SALM
S
CT
NS
WI
REA
FFC0009
1996-05-01 00:00:00
Sport
OBL
FFC0011
1995-05-01 00:00:00
CM
AN
(ESTIMATED ESCAPEMENT:  1993- 40, 1992- 150 (210 BROOD), 1991- 1, 1990- N/O REF#=CR030)
CR030
1993-01-01 00:00:00
Salmon
CO
(ESTIMATED ESCAPEMENT: 1993- N/O, 1992- 50, 1991- 5, 1990- N/O REF#=CR030)
DV
SISSM01
1995-01-01 00:00:00
KO
PK
(ESTIMATED ESCAPEMENT: 1993- N/O, 1992- N/O, 1991- UNKNOWN, 1990- N/O REF#=CR030)(HISTORICAL PRESENCE REF#=13-1)
13-1
1977-01-01 00:00:00
UPPER LIMIT UNKNOWN
FFC0006
1997-05-01 00:00:00
(PRESENCE NOTED REF#=13-1)
(COHO FRY OBSERVED REF#=CR036)(PRESENCE NOTED REF#=13-1)
CR036
FFC0010
1994-05-01 00:00:00
(PRESENCE NOTED. REF#=13-3)
13-3
1990-01-01 00:00:00
(ESTIMATED ESCAPEMENT: 1993 N/O, 1992 500 (100 BROOD), 1991 UNK, 1990 UNK. REF#=CR040)
CR040
(OBSERVED IN CULVERT UNDER HIGHWAY. REF#=CR040)(THROUGHOUT ACCESSIBLE HABITAT. REF#=13-1)(ESTIMATED ESCAPEMENT: 1993 10, 1992 UNK, 1991 UNK, 1990 UNK. REF#=CR040)
AD
(THROUGHOUT. REF#=13-3)
(PRESENCE NOTED. REF#=13-1)
ST
(FEW PRESENT. REF#=13-1)
(ESTIMATED ESCAPEMENT: 1992 300 (BROOD), 1990 300. REF#=CR039)(PRESENCE NOTED. REF#=13-1)
CR039
(BROOD ESCAPEMENT (1992) 110. REF#=CR048)(PRESENCE NOTED. REF#=13-1)
CR048
SPL
(SPAWNING THROUGHOUT (NO UPPER LIMIT GIVEN). REF#=CR048)
(9 (+ UNK) OBSERVED 1990. REF#=CR048)(PRESENCE NOTED. REF#=13-1)
CH
(ESCAPEMENTS: (1990-91) - NOT INSPECTED, (1992) - NO REPORT, (1980-1992) - AVERAGE 2. REF#=PH006)(FEW PRESENT. REF#=13-1)
PH006
1994-01-01 00:00:00
(ESCAPEMENTS: 1993 - 150, 1992 - 25 (150 BROOD), 1991 - N/I, 1990 - N/O (1980 - 1992) - AVERAGE: 2. REF#=CR001B,PH006)
CR001B
(ESCAPEMENTS: 1992 N/I, 1991 N/I, 1990 N/I, (1980-92) AVERAGE: 24. REF#=PH006)
(ESCAPEMENTS: 1993 - , 1992 - 13500, 1991 - N/I, 1990 - 22000; (1980-92) AVE. 759. REF#=CR001A)
CR001A
(SMALL CT OBSERVED. REF#=13-11,CR001A)
13-11
CAL
MJL004
1999-02-01 00:00:00
Other
CAS
CCT
FRY AND PARR
(ESCAPEMENTS: 1100 (1990); 3500 (1991); 300 (1992); AVG. 1196 (1980-92); BROOD ESC. 400 (1992). REF#=PH006,SA026)
SA026
1992-01-01 00:00:00
(NO. OF FISH ON SPAWNING GROUNDS: 1100 (1990); 3500+(1991), 300 (1993). (ALSO REF SA027) REF#=SA024,SA025)(SPAWNING LOCATION: MAINLY BELOW THE SALMON RIVER/WHITE RIVER CONFLUENCE (1990); BELOW BIG TREE CREEK (1991); ABOVE HIGHWAY (1992/93). (ALSO REF # S
SA024
SA025
1991-01-01 00:00:00
(ESCAPEMENTS: NON OBSERVED (1990); 50 (1991); NOT INSPECTED (1992). AVERAGE: 212 (1980-92), BROOD ESCAPEMENT 300 (1992). REF#=PH006,SA026)
(NUMBER FO FISH ON SPAWNING GROUNDS: <50 (1991); UNKNOWN (1993). REF#=SA025,SA027)
SA027
(ESCAPEMENTS: 250 (1990); 2000 (1991); NOT INSPECTED (1992) AVG. 1754 (1980-92); BROOD ESC. 2000 (1992). REF#=PH006,SA026)(THROUGHOUT ACCESSIBLE HABITAT. REF#=13-1)
