The purposes of this article are to:
(1) 
Regulate land use to avoid adverse effects on wetlands and maintain no net loss of wetland functions and values throughout Lewis County.
(2) 
Protect the beneficial functions performed by wetlands, which include, but are not limited to: providing food, breeding, nesting and/or rearing habitat for fish and wildlife; providing habitat for endangered, threatened and sensitive species; recharging and discharging ground water; contributing to stream flow during low flow periods; stabilizing stream banks and shorelines; storing storm and floodwaters to reduce flooding and erosion; and improving water quality through biofiltration, adsorption, and the retention and transformation of sediments, nutrients, and toxicants.
(3) 
Establish review procedures for development proposals, which are consistent with best available science as defined by WAC 365-195-900 through 365-195-925, in and adjacent to wetlands.
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)
(1) 
Administration of this article shall occur in accordance with Article I of this chapter.
(2) 
When a project is subject to these requirements and does not fall within the activities listed in LCC § 17.38.060, the reports in Table 17.38-1 shall be required to review the projects. Wetland assessment reports are required when wetland conditions are known or likely to be present based on visual observations or publicly available data.
Table 17.38-1
Report
When Required
Standards
Wetland Assessment Report
Within an area of mapped hydric soil or within 300 feet of a mapped wetland
LCC § 17.38.320
Wetland Mitigation Report
When an impact is proposed to a wetland or wetland buffer (per LCC § 17.38.270), including proposed buffer modification (per LCC § 17.38.280 or § 17.38.290)
LCC § 17.38.330
(3) 
State and federal permits may be required even when a wetland is exempt from county requirements.
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)
(1) 
Wetlands shall be identified and delineated in accordance with the requirements of RCW 36.70A.030(48) and WAC 173-22-035 using the 1987 U.S. Army Corps of Engineers Wetland Delineation Manual and the 2010 Western Mountains, Valleys, and Coast Regional Supplement, or as amended. Wetland delineations are valid for five years; after such date the county shall determine whether a revision or additional assessment is necessary. Wetland delineations will be documented on a ground-verified map using either professional surveying methods or an equivalent professional method using GPS with submeter accuracy.
(2) 
The administrator may accept a written determination by the U.S. Army Corps of Engineers and the Washington State Department of Ecology (Ecology) that a specific parcel is not a wetland, as long as the determination is consistent with current local, state or federal law.
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)
(1) 
Rating. Wetlands shall be identified and rated according to the Washington 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 amended, which contains the definitions and methods for determining whether the criteria below are met.
(a) 
Category I. Category I wetlands are: (i) wetlands of high conservation value that are identified by scientists of the Washington Natural Heritage Program/DNR; (ii) bogs; (iii) mature and old-growth forested wetlands larger than one acre; or (iv) wetlands that perform many functions well (scoring 23 points or more). The wetlands: (i) represent unique or rare wetland types; (ii) are more sensitive to disturbance than most wetlands; (iii) are relatively undisturbed and contain ecological attributes that are impossible to replace within a human lifetime; or (iv) provide a high level of functions.
(b) 
Category II. Category II wetlands are wetlands with a moderately high level of functions (scoring between 20 and 22 points).
(c) 
Category III. Category III wetlands are: (i) wetlands with a moderate level of functions (scoring between 16 and 19 points); and (ii) can often be adequately replaced with a well-planned mitigation project. Wetlands scoring between 16 and 19 points generally have been disturbed in some way and are often less diverse or more isolated from other natural resources in the landscape than Category II wetlands.
(d) 
Category IV. Category IV wetlands have the lowest levels of functions (scoring fewer than 16 points) and are often heavily disturbed. These wetlands are often able to be replaced, or in some cases improved. However, experience has shown that replacement cannot be guaranteed in any specific case. The wetlands may provide some important functions, and should be protected to some degree.
(2) 
Illegal Modifications. Illegal modifications to a wetland made by the applicant or with the applicant's knowledge shall not change a wetland's rating.
