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Ordinance 4175-26
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Ordinance 4175-26
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5/11/2026 1:13:14 PM
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5/11/2026 1:10:37 PM
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Ordinances
Ordinance Number
4175-26
Date
4/15/2026
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Exhibit B <br />ORDINANCE Exhibit A - Page 47 of 55 <br />19.37.185 BUFFER WIDTH AVERAGING FOR WETLANDS, LAKES AND STREAMS. <br />The city may allow buffer width averaging; provided, that the total area on the lot contained within the <br />buffer is not less than that required within the standard buffer, and that averaging will not reduce the <br />critical area functions. The city may require buffer width averaging in order to provide protection to a <br />particular portion of a critical area which is especially sensitive, or to incorporate existing significant <br />vegetation or habitat areas into the buffer. Buffer width averaging shall not adversely impact the <br />functions and values of the critical area. The adjusted minimum buffer width shall not be less than <br />seventy-five percent of the standard buffer width. <br />19.37.190 FISH AND WILDLIFE HABITAT CONSERVATION AREAS. <br />A. All areas meeting the definition of fish and wildlife habitat conservation areas are subject to the <br />regulations in this chapter. <br />B. Fish and Wildlife Habitat Conservation Areas Mapping. The approximate location and extent of fish <br />and wildlife habitat conservation areas within the city of Everett’s planning area are shown on maps <br />compiled and maintained by the city planning and community development department. These maps <br />shall be used as a general guide only for the assistance of property owners, project applicants, and other <br />interested parties; boundaries are generalized. The actual type, extent and boundaries of fish and <br />wildlife habitat conservation areas shall be determined by a qualified scientific professional according to <br />the procedures, definitions and criteria established by this chapter. In the event of any conflict between <br />the habitat location or type shown on the city’s fish and wildlife habitat conservation areas maps and <br />the criteria or standards of this chapter, the criteria and standards resulting from the field investigation <br />shall control. <br />C. Other mapping sources include the Washington State Department of Fish and Wildlife priority <br />habitat and species maps. <br />D. Goals and Additional Requirements. If a development or redevelopment is proposed on or within a <br />distance which could impact habitats of primary association, significant biological areas, and/or <br />vegetative corridors linking watersheds, as described in this title, the applicant shall provide a habitat <br />assessment. In areas within the riparian habitat zone or special flood hazard area, a biological <br />assessment is required. The biological assessment shall be prepared in accordance with Regional <br />Guidance for Floodplain Habitat Assessment and Mitigation produced by FEMA Region 10, April 2011, or <br />as amended. The biological assessment must demonstrate that any proposed development in the <br />riparian habitat zone or the floodway, coupled with appropriate habitat conservation measures, does <br />not adversely affect water quality, water quantity, flood volumes, flood velocities, spawning substrate, <br />and/or floodplain refugia for listed salmonids. <br />If the habitat assessment/biological assessment determines that the proposed development could <br />potentially adversely impact a fish and wildlife habitat conservation area, the applicant shall provide a <br />habitat management plan (HMP) as described in subsection G of this section, prepared by a wildlife <br />biologist for evaluation by the city, state and federal agencies. The HMP must address activities that can <br />be taken to preserve, protect, or enhance the affected fish and wildlife habitat conservation areas. The <br />HMP shall be based upon sound habitat management practices and be designed to achieve specific <br />habitat objectives. If the habitat assessment finds that the proposed development could result in <br />substantial elimination of or significant reduction in riparian corridors, existing connections between <br />critical areas, or continuous vegetated corridors linking watersheds, the HMP must analyze alternatives
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