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CHAPTER 5. CAPABILITY ASSESSMENT <br />5-3 <br />has been proposed, agencies receive comment and conduct further scientific reviews, after <br />which they must decide if the listing is warranted. Economic impacts cannot be considered in <br />this decision, but it may include an evaluation of the adequacy of local and state protections. <br />• Section 7: Consultation—Federal agencies must ensure that any action they authorize, fund, <br />or carry out is not likely to jeopardize the continued existence of a listed or proposed species <br />or adversely modify its critical habitat. This includes private and public actions that require a <br />federal permit. Once a final listing is made, non-federal actions are subject to the same review, <br />termed a “consultation.” If the listing agency finds that an action will “take” a species, it must <br />propose mitigations or “reasonable and prudent” alternatives to the action; if the proponent <br />rejects these, the action cannot proceed. <br />• Section 9: Prohibition of Take—It is unlawful to “take” an endangered species, including <br />killing or injuring it or modifying its habitat in a way that interferes with essential behavioral <br />patterns, including breeding, feeding or sheltering. <br />• Section 10: Permitted Take—Through voluntary agreements with the federal government <br />that provide protections to an endangered species, a non-federal applicant may commit a take <br />that would otherwise be prohibited as long as it is incidental to an otherwise lawful activity <br />(such as developing land or building a road). These agreements often take the form of a “Habitat <br />Conservation Plan.” <br />• Section 11: Citizen Lawsuits—Civil actions initiated by any citizen can require the listing <br />agency to enforce the ESA’s prohibition of taking or to meet the requirements of the <br />consultation process. <br />With the listing of salmon and trout species as threatened or endangered, the Pacific Coast states have been <br />impacted by mandates, programs and policies based on the presumed presence of listed species. Most West <br />Coast jurisdictions must now take into account the impact of their programs on habitat. <br />The Clean Water Act <br />The federal Clean Water Act (CWA) employs regulatory and non-regulatory tools to reduce direct pollutant <br />discharges into waterways, finance municipal wastewater treatment facilities, and manage polluted runoff. <br />These tools are employed to achieve the broader goal of restoring and maintaining the chemical, physical, <br />and biological integrity of the nation’s surface waters so that they can support “the protection and <br />propagation of fish, shellfish, and wildlife and recreation in and on the water.” <br />Evolution of CWA programs over the last decade has included a shift from a program-by-program, source- <br />by-source, and pollutant-by-pollutant approach to more holistic watershed-based strategies. Under the <br />watershed approach, equal emphasis is placed on protecting healthy waters and restoring impaired ones. A <br />full array of issues are addressed, not just those subject to CWA regulatory authority. Involvement of <br />stakeholder groups in the development and implementation of strategies for achieving and maintaining <br />water quality and other environmental goals is a hallmark of this approach. <br />National Flood Insurance Program <br />The National Flood Insurance Program (NFIP) provides federally backed flood insurance in exchange for <br />communities enacting floodplain regulations. Participation and good standing under NFIP are prerequisites <br />to grant funding eligibility under the Robert T. Stafford Act. The County and most of the partner cities for <br />this plan participate in the NFIP and have adopted regulations that meet the NFIP requirements. At the time <br />of the preparation of this plan, all participating jurisdictions in the partnership were in good standing with <br />NFIP requirements.