TAHS
S
CH
AN
NS
OBL
(PRESENCE NOTED. REF#=26-2)
26-2
1980-01-01 00:00:00
Salmon
SPL
HQ0285
1996-09-01 00:00:00
CM
(THE CHUM SPAWN WAS CONCENTRATED IN THE MIDDLE AND UPPER REACHESOF THE RIVER. ESTIMATED ESC.:21,000, OPTIMUM ESC.: 25,000 REF#=KY016)
KY016
1992-01-01 00:00:00
CO
CT
(PRESENCE NOTED REF#=26-16)
26-19
Sport
PK
SK
WST
CAS
(DFO SISS DATA. REF# = HQ0280)
HQ0280
Other
(DFO RECORDS INDICATE CHINOOK SPAWN IN KAUWINCH RIVER. REF# = HQ0280)
(DFO RECORDS INDICATE CHUM SPAWN IN KAUWINCH RIVER. REF# = HQ0280)
(PRESENCE NOTED. REF#=26-2)(DFO SISS DATA. REF# = HQ0280)
(DFO RECORDS INDICATE THE COHO SPAWN IN THE KAUWINCH RIVER. REF# = HQ0280)
(DFO RECORDS INDICATE PRESENCE. REF# = HQ0280)
26-18
DV
(ESTIMATED ESC.:12, OPTIMUM ESC.:50,000.(NO LOCATIONS SPECIFIED) REF#=KY018)
KY018
(DFO RECORDS INDICATE PINK SALMON SPAWN IN KAUWINCH RIVER. REF# = HQ0280)
RB
(PRESENCE NOTED. REF#=26-18)
(DFO RECORDS INDICATE SK SPAWN IN KAUWINCH RIVER. REF# = HQ0280)
(DFO RECORDS INDICATE WST SPAWN IN KAUWINCH RIVER. REF# = HQ0280)
(ESCAPEMENTS: 200 (1990); 120 (1991); 600 (1992). AVG. 667 (1980-92). REF#=PH006)(ESTIMATED ESC.: 600 (1992). OPTIMUM ESC.: 10,000 (1992). REF#=KY027)
KY027
1994-01-01 00:00:00
PH006
(ESCAPEMENTS; 2000 (1990); 20,000 (1991); 17,000 (1992). AVG. 11692 (1980-92) REF#=PH006)(ESTIMATED ESC.: 17,000 (1992). OPTIMUM ESC. 30,000 (1992).  11692 (1980-92) REF#=PH006)
(ESCAPEMENTS: 2500 (1990); 1200 (1991); 2000 (1992). AVG. 1200 (1980-92). REF#=PH006)(ESTIMATED ESC.: 2000 (1992). OPTIMUM ESC.: 5000 (1992). REF#=KY027)
(ESCAPEMENTS: 10 (1990); NOT INSPECTED (1991); NO REPORT (1992). AVG. 261 (1980-92). REF#=PH006)
(ESCAPEMENTS: 100 (1990); 100 (1991); 100 (1992). AVG. 68 (1980-92). REF#=PH006)(ESTIMATED ESC. 100 (1992). OPTIMUM ESC.; 10,000 (1992). REF#=KY027)(PRESENCE NOTED. REF#=26-2)
ST
(ABOVE THE FALLS. REF#=KY026)
KY026
(PRESENCE NOTED REF#=25-2)
25-2
1979-01-01 00:00:00
(ESCAPEMENTS: NOT INSPECTED (1990); 10 (1991); 500 (1992). AUG. 128 (1980-92). REF#=PH006)(ESTIMATED ESCAPEMENTS: 500 (1992). OPTIMUM ESC.;P 500 (1992). REF#=KY025)(RECORDED IN 1979. REF#=26-17)
26-17
KY025
(ESCAPEMENT: 4000 (1992). REF#=KY027)(ESCAPEMENTS: 700 (1990); NO REPORT (1991); 0 (1992); AVG. 450 (1980-92). REF#=PH006)
(ESCAPEMENTS: NONE OBSERVED (1990); NO REPORT (1991); 0 (1992); AVG. 13 (1980-92) REF#=PH006)(PRESENCE NOTED. REF#=26-17)
AD
(PRESENCE NOTED. REF#=26-5)
26-5
(ESTIMATED ESC.: 10. OPTIMUM ESC.: 5000. REF#=KY009)
KY009
(ESTIMATED ESC.: 5000; OPTIMUM ESC.: 8000 REF#=KY009)(PRESENCE NOTED. REF#=26-2)
