Clayton Falls Project Water Use Plan Aquatic - BC Hydro
Clayton Falls Project Water Use Plan Aquatic - BC Hydro
Clayton Falls Project Water Use Plan Aquatic - BC Hydro
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<strong>Clayton</strong> <strong>Falls</strong> WUP <strong>Aquatic</strong> Productivity Monitoring Program – Year 1, 2005<br />
2. METHODS<br />
The <strong>Aquatic</strong> Productivity monitoring program required selection of two sample sites for stream, fish and<br />
invertebrate data collection. One site was selected in Reaches 2 (downstream of falls) and another in<br />
reach 3 (upstream of falls). Snorkeling was also completed at each of these sites during 2005 sampling.<br />
2.1 Site Selection<br />
Sample site selection was based on methods devised my MOE (Ptolemy et al. 2006) for similar<br />
fry sampling in the Bella Coola <strong>Water</strong>shed, with each site area measuring near 100m 2 . A<br />
minimum area of 100m 2 was sought where practical, to standardize results with other studies in<br />
the region (e.g., Ptolemy et al., 2006). Fish density was expressed in fish number per 100 m 2 or<br />
fish per unit (FPU). Sites were fully (reach 2) or partially (reach 3) enclosed. Sites offering<br />
natural physical barriers such as mid-channel boulders were preferred since upstreamdownstream<br />
barrier nets were easier to install, more readily isolating the sample site. Based on<br />
methods described by Ptolemy et al., 2006, anticipated salmonid fry (e.g., Dolly Varden-<br />
Salvelinus malma, and coho- Oncorhynchus kisutch juveniles) were typically bounded by high<br />
velocities in mid stream sections; barrier nets extended well into the mid-stream area of the<br />
channel for the partially enclosed site (Photo 3).<br />
Physical site attributes and habitat types were recorded during site layout and included: habitat<br />
classification (riffle, rapid, cascade, glide, run, or pool) at each site; descriptions of depthvelocity<br />
profile at 0.25-0.5 m intervals perpendicular to flow (with shorter intervals over high<br />
velocity gradients); riparian vegetation; channel confinement; bed material composition;<br />
dominant particle size (Dmax and D90 cm); large woody debris (LWD) content; substrate<br />
embeddedness; site length; site wetted width; estimated available cover; and, maximum depth.<br />
2.2 Fish Collection<br />
Methods described by Ptolemy (pers. com, 2005 and Ptolemy et al. 2006), were used for<br />
sample site set up and sampling. Areas providing safe wading in the swift stream current (e.g.,<br />