265 Critical Aquifer Recharge Areas
A. The purpose of this chapter is to designate and protect critical aquifer recharge areas (CARAs) pursuant to the Growth Management Act (Chapter 36.70A RCW) in order to safeguard the public health, safety, and welfare and to protect groundwater resources. CARAs include: sole source aquifers, Group A wellhead protection areas as identified and defined by the Washington State Department of Health, and areas sensitive to groundwater contamination. These areas contribute to the recharge of aquifers, springs, and/or wells, and are susceptible to contamination through infiltration of pollutants through the soil.
B. This chapter applies to the following activities:
1. Development proposals requiring land use applications.
2. Building permits.
3. Any other use or activity with the potential to harm water quality or water quantity within critical aquifer recharge areas. (Ord. 2533, 2025)
A. CARAs are those land areas that contain hydrogeologic conditions that facilitate aquifer recharge and/or transmission of contaminants to an underlying aquifer. Some may also have recharging effects on streams, lakes, and wetlands that provide critical fish and wildlife habitat. Factors considered in the identification of critical aquifer recharge areas include depth to water table, presence of highly permeable soils (Group A hydrologic soils), presence of flat terrain, and the presence of more permeable surficial geology.
B. CARAs are classified based on the following criteria:
1. Sole source aquifers designated by the U.S. Environmental Protection Agency in accordance with the Safe Drinking Water Act of 1974 (Public Law 93-523).
2. Areas within the 10-year travel zone of Group A wellhead protection areas, determined in accordance with delineation methodologies specified by the Washington Department of Health under authority of Chapter 246-290 WAC.
3. Areas of high, medium, and low sensitivity to groundwater contamination, based on depth to groundwater and in accordance with the Ground-Water System and Ground-Water Quality in Western Snohomish County, Washington (United States Geological Survey, Water Resources Investigations, Report No. 96-4312, 1997).
4. Those areas with a hydrologic soil group rating of “A” according to the most recent NRCS soil survey for the area, as designated and mapped in the Web Soil Survey and as may be periodically amended by NRCS.
C. Only CARAs meeting the criteria of subsections (B)(3) and (B)(4) of this section are identified in Snohomish. Future designations may occur.
D. Mapping resources referenced in this chapter are advisory only and are subject to evaluation by a qualified professional. Final designations shall be based on site conditions and other available data. (Ord. 2533, 2025)
The submittal requirements of this section shall be in addition to the requirements of Chapter 14.255 SMC, specifically the critical areas report requirements of SMC 14.255.070.
A. Site Plan Requirements. All applications subject to this chapter shall be required to submit a site plan of the proposed development. The site plan required pursuant to this chapter may be combined with the land use or building permit application materials, as long as all submittal requirements are met. The site plan shall be drawn to a standard engineering scale and include the following elements:
1. Boundary lines and dimensions of the property.
2. Boundary lines and dimensions of the development site.
3. Contour lines at topographic intervals of a maximum of five feet.
4. Location of all existing improvements on the site, including size, dimensions, type, and use. Improvements include any structures, impervious surfaces, or other previous development activities.
5. All proposed development activities on the site, including location, size, dimensions, type, and use.
6. Location, size, and type of all critical aquifer recharge areas on the subject property.
7. Location of all other regulated critical areas pursuant to this title on the property and within 300 feet of the site.
8. All structural setbacks required pursuant to Chapter 14.210 SMC.
B. When a Hydrogeologic Assessment Is Required. A hydrogeologic assessment is required for any of the following:
1. Any proposal that does not meet the nonendangerment standard in WAC 173-218-080, 173-218-090, or 173-218-100 when proposed within a CARA.
2. Any use or activity proposed within a hydrologic soil group rating of “A” pursuant to SMC 14.265.020(B)(4), or as identified in a soils report prepared by a qualified professional.
3. Any use or activity proposed within a CARA not identified in SMC 14.265.050 and the Department determines there is potential for harm or impairment to water quality within the CARA.
