A. 
Wetlands are those areas that are inundated or saturated by surface or ground water at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil conditions. Wetlands generally include swamps, marshes, bogs, and similar areas. All areas meeting the definition of a wetland and identification criteria as wetlands pursuant to SMC § 20.80.415, regardless of any formal identification, are hereby designated critical areas and are subject to the provisions of this chapter.
Wetlands do not include those artificial wetlands intentionally created from nonwetland sites, including, but not limited to, irrigation and drainage ditches, bioswales, canals, detention facilities, wastewater treatment facilities, farm ponds, and landscape amenities, or those wetlands created after July 1, 1990, that were unintentionally created as a result of the construction of a road, street, or highway. Wetlands may include those artificial wetlands intentionally created from nonwetland areas to mitigate the conversion of wetlands.
B. 
Wetlands help to maintain water quality; store and convey stormwater and floodwater; recharge ground water; provide important fish and wildlife habitat; and serve as areas for recreation, education, scientific study and aesthetic appreciation.
C. 
The City’s overall goal shall be to achieve no net loss of wetlands. This goal shall be implemented through retention of the function, value and acreage of wetlands within the City. Wetland buffers serve to moderate runoff volume and flow rates; reduce sediment, chemical nutrient and toxic pollutants; provide shading to maintain desirable water temperatures; provide habitat for wildlife; protect wetland resources from harmful intrusion; and generally preserve the ecological integrity of the wetland area.
D. 
The primary purpose of the wetland regulations is to avoid detrimental wetland impacts and achieve a goal of no net loss of wetland function, value and acreage; and where possible enhance and restore wetlands.
(Formerly 20.80.310. Ord. 238 Ch. VIII § 5(A), 2000; Ord. 398 § 1, 2006; Ord. 695 § 1 (Exh. A), 2014; Ord. 723 § 1 (Exh. A), 2015; Ord. 1045 § 1 (Exh. A), 2025)
A. 
All wetlands shall be rated by a qualified professional according to the current Washington State Department of Ecology wetland rating system, as set forth in the Washington State Wetland Rating System for Western Washington 2014 Update, Version 2.0 (Ecology Publication No. 23-06-009, or as revised). Wetland rating categories shall be applied as the wetland exists on the date of adoption of the rating system by the City, as the wetland naturally changes thereafter, or as the wetland changes in accordance with permitted activities.
1. 
Category I. Category I wetlands are those that represent unique or rare wetland types, are more sensitive to disturbance than most wetlands, are relatively undisturbed and contain ecological attributes that are impossible to replace within a human lifetime, or provide a high level of functions. The following types of wetlands are Category I:
a. 
Relatively undisturbed estuarine wetlands larger than one acre;
b. 
Wetlands of high conservation value that are identified by scientists of the Washington Natural Heritage Program/DNR;
c. 
Bogs;
d. 
Mature and old-growth forested wetlands larger than one acre;
e. 
Wetlands in coastal lagoons; and
f. 
Wetlands that perform many functions well (scoring 23 points or more based on functions).
2. 
Category II. Category II wetlands are those that are difficult, though not impossible, to replace and provide high levels of some functions. The following types of wetlands are Category II:
a. 
Estuarine wetlands smaller than one acre, or disturbed estuarine wetlands larger than one acre;
b. 
Interdunal wetlands larger than one acre or those found in a mosaic of wetlands; and
c. 
Wetlands with a moderately high level of functions (scoring between 20 and 22 points).
3. 
Category III. Category III wetlands are those with a moderate level of functions, generally have been disturbed in some ways, can often be adequately replaced with a well-planned mitigation project, and are often less diverse or more isolated from other natural resources in the landscape than Category II wetlands. The following types of wetlands are Category III:
a. 
Wetlands with a moderate level of functions (scoring between 16 and 19 points); or
b. 
Interdunal wetlands between 0.1 and one acre.
4. 
Category IV. Category IV wetlands are those with the lowest levels of functions (scoring below 16 points) and are often heavily disturbed. These are wetlands that should be able to replace, or in some cases to improve. However, experience has shown that replacement cannot be guaranteed in any specific case. These wetlands may provide some important functions, and also need to be protected.
