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Wahleach Project Water Use Plan Lower Jones Creek ... - BC Hydro

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and the April 25 and April 29 capture efficiency results (0.565 and 0.336 respectively) were the<br />

highest on record since monitoring was initiated (Table 12). The increased efficiencies from<br />

these three tests increased the mean for this year from about 10% observed in previous years<br />

to about 25% (Table 12).<br />

Table 12 Summary of <strong>Jones</strong> <strong>Creek</strong> capture efficiencies during the WUP monitoring program.<br />

2008 -09 2007 - 08 2006 - 07 2005 - 06<br />

Test Chum Pink Chum Chum Pink Chum<br />

1 11.3% 11.4% 13.2% 13.6% 15.0% 20.5%<br />

2 6.5% 10.6% 12.1% 13.0% 15.3%<br />

3 56.5% 1.3% 9.5% 18.3% 8.0%<br />

4 33.6% 6.2% 8.2% 12.1% 6.8%<br />

5 19.3% 15.2% 12.1% 18.4% 18.9%<br />

6 8.4%<br />

7 10.7%<br />

Mean 25.4% 9.1% 13.2% 11.1% 15.4% 13.9%<br />

Note: Bold, italicized efficiencies shown for 2008-09 were observed during the dual-trap configuration<br />

described in this report.<br />

5.4 Flow and Channel Morphology<br />

Flows in <strong>Lower</strong> <strong>Jones</strong> <strong>Creek</strong> were periodically below the target flow of 1.1cms between<br />

September 15 and November 30 (Figure 5). Sub-target flows were measured between<br />

September 15 and October 30, 2008 while flows remained above 1.1cms for the remainder of<br />

the spawning period after October 30. During the period of sub-target flows, water in <strong>Lower</strong><br />

<strong>Jones</strong> was augmented from the siphon at <strong>Jones</strong> Lake Reservoir and the diversion at Boulder<br />

<strong>Creek</strong>. Metered flows of water from the siphon throughout this period indicated that<br />

approximately 50 to 60 % of the flow in <strong>Lower</strong> <strong>Jones</strong> <strong>Creek</strong> was being provided from the siphon.<br />

Continuous flow data for the spawning period is not available since the hydrometric station was<br />

not in service. The actual flows between the dates of our flow measurements are unknown.<br />

There were 12 flow measurements taken between Sept. 12 and Oct. 30 and 8 were below 1.1<br />

cms and 4 were above (Figure 5). Without the continuous flow data it is not clear exactly how<br />

long flows were above or below the 1.1 cms target.<br />

The low flows in <strong>Lower</strong> <strong>Jones</strong> <strong>Creek</strong> during the early and peak stages of spawning did not<br />

appear to prohibit access to spawning areas in the creek. Chum salmon were observed actively<br />

spawning in all areas of the creek during the sub-target flow period although the majority of the<br />

fish spawned in the lower sections of the creek.<br />

Although there have been no barriers to fish access identified during low flow conditions over<br />

the past few years, potential impacts do exist. Spawning habitat availability is reduced with<br />

lower flows, and could lead to crowding and redd superimposition. Fish may also undergo<br />

increased stress migrating through shallow waters, and could be more susceptible to predation.<br />

5.5 <strong>BC</strong> <strong>Hydro</strong> Enhancement Monitoring<br />

Over the past several years <strong>BC</strong> <strong>Hydro</strong> has undertaken habitat enhancement in lower <strong>Jones</strong><br />

<strong>Creek</strong> and Lorenzetti <strong>Creek</strong>. These enhancements include removal of the diversion weirs in<br />

<strong>Lower</strong> <strong>Jones</strong> <strong>Creek</strong> and the construction of off-channel rearing habitat and spawning platforms<br />

<strong>Lower</strong> <strong>Jones</strong> <strong>Creek</strong> Fish Productivity Monitoring 2008-2009 26

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