C. Hydrogeologic Assessment Requirements. The hydrogeologic assessment shall be prepared by a qualified professional such as a geologist, hydrogeologist, or engineering geologist, licensed in Washington State, with experience preparing hydrogeologic assessments. The hydrogeologic assessment shall contain the following information:
1. Surface location of all CARAs located on site or immediately adjacent to the site, and the permeability of the unsaturated zone.
2. Groundwater depth, flow direction, and gradient, based on best available information.
3. Location of and data for wells and springs within one-quarter mile of the site.
4. Location of and data for surface waters within one-quarter mile of the site.
5. Historic water quality data for the area that will be affected by the proposed use or activity, compiled for at least the previous five-year period.
6. Narrative describing the effects of the proposed project on the groundwater quality and quantity, including:
a. Predictive evaluation of groundwater withdrawal effects on nearby wells and surface water features.
b. Predictive evaluation of contaminant transport based on potential releases to groundwater.
c. Recharge potential of the site including permeability and transmissivity.
d. If water use is proposed for the development activity, a description of the groundwater source of water to the site or a letter from an approved water purveyor stating the ability to provide water to the site.
7. Best management practices relevant to the proposed activity or use.
8. Monitoring provisions for groundwater quality and quantity.
9. A spill plan identifying equipment and structures that could fail, resulting in an impact to the CARA. Spill plans shall include provisions for regular inspection, repair, and replacement of structures and equipment with the potential to fail, and a remediation plan for if cleanup is necessary.
10. An assessment of how the development activity meets the protection standards of SMC 14.265.040.
11. If impacts to CARAs are identified, identify and provide an analysis of alternatives by which such impacts could be avoided or prevented.
12. Recommendations for implementation and operation of activities, including size limitations, monitoring, reporting and best management practices (BMP).
13. An evaluation of potential nitrate and nitrite impacts on the aquifer, including cumulative impacts of adjacent or surrounding developments and activities, and provide recommendations for monitoring and BMP of nitrate and nitrite generating activities.
14. Any other information necessary to demonstrate compliance with this chapter. (Ord. 2533, 2025)
In addition to the substantive requirements of SMC 14.255.110, the following requirements shall apply to critical aquifer recharge areas:
A. The project proponent shall make all reasonable efforts to avoid and minimize impacts to critical aquifer recharge areas pursuant to the requirements of this section, in the following sequential order of preference:
1. Avoiding impacts altogether by not taking a certain action or parts of an action.
2. Avoiding or minimizing impacts by limiting the degree or magnitude of the action and its implementation, using appropriate technology, or by taking affirmative steps, such as project redesign, relocation, or timing, to avoid or reduce impacts.
3. When avoidance is not possible, mitigation for the impacts to the critical aquifer recharge area.
B. Any activity or use specifically listed in SMC 14.265.050 shall comply with the best management practices and mitigation plan identified in the hydrogeologic assessment, when required.
C. All development activities shall comply with the groundwater quality standards contained in Chapter 173-200 WAC and Chapter 90.48 RCW.
D. Where the Department determines that a use or activity not specifically listed in SMC 14.265.050 has the potential to harm water quality or quantity within CARAs, the applicant shall provide all submittal requirements of SMC 14.265.030 and apply best management practices and all known and available reasonable technology appropriate to protect CARAs.
E. Proposed developments shall not cause contaminants to enter the aquifer or significantly reduce the recharging of the aquifer and shall comply with the water source protection requirements and recommendations of the U.S. Environmental Protection Agency, Washington State Department of Health, Washington State Department of Ecology, and Snohomish County Health Department.
F. Underground facilities for storing hazardous substances shall be designed to prevent releases due to corrosion or structural failure for the operational life of the tank.
G. Above-ground facilities for storing hazardous substances shall be designed to prevent accidental release, shall have a primary containment enclosing or underlying the tank, and shall have a secondary containment built into the tank structure or consisting of an external dike.