B. 
Illegal Modifications. Wetland rating categories shall not change due to illegal modifications or alterations. A wetland’s category shall be based on the pre-modification/alteration analysis of the wetland.
C. 
At the time of adoption of the updated critical areas regulations, Ordinance 1045, there were no identified Category I wetlands identified within the City of Shoreline. If this category of wetland is subsequently identified, any applicable standards may be added or modified by the Director based on Washington State guidance on protection of the identified type of resource where the adopted regulations do not address the specified type of wetland.
(Formerly 20.80.320. Ord. 238 Ch. VIII § 5(B), 2000; Ord. 398 § 1, 2006; Ord. 695 § 1 (Exh. A), 2014; Ord. 723 § 1 (Exh. A), 2015; Ord. 1045 § 1 (Exh. A), 2025)
A. 
Standard Wetland Buffer Width. The standard buffer widths in Table 20.80.420(A)(1) have been established in accordance with the best available science. The buffer widths shall be determined based on the category of wetland and the habitat score as assigned by a qualified wetland professional using the Washington State Wetland Rating System for Western Washington.
1. 
All buffers shall be measured perpendicular from the wetland boundary as surveyed in the field. The buffer for a wetland created, restored, or enhanced as compensation for approved wetland alterations shall be the same as the buffer required for the category of the created, restored, or enhanced wetland.
2. 
The standard buffer widths assume that the buffer is a relatively intact native plant community in the buffer zone adequate to protect the wetland functions and values at the time of the proposed activity. If the existing buffer is bare ground, sparsely vegetated, or vegetated with nonnative or invasive species that do not perform needed functions, then the applicant must either develop and implement a wetland buffer restoration or enhancement plan to maintain the standard width to create the appropriate plant community or the buffer must be widened to ensure that adequate functions of the buffer are provided.
3. 
The use of the standard buffer widths requires the implementation of the mitigation measures in Table 20.80.420(A)(2), where applicable to the development type, to minimize the impacts of the adjacent land uses.
4. 
If an applicant chooses not to apply the appropriate mitigation measures in Table 20.80.420(A)(2), then a 33 percent increase in the width of all buffers is required. For example, a 75-foot buffer with the mitigation measures would be a 100-foot buffer without them.
Table 20.80.420(A)(1) Wetland Buffer Requirements
Wetland Category
Buffer Width According to Habitat Score
Habitat Score of 3 – 4
Habitat Score of 5
Habitat Score of 6 – 7
Habitat Score of 8 – 9
Category I: Based on total score or Forested
75 ft
105 ft
165 ft
225 ft
Category I: Estuarine
150 ft (no change based on habitat scores)
Category II: Based on total score
75 ft
105 ft
165 ft
225 ft
Category III (all)
60 ft
105 ft
165 ft
225 ft
Category IV (all)
40 ft (no change based on habitat scores)
Table 20.80.420(A)(2) Required Measures to Minimize Impacts to Wetlands (Measures are required, where applicable to a specific proposal)
Disturbance
Activities and Uses That Cause Disturbances
Required Measures to Minimize Impacts
Lights
• Parking lots
• Warehouses
• Manufacturing
• Residential
• Direct lights away from wetland.
Noise
• Manufacturing
• Residential
• Locate activity that generates noise away from wetland.
• If warranted, enhance existing buffer with native vegetation plantings adjacent to noise source.
• For activities that generate relatively continuous, potentially disruptive noise, such as certain heavy industry or mining, establish an additional 10 ft heavily vegetated buffer strip immediately adjacent to the outer wetland buffer.
Toxic runoff*
• Parking lots
• Roads
• Manufacturing
• Residential areas
• Application of agricultural pesticides
• Landscaping
• Route all new, untreated runoff away from wetland while ensuring wetland is not dewatered.
• Establish covenants limiting use of pesticides and fertilizers within 150 ft of wetland.
• Apply integrated pest management.
Stormwater runoff
• Parking lots
• Roads
• Manufacturing
• Residential areas
• Commercial
• Landscaping
• Retrofit stormwater detention and treatment for roads and existing adjacent development.
