78, 911-916.
Cowen, L., Walsh, S. J., Schwarz, C. J., Cadigan, N. and Morgan, J. 2009. Estimating exploitation rates of migrating yellowtail flounder (Limanda ferruginea) using multi-state mark-recapture methods incorporating tag loss and variable reporting rates. Canadian Journal of Fisheries and Aquatic Sciences 66, 1245-1255.
Hoenig, J. M., Barrowman, N.J., Hearn, W. S. and Pollock, K. H. 1998a. Multiyear tagging studies incorporating fishing effort data. Canadian Journal of Fisheries and Aquatic Sciences 55, 1466-1476.
Hoenig, J. M., Barrowman, N.J., Pollock, K. H., Brooks, E.N., Hearn, W. S. and Polacheck, T. 1998b. Models for tagging data that allow for incomplete mixing of newly tagged animals. Canadian Journal of Fisheries and Aquatic Sciences 55, 1477-1483.
McCracken, F.D., 1958. On the biology and fishery of the Canadian Atlantic halibut, Hippoglossus hippoglossus L. J. Fish Res. Board Can. 15: 1269-1311.
Neilson, J.D., Waiwood, K.G., and Smith, S.J. 1989. Survival of Atlantic Halibut (Hippoglossus hippoglossus) caught by longline and otter trawl gear. Can. J. Fish. Aquat. Sci. 46, 887-897.
Pollock, K. H., and Raveling, D. G. 1982. Assumptions of modern band-recovery models with emphasis on heterogeneous survival rates. Journal of Wildlife Management 46, 88-98.
Seber, G. A. F., and Felton, R. 1981. Tag loss and the Petersen mark-recapture experiment. Biometrika 68, 211-219.
Stobo, W., Neilson, J.D., and Simpson, P. 1988. Movements of Atlantic halibut (Hippoglossus hippoglossus) in the Canadian North Atlantic: inference regarding life history. Can. J. Fish. Aquat. Sci. 45, 484-491.
Trzcinski, M.K., Armsworthy, S.L., and Wilson, S. 2010. Atlantic Halibut on the Scotian Shelf and Southern Grand Banks (Divs. 3NOPs4VWX5Zc) – Industry/DFO Longline Survey and Tagging Results to 2008. Research Document.
Trzcinski, M.K., Armsworthy, S.L., Wilson, S., Mohn, R.K., and Campana, S.E. 2010. A Framework for the assessment of the Scotian Shelf and southern Grand Banks Atlantic halibut stock. Working paper.
Table 1. Expected number of recoveries given fish tagged and released in year i and recovered in year j assuming a constant instantaneous natural mortality M, year-specific instantaneous fishing mortality under complete mixing and under incomplete mixing, constant immediate tagging survival , constant tag reporting rate and a probability that a fish released with 2 tags will have t tags retained (t=1, 2) in the kth year after release (k=1, …) . The extension to recovery years 4 and 5 follows the same pattern. Fishing is assumed to occur uniformly over the calendar year. Incomplete mixing of tags in the second half of the calendar year of release is allowed.
|
|
Expected recoveries in year
|
|
1
|
2
|
3
|
1
|
|
|
|
2
|
|
|
|
3
|
|
|
|
Table 2. The number of halibut tagged and released as part of the all-sizes tagging program by NAFO between 2006 and 2008 (n=2061).
|
NAFO
|
Proportion
Allocated
|
2006
|
2007
|
2008
|
Total
|
Proportion
of Total
|
3N
|
0.22
|
93
|
54
|
54
|
201
|
0.10
|
3O
|
0.13
|
32
|
57
|
58
|
147
|
0.07
|
3Ps
|
0.19
|
30
|
237
|
143
|
410
|
0.20
|
4V
|
0.19
|
103
|
264
|
185
|
552
|
0.27
|
4W
|
0.16
|
165
|
132
|
166
|
463
|
0.22
|
4X
|
0.12
|
103
|
84
|
101
|
288
|
0.14
|
Table 3a. Summary of recovery data. Each cell has two entries. The first entry is the number of fish with a single tag recovered; the second entry is the number of fish with both tags recovered. All fish released had two tags. Pooled over all lengths at release, all areas released, areas recovered, etc. Year classes are calendar years.
