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here. - Ministry of Forests, Lands and Natural Resource Operations

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In the Thompson-Okanagan Region, western hemlock looper was found at 69% <strong>of</strong> the 16 three-tree beating sites<br />

sampled, with an average <strong>of</strong> 9.6 larvae per site, down from 28.0 larvae per site in 2011. Decline <strong>of</strong> the hemlock<br />

looper in the Serpentine <strong>and</strong> Mud Lake sites was likely due to the operational spray program undertaken in 2012.<br />

In the North Thompson, few larvae were recorded at Finn Creek <strong>and</strong> TumTum Lake <strong>and</strong> no larvae were found at<br />

Serpentine Creek, Thunder River, Mud Lake <strong>and</strong> Murtle Lake (Table 14). Population trends in the Mabel Lake/<br />

Three-Valley Gap to Scotch Creek area varied, with small increases at Perry River North <strong>and</strong> Yard Creek, <strong>and</strong><br />

significant decreases at Three Valley Gap, Perry River South <strong>and</strong> the Mabel Lake area (Kingfisher Creek <strong>and</strong><br />

Noisy Creek). Minor decreases in larval abundance were noted at Scotch Creek <strong>and</strong> Crazy Creek. Larval populations<br />

increased slightly, just south <strong>of</strong> Sugar Lake along the Shuswap River <strong>and</strong> Greenbush Lake. Figure 8 shows<br />

the variation from 2010 to 2012 in the number <strong>of</strong> western hemlock looper larvae present in three-tree beatings at<br />

sites in the Thompson Okanagan Region.<br />

In the Kootenay-Boundary Region, western hemlock looper was recorded at 63% <strong>of</strong> the 25 three-tree beating<br />

sites sampled, compared to 84% in 2011, <strong>and</strong> 71% in 2010 (one site was not sampled in 2012 due to flooding).<br />

Larval counts were down slightly with an average <strong>of</strong> 18.9 per site in 2012 compared to 21.9 per site in 2011. The<br />

highest larval counts were east <strong>of</strong> Revelstoke at Beaver River <strong>and</strong> Jumping Creek, followed by two sites north<br />

<strong>of</strong> Revelstoke at Bigmouth <strong>and</strong> Pitt Creeks. The only sites with notable larval increases were Sutherl<strong>and</strong> Falls,<br />

Martha Creek <strong>and</strong> Jumping Creek. Overall populations south <strong>of</strong> Revelstoke decreased from an average <strong>of</strong> 5.6<br />

larvae per site to 1.8 larvae per site, while north <strong>and</strong> east <strong>of</strong> Revelstoke, the average larval count decreased from<br />

39.5 larvae per site to 21.0 larvae per site (Figure 9). These decreases are in part due to the 2012 operational spray<br />

program conducted north <strong>of</strong> Revelstoke at the Goldstream <strong>and</strong> Downie Creek sites. Trace defoliation was noted<br />

at two sites: Goldstream River <strong>and</strong> Pitt Creek.<br />

The three major defoliators found during the 2001 to 2003 outbreak in the Kootenay Boundary Region were<br />

western hemlock looper, sawflies <strong>and</strong> western blackheaded budworm, in order <strong>of</strong> relative abundance. Since 2008,<br />

sawflies numbers have remained consistent, while hemlock looper numbers increased in 2011 <strong>and</strong> 2012. Very<br />

low numbers <strong>of</strong> western blackheaded budworm have been observed since 2006.<br />

Figure 8. Western hemlock looper larval counts at sixteen sites in the Thompson Okanagan Region<br />

from 2010 through 2012.<br />

<strong>Ministry</strong> <strong>of</strong> <strong>Forests</strong>, <strong>L<strong>and</strong>s</strong> <strong>and</strong> <strong>Natural</strong> <strong>Resource</strong> <strong>Operations</strong>, Kamloops, B.C.<br />

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