• Prevent channelized flow from lawns that directly enters the buffer.
• Use low intensity development techniques (per PSAT publication on LID techniques).
Change in water regime
• Impermeable surfaces
• Lawns
• Tilling
• Infiltrate or treat, detain, and disperse into buffer new runoff from impervious surfaces and new lawns.
Pets and human disturbance
• Residential areas
• Use privacy fencing OR plant dense vegetation to delineate buffer edge and to discourage disturbance using vegetation appropriate for the ecoregion.
• Place wetland and its buffer in a separate tract or protect with a conservation easement.
Dust
• Tilled fields
• Use best management practices to control dust.
Disruption of corridors or connections
• Maintain connections to off-site areas that are undisturbed.
• Restore corridors.
Notes:
* These examples are not necessarily adequate for minimizing toxic runoff if threatened or endangered species are present at the site. Additional mitigation measures may be required based on recommendation of a qualified professional, third party review, or State agency recommendations.
B. 
Increased Wetland Buffer Width. Buffer widths shall be increased, on a case-by-case basis as determined by the Director, when a larger buffer is necessary to protect wetland functions and values. This determination shall be supported by a critical area report, prepared by a qualified professional at the applicant’s expense, showing that it is reasonably related to protection of the functions and values of the wetland. The critical area report must include, but not be limited to, the following criteria:
1. 
The wetland is used by a plant or animal species listed by the Federal government or the State as endangered, threatened, candidate, sensitive, monitored, or documented priority species or habitats, or the wetland is essential or outstanding habitat for those species or has unusual nesting or resting sites such as heron rookeries or raptor nesting trees; or
2. 
The adjacent land has slopes greater than 15 percent and is susceptible to severe erosion, and erosion-control measures will not effectively prevent adverse wetland impacts; or
3. 
The adjacent land has minimal vegetative cover. In lieu of increasing the buffer width where existing buffer vegetation is inadequate to protect the wetland functions and values, development and implementation of a wetland buffer restoration/enhancement plan in accordance with SMC § 20.80.435 may be substituted.
C. 
Reduced or Averaged Wetland Buffer Width. A reduced or averaged standard wetland buffer width may be allowed under the following circumstances:
1. 
Buffer averaging to improve wetland protection may be permitted when all of the following conditions are met:
a. 
The wetland has significant differences in characteristics that affect its habitat functions, such as a wetland with a forested component adjacent to a degraded emergent component or is a “dual-rated” wetland with a Category I area adjacent to a lower rated area;
b. 
The buffer is increased adjacent to the higher functioning area of habitat or more sensitive portion of the wetland and decreased adjacent to the lower functioning or less sensitive portion as demonstrated by a critical areas report from a qualified wetland professional;
c. 
The total area of the buffer after averaging is equal to the area required without averaging; and
d. 
The buffer at its narrowest point is never less than either three-fourths of the required width or 75 feet for Category I and II, 50 feet for Category III, and 25 feet for Category IV, whichever is greater.
2. 
Averaging, through a critical area reasonable use permit consistent with SMC § 20.30.333 or critical area special use permit consistent with SMC § 20.30.336 or a shoreline variance consistent with 20.220.040, may be permitted when all of the following are met:
a. 
There are no feasible alternatives to the site design that could be accomplished without buffer averaging;
b. 
The averaged buffer will not result in degradation of the wetland’s functions and values as demonstrated by a critical areas report from a qualified wetland professional;
c. 
The total buffer area after averaging is equal to the area required without averaging; and
d. 
The buffer at its narrowest point is never less than either three-fourths of the required width or 75 feet for Category I and II, 50 feet for Category III, and 25 feet for Category IV, whichever is greater.
3. 
When the voluntary creation or expansion of a wetland that is not required as mitigation for a development proposal and would increase the area of the wetland and/or wetland buffer a buffer that is no less than 75 percent of the standard width shall be established. Further reductions in standard buffer width may be granted if the following are demonstrated:
a. 
A wetland buffer 75 percent of standard width would significantly limit the use of the property for existing or permitted uses, thus making the wetland creation or expansion project infeasible;
b. 