(NUMBER OF FISH ON SPAWNING GROUNDS: 250 (1990); 2000 (1991); UNKNOWN (1993). (ALSO REF #SA027) REF#=SA024,SA025)(SPAWNING DISTRIBUTION: THROUGHOUT THE RIVER. REF#=SA025)
(THROUGHOUT. REF#=13-29)
13-29
(ESCAPEMENTS: 200000 (1990); 5000 (1991); 15000 (1992) AVG. 26508 (1980-92); BROOD ESC. 5000 (1992). REF#=PH006,SA026)
(NUMBER OF FISH ON SPAWNING GROUNDS : 200000 (1990); 5000 (1991); 15000 (1993).(ALSO REF #SA027) REF#=SA024,SA025)(SPAWNING LOCATION: MAINLY BELOW BIG TREE CREEK (1991/92/93). (ALSO REF #SA027) REF#=SA025,SA026)
RB
SK
(ESCAPEMENTS: NONE OBSERVED (1990); NOT INSPECTED (1991); NO REPORT (1992); AVG. 49 (1980-92). REF#=PH006)(FEW PRESENT. REF#=13-19)
13-19
(18 FISH WERE CAUGHT IN 5 SITES DOWNSTREAM OF GRILSE CREEK. REF#=SA029)(PRESENT IN MAIN RIVER AND TRIBUTARIES. REF#=13-1)
SA029
(ESCAPEMENTS: NONE OBSERVED (1990/91); NOT INSPECTED (1992); AVG. 150 (1980-92). OPTIMUM ESC. 200 (1993). REF#=PH006,SA036)(PRESENCE NOTED. REF#=13-1)
(ESCAPEMENTS: 200 (1990); 200 (1991); 260 (1992); AVG. (1980-92); ESTIMATED ESC. 70 (1993), OPTIMUM ESC. 200 (1993). REF#=PH006,SA036)(OBSERVED TO HEADWATERS, WHITE GOLD PASS AREA. REF#=13-10)(RELATIVELY LOW FRY AND PARR NUMBERS. REF#=SA030,SA031)
13-10
(NO. OF FISH ON SPAWNING GROUNDS 200+ (1990-91); SPAWNING LOCATION: THROUGHOUT THE STREAM (1990) TO THE UPPER REACHES (1991). REF#=SA034,SA035)
SA034
SA035
(RELATIVELY LOW FRY AND PARR NUMBERS. REF#=SA030,SA031)
SA030
SA031
(ESCAPEMENTS: 5000 (1990); 500 (1991); 250 (1992); AVG. 1438 (1980-92). REF#=PH006)(PRESENCE NOTED. REF#=13-1)
(NO. OF FISH ON SPAWNING GROUNDS: 5000+ (1990); 500 (1991). REF#=SA034,SA035)(SPAWNING LOCATION: TO THE CANYON. REF#=SA034,SA035)
(RELATIVELY LOW FRY AND PARR NUMBERS. REF#=SA030)(WINTER RUN BELOW CANYON. REF#=13-10)
SA037
OBSERVED IN TRIBUTARY
REARING AREAS IN TRIBUTARIES. IN KAY CREEK, FROM MOUTH TO 800 METERS UPSTREAM
SPAWNING AND REARING AREAS ARE DISTRIBUTED THROUGHOUT REACH III
REARING AREAS THROUGHOUT LOWER 800 METERS OF KAY CREEK
SPAWNING AND REARING AREAS THROUGHOUT THE LOWER 800 METERS OF KAY CREEK
THINLY DISTRIBUTED THROUGHOUT THE MEMEKAY RIVER AND TRIBUTARIES. THE ONLY FISH FOUND ABOUT THE BARRIER AT 18000 METERS UPSTREAM
REARING THROUGHOUT THE LOWER 800 METERS OF KAY CREEK
SPAWNING AND REARING THROUGHOUT THE LOWER 800 METERS OF KAY CREEK
13-32
1976-01-01 00:00:00
JUVENILE STEELHEAD ARE THE MOST ABUNDANT FISH IN THE MEMEKAY RIVER
REARING AREAS ARE DISTRIBUTED THROUGHOUT THE ACCESSIBLE AREAS OF THE MAINSTEM, THE LOWER 800 METERS OF KAY CREEK. SPAWNING AREAS IN REACH III
SPAWNING AREAS THROUGHOUT LOWER 800 METERS OF KAY CREEK
(STOCKED. REF#=CR114,CR117)
CR114
CR117
(PRESENT. REF#=PC02)
PC02
TSB