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Barrie Creeks, Lovers Creek, and Hewitt's Creek Subwatershed Plan

Barrie Creeks, Lovers Creek, and Hewitt's Creek Subwatershed Plan

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The <strong>Barrie</strong> <strong><strong>Creek</strong>s</strong>, <strong>Lovers</strong> <strong>Creek</strong> <strong>and</strong> Hewitt’s <strong>Creek</strong> <strong>Subwatershed</strong> <strong>Plan</strong><br />

Long Term Trends at Site LOV101 of <strong>Lovers</strong> <strong>Creek</strong><br />

Site LOV101 is the monitoring site closest to the mouth of <strong>Lovers</strong> <strong>Creek</strong>. Data has been<br />

collected at this site since 2002 <strong>and</strong> is available up until 2010. Long term trends are available for<br />

IBI scores from 2003 to 2010, the correlation of effort spent versus amount of mottled sculpin<br />

captured (2003-2010) <strong>and</strong> the comparison of Hilsenhoff versus EPT (the difference between the<br />

Hilsenhoff <strong>and</strong> EPT index is that Hilsenhoff is an index that uses all the family groups of insects<br />

to evaluate the organic pollution in a stream, while EPT uses Ephemeroptera, Plecoptera <strong>and</strong><br />

Tricoptera – or shredders - as a percent of the entire sample of invertebrate to assess health)<br />

trends from 2002 to 2010.<br />

Figure 5-15 illustrates the long term IBI trends for Site LOV101. Based on the score rating<br />

mentioned previously, it can be seen that on average the site has a ‘fair’ rating. In 2003 <strong>and</strong><br />

2007, it had a rating of good. In 2005 though, there was a noticeable drop in the ecological<br />

integrity of the site down to a ‘poor’ rating. During this year, the fish community had low<br />

diversity, no top predators, no brook trout <strong>and</strong> an overall low abundance of fish.<br />

Figure 5-15: <strong>Lovers</strong> <strong>Creek</strong> IBI Scores for Site LOV101 (2003 - 2010).<br />

While long term data was not available for brook trout (the<br />

only record is one caught in 2010), it was for mottled<br />

sculpin, which are also a cold water species <strong>and</strong> occupy<br />

habitat similar to that used by brook trout. When years of<br />

data are compared, it is expected that with increased effort<br />

spent to capture fish there is a corresponding increase in<br />

the amount (weight) of fish caught. Changes in the<br />

community are indicated when effort increases but weight<br />

decreases (indicating that mottled sculpin populations have<br />

decreased) or when effort decreases <strong>and</strong> weight increases<br />

(indicating that mottled sculpin populations have<br />

increased). In 2006, the effort spent electrofishing<br />

increased but the overall weight of all the fish caught<br />

Mottled sculpin<br />

(Cottus bairdi)<br />

decreased, suggesting that populations had dropped that year. In 2008 <strong>and</strong> 2009, there was a<br />

decrease in effort <strong>and</strong> an increase in weight, suggesting that whatever decrease was seen two<br />

years prior had rebounded (Figure 5-16).<br />

Chapter 5: Aquatic Natural Heritage 248

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