CRITICAL AREAS REVIEW TECHNICAL REPORT_Crystal Springs Road Short Plat_2023-0308Critical Areas Report Dolgovyazov Duplex Project
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LAND SERVICES
NORTHWEST
120 STATE AVE NE PMB 190
OLYMPIA, WA 98501
360-481-4208
3/8/2023
RE: CRITICIAL AREA REVIEW FOR PARCEL# 22719220113
INTRODUCTION
This letter is the result of a critical area review conducted on January 31, 2023, at the 1.07 acre parcel #
22719220113 at 1001 Crystal Springs Road NW, Yelm, WA 98597 with the legal description of L Section
19 Township 17 Range 2E Quarter NW NW Testamentary Division LT 8 Document 4028308 located
in Thurston County, Washington (Figure 1).
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SITE CONDITIONS
The site was visited on January 31, 2023. The day was relatively clear with light precipitation occurring in
the week before. The temperature was about 42 degrees and the ground was bare, however the ground
itself was not frozen.
CURRENT CONDITIONS
Parcel #22719220113 is a relatively flat parcel maintained as a grassy field with invasive scotch broom
(Cytisus scoparius) that is bounded single family residences to the south and vacant parcel to the west,
Crystal Springs Road to the east and a storage yard to the east . There is a slight grade to the west
although most of the site is very flat (Figure 2).
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EXISTING INFORMATION REVIEW
In order to get a better understanding of the properties and their position of the landscape, the
following information was reviewed:
National Wetlands Inventory (NWI) Map (Appendix B)
The US Fish and Wildlife Service wetland shapefile data does not show any wetlands within 300 feet of
the property. Yelm Creek is approximately 500 feet to the west.
Thurston County Area Soil Survey, Soil Conservation Service (U.S. Department of Agriculture, 1973)
National Resource Conservation Service Shapefiles (NRCS Web Soil Survey, 2022) (Appendix C)
The NRCS Soil Survey shows the property as containing:
• Spanaway gravelly sandy loam 0-3%
• Spanaway gravelly sandy loam 3-15%
The Spanaway series consists of very deep, somewhat excessively drained soils that formed in glacial
outwash. They are on terraces and plains. Slopes are 0 to 15 percent. The mean annual precipitation is
about 1,270 millimeters. The mean annual temperature is about 10 degrees C.
TAXONOMIC CLASS: Sandy-skeletal, isotic, mesic Typic Humixerepts
TYPICAL PEDON: Spanaway gravelly sandy loam - fern-grass prairie. (Colors are for moist soil unless
otherwise stated.)
Oa--0 to 3 centimeters; black (10YR 2/1) highly decomposed plant material, very dark brown (10YR 2/2)
dry; mostly from grass roots and moss. (0 to 4 centimeters thick)
A--3 to 38 centimeters; black (10YR 2/1) gravelly sandy loam, very dark grayish brown (10YR 3/2) dry;
weak fine granular structure; soft, very friable, nonsticky and nonplastic; many fine roots; very high in
organic matter content, has mellow, sooty feel; 34 percent gravel; strongly acid (pH 5.4); clear smooth
boundary. (25 to 50 centimeters thick)
Bw--38 to 48 centimeters; dark grayish brown (10YR 4/2) very gravelly sandy loam, grayish brown (10YR
5/2) dry; weak fine subangular blocky structure; soft, very friable, nonsticky and nonplastic; common
fine roots; 45 percent gravel, 10 percent cobbles; moderately acid (pH 5.8); clear smooth boundary. (8
to 20 centimeters thick)
RANGE IN CHARACTERISTICS: Solum thickness is 35 to 70 centimeters. The mean annual soil
temperature is 9 to 12 degrees C. These soils are usually moist but are dry in the moisture control
section for 75 to 90 consecutive days following summer solstice. The umbric epipedon is 25 to 50
centimeters thick. Rock fragments are 35 to 85 percent, with 35 to 60 percent gravel, 0 to 60 percent
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cobbles and 0 to 5 percent stones
The A horizon has hue of 10YR through 5YR, value of 2 to 4 dry, and chroma of 1 or 2 moist and dry. It
has weak granular or blocky structure and is moderately acid or strongly acid.
The Bw horizon has value of 4 or 5 dry and 3 or 4 moist. It is very gravelly sandy loam, very gravelly loam
or extremely gravelly sandy loam. It has weak fine or medium blocky structure and is strongly acid to
slightly acid.
GEOGRAPHIC SETTING: Spanaway soils are on glacial outwash terraces and plains at elevations of about
30 to 150 meters. Slopes are 0 to 15 percent. These soils formed in glacial outwash. These soils are in a
maritime climate with cool, dry summers and mild, wet winters. The mean annual precipitation is 890 to
1650 millimeters. The mean annual temperature is about 10.5 degrees C. The frost-free season is 150 to
200 days
DRAINAGE AND SATURATED HYDRAULIC CONDUCTIVITY: Somewhat excessively drained; slow runoff;
high saturated hydraulic conductivity.
