• <br /> Environmental Consequences <br /> C This chapter is the scientific and analytic basis for <br /> ap ya the comparison of the alternatives. This chapter <br /> describes the probable consequences (Le., effects) of each alternative on the selected <br /> environmental resources. The chapter is arranged by alternatives, with a discussion of issues (in <br /> the same order they were presented in Chapter 3) under each alternative. <br /> Alternative 1 (Proposed Action) <br /> Watershed drainage function <br /> Alternative 1 would not affect watershed drainage functions. Current conditions including the acreage <br /> of protected riparian area and the length of protected waterways would remain unaltered. <br /> Wildlife Habitat <br /> Alternative 1 would not impact wildlife habitat. Current habitat including the acreage of habitat <br /> vegetated with native forest and the contiguity with adjacent wildlife habitat would remain unaltered. <br /> Native Plant Populations <br /> Alternative 1 would not impact native plant populations. Current habitat including the acreage of <br /> native dominated plant communities, and acres of the site vulnerable to invasion would remain <br /> unaltered. Currently there are 5.5 acres of the property that are within 50' of Dillard Road. This <br /> acreage would not change. <br /> Soil Resources <br /> Alternative 1 would not impact soil resources. Current soil resources including the acreage of <br /> disturbed soil would remain unaltered and in its current stable condition. <br /> Alternative 2 (No Action) <br /> Watershed drainage function <br /> Alternative 2 would lead to degradation of watershed drainage functions. Development of home <br /> sites, roads, and utility infrastructure would leave waterways and riparian buffers unprotected. <br /> There would likely be several road crossings installed with culverts and it is possible that backyard <br /> fences would abut the waterway leaving it vulnerable to dumping and other degradation. <br /> Impervious surface would be increased significantly. Using the lower end estimate of 77 homes at <br /> an average roof area of 1,800 ft and a driveway of 900 ft produces 4.8 acres of impervious surface. <br /> In addition, estimating approximately 15,000 feet of new roads (a double loop road across the site) <br /> and sidewalks at a width of 38' produces another 13 acres of impervious surface. Thus, the <br /> development would increase impervious surface by at least 17.8 acres. Using the higher figure of <br /> 115 homes results in a total impervious surface increase of over 20 acres. <br /> The increase in impervious surface, reduction in riparian buffer and reduction in forest cover would <br /> result in an increase in both the rate and quantity of flow in the waterways during storm events. This <br /> increase would lead to erosion of the channel bottom and sides destabilizing the channel and leading <br /> to downcutting. <br /> Wildlife Habitat <br /> Alternative 2 would significantly reduce wildlife habitat. Using the minimum number of home sites (77) <br /> and multiplying by the minimum lot size in a low density R -1 development (4,500 ft results in a <br /> reduction of 8 acres of habitat vegetated with native forest. In addition, native forest habitat is further <br /> reduced 13 acres by roads, assuming 15,000 linear feet of roads at a width of 38'. Thus, at a <br /> minimum the site would have 21 acres of habitat loss. Using the higher figure of 115 home sites to <br /> calculate habitat loss results in 25 acres. <br /> In addition, the site will be fragmented by roads and home sites." Remaining habitat will be in small <br /> patches and will not likely be contiguous to adjacent wildlife habitat areas. <br />