The proposed width reduction is the minimum necessary to achieve the restoration project;
c. 
There will be a net environmental benefit from the restoration project with the reduced riparian management zone width;
d. 
Granting the proposed relief is consistent with the objectives of the wetland creation or expansion project and consistent with the purposes of the City’s critical area regulations.
D. 
Buffers on Mitigation Sites. All mitigation sites shall have buffers consistent with the buffer requirements of this chapter. Buffers shall be based on the expected or target category of the proposed wetland mitigation site.
E. 
Buffer Maintenance. Except as otherwise specified or allowed in accordance with this chapter, wetland buffers shall be retained in an undisturbed or enhanced condition. In the case of compensatory mitigation sites, removal of invasive nonnative weeds is required for the duration of the required monitoring period.
F. 
Overlapping Critical Area Buffers. If buffers for two contiguous critical areas overlap (such as riparian management zone for a stream and a wetland buffer), the wider area applies.
G. 
Physically Separated and Functionally Isolated Wetland Buffers. Consistent with the definition of “buffers” (SMC § 20.20.012), areas that are functionally isolated and physically separated from wetland due to existing, legally established roadways, railroads, or other legally established structures or paved areas eight feet or more in width that occur between the area in question and the wetland shall be considered physically isolated and functionally separated wetland buffers and shall not be subject to the standards of this chapter. The obstruction causing the physical isolation or functional separation shall be significant enough in size that the wetland buffer cannot reasonably perform any of the ecological functions of a buffer including water quality, stormwater and floodwater conveyance, groundwater recharge and wildlife habitat. A critical areas assessment prepared by a qualified professional determining whether the area is functionally isolated is required unless deemed unnecessary by the Director.
(Formerly 20.80.330. Ord. 238 Ch. VIII § 5(C), 2000; Ord. 398 § 1, 2006; Ord. 469 § 1, 2007; Ord. 695 § 1 (Exh. A), 2014; Ord. 723 § 1 (Exh. A), 2015; Ord. 1045 § 1 (Exh. A), 2025)
A. 
Report Required. If the Director determines that the site of a proposed development includes, is likely to include, or is adjacent to, a wetland, a wetland critical area report shall be required, at the applicant’s expense. Critical area report requirements for wetland areas are generally met through submission to the Director of one or more wetland critical area reports. In addition to the general critical area report requirements of SMC § 20.80.065, critical area reports for wetlands must meet the requirements of this section. Critical area reports for two or more types of critical areas must meet the report requirements for each relevant type of critical area.
B. 
Minimum Report Contents for Wetlands. The written critical area report(s) and accompanying plan sheet(s) shall contain the following information, at a minimum:
1. 
The minimum report contents required per SMC § 20.80.065(D);
2. 
For each wetland identified on site and off site within 300 feet of the project site provide:
a. 
The wetland rating, including a description of and score for each function, per wetland ratings (SMC § 20.80.415);
b. 
Required buffers (SMC § 20.80.420);
c. 
Hydrogeomorphic classification;
d. 
Wetland acreage based on a professional survey from the field delineation (acreages for on-site portion and entire wetland area including off-site portions);
e. 
Cowardin classification of vegetation communities;
f. 
Habitat elements;
g. 
Soil conditions based on site assessment and/or soil survey information; and
h. 
To the extent possible, hydrologic information such as location and condition of inlet/outlets (if they can be legally accessed), estimated water depths within the wetland, and estimated hydroperiod patterns based on visual cues (e.g., algal mats, drift lines, flood debris, etc.). Provide acreage estimates, classifications, and ratings based on entire wetland complexes, not only the portion present on the proposed project site.
3. 
An analysis of site development alternatives, including a no-development alternative;
4. 
An assessment of the probable cumulative impacts to the wetlands and buffers resulting from the proposed development;
5. 
A conservation strategy for habitat and native vegetation that addresses methods to protect and enhance on-site habitat and wetland functions; and
6. 
An evaluation of the functions of the wetland and adjacent buffer. Include reference for the method used and data sheets.
