<strong>Adaptation</strong> <strong>and</strong> Mitigation 107infrastructure. When deltaic processes are re-established by reconnecting these marshareas to the Mississippi River, evidence from past projects indicates that they may besustainable even under some accelerated sea-level rise scenarios (DeLaune et al., 2003;Lane et al., 2006).Tidal WETLAND RESTORATION. By their nature, intertidal wetl<strong>and</strong> ecosystems occurwithin a narrow tidal range <strong>and</strong> are extremely vulnerable to even small changes insea level. <strong>Coastal</strong> wetl<strong>and</strong>s also sequester carbon at rates three to five times greater thanmature tropical forests (Murray et al., 2011); therefore, tidal wetl<strong>and</strong> restoration has implicationsfor minimizing the impacts of climate change on ecosystem services as well asmitigating climate change caused by greenhouse gas emissions.Recognizing this, Louisiana has been considering climate with regards to the sustainability<strong>and</strong> resilience of wetl<strong>and</strong>s restoration projects (CPRA, 2012). In the mid-Atlantic,coastal managers are strategically targeting restoration <strong>and</strong> protection efforts to ensurespace for wetl<strong>and</strong>s to migrate inl<strong>and</strong> as sea level rises <strong>and</strong> in many other areas of thecountry, coastal managers are working to create or restore tidal marsh to protect communities<strong>and</strong> assets from some coastal storm risk (Gregg et al., 2011) <strong>and</strong> evaluating theprojected resilience of individual marsh restoration projects in the context of acceleratedsea-level rise <strong>and</strong> sediment availability projections (Stralberg et al., 2011).Protecting Cultural RESOURCES. The above strategies are key to protectingbuilt infrastructure in the coastal zone. Wetl<strong>and</strong> restoration <strong>and</strong> the nourishment of barrierisl<strong>and</strong>s with sediment have the potential to reduce some of the impacts from sea-levelrise <strong>and</strong> storms to cultural resources. Cultural resources require unique managementstrategies because they are non-renewable. Some key areas of research, including materialsvulnerability, change monitoring, cultural heritage management, <strong>and</strong> damageprevention (UNESCO, 2008), are still needed to help identify the most relevant managementstrategies in the coastal zone. Increased flooding in the coastal zone will damagebuildings not designed to withst<strong>and</strong> prolonged immersion. Increases in storm intensity<strong>and</strong> high winds can lead to structural damage (UNESCO, 2008). In coastal communitiesin Alaska, diminished sea ice <strong>and</strong> melting of thermal coastal features are leadingto increased rates of erosion <strong>and</strong> are increasing the vulnerability of communities likeShishmaref <strong>and</strong> Kivilina. The challenges faced by some coastal communities <strong>and</strong> culturalresources will be to identify the relevant management strategy such as relocation/retreat, undertaken for the Cape Hatteras Lighthouse in North Carolina; protect in place,undertaken at Fort Massachusetts in Mississippi; or accommodate <strong>and</strong> allow coastalprocesses to alter the configuration of the coast at the site of these coastal resources (Caffrey& Beavers, 2008).Challenges, Needs, <strong>and</strong> OpportunitiesThe ability of institutions to conduct resource management <strong>and</strong> restoration in the contextof climate change is determined by many factors that collectively affect the institution’scapacity for dealing with change. These factors include the institution’s structure<strong>and</strong> mechanisms to affect change, ability to address complex technical information, recognitionof ecosystem service values, <strong>and</strong> need for actionable climate science.
108 <strong>Coastal</strong> <strong>Impacts</strong>, <strong>Adaptation</strong>, <strong>and</strong> <strong>Vulnerabilities</strong>Institutional STRUCTURE/MECHANISMS.It will be crucial to imbue all of our decisions (research, management, communications,<strong>and</strong> policy) with clear recognition as to the role climate change will play in their successor failure, <strong>and</strong> to incorporate uncertainty about the future into our planning.Hansen & Hoffman, 2010: pg. 33As discussed in the prior sections, consideration of climate change in coastal resourcemanagement <strong>and</strong> restoration efforts is growing in practice through a range of focused<strong>and</strong> exploratory efforts; however, in order to realize consideration of climate change,policies <strong>and</strong>/or directives are necessary to institutionalize consideration of climatechange in coastal management <strong>and</strong> restoration. Policies <strong>and</strong> directives have been established,such as the Maryl<strong>and</strong> Department of Natural Resources’ <strong>Climate</strong> Change Policythat directs the agency to “proactively pursue, design <strong>and</strong> construct habitat restorationprojects to enhance the resilience of bay, aquatic <strong>and</strong> terrestrial ecosystems to the impactsof climate change <strong>and</strong>/or increase on-site carbon sequestration” (Maryl<strong>and</strong> Departmentof Natural Resources, 2010: pg 14). Many more directives like this one will beneeded, particularly at the national scale, in order for climate resilience to be realized.Technical INFORMATION. Underst<strong>and</strong>ing the interactions between climatechange <strong>and</strong> the range of physical, chemical, <strong>and</strong> biological characteristics of coastal resourcesis complex (see Chapters 2 <strong>and</strong> 3 for an explanation of the nature of these complexities).Likewise, ascertaining how to incorporate consideration of climate changeinto coastal resource management <strong>and</strong> restoration efforts is difficult. Although sizablescientific confidence supports the need for activities that reduce non-climate stressors,the effectiveness of the measures that help systems adapt to climate change is not as evident,<strong>and</strong> their consideration requires a clear underst<strong>and</strong>ing of how a system functions<strong>and</strong> how it might be affected by climate change (Julius & West, 2008). In recognition ofthis need, a number of organizations, including non-profit, federal, state, <strong>and</strong> regionalpartners, have begun to develop frameworks (Figure 5-1) <strong>and</strong> exploratory guides to supportthe integration of climate change considerations into the restoration efforts (Glick etal., 2011; Hansen & Hoffman, 2010; Kane et al., 2011).Valuing ECOSYSTEM SERVICES. Recently, emphasis has been placed on the servicesthat ecosystems provide, such as storm surge buffers, clean water, <strong>and</strong> migratorybird habitat. In some cases an actual dollar value can be placed on the services provided,which has created new incentives for financial investments by the government, private,<strong>and</strong> corporate sectors in coastal resource protection <strong>and</strong> restoration (Cooley & Ol<strong>and</strong>er,2011). When managed effectively, protection or restoration of coastal ecosystems canprovide mutual societal, ecological, <strong>and</strong> financial co-benefits. This is an important newconcept because connecting the ecosystem services provided for greenhouse gas mitigationpurposes with adaptation needs is now conceptually possible. This may result innew mechanisms to fund costly adaptation strategies; for example, salt marsh restorationdesigned to be eligible for financial benefits such as carbon offset credits must demonstrate,among other factors, a life-expectancy of 75-100 years. In order to meet thesecriteria, the project design must take into account such external forces as sea-level rise,
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Chapter 3Lead Author: Carlton H. He
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ContentsKey TermsAcronymsCommunicat
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