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)
Projects proposed in or adjacent to wetlands are required to utilize the mitigation sequence to avoid and minimize impacts, and provide compensatory mitigation for any unavoidable impacts. Mitigation sequencing is detailed in LCC § 17.38.080(2).
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)
(1) 
The following wetlands may be exempt from the requirement to avoid impacts to wetlands (as defined in the mitigation sequence in LCC § 17.38.080(2)(a)). The wetlands may be filled if the remaining actions in the mitigation sequence (LCC § 17.38.080(2)(b) through (2)(f)) ensure that no net loss of wetland functions and values will occur from the activity and other agency permits are obtained consistent with LCC § 17.38.020.
(a) 
All isolated Category IV wetlands less than 4,000 square feet that:
(i) 
Are not associated with riparian areas or their buffers.
(ii) 
Are not associated with shorelines of the state or their associated buffers.
(iii) 
Are not part of a wetland mosaic.
(iv) 
Do not score six or more points for habitat function based on the wetland rating per LCC § 17.38.230(1).
(v) 
Do not contain a federally listed species or their critical habitat, priority habitat or species identified by the Washington Department of Fish and Wildlife, or species of local importance identified in LCC § 17.38.420.
(b) 
Wetlands less than 1,000 square feet that meet the above criteria and do not contain federally listed species or their critical habitat are exempt from the buffer provisions contained in this chapter.
(2) 
To ensure that no reduction of wetland values and functions occurs as a result of this section, a wetland assessment report and mitigation plan meeting the requirements in LCC § 17.38.320 and § 17.38.330 must be submitted.
(Ord. 1284 § 4, 2018; Ord. 1327 § 2, 2021; Ord. 1370 (Exh. B), 2025)
The use intensities in Table 17.38-2 shall be used in connection with the standards to classify wetlands in LCC § 17.38.230 to determine required buffers.
Table 17.38-2
Level of Impact from Proposed Change in Land Use
Common Types of Land Use
High
Commercial
Urban
Industrial
Institutional
Retail sales
Residential or home-based business (density greater than 1 unit/acre)1
Conversion to high-intensity agriculture (dairies, nurseries, greenhouses, growing and harvesting crops requiring annual tilling and raising and maintaining animals, etc.)
High-intensity recreation (golf courses, ball fields, etc.)
Hobby farms
Moderate
Residential or home-based business (density between 1 unit per acre and 1 unit per 4.99 acres)1
Moderate-intensity open space (parks with biking, jogging, etc.)
Conversion to moderate-intensity agriculture (orchards, hay fields, etc.)
Paved trails
Building of logging roads
Utility corridor or right-of-way shared by several utilities and including access/maintenance road
Low
Forestry (cutting of trees only)
Low-intensity open space (hiking, bird-watching, preservation of natural resources, etc.)
Unpaved trails
Utility corridor without a maintenance road and little or no vegetation management
Residential or home-based business (density at or lower than 1 unit per 5 acres)1
1 Measured as density averaged over a development site, not necessarily an individual lot size. In the context of this table, an accessory dwelling unit (ADU) constitutes one unit.
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)
(1) 
Utilizing the impact levels specified above, the buffer widths in Table 17.38-3 have been established in accordance with best available science.
(a) 
Buffers.
Table 17.38-3
Category I Wetlands
Impact Level1
Low
Moderate
High
High level of function for habitat (score for habitat 9 points)
150
225
260/3002
Wetlands of high conservation value
125
190
250
Bogs
125
190
250
Forested
Buffer width to be based on score for habitat functions or water quality functions
Moderate level of function for habitat (score for habitat 6 - 7 points)
75
110
150
High level of function for water quality improvement (8 - 9 points) and low for habitat (5 points or less)
50
75
100
Not meeting any of the above characteristics
50
75
100
Category II Wetlands
Low
Moderate
High
High level of function for habitat (score for habitat 8 - 9 points)
150
225
260/3002
Moderate level of function for habitat (score for habitat 6 - 7 points)
75
110
150
High level of function for water quality improvement and low for habitat (score for water quality 8 - 9 points; 5 habitat points or less)
50
75
100
Not meeting above characteristics
50
75
100
Category III Wetlands
Low
Moderate
High
Moderate level of function for habitat (score for habitat 6 - 7 points)*
*If wetland scores 8 - 9 habitat points, use Category II buffers for high level of function for habitat.