(Formerly 20.80.340. Ord. 723 § 1 (Exh. A), 2015; Ord. 1045 § 1 (Exh. A), 2025)
A. 
Activities and uses shall be prohibited in wetlands and wetland buffers, except as provided for in this chapter.
B. 
Activities Allowed in Wetlands. The activities listed below are allowed in wetlands. Additional allowed activities are listed in SMC § 20.80.080, Allowed Activities. Exemptions are listed in the provisions established in SMC § 20.80.075, but do not apply within the shoreline jurisdiction. These activities do not require submission of a critical area report, except where such activities result in a loss of the functions and values of a wetland or wetland buffer.
1. 
Conservation or preservation of soil, water, vegetation, fish, shellfish, and/or other wildlife that does not entail changing the structure or functions of the existing wetland.
2. 
Drilling for utilities/utility corridors under a wetland, with entrance/exit portals located completely outside of the wetland buffer; provided, that the drilling does not interrupt the ground water connection to the wetland or percolation of surface water down through the soil column. Specific studies by a hydrologist are necessary to determine whether the ground water connection to the wetland or percolation of surface water down through the soil column will be disturbed.
C. 
Activities Allowed in Wetland Buffers. The activities listed below are allowed in wetland buffers. Additional allowed activities are listed in SMC § 20.80.080, Allowed activities. Exemptions are listed in SMC § 20.80.075, but do not apply within the shoreline jurisdiction. These activities do not require submission of a critical area report, except where such activities result in a loss of the functions and values of a wetland or wetland buffer.
1. 
Utility Drilling. Drilling for utilities/utility corridors under a buffer, with entrance/exit portals located completely outside of the wetland buffer boundary; provided, that the drilling does not interrupt the ground water connection to the wetland or percolation of surface water down through the soil column. Specific studies by a hydrologist are necessary to determine whether the ground water connection to the wetland or percolation of surface water down through the soil column is disturbed.
2. 
Low Impact Stormwater Management Facilities. Stormwater management facilities are limited to stormwater dispersion outfalls, bioswales, and other low-impact facilities consistent with the adopted stormwater manual. They may be allowed within the outer 25 percent of the buffer of Category III or IV wetlands only; provided, that:
a. 
No other location is feasible;
b. 
The location of such facilities will not degrade the functions or values of the wetland; and
c. 
Stormwater management facilities are not allowed in buffers of Category I or II wetlands.
D. 
Subdivisions.
1. 
The subdivision and/or short subdivision of land in wetlands and associated buffers are subject to the following:
a. 
Land that is located wholly within a wetland and/or its buffer may not be subdivided; and
b. 
Land that is located partially within a wetland and/or its buffer may be subdivided; provided, that an accessible and contiguous portion of each new lot is:
i. 
Located outside of the wetland and its buffer; and
ii. 
Meets the minimum lot size requirements of SMC § 20.50.020.
E. 
Alterations of Category I Wetlands. Unless specifically exempted under SMC § 20.80.075 and/or allowed under SMC § 20.80.080, subsection B or C of this section, development activities and uses that result in alteration of Category I wetlands and their associated buffers shall be prohibited subject to the reasonable use provisions and special use provisions of SMC § 20.30.333 and 20.30.336, unless otherwise allowed by the exemptions or allowed activities provisions of this chapter, or subject to the provisions of the Shoreline Master Program where the proposed development activity is located within the shoreline jurisdiction.
F. 
Alteration of Category II and III Wetlands. Development activities and uses that result in alteration of Category II and III wetlands and their associated buffers are prohibited, unless the applicant can demonstrate that:
1. 
The basic project proposed cannot reasonably be accomplished on another site or sites in the general region while still successfully avoiding or resulting in less adverse impact on a wetland;
2. 
All on-site alternative designs that would avoid or result in less adverse impact on a wetland or its buffer, such as a reduction to the size, scope, configuration, or density of the project are not feasible; and
3. 
Full compensation for the loss of acreage and functions and values of wetland and buffers due to unavoidable impacts shall be provided in compliance with the mitigation performance standards and requirements of this chapter.
G. 
