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improvement function on or immediately offsite in the same drainage basin. The habitat <br />functions for these wetlands can be mitigated off-site. <br />The basis for these recommendations is that the maintenance of stormwater/floodwater <br />control and water quality control functions, especially in upper watershed wetlands within <br />developed areas, is critical to the maintenance of the habitat functions of downstream <br />wetlands. Many of the upper watershed wetlands will have over 20% of their contiguous <br />basin developed in impervious surfaces. In fact some drainage basins are anticipated to have <br />60 - 80% of the portion of the basin in the Subarea in impervious surfaces. Therefore, it is <br />likely that these wetlands will have water level fluctuations that significantly reduce species <br />richness for plants and amphibians. Additionally, these wetlands are isolated and located <br />several thousands of feet from adjoining wetlands, wildlife corridors and riparian corridors <br />and have, therefore, limited importance to wildlife and low performance of habitat functions. <br />In these circumstances, it may be acceptable to move the habitat function to a larger offsite or <br />out of basin wetland ecosystem that has a higher potential to provide significant gains in the <br />habitat function. <br />When the water quality improvement and stormwater control functions of a wetland are <br />required to be maintained on or immediately adjacent to the site, they can be incorporated <br />into wetpond design for a proposed development. These existing functions, however, must <br />be provided in addition to what is required to treat and detain stormwater per City standards <br />for a new development or redevelopment. (SEPA Plant and Animal, Water, and Land and <br />Shoreline Use Policies) <br />3. When an applicant proposes to fill or alter all or a portion of a wetland, the wetland <br />replacement ratios shall be per the requirements of Chapter 37 of the Zoning Code unless <br />otherwise described below. Conceptual and detailed mitigation plans must be approved by <br />the Planning Director per the requirements of Chapter 37 of the Zoning Code. The following <br />potential mitigation sites/activities shall be considered: <br />• Creation or enhancement of wetlands and buffers where the mitigation would result in <br />connection of isolated habitat or widening narrow riparian or wildlife corridors. Where <br />significant additional upland buffers/wildlife corridors and connections are created and <br />the overall habitat function is increased beyond what would have occurred with the <br />creation and enhancement by itself using Zoning Code replacement ratios, the Planning <br />Director shall have the discretion to reduce wetland replacement ratios down to a <br />minimum of 1:1. <br />• Table 4-1 provides a summary of potential wetland mitigations by basin. <br />Note that where mitigation measures include raising the elevation of outlets in flow <br />through riparian systems, the mitigation will be subject to site-specific analysis <br />addressing the feasibility of the mitigation. The mitigation shall not be used for meeting <br />on-site stormwater detention requirements. The intent is to create additional wetlands <br />and increase the range of water depths to approximately .5 to 2 feet so that a mosaic of <br />