H. Abandoned wells shall be decommissioned to comply with Federal and State standards.
I. The uses and activities listed in SMC 14.265.050 shall be conditioned as necessary to protect CARAs in accordance with the applicable State and Federal regulations and to the extent that a City approval is required for said uses. (Ord. 2533, 2025)
A. Level 1 CARAs are those with low sensitivity as described in SMC 14.265.020(B).
B. Level 2 CARAs are those with medium or high sensitivity as described in SMC 14.265.020(B).
C. No sole source aquifers or Group A wellhead protection areas are in Snohomish. If information is obtained that causes the City to designate sole source aquifers or Group A wellhead protection areas, they will be a separate level of CARA with different requirements than those in Table 1.
D. Permitted uses and activities shall be subject to the substantive requirements of SMC 14.265.040.
Table 1. Groundwater-Impacting Uses and Activities
Use/Activity | Level 1 CARAs | Level 2 CARAs | Applicable Statute/Regulation or Guidance |
|---|---|---|---|
Animal feedlots, animal feeding operations/concentrated animal feeding operations | Prohibited | Prohibited | Ch. 173-216 WAC; Ch. 173-220 WAC; 40 CFR Parts 122, 123, and 412 |
Automobile washing facilities | With conditions | With conditions | Ch. 173-216 WAC, Best Management Practices for Vehicle and Equipment Discharges (Washington Dept. of Ecology Pub. No. WQ-R-95-56, or latest edition) |
Chemical treatment, storage and disposal facilities | Prohibited | Prohibited | Ch. 173-303 WAC |
Dangerous waste | Prohibited | Prohibited | Ch. 70.105 RCW; Ch. 173-303 WAC; Snohomish County Board of Health Ordinances |
Dry cleaning using chlorinated solvents | Allowed | Prohibited | |
Junk yards and salvage yards | Prohibited | Prohibited | Ch. 173-304 WAC; Ch. 173-350 WAC; Ch. 173-351 WAC; Best Management Practices for Vehicle and Metal Recyclers (Washington State Dept. of Ecology Pub. No. 94-146, or latest edition) |
Solid waste handling and recycling facilities, landfills, outdoor storage facilities, and outdoor recycling centers, including those for hazardous or dangerous waste, electronic waste, contaminated soil or dredged materials, municipal waste, special waste, wood waste, or demolition waste | Prohibited | Prohibited | |
Storage, processing, or disposal of radioactive substances, except for medical equipment or materials that are used within a medical facility, and medical waste as defined in RCW 70.99.020 that is generated within a medical facility and held for proper disposal | Prohibited | Prohibited | |
Mining of metals and hard rock | With conditions | Prohibited | |
Pesticide, herbicide, and fertilizer storage and use, except when stored according to manufacturer’s label instructions | Prohibited | Prohibited | Ch. 15.54 RCW; Ch. 17.21 RCW; Chs. 16-200 through 16-232 WAC |
Reclaimed water for groundwater recharge | Allowed | Allowed | |
Petroleum processing and recycling facilities | Prohibited | Prohibited | 40 CFR Part 443 (paving and roofing materials); 40 CFR Part 419 (effluent guidelines); Ch. 70A.224 RCW (used oil recycling); Ch. 90.56 RCW (spill prevention) |
Sawmills | With conditions | With conditions | Ch. 173-303 WAC; Ch. 173-304 WAC; Industrial Stormwater General Permit Implementation Manual for Log Yards (Washington Dept. of Ecology Pub. No. 04-10-031, or latest edition) |
Storage tanks, above ground | Allowed | With conditions | WAC 173-303-640 |
Storage tanks, below ground | With conditions | With conditions | Ch. 173-360A WAC; Ch. 90.76 RCW; RCW 43.131.394 |
Surface mining | Prohibited | Prohibited | Ch. 332-18 WAC |
Underground injection control wells (Class II and V only; all others are prohibited) | With conditions1 | Prohibited | WAC 173-218-040 |
Wastewater application to land surface | With conditions | With conditions | |
Wood treatment facilities occurring over permeable surfaces, natural or manmade | With conditions | Prohibited | |
Wrecking yards | Prohibited | Prohibited |
1Class II UIC wells are subject to SMC 14.265.060
(Ord. 2533, 2025)
A. Underground injection control wells shall be conditioned as necessary to protect CARAs in accordance with the applicable State and Federal regulations and recommendations from an approved hydrogeologic report required pursuant to SMC 14.265.030.
