 0 o 0 o 0 o 0 o 0o0 o 0o0 o 0o0 o o o o 1 1 o oo o 88 oo o o o oo o o o o o 0 b 0 o 0 o 0 01 o 1 o 0 o 0 o 0o0o.88 o 0c c o 0 o 0 o 0 o 0o0 o 0 o 0 o 0 o 0 Chinook Creek 156.8 8/6 B/11 8/18 B/22 10/25 Excellent Good Excellent Good Goorl 2.0 1.5 1.0 2.0 0.1 5 1 1 o o oo o O' o 5 1 1 o o oo o o f) o o oo o o o oo o o o oo o o o o C G oo o n (] oo [) o () o c oo o o o o o f) o o o o l) o o o o o o o o o o Devil Creek Hi).0 8/6 8/11 8/18 Fl/22 10/25 Excellent Excellent Excellent ExCf'llent Goor! ?O 0 2.0 0 ?.0 (1 ".0 0 1.0 I 0 I I o o o o o oo coo o o c o o o (] G o o o o (] o o o o o o o o f) o (\ o G n (] n o o G n n o oo (1 n o o f) (1 o o o a o o o o r r; o o o (J (1 r o )J ) 1 ~,)J '~ I ;~~J J J ~ ~ I I "-=---i ------i -------j -'-'------1 ~ ) ]1 J ) J ] ~ I\') Q) (,) Appendix Table 2-G-3.Sockeye salmon spawning ground surveys of selected spawning areas and resultant tagged to untagged ratios,Adult Anadromous Investigations,Su Hydro Studies,1982. LUl.AllUN TAGS IALF.I:.I:.INA IAIi:>r.;UHHY lAb:> RiverY Survey Tagged Total ~atio Tagged Total Ratio Tagged Total Ratio Spawning Area Mile Date Conditions (r)Untagged (c)c/r)(r)UntagQed Cc)(c/r)(r)Untaaaed (c)(c/r) Unnamed Slough 96.9 8/31 Excellent 1 56 57 57.0 9/9 Good 1 69 70 70.0 9/24 Good 0 11 11 0.0 Unnamed Slough 97.1 7/31 Good 85 158 243 2.9 8/21 Excellent 13 51 64 4.9 Fi sh Creek .97.1 8/1 Excellent 30 114 144 4.8 Larson Creek 97.1 8/6 Excellent 28 174 202 7.2 Unnamed Creek 97.8 8/7 Excellent 14 189 203 14.5 Swan Lake 97.8 9/25 Good 5 81 86 17.2 Byers Creek 97.8 8/15 Good 2 42 44 22.0 8/25 Good 7 82 89 12.7 . 9/3 Good 0 40 40 0.0 Troub 1esome 97.8 8/25 Good 0 0 0 0.0 Creek 9/3 Fair 0 2 2 0.0 9/9 Good 0 0 0 0.0.. Slough 8C 121.9 9/12 Excellent 0 1 1 0.0 0 1 1 0.0 1 0 1 1.0 Slough 8B 122.2 9/6 Excellent 1 1 2 2.0 1 1 2 2.0 0 2 2 0.0 9/12 Excellent 1 0 1 1.0 0 1 1 0.0 0 1 1 0.0 9/14 Excellent 0 1 1 0.0 1 0 1 1.0 0 1 1 0.0 Moose Slough 123.5 8/31 Excellent 0 4 4 0.0 0 4 4 0.0 1 3 4 4.0 Slough 8A 125.1 8/12 Fair 4 47 51 12.8 7 44 51 7.3 6 45 51 8.5 8/17 Good 4 47 51 12.8 3 48 51 17.0 4 47 51 12.8 8/23 Excellent 1 18 19 19.0 1 18 19 19.0 2 17 19 9.5 8/31 Excellent 0 27 27 0.0 0 27 27 0.0 0 27 27 0.0 9/6 Excellent 2 20 22 11.0 1 21 22 22.0 5 17 22 4.4 9/13 Excellent 3 7 10 3.3 0 10 10 0.0 1 9 10 10.0 » I\) en .~ Appendix Table G-2-3.Continued. LOCATION TAGS-IALKtl:INA IA(j~CURRY TAGS River!'Survey Tag~)d Total Ratio Tagjed Total Ratio Tagged Total Rati.) Soawnino Area Mile Date Conditions (r UntaoQed (c)(c/r).(r Un tagged (c)(c/r)(r)Untaooed (c)(c/r Slough 8A 9/20 Excellent 2 13 15 7.5 0 15 15 0.0 3 12 15 5.0 9/25 Excellent 2 9 11 5.5 0 11 11 0.0 2 9 11 5.5 10/2 Exce 11 ent 0 0 2 0.0 0 2 2 0.0 0 2 2 0.0 '.' Slough 8 126.3 8/19 Excellent .0 1 1 0.0 1 0 1 1.0 0 1 1 0.0 9/5 Excellent.··1 3 4 4.0 2 2 4 2.0 0 4 4 0.0 9/13 Good 1 2 3 3.0 2 1 3 1.5 0 3 .3 0.0 Slough 9 128.3'8/23 Excellent 0 1 1 0.0 '0 1 1 0.0 0 1 1 0.0 8/30 Excellent 1 0 1 1.0 0 1 1 0.0 0 1 1 0.0 9/5 Excellent 1 i 2 2.0 0 2 2 0.0 0 2 2 0.0 9/13 Excellent '.0 2 2 0.0 1 1 2 2.0 0 2 2 0.0 Slough 98 129.2 9/19 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 Slough 9A 133.3 9/19 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 Slough 11 135.3 8/11 Fai r 20 .54 74 3.7 11 63 74 6.7 11 63 74 6.7 8/17 Excellent 1 9 10 10.0 3 7 10 3.3 2 8 10 5.0 8/23 Excellent 19 200 219 11.5 39 180 219 5.6 22 197 219 10.0 8/30 Excellent 19 341 360 19.0 46 314 360 7.8 30 330 360 12.0 9/5 Excellent 19 224 243 12.8 32 211 243 7.6 28 215 243 8.7 9/13 Excellent 19 265 284 15.0 40 244 284 7.1 18 266 284 15.8 9/19.Excellent 8 196 204 25.5 27 177 204 7.6 13 191 204 15.7 9/25 Excellent 3 124 127 42.3 6 121 127 21.2 6 121 127 21.2 10/1 Excellent 1 51 52 52.0 6 46 52 8.7 1 51 52 52.0 10/5 Excellent 2 18 20 10.0 3 17 20 6.7 1 19 20 20.0 Slough 17 138.9 9/23 Excellent 0 4 4 0.0 :0 4 4 0.0 0 4 4 0.0 Slough 21 141.0 8/22 Excellent 0 9 9 0.0 0 9 9 0.0 1 8 9 9.0 8/29 Good 1 11 12 12.0 1 11 12 12.0 1 11 12 12.0 9/4 Excellent 0 31 31 0.0 7 24 31 4.4 5 26 31 6.2 .9/12 Excellent 2 41 43 21.5 B 35 43 5.4 5 38 43 8.6 9/18 Good 3 19 22 7.3 4 18 22 5.5 j 1 21 22 22.0 9/23 Excellent 0 15 15 0.0 2 13 15 7.5 1 14 15 15.0 9/30 Excellent 0 4 4 0.0 0 4 1\0.0 0 4 4 0.0 Portage Creek 148.9 8/29 Good 0 4 4 0.0 0 4 4 0.0 I 0 4 4 0.0 llConfluence of stream or their receiving water with Susitna River mainstem. )\ J ~.1 J )I J J ~I .~,J I )I I ~~ J ---]i 1 J J i 1 j >- I\) co 01 Appendix Table 2-G-4.Pink salmon spawning ground surveys of selected spawning areas and resultant tagged to untagged ratios~Adult Anadromous Investigations~Su Hydro Studies~1982. LOCATION ::,UNSHINt TAG::,IALKEETNA TAGS CURRY TAGS Riverll Survey Tagged Total Ratio Tagged Total Ratio Tagged Total Ratio SoawninQ Area Mile Date Conditions (r)Untaqqed (c)(c/r)(r)Untagged (c)(c/r)(r)UntaQged (c)(c/r) Birch Creek 88.4 8/14 Good 93 5314 5407 58.1 8/25 Good 55 6249 6304 114.6 Unnamed Slough 96.9 8/31 Excellent 0 5 5 0.0 Fish Creek 97.1 8/15 Good 54 5821 5875 108.8 8/25 Excellent 7 519 526 75.1 8/21 Excellent 4 1026 1030 257.5 Byers Creek 97.8 8/15 Good 10 1100 1110 111.0 8/25 Good 0 129 129 0.0 Troub 1esome Creek 97.8 8/25 Good 0 174 174 0.0 Whiskers Creek 101.4 8/8 Excellent 4 69 73 18.3 8/13 Excellent 6 21 27 4.5 8/18 Fa ir 6 31 37 6.2 8/23 Good 0 39 39 0.0 Chase Creek 106.9 I 8/8 Excellent 0 4 4 0.0 1 3 4 4.0 8/20 Excellent 0 4 4 0.0 0 4 4 0.0 Slough 6A 112.3 8/7 Fa ir 0 35 35 0.0 6 29 35 5.8 3 32 35 11.7 Lane .Creek 113.6 8/7 Excellent 20 484 504 25.2 89 56 504 5.7 8/13 Excellent 2 630 632 316.0 118 514 632 5.4 8/19 Excellent 5 507 512 102.4 68 444 512 7.5 8/25 Excellent 2 238 240 120.0 26 214 240 9.2I8/31 Good 0 4 4 0.0 0 4 4 0.0 Lower McKenz ie 116.2 8/19 Excellent 0 15 15 0.0 ,1 14 15 15.0 Creek !i/25 Excellent 0 6 6 0.0 3 3 6 2.0 I McKenzie Creek 116.7 8/19 Excellent 0 13 13 0.0 5 8 13 2.6 I I I i Appendix Table G-2-4.Continued. 10.8 14.8 465 177 LUCATIUN ~UN~HINt.IA(;j~TALKEETNA TAGS CURRY TAGS River!J Survey Tagged Tota 1 Rat io Tag Jed Total Ratio TagJed Total Ratio Spawning Area Hile Date Conditions (r)Untaooed (c)(c/r)(r UntaQoed (c)(c/r)(r UntagQed (c)(c/r) Little Portage 117.9 8/13 Excellent 0 138 138 0.0 26 112 138 5.3 Creek 8/19 Excellent i .0 46 46 0.0 8 38 46 5.8 8/25 Excellent 0 46 46 0.0 4 42 46 11.5 Moose Slough 123.5 8/6 Fair 0 8 8 0.0 I 1 6 8 8.0 I 1 7 8 'S.O 8/12 Excellent 0 6 6 0.0 j 0 6 6 0.0 .