Alterations of Category IV Wetlands, Except Small Hydrologically Isolated Wetlands. Development activities and uses that result in unavoidable impacts may be permitted in Category IV wetlands and associated buffers in accordance with an approved critical area(s) report and compensatory mitigation plan, and only if the proposed activity is the only reasonable alternative that will accomplish the applicant’s objectives. Full compensation for the loss of acreage and functions and values of wetland and buffers shall be provided in compliance with the mitigation performance standards and requirements of these regulations.
H. 
Small, Hydrologically Isolated Category IV Wetlands. The Director may allow small, hydrologically isolated Category IV wetlands to be exempt from the avoidance sequencing provisions of SMC § 20.80.095 and subsection F of this section and allow alteration of such wetlands; provided, that a submitted critical area report and mitigation plan provides evidence that all of the following conditions are met:
1. 
The wetland is less than 1,000 square feet in area;
2. 
The wetland is a low quality Category IV wetland with a habitat score of less than three points in the adopted rating system;
3. 
The wetland does not contain habitat identified as essential for local populations of priority species identified by the Washington Department of Fish and Wildlife or species of local importance which are regulated as fish and wildlife habitat conservation areas in Chapter 20.80, Subchapter 3;
4. 
The wetland is not associated with riparian areas or buffers;
5. 
The wetland is not part of a wetland mosaic; and
6. 
A mitigation plan to replace lost wetland functions and values is developed, approved, and implemented consistent with SMC § 20.80.435.
(Formerly 20.80.324. Ord. 723 § 1 (Exh. A), 2015; Ord. 1045 § 1 (Exh. A), 2025)
A. 
Requirements for Mitigation. Mitigation is required where impacts cannot be avoided and must be sufficient to achieve no net loss of ecological functions. Mitigation plans shall be submitted as part of the required critical area report, consistent with the requirements of SMC § 20.80.100, this section, and with Wetland Mitigation in Washington State – Part 2: Developing Mitigation Plans (Version 1) (Ecology Publication No. 06-06-011b, March 2006, or as revised). Mitigation requirements may also be determined using the credit/debit tool described in “Calculating Credits and Debits for Compensatory Mitigation in Wetlands of Western Washington: Operational Draft” (Ecology Publication No. 10-06-011, February 2011, or as revised) consistent with subsection E of this section.
B. 
Preference of Mitigation Actions. Methods to achieve compensation for wetland functions and values shall be approached in the following order of preference:
1. 
Restoration. Restoration of wetlands.
2. 
Creation. Creation (establishment) of wetlands on disturbed upland sites, such as those with vegetative cover consisting primarily of nonnative species. This should be attempted only when there is an adequate source of water and it can be shown that the surface and subsurface hydrologic regime is conducive to the wetland community that is anticipated in the design.
3. 
Enhancement. Enhancement of significantly degraded wetlands in combination with restoration or creation. Enhancement includes replacing the impacted area and meeting appropriate ratio requirements.
4. 
Preservation. Preservation of high-quality, at-risk wetlands as compensation is generally acceptable when done in combination with restoration, creation, or enhancement; provided, that a minimum of 1:1 acreage replacement is provided by reestablishment or creation. Preservation of high-quality, at-risk wetlands and habitat may be considered as the sole means of compensation for wetland impacts when the following criteria are met:
a. 
Wetland impacts will not have a significant adverse impact on habitat for listed fish, or other ESA-listed species;
b. 
There is no net loss of habitat functions within the watershed or basin;
c. 
Mitigation ratios for preservation as the sole means of mitigation shall generally start at 20:1. Specific ratios should depend upon the significance of the preservation project and the quality of the wetland resources lost;
d. 
The impact area is small (generally less than one-half acre) and/or impacts are occurring to a low-functioning system (Category III or IV wetland); and
e. 
All preservation sites shall include buffer areas adequate to protect the habitat and its functions from encroachment and degradation.
C. 
