The applicant shall be required to submit reports as appropriate for the applicable critical areas found in the critical areas determination. The report shall be prepared in accordance with the minimum requirements listed below and within the additional requirements listed for each applicable critical area found in this chapter. Critical areas reports for two or more types of critical areas shall meet the report requirements for each relevant type of critical area.
Location and dimensions of all existing and proposed development or alterations, including public and private roads, sewer and water lines, wells, utilities, easements, water sources, lakes and springs, drainage facilities, on-site sewage disposal, and drain field areas, within the property boundary;
A discussion of the development standards applicable to the critical areas and proposed activity.
A mitigation plan, if needed, to offset any impact will be prepared in accordance with mitigation plan requirements of each applicable critical area found in this chapter.
Critical Areas Reports: Wetlands. In addition to the general critical areas reports requirement of LMC § 17.12.010, a critical areas report for wetlands shall meet the requirements of this section.
A wetland determination report is a limited study and determines the presence or absence of wetlands. A wetland determination is used to provide an environmental analysis to justify that wetlands are not present within the project area.
A wetland delineation report is a more detailed study and is prepared when a project area does contain critical areas. A wetland delineation report shows the boundary of the wetland as determined in the field and provides detailed analysis of environmental conditions and regulatory requirements.
Preparation by a Qualified Expert. A critical areas report for wetlands and an on-site wetland determination or wetland delineation report shall be prepared by a qualified expert for wetlands meeting the requirements in LMC § 17.10.050, Definitions.
Critical Areas Reports: Wetlands. A critical areas report for wetlands shall contain a written assessment and accompanying maps of the wetlands and their buffers within and adjacent to the project area. The following information shall be provided at a minimum:
Site characteristics including topography, total acreage of the property, and maps showing delineated wetlands and other water bodies within the study area in accordance with the approved federal wetland delineation manual and applicable regional supplement;
Assessment of existing conditions of wetlands and wetland buffers including wetland acreage (or square footage), water regime, vegetation, soils, landscape position, surrounding land uses, and functions;
Description of Cowardin classifications of vegetation communities, hydrogeomorphic classification, and estimated distances to and area of other off-site wetlands and water bodies within the vicinity of the subject wetland;
Identification of the wetland's category as defined in this chapter, including the wetland category using the Washington State Wetland Rating System for Western Washington: 2014 Update (Ecology Publication No. 14-06-029 or as revised and approved by Ecology), and appropriate wetland rating forms with associated maps;
Completed wetland determination data forms from the U.S. Army Corps of Engineers' Regional Supplement for the Western Mountains, Valleys, and Coast Region: Version 2 (2010), or as revised, numbered to correspond to each sample point;
USGS quadrangle map drawn to scale and including a north arrow, public roads and other known landmarks in the vicinity with the site boundaries clearly defined.
Site Map. This map shall be drawn to a useable scale, one inch equals 100 feet or better, and shall include a north arrow and all of the following requirements:
Existing physical features of the site including, but not limited to, buildings and other structures, fences, roads, utilities, parking lots, water bodies; and
Wetland Mitigation Plans. All critical areas mitigation projects required pursuant to this chapter either as a permit condition or as the result of an enforcement action shall follow a mitigation plan approved by the department prior to any site disturbance. Prior to any submittals of mitigation plans for critical areas alterations, the applicant shall demonstrate mitigation sequencing for any impacts, intentional or otherwise. Mitigation sequencing shall follow the standards described in LMC § 17.10.110(7)(a).
The director may determine a peer review be conducted at the applicant's expense. The director may seek assistance from resource agencies prior to making a decision on the completeness of their application.
Preparation by a Qualified Expert. When a wetland mitigation plan is required, it shall be prepared by a qualified expert for wetlands meeting the requirements in LMC § 17.10.050, Definitions.
Critical Areas Reports: Wetlands. A critical areas report for wetlands shall accompany or be included in the mitigation plan and include the minimum parameters described in subsection (1) of this section.
