<strong>Adaptation</strong> <strong>and</strong> Mitigation 113al., 2011). Such systematic assessments will be essential to supporting informed tool selectionby potential users (NRC, 2009).Although specifics vary, most guidance on tool selection centers on roughly the samecore idea: the importance of selecting tools based on an assessment of user goals, objectives,context, resources, <strong>and</strong> skills rather than trying to make management or researchproblems fit within the framework of a previously selected tool. Commonly expressedconcerns are that users will select inappropriate tools based on what sounds impressive,seems easy, or has been used by others they know (for example, using a rankingtool when the management question is how to reduce the vulnerability of a particularspecies), or will seek or put too much emphasis on projections for species distributionchanges or similar ecological shifts when data are insufficient to support such analyses.These problems clearly occur; what is unclear is how common they are <strong>and</strong> how muchtime is wasted, both of which could lead to poor decision-making. Further, no clearthreshold has been established for when data or analyses are too limited or flawed to bevalid; increasing guidance on how to decide when available data cannot support the desiredtool or what caveats must be included with the outputs would be extremely useful.Another commonly expressed concern relates to the need to provide support <strong>and</strong>guidance for decision making under conditions of uncertainty. Tools can be designed<strong>and</strong> used to facilitate <strong>and</strong> improve vulnerability assessment <strong>and</strong> adaptation planning regardlessof gaps or flaws in the data (NRC, 2009). By using a variety of tools or runningthem multiple times with a range of different parameters such as sea-level-rise rates,exploring a range of plausible future scenarios is possible. Formal or informal sensitivityanalyses can help to identify the variables with the largest uncertainty as well as thosevariable that have the greatest influence on the decisions at h<strong>and</strong> or, for purely scientificendeavors, the variables with the greatest influence on the system under consideration(Stralberg et al., 2011).Policy <strong>and</strong> Regulatory ToolsPolicy options for adapting to climate change include both a broad array of governmentalauthorities <strong>and</strong> a range of possible pathways. The governmental activities includeregulatory, taxation, planning, spending, <strong>and</strong> the general facilitation of private action(Grannis, 2011). The possible pathways include protecting existing l<strong>and</strong> uses from thesea, which includes shoreline armoring; relocating human activities through retreat; <strong>and</strong>modifying human activities to enhance adaptive natural capacity of ecosystems by reducingstressors).Governments are evaluating how to factor climate change into spending decisionsto conserve public funds over the long-term <strong>and</strong> ensure that public assets such as roadways<strong>and</strong> wastewater treatment facilities are resilient. Maryl<strong>and</strong>’s plan recognizes thatpublic investments in shore protection will be needed to protect critical facilities. Otherstates, such as California, are examining how they can direct funding to protect coastalresources to acquire vulnerable l<strong>and</strong>s for conservation, to provide room for ecosystemsto migrate inl<strong>and</strong> to keep pace with sea-level rise, to provide a buffer for infrastructure,<strong>and</strong> to buy out vulnerable property owners.Governments are also re-evaluating how they regulate coastal areas. Regulatoryoptions include using zoning powers to require additional setbacks from shorelines,
114 <strong>Coastal</strong> <strong>Impacts</strong>, <strong>Adaptation</strong>, <strong>and</strong> <strong>Vulnerabilities</strong>density restrictions, clustered subdivisions, <strong>and</strong> building-size limits (NOAA, 2010). InMaryl<strong>and</strong>, the state is instituting regulatory measures through its Living Shorelines ProtectionAct to encourage l<strong>and</strong>owners to use soft alternatives to shoreline armoring wherefeasible. Some authors have suggested the use of the “rolling easement” approach inwhich l<strong>and</strong>owners are entitled to build <strong>and</strong> use their l<strong>and</strong> as long as it remains dry buthave no expectation of preventing the rising sea from reclaiming their l<strong>and</strong> (Titus, 1998).Some states, such as Oregon, Texas, South Caroline, Rhode Isl<strong>and</strong>, Massachusetts, <strong>and</strong>Maine, have applied this approach in statutes or regulations. A recent federal report emphasizesthat rolling easements can also be implemented by the private sector throughconservation easements or traditional property law arrangements (Titus, 2011). Thesereports acknowledge that the timing for implementing any regulatory approach will becritical; although coastal armoring is well understood <strong>and</strong> generally requires a lead timeof a decade or less, nonstructural pathways, such as a gradual retreat from the coast, areless tested <strong>and</strong> may require a lead time of several decades.Governments are also considering tax- <strong>and</strong> market-based incentives to promote differentpathways. Some examples include incentives such as conservation easements toencourage l<strong>and</strong>owners to conserve vulnerable l<strong>and</strong>s, density bonuses <strong>and</strong> transferrabledevelopment rights to develop sites upl<strong>and</strong>, or tax rebates for homeowners who designstructures to exceed building code requirements by elevating structures to increaseresiliency.Several different approaches have been proposed for evaluating responses to employ<strong>and</strong> evaluating the tradeoffs. In choosing options, some of the issues that policymakersare weighing include: the relative economic costs <strong>and</strong> benefits of a particular responses;how protective the response is for the health, safety, <strong>and</strong> welfare of the community;<strong>and</strong> the environmental benefits or impacts of a response (NOAA, 2010). To be successful,chosen responses must also be administratively <strong>and</strong> legally feasible. Administrativechallenges to this include budget <strong>and</strong> staffing constraints, <strong>and</strong> technical complexity(IPCC, 1990; NOAA, 2010); government actors also must have legal authority to implementa response <strong>and</strong> responses must be consistent with existing laws <strong>and</strong> constitutions(Grannis, 2011).5.4 <strong>Coastal</strong> Mitigation OpportunitiesThe coastal zones of the U.S. have the potential to host many of our climate changemitigation efforts. This includes siting of non-greenhouse emitting energy generationthrough off-shore wind, tidal, <strong>and</strong> wave generation <strong>and</strong> ocean thermal conversion todisplace or replace fossil fuel combustion methods of generation. Recent Departmentof Energy reports indicate that about one-third of the country’s annual electricity needscould be generated through wave <strong>and</strong> tidal current (EPRI, 2011; Haas et al., 2011). Additionally,initial exploration of the concomitant carbon sequestration benefit may be realizedwhen new resource management practices are employed in coastal habitats such assalt marshes, seagrasses, <strong>and</strong> mangroves.<strong>Coastal</strong> Renewable TechnologiesAs the U.S. develops strategies to reduce greenhouse gas emissions <strong>and</strong> foster energy
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Chapter 3Lead Author: Carlton H. He
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ContentsKey TermsAcronymsCommunicat
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Key TermsxixExposure 3 - The nature
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