75
110
150
Low level of function for habitat (score for habitat 5 points or less)
40
60
80
Category IV Wetlands
Low
Moderate
High
Score for all 3 basic functions is less than 16 points
25
40
50
1 Buffer widths in the table assume it is vegetated with a native plant community appropriate for the ecoregion or with one that performs similar functions.
2 Buffers are 260 feet for eight habitat points and 300 feet for nine habitat points.
(b) 
Other Protections. Uses with proximity impacts, such as noise, light, glare or other characteristics that may affect wetland ecological functions, may be required to provide greater buffers than indicated, or to provide site design and layout, or operational measures, that reduce project impacts to levels appropriate to the designated buffer. Elements to reduce potential buffer impacts include screening the buffer edge with dense plantings or fencing, and other items.
(Ord. 1284 § 4, 2018; Ord. 1327 § 3, 2021; Ord. 1370 (Exh. B), 2025)
Buffer widths may be reduced in the following instances without the submittal of a mitigation plan:
(1) 
Reduction in Buffer Width by Reducing the Intensity of Land Use Impacts. The widths of buffers recommended for proposed land uses with high-intensity impacts can be reduced to the buffers recommended for moderate-intensity impacts under the following conditions:
(a) 
For wetlands that score moderate or high for habitat (six points or more for the habitat functions), the width of the buffer can be reduced if both of the following criteria are met:
(i) 
A relatively undisturbed, vegetated corridor at least 100 feet wide is protected between the wetland and any other priority habitats as defined by the Washington State Department of Fish and Wildlife. The latest definitions of priority habitats and their locations are available on the WDFW website at: http://wdfw.wa.gov/hab/phshabs.htm. The corridor must be protected for the entire distance between the wetland and the priority habitat by some type of legal protection such as a conservation easement.
(ii) 
Measures to minimize the impacts of different land uses on wetlands, such as the examples summarized in Table 17.38-4, are applied; provided, that the administrator may approve of alternative impact reduction measures that are demonstrated to have equivalent effectiveness in reducing impacts on wetland functions.
(b) 
For wetlands that score five or less points for habitat, the buffer width can be reduced to that required for moderate land-use impacts by applying the measures to minimize the impacts of the proposed land uses (see examples in Table 17.38-4).
Table 17.38-4
Impact Type
Activities and Uses that Cause Disturbances
Examples of Measures to Reduce Impacts
Stormwater runoff
• Parking lots
• Roads
• Manufacturing
• Residential areas
• Commercial
• Landscaping
• Provide stormwater detention and treatment meeting the latest adopted Stormwater Management Manual for all impervious surfaces that drain to the wetland
• Provide infiltration, except where soil conditions preclude
• Prevent flow from lawns that directly enters the buffer through swales or other interception
Lights
• Residential
• Warehouses
• Manufacturing
• Parking lots
• Direct lights away from wetland
Noise
• Residential
• Commercial
• Warehouse
• Manufacturing
• Locate activity that generates noise away from wetland
• Place loading areas, garbage pickup and other pickup/delivery functions on the building side furthest removed from the wetland
Toxic runoff
• Parking lots
• Roads
• Manufacturing
• Residential areas
• Application of agricultural pesticides
• Landscaping
• Pesticides
• Herbicides
• Fertilizer
• Route all new, untreated runoff away from wetland while ensuring wetland is not dewatered
• Establish covenants limiting use of pesticides within 150 feet of wetland
• Require development and implementation of integrated pest management plan to reduce chemical use
Pets and human disturbance
• Residential areas
• Fence buffer area with privacy fencing
• Plant dense native vegetation to delineate buffer edge
Lack of native vegetation in buffer
• Buffer will not provide functions
• Ensure minimum vegetation relative density of 20 or plant to 300 stems per acre
Change in water regime
• Impermeable surfaces
• Lawns
• Tilling
• Infiltrate or treat, detain, and disperse into buffer new runoff from impervious surfaces and new lawns
Dust
• Tilled fields
• Use best management practices to control dust
(2) 
Functionally Disconnected Buffer Area Where Existing Roads or Structures Lie Within the Buffer.