Mitigation Performance Standards. The performance standards in this section shall be incorporated into mitigation plans submitted to the City for impacts to wetlands. The following performance standards shall apply to any mitigations proposed within Category I, II, III and IV wetlands and their buffers. Modifications to these performance standards consistent with the guidance in Wetland Mitigation in Washington State – Part 2: Developing Mitigation Plans (Version 1) (Ecology Publication No. 06-06-011b, March 2006, or as revised) may be considered for approval by the Director as alternatives to the following standards:
1. 
Plants indigenous to the region (not introduced or foreign species) shall be used.
2. 
Plant selection shall be consistent with the existing or projected hydrologic regime, including base water levels and stormwater event fluctuations.
3. 
Plants should be commercially available or available from local sources.
4. 
Plant species high in food and cover value for fish and wildlife shall be used.
5. 
Mostly perennial species should be planted.
6. 
Committing significant areas of the site to species that have questionable potential for successful establishment shall be avoided.
7. 
Plant selection, planting densities, and placement of plants shall be determined by a qualified professional.
8. 
The following standards shall apply to wetland design and construction:
a. 
Water depth shall not exceed six and one-half feet (two meters).
b. 
The grade or slope that water flows through the wetland shall not exceed six percent.
c. 
Slopes within the wetland basin and the buffer zone shall not be steeper than 3:1 (horizontal to vertical).
d. 
The wetland (excluding the buffer area) should not contain more than 60 percent open water as measured at the seasonal high water mark.
9. 
Substrate should consist of a minimum of one foot, in depth, of clean (uncontaminated with chemicals or solid/hazardous wastes) inorganic/organic materials.
10. 
Stockpiling soil and construction materials should be confined to upland areas and contract specifications should limit stockpiling of earthen materials to durations in accordance with City clearing and grading standards, unless otherwise approved by the City.
11. 
Planting instructions shall be submitted which describe placement, diversity, and spacing of seeds, tubers, bulbs, rhizomes, sprigs, plugs, and transplanted stock.
12. 
Controlled release fertilizer shall be applied (if required) at the time of planting and afterward only as plant conditions warrant as determined during the monitoring process.
13. 
An irrigation system shall be installed, if necessary, for the initial establishment period.
D. 
Type and Location of Compensatory Mitigation. Unless it is demonstrated that a higher level of ecological functioning would result from an alternative approach, compensatory mitigation for ecological functions shall be either in kind and on site, or in kind and within the same stream reach, sub-basin, or drift cell (if estuarine wetlands are impacted). Compensatory mitigation actions shall be conducted within the same sub-drainage basin and on the site of the alteration, except when all of the following apply:
1. 
There are no reasonable opportunities on site or within the sub-drainage basin (e.g., on-site options would require elimination of high-functioning upland habitat), or opportunities on site or within the subdrainage basin do not have a high likelihood of success based on a determination of the capacity of the site to compensate for the impacts. Considerations should include:
a. 
Anticipated replacement ratios for wetland mitigation;
b. 
Buffer conditions and proposed widths;
c. 
Available water to maintain anticipated hydrogeomorphic classes of wetlands when restored; and
d. 
Proposed flood storage capacity, and potential to mitigate riparian fish and wildlife impacts (such as connectivity);
2. 
Off-site mitigation has a greater likelihood of providing equal or improved wetland functions than the impacted wetland;
3. 
Off-site locations shall be in the same subdrainage basin, unless watershed goals for water quality, flood storage or conveyance, habitat, or other wetland functions have been established by the City and strongly justify location of mitigation at another site; and
4. 
The design for the compensatory mitigation project needs to be appropriate for its location (i.e., position in the landscape). Therefore, compensatory mitigation should not result in the creation, restoration, or enhancement of an atypical wetland. An atypical wetland refers to a compensation wetland (e.g., created or enhanced) that does not match the type of existing wetland that would be found in the geomorphic setting of the site (i.e., the water source(s) and hydroperiod proposed for the mitigation site are not typical for the geomorphic setting). Likewise, it should not provide exaggerated morphology or require a berm or other engineered structures to hold back water.
E. 
Wetland Mitigation Ratios1.
Table 20.80.435(E). Wetland mitigation ratios apply when impacts to wetlands cannot be avoided or are otherwise allowed consistent with the provisions of this chapter.
