Recreational Fishery
Stock Assessment
1999 Final Report |
PHOTO 1. Cobb Lake
Aerial Photo. June 2001. Click
image to view 57K JPG |
|
|
|
Introduction
This report presents the results of a stock assessment
of Cobb Lake, completed by Ted Zimmerman and Sean Barry
on May 28, 1998. Cobb Lake was initially stocked with brook
trout in 1984 and rainbow
trout in 1986. No stock assessments had been performed
prior to this assessment, however brook trout creel surveys
were conducted in 1986 (Euchner)
and 1988 (Labach). Cobb Lake was therefore
targeted as a high priority for sampling as part of a region-wide
stock assessment program in 1998.
Methods
An experimental, 91.2m sinking monofilament gill net was
set in Cobb Lake on May 28,1998 according to the methods
prescribed in the Resource Inventory Committee document
Fish
Collection Methods and Standards. The net was deployed
at 14:15 and retrieved the same day at 17:43, for a total
soak time of 3 hours, 28 minutes.
|
FIGURE 1. 1998 Net set location Click
image to view 45K GIF |
|
The net was set in a NW-SE direction from the south shore,
originating near the lake's primary inlet (Figure 1).
The net ranged in depth from the surface to approximately
8 m.
All trout captured were sampled for fork
length and weight. Fin rays were removed from brook
trout for ageing, and otoliths
were removed from a subset of brook trout for verification
of age techniques. Scale
samples were taken from all rainbow trout. Age structures
were sent to Darlene
Gillespie of TimeMark Consulting (Nanaimo, B.C.) on
June 17, 1998. During the survey, two groups of anglers
were interviewed and their catch was also sampled for length
and weight. Scale samples were also obtained.
Results and Discussion
CATCH SUMMARY
The net catch yielded 7 eastern brook trout (EB), 32
rainbow trout (RB), 50 suckers (unid.) and 1 lake
chub, for a catch per unit effort of 2.0 EB and 9.2
RB per net-hour. All suckers were released alive from the
net. See Appendix 1 for individual
rainbow trout sample data, and Appendix
2 for individual brook trout sample data. Of the 32
rainbow trout captured in the gill net, 22 (69%) were female,
9 (28%) were male, and 1 (3%) could not be identified.
Table 1. Population characteristics of trout sampled
in the gill net in Cobb Lake, May 28, 1998
Species |
Number |
Length (mm) |
Weight (g) |
Condition |
Mean |
Range |
SD |
Mean |
Range |
SD |
Mean |
Range |
SD |
RB |
32 |
395 |
286-456 |
38 |
635 |
270-910 |
162 |
1.01 |
0.85-1.17 |
0.08 |
EB |
7 |
319 |
241-384 |
59 |
455 |
195-770 |
232 |
1.28 |
1.11-1.39 |
0.11 |
A total of 8 rainbow trout were sampled from anglers. The
following table describes the attributes of the angled fish.
Table 2. Population characteristics of rainbow trout
angled in Cobb Lake, May 28, 1998
No. Sampled |
Mean Length (mm) |
Mean Weight (g) |
Mean Condition |
8 |
395 |
584 |
0.94 |
|
FIGURE 2. Length vs. weight of rainbow
trout captured in Cobb Lake, 1998
|
|
|
|
|
FIGURE 3. Length frequency distribution
of rainbow trout captured in 1998
|
|
|
|
|
FIGURE 4. Age vs. length of rainbow trout
captured in 1998. |
|
|
|
|
FIGURE 5. Length frequency distribution
of brook trout sampled by creel, Jan/Feb
1988. |
|
|
|
|
FIGURE 6. Length frequency distribution
of brook trout sampled by gill net, May
1998. |
|
|
RAINBOW TROUT ANALYSIS
Condition
The weight of Cobb Lake rainbow trout (all samples combined)
increased according the equation W = 6E-5 x L^2.7132, this
relationship is expressed in Figure 2. In general,
Cobb Lake rainbow trout were slightly lighter for their
length than those sampled in other lakes in the region during
the same time period. This phenomenon is known to occur
in lakes in the Omineca region in which both brook trout
and rainbow trout have been co-stocked, and may reflect
some degree of interspecific competition.
Size Distribution
Figure 3 shows that the catch composition of the
gill net was biased towards larger rainbow trout. This is
an expected result since the net was intentionally placed
near the inlet stream and therefore targeted mature fish
(see Appendix 1) that were
attempting to spawn. It is likely that the smaller cohorts
were not available to the catch due to displacement by their
larger counterparts. The angling size distribution reflects
the gill net size distribution, which is likely due to anglers
targeting the high-use area at the mouth of the inlet stream
as well.
Growth
Cobb Lake rainbow trout appear to exhibit good growth rates
(Figure 4), with age 3 fish attaining a mean length
of 372 mm (+/- 25mm SD) and a mean weight of 509 g (+/-
96g SD). The length-at-age data may be biased due to the
sample having targeted spawners, however 1998 stock assessments
in Eena, Chubb, and Trapping
lakes similarly targeted spawning populations which did
not exhibit the growth rates observed in the Cobb Lake sample.
The asymptotic growth rates are consistent with other stock
assessments.
BROOK TROUT ANALYSIS
Since only seven brook trout were captured in the current
study, few inferences can be made regarding their status
in Cobb Lake. Cobb Lake brook trout exhibited a slightly
reduced condition relative to other lakes stocked exclusively
with brook trout. This phenomenon is consistent with that
observed for rainbow trout and is likely attributable to
interspecific competition, as discussed above.
Figure 5 shows the length frequency distribution
of rainbow trout sampled during a winter creel survey in
1988 (Labach). By way of comparison, Figure 6 shows
the results from the May 1998 survey. The size of fish captured
in 1998 appears to be within the range of those captured
by anglers 10 years earlier. While it is likely that the
brook trout in Cobb Lake today are exhibiting similar growth
and abundance to those sampled in 1988, a comparative winter
creel survey should be performed to confirm the status of
brook trout in Cobb Lake.
Management Recommendations
While the condition of both species of trout is slightly
lower than that observed in other monoculture lakes within
the region, Cobb Lake continues to support a viable fishery,
with good sized trout available to the recreational angler.
The current stocking rate for both species appears to be
meeting angler needs, and anglers that were encountered
during the assessment expressed satisfaction in their fishing
experience.
To better understand the status of brook trout in Cobb
Lake, a winter creel survey should be completed, preferably
during the same time period as those performed in 1986 and
1988. This would provide fisheries managers with a larger
sample of trout by which to base management decisions, as
well as information on winter angling pressure and its relative
pressure on the resource.
Appendix 1.
Appendix 2.
Literature Cited
Euchner, T. 1986. Creel survey of
the winter 1985/86 Cobb Lake brook trout ice-fishery. Ministry
of Environment, Lands and Parks. Prince George.
Labach, M. 1988. Creel survey of the
winter 1987/88 Cobb Lake ice-fishery. Ministry of Environment,
Lands and Parks. Prince George.
For More Information:
Contact :Ted
Zimmerman
Sr. Fisheries Biologist, Omineca sub-Region
Prince George, B.C.
250-565-6852 |