Thurston County Geodata Wetland, Stream and Waterbody Inventory (Appendix D)
Thurston County maintains a geodatabase of wetland stream and waterbody features. These shapefiles
did not show any wetlands streams or waterbodies within 315 feet of the subject properties.
USGS 7.5 Minute Quadrangle Topographic Maps (Appendix E)
The USGS maintains topographic maps which show natural and man-made features. This map does not
show any hydrologic features within 300 feet of the subject properties. Yelm Creek lies beyond this
distance. to the west.
Washington Department of Natural Resources Stream Type Map (Appendix F)
The WA Dept of Natural Resources has a map that shows stream types in accordance with the WAC 222-
16-31. This map does not show any streams or wetlands within 300 feet of the subject property.
Washington Department of Fish and Wildlife Priority Habitats and Species Database (Appendix G).
The Washington Department of Fish and Wildlife Priority Habitats and Species Mapper shows the
Townsend's Big-eared Bat and Yuma myotis. These are general polygons. The bats may feed on
macroinvertabrates in the area, or rest in the attics of the garage or the single-family homes, however
no guano or other signs of bats were found on the site during the visits.
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These are general inventories of information gathered by remote sensing and a site visit was necessary
to verify the information.
RECONNAISSANCE METHODS
Land Services Northwest personnel surveyed the property on January 31, 2023, looking at plant
communities, slopes, drainage patterns while paying special attention to swales and low spots where
water might collect. We had previously conducted a Mazama pocket gopher study during the 2022
season, so we were somewhat familiar with this property
Land Services Northwest based its wetland evaluation on the routine on-site determination method
published in the 1987 Wetland Identification and Delineation Manual (Environmental Laboratory, 1987)
and the Western Mountains Valleys and Coast Region (Version 2.0) (USACE, 2010). The Wetland-
adapted plant species (hydrophytes) were evaluated as indicators of soil saturation and inundation.
Soils were excavated to 18 – 24 inches below the surface within representative test pits to evaluate soil
characteristics and hydrological conditions. The subject areas were evaluated for wetland hydrology,
including pooling, ponding, and soil saturation. Hydrological conditions were observed through surface
or soil indicators. Wetlands were rated using the current version of the Wetland Rating System for
Western Washington (Hruby, 2014). No water or signs of water were found on site.
Streams were classified using WAC 222-12-32 Forest Practices and Yelm Municipal Code.
FINDINGS
No wetlands or other suspicious areas which warranted further exploration were found onsite
No streams were found on site with a bed and bank or sorted gravels signs of water flow.
No Floodways are found onsite or within 300 feet of the site.
Yelm Creek is located offsite beyond the 315 foot study limits and did not warrant further study.
No other suspicious areas were found in the vicinity of the subject property; however, we were limited
to what we could see from the property line, and aerials as we did not have permission to visit the
adjacent properties.
PROPOSED PROJECT
The project is to build three duplexes with a road, driveways and associated infrastructure
“Proposed development of the site will consist of 3 duplexes with associated roadways, utilities,
stormwater management, and open space.
Stormwater management and runoff treatment for the site are proposed to be addressed through the
implementation of a bioretention facility in the northwestern portion of the site.
The subject properties drainage facilities were designed using the guidelines and requirements
established in the 2019 DOE Stormwater Management Manual for Western Washington (2019
SWMMWW) as indicated by the City of Yelm Municipal Code.
The project is located within a critical aquifer recharge area. In order to protect groundwater from
pollution during construction, pollutants will be handles with care and disposed of through approved
methods only per the requirements of the 2019 SWMMMWW. Maintenance, fueling, and/or repair of
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heavy equipment and vehicles is not anticipated to occur on site. Bulk cement and new concrete
washing or curing waters are anticipated to be present on site as pH-modifying sources. In order to
protect groundwater from these pollutants, BMP C252 (Treating and Disposing of High pH Water) of the
2019 SWMMWW will be implemented to ensure no discharge to groundwater. Additionally, concrete
trucks will not be washed out onto the grounds, or into storm drains, open ditches, streets, or streams.
Excess concrete must not be dumped on-site, except in the designated concrete washout areas with
appropriate BMPs installed. In order to protect onsite soils from siltation, a lined temporary sediment
pond will be located upstream of the bioretention facility to allow for sediment to settle out of the
construction runoff prior to discharge.
Insert Site Plan Figure 3
CRYSTAL SPRINGS ST NWSEC. 19, T17N., R02W., W.M.JOB NO:DRAWING FILE NO:DATE:DESIGNER:BYDATEREVISIONSDRAWN BY:SHEET TITLE:OFDRAWING NO:SHEET NO:PROJECT NAME:SEAL:APPROVED BY:CRYSTAL SPRINGS STREET NWYELM, WA 98597ZNGMARCH, 202322-0009771CRYSTAL SPRINGS ROAD SHORT PLAT8730 TALLON LANE NE, SUITE 200, LACEY, WA 98516P: 360.352.1465SCJALLIANCE.COMZNGSITE PLAN EXHIBITSETBACK NOTES:
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REGULATORY REVIEW
The City of Yelm is in an Aquifer Recharge area covered by YMC 18.21.070 Critical aquifer recharge areas
which is covered with comments referring to the proposed development below (Comment in Italics).
A. Critical Aquifer Recharge Areas Designation. Critical aquifer recharge areas are those areas
with a critical recharging effect on aquifers used for potable water as defined by WAC 365-190-
030(2). A critical aquifer recharge area has prevailing geologic conditions associated with
infiltration rates that create a high potential for contamination of ground water resources or
contribute significantly to the replenishment of ground water.
Noted.
B. Designation of Critical Aquifer Recharge Areas. The entire city of Yelm and its urban growth
area is identified as a highly susceptible critical aquifer recharge area.
Noted.
C. Performance Standards – General Requirements..
1. Activities may only be permitted in a critical aquifer recharge area if the applicant can
show that the proposed activity will not cause contaminants to enter the aquifer and that
the proposed activity will not adversely affect the recharging of the aquifer.
The activities that will be permitted in this area would be consistent with typical residential
activities. No commercial activity is planned or expected to be associated with the residences
except for typical home based office activity business that are common these days. No
automotive repair businesses or businesses that use commercial cleaning chemicals will be
used and disposal of wastes generated by the single or multifamily residences will use typical
waste collection services.
The construction of the site will use construction bmp’s such as silt fences, straw wattles and
other stormwater BMP’s to prevent discharge of turbid waters to waters of the state using the
most recent accepted City of Yelm Stormwater Manual.
2. The proposed activity must comply with the water source protection requirements and
recommendations of the U.S. Environmental Protection Agency, Washington State
Department of Health, and the Thurston County environmental health division.
All activites that are proposed will be compliant with the water source protection requirements
and the recommendations of the US Environmental Protection Agency, Washington State
Department of Health and the Thurston County Environmental Health Division.
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3. All new development, redevelopment, and small parcel development shall meet the
water quality requirements of the stormwater manual as adopted by the city of Yelm.
A Stormwater Pollution Prevention Plan will be developed that will be consistent with the most
recently adopted stormwater water quality manual adopted by the City of Yelm. A memo is
attached outlining many of those features.
D. Performance Standards – Specific Uses.
1. Storage Tanks. All storage tanks proposed to be located in a critical aquifer recharge
area must comply with local building code requirements and must conform to the
following requirements:
a. Underground Tanks. All new underground storage facilities proposed for use in
the storage of hazardous substances or hazardous wastes shall be designed and
constructed so as to:
i. Prevent releases due to corrosion or structural failure for the operational life
of the tank;
ii. Be protected against corrosion, constructed of noncorrosive material, steel
clad with a noncorrosive material, or designed to include a secondary
containment system to prevent the release or threatened release of any stored
substances; and
iii. Use material in the construction or lining of the tank that is compatible with
the substance to be stored.
No underground tanks will be installed for use in the storage of hazardous
substances or hazardous wastes. No generators of toxic or hazardous wastes are
expected as the applicant proposes single family residences or multifamily
residences which do not create hazardous wastes that would need to be stored in
tanks.
b. Aboveground Tanks. All new aboveground storage facilities proposed for use in
the storage of hazardous substances or hazardous wastes shall be designed and
constructed so as to:
i. Not allow the release of a hazardous substance to the ground, ground waters,
or surface waters;
Hazardous substances will be disposed of in an environmentally responsible manner
and would not allow the release of a hazardous substance to the ground, ground
waters, or surface waters;
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ii. Have a primary containment area enclosing or underlying the tank or part
thereof; and
It is not expected that any of this would be needed. No containment area would be
required as no hazardous wastes will be generated beyond the small amounts that
could be associated with a single-family residence
iii. A secondary containment system either built into the tank structure or a dike
system built outside the tank for all tanks.
No above ground tanks will be installed on site to hold or release any hazardous
substance to the ground, ground waters, or surface waters;
2. Vehicle Repair and Servicing.
a. Vehicle repair and servicing must be conducted over impermeable pads and within
a covered structure capable of withstanding normally expected weather conditions.
Chemicals used in the process of vehicle repair and servicing must be stored in a
manner that protects them from weather and provides containment should leaks
occur.
