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. 2018 Oct 11;12(2):230–254. doi: 10.1111/eva.12711

Table 10.

Observed number of CWTs from 2017 Canadian fishery sampling, estimated 2017 catch in Canadian fisheries of hatchery‐origin adult coho salmon via CWTs, ER (%) via CWTs of adult coho salmon in Canadian fisheries, estimated 2017 escapement of hatchery‐origin adult coho salmon, observed assignments via PBT from 2017 fishery sampling, estimated catch via PBT‐GSI, ER of clipped adult coho salmon, total adult 2017 escapement, adipose fin clip rate observed in escapement, and clipped hatchery component of adult escapement for selected coho salmon populations. N/A is not applicable as CWTs were not applied to the population

Population Coded‐wire tags PBT‐GSI Adipose clips
Catch Escapement Catch Escapement
Obs. CWTs (adults) Estimated catch (adults) ER Hatchery‐origin Obs. PBT Estimated catch ER Total adults Clip rate Hatchery‐origin clipped
Quinsam 62 1,323 31 3,010 88 1,135 28 3,480 82.3[Link] 2,864
Puntledge 3 142 10[Link] 1,330 3 81 32 2,397 7.1[Link] 170
Big Qualicum 40 1,365 22 4,834 71 1,679 22 6,933 84.9 5,886
Robertson (swim‐ins)[Link] 117 4,030 44 5,206 267 3,110 27 9,511 88.0 8,370
Inch 117 1,879 41 2,781 108 1,488 35 2,779 99.7 2,771
Coldwater 9 97 16 518 8 157 23 2,178 24.1 525
Salmon 4 51 10 453 5 87 16 676 65.4 442
Nitinat (swim‐ins)[Link] N/A 23 723 33[Link] 1,497 96.1 1,439
Conuma N/A 10 399 20[Link] 3,910 41.9 1,638
Rosewall N/A 4 151 65[Link] 80 100.0 80
Goldstream N/A 7 746 96 99 33.3 33
Tenderfoot N/A 41 852 55[Link] 925 74.7 691
Capilano N/A 135 3,089 21[Link] 12,244 96.9 11,864
Chilliwack (swim‐ins) N/A 253 5,507 28[Link] 14,492 97.7 14,159
Chehalis (swim‐ins) N/A 57 924 72[Link] 587 61.5 361

CWT hatchery‐origin includes unclipped tagged which do not get counted in clipped hatchery‐origin for Quinsam River.

In 2014 broodyear, 12.8% of Puntledge fry release was clipped and tagged, and the remainder was released unclipped. In 2017 escapement sampling, a CWT loss rate of 31% was observed due to sampling for otoliths and CWTs from the same individual.

Total escapement to the Stamp River plus Robertson Creek was 21,175 adults. 9,511 adults is the hatchery return, which is all that was sampled.

Total escapement to the Nitinat River was 4,883 adults. Clip rate is from swim‐ins so total adults is just swim‐ins, same as Robertson Creek.

Minor components of the escapement were not enumerated; however, the exploitation rate can be considered reasonably accurate due to the very high percentage of total return that were enumerated in the hatchery swim‐in count at Nitinat River, Capilano River, and Chilliwack River.

Significant components of the escapement were not enumerated; consequently, exploitation rate was overestimated by a large but unknown percentage.