•'0 6 6 0.0 5th of July 123.7 8/6 Excellent 1 16 17 17.0 I 2 15.17 8.5 0 17 17 0;0 Creek 8/12 Excellent 0 61 61 0.0 I 9 52 61 6.8 8 53 61 7.6 8/19 Excellent 20 93 113 ~.7 17 96 113 6.7 15 98 113 7.5 8/23 Excellent 0 15 15 0.0 1 14 15 15.0 3 12 15 '5.0 Skull Creek 124.7 8/12 Excellent 1 11 12 12.0 1 11 12 12.0 3 9 12 4.0 8/17 Excellent 2 10 12 6.0 3 9 12 4.0 1 11 ,12 12.0 8/23 Excellent 0 6 6 0.0 2 4 6 3.0 0 6 6 0.0 Slough 8A 125.1 8/12 Fair 3 25 28 9.3 10 18 28 2.8 7 21 28 4.0 8/17 Good 0 5 5 0.0 0 0 5 0.0 0 5 5 0.0 8/23 Excellent 0 2 2 0.0 0 0 2 0.0 0 2 2 0.0 Slough B 126.3 8/12 Excellent 0 32 32 0.0 4 28 32 8.0 3 29 32 10.7 8/23.Good 0 2 2 0.0 0 2 2 0.0 0 2 2 0.0 Slough 9 128.3 S/17 Exce 11 ent 0 10 10 0.0 1 9 10 10.0 2 8 10 5.0 8/23 Excellent 1 8 9 9.0 3 6 9 3.0 3 6 9 3.0 8/30 Excellent 0 1 1 0.0 0 1 ::1 0.0 0 1 1 0.0 Sherman Creek 130.8 8/6 Excellent 0 5 5 0.0 1 4 5 5.0 I 1 4 5 5.0 8/12 Excellent 0 23 23 0.0 3 20 23 7.7 2 21 23 11.5 8/17 Exce 11 ent 1 3 4 4.0 .I 1 3 4 4.0 1 3 4 4.0 0 63 63 0.0 r 12 51 63 5.3 6 57 63 10.5 4 504 508 127.0 I 104 404 508 4.9 37 471 508 13.7I8/17 Excellent 2 463 465 232.5!97 368 465 4.8 II'43 422 I ,8/23 Excellent 1 176 177 177.0 i 31 146 177 5.7 I 12 165 _____"I 1 _ » I\) (X) 0) ~l ~ / I ;J ~~,J I )!1 }~J I I ~J I ) ~--'1 ---1 -----, ) ~--l 1 1 ----1 } J j » I\) 03 ...... Appendix Table 2-G-4.Continued. lUCAllUN ',IN'H 'N~TAGS IALKEETNA IA(i~CURKY TAG~ Ri verY Survey Tagged Total ~atio Tagged Total Ratio Tagged Total Ratio Spawning Area ~1ile Date Conditions (r)Untaqqed (c)c/r)(r)Untaqqed (c)(c/r)(r)Un tagged (c)(c/r) Slough 11 135.3 8/11 Fai r 0 39 39 0.0 11 28 39 3.6 3 36 39 13.0 8/17 Excellent 0 131 131 0.0 19 112 131 6.9 4 127 131 32.8 8/23 Excellent 1 101 102 102.0 14 88 102 7.3 8 94 102 12.8 8/30 Excellent 0 41 41 0.0 1 40 41 41.0 4 37 41 10.3 Gold Creek 136.6 8/11 Good 0 11 11 0.0 3 8 11 3.7 0 11 11 0.0 8/23 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 Slough 15 137.2 8/4 Fair 0 24 24 0.0 13 11 24 1.9 3 21 24 8.0 8/11 Excellent 1 130 131 131.0 33 98 131 4.0 8 123 131 16.4 8/17 Excellent 0 2 2 0.0 0 2 2 0.0 0 2 2 0.0 Indian River 138.6 8/5 Good 6 196 202 33.7 41 161 202 4.9 17 185 202 11.9 8/11 Exce 11 ent 11 724 735 66.8 125 610 735 5.9 47 688 735 15.6,8/16 Excellent 4 533 537 134.3 93 444 537 5.8 50 487 537 10.7,8/23 Excellent 3 235 238 79.3 29 209 238 8.2 15 223 238 15.9 't 8/19 Excellent 0 8 8 0.0 0 8 8 0.0 0 8 8 0.0 Slough 20 140.1 8/11 Excellent 1 50 51 51.0 15 36 51 3.4 1 50 51 51.0 ? 8/16 Excellent 1 63 64 64.0 13 51 64 4.9 3 61 64 21.3 8/22 Exce 11 ent 1 36 37 37.0 10 27 37 3.7 1 36 37 37.0 8/30 Excellent 0 2 2 0.0 0 2 2 0.0 0 2 2 0.0. Slough 21 141.0 8/16 Excellent 1 5 6 6.0 0 6 6 0.0 0 6 6 0.0 8/22 Excellent 0 7 7 0.0 4 3 7 1.8 0 7 7 0.0 8/29 Good 0 3 3 0.0 0 3 3 0.0 0 3 3 0.0 Jack long Creek 144.5 8/11 Excellent 0 15 15 0.0 4 11 15 3.8 2 13 15 7.5 8/16 Excellent 1 20 21 21.0 0 21 21 0.0 3 18 21 7.0 8/22 Excellent 0 5 5 0.0 1 4 5 5.0 1 4 5 5.0 Portage Creek 148.9 8/9 Exce11 ent 2 144 146 73.0 32 110 146 4.6 17 129 146 8.6 8/16 Excellent 1 165 166 166.0 22 144 166 7.6 15 151 166 11.1 8/22 Excellent 0 III 111 0.0 23 88 111 4.8 9 102 111 12.3 8/29 Fai r 1 14 15 15.0 1 14 15 15.0 1 14 15 15.0 1J Confluence of stream or their receiving water with Susitna River mainstem. Appendix Table 2-G-5.Chum salmon spawning ground surveys of selected spawning areas and resultant tagged to untagged ratios.Adult Anadromous Investigations.Su Hydro Studies.1982. > N (X) (X) LUCAllUN IA(j~TALKEETNA TAGS cUKln TAGS River Y Survey ra{g ed Total Ratio Tag}ed Total Ratio Tagged Total Ratio SpawninQ Area Mile Date Cond it i o.l1S r)UntaQQed (c)(c/r)(r UntaQQed (c}(c/r)(r)UntaQQed (c)(c/r' Birch Creek 88.4 8/14 Good 0 3 3 0.0 (lower)8/25 Good 0 2 2 0.0 Cache Creek 95.4 9/25 Good 2 66 68 34.0 Unnilmed Slough 96.9 8/31 Excell ent 1 '81 .82 82.0 9/9 Good 24 315 339 14.1 9/24 Good 1 .34 35 35.0 Unnilmed Slough J 97.1 8/21 Excellent 13 25 38 2.9 Fish Creek 97.1 8/15 Good 1 15 16 16.0 8/25 Excellent "14 16 8.0<- Byers Creek 97.8 8/15 Good 1 53 54 54.0 8/25 Good 12 405 417 34.8 9/3 Good 20 364 384 19.2 Troublesome 97.8 8/25 Good 22 563 585 26.6 Creek 9/3 Fair 1 47 48 48.0 9/9 Good 19 276 295 15.5 Slough 5 107.6 8/7 Good 0 2 2 0.0 2 0 2 1.0 Lane Creek 113.6 8/7 Excellent 0 1 1 0.0 0 1 1 0.0 8/15 Excellent 0 1 1 0.0 0 1 1 0.0 8/19 Excellent 2 1 3 1.5 1 2 3 3.0 8/25 Excellent 2 7 9 4.5 1 8 9 9.0 8/31 Good 0 10 10 0.0 1 9 10 .10.0 9/6 Excellent 0 1 1 0.0 0 1 1 0.0 Little Portilge 117.7 8/31 Excellent 1 4 5 5.0 0 5 5 0.0 Creek 9/6 Excellent 0 18 18 0.0 0 18 18 0.0 SloU9h 80 121.8 9/12 Excellent 0 4 4 0.0 0 4 4 0.0 0 4 4 0.0 9/25 Excellent 1 10 11 11.0 0 11 11 0.0 0 11 11 0.0 '\\ J j I I 1 I J I I J .I .t )I i J J l ,.~ .1'J =------J -------j .~ ) Appendix Table 2-G-5.Continued. "'-'----4 ~~ ) J » I\) 03 CO LOCATION ::iUNSHINE TAGS TALKl:.tTNA TAGS CURRY TAGS River!.}Survey Tagged Total ~atio Tagged Total Ratio Tagged Total Ratio Spawnino Area Mile Date Conditions (r)Untaooed (c)c/r}(r)UntaQQed (c)(c/r)(r)UntaQQed (c)(c/r) Slough 8C 121.9 8/29 Excellent 1 22 23 23.0 1 22 23 23.0 2 21 23 1l.5 9/12 Excellent 0 43 43 0.0 0 43 43 0.0 1 42 43 43.0 9/14 Good 0 4 4 0.0 0 4 4 0.0 0 4 4 0.0 Slough 88 122.2 8/15 Excellent 0 2 2 0.0 0 2 2 0:0 0 2 2 0.0 8/19 Excellent 1 8 9 9.0 0 9 9 0.0 0 9 9 0.0 8/22 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 8/31 Excellent 4 59 63 15.8 6 59 63 10.5 5 58 63 12.6 9/12 Excellent 2 25 27 13.5 1 26 27 27.0 1 26 27 27.0 9/14 Excellent 0 20 20 0.0 0 20 20 0.0 1 19 20 20.0 ~'oose Slough 123.5 8/6 Fair 0 2 2 0.0 1 1 2 2.0 0 2 2 0.0 8/12 Excellent 1 6 7 7.0 2 5 7 3.5 0 7 7 0.0 8/19 Excellent 2 7 9 4.5 1 8 9 9.0 3 6 9 3.0 8/25 Excellent 2 7 9 4.5 1 8 9 9.0 1 8 9 9.0 8/31 Excellent 2 19 21 10.5 3 18 21 7.0 1 20 21 21.0 9/6 Excellent 1 10 11 11.0 0 11 11 0.0 0 11 II 0.0 4th of July 123.7 8/12 Excellent 1 7 8 8.0 3 5 8 2.7 1 7 8 8.0 Creek 8/17 Excellent 7 71 79 11.1 5 73 78 15.6 5 73 78 15.6 8/23 Excellent 3 149 152 50.7 11 141 152 13.8 9 143 152 16.9 8/30 Excellent 5 131 136 27.2 1 135 136 136.0 6 130 136 22.7 9/5 Excellent 12 113 125 10.4 8 117 125 15.6 7 118 125 17.9 9/13 Fai r 0 4 4 0.0 0 4 4 0.0 2 2 4 2.0 9/19 Good 1 37 38 38.0 0 38 38 0.0 1 37 38 38.0 9/25 Excellent 1 17 18 18.0 0 18 18 0.0 0 18 18 0.0 10/1 Excellent 0 