(a) 
The administrator may exclude a buffer area that is functionally disconnected by a legally established substantial improvement such as a road, railroad, or structure that serves to eliminate or greatly reduce the impact of a proposed activity upon a wetland buffer.
(b) 
Where such a substantial improvement exists, the buffer may be reduced to the critical area edge of the existing substantial improvement.
(c) 
If a project has the potential to impact the functions of a wetland or its buffer, even though such a substantial improvement exists, the administrator shall require the applicant to submit a wetland assessment report to ensure that no net loss of ecological values and functions occurs. A mitigation plan may be required.
(d) 
As used within this section only, substantial improvements shall include developed public infrastructure such as roads and railroads, and private improvements such as homes, commercial structures, and paved parking lots. Substantial improvements shall not include paved trails, sidewalks, private driveways, resident parking areas, and accessory buildings that do not require a building permit.
(e) 
Where questions exist regarding whether a development functionally disconnects the buffer, or the extent of that impact, the administrator may require a critical area report to analyze and document the buffer functionality.
(3) 
Legally Established Buffers.
(a) 
Where a buffer has been previously established on a legally created parcel or tract that was legally established according to the regulations in place at the time of establishment and is permanently recorded on title or placed within a separate tract, and the parcels that are included on the plat at the time of recording of the subject parcel or tract, then the buffer shall remain as previously established, provided:
(i) 
It is equal to or greater than 50 percent of the required standard buffer distance for the applicable wetland category; and
(ii) 
Impact minimization measures are applied. See Table 17.38-4 for more information.
(Ord. 1284 § 4, 2018; Ord. 1327 § 4, 2021; Ord. 1370 (Exh. B), 2025)
The administrator may allow modification of the standard wetland buffer width in accordance with the best available science on a case-by-case basis by averaging buffer widths. Applicants cannot use buffer averaging and buffer reduction allowances together.
(1) 
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 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 habitat area or more sensitive portion of the wetland and decreased adjacent to the lower functioning or less sensitive portion.
(2) 
Averaging to allow the reasonable use of a parcel may be permitted when all of the following are met:
(a) 
Buffer averaging is necessary to accommodate existing conditions, such as topography, existing roads, public facilities, or similar features that prevent reasonable development in compliance with standard buffers.
(b) 
There are no feasible site design alternatives that could be accomplished without buffer averaging.
(c) 
Averaging will not impair or reduce the habitat, water quality purification and enhancement, stormwater detention, ground water recharge, shoreline protection, erosion protection, and other functions of the wetland and buffer as demonstrated by a report from a qualified wetland professional.
(3) 
Buffer averaging must meet the following criteria:
(a) 
The total area of the buffer on the subject property is not less than the buffer that would be required if averaging was not allowed, and all increases to the buffer dimensions from averaging are generally parallel to the wetland boundary (to avoid creating buffer panhandles); and
(b) 
No part of the width of the buffer is less than 75 percent of the required width; and
(c) 
Enhancement of reduced or average buffer areas may be required to ensure that no net loss of buffer functions and values will occur as a result of the decreased buffer width. Standards included in Table 17.38-4 may be utilized as a means to help preserve habitat function and value.
