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<br />..................................................................................................................................,.. F RAY E 0 S A F E T Y NET S <br /> <br />fa <br /> <br />study must be performed, but incidental take <br />outside potential habitat is permitted through <br />the HCP. For the bay checkerspot butterfly, the <br />only individuals lived on one portion of the <br />mountain, which was already protected by San <br />Mateo County. The HCP simply contained a <br />prohibition on development or trail building <br />within those areas of the county park and estab- <br />lished annual monitoring for this species. <br />Particular care was taken to avoid impacts on <br />another federally endangered species, the San <br />Francisco garter snake (Thamnophis sirtalis <br />tetrataenia). FWS and the California <br />Department of Fish and Game had determined <br />that suitable habitat existed on the mountain, <br />but they could not find the species in searches of <br />the area. When the HCP was developed, the <br />environmental consulting firm contracted a <br />research herpetologist at U.c. Berkeley expert on <br />the San Francisco garter snake, Ted Papenfuss, to <br />prepare a map of the snake's potential habitat on <br />the mountain. As with the elfin, further impact <br />studies must be done for development to occur <br />in those Botential habitat areas. If snakes are <br />found, no take can occur. Outside potential <br />habitat areas, incidental taking through develop- <br />ment is permitted under the HCP. <br />The approach contained in this HCp, which <br />emphasizes thorough survey for the covered <br />species, designation and protection of potential <br />habitat, and assurances to landowners for areas <br /> <br />outside potential habitat, is a practical approach <br />to planning for multiple species. Under this <br />approach, landowners can receive assurance that <br />development can occur in areas that are not <br />potential habitat, but habitat destruction is not <br /> <br />permitted in occupied or suitable unoccupied <br />habitat until more information is available and <br />the exact impact is known. <br /> <br />Washington DNR's Blanket Assurances <br /> <br />Since the San Bruno Mountain HCP in <br />1982, conservation plans have become consider- <br />ably more complicated, covering larger areas and <br />affecting more sensitive species. In Washington, <br />the HCP for state-owned land managed by the <br />Department of Natural Resources (1.6 million <br />acres) contains assurances that the incidental take <br />permit will include each species that becomes <br />listed during the 70 to 100 years of the HCP, <br />unless the plan would jeopardize the species' <br />continued existence. Determining jeopardy to <br />such species, however, will be extremely difficult <br />because DNR did not survey for these species <br />before the HCP, and "under this HCP, DNR <br />shall not be required to survey for nests, dens, <br />roosts, or individual occurrences of unlisted <br />species" (p. N-134, Draft HCP). <br />In the HCP document, each unlisted but <br />sensitive species that may be on the property is <br />individually addressed. For nearly every sensitive <br />species, however, there is a justification of why <br />the conservation strategy designed for owls, mur- <br />relets and salmon suffices for habitats needed by <br />these other sensitive species. It may be true that <br />species that become listed in the future will coin- <br />cide with suitable habitat created under the <br />HCP. Unfortunately, for many species it will be <br />impossible to predict whether this is true, despite <br />the blanket assurances for DNR provided under <br />the HCP. For example, species that depend <br />upon old growth habitat will be included in the <br />