4 4 0.0 0 4 4 0.0 0 4 4 0.0 Skull Creek 124.7 8/31 Good 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 Slough 8A 125.1 8/6 Exce 11 ent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 8/12 Fair 7 73 80 11.4 12 68 80 6.7 5 75 80 16.0 8/17 Excellent 18 172 190 10.6 8 182 190 23.8 13 177 190 14.6 8/23 Exce11 ent 33 274 307 9.3 11 296 307 27.9 10 297 307 30.7 8/31 Excellent 33 240 273 8.3 8 265 273 34.1 15 258 273 18.2 9/6 Excellent 14 191 205 14.6 1 204 205 205.0 II 194 205 18.6 9/13 Excellent 1 61 62 62.0 0 62 62 0.0 2 60 62 31.0 > I\) COo Appendix Table 2-G-5.Continued. lULA UN <::IN':U"M.TAGS (H N,IAli~CURRY TIms- River!)Survey Tagged Total Ratio Tagged Total Ratio Tagged Total Ratio Soawn i nq Area Mile Date Conditions (r)Untaooed (c)(c/r)(r)Untaqqed (c)(c/r)(r)Untaooed (.c)(c/r) Slough 8A 9/20 Excell ent 0 17 17 0.0 0 17 17 0.0 0 17 IT 0.0 9/25 Excellent 0 8 8 0.0 0 8 8 0.0 0 8 8 0.0 10/2 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 Slough 8 126.3 8/12 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 8/19 Excellent 0 10 10 0.0 4 6 10 2.5 1 9 10 10.0 8/23 Good 2 14 16 8.0 4 12 16 4.0 0 16 16 0.0 8/31 Excellent 3 20 23 7.7 0 23 23 0.0 1 22 23 23.0 9/5 Excellent 3 33 36 12.0 3 33 36 12.0 3 33 36 12.0 9/13 Good 1 1 2 2.0 0 2 2 0.0 0 2 2 0.0 Slough 9 128.3 8/17 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 8/23 Excellent 2 43 45 22.5 1 44 45 45.0 5 40 45 9.0 9/5 Excellent 12 230 242 20.2 7 235 242 34.6 12 230 242 20.2 9/13 Excellent 3 106 109 36.3 0 109 109 0.0 6 103 109 18.2 Slough 9B 129.2 9/19 Exce 11 ent 0 4 4 0.0 0 4 4 0.0 0 4 4 0.0 Slough 9A 133.3 8/23 Good 2 23 25 12.5 1 24 25 25.0 2 23 25 12.5 9/6 Excellent 8 99 107 13.4 3 104 107 35.7 7 100 107 15.3 9/19 Excellent 0 2 2 0.0 0 2 2 0.0 0 2 2 0.0 Slough 11 135.3 8/11 Fair 1 19 20 20.0 1 19 20 20.0 1 19 20 20.0 8/17 Exce 11 ent 0 13 13 0.0 2 11 13 6.5 1 12 13 13.0 8/23 Excellent 8 156 164 20.5 5 159 164 32.8 6 158 164 27.3 8/30 Excellent 38 357 395 10.4 22 373 395 18.0 19 376 395 20.8 9/5 Excellent 22 257 279 12.7 8 271 279 34.9 8 271 279 34.9 9/13 Excellent 1 140 141 141.0 3 138 141 47.0 2 139 141 70.5 9/19 Excellent 2 64 66 33.0 1 65 66 66.0 1 65 66 66.0 9/25 Excellent 0 17 17 0.0 1 16 17 10.7 0 17 17 0.0 10/1 Excellent 0 3 3 0.0 0 3 3 0.0 0 3 3 0.0 Slough 15 137.2 8/17 Excellent 1 0 1 1.0 0 1 1 0.0 0 1 1 0.0 !ndian River 138.6 8/5 Excellent 2 14 16 8.0 4 12 16 4.0 0 16 16 0.0 8/11 Excellent 10 124 134 13.4 5 129 134 26.8 0 134 134 0.0 8/16 Excellent 11 351 362 32.9 20 342 362 18.1 9 353 362 40.2 8/23 Excellent 10 174 184 18.4 10 174 184 18.4 6 178 184 30.7 )•\ J I ]I J j )~I J .J J B I J J J I > f\) (I) ~ !j )I J )II )I j 1 ._J ~!,) Appendix Table 2-G-5.Continued. LOCATION I )UNSH HiE TAGS TALKEETNA TAGS CURRY TAGS RiverlJ I Survey Ta{ged Tota'Ratio Tagged Total Ratio Tagged Total Ratio Spawning Area Mile Date Condit ions r)Untaqqcd (c)(cJr)(r)UntaQQed (e)(cJr)(1')UntaQqed (e)(e/r) Indian River 8/29 Gcod 12 108 120 10.0 6 114 120 20.0 6 114 120 20.0 9/4 E~cellent 70 815 886 12.7 17 B69 886 52.1 33 853 886 26.9 9/12 Excel'ent 5 144 149 29.8 1 148 149 149.0 5 144 149 29.8 9;18 Excellent 0 32 32 0.0 0 32 32 0.0 0 32 32 0.0 9/30 Excellent 0 2 2 0.0 0 2 2 0.0 0 2 2 0.0 Jack Long Creek 138.6 8/30 Good a 2 2 0.0 0 2 ;;0.0 a 2 2 0.0 Slough 17 138.9 8/30 Excellent 1 3 4 4.0 0 4 4 0.0 a 4 4 0.0 9/18 Exce 1lent 0 2 2 0.0 0 2 2 0.0 0 2 2 0.0 9/23 Excellent 0 17 17 0.0 0 17 17 0.0 a 17 17 0.0 Slough 2C 140.0 1 f/22 Exceiient 1 2 3 3.0 ,0 3 3 0.0 a 3 3 0.0 i 8/30 Good 1 2 3 3.0 0 3 3 0.0 1 2 3 3.0 9/4 Excellfent 0 23 23 0.0 2 21 23 11.5 2 21 23 11.5 Slough 21 141.1 8/11 Excellent 1 6 7 7.0 4 3 7 1.8 0 7 7 0.0 8/15 E):ce 11 ent 7 82 89 12.7 7 82 89 12.7 10 79 89 8.9 8/22 Excellent 9 222 231 25.7 18 213 231 12.8 18 213 231 12.8 8/29 t>,ce 11 ent 31 537 568 18.3 43 525 568 13.2 36 532 568 15.8- 9/4 Excellent 37 578 615 15.6 I 17 598 615 36.2 29 586 615 21.2 I 9(12 Excellent 16 325 341 21.3 2 339 341 170.5 14 327 341 24.4 9/18 Good 0 28 28 0.0 1 27 28 28.0 1 27 28 28.0.L 9/23 b,ce11ent 1 16 17 17.0 1 16 17 17.0 1 16 17 17.0I9/30 EJ<Ce"ent 0 2 2 0.0 a 2 2 0.0 0 Z 2 0.0 Portage Creek 148.9 8/9 Exee 11 ent 4 21 25 6.3 2 23 25 12.S 1 24 25 25.0 8/16 Exee 11 ert 7 64 71 10 .1 5 66 71 14.2 :.66 71 14.2 8/22 Excellent 12 131 143 11.9 3 140 143 47.7 3 140 143 47.7 8/29 Good 5 1G 21 4.2 a 21 21 0.0 2 19 21 10.5 9/3 Exee',erlt 1 5 6 6.0 1 5 6 6.0 0 6 6 0.0 9/29 Exce lJ ent 0 3 3 0.0 C ~3 0.0 0 3 3 0.0 ~- 11 f:onfiuence of streiJJIl or their n;(t:1ving watet'~illil Susit.nil River main:.tem. Appendix Table 2-G-6.Coho salmon spawning ground surveys of selected spawning areas and resu1 tant tagged to untagged ratios,Adult Anadromous Investigations,Su Hydro Studies,1982. » r\) CD r\) LUCAI ION <;IIN<;I-IINI=TAGS TALKI::I::INA rAG~CORKY TAGS Ri ver!l Survey Tagged Total .~ati 0 Tagged Total Ratio Tagged Total ~~tiOSpawningAreaMileDateConditions(r)Untaooed (C)e/r)(r)Untaooed (c)(c/r)(r)Untaoqed (~l c/r) Answer Creek 84.1 9/25 Good 7 17 24 3.4 Question Creek 84.1 9/25 Good 61 308 369 6.1 Lower Birch Creek 88.4 8/14 Good 0 0 0 0.0 .8/25 Good 0 0 0 0.0 9/25 fair 7 34 41 5.9 Cache Creek 95.4 9/25 Good 0 2 2 0.0 Fish Creek 97.1 8/15 Good 5 37 42 8.4 8/21 Excellent 47 144 191 4.1 8/25 Exee 11 ent 0 1 1 0.0 Byers Creek 97.8 8/15 Good 0 0 0 0.0 8/25 Good 1 35 36 36.0 9/3 Good 5 51 56 11.2 Troublesome 97.8 8/25 Good 1 8 9 9.0 Creek 9/3 fair 0 0 0 0.0 9/9 Good 4 35 39 9.8 Unnamed Creek 97.B 9/24 Good 1 7 8 8.0 Whiskers Creek 101.9 8/13 Exce.llent 6 26 32 5.3 8/23 Excellent 28 106 134 4.8 9124 Good 0 39 39 0.0 Chase Creek 106.9 9/17 Good 0 1 1 0.0 0 1 1 0.0 9121 Excellent 0 1 1 0.0 0 1 1 0.0 9127 Excellent 4 22 26 6.5 0 26 26 0.0 Slash Creek 111.2 9/21 Excellent 1 5 6 6.0 a 6 6 0.0 .~,) j' J I J I ])J )J J .~1 1 ~)J J J J 1 }1 )-]J --l ) --------i ~~ Appendix Table 2-G-6.Continued.