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compensation (i.e., which is the limiting function) will determine the required overall <br /> compensation acreage in order to ensure that the limiting function is adequately <br /> compensated for. Excess compensation acreage for the nonlimiting function shall not be <br /> available as compensation for other habitat impacts. <br /> 9. Use of Average Restoration Potential Per Acre. An average restoration potential per acre <br /> shall be used to establish the compensation requirements in cases where several AUs are <br /> restored simultaneously (as in a compensation bank) or where several individual project <br /> impacts are to be mitigated in a single restoration project. This average is calculated by <br /> summing the potential increase in IVA-acre points and dividing by the total acreage of <br /> the site. This average shall then be used to determine the acres of compensation required <br /> according to Regulations 35.A. 3 and 6 or 7. <br /> 10. Guidelines for Developing Compensatory Mitigation Plans. Compensatory mitigation <br /> and monitoring plans (CMMPs) with applicable performance standards submitted under <br /> the SEWIP plan should follow the interagency "Guidelines for Developing Freshwater <br /> Wetlands Mitigation Plans and Proposals" (Department of Ecology Publication #94-29), <br /> which is subject to amendment by Department of Ecology and future acceptance by the <br /> City. CMMPs shall be circulated to the SSOTAC for review and comment and for <br /> adaptive management purposes as provided in Salmon Overlay Section 5.6. Applicants <br /> should consider the overall restoration objectives set forth in SO Chapter 6. <br /> 11. Performance Criteria. Standards and performance criteria shall be established for each <br /> mitigation action as described in SO Section 5.6 and stated in the CMMP. <br /> 12. Monitoring Requirements. Each compensation site shall be monitored over a period of <br /> up to10 years as described in SO Section 5.6. <br /> 13. Threatened, Endangered, or Commercially Important Species. All tidal and associated <br /> riparian areas within the SEWIP planning area are designated critical habitat for chinook <br /> salmon and are likely to also constitute important habitat for coho salmon and <br /> anadromous native char. If areas in the UGA have other threatened, endangered or <br /> commercially important species,then the compensation plan shall incorporate design <br /> measures to mitigate any impacts to these species and their habitats. <br /> 14. 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 /> 15. 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 /> 38 <br />