HomeMy WebLinkAboutConstruction Stormwater Pollution Prevention Plan - BLD Engineering / Geo-tech Reports - 12/21/2017 Thy if fl^45 MUST BE
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MR INSPEOriON
Construction Stormwater Pollution Prevention Plan
for
Shearer Logging & Single Family Residential Property
401 NE Timberline Drive
Parcel No. 12320-34-00030
Mason County, Washington
December 21, 2017
Project#17195 RECEIVED
JAN 0 8 2018
615 W. Alder Street
TO BE KEPT IN THE
PARCEL FILE
Prepared For:
Tom Shearer
PO Box 1959
Belfair, Washington 98528 �� CLYDt s
AS TIT
Prepared By:
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Envirotