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contingency bond. The area of this in-kind maintenance and contingency bond shall be at <br /> least equal to one-half the area required for compensation (1 additional acre of restoration <br /> for every 2 acres needed as compensation). Habitats that are restored/enhanced for the <br /> maintenance and contingency bond may be used or sold by the applicant to compensate <br /> for other impacts when all the 5-year performance standards established in the mitigation <br /> plan are met. Separate bonds may be required for monitoring. <br /> 15. Projects with Impacts Outside of the Estuary Study Area. Projects with impacts outside <br /> of the SEWIP study area may be compensated for within the SEWIP study area, <br /> consistent with the SEWIP restoration and/or enhancement goals and objectives. <br /> 16. Loss of Palustrine Wetlands. Compensation is required where existing palustrine <br /> wetlands will be converted to tidal habitat for compensatory mitigation. The acreages <br /> calculated per this regulation are set aside within the restored mitigation site and may not <br /> be considered as compensatory mitigation. However, to provide an incentive to <br /> developers to undertake tidal restoration as compensatory mitigation, while recognizing <br /> the range of functions provided by different types of isolated palustrine wetlands, the <br /> following ratios shall apply for wetlands, based on existing scores from the SEWIP <br /> freshwater model (SO Figure 5.1). Alternatively, a project proponent may rescore the <br /> site using that model to reflect existing conditions: <br /> • Fourth quartile (highest quality)—0.75 acre for each acre lost <br /> • Third quartile (moderate quality)—0.5 acre for each acre lost <br /> • Second quartile (fair quality)—0.3 acre for each acre lost <br /> • First quartile(lowest quality)—0.1 acre for each acre lost <br /> • No compensation shall be required for vegetated freshwater wetlands lost through <br /> restoration of tidal functions, if the restoration project is not used as compensatory <br /> mitigation. <br /> B. 1997 SEWIP Regulations (Apply to palustrine compensation only) <br /> The following mitigation ratios apply only to the development footprint identified in Figure 2.3A <br /> in SEWIP. <br /> 1. Unavoidable Impacts. Unavoidable impacts to wetland functions in the Snohomish River <br /> Estuary shall be compensated by restoring historic wetlands in the Estuary identified in <br /> the restoration plans (Table 2.1 and Chapter 5 in the 1997 SEWIP). <br /> lb. Where Compensation Can Occur. Compensation for impacts to vegetated palustrine <br /> wetlands may occur within the same Ecological Management Unit or within the adjacent <br /> Ecological Management Unit (See EMU Map, Figure 2.2 in the 1997 SEWIP). <br /> 2. Minimum Compensation Requirements. The minimum requirements for compensation <br /> will be one acre of restored wetland for one acre of wetland lost. <br /> 3a. How Compensation is Calculated. The acreage of compensation shall be calculated from <br /> the IVA function performance scores using the following ratio, provided that the <br /> 32 <br />