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)
(1) 
Wetland Mitigation. The alteration of wetlands shall require the creation, restoration, or enhancement of wetlands to provide equivalent or greater functions and values. In order to address the risk and time lag associated with the creation, restoration, or enhancement of wetlands, the following acreage replacement ratios shall be required, except as provided for in subsection (5) of this section. The listed ratios assume that the replacement wetland will be similar in type and structure to the wetland being altered.
Table 17.38-5
Wetland Mitigation Type and Replacement Ratio*
Wetland Category
Creation or Reestablishment
Rehabilitation
Enhancement or Preservation
Category I: Bog, Natural Heritage Site
Not considered possible
Case by case
Case by case
Category I: Mature Forested
6:1
12:1
24:1
Category I: Based on Functions
4:1
8:1
16:1
Category II
3:1
6:1
12:1
Category III
2:1
4:1
8:1
Category IV
1.5:1
3:1
6:1
*Ratio is the replacement area: impact area.
(2) 
Buffer Mitigation. Impacts to wetland buffers shall be mitigated at a minimum 1:1 ratio. Although buffer widths determined pursuant to LCC § 17.38.270 assume native vegetation cover, compensatory buffer mitigation shall replace the buffer functions lost from development.
(3) 
Increasing or Decreasing Replacement Ratios. Mitigation ratios may be increased or decreased based on the following circumstances:
(a) 
The degree of uncertainty as to the probable success of the proposed mitigation;
(b) 
The period of time between the alteration of the wetland or buffer and the replacement of lost functions and values; and
(c) 
The projected gains or losses in functions and values; provided, that the findings of special studies coordinated with agencies with expertise demonstrate that no loss of wetland functions or values will result from a reduced ratio.
(4) 
Replacement of Functions and Values. In lieu of mitigation based on land area, as provided above, an applicant may alternatively propose mitigation based on the credit/debit methodology established by the Washington State Department of Ecology. Such a proposal shall follow the process and provide the details established in Calculating Credits and Debits for Compensatory Mitigation in Wetlands of Western Washington dated March 2012 and note:
(a) 
The degree of uncertainty as to the probable success of the proposed mitigation;
(b) 
The period of time between the alteration of the wetland or buffer and the replacement of lost functions and values;
(c) 
Projected gains or losses in functions and values; provided, that findings of special studies, coordinated with agencies with expertise, demonstrate that no loss of wetland functions or values will result from the proposal.
(5) 
Standards for Mitigation. Mitigation projects shall meet the following requirements:
(a) 
Location. Compensatory mitigation actions shall generally be conducted within the same subdrainage basin and on the site of the alteration, except when the applicant can demonstrate that off-site mitigation is ecologically preferable.
(b) 
Allowed Mitigation Approaches. The following wetland mitigation approaches are allowed:
(i) 
Wetland Mitigation Banks. Credits from a certified wetland mitigation bank may be used to compensate for wetland and buffer impacts that are located within the service area specified in the mitigation bank instrument. Standards for the creation of a wetland mitigation bank are available in Chapter 173-700 WAC.
(ii) 
Permittee-Responsible Mitigation. Permittee-responsible mitigation may occur at the site of the permitted impacts or at an off-site location within the same watershed. With permittee-responsible mitigation, the permittee performs the mitigation after the permit is issued and is ultimately responsible for the implementation, monitoring and success of the mitigation.
(iii) 
Additional mitigation approaches (such as in-lieu fee mitigation) may also be approved, so long as: the administrator determines that the approach ensures that no net loss of wetland functions and values will occur; an appropriate organizational entity will implement the mitigation; and a monitoring plan will be provided to show the success of the mitigation. Approved in-lieu-fee program credits may be used for wetland and buffer impacts that are situated within a service area specified within an approved in-lieu-fee instrument. Project applicants should contact the U.S. Army Corps of Engineers, Seattle District, for more information.
(iv) 
The director may approve innovative mitigation projects that are based on the best available science.
(Ord. 1284 § 4, 2018; Ord. 1370 (Exh. B), 2025)