B. Water reuse projects for reclaimed water and stormwater are regulated in accordance with the adopted water, sewer, or stormwater comprehensive plans that have been approved by the Departments of Ecology and Health. Where allowed, underground injection control wells shall be subject to City review and approval and shall comply with the requirements of Chapters 173-200 and 173-218 WAC and the Snohomish Municipal Code. For all proposals that include infiltration or injection of stormwater, unless waived by the City and the local water purveyor, a hydrogeologic assessment shall be submitted that includes an analysis to assess the risks to the specific aquifer and viability of the proposed infiltration and/or UIC. The report shall meet the requirements described in SMC 14.265.030 and Chapter 173-218 WAC.
C. Underground injection control wells designed in conjunction with stormwater handling facilities shall conform to the City’s adopted stormwater manual. For all proposals that include infiltration or injection of stormwater, unless waived by the City and the local water purveyor, a hydrogeologic assessment shall be submitted that includes an analysis to assess the risks to the specific aquifer and viability of the proposed infiltration and/or UIC. The report shall meet the requirements described in SMC 14.265.030 and Chapter 173-218 WAC. (Ord. 2533, 2025)
In addition to the developments listed in SMC 14.255.050, the following developments shall be exempt from this chapter:
A. Construction of structures, improvements, and additions of less than 2,000 square feet of total site impervious surface area, which do not increase the risk to the critical area from hazardous substances.
B. Development of parks, recreation facilities, or conservation areas that do not increase the risk to the critical area from hazardous substances. (Ord. 2533, 2025)
Protection of critical aquifer recharge areas located within shorelines of the State, as defined in Chapter 90.58 RCW, shall be accomplished through compliance with the provisions of this chapter. Nothing in this section shall be construed to be inconsistent with RCW 36.70A.480. (Ord. 2533, 2025)
The Director shall have the authority to adopt administrative rules to implement the provisions of this chapter. Rulemaking authority shall include, but is not limited to, the adoption of best management practices for the protection of critical aquifer recharge areas. (Ord. 2533, 2025)
265 Critical Aquifer Recharge Areas
A. The purpose of this chapter is to designate and protect critical aquifer recharge areas (CARAs) pursuant to the Growth Management Act (Chapter 36.70A RCW) in order to safeguard the public health, safety, and welfare and to protect groundwater resources. CARAs include: sole source aquifers, Group A wellhead protection areas as identified and defined by the Washington State Department of Health, and areas sensitive to groundwater contamination. These areas contribute to the recharge of aquifers, springs, and/or wells, and are susceptible to contamination through infiltration of pollutants through the soil.
B. This chapter applies to the following activities:
1. Development proposals requiring land use applications.
2. Building permits.
3. Any other use or activity with the potential to harm water quality or water quantity within critical aquifer recharge areas. (Ord. 2533, 2025)
A. CARAs are those land areas that contain hydrogeologic conditions that facilitate aquifer recharge and/or transmission of contaminants to an underlying aquifer. Some may also have recharging effects on streams, lakes, and wetlands that provide critical fish and wildlife habitat. Factors considered in the identification of critical aquifer recharge areas include depth to water table, presence of highly permeable soils (Group A hydrologic soils), presence of flat terrain, and the presence of more permeable surficial geology.
B. CARAs are classified based on the following criteria:
1. Sole source aquifers designated by the U.S. Environmental Protection Agency in accordance with the Safe Drinking Water Act of 1974 (Public Law 93-523).
2. Areas within the 10-year travel zone of Group A wellhead protection areas, determined in accordance with delineation methodologies specified by the Washington Department of Health under authority of Chapter 246-290 WAC.
3. Areas of high, medium, and low sensitivity to groundwater contamination, based on depth to groundwater and in accordance with the Ground-Water System and Ground-Water Quality in Western Snohomish County, Washington (United States Geological Survey, Water Resources Investigations, Report No. 96-4312, 1997).
4. Those areas with a hydrologic soil group rating of “A” according to the most recent NRCS soil survey for the area, as designated and mapped in the Web Soil Survey and as may be periodically amended by NRCS.