Wetland Mitigation Plans. Full guidance can be found in Wetland Mitigation in Washington State – Part 2: Developing Mitigation Plans (Version 1), Publication No. 06-06-011b, March 2006, or as revised. If a wetland mitigation bank is used to compensate for wetland impacts, then the most current Interagency Review Team guidance for preparing bank use plans should be followed. The wetland mitigation plan shall include a written report and plan sheets that contain, at a minimum, the following elements:
Description of the existing wetlands and buffers proposed to be altered. Include acreage (or square footage), water regime, vegetation, soils, landscape position, surrounding land uses, and functions.
Description of impacts in terms of acreage by Cowardin classification, hydrogeomorphic classification, and wetland rating, based on the Washington State Wetland Rating System for Western Washington: 2014 Update (Washington Department of Ecology Publication No. 14-06-029, or as revised and approved by Ecology).
Description of the 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.
Surface and subsurface hydrologic conditions, including an analysis of existing and proposed hydrologic regimes for enhanced, created, or restored mitigation areas. Include illustrations of how data for existing hydrologic conditions were used to determine the estimates of future hydrologic conditions.
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 classifications, and categories of wetlands.
Performance standards (measureable standards for years post-installation) for upland and wetland communities, a monitoring schedule, and a maintenance schedule and actions proposed by year.
A description that the monitoring reports shall be submitted to document the performance standards, successes, problems, and contingency actions of the mitigation project. The mitigation project shall be monitored by the applicant or a qualified expert for a period necessary to establish that the mitigation is successful, but not for a period of less than five years. Creation and forested wetland mitigation shall be monitored for a period of at least 10 years. Monitoring reports shall be submitted to the department in years one, three, five, seven and 10.
Boundaries of the existing wetland and buffers, proposed areas of wetland and/or buffer impacts, location of proposed wetland and/or buffer compensation actions.
Existing topography in the zone of the proposed mitigation actions if any grading activity is proposed in the mitigation area(s). Include existing cross-sections of wetland areas on the development site that are proposed to be altered and for the proposed areas of wetland or buffer mitigation.
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.
A planting plan for the mitigation area, including all species by proposed community type and water regime, size and type of plant material to be installed, spacing of plants, typical clustering patterns, total number of each species by community type, and timing of installation.
Critical Areas Reports: Species and Habitat. In addition to the general critical areas report requirements of LMC § 17.12.010, a critical areas report for fish and wildlife habitat conservation areas shall meet the requirements of this section. Technical justification shall be provided where any information is not deemed applicable by the qualified expert.
Preparation by a Qualified Expert. A critical areas report for fish and wildlife habitat conservation areas and an on-site field investigation to evaluate the potential presence or absence of designated critical fish or wildlife species or habitat shall be prepared by a qualified expert for fish and wildlife habitat conservation areas meeting the requirements in LMC § 17.10.050, Definitions.
Critical Areas Reports: Species and Habitat. A fish and wildlife habitat conservation area report is a written report and accompanying maps, which shall contain, at a minimum, the following:
Identification of any species of local importance, priority species, or state or federally designated endangered, threatened, sensitive, or candidate species that have a primary association with habitat on or adjacent to the project area, and assessment of potential project impacts to the use of the site by the species;
A discussion of any federal, state, or local special management recommendations, including Washington Department of Fish and Wildlife habitat management recommendations, that have been developed for species or habitats located on or adjacent to the project area;
A detailed discussion of the project and direct and indirect potential impacts on habitat by the project, including potential impacts to water quality; and
Additional Information May Be Required. When appropriate due to the type of habitat or species present or the project area conditions, the city planner may also require the habitat conservation area report to include:
An evaluation by an independent qualified expert regarding the applicant's analysis and the effectiveness of any proposed mitigating measures or programs, to include any recommendations as appropriate; or
Preparation by a Qualified Expert. A habitat management plan shall be prepared by a qualified expert for fish and wildlife habitat conservation areas meeting the requirements in LMC § 17.10.050, Definitions.
Critical Areas Reports: Species and Habitat. A critical areas report for fish and wildlife habitat conservation areas shall accompany or be included in the habitat management plan and include the minimum parameters described in LMC § 17.12.010.
