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Design of US Habitat Banking Systems to Support the Conservation ...

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A DETAILED LOOK AT WETLAND AND CONSERVATION BANKINGlocal regula<strong>to</strong>ry and resource agency representativesthat are signa<strong>to</strong>ries <strong>to</strong> a bank agreement and oversee<strong>the</strong> establishment, use, and operation <strong>of</strong> a conservationbank.” Apart from this definition, <strong>the</strong> Guidancementions such review teams only twice, and <strong>the</strong>n onlyin passing. Those brief mentions provide that <strong>the</strong> parties<strong>to</strong> a banking agreement should establish a reviewteam and that state and local agencies that participatein a bank agreement should be part <strong>of</strong> <strong>the</strong> team. Theonly specific task <strong>of</strong> <strong>the</strong> team o<strong>the</strong>rwise mentioned in<strong>the</strong> Guidance is that <strong>of</strong> receiving moni<strong>to</strong>ring reportssubmitted <strong>to</strong> it in accordance with <strong>the</strong> terms <strong>of</strong> abanking agreement.Characterization and Quantification <strong>of</strong> Creditsand DebitsThe goal <strong>of</strong> any form <strong>of</strong> compensa<strong>to</strong>ry environmentalmitigation is <strong>to</strong> secure some resource gain from conservationefforts at a mitigation site <strong>to</strong> compensate, or<strong>of</strong>f-set, a resource loss at an authorized impact site.Of necessity, this requires that resource agencies beable <strong>to</strong> characterize and quantify <strong>the</strong> relevant gainsand losses at <strong>the</strong> two sites in a manner that allows fora meaningful comparison. This is an inherently difficulttask, but it bears emphasis that it is a task thatresource agencies must undertake regardless <strong>of</strong> <strong>the</strong>mitigation method employed (i.e. project-by-projectversus banking). In order <strong>to</strong> avoid completely arbitraryproject-by-project mitigation decisions, resource agenciesresponsible for setting mitigation requirementsmust do so in accordance with some consistentlyapplied principles.Whereas <strong>the</strong> principles that guide project-by-projectcompensa<strong>to</strong>ry mitigation decisions are <strong>of</strong>ten not readilydiscerned, those that apply <strong>to</strong> wetland and conservationbanks are generally quite transparent. Indeed,one <strong>of</strong> <strong>the</strong> virtues <strong>of</strong> banking may be that it obligesresource agencies <strong>to</strong> clearly articulate <strong>the</strong> consistentprinciples upon which <strong>the</strong>ir mitigation decisions willbe made. Those principles determine not only howmany credits a bank may <strong>of</strong>fer, but also how many <strong>of</strong>those credits will be required <strong>to</strong> compensate for specificresource losses at impact sites.Wetland Mitigation BanksWetland mitigation banks need a system for evaluating<strong>the</strong> amount <strong>of</strong> functional loss at <strong>the</strong> impact siteand <strong>the</strong> amount <strong>of</strong> functional gain at <strong>the</strong> bank site <strong>to</strong>determine <strong>the</strong> amount <strong>of</strong> compensation required <strong>to</strong><strong>of</strong>fset <strong>the</strong> functional loss. The “currency” that is used <strong>to</strong>evaluate <strong>the</strong> amount <strong>of</strong> compensation that is requiredis a wetland credit. A wetland mitigation bank credit isdefined as a “unit <strong>of</strong> measure representing <strong>the</strong> accrualor attainment <strong>of</strong> aquatic functions” at a bank. 171 Creditsare generally characterized by a functional measure,acres, or some combination <strong>the</strong>re<strong>of</strong>.The anticipated number <strong>of</strong> credits that <strong>the</strong> bank willgenerate is generally outlined in <strong>the</strong> bank instrument.Before credits may be released for sale <strong>the</strong>y must becertified by <strong>the</strong> MBRT. The banking instrument alsospecifies <strong>the</strong> method or methods that will be used <strong>to</strong>certify credits. Federal guidance states that mitigationshould provide for functional replacement andsuggests that bank sponsors use an “appropriate functionalassessment methodology” 172 <strong>to</strong> assess <strong>the</strong> results<strong>of</strong> compensa<strong>to</strong>ry activities and determine <strong>the</strong> number<strong>of</strong> credits that will be available at <strong>the</strong> bank. In order<strong>to</strong> evaluate whe<strong>the</strong>r or not functional replacement isbeing achieved, <strong>the</strong> same functional assessment methodologyused <strong>to</strong> evaluate credits at <strong>the</strong> compensationsite should be used <strong>to</strong> evaluate debits at <strong>the</strong> impactsite.Several federal guidance documents have stated thatin <strong>the</strong> absence <strong>of</strong> more definitive information on<strong>the</strong> functions <strong>of</strong> a specific wetland site, a minimumone-<strong>to</strong>-one acreage replacement may be used as areasonable surrogate <strong>to</strong> achieve no net loss <strong>of</strong> wetlandfunctions. 173 In practice, banks <strong>of</strong>ten rely on acreage,or some combination <strong>of</strong> functional assessment, acreage,and best pr<strong>of</strong>essional judgment, <strong>to</strong> determine <strong>the</strong>number <strong>of</strong> credits available.Functional equivalency measuresAlthough <strong>the</strong> use <strong>of</strong> functional equivalency measuresfor determining credits remains <strong>the</strong> goal, <strong>the</strong> devel-171 <strong>Banking</strong> Guidance (1995), § III. F.172 <strong>Banking</strong> Guidance (1995), § D.7.173 1990 MOA, § III. B.; <strong>Banking</strong> Guidance (1995), § 2.d.7.; RGL 02-2(2002), § 2.d.4.44 Environmental Law Institute

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