|
Year of release
|
Number released
|
Year of recovery
|
2006
|
2007
|
2008
|
2009
|
2010
|
2006
|
526
|
1 / 15
|
13 / 25
|
9 / 17
|
7 / 12
|
4 / 4
|
2007
|
828
|
|
5 / 13
|
34 / 75
|
23 / 35
|
12 / 12
|
2008
|
707
|
|
|
3 / 18
|
12 / 43
|
11 / 6
|
Table 3b. Summary of recovery data. Each cell has two entries. The first entry is the number of fish with a single tag recovered; the second entry is the number of fish with both tags recovered. All fish released had two tags. Only fish released that are 71+ cm but pooled over all areas released, areas recovered, etc. Year classes are calendar years.
|
Year of release
|
Number released
|
Year of recovery
|
2006
|
2007
|
2008
|
2009
|
2010
|
2006
|
478
|
1 / 14
|
12 / 25
|
8 / 16
|
6 / 11
|
3 / 2
|
2007
|
732
|
|
5 / 12
|
33 / 71
|
20 / 33
|
9 / 9
|
2008
|
659
|
|
|
2 / 15
|
12 / 42
|
11 / 6
|
Table 5. Estimated cumulative tag-loss.
|
Time at large (days)
|
Recovered fish with double tags
|
Recovered fish with a single tag
|
Estimated cumulative tag-loss.
|
(0,100]
|
36
|
3
|
0.04
|
(100,200]
|
16
|
11
|
0.26
|
(200,400]
|
99
|
46
|
0.19
|
(400,600]
|
46
|
30
|
0.25
|
(600,800]
|
42
|
29
|
0.26
|
(800,1200]
|
30
|
21
|
0.26
|
(1200,2000]
|
5
|
4
|
0.29
|
Table 4a. The number of halibut tagged and released as part of the all-sizes tagging program by month between 2006 and 2008 (n=2061).
|
Month
|
Years
|
Total
|
|
2006
|
2007
|
2008
|
|
4
|
0
|
0
|
99
|
99
|
5
|
11
|
164
|
71
|
246
|
6
|
254
|
0
|
441
|
695
|
7
|
218
|
653
|
96
|
967
|
8
|
43
|
11
|
0
|
54
|
Table 4b. The number of halibut recaptured as part of the all-sizes tagging program by month between 2006 and 2008 (n=409).
|
Month
|
Year
|
Total
|
|
2006
|
2007
|
2008
|
2009
|
2010
|
|
1
|
0
|
5
|
13
|
17
|
6
|
41
|
2
|
0
|
4
|
14
|
11
|
17
|
46
|
3
|
0
|
6
|
6
|
15
|
7
|
34
|
4
|
0
|
1
|
5
|
4
|
7
|
17
|
5
|
0
|
2
|
6
|
16
|
0
|
24
|
6
|
1
|
5
|
35
|
25
|
8
|
74
|
7
|
1
|
10
|
35
|
21
|
3
|
70
|
8
|
3
|
9
|
16
|
11
|
1
|
40
|
9
|
5
|
4
|
11
|
5
|
|
25
|
10
|
3
|
5
|
2
|
2
|
|
12
|
11
|
2
|
3
|
8
|
2
|
|
15
|
12
|
1
|
2
|
5
|
3
|
|
11
|
Table 6. Summary of parameter estimates using the incomplete-mixing model under several scenarios for the initial tagging survival (ITS) and tag reporting rate (RR) and two subsets of fish released. First entry in estimates of F represents F* (instantaneous fishing mortality during the first 6 months after release) and the second entry represents F for complete mixing.