(ESTIMATED ESC.: 500. OPTIMUM ESC.; 3000. REF#=KY009)
REA
(COHO FRY ABUNDANT. REF#=KY008)
KY008
(OPTIMUM ESC.: 5000 REF#=KY009)(PRESENCE NOTED. REF#=26-17,26-2)(OPTIMUM ESC.: 15,000 REF#=KY009)
HOL
(SEVERAL GOOD HOLDING POOLS. REF#=KY008)
(LARGE AGGREGATIONS OF ST PARR ASSOCIATED WITH LARGE WOODY DEBRIS. JUVENILES WELL DISTRIBUTED THROUGHOUT POOL AND RIFFLE HABITATS. REF#=KY008)
(PRESENCE NOTED. REF#=26-14)
26-14
(DFO RECORDS INDICATE CHINOOK HAVE SPAWNED IN KASHUTL RIVER (<15 FOR 10 YR PERIOD 82-91). REF# = HQ0202)
HQ0202
(DFO RECORDS INDICATE CHUM HAVE SPAWNED IN KASHUTL RIVER (AVG 5505 OVER 10 YR PERIOD 82-91). REF# = HQ0202)
(DFO RECORDS INDICATE COHO HAVE SPAWNED IN KASHUTL RIVER (AVG 84 OVER 10 YR PERIOD 82-91). REF# = HQ0202)
(DFO RECORDS INDICATE PINK HAVE SPAWNED IN KASHUTL RIVER (AVG <15 OVER 10 YR PERIOD 82-91). REF# = HQ0202)
(DFO RECORDS INDICATE SOCKEYE HAVE SPAWNED IN KASHUTL RIVER (AVG <15 OVER 10 YR PERIOD 82-91). REF# = HQ0202)
(BOTH SUMMER AND WINTER RUNS. REF#=KY005)
KY005
NOW SPAWNING IN INLET CREEK TO CROSS LAKE
PC07
1995-01-01 00:00:00
(SOCKEYE USE THE LAKE FOR SPAWNING. ESTIMATED ESCAPEMENT: 50; OPTIMUM ESC.: 4000. REF#=KY015)
KY015
(PRESENCE NOTED REF#=26-2)
(OPTIMUM ESCAPEMENT.: 500. REF#=KY010)
KY010
(OBSERVED IN 1994 REF#=PH006)
(COHO HAVE BEEN OBSERVED CLEARING THE FALLS AT 4.0 KM UPSTREAM. REF# = 26-2)
(PRSENCE NOTED. REF#=26-2)
(PRSENCE NOTED. REF#=26-17)
(SUMMER AND WINTER RUNS OF STEELHEAD. REF# = 26-2)
(ESTIMATED ESC.: 12; OPT. ESC.: 3000. REF#=KY020)
KY020
(IN LOWER RIVER. REF#=26-2)
(ESTIMATED ESCAPEMENT: 4. REF#=KY020)(PRESENCE NOTED REF#=26-17)
TR
(IN HEADWATERS. REF#=26-14)
(ESCAPEMENTS: 150 (1991); 500 (1992). AVG. 519 (1980-92). REF#=PH006)(ESTIMATED ESC.: 500 (1992). OPTIMUM ESC. : 1500 REF#=PH006)(PRESENCE NOTED REF#=26-2)
(AVG. ESCAPEMENTS (1980-92): 29. REF#=PH006)(OPTIMUM ESC.: 100 (1992) REF#=KY028)(PRESENCE NOTED. REF#=26-2)
KY028
(OBSERVED TO THE LAKE AT 2.4 KM REF#=26-19)
CC
(CAUGHT IN MINNOW TRAPS. REF# = HQ0234)
HQ0234
1997-09-01 00:00:00
(CAUGHT IN MINNOW TRAPS REF# = HQ0234)
(ESCAPEMENTS: 140 (1980-92) REF#=PH006)(OPTIMUM ESC.: 1000 REF#=KY006)
KY006
(ESCAPEMSNTS:45 (1980-92) REF#=PH006)(OBSERVED IN MINOR TRIBUTARIES REF#=26-2)(OPTIMUM ESC. : 500 REF#=KY006)
(IN RIVER ABOVE FALLS REF#=6N-28)
6N-28
(PRESENCE NOTED REF#=26-17)
(OPTIMUM ESC.: 500 REF#=KY003)
KY003
(POSSIBLY CH PRESENT ALSO REF#=KY001)
KY001
(OBSERVED IN STREAM REF#=M036)
M036
1989-01-01 00:00:00