C. Only CARAs meeting the criteria of subsections (B)(3) and (B)(4) of this section are identified in Snohomish. Future designations may occur.
D. Mapping resources referenced in this chapter are advisory only and are subject to evaluation by a qualified professional. Final designations shall be based on site conditions and other available data. (Ord. 2533, 2025)
The submittal requirements of this section shall be in addition to the requirements of Chapter 14.255 SMC, specifically the critical areas report requirements of SMC 14.255.070.
A. Site Plan Requirements. All applications subject to this chapter shall be required to submit a site plan of the proposed development. The site plan required pursuant to this chapter may be combined with the land use or building permit application materials, as long as all submittal requirements are met. The site plan shall be drawn to a standard engineering scale and include the following elements:
1. Boundary lines and dimensions of the property.
2. Boundary lines and dimensions of the development site.
3. Contour lines at topographic intervals of a maximum of five feet.
4. Location of all existing improvements on the site, including size, dimensions, type, and use. Improvements include any structures, impervious surfaces, or other previous development activities.
5. All proposed development activities on the site, including location, size, dimensions, type, and use.
6. Location, size, and type of all critical aquifer recharge areas on the subject property.
7. Location of all other regulated critical areas pursuant to this title on the property and within 300 feet of the site.
8. All structural setbacks required pursuant to Chapter 14.210 SMC.
B. When a Hydrogeologic Assessment Is Required. A hydrogeologic assessment is required for any of the following:
1. Any proposal that does not meet the nonendangerment standard in WAC 173-218-080, 173-218-090, or 173-218-100 when proposed within a CARA.
2. Any use or activity proposed within a hydrologic soil group rating of “A” pursuant to SMC 14.265.020(B)(4), or as identified in a soils report prepared by a qualified professional.
3. Any use or activity proposed within a CARA not identified in SMC 14.265.050 and the Department determines there is potential for harm or impairment to water quality within the CARA.
C. Hydrogeologic Assessment Requirements. The hydrogeologic assessment shall be prepared by a qualified professional such as a geologist, hydrogeologist, or engineering geologist, licensed in Washington State, with experience preparing hydrogeologic assessments. The hydrogeologic assessment shall contain the following information:
1. Surface location of all CARAs located on site or immediately adjacent to the site, and the permeability of the unsaturated zone.
2. Groundwater depth, flow direction, and gradient, based on best available information.
3. Location of and data for wells and springs within one-quarter mile of the site.
4. Location of and data for surface waters within one-quarter mile of the site.
5. Historic water quality data for the area that will be affected by the proposed use or activity, compiled for at least the previous five-year period.
6. Narrative describing the effects of the proposed project on the groundwater quality and quantity, including:
a. Predictive evaluation of groundwater withdrawal effects on nearby wells and surface water features.
b. Predictive evaluation of contaminant transport based on potential releases to groundwater.
c. Recharge potential of the site including permeability and transmissivity.
d. If water use is proposed for the development activity, a description of the groundwater source of water to the site or a letter from an approved water purveyor stating the ability to provide water to the site.
7. Best management practices relevant to the proposed activity or use.
8. Monitoring provisions for groundwater quality and quantity.
9. A spill plan identifying equipment and structures that could fail, resulting in an impact to the CARA. Spill plans shall include provisions for regular inspection, repair, and replacement of structures and equipment with the potential to fail, and a remediation plan for if cleanup is necessary.
10. An assessment of how the development activity meets the protection standards of SMC 14.265.040.
11. If impacts to CARAs are identified, identify and provide an analysis of alternatives by which such impacts could be avoided or prevented.
12. Recommendations for implementation and operation of activities, including size limitations, monitoring, reporting and best management practices (BMP).
13. An evaluation of potential nitrate and nitrite impacts on the aquifer, including cumulative impacts of adjacent or surrounding developments and activities, and provide recommendations for monitoring and BMP of nitrate and nitrite generating activities.
