Recreational
Fishery Stock Assessment
1999 Final Report
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Introduction
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TABLE 1. Physical Attributes of
Byers Lake.*
Waterbody identifier |
01240STUR |
Water surface area |
18.3 ha. |
Area above 6 m contour |
14.4 ha. |
Shoreline perimeter |
4600 m |
Maximum depth |
11 m |
Volume |
587,000 m3> |
Mean depth |
3.2 m |
Elevation |
758 m |
T.D.S. |
140 mg/L |
Morphoedaphic index |
44 |
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This report presents the results of a stock assessment
of Byers Lake, completed on August 27, 1999 under
a partnership arrangement between the Ministry of Environment,
Lands and Parks and the Carrier
Sekani Tribal Council (CSTC), with funding obtained
from Fisheries
Renewal B.C. through the Upper Fraser-Nechako
Fisheries Council. Field activities were carried out
by Gary George and Lawrence Ward of the CSTC. Analysis and
reporting of the field results were conducted by the author.
Inquiries pertaining to this report should be directed to
the author at the email and address located at the bottom
of this page.
Byers Lake is one of five stocked lakes that are managed
within Eskers
Provincial Park, located 33 km northwest of Prince George.
The lake was initially surveyed in 1985
and was determined to be barren of fish based on gill net
and minnow trap surveys at that time. The lake was subsequently
stocked in 1988 and 1989 with
eastern brook trout fingerlings, after which stocking was
ceased at the request of the Parks Branch. The cessation
of stocking was brought about due to concerns regarding
uncontrolled angler access to the lakes, which was occurring
in response to the stocking program but in advance of the
completion of adequate infrastructure to support the increased
traffic.
After the stocking program ceased, unconfirmed reports
were submitted to Fisheries and Parks staff that some of
the lakes were continuing to produce brook trout, presumably
through natural recruitment. Reports were also received
that indicated that fish may have been transferred between
lakes, a situation which, if true, would have a direct bearing
on the management objectives for each of the lakes initially
stocked. In 1996, Parks Branch requested that the stocking
program be reinvoked, as it was felt that angler use could
now be controlled given the state of the park's infrastructure.
The lake was accordingly stocked in 1997 at an alternate-year
stocking frequency.
Since no assessments had been done on any of the lakes
since stocking was initiated in the late 1980s, and since
the renewed stocking program had been in effect for two
years, Byers Lake was assigned a high priority for assessment
in 1999.
Methods
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 FIGURE 1. Location of Byers Lake gill net
set, August 27, 1999. Click image to view full
bathymetric map.
Click image to view 37K GIF |
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A 91.4 m sinking monofilament gill net with experimental
mesh sizes was set in Byers Lake on August 26, 1999, according
to the methods specified in the Resource Inventory Committee
document Fish
Collection Methods and Standards. The net was deployed
at 3:00 PM and retrieved August 27 at 11:00 AM, for a total
soak time of 20 hours. The net was set from the south shore
near the east end of the lake, and extended in a NNW orientation.
The net ranged in depth from the surface to approximately
9 m. (Figure 1).
All trout collected were sampled for fork length, sex,
and maturity. Weight was measured from a sub-sample of the
fish surveyed, and was collected to the nearest 100 g. Fin
rays were collected for age structure analysis. This analysis
was performed by Darlene
Gillespie of TimeMark Consulting Ltd. (Nanaimo, B.C.).
Results and Discussion
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TABLE 2. Physical attributes of brook
trout sampled in Byers Lake,
August 27, 1999.
Attribute |
Mean |
Range |
Std. Dev. |
Length (mm) |
196 |
148-455 |
58 |
Weight (g)* |
207 |
100-1600 |
400 |
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*Weight only recorded
for 14 fish sampled |
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CATCH SUMMARY
The net catch yielded 24 eastern brook trout (EB),
for a catch per unit effort (CPUE) of 1.2 EB per net-hour.
The complete data set can be viewed in Appendix
1. Seven of the 24 brook trout sampled were classified
as "immature" and their sex could therefore not
be determined. Of the remaining 17 fish, 1 was classified
as a mature male, and the remaining were either not sampled
or were classified as "unknown". Since 1997, the
brook trout released in Byers Lake have been of triploid
origin, which are permanently immature so as to prevent
natural recruitment for this introduced species. The single
mature male that was sampled is likely the progeny of the
1988 or 1989 stock, which were fully viable and therefore
capable of reproduction.
CONDITION
A condition assessment cannot be completed for this data
set since only a sub-sample of the fish that were captured
were weighed. Additionally, weight was only measured to
the nearest 100 g, thereby precluding an accurate analysis
of the fish that were sampled.
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FIGURE 2. Length frequency
distribution of brook trout captured in Byers
Lake, August 27, 1999. Bold numbers indicate
age of size class.
Click image to view 5K GIF |
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LENGTH FREQUENCY DISTRIBUTION and GROWTH
The length frequency distribution (Figure
2) of the catch shows that the population was dominated
by 160 - 200 mm 2-year-old sub-adults, which were stocked
into Byers Lake as finglerings on June 17, 1997, at a mean
weight of 3.01 g (Appendix 2).
The remainder of the 1999 catch consisted of a single 4-year-old
adult brook trout, (Figure 3)
which weighed 1600 g and was 455 mm in length. This individual
is likely the progeny of the viable population that was
stocked in 1989 (see below).
At 185 mm, the mean growth rate of 2-year-old brook trout
was not as rapid as that observed in Bow
Lake or Butterfly
Lake, both of which received identical stocking treatments
to Byers. The age structure of the larger fish sampled was
not analyzed by the ageing contractor as its fin ray was
cut too far from the base of the fin. Its age has been estimated
at 4 years, but it has not been included in the growth analysis.
Management Recommendations

FIGURE 3. Brook trout sampled
at Byers Lake, August 27, 1999.
Click image to view 55K JPG |
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Byers Lake is more productive (TDS=140 mg/L) and has a
much larger surface and shoal area relative to Bow and Butterfly
lakes. These attributes suggest that the growth rate of
brook trout in Byers Lake should equal or exceed that determined
for the latter two lakes, since the stocking treatments
for all three lakes have been identical. However, the survey
data suggests that the opposite situation exists, whereby
growth of 2-year-old fish in Byers Lake is slower than that
recorded in the other lakes. This seemingly contradictory
finding supports a recommendation for additional sampling
in Byers Lake.
The presence of the 4-year-old brook trout suggests that
some limited natural recruitment may have occurred in the
past. Alternatively, this fish may have been part of an
illegal transfer of brook trout from another lake in the
park. Regardless of its origin, the extent of natural recruitment
in Byers Lake appears to be limited and is not likely to
be a cause for concern.
The current stocking plan for Byers Lake calls for 3000
fingerlings to be stocked at an alternate year frequency.
This schedule should be adhered to until such time as additional
growth data can be obtained from Byers Lake. A follow-up
sample in the summer of 2000 would substantiate the results
of the 1999 survey, and may provide some insight into the
anomolies noted in this study.
Literature Cited
Philip, D.F. 1985. A Reconnaissance
Survey of Byers Lake. Report prepared for the Fisheries
Branch, Ministry of Environment. Prince George.
Appendix 1.
Appendix 2.
For More Information:
Contact :Ted
Zimmerman
Sr. Fisheries Biologist, Omineca sub-Region
Prince George, B.C.
250-565-6852 |