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<br />,.............. ...........".,.... ... ....".,.......... ..........,..,.............. ........ ................,..".".,.........,..........,..,.".,..,..,........,.......... F RAY E 0 <br /> <br />SAFETY NETS <br /> <br />protection, edge effects and the effects of urban- <br />ization may have a large impact on the warblers. <br />Twenty percent of the plan's preserves are within <br />330 feet of the preserve boundary or other type <br />of edge. The biological advisory team recom- <br />mends that less than five percent of any preserve <br />be within that distance from an edge, and <br />research subsequent to the team's recommenda- <br />tions indicated that these warblers will not occu- <br /> <br />py otherwise suitable habitat that has 1-10 <br />homes within 1,650 feet or has 11-30 percent <br />urbanization within one kilometer (Engels <br />1995). In addition, utility corridors currently <br />cut through some of the preserves, increasing <br />edge (although there are steps to reduce this <br />under the plan). Moreover, urbanization itself <br />has other effects such as increased numbers of <br /> <br />o <br /> <br />nest predators such as blue jays (Cyanocitta <br />cristata), which will add to edge effects in <br />decreasing the carrying capacity of reserves <br />(Engels and Sexton 1994). Given these indica- <br />tions from biological research, the plan's preserve <br />design may support a much smaller warbler pop- <br />ulation than anticipated. <br />According to the recovery plan for the gold- <br />en-cheeked warbler (FWS 1992b), recovery will <br />not be sufficient until each of eight regions has at <br />least one viable population on its own or <br />through connections to other regions. One of <br />the eight regions encompasses the Balcones plan- <br />ning area. In addition, the warblers in Travis <br />County are particularly important because the <br />county has 40 percent more warbler habitat than <br />any other county. Despite the importance of this <br />area, it is possible that the planning area will not <br />sustain viable populations of the two bird species <br /> <br />because of the insufficient preserve acreage, edge <br />effects and lack of intensive habitat management. <br /> <br />Multiple-Species Planning <br /> <br />The complexity of preserve design discussed <br />above is magnified when multiple species are <br />taken into account. Nevertheless, all conserva- <br /> <br />tion plans affect multiple species, whether or not <br />they result in incidental-take permits for multi- <br />ple species. Conservation planning for multiple <br />species, including unlisted species, can address <br />the dilemma of preventing the decline of species <br />before they are critically endangered and receive <br />protection under the E~A. The trade-off, how- <br />ever, is that landowners want incidental-take per- <br />mits issued for multiple endangered species, as <br />well as a commitment that the HCP is sufficient <br /> <br />for unlisted species, so that no additional actions <br />are required upon new listings. When this assur- <br />ance is granted, unlisted species that become list- <br />ed in the future will be included in the inciden- <br />tal take permit unless FWS can demonstrate that <br />the HCP would jeopardize the continued exis- <br />tence of the species. This assurance to the <br />landowner regarding his/her responsibilities for <br />species that could be listed in the future is an <br />extremely important incentive to landowners, <br />especially those in areas with a high density of <br />proposed and candidate species, such as <br />California and Florida. <br />Providing assurances to landowners for <br />unlisted species must be accompanied by ade- <br />quate conservation for those species in the con- <br />servation plan. Congress clearly intended as <br />much in establishing Section lOin 1982: "In the <br />event that an unlisted species addressed in the <br />