14. Any other information necessary to demonstrate compliance with this chapter. (Ord. 2533, 2025)
In addition to the substantive requirements of SMC 14.255.110, the following requirements shall apply to critical aquifer recharge areas:
A. The project proponent shall make all reasonable efforts to avoid and minimize impacts to critical aquifer recharge areas pursuant to the requirements of this section, in the following sequential order of preference:
1. Avoiding impacts altogether by not taking a certain action or parts of an action.
2. Avoiding or minimizing impacts by limiting the degree or magnitude of the action and its implementation, using appropriate technology, or by taking affirmative steps, such as project redesign, relocation, or timing, to avoid or reduce impacts.
3. When avoidance is not possible, mitigation for the impacts to the critical aquifer recharge area.
B. Any activity or use specifically listed in SMC 14.265.050 shall comply with the best management practices and mitigation plan identified in the hydrogeologic assessment, when required.
C. All development activities shall comply with the groundwater quality standards contained in Chapter 173-200 WAC and Chapter 90.48 RCW.
D. Where the Department determines that a use or activity not specifically listed in SMC 14.265.050 has the potential to harm water quality or quantity within CARAs, the applicant shall provide all submittal requirements of SMC 14.265.030 and apply best management practices and all known and available reasonable technology appropriate to protect CARAs.
E. Proposed developments shall not cause contaminants to enter the aquifer or significantly reduce the recharging of the aquifer and shall comply with the water source protection requirements and recommendations of the U.S. Environmental Protection Agency, Washington State Department of Health, Washington State Department of Ecology, and Snohomish County Health Department.
F. Underground facilities for storing hazardous substances shall be designed to prevent releases due to corrosion or structural failure for the operational life of the tank.
G. Above-ground facilities for storing hazardous substances shall be designed to prevent accidental release, shall have a primary containment enclosing or underlying the tank, and shall have a secondary containment built into the tank structure or consisting of an external dike.
H. Abandoned wells shall be decommissioned to comply with Federal and State standards.
I. The uses and activities listed in SMC 14.265.050 shall be conditioned as necessary to protect CARAs in accordance with the applicable State and Federal regulations and to the extent that a City approval is required for said uses. (Ord. 2533, 2025)
A. Level 1 CARAs are those with low sensitivity as described in SMC 14.265.020(B).
B. Level 2 CARAs are those with medium or high sensitivity as described in SMC 14.265.020(B).
C. No sole source aquifers or Group A wellhead protection areas are in Snohomish. If information is obtained that causes the City to designate sole source aquifers or Group A wellhead protection areas, they will be a separate level of CARA with different requirements than those in Table 1.
D. Permitted uses and activities shall be subject to the substantive requirements of SMC 14.265.040.
Table 1. Groundwater-Impacting Uses and Activities
Use/Activity | Level 1 CARAs | Level 2 CARAs | Applicable Statute/Regulation or Guidance |
|---|---|---|---|
Animal feedlots, animal feeding operations/concentrated animal feeding operations | Prohibited | Prohibited | Ch. 173-216 WAC; Ch. 173-220 WAC; 40 CFR Parts 122, 123, and 412 |
Automobile washing facilities | With conditions | With conditions | Ch. 173-216 WAC, Best Management Practices for Vehicle and Equipment Discharges (Washington Dept. of Ecology Pub. No. WQ-R-95-56, or latest edition) |
Chemical treatment, storage and disposal facilities | Prohibited | Prohibited | Ch. 173-303 WAC |
Dangerous waste | Prohibited | Prohibited | Ch. 70.105 RCW; Ch. 173-303 WAC; Snohomish County Board of Health Ordinances |
Dry cleaning using chlorinated solvents | Allowed | Prohibited | |
Junk yards and salvage yards | Prohibited | Prohibited | Ch. 173-304 WAC; Ch. 173-350 WAC; Ch. 173-351 WAC; Best Management Practices for Vehicle and Metal Recyclers (Washington State Dept. of Ecology Pub. No. 94-146, or latest edition) |
Solid waste handling and recycling facilities, landfills, outdoor storage facilities, and outdoor recycling centers, including those for hazardous or dangerous waste, electronic waste, contaminated soil or dredged materials, municipal waste, special waste, wood waste, or demolition waste | Prohibited | Prohibited | |