A discussion of measures, including avoidance, minimization, and mitigation, proposed to preserve existing habitats and restore any habitat that was degraded prior to the current proposed land use activity.
Provisions to reduce or eliminate the impact of the proposed development activities on any fish and wildlife habitat conservation area and critical species, and description of replacement of any lost habitat functions.
Establishment of buffers around fish and wildlife habitat conservation areas demonstrating rationale for buffers consistent with WAC 365-195-900 through 365-195-925.
A detailed description of vegetation on and adjacent to the project area and its associated buffers and demonstration of how the applicant will retain vegetation or vegetation critically important to threatened and endangered species.
Establishment of monitoring and management practices that will protect habitat after the site has been developed, including proposed monitoring and maintenance programs.
All lakes, ponds, streams, wetlands, or tidal waters on, or within 300 feet of, the subject property, including the name (if named), and ordinary high water mark of each, and stream type and wetland category consistent with WAC 222-16-030 and LMC § 17.10.110(2);
The location and description of the fish and wildlife habitat conservation area on the subject property, as well as any potential fish and wildlife conservation areas within 300 feet of the subject property as shown on maps identified in the Summary of Map Sources (Table 17.10.100) and/or housed within the department;
Review and comments by the Washington Department of Fish and Wildlife, and other appropriate state and federal agencies that review SEPA environmental checklists.
The director may determine a peer review be conducted by the applicant at the applicant's expense. The director may seek assistance from resource agencies prior to making a decision on the completeness of the application.
Geotechnical Reconnaissance Reports. A geotechnical reconnaissance is intended to be a limited study of geological hazards at a site, and does not include the collection of any subsurface soil, rock and groundwater data (i.e., no borings, test pits or cone penetration tests are performed). The scope of services shall include, at a minimum, a site visit and literature review performed by the qualified expert for geological hazards. A geotechnical reconnaissance is appropriate for erosion, volcanic and mine hazards, but will limit the ability of the qualified expert to evaluate landslide and seismic (primarily liquefaction) hazards. A geotechnical reconnaissance is not acceptable to evaluate landslide and seismic hazards, unless the qualified expert can provide compelling evidence as to why a geotechnical investigation is not required. After evaluating erosion, volcanic, and mine hazards with a geotechnical reconnaissance, it is possible that the qualified expert may recommend preparing a supplemental geotechnical investigation report as detailed in subsection (2) of this section.
Preparation by a Qualified Expert. A geotechnical reconnaissance report shall be prepared by a qualified expert for geological hazards meeting the requirements in LMC § 17.10.050, Definitions.
A site plan of the area delineating all areas of the site subject to landslide geological hazards (i.e., erosion, sliding, earthquake, and other geological events) based on mapping and geotechnical evaluation. Additionally, all geological hazards within 200 lateral feet of the site and all landslide hazards off the property but anticipated to impact the proposed development should be indicated on the site plan.
A contour map of the proposed site, at a reasonable scale (not smaller than one inch equals 100 feet) that clearly delineates slopes for ranges between 15 and 29 percent and 30 percent and greater, and includes figures for area coverage of each slope category on the site.
Topographic data. Contour map of proposed site at a scale no greater than one inch equals 100 feet that clearly delineates the slopes 15 percent and greater, including figures for area coverage of each slope category on the site.
Structural foundation requirements and estimated total and differential foundation settlements, including dynamic settlement in areas determined to be susceptible to soil liquefaction;
Site Evaluation. Evaluation of the ability of the site to accommodate the proposed activity. Where a valid geotechnical investigation report has been prepared within the last five years for a specific site, and where the proposed activity and surrounding site conditions are unchanged, said report may be used and a new report may not be required, at the discretion of the director or the city engineer, and provided the geotechnical report complies with the current building code.
Geotechnical Investigation Reports. A geotechnical investigation report includes investigating subsurface soil, rock, and groundwater conditions to better assess the geological site hazards. The scope of services shall include, at a minimum, a site visit, a subsurface investigation (i.e., borings, test pits, or cone penetration tests) and literature review performed by the qualified expert for geological hazards. A geotechnical investigation shall be required to evaluate landslide and seismic hazards, unless the qualified expert can provide compelling evidence as to why a geotechnical reconnaissance is sufficient.
