Wahleach Project Water Use Plan Lower Jones Creek ... - BC Hydro
Wahleach Project Water Use Plan Lower Jones Creek ... - BC Hydro
Wahleach Project Water Use Plan Lower Jones Creek ... - BC Hydro
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
were completed for pink salmon during the spawning channel operation, recent site specific<br />
survey life is not available for either chum or pink in <strong>Lower</strong> <strong>Jones</strong> <strong>Creek</strong>. The<br />
values used for survey life (r) are based on available information from the literature. A<br />
maximum survey life value for both chum and pink salmon was applied to a model<br />
developed by Korman et al. (2002) (Equation 2) which results in a decaying survey life<br />
value as the spawning period progresses. With this model each day within the spawning<br />
period is given a specific survey life and the day-specific survey life is applied to the total<br />
count on the corresponding day.<br />
Equation 2. Daily survey life calculation<br />
�<br />
�<br />
�<br />
max�<br />
�<br />
��<br />
ri � r 1�<br />
r<br />
r<br />
�<br />
half �c<br />
t<br />
�<br />
i<br />
�<br />
�<br />
rhalf<br />
�c<br />
rhalf<br />
�c<br />
�<br />
� t<br />
half i ��<br />
Where:<br />
c = modified slope constant<br />
r max = maximum survey life possible<br />
t half = the day at which the survey life is half the maximum<br />
t l = day of the run<br />
The maximum survey life ( r max) is determined using the mean r calculated by Perrin and Irvine<br />
(1990), for salmon spawning in the Georgia Straight Region. The maximum<br />
survey life selected for both chum and pink salmon was 18 days. The day at which the<br />
survey life is half of the maximum value ( t half) was defined as the date at which the sum<br />
of the peak live plus dead count was greatest. The rate of change of the survey life or<br />
slope of the survey life curve (c = 1.25 for pink, c = 1.0 for chum) has been used in<br />
previous studies and was tailored to ensure a reasonable minimum survey life ( r min) as<br />
defined by the literature.<br />
Uncertainty regarding survey life is assumed to be normally distributed around the<br />
assessed value, with a standard deviation assessed in Perrin and Irvine (1990) and<br />
outlined in Table 1. The normally distributed error for survey life eri is then calculated as:<br />
Equation 3. Survey life estimate error calculation<br />
Er = 1.96 √ V(r)<br />
Table 1 Survey-life calculation constants applied to escapement calculations<br />
Species rmax V(r) c<br />
Chum 18 0.42 1.25<br />
Pink 18 0.44 1.00<br />
where:<br />
rmax<br />
= maximum estimated survey life<br />
V(r)= Variance (r)<br />
c = modified slope constant<br />
The WUP monitoring TOR also describes a visibility/observer efficiency error calculation.<br />
<strong>Lower</strong> <strong>Jones</strong> <strong>Creek</strong> Fish Productivity Monitoring 2008-2009 6