Storage, processing, or disposal of radioactive substances, except for medical equipment or materials that are used within a medical facility, and medical waste as defined in RCW 70.99.020 that is generated within a medical facility and held for proper disposal | Prohibited | Prohibited | |
Mining of metals and hard rock | With conditions | Prohibited | |
Pesticide, herbicide, and fertilizer storage and use, except when stored according to manufacturer’s label instructions | Prohibited | Prohibited | Ch. 15.54 RCW; Ch. 17.21 RCW; Chs. 16-200 through 16-232 WAC |
Reclaimed water for groundwater recharge | Allowed | Allowed | |
Petroleum processing and recycling facilities | Prohibited | Prohibited | 40 CFR Part 443 (paving and roofing materials); 40 CFR Part 419 (effluent guidelines); Ch. 70A.224 RCW (used oil recycling); Ch. 90.56 RCW (spill prevention) |
Sawmills | With conditions | With conditions | Ch. 173-303 WAC; Ch. 173-304 WAC; Industrial Stormwater General Permit Implementation Manual for Log Yards (Washington Dept. of Ecology Pub. No. 04-10-031, or latest edition) |
Storage tanks, above ground | Allowed | With conditions | WAC 173-303-640 |
Storage tanks, below ground | With conditions | With conditions | Ch. 173-360A WAC; Ch. 90.76 RCW; RCW 43.131.394 |
Surface mining | Prohibited | Prohibited | Ch. 332-18 WAC |
Underground injection control wells (Class II and V only; all others are prohibited) | With conditions1 | Prohibited | WAC 173-218-040 |
Wastewater application to land surface | With conditions | With conditions | |
Wood treatment facilities occurring over permeable surfaces, natural or manmade | With conditions | Prohibited | |
Wrecking yards | Prohibited | Prohibited |
1Class II UIC wells are subject to SMC 14.265.060
(Ord. 2533, 2025)
A. Underground injection control wells shall be conditioned as necessary to protect CARAs in accordance with the applicable State and Federal regulations and recommendations from an approved hydrogeologic report required pursuant to SMC 14.265.030.
B. Water reuse projects for reclaimed water and stormwater are regulated in accordance with the adopted water, sewer, or stormwater comprehensive plans that have been approved by the Departments of Ecology and Health. Where allowed, underground injection control wells shall be subject to City review and approval and shall comply with the requirements of Chapters 173-200 and 173-218 WAC and the Snohomish Municipal Code. For all proposals that include infiltration or injection of stormwater, unless waived by the City and the local water purveyor, a hydrogeologic assessment shall be submitted that includes an analysis to assess the risks to the specific aquifer and viability of the proposed infiltration and/or UIC. The report shall meet the requirements described in SMC 14.265.030 and Chapter 173-218 WAC.
C. Underground injection control wells designed in conjunction with stormwater handling facilities shall conform to the City’s adopted stormwater manual. For all proposals that include infiltration or injection of stormwater, unless waived by the City and the local water purveyor, a hydrogeologic assessment shall be submitted that includes an analysis to assess the risks to the specific aquifer and viability of the proposed infiltration and/or UIC. The report shall meet the requirements described in SMC 14.265.030 and Chapter 173-218 WAC. (Ord. 2533, 2025)
In addition to the developments listed in SMC 14.255.050, the following developments shall be exempt from this chapter:
A. Construction of structures, improvements, and additions of less than 2,000 square feet of total site impervious surface area, which do not increase the risk to the critical area from hazardous substances.
B. Development of parks, recreation facilities, or conservation areas that do not increase the risk to the critical area from hazardous substances. (Ord. 2533, 2025)
Protection of critical aquifer recharge areas located within shorelines of the State, as defined in Chapter 90.58 RCW, shall be accomplished through compliance with the provisions of this chapter. Nothing in this section shall be construed to be inconsistent with RCW 36.70A.480. (Ord. 2533, 2025)
The Director shall have the authority to adopt administrative rules to implement the provisions of this chapter. Rulemaking authority shall include, but is not limited to, the adoption of best management practices for the protection of critical aquifer recharge areas. (Ord. 2533, 2025)