( > f\) CO CAl LOCATION SUNSHINE TAGS TALKEETNA TAGS CURRY TAGS Riverll Survey Tag~)d Total Ratio Tagged Total Ratio Tagged Total Ratio Spawning Area Mile Date Conditions (r UntaQQed (c)(c/r)(r)Un tagged (e)(e/r)(r)Un tagged (e)(e/r) Gash Creek 111.6 9/23 Excellent 10 44 54 5.4 7 47 54 7.7 9/27 Exce llent .8 40 48 6.0 7 41 48 6.9 10/2 Excellent 3 14 17 5.7 0 17 27 0.0 Slough 6A 112.3 8/19 Excellent 5 19 24 4.8 3 21 24 8.0 8/25 Excellent 3 16 19 6.3 2 17 19 9.5 Lane Creek 113.6 8/13 Exce llent 0 1 1 0.0 0 1 1 0.0 9/6 Excellent 1 0 1 1.0 0 1 1 0.0 9/14 Excellent 2 1 3 1.5 0 3 3 0.0 9/21 Fair 1 0 1 1.0 0 1 1 0.0 Lower McKenzie 116.2 9/14 Excellent 24 51 75 3.1 20 55 75 3.8 Creek 9/21 Good 18 59 77 4.3 5 72 77 15.4 9/27 Excellent 11 50 61 5.6 6 55 61 10.2 10/2 Excellent 3 15 18 6.0 5 13 18 3.6 Little Portage 117.2 9/27 Excellent 1 3 4 4.0 0 4 4 0.0 Creek 10/2 Excellent 1 5 6 6.0 1 5 6 6.0 Slou9h 8A 125.1 9/20 .Excellent 0 3 3 0.0 0 3 3 0.0 0 3 3 0.0 9/25 Excellent 1 1 2 2.0 0 2 2 0.0 0 2 2 0.0 10/2 Exce 11 ent 0 2 2 0.0 0 2 2 0.0 0 2 2 0.0 4th of July 131.0 9/13 Fair 0 1 1 0.0 0 1 1 0.0 1 0 1 1.0 Creek 9/25 Excellent 1 2 3 3.0 0 3 3 0.0 0 3 3 0.0 10/1 Excellent 0 1 1 0.0 0 1 1 0.0 0 1 1 0.0 Slough 15 137.2 8/11 Excellent 3 5 8 2.7 1 7 8 8.0 2 5 8 4.0 8/17 Excellent 1 1 2 2.0 2 0 2 1.0 0 2 2 0.0 Indian River 138.6 8/16 Excellent 0 8 8 0.0 0 8 8 0.0 1 7 8 8.0 8/29 Fair 3 9 12 4.0 2 10 12 6.0 1 11 12 12.0 9/4 Excellent 5 9 14 2.8 2 12 14 7.0 3 11 14 4.7 9/12 Excellent 7 18 25 3.6 2 23 25 12.5 2 23 25 12.5 9/18 Excellent 9 11 20 2.2 3 17 20 6.7 4 16 20 5.0 9/24 Excellent 12 128 140 11.7 7 133 140 20.0 4 136 140 35.0 9/30 Excellent 1 22 23 23.0 2 21 23 11.5 6 17 23 3.8 Appendix Table 2-6-6.Continued. LOCATION TAli::>I.ALKtt.l NA TAGS C/jRRY TAGS Riverll Survey Tagged Total Rat io '.Tagged.Total Ratio Tagged Total Ratio Spawninq Area·Mile Date,Conditions'"(r)UntaQQed (cl (c/r)(r).UntdQQed (c)(c/r)(r)Untaqqed{c)(c/r) Jack Long Creek 144.5 9/30 Good a 1 1 0.0 a 1 j,0.0 a 1 1 0.0 Portage Creek 148.9 8/22 Excellent a 1 1 0.0 a 1 1 0.0 a 1 1 0.0 8/29 Good a 1 1 0.0 a 1 1 0.0 a 1 1 0.0 9/24 Excellent 10 121 131 13.1 3 128 13i 43.7 2 129 131 65.5 ~l!Confluence of stream or their receiving water with Susitna River mainstem. ~ ~ ~ I I j ))I I ].~.1 J J I J J !1 APPENDIX 2-H STOCK SEPARATION REPORT - I~ <DNPARISON OF SCALE PATrERNS FROl-l 9XKEYE SAUial SN-1PLID FooH DIFFERENT S'IDa~S n~WE SUSITNA RIVER IN 1982 By Dav id R.Bernard Glen Oliver Hill iam Goshert and Bev Cross Alaska Department of Fish and Game Division of Cornnercial Fisheries Statewide Stock Biology Group January,1983 TABLE OF COlJ'l'EN'l'S Section .-LIST OF FIGURES ................................-............•i LIST OF TABLES ..-......•....................................ii J\B S'IRACI'•••••••••••••••••••••••••••••••••••••••••••••'.• • • • •v IN'lIDOOCfIOi'1 •••••••••••••••••••••••••••••••••••••••••"••••••1 L·JE'UIODS .0 •••••••••••••••••••••-•••••••••••••••••••••••••••••2 •••••••••••••••••••••••••••••e~••-•••• ·. .......................................................... 2 2 4 4 7 Sample Collection Age CoI11[nsition •••..•"•.••••••••.•••••'•••••••.•'•.••.••• Comparison of Scale Patterns Scale £.Ieasurements Classification f~trices RESUL~••••••'••••••••••••'•••••-•••••••••••,_••••".'•••a'•.••• • • • •8 ............................... .......................................Age Ccm{:X)sition Comp.arison of Scale Patterns Variable Selection Classification Accuracy ·. ·. 8 8 8 12 DISCUSSION •••••••••••••••••e _••••••••••••••••••••••••••••••18 ACFJ,IQ'VLEOO.Er·1Et·fl'1S ••••••••••••••••••••,•••••••~• • • • • • • • • • • • ••23 LITmA1URE CITED ...........................................24 LIST OF FIGUHES Figure 1.Hap of Susitna River ano sampling sites for sockeye salmon in 1982 •••••••••••••••••••••••••••••3 2.Photograph of a sockeye salmon scale shooing, the three zones measured •••••••••••••••••••••••••••••••5 3.Frequency histograms of the most discriminating scale pattern'variables used to compare stocks of sockeye salmcrn from within the Susitna River in 1982 •••••••••••••••••10 -i- LIST OF ri'ABLES Table· 1.Variables computed from scale patterns for inclusion in the linear aiscriminant function analysis "...............•............•.e......6 2.Age composition of sockeye salmon samples from Curry Station,rl'alkeetna Station, Larson Lake (Talkeetna River),and Tokositna River (tributary to Chul itna River)••••••••••••••••••9 3.I~an values and stanaarddeviations of scale pattern variables •••••••••••••'••••••••••••••••~11 4.Four-way jackknife classification matrix £rem aiscriminantana1ysis of scale patterns on soch'lye salmon of age 1.3 san1pled from escuJ,:;ements at Curry Station,Talkeetna Station, TOKositna Rivers,and Larson Lake in 1982 •••••••••••••13 's.Three-\.;ay jackknife classificCJ.tion matrix from discriminant analysis of scale patterns on sockeye salmon at age 1.3 sampled from escapements at Cu~ry Station,Tokositna River, and Larson Lake in 1982 ••••••••••••••••••••••••••••••14 6.1w~ay jackknife classification matrix fram discriminant analysis of scale patterns on sockeye salmon of age 1.3 sampled from escapements at Curry Station ana Tokositna River in 1982 ..,.e.•••e._•••".• • • • • • • • • • • • • • • • • • • • • • • • • • • ••15 7.~\vo-way jackknife classification matrix from dis,cri.minant analysis of scale patterns on oockeye salmon of age 1.3 sampled from escapements at Curry Station and Larson Lake in 1%2 .••..•..\•••'.•-:................................16 B.T\'lo-way jackknife classification matrix [rum uiscriminant analysis of scale patterr.s on sockeye salmon of age L 3 sampled from escapements at Tokositna Hiver and Larson Lake in 1982 ••••••••••••••••••••••••••••••••••••••••17 a....r,)ost fOweriul scale pattern variables in the linear discrim~nant functions according to the frequency tbey awear in all rive models and to their strength in the ONo-Nay and three-way mooels ••••••••••••••••••••••••••••••• -ii- 19 - .- - ABSTRACI' Scale pattern analysis with linear discriminant functions \-las used to examine the probable fate of sockeye sali~orl fry spa\'lned upstream of Curry Station on the Susitna River.Scale samples were taken from sockeye salmon collected at Talkeetna Station,at Curry Station,trom the Tokositna River,and from the confluence of the outlet from Larson Lake and the Talkeetna River.Fish aged 1.3 aominate the silmples and are used in the analysis.Gro.vth during the first season of 1 ite (1977)is the most discriminating scale pattern variable. Scale patterns from fish sampled at Tokositna River and at Larson Lake are most different.Fish froTIl Larson Lake grew slOVler for a longer period of tline than did fish from the Tokosi tna River.Fish from Talkeetna Station on the Susitna River are more like·fish samFled at Larson Lake on the Talkeetna River.Fish from Curry Station are misclassified as being from Tokositna River or from Larson Lake more often than from upstream of Curry .Station. Sockeye salrr,on passing Curry Station are probably not a separate stock,but are strays from Talkeetna and Chulitna Rivers.Fry hatched upstreaQ of Curry Station most probably oieor move to the lower Susitna to rear. -iii- IH'IRODUCl'IOH The Adult IUladrornous Fisheries Studies of the Susitna Hydroelectric Project, Alaska Department of Fish ana Game is charc;ed with describing the fisheries resources in the Susitna River with estimating probable impacts of proposec !"'