|
|
|
Parameter Estimates1
|
|
Model
|
M
|
|
|
|
|
|
R1^
|
R2
|
AICc4
|
|
M(dot), F(t), F*(t), R(2), ITS=0.8, RR=0.9 ALL fish
|
0.184
|
0.092
NA2
|
0.061
0.149
|
0.092
0.218
|
NA3
0.174
|
NA3
0.092
|
0.83
|
0.91
|
-1739.4
|
|
M(dot), F(t), F*(t), R(2), ITS=0.8, RR=1.0 ALL fish
|
0.203
|
0.086
NA
|
0.055
0.134
|
0.083
0.198
|
NA
0.157
|
NA
0.084
|
0.83
|
0.91
|
-1739.5
|
|
M(dot), F(t), F*(t), R(2), ITS=0.9, RR=0.9 ALL fish
|
0.205
|
0.085
NA
|
0.055
0.132
|
0.082
0.196
|
NA
0.156
|
NA
0.083
|
0.83
|
0.91
|
-1739.6
|
|
M(dot), F(t), F*(t), R(2), ITS=0.9, RR=1.0 ALL fish
|
0.222
|
0.076
NA
|
0.050
0.119
|
0.073
0.178
|
NA
0.141
|
NA
0.076
|
0.83
|
0.91
|
-1739.6
|
|
M(dot), F(t), F*(t), R(2), ITS=1.0, RR=0.9 ALL fish
|
0.222
|
0.076
NA
|
0.050
0.119
|
0.073
0.178
|
NA
0.141
|
NA
0.076
|
0.83
|
0.91
|
-1739.6
|
|
M(dot), F(t), F*(t), R(2), ITS=1.0, RR=1.0 ALL fish
|
0.237
|
0.069
NA
|
0.045
0.107
|
0.066
0.161
|
NA
0.127
|
NA
0.069
|
0.83
|
0.91
|
-1739.6
|
|
M(dot), F(t), F*(t), R(2), ITS=0.8, RR=0.9 71+ cm
|
0.226
|
0.101
NA2
|
0.066
0.169
|
0.080
0.249
|
NA3
0.197
|
NA3
0.096
|
0.83
|
0.91
|
-1571.7
|
|
M(dot), F(t), F*(t), R(2), ITS=0.8, RR=1.0 71+ cm
|
0.248
|
0.090
NA
|
0.060
0.152
|
0.072
0.227
|
NA
0.179
|
NA
0.088
|
0.83
|
0.91
|
-1571.9
|
|
M(dot), F(t), F*(t), R(2), ITS=0.9, RR=0.9 71+ cm
|
0.250
|
0.089
NA
|
0.059
0.150
|
0.070
0.224
|
NA
0.177
|
NA
0.087
|
0.83
|
0.91
|
-1571.9
|
|
M(dot), F(t), F*(t), R(2), ITS=0.9, RR=1.0 71+ cm
|
0.270
|
0.080
NA
|
0.054
0.135
|
0.064
0.204
|
NA
0.161
|
NA
0.080
|
0.83
|
0.91
|
-1572.0
|
|
M(dot), F(t), F*(t), R(2), ITS=1.0, RR=0.9 71+ cm
|
0.270
|
0.080
NA
|
0.054
0.135
|
0.064
0.204
|
NA
0.161
|
NA
0.080
|
0.83
|
0.91
|
-1572.0
|
|
M(dot), F(t), F*(t), R(2), ITS=1.0, RR=1.0 71+ cm
|
0.288
|
0.072
NA
|
0.049
0.122
|
0.058
0.185
|
NA
0.146
|
NA
0.073
|
0.83
|
0.91
|
-1572.2
|
|
1 Standard errors were computed, but are not reported here and are approximately (after adjusting for ) 0.10 for M; 0.04 for Fi; 0.06 for Ri.
2 No estimate is available for the instantaneous fishing mortality in year 1 for complete mixing (see text)
3 No estimates are available for the initial instantaneous fishing mortality for incomplete mixing for these years because releases terminated in 2006
4 Because subset of data was used for the analysis of fish in the 71+ cm size category, AICc should not be compared between these two analyses.
# F2010 is based on tags recovered up to the end of August and so does not represent a full fishing year.
^ R1 is the annual tag retention rate in the first year of release on an annual basis. It is prorated for the first ½ year after release in the model.
Figure 1. Estimated cumulative tag-loss by time-at-large.
Share with your friends: |