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' Only one black bear was observed in the Lick Creek drainage, but there was considerable <br />evidence of black bear activity found throughout the study area. The black bear <br />population in the North Fork Valley is high and continues to grow. Development <br />' activities in this and other project areas have not been a deterrent to their activities. <br />t When evaluating potential effects on big game habitat use from proposed development <br />activities two things must be considered; (1) numbers of animals that might use the area <br />for winter or transition range and (2) total amount of habitat available. Based upon <br />' observations made during these studies elk and deer numbers are low from spring <br />through fall. In the winter most animals will be found below where most development <br />activity will occur. Considering the amount of suitable habitat available throughout the <br />' area from spring through fall transition periods there will be little affect on either deer or <br />elk activity. <br />' NEOTROPICAL BIRDS <br />Birds observed, other than listed species and raptors, were what would be expected in the <br />' various habitat types found in the project area. A total of 68 species were observed while <br />conducting transects or as opportunistic observations. (See Table 5) In May there were <br />numerous species of migrating birds observed in the study area. By June numbers of <br />' those species declined as they had moved on through the area. In June and July birds that <br />breed in the area were observed almost exclusively. <br />' As is commonly found when conducting bird studies, there are preferred habitat types <br />within any study area. In addition, there are birds that are habitat generalists and others <br />that have specific habitat requirements. As shown by the data collected for this project <br />' the greatest diversity of birds was found in aspen and Gamble oak/mountain shrub <br />habitat. Riparian habitat typically has the highest diversity and density of birds and <br />would probably have been higher had there been more diverse riparian habitat in the <br />' study area. Riparian habitat was limited and lacked the vegetation typically found in <br />riparian areas where density and diversity of birds is higher. The greatest diversity of <br />birds in riparian habitat was found along the Dry Fork of Minnesota Creek in areas where <br />' there was less gradient and vegetation such as willows, hawthorn, alder and red osier <br />dogwood were more common. Many of the bird species shown for the riparian habitat <br />were also found in other adjacent oakbrush/mountain shrub habitat. This is a reflection <br />of the influence of neighboring habitat types. <br />The large expanses of aspen and oakbrush/mountain shrub habitat help minimize the <br />' potential impacts to neotropical birds from lost habitat due to construction of drill pads <br />and access roads. Considering the total number of acres of these types available and the <br />few acres that will be lost, potential impacts to these birds will be minor. In addition, as <br />' sites and roads are reclaimed species used to revegetate these areas will add to the <br />diversity of the areas. Observations made during other surveys conducted for energy <br />development projects in the North Fork Valley have shown that as vegetation becomes <br />' established along the road corridors and around pads, both the density and diversity of <br />birds increases. <br />15