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<br />............................................................................................................. F RAY E 0 SA F E T Y NET S <br /> <br />In 1994 and 1995, Defenders of Wildlife <br /> <br />sponsored a series of roundtable discussions of <br />the ESA among industrial and non-industrial <br />private landowners, conservationists and govern- <br />ment representatives. Although there were dis- <br />agreements, participants agreed that some prob- <br />lems could be solved if the ESA was funded ade- <br /> <br />quately and used to encourage more public-pri- <br />vate conservation partnerships (Ferris 1996). <br />Meanwhile, other experts were recommending <br />that economic incentives be used to engage more <br />private landowners in conservation. In this set- <br />ting, conservation planning has emerged as an <br />incentive-based approach that potentially can <br />address both conservationist and private <br />landowner concerns. <br /> <br />. <br /> <br />Advent of Conservation Planning <br /> <br />In 1982, Congress amended the ESA in a <br />way that radically altered its application on non- <br />federal land. This was by authorizing habitat <br />conservation plans. The impetus came from a <br />decade-long battle between developers and envi- <br />ronmentalists over the fate of San Bruno <br />Mountain, several thousand acres of mostly <br />undeveloped land five miles from San Francisco. <br />Two endangered butterfly species occurred on <br />the mountain. In a highly unusual move, devel- <br />opers and environmentalists, joined by local offi- <br />cials, developed a plan allowing some develop- <br />ment to occur but protecting most of the butter- <br />flies' habitat. But there was concern that the plan <br />would violate the ESA because it allowed <br />destruction of some occupied butterfly habitat. <br />To remedy the problem, Congress changed the <br />ESA to permit incidental taking of endangered <br /> <br />species by private landowners provided they <br />develop habitat conservation plans (HCPs) to <br />offset the damage. <br />Few landowners developed HCPs until the <br />early 1990s. Only 12 HCPs were approved <br />between 1983 and 1992 (FWS and NMFS <br />1996). Since 1992, however, there has been an <br />explosion of such approvals - 200 by the end of <br />1996. By September, 1997, millions of acres <br />nationwide were covered by more than 220 <br />HCPs. Indeed, HCPs have become one of the <br />most prominent mechanisms employed by FWS <br />to address the problem of threatened and endan- <br />gered species on private lands. <br />This rapid proliferation has led in turn to <br />widespread concern among conservationists and <br />independent scientists that plans are not being <br />prepared with adequate scientific guidance and, <br />in fact, may seriously undermine species recovery <br />(Murphy et al. 1997-see Appendix B). ESA- <br />related conservation planning for private <br />landowners, however, now goes beyond HCPs. <br />Increasingly, new legal tools are being developed <br />to address multispecies and ecosystem planning, <br />raising some of the same concerns that are being <br />directed toward H CPs. <br /> <br />Types of ESA-Related Conservation Plans <br /> <br />Landowners can develop several different <br />types of ESA-related conservation plans. The <br />HCP is the most widely used. Because it is avail- <br />able only for landowners with listed species on <br />their property, the Clinton administration has <br />established "safe harbor" agreements that encour- <br />age landowners to maintain suitable habitat not <br />occupied by endangered species. The administra- <br />