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Appendix
North Canol area
Frances Lake area
Winter
No. of
moose/1000 km
2
Finite rate
of change
No. of
moose/1000 km
2
Finite rate
of change
Mean moose
density
1989–1990
a
252
1.164
274
1.18
263
1990–1991
a
293
1.164
323
1.18
308
1991–1992
b
341
1.11
382
1.12
361
1992–1993
c
379
1.10
427
1.10
403
1993–1994
417
470
443
a
The finite rate of increase is interpolated from population estimates using stratified random block surveys in November
1987 (Jingfors 1988) and 1991 (Larsen and Ward 1995).
b
The finite rate of increase is from Larsen and Ward (1995).
c
The rate of increase is from Hatter and Bergerud (1991, see Methods), where R is 0.18 and M is the mean adult mortality
rate (0.095; Larsen and Ward 1995).
Table A1. Estimated moose density each winter in two regions in the Finlayson Study Area.
Year
Pack
No. of hours
between
locations
No. of
wolves
No. of days
studied
% of days
observed
No. of moose
killed
No. of
caribou
killed
Total mass
of prey
killed
a
(kg)
Mass of prey
per wolf per
day (kg)
1990
Frances L.
24
17
14
71
6
0
1 850
7.8
Jackfish L.
24
2
31
84
6
0
1 125
18.1
Ketza R.
48
2
31
65
3
0
700
11.3
Lapie R.
48
5
30
53
5
0
1 676
b
11.2
Prevost R.
24
6
19
79
4
0
925
8.11
Seven Wolf L.
24
2
38
89
2
1
452
6.0
Tyers R.
48
2
20
60
2
0
800
20
Tuchitua R.
24
11
36
75
5
0
1 725
4.4
Weasel L.
24
6
16
81
5
0
1 513
15.8
Woodside R.
24
4
39
77
7
0
2 063
13.2
Yusezyu R.
24
2
30
87
6
0
1 163
19.4
Upper Pelly R.
24
2
14
79
3
0
450
16.1
Total
318
54
1
14 442
1991
Finlayson L.
6
2
9
100
1
2
205
11.4
Ketza R.
6
2
12
92
3
0
925
38.5
Light Creek
48
2
6
67
1
0
150
12.5
Mink Creek
6
4
11
100
1
3
869
19.8
McEvoy L.
48
2
16
56
1
0
400
12.5
Woodside R.
48
7
8
50
1
0
150
2.68
Wolverine L.
24
2
9
78
2
0
813
45.2
Seven Wolf L.
6
7
13
100
4
1
1 515
16.6
Total
84
14
6
5 027
Table A2. Composition of ungulate prey killed and kill rate by wolves in 21 packs monitored during late winter 1990 through 1994 in
the Finlayson Study Area.
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Hayes et al.
59
1992
Campbell Creek
24
14
22
91
6
6
3 112
10.1
Finlayson L.
24
2
28
57
5
0
1 450
25.9
Fire Creek
48
3
24
50
3
0
800
11.1
Frances L.
48
9
21
81
3
0
1 600
8.5
Jackfish L.
48
11
23
48
6
0
2 150
8.5
Ketza R.
48
2
19
63
3
0
1 200
31.6
Light Creek
48
6
19
52
4
0
1 588
13.9
Mink Creek
48
8
23
48
0
3
456
2.5
Otter Creek
48
2
23
52
2
0
800
17.4
Prevost R.
48
10
10
50
3
0
925
9.3
Total
212
35
9
14 081
1993
Seven Wolf L.
24
10
24
79
5
2
1 817
7.6
Tuchitua R.
48
10
27
52
5
0
1 225
4.5
Tyers R.
48
2
19
63
2
0
550
14.5
Weasel L.
48
10
23
47
5
1
1 877
8.2
Wolverine L.
48
2
21
52
3
0
950
22.6
Woodside R.
48
11
24
58
4
0
1 350
5.1
Yusezyu R.
48
11
33
48
7
0
1 788
4.9
Total
171
31
3
9 537
1994
Campbell Creek
24
20
27
96
11
2
3 442
6.4
Mink Creek
24
11
26
92
4
1
1 752
6.1
Light Creek
24
11
26
73
6
0
1 900
6.6
Nipple Mt.
24
2
24
83
2
0
800
16.7
Otter Creek
24
6
21
81
3
0
713
5.7
Upper Pelly R.
24
5
21
81
3
0
1 200
11.4
Wolverine L.
24
4
26
73
7
0
2 025
19.5
Yusezyu R.
24
13
26
81
9
0
2 825
8.4
Total
197
45
3
14 657
Grand total
982
179
25
57 764
a
Based on estimated masses (kg): cow moose 375, bull moose 413, unknown adult moose 400, yearling moose 250, calf moose 150, adult caribou 152,
calf caribou 55, and mountain sheep 75. See methods for sources of live masses.
b
Includes one mountain sheep.
Table A2 (
concluded).
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