It is not expected that vehicle repair or servicing would be done at any of the newly
created residences as it is not a typical residential activity,
b. No dry wells shall be allowed in critical aquifer recharge areas on sites used for
vehicle repair and servicing. Dry wells existing on the site prior to facility
establishment must be abandoned using techniques approved by the state
Department of Ecology prior to commencement of the proposed activity.
No Vehicle repair or servicing will be conducted onsite. No dry wells for vehicle repair or
servicing will be required for these activities. No known dry wells are onsite. If any are
found they will be abandoned using techniques approved by the WA State Department of
Ecology
3. Use of Reclaimed Water for Surface Percolation or Direct Recharge. Water reuse
projects for reclaimed water must be in accordance with the adopted water or sewer
comprehensive plans that have been approved by the State Departments of Ecology and
Health.
a. Use of reclaimed water for surface percolation must meet the ground water
recharge criteria given in RCW 90.46.010(10) and 90.46.080(1). The State Department
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of Ecology may establish additional discharge limits in accordance with
RCW 90.46.080(2).
No reclaim water for surface percolation will be done or generated onsite.
b. Direct injection must be in accordance with the standards developed by authority
of RCW 90.46.042. (Ord. 995 § 12 (Exh. A), 2015).
No direct injection will be conducted on site. If for some reason direct injection would be
necessary, it would be done in accordance with the standards developed by authority of
RCW 90.46.042.
CONCLUSION
The subject properties were reviewed using the onsite determination method for wetlands looking for
hydrologic features or signs of wetlands. No wetlands, streams, floodways, steep slopes, or other
critical areas were found during the literature review or onsite survey. The area lies in a Critical Aquafer
Recharge area. BMP’s and project design will maintain water quality and no discharges of untreated
water to waters of the state are expected.
LIMITATIONS
This report was created with care and best professional judgment using the current best available
science, but the report is subject to interpretation by local state and federal regulators who have the
final regulatory authority on critical areas and their boundaries. No recommendations or suggestions
should be undertaken without regulatory approval of this report.
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Appendix A – PHOTOGRAPHS
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Appendix B – USFWS NATIONAL WETLAND INVENTORY
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APPENDIX C – NRCS SOIL SURVEY FOR THURSTON COUNTY
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APPENDIX D – THURSTON COUNTY WETLAND, STREAM AND WATERBODY SHAPEFILES
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APPENDIX E – USGS TOPOGRAPHIC MAP
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APPENDIX F – WADNR FOREST PRACTICES STREAM TYPE MAP
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APPENDIX G – WASHINGTON DEPARTMENT OF FISH AND WILDLIFE PRIORITY HABITATS AND SPECIES MAP
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Appendix H – Thurston County FEMA Floodway Map
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Appendix I – SCJ Ground and Surface Water Protection Memo
MEMORANDUM
Date: March 23, 2023
To: Alex Callendar, Land Services NW
From: Bill Dunning, PE
Re: Crystal Springs Road Plat
Stormwater Management Water Quality
Project #22-000977
The Dolgovyasov Short Subdivision project is located at 1001 Crystal Springs Road SE in Yelm,
Washington on a single parcel. The total project site area is 46,609.2 square feet (1.07 acres).
Residential properties are to the south with a storage yard to the north and a vacant lot to the west
and Crystal Springs Road SE to the East.
Proposed development of the site will consist of three duplex buildings on three separate parcels with
associated roadway, utility, stormwater management, and open space improvements as required by
code. Stormwater management and runoff treatment for the site are proposed to be addressed
through the implementation of a vegetated filter strip for water quality and an underground
infiltration facility located in the back yard of each duplex building.
The subject property's drainage facilities were designed using the guidelines and requirements
established in the 2019 DOE Stormwater Management Manual for Western Washington (2019
SWMMWW) as indicated by the City of Yelm Municipal Code. The project is located within a critical
aquifer recharge area. In order to protect groundwater from pollution during construction, pollutants
will be managed with care and disposed of through approved methods only per the requirements of
the 2019 SWMMMWW.
Maintenance, fueling, and/or repair of heavy equipment and vehicles is not anticipated to occur on
site. Bulk cement and new concrete washing or curing waters are anticipated to be present on site as
pH-modifying sources. In order to protect groundwater from these pollutants, BMP C252 (Treating
and Disposing of High pH Water) of the 2019 SWMMWW will be implemented to ensure no discharge
to groundwater. Additionally, concrete trucks will not be washed out onto the ground, or into storm
drains, open ditches, streets, or streams. Excess concrete must not be dumped on-site, except in the
designated concrete washout areas with appropriate BMPs installed. In order to protect onsite soils
from siltation, a lined temporary sediment pond will be located upstream of the bioretention facility
to allow for sediment to settle out of the construction runoff prior to discharge. Add any other
considerations such as primary use expected and how that will not discharge to waters of the state
(Groundwater).