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 />
Site CF2 yielded considerably less fish during similar collection efforts as Site CF1. This was<br />
attributed largely to Site CF2 being upstream of <strong>Clayton</strong> <strong>Falls</strong>, which provides a natural<br />
upstream barrier to fish migration. Only two Dolly Varden were collected during intensive single<br />
pass electrofishing at Site CF2 on Septemer 13, 2005. No other fish were observed at this site<br />
during the fish collection period.<br />
Species<br />
Dolly<br />
Varden<br />
Total<br />
Catch<br />
Capture<br />
Probability<br />
Table 5: Fish Collection Data 1 , Site CF 2<br />
Site Pop. Estimate<br />
(95% confidence)<br />
Avg.<br />
weight (g)<br />
Total<br />
weight (g)<br />
Biomass<br />
(g/100m 2)<br />
Avg.<br />
length (mm)<br />
Condition<br />
Factor<br />
2 1.0 2 9.1 18.2 17.51 102.0 0.729<br />
1- Data assessed through MicroFish 3.0 for Windows<br />
Supplementary Snorkelling<br />
Unadjusted snorkel counts were completed on September 13 at Site CF1. A single snorkeler,<br />
encompassing one half of the stream unit of Reaches 2 and 1 (from the base of the waterfall to<br />
tide water and North Bentnick Arm, completed the count. The following numbers of fish were<br />
observed:<br />
• 64 adult pink salmon;<br />
• 29 juvenile coho (fry and parr); and,<br />
• 53 Dolly Varden (parr and sub adults).<br />
Two person unadjusted snorkel counts were also completed on one half of the stream unit of<br />
the sample site at Reach 3 on September 20, resulting in observation of one (1) Dolly Varden<br />
sub adult.<br />
3.2 Benthic Invertebrate Sampling<br />
Benthic invertebrate sampling in <strong>Clayton</strong> Creek presented many field and logistical difficulties,<br />
ultimately resulting in inadequate data collection for useful ecological monitoring. Original<br />
design required placement of gravel and cobble filled wire baskets (Anon., 1997), however;<br />
baskets available from <strong>BC</strong> <strong>Hydro</strong> were insufficient size and dimension to accommodate<br />
substrate of an adequate amount and size for effective invertebrate colonization in the turbulent<br />
water of <strong>Clayton</strong> Creek. The baskets supplied were relatively ‘flat’, measuring 30 cm x 30 cm x<br />
10 cm high (Photo 5), limiting large cobble inclusion and also inhibiting basket placement depth<br />
within the stream substrate. It was also noted stream substrate in reach 2 (below the falls) was<br />
typically large boulder, cobble and bedrock substrate, making it difficult to place baskets in the<br />
stream channel with limited substrate smaller than boulder (>256 mm) present in Reach 2,<br />
limiting ability to embed baskets in substrate as described in the available guidance document<br />
(Anon., 1997).<br />
During Sept 10 basket placement stream flow was relatively high (actual discharge<br />
undetermined; Photo 6). Subsequently, on later return to the sample site for routine monitoring<br />
by personnel during anticipated low water (November, 8 2005), it appeared some baskets had<br />
previously been, or ultimately would be de-watered. Upon consultation with <strong>BC</strong> <strong>Hydro</strong>, it was<br />
determined to leave the baskets in location for later retrieval. On or around November 10<br />
through 15, 2006 there was a significant rain-on-snow freshet event resulting in high- to<br />
Kynoch Resources<br />
9