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Yukon River Chum Salmon
Freshwater Ecology and
Environmental Influences On Their Survival:
Ongoing
research and analyzes
(continued)
Methods
The
first step taken in the project was to characterize the study areas. Stream habitat measurements (e.g. water velocity, substrate
composition) were taken along transects.
The study sites were then mapped using surveying equipment. These
maps detail the stream channel, both full bank and low water flow, and
major features (e.g. beaver dams, weirs).
Benchmarks were established along the study area to facilitate
mapping of the study area and spawning locations (redds).
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Habitat
measurements along a transect in Hodgin’s Slough (left).
Field personnel use a theodolite to map in redd locations in Bluff
Cabin Slough (right).
Click on images for larger view. |
Two
weirs have been established each year at both Hodgin’s Slough (July –September)
and Bluff Cabin Slough (September – November), defining the lower and
upper boundaries of each study area.
Weirs are operated on a continual basis allowing free passage of
fish either upstream or downstream while maintaining a count of all fish
within the study area. Chum
salmon are processed as they enter the study area for the first time.
Mideye-hypural length, mideye-fork length, maximum depth, weight,
sex and condition are recorded and a genetic sample is taken.
A Peterson disk tag, with a unique color/number combination, is
affixed to allow identification. Otolith
and vertebrate samples are taken from carcasses, for aging purposes.
Foot surveys are conducted on a regular basis to provide an
independent estimate of the number of fish in the area and retrieve
carcasses.
Tracking
the number and movement of female chum salmon is an important aspect of
the study. By knowing the
number of females in the study area, a fecundity/length relationship can
be used to estimate potential egg deposition (PED).
Females are tracked, and spawning locations (redds) are mapped
using a theodolite. These
redd locations are then used to create a spawning distribution for the
area. Redd locations are
characterized in terms of habitat (e.g. water velocity, substrate
composition, and intergravel water temperature).
During
spring, emigrating smolts are captured using fyke nets.
Wings are attached to the fyke nets to increase channel coverage
and are extended or retracted to respond to flow changes.
The Hodgin’s Slough site requires high-water submersible funnel
nets during high-water events. Traps
are checked on a regular basis and species are identified, counted, and
immediately released.
Trap
efficiency is calculated by releasing known numbers of marked chum smolt
upstream of the trap. The
numbers of smolt leaving the study area are compared with the PED estimate
from the previous year to produce an estimate of egg-to-smolt survival
rates within the study areas.
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Comparison
of marked to unmarked chum
salmon smolt. Bismarck
Brown is used to produce the mark seen above.
Click on image for larger view.
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One
of our main focuses to date at the study sites has been to refine and
standardize methodologies. During
1997 and 1998, a hydraulic redd pump was used to estimate intergravel egg
and alevin survival rates and densities.
A further evolution of this research began in 1999 with the
initiation of a new sub-study.
This
sub-study is entitled “Quantification of upwelling as a determinant of
spawning site selection and quality for Yukon River chum salmon”.
Mini-piezometers
(stand pipes) have been systematically deployed along transects in both
summer-run and fall-run chum salmon spawning areas.
Piezometers allow us to measure vertical hydraulic gradient (VHG,
the pressure difference between intergravel and surface waters), substrate
permeability, and subsurface water velocity.
In addition, we take measure dissolved oxygen (DO), conductivity,
and temperature within each piezometer.
These data are allowing us to refine our characterization of
spawning habitat at both sites.
Initial
hydraulic and water quality measurements were used to determine the
appropriate sampling scheme for deployment of incubation basket groups.
These in situ incubation baskets are used to evaluate the
survival of eggs and alevins in relation to intergravel environmental
conditions. During 1999, at
both study sites, the eggs from three females were pooled and fertilized
using three males. Eggs were
counted into groups of 100 and each group placed into an incubation basket
with sieved gravel. Incubation
baskets were buried in clusters of three associated with individual
piezometers. One basket from
each group of three was removed at different life stages: one basket at
the eyed-egg stage, one at the pre-emergent stage, and the third basket
remaining in the gravel until emergence (Spring 2000).
Egg baskets were examined, and individual eggs, alevins, and fry
were enumerated and classified in the field as live or dead.
Results
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