." dams in the upper river.To meet this end,personnel of the Department conducted extensive field studies on the Susitna River in 1981.Field sampl ing in 1982 was altered to provide inform~tion not obtained through the program in 1981.This report,authored by personnel (;f the Statewide Biology Group in cooperation with the Adult Anadromous Fisheries Project,contains analysis of this new intormation. Al tho~gh an est ima ted 2,8 a4 sockeye sulmon (QncQrynchu~nerka)passed Curry Station in 1981 (ADFG 1981),no notable fry rearing activity was obserVed north of this station that year (Bruce Barrett,personal cOIiUUunication). About 98.5 percent of the sockeye aaul ts caught at Curry Station have at least one freSI"5'later check on their scales.If the spawn of the sockeye salmon that passed Curry Station did not rerJain upstream of tl:is station to rear, then where did they go? In 1982,personnel 01 the Aault ~D2dromous Fisheries Project collectea scales from sockeye salr.,on ac:ul ts from tour 5i tes in the Susi tna niver \'/ater shed ana gave tnese scales to the Statew iae Stock Biology Group for onalysi5.To indicate possible rearing locations for try,we searched for similari ties and differences arJong scales patterns 'vllth 1 inear discriminant an<J.lysis. -1- [·1ETHODS Sample Collection: Scales were taken f rom esca~ments of sockeye salmon at Curry Stution on the Susitna River,at Talkeetna Station,at the confluence of the outlet from Larson Lake.anti the Talkeetna River,and .:It the Tokositna River \V'hich is a tributary to the Chulitna River (Figure 1)•Sockeye salr:lOn were collected with fish wheels at Curry ana Talkeetna Stations.Scales were collected from the left side of the fish approximately two rows above the lateral line and on tne diagonal rO\-1 ClOl;lI1\'lard f rom the poster ior insertion of the dorsal fin - (n.WFC 1961). Aqe CQIDwsitioni. Sockeye salmon ages were determinecl through visual examination of scale samples.Scales were mounted ongurn cards and impressions were r.1ade in cellulose acetate (Clutter and ~'Jhi tesel 1956).Ages were recorded in European l notation.Because 1.3 tish predominate in the samples,only scales fran these fish are·used in the analysis. "'"'I 1 European·formula:··Nl.II11erals lJreceeuing the Liecimal refer to the number of freshwater annuli ~numerals io110"Wing theuecimal are the nurnberof marine amuli.Total age is tne sum of tJ:::ese two numoers plus 1. -2-~, - - Figure 1.Map of Susitna River and sampling sites for sockeye salmon in 1982. -3- I I Com}2riSQD of Scal~Patterns: Scale Heal:iurements: Scale impressions were llIagnHieci to 100 l-Dwer and projected onto t:l digitizinq tablet using equil:ment siruilt:lrto that described by l~yan and Christie (1976). Data were recorded onto computer diskettes irem the digitizer tablet uncler control of a FORTP~~prograr.\executin9 on a microcomputer.Scale measurements vlere taken along a stanuarciz<!5 axis Cl[.proximately 20 degrees oft the primary axis and perpendicular to tbe ~culptured fielu.'l'he distance between each circulus in G<:lCLl ut tbree Lcal12 IDttern zones \'Ja5 measured.Tlle zoneu were: scale tocus to the last circulus of the first freshvJa~er annulus;the last circulus ot the first f·reshwater annulus to the last circulus of the second freshwater annulus (the zone of plus gra.;rth);the last circulus of the second freshwater annulus to the last circulus of the first marine annulus.The three zones are shown in a photograph of a scale from an age 1.3 sockeye .salrc.on (Figure 2)•A set ot 11 variables was then computed for each of these three zones ('rable 1).Only normally distriuutcd variD.bles were used to builu 1 incar uiscrimin,mt functions. In though all scales were ageu,not all scales were measured.Scales fran sockeye salmon other tb.ari age 1.3 were not r.leasured./\lso,no more than 100 randoIll1y selected scales were measured from each sample:100 is a number sufficiently large for linear discriminant analysis.If a sample contains , less ttan 100 scales trcm 1.3 tish,as liO sanples frcm Curry Station unG frail 'I'okositna River,i)11 usable scales were measured. -4-~". """ - >----ZONE a :~~---ZONE 2 >---ZONE , Figure 2.Photograph of a sockeye salmon scale showing the three zones measured. -5- Table 1.V<.iriables comFutcd f refa scale p.:l.tterrls for inclusion in the 1 iDear aiscril'linont luncticn analysis. ---------------------~----------------,----------------------------------------- Vari able IJi1Iile liC (i)1/ ID (i) '1\10 (i) FOUH(i) Se~(i) 1 (j\EIGlJ"l'(i)I LIil(i) rll'::(i) alIi)(i) Uk\f:(i) [J(ll(i) Ll:;~(;'lH 1/\"Jhere i~l,2,3. Description 11lIrliber ofci rcul i in zone (i). lieasureQsize of zone (i). Distance frau tne begilminCj at zone (i)to tte L~conu circulus of z~le (i). Distance hem tbe beginning of zone (i)to trk tourtn circulus of.zone (i). Distance frci:":the be~dlming of zone (i)to tilC: si:a:L circulus of zone (i). Dist.:lilce iran the beginning of zone (i)to tr.e eigntn circulus of zone (i). Distance bet\-lt.'e11 the Q.lO closest circul i in zone (i)• The r;l.:lximLiili uistance bet1;leen b-1O contiguous circuli in zone (i). 'rile distance fran the _beginnins of the zone (i)to the tirst circulus ot variable i-lIlJ(l)in :wne (i). The distance f run the bCgirming of zone (i)to the drst circulus of variuble (';}'.x(i)in zone (i). 'l'hellllIaber of circuli in tbe first [lair of zone (i). 