Category and Type of Wetland2
Creation or Reestablishment (Area – in square feet)
Rehabilitation (Area – in square feet)
Enhancement (Area – in square feet)
Preservation (Area – in square feet)
Category I: Based on total score for functions
4:1
8:1
16:1
20:1
Category I: Mature forested
6:1
12:1
24:1
24:1
Category I: Estuarine
Case-by-case
6:1
Case-by-case
Case-by-case
Category II: Based on total score for functions
3:1
6:1
12:1
20:1
Category III (all)
2:1
4:1
8:1
15:1
Category IV (all)
1.5:1
3:1
6:1
10:1
Notes:
1 Ratios for rehabilitation and enhancement may be reduced when combined with 1:1 replacement through creation or reestablishment. See Table 1a or 1b, Wetland Mitigation in Washington State – Part 1: Agency Policies and Guidance – (Version 1) (Ecology Publication No. 06-06-011a, March 2006, or as revised).
2 Category and rating of wetland as determined consistent with SMC § 20.80.415.
F. 
Buffer Mitigation Ratios. Impacts to buffers shall be mitigated at a 1:1 ratio. Compensatory buffer mitigation shall replace those buffer functions lost from development.
G. 
Additional Requirements For Wetland Mitigation Plan. The mitigation plan must meet the following additional standards:
1. 
Description of the existing wetland and buffer areas proposed to be impacted. Include acreage (or square footage), water regime, vegetation, soils, landscape position, surrounding land uses, and functions. Also describe impacts in terms of acreage by Cowardin classification, hydrogeomorphic classification, and wetland rating, based on wetland ratings (SMC § 20.80.415);
2. 
Description of the compensatory mitigation site, including location and rationale for selection. Include an assessment of existing conditions: acreage (or square footage) of wetlands and uplands, water regime, sources of water, vegetation, soils, landscape position, surrounding land uses, and functions. Estimate future conditions in this location if the compensation actions are not undertaken (i.e., how would this site progress through natural succession);
3. 
A description of the proposed actions for compensation of wetland and upland areas affected by the project. Include overall goals of the proposed mitigation, including a description of the targeted functions, hydrogeomorphic classification, and categories of wetlands;
4. 
A description of standards for success for the mitigation plan. Standards for success shall be established based on the performance standards identified and the functions and values being mitigated based on the guidance in Wetland Mitigation in Washington State – Part 2: Developing Mitigation Plans (Version 1) (Ecology Publication No. 06-06-011b, March 2006, or as revised).
5. 
In addition to the general mitigation plan requirements in SMC § 20.80.100, scaled plan sheets for the compensatory mitigation must contain, at a minimum:
a. 
Surveyed edges of the existing wetland and buffers, proposed areas of wetland and/or buffer impacts, location of proposed wetland and/or buffer compensation actions;
b. 
Existing topography, ground-proofed, at two-foot contour intervals in the zone of the proposed compensation actions if any grading activity is proposed to create the compensation area(s). Also existing cross-sections of on-site wetland areas that are proposed to be impacted and cross-section(s) (estimated one-foot intervals) for the proposed areas of wetland or buffer compensation;
c. 
Surface and subsurface hydrologic conditions, including an analysis of existing and proposed hydrologic regimes for enhanced, created, or restored compensatory mitigation areas. Also, illustrations of how data for existing hydrologic conditions were used to determine the estimates of future hydrologic conditions;
d. 
Conditions expected from the proposed actions on site, including future hydrogeomorphic types, vegetation community types by dominant species (wetland and upland), and future water regimes;
e. 
Required wetland buffers for existing wetlands and proposed compensation areas. Also, identify any zones where buffers are proposed to be reduced or enlarged outside of the standards identified in this chapter.
(Formerly 20.80.350. Ord. 238 Ch. VIII § 5(E), 2000; Ord. 398 § 1, 2006; Ord. 581 § 1 (Exh. 1), 2010; Ord. 723 § 1 (Exh. A), 2015; Ord. 789 § 1 (Exh. A), 2018; Ord. 1045 § 1 (Exh. A), 2025)