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Wahleach Project Water Use Plan Wahleach Reservoir ... - BC Hydro

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hydroacoustic surveys was used in order to reduce the equipment requirements and<br />

effort necessary, but still allow for monitoring of the effects of fertilization on the<br />

reservoir fish populations.<br />

Gillnetting sampling sessions were completed in the spring of 2004 and 2005 (3 June<br />

2004, 7 June 2004) and in the fall of 2006 (21 October 2006). A springtime gillnetting<br />

session was planned for the end of June 2006 but was cancelled due to extremely<br />

warm water temperatures. During each sampling trip, three sinking and three floating<br />

gillnets were set in the <strong>Reservoir</strong> (Fig. 1). Each net consisted of panels of six different<br />

mesh sizes (25, 89, 51, 76, 38, 64 mm stretch mesh) and in total was 28 m long and 2<br />

m deep. All nets extended perpendicular from the shore. The floating nets were set<br />

in 3 m of water and the sinking nets were weighted to the bottom to the 10 m contour.<br />

Six baited Gee traps, baited with salmon roe, were also set in the evening and<br />

retrieved in the morning (Fig. 1). The traps sat on the bottom in approximately 2 m of<br />

water, a depth favored by sticklebacks. All gillnets and Gee traps were set in the late<br />

afternoon, fished overnight, and were retrieved the next morning. The minimum set<br />

time was 16 hours. Data from all nets were combined for calculation of mean catch<br />

per unit effort (CPUE) by species. Individual nets were not treated as replicates.<br />

Captured fish were identified using the Field Key to the Freshwater Fishes of British<br />

Columbia (McPhail and Carveth, 1993), with weight (on an electronic balance, or a<br />

Pasula spring scale for fish >600 g) and fork length recorded for each. Maturity<br />

stage (immature, maturing, mature, spawning, spent, resting) was visually<br />

determined from all kokanee, rainbow and cutthroat trout. Scale samples from each<br />

kokanee were taken, processed, and read as described in Ward and Slaney (1988).<br />

Scales were pressed into acetate and the imprint read under 30x magnification, with<br />

age determined by counting annuli. Condition factors were calculated which was<br />

defined as W/L 3 ·10 5 where W = weight in grams, L = fork length in mm. Aging data<br />

for 2004 and 2005 are currently being processed and will be examined in future<br />

reports.<br />

3.9 <strong>Hydro</strong>acoustics<br />

<strong>Hydro</strong>acoustic surveys have formed the basis of stock assessments in lakes and<br />

reservoirs for many years. A survey was completed in late July which determined<br />

stock distributions, size and abundance. A Simrad 120 kHz split beam echosounder<br />

with a downward looking 7.0 degree transducer was employed to collect the survey<br />

data. The transducer was towed along side of the survey boat at a depth of 0.5m,<br />

survey data was collected at 2pps along transects lines and stored on hard disk of a<br />

notebook computer. A Lowrance Sounder / GPS plotter was used to navigate along<br />

11 predetermined transect lines at a boat speed of ~1.5m·s -1 , Fig. 5.<br />

Split beam data was analyzed using Simrad EP500 version 5.3 processing software.<br />

This software calculates fish density per hectare (fish·ha -1 ) and fish target strength<br />

(TS) simultaneously by applying 20 and 40 log R Time Varied Gain (TVG) functions.<br />

<strong>Wahleach</strong> <strong>Reservoir</strong> Fertilization <strong>Project</strong>, 2004-2006.<br />

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