Recreational Fishery Stock Assessments
:
1999/2000 Data Report with
Management Recommendations
|

PHOTO 1. Nelson Lake
Aerial View, June 2001. Click
image to view 92K JPG |
|
|
|
|

PHOTO 2. Nelson Lake, May 2000.
Click image to view 92K JPG |
|
|
|
Introduction
|
TABLE 1. Physical Attributes of
Nelson Lake.
Waterbody identifier |
01162LCHL |
Water surface area |
10.9 ha. |
Area above 6 m contour |
7.0 ha. |
Shoreline perimeter |
1,800 m |
Maximum depth |
10 m |
Volume |
464,000 m3 |
Mean depth |
4.3 m |
Elevation |
861 m |
T.D.S. |
98 mg/L |
Morphoedaphic index |
22.8 |
|
|
This report presents the results of two stock assessment
surveys conducted on Nelson Lake between 1999 and
2000. A gill net survey was performed on July 15, 1999 under
a partnership arrangement between the Ministry of Environment,
Lands and Parks and the Carrier
Sekani Tribal Council (CSTC). A followup angling
survey was subsequently conducted on June 25, 2000 to evaluate
angling catch success rates and to obtain an additional
sample of stocked rainbow trout for comparison with the
1999 data. This work was done in partnership with the Spruce
City Wildlife Association. The following report
presents the results of both assessments.
Nelson Lake is located 42 km south of Prince George, or
31.6 km south of Highway 16 on the Blackwater Forest Service
road. The lake is accessed by a 100 metre trail from the
road to the lake's shore.
The lake was first surveyed in October 1988,
after it had been initially stocked
with rainbow trout in May of the same year. No other species
of fish were captured, and it is assumed that the lake was
barren prior stocking. The lake was stocked to provide a
low-use, high yield "family" fishery to recreational anglers.
An alternate year stocking schedule was established in 1992,
four years after its initial stocking, and the lake remained
on this schedule until 1996.
In the spring of 1997 anecdotal reports were received that
suggested a winterkill may have occurred during the winter
of 1996/97, as no fish had been observed or angled that
spring. A one day survey was completed by the Ministry in
July 1997, (data on file) during which angling was conducted
and a gill net was deployed. This effort yielded 9 rainbow
trout, 8 of which were angled, confirming that a winterkill
had not occurred, or at least had not significantly reduced
the trout population.
Also in 1997 the SCWA elected to take an active role in
the management of the Nelson Lake fishery by growing at
their hatchery the yearlings that were originally earmarked
for spring release into Nelson Lake. The trout were grown
on site through the summer and were then released in the
fall; the Association continued to hold, mark, and release
yearlings in this manner until 1999.
By 1999 the lake was given a high priority for assessment
in order to determine the status of the recreational fishery
and the success of the SCWA summer rearing program. Funding
for this work was obtained from Fisheries
Renewal B.C., administered through the Upper
Fraser-Nechako Fisheries Council. Margo French, Lawrence
Ward, and James Prince of the CSTC conducted the fieldwork
for the 1999 assessment.
Upon preliminary review of the 1999 field data, it was
determined that the sample size of fish captured was too
small to permit a thorough review of the status of the fishery.
This was partially due to the vandalism of one of the net
sets (see below) and the destruction of its catch. To increase
the sample size while minimizing fish mortalities, a live
sampling program was scheduled for 2000. This effort was
funded internally by BC Environment and was performed by
Ministry staff and SCWA volunteers.
Methods
1999 GILL NET SURVEY
A 91.4 m sinking monofilament gill net with experimental
mesh sizes was set in Nelson Lake at 10:20 AM on July 14,
1999, according to the methods specified in the Resource
Inventory Committee document Fish
Collection Methods and Standards. The net was deployed
in an E-W orientation from the east shore (Figure 1) and was retrieved on July 15 at 9:20 AM. The net
was then re-deployed from the north shore in a N-S orientation
and left overnight. On July 16, it was discovered that the
net and the fish it had captured overnight had been pulled
into shore and burned. Only the results of the first net
set are reported here; the total soak time of this set was
23.0 hours.
|
 FIGURE 1. Location of Nelson Lake
gill net sets, July 15, 1999. Click image to
view detailed 69K map. |
|
All trout collected were sampled for fork length (mm),
weight (to 50 g), sex, and maturity. Stomach contents were
examined in the field. Scales were collected for age structure
analysis, which was performed by Darlene
Gillespie of TimeMark Consulting Ltd. (Nanaimo, B.C.).
2000 ANGLING SURVEY
A total of 9 anglers fished Nelson Lake on June 25, 2000
using a variety of hardware. Seven of the anglers fished
from 10:20 AM until 2:20 PM; the remaining two anglers fished
until 1:20 PM, for a total combined effort of 34 angler-hours.
All but 10 captured fish were measured for fork length (mm)
and weight (± 1 g). Sex, maturity, and stomach contents
were not evaluated due to the live sampling techniques employed.
Scale samples were collected, however these structures were
not aged at the time of writing.
Results and Discussion
CATCH SUMMARY
1999 GILL NET SAMPLE
The net catch yielded 17 rainbow trout (RB) for
a catch per unit effort (CPUE) of 0.74 RB per net-hour.
No other species were captured. See Appendix
1 for specific fish attribute data. Two fish were classified
as immature; the remaining 15 were mature. Fifteen fish
were female, one was male, and the sex of one could not
be identified.
TABLE 2. Physical attributes of
rainbow trout sampled in Nelson Lake, comparing 1999
and (2000) results.
|
Attribute |
Mean |
Range |
Std. Dev. |
Length (mm) |
291 (233) |
170-380 (156-345) |
58 (49) |
Weight (g) |
201 (146) |
10-500 (40-470) |
152 (99) |
Condition |
0.63 (1.01) |
0.11-0.91 (0.86-1.15) |
0.23 (0.06) |
|