'l'i1e rork lengtt or the t iSh. ))\ )I J J ),B J J ].J )I )~,I ...., [ - - Classif ication {;Ia trices: Scale Patterns for sockeye salmon from each sample were compared with linear discrUninant function analysis (Fisher 19361 Dixon and Erown 1976).To build a single discriminate function,a stepdise procedure was used to select those scale pattern variables with the most discriminating power.Variables were added to the function until those remaining could not meet the cri ted an for inclusion (a F ratio set at 4).To build a single classification matrix for all stocks,a jackknife procedure was used.2 Classification matrices were built for a Talkeetna-Curry-Tokositna-Larson canparison,for a Curry-Tokositna-Larson comparison,anc)for all possible two-way cOf.lparisons among samples from Curry Station,Tokositna River,and Larson Lake.Samples fran Talkeetna Station were not used in any three-way or t\'o'O-way comparisons because these samples coUld have contained fish that migrated on to Curry Station • 2 A discriminate function is built on scale variables for a.ll sar.lpled fish but one.The function is then used to classify the stock of that one fish. Since the stock of that one fish is known,so therefore is the veri ty of its classification.The procedure is then repeated only with a new fish excluded. The jackknife procedure continues until all sampled fish are classified. -7- ,..". t.CjQ COIDr;ositioU; Or the 853 ~()c[.~eyc :.K.llllpleLl,over two-tlJin.1s are ~gc 1.3 tish ('rable 2).This dominance is consistant over all sam~ling sites save Curry Station where ages are almost evenly distributed.IJowever,the age cOr.lposition of tte iish sampled at Curry Station is probably a poor estir,1ate of the age composi tion ot the sockeye salmon ,that passeci this ~tation because the sample is small and vJas ta~~en over a 59~cJY period.l\lthouqhmore Ush were sampled at:.Talkeetna Station,tne S':HLlplinCj f.,c:riou i~lon~1 here <..l!::lC><.lI1U attccts the precision ur the estimate of age composition of fish that FJ.sSeQ this station as well. Comparison of Scale Pat,ten:s; Variaole Selection: ~\ Ilo~t scale lJ,-tttern Vi..lriilllles ill tile cilIllpleLi <.Ire normally distributed (e.9., Fisure 3).Each of the two most ui~crirlliri<:lting variables (SIXl am.:.HC1)have sirhilar stanuard cleviaticns in sauflles from Talkeetna Staticn,Tokositna River,and Larson Lake,but have different means (Table 3).For both these variables,their distributi'J'_I.tbe sam[:.le from Curry Station is somC".olhat __ bimodal,est;:ecially for SIXl. --8- -,J !I 1 J I >J J 1 J I )j D 1'})/ 'l'atJle 2.[.0';:COflltXlsiticn 0:[sod~eye @lmon samples fran curry Station,'I'alj~ectna Station,Larson wt~e ('l'alkeetnc Hiver),anu 'l'okositna River (tributary to Chulitna River). 1.3 Lomt i Ofl 'rota1 1.2 sampleu Digitize.'C!Other Da te Sampl ed ---------~-----------------------.------------------------------------'------------------------------- Curry Stc.tial 110 30 43 43 37 7/11 -8/2B/82 'l'alkE£tta Sti-ticn 378 56 291 100 31 6/7 -9/9/82 Tol~ositr.a Eivcr leS 86 97 94 2 8/7 -8/8/82' La rson/Tu1 f~ee tniJ lUO 31 147 100 2 8/6/82 Conil uerlC€ I ---------\0 I Total cl 53 203 578 337 72 1/SC~le ~ttern variable measureG. Ne1 ... N r- - -- ..i SI X 1 - Figure 3.Frequency histograms of the most discriminating scale pattern variables used to compare stocks of sockeye salmon from within the Susitna River in 1982. -1.0- I 1 ~l 1 1 1 I 1 ) J )I 1 1 J ]) Table 3.I'lean values and standard deviations of normally distributed scale ~ttern variables.1/ •__MW •••_ __________________________________.I __ __ Talkeetna St.Tokositna River -.._------ Standard Deviation Larson/Ta1keetna Hean --------------------Standard DeviationHean Standard Deviation Curry St. (~an Standard DeviatiooI'lean Variable '1H01 FOUR! SIXl EIGlrr1 HAX1 HINI NC1 ID1 UClll I.....T.'J02 'I FOUP2 SIX2 EIGlfl'2 Hi\X2· lUN2 UIl'.J(2 Ne2 ID2 NCB 2 'IH03 .FOUR3 SIX3 ·EIGHT3 I'lAX3 l'lIlB UlAX3 Ne3 lD3 I,Fl~G'llI NOn 42.6 64.6 83.9 96.6 30.7 6.2 10.9 125.8 3.4 20.5 2fj.7 26.1 8.4 13.4 8.2 2.9 4.9 51.7 1.9 30.3 62.7 97.6 133.8 26.4 9.5 8.9 22.6 357.3· 576.4 10.0 5.2 7.9 10.3 25.4 4.2 1.4 2.0 22.3 1.0 4.9 20.0 31.9 25.4 2.6 2.0 1.8 2.1 22.8 1.1 7.2 11.1 13 .9 16.6 5.3 1.6 5.5 2.4 40.6 35.5 1.3 42.2 64.7 84.5 91.0 29.6 6.4 9.9 118.7 3.1 22.2 37.5 31.2 17.8 14.4 8.1 2.9 5.6 62.2 2.3 30.8 63.1 96.4 131.0 24.3 9.3 8.9 23.6 362.3 565.1 10.5 6.5 10.3 13.2 36.3 4.6 106 2.1 22.7 1.2 4.6 17.8 32.7 35.4 2.5 1.7 1.9 2.2 23.4 1.3 5.6 9.5 1103 13.4 ~.3 1.7 5.5 3.4 47.9 43.2 1.7 46.1 71.9 93.9 98 .6 31.6 7.1 9.3 125.6 2.7 21.6 38.6 31.9 15.3 14.7 9.2 2.B 5.3 61.9 2.2 32.0 65.7 100.4 135.7 25.4 9.6 8.7 22.9 361.3 574.3 HI.1 6.7 8.8 1105 41.8 5.1 1.9 1.9 27.9 0.9 7.2 19.2 35.4 34.2 2.9 1.9 107 2.3 26.6 1.2 6.2 9.2 11.5 13.8 4.8 1.5 5.2 2.6 38.:,; 26.4 1.3 42.2 64.5 83.8 97.9 29.9 6.0 10.7 123.9 3.3 20.6 36.5 25.2 5.5 13.1 7.9 2.8 5.3 54.0 2.1 29.0 59.9 93.4 129.3 26.0 9.2 9.5 22.9 ;:;Jv •~~ 57S'.7 10.4 5.3 7.1 8.8 19.6 4.1 1.3 1.8 19.4 0.9 4.1 14.4 30.8 20.3 2.3 108 1.8 1.6 16.9 0.9 6.1 10.7 12.9 15.1 4.6 1.6 4.9 2.4 3(:.3 27.9 103 ----------~----------~---------------------------~--------------------------------------------- 1/Based on 100 fish sampled at Talkeetna station,43 fish at Curry Station,94 fish at Tokosi tna River, and 100 at the confluence of the outlet from Larson Lake and the Talkeetna River. Classification l\iccuracy: The overall accuracy of the four-wayraodel (all sar.lples included)is alrr:ost 50 percent (Table 4).Fish frora Larson Lake are r.1.ost lil~e those from Talkeetna Station wbile fish tram Tokositna Hiver arc morc unique.Fitjl)trem Curry Sr..i.ltiun L.lre l110lit otten 1lli.~~duti:..;iLi(~d Litl l)ein~j trom either 'I'o.~ositna River or Lar.son Luke anu are miscli,lss it ieLJ morc otten than not.CueGssinq at the origin of fish ar.lOng four stocks would produce 25 percent accuracy;the accuracy ror fish from Curry Station is little better than guessing while accuracy for the other samples is tvJO to three times better. The overall accuracy of thethree~way ~ooel (Curry-Tokositna-Lar~on)is aDOut 62 percent (Table 5).i\ccurucy in cla::mityinq Larson Lake ti::;h and rl'okosi tm.l Hiver tish is much higher t1lc:H1 th,"t lor Curry ~::tc::tion fish.Cuessinc.l the origin or fish among three stock~would produce a 33 percent accuracy,a level not even attained tor tish irem Curry Station.'l'he r;;erccnt offish from Curry Station misclassitied is split about evenly between the Tokosi tna.River and Larson Lake. The overall accurc::cies of the tWO-Wily f,louels·is about 70 percent for Curry~okositna.