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the following modifications were implemented: (1) wrap additional "bridge trees" with metal <br />flashing; (2) raise the metal flashing on multi- stemmed trees to the height at which the stems were <br />separated by at least 24 inches (60 cm); (3) rotate the seam on the metal flashing to the downward <br />side of the trunk if possible; and (4) fell "suckers ", as needed, near the main trunk of the tree <br />(typically on basswoods, Tilia americana). <br />Colony status <br />With only 36 active nests in 24 trees, the 2005 season marked the lowest population of the Peltier <br />Lake colony since 1990. In 2005 only four Great Blue Herons fledged from three nests located in <br />two trees. However, these juveniles represented the first confirmed productivity from Peltier Lake <br />since at least 2003 and possibly since 2000. From 2006 to 2008, ground survey data (Table 5) <br />indicated a general increase in the size and productivity of the Peltier Lake colony. In 2008, a <br />minimum of 29 active trees, 54 active nests, and 70 chicks were documented. This represented an <br />increase above 2007 levels by 7.4 %, 28.6 %, and 29.6% respectively (Figure 31). As of 8 July 2008, a <br />minimum of 58 surviving chicks (presumed to have fledged) were documented; this estimate was a <br />34.9% increase above that recorded for the 2007 season. Since 2005, the Peltier Lake colony <br />experienced significant growth in the number of successful trees <br />An examination of the metal flashing on the two successful trees in 2005 showed no sign of <br />mesopredator climbing activity on one tree, but the second tree appeared to have been climbed <br />successfully (i.e., „breached ") despite having a predator guard. Given that this tree produced <br />fledglings, I assumed that the raccoon climbed past the predator guard after the chicks fledged. <br />Scratch patterns in the painted sheet -metal suggested that raccoons attempted to climb 47% (n = <br />81) of all protected trees during the 2005 season, 60% (n = 49) of which appeared to be successful <br />(Figure 32). Overall, 28% of the protected trees were successfully climbed. Thirty -nine trees <br />showing evidence of climbing attempts contained intact nests. Of the 19 active nest trees within the <br />colony, 79% (n = 15) showed evidence of attempted climbs and 58% (n = 11) appeared to have been <br />successfully climbed. Trees containing active nests were scratched disproportionately more than <br />those containing inactive nests (Chi- squared test, X2 = 11.15, df = 1, p = 0.0008). Based on nest <br />status (active vs. inactive), no significant difference in predator guard failure rate was detected. <br />Furbearer removal <br />In the fall of 2005, a total of 10 raccoons (3 ?) and 7 opossum (4 y) were harvested over a total of <br />181 trap nights. During the fall of 2006, a total of four raccoons (4 ?) and 14 opossum (only 2 9 <br />were recorded) were harvested over a total of 324 trap nights (Figure 34). During both seasons, <br />trapping activity was temporarily halted when island access became impossible during the lake°`s <br />winter "freeze -up" and as raccoon activity decreased with the temperature. <br />An interesting example of the benefits of tree guards is illustrated by the history of a specific large <br />basswood which was composed of three large trunks in close proximity (tag numbers #708, #709, <br />#999). This tree complex contained five and four active heron nests in 2005 and 2006 respectively. <br />