Preparation by a Qualified Expert. A geotechnical investigation report shall be prepared by a qualified expert for geological hazards meeting the requirements in LMC § 17.10.050, Definitions.
A site plan of the area delineating all areas of the site subject to landslide geological hazards (i.e., erosion, sliding, earthquake, and other geological events) based on mapping and geotechnical evaluation. Additionally, all geological hazards within 200 lateral feet of the site and all landslide hazards off the property but anticipated to impact the proposed development should be indicated on the site plan.
A contour map of the proposed site, at a reasonable scale (not smaller than one inch equals 100 feet) that clearly delineates slopes for ranges between 15 and 29 percent and 30 percent and greater, and includes figures for area coverage of each slope category on the site.
Topographic data. Contour map of proposed site at a scale no greater than one inch equals 100 feet that clearly delineates the slopes 15 percent and greater, including figures for area coverage of each slope category on the site.
Subsurface data. Logs of borings, test pits and other exploratory methods, soil and rock stratigraphy, groundwater levels including seasonal changes, and laboratory test results.
Slope stability studies and opinion of slope stability based on a stated factor of safety for static and dynamic slope stability and a minimum horizontal ground acceleration as established by the current version of the building code (the minimum acceptable factor of safety for static slope stability shall be 1.5 and the minimum acceptable factor of safety for dynamic slope stability shall be 1.1);
Structural foundation requirements and estimated total and differential foundation settlements, including dynamic settlement in areas determined to be susceptible to soil liquefaction;
Site Evaluation. Evaluation of the ability of the site to accommodate the proposed activity. Where a valid geotechnical investigation report has been prepared within the last five years for a specific site, and where the proposed activity and surrounding site conditions are unchanged, said report may be used and a new report may not be required, at the discretion of the director or the city engineer, and provided the geotechnical report complies with the current building code.
Preparation by a Qualified Expert. An erosion hazard assessment shall be prepared by a qualified expert for geological hazards meeting the requirements in LMC § 17.10.050, Definitions.
An assessment of the probability for stream induced erosion to occur on the subject property and the estimated extent of the property that would be affected;
A site map of the property, drawn to scale, delineating the relationship of the stream to the property, and existing erosion areas and/or potential erosion areas, and the proposed development, including structural dimensions;
A cross-section map, drawn to scale and at two-foot contour intervals from the edge of the river's surface to the furthest landward boundary of the property, and including the proposed development;
Preparation by a Qualified Expert. An aquifer impact assessment shall be prepared by a qualified groundwater expert meeting the requirements in LMC § 17.10.050, Definitions.
Identification of the proposed land development activity including size, amount of impervious surface, vehicular usage and storage, and sources of water for consumption and other on-site usage.
Identification of geological, soil, topographic, and hydrologic features and conditions at the subject and abutting properties based on existing public information (e.g., soil surveys, topographic maps, Washington geology mapping, existing site well logs, etc.). These shall be displayed on a site map.
Proposed plans for management of runoff including routing and infiltration if applicable. Infiltration of uncontaminated (e.g., roof) runoff is encouraged where feasible.
An evaluation of the proposed project impacts on groundwater quality and quantity for the CARA including a plan for the mitigation of any potential impacts on the CARA.
Hydrogeologic Testing and Site Evaluations. If the director determines that hydrogeologic testing and site evaluation are required for development within a CARA, these investigations shall be conducted by a qualified groundwater expert meeting the requirements of LMC § 17.10.050, Definitions, and approved by the city engineer, and shall typically include at least the following, listed below. Applicants are encouraged to use existing studies and resources within the same locality to the fullest extent possible such as: U.S. Soil Conservation Service data and USGS data, when available, and select qualified experts with localized knowledge of the Longview area.
Preparation by a Qualified Expert. The hydrogeologic testing and site evaluation shall be conducted and a written report prepared by a qualified groundwater expert meeting the requirements in LMC § 17.10.050, Definitions.