(Table6),about 69 percent for Curry-Larson (Table 7),and ubout b 1 percent tor Tokositna-Larson (Table 8).Cuessingwoulli prouuce an accuracy ot 50 percent;all t.\vo-vJay moclcls,esr:ecially the To~~os i tna-Lar son, aiscriminate wich accuracy nillch higher than 50 percent. -12- i J ·'-1 )I 1 i )·1 J ]1 R J 1 ~-,) )" !J 'l'dule 4:.FoiJr-iiay jackkfiife classitication matrix from discrir.lina.nt allClysis of scale r.ar.terns on sockeye solmon of age 1.3 sarnpleu trCf;l escat~ments at Curry Station, T.:llkeetn.d.Station,TakositIta Rivers,and LarEDn Lake in 1982. ---------------------------------------------------------~------------------------------- Actual Gr0Lp of Ongin Sample Size Classified Grou~p of Origin--.------------_.------_. Talkeetna St. rl'all~(;etau St.100 •43 - Lc::.r son/tal Kffrna.IUD .20 '1'01:05 i tna i:iver 1)4 .oe I..-Curr:/St.43 .OUw I Lcr50n/Talkeetna .28 .46 .ou .33 Tokositna R.Curry St• .15 .15 .13 .21 .67 .17 .26 .33 Overall classiricationaccura~l=.495 l!ou::Unuerlwf:C:iXGi::ortions represent prol:Qrtion correctly classii ied. All otLEr f'rul-ortions are misclassifiea. '1'001(;S.'.l'nrE:e-\vilY jad:knite cL.l~sitication TilUtri;;;:[nXil uiscrir;iillc.llt itll<_lysi:.; or bCcile l:AALterlili ull sockeye salmon at age 1.3 setf.lLJleu trcfll e~cur.efllents at Curry Stction,'l'okositna Hiver,anLl L;:;rt:on LaJ~e in 10£;2. Actual Croup ot Ori'jin Sample Size Classifieu Grcup or uriyill I....... .p- I Lan:on/1'a11~eetna 'l'okosi tIla H.Curry St. [.(;.r :;,on/Tal kCetllo luD .n .ll .16-- 'i'OKosi tllGi niver ~.i';.13 .66 .21 Curr~'St.43 .40 .35 .25 Overall·classif ication ~lccurciCY =.616 l:ut:e:Ulll••cr lineu uroLDrtioo5 rC::L,re::-;ent i.,rOrorticll currect:ly cldo:sir ie<.o. III otiil::r to[({.onions are uisclassit ied... )~\ I J I I J J J ~~)],I J J ]~...~ )J ]i i 1 J j 1 J j B )1 J 1 J j )) 'l'",ule 6.'l\io-\iC.iY jacf:knife calssifica.r.ion lLlatrix fra.\<liscriminant analysis 01 swle [--att€:rns on socb:~ye sal.rlon ot a~]e 1.3 sahlUleo rrun e~t.clilents at Curry Si.:c.tiun,'l'okoEitnu H.ivcr,':>11U Lan::on Lal:c:in l~2. i>ctl...lC.l Grcllp or Origin Sill"r,le Size Classifit'O Group of Origin I..... ln I 'l'okosi tna H.Curry St. 'l'cikosi bkl r:.~t}.7U .30-- Curry St..'13 .30 .70 CNeraU cla:::,sif icatic:n accur2cy =.701 ilow:UIlC,erl1nc;u £irotvrt.icllS repres~nt t,r0l-Drl:lCn correctly classirieu. Hi ctl,(;r l[ljL;Cnic.I~'are l,iiscJ.abSldl:-U. TaGle 7.'1\10-\';<.\1'jacl.:lmife calssification llIatrh:1:raj ciiscri;"imnt ~nulysiG of scale patterns on sockeye salrnon of at.:ic 1.3 SdflliJleu t rLin eSCar€I.lents at Curry Station anu Larwn Lilke in 1982. l'.ct\JQl ercup or Oriyin SaLiple' "Size Classifieu Group of OrigHl La r bC,n~l'al KeetmJ. ,Curry St. lUO 43 Larson/Talkeetna .72 .40 Curry St. 'J"•..:.U .60 I I-' '"I OVerall classit ication accuracy =.GUS iJot:c:Un~rl ineO prol.ortions rel-,re~nt ljrc,portioll currectly classH ieU. lUi Gtuer l-,r0i:0rtions are rl1isclassit it.>u. )\ / J ~I )~J t I 1 »J ~,)J J ! '. I J -1 )I )J J )J J J j J j J '1 I ~}"~ ) 'l'~U.le U.':..'.:c,-'::<.J/jcJckkniLe calssiI iQit10il i;,c<tri;~t ((Ail l.i~;crilliil1allt ::,.21:.:""1::"at sCClle h:atterrcS 0n wci:eye salH.on 01:uSC 1.3 ",~.,!..J.(;,-,J:[I...Ll (;~cal:eh:elits at '.l.'o;;,uGitnu niver anli Lc:.rwn L2.,;·,:in 1~2. j~tual Gr~) Or (lrlsin Salilple C;ize Class if ic.-u Gr0l.Jl1 of Ori<;111 u.rwn/~·al~i;;E:t.rL.l '1'ol·:o::,i LlJ5 •.• lUO % La rbOn!'la1 Keetna .84 .22 rl'okosi tna R. .16 .73 I.-. -....I I Gverall clLlssitication accuracy =.809 liot\:::Ui,lkrll:::::'':''l)rq.oniom,rerrese:-nt l>rc'l:-crtion correctly classit ieu • .fo-Ll cc,,::[erq-Grtiom;are iniscldssit 121:..• I I The scale patt.etn variables SIXl (length to the sixth circulus in the tirst zone)and HCl (number ofcirc~li in the first zone)have the most ciiscriminating po\/er (Table 9).Uov<:Jriable appeared in ull five models,but SIXl appeared in four and NCl appeared in three.Botbvariables accounted for much of the observed variation in in scale patterns,.and both had their greatest independent effect in the Tokositna-Larson two""\'lay model.The length or the first zone (101)aid not appear in any discriminant function.About 85 percent at the scales from Tokositna River had eight circuli in the first zone \'lhile about 97 percent from Lurson Lake had ei9ht,yet there is little difference in aVE:rage t>ize o[the zone between sami:Jles.Th.erefore as first yeur fry in 1977,tish in'fukosi tna Hiver srf;.~"raster for tl.shorter I:€riod of tUne than did their counterparts in Larson take. In surc!1lary,sampled fish from Tokositna River ana Larson Lake are the r:lost different,Eish sampled at Curry Station are more 1 ike To~;.ositna and Lar son Lake dsh than cneyare unique,anG fish samplec.i at Talkee.tD.a Station are more like Larson Lake fish thtin any other.Differences (or the-lack of c.:ifrerences)among samples are due to gro.."th between hatching and the lilinter ot 1977-8. DISaJssIOU Scale pattern analysis is usually employed to separate the components of a .mixed stocKi for the stocks Hithin tt:e Susitna,scale pattern analysis is used to show sUnilarities.As such,linear discrll~inant analysis provides -18- """ - "'"" - ~'-~ ~I J J l j J )..1 }1 J J 1 )1 1 1 J ] j 'l'aule so.i·JO;..,t i-v.iCL:La.:::~le j,.atterrl variublcs in linear ciscrimillc.nt functions accorciing to tt!e nwaler to tnt.:nUd:...::r CL tUd:::L tlIey occur in five f.1ouels unu to tedr strengtb in the three-anl.i two-~'Jay (dO(;21~. I:'i ve loUf::l::.Four Louels '1'im::c l'1OUels '1\10 lloLJels One IbUel SIXl 1£:1 F()UK3 LU;G'l'H EIGll'l'2 j.!l0-:1 ilH12 H\X2 SIX2 IJC3 roo nUG l;ost SI~-~l 2.3.(; l.e"t:I;Cl 13 .:.. Curry-~okosiDic-Lc.r~on Curry-Larson Curry-'l.'okosi tna 47.6 33.3 F-rc.tio SIXl nCI Variable Tokositna-Lar~on 18.0 4.5 F-ratio SIXl LEI:Gl'i! Vc:riable 9.0 5.7 F-ratic LIGliT2 r.1~{2 Variablef-r.::.tio 1/Vd.riuLJle P()\'ler I....... \0 I 1/F-r2tic on resiaucl vGrial~es. "necessary condi tions"to sha....\'l!lat happens to fry spawned upstream or Curry St:ation;it does not provide definitive pro01:.Our analysis does sha.v that 1) scale patterns of sockeye salmon passing Curry Station in 1981 are more like patterns an scales of fish taken from the escapements to the Tokositna River anc.:to Larson Lake than they .:lre uniquean<..i 2).scale patterns on scales from Larson Lake and Tokositna laver are distinct Eor the 1977 year class.From these two facts (and other information obtained in 1981),six bYfX)theses as to why no fry are found above Curry Station are possibly true: 1.Sockeye salmon adults that SI;2Q.\'l0 in the slo.ugb~-Yb'stream of Curry station are homing to this area.anu their rryrear in lakes and slouoos in both the Chul itna and in the Talkeetna \'later sheets.If true,fry filust move down the Susi tna to the tributaries then upstream.Imprinting must occur after spawning and berare fry move out of the main river and upstream in the tributaries.Fry select a Vlatershed in which to overwinter according to which siLie 01:the Susitm they travel along as they move dlklnstream. 2.Sockeye salmon.adyl tD that EWlli1 in the sl.o.J.mUs L.Wll.QJlL.Q.L.C.un::L-.s.t.wlli.n are strays frorneitber tile ChiJlitna or the TaH;eetna watersheds.anel their fry rea r in 1 akes or slQughs flOW ing into either the Chyl itna or into the .'J.£ilkeetna River.In either case,imprinting must occur after fry enter the tributaries. 3.~ockeye salmon adylts that s~'dn in the sl~s IJPstream of Curry Station ~re str9;ls irem either toe Chulitna or the 1'g.ll.c.e.tca watersheds.and their fry arc cisriLaced QO\'lnst.I~m to become Q~heck fisb. 4.~J::Keve salmoo a~u.J..t.~L.thQ.L~.n_.i.lLthc~.\..\OlliLWl;'j.t.r.e.wliL.Qf CUrrY StMtj,Ctl s;;r c;St t'iJ y~llyn eU~.L..tl:&-.C.b.W..i.trli.l-oL.t~-'l'ill~tnaYlQ.t~~1UL-'ill.l..Lt.tleir try ~t'yiye i~..u pl,JJjlbers.i[at uU. 5.b siqntfican.t...lli.llr:ber of socke~re s41won adult~L.t.batr:qf;js CurryCJ;:.ation pre stra;ts t rum eitber CDe ChUl itna or '.I.'cilkeetDi:l Biyet's aru.l "to not SW\:lO rilbove Cut't';t Station,out moyebacl)dOVlDstt'eam to enter thei.LD~l streams. 6.Socls.eye salIDonadults that SWVlO uw~-Of Curry Station are a SElwrote stock whose try rear in an at'ea not samolea.Neither tile 'l'okositna River nor Larson Lake are rearing areas,but some area that has a heterogenous environment with parts similar to both these areas. -20... - - - ~I .- -. Although all six hypotheses are possible,some are more probable than others. The distance betvleen Curry Station and the To}~ositna River and Larson Lake make the first hypothesis rather improbable.Sockeye sal~on fry tend to imprint the memory their natal streams early.~long migration down the Susitna River then up either the Chulitr":l.or Talkeetna Rivers before imprinting is rather improbable.Also,the long journey through mvift \'later is not conducive to try survival,anu natural selection is a<;rainst such a stock occurring • The last hypothesis is unlikely as well.Scale patterns on fish taken at Curry Station sha.v these fisb not to comprise a unique sroup,but two groups, one with scale patterns sWlilar to patterns on fish from Larson Lake and one ,."i th patterns similar to those on fish from the Tokosi tna River.'l'he e}:i stance at a single rear ing area that could proLlUce such a group of scale patterns is not likely. 'fhat Ush moving past Curry Stu ti un are strays aUlD tbe Chul itna and tbe Talkeetna watersheds is more probable than these fish being a separate stock. The estimated numoer of sockeye salrr,on passing Curry Station is only 2.1 percent ot the sockeye salmon IXl,ssin0 ~LU1sbinL'Station (!lDFe 1981);sinCE:the rish passing Sunshine Stati0n cunt&in all Lish migratiny to the Talke~tna., Chuli'Cna,and the uEJstream Susitna lUvers,the small portion passing Curry Station coula easily represent strays. -21- \'1hat is the fate of "the spawn fror.l fish passing Curry Station?Again,the distances involved would mal<e pa ssage of fry down the Susi tna and up the Chu~itna or up the Talkeetna Hivers LU1likely.110re probably,fry would move dcwn the Susitna River to overwinter in sloughs,move Qut to Cook Inlet as O-check fish,or die.~ny one (or all}of these three situations could have occurred in 1977.Whichever is the "case,the result is extremely poor ~ production f rom these fish.IUl O-ched~fish represent only 1.5 percent of returning adults (Bruce Barrett~personal communication),and survival in river sloughs along the lower Susi tna River must be substantial if the 2.1 percent of the spawning stock above Curry Station is impor tant to the productivity of the Susistna River. FiSh passing Curry Station could have turned around and migrated back downstream,but this is not probable.Such a switch in direction would inflate estimates of escapement above the fishwheels at Curry Station although the estimate of the number passing the fishwheel would be correct.Yet peak spa\ol11ing counts (a conservative estimate of the number of fish)in sloughs above Curry Station in 1981 are 1232,almost half the fish esti.ma ted passing _, the Station (ADFG 1981)•. t-lost probably adult sockeye salmon passing Curry Station are strays ~ran the Qlulitna and Talkeetna Rivers and are not a separate stock.£.lost of thes fish spa\'l11 in sloughs above Curry Station,and their fry either move dO\vn to the Lcwer Susitna River to overwinter and/or die. -22- AQ<NQ'lLECGEI:'lENTS Sam Sharr,Hathy RCMell,Scott LlcPherson,and Scott narshall provided valuable ideas for the analysis.Addi tional thanks are due to Virginia Burton for shouldering the burden of constructins the tables in this report from our,..... pigdin notes,to Debbie Hicks for transcribing numbers,and to Scott llcPherson _for his art work. -23- LITEW\'I'URE CITED Alaska Department of Fish pnd Game.1981..&l.u.ll AnadrQIDoJ,15 fi~t~tojeet, Phase I Final Dip[t RepQ..U..'l\laska PO\'ler Authori ty and Susitna Hydroelectric Project.8usitna Hydro hquatic studies,2207 Spenard Rd., f~chorage,AK 99503.. Clutter,R.and L.~'lhi tesel.1956.Collection and interpretation of sockeye salmon scales.Bull.Int.Pac.Salmon Fish.Comm.,No.9, 159 p. Dixon,('I.and n.Bro.m.1~79.Bianeuical comt!Utcr'prO(;]rcU\1S p-series.Univ.of calif.Press,Berkeley.UUO p. Fisher,H.1936.The use at Illul til:le llleasurE:ments in taxonomic problems.J'~n.Eugenics.7:179-188. International North Pacific Fisheries Cor.lluission.1963.i\nnual Report 1961:167 p. Ryan,P.and H.Christie.'1976.Scale reading equifJTIent., Fisheries and Marine Service,Canada,Technical Report No.PAC!T-75-43,38 p. Personal CoulllU1ications Barrett,13.i·leBo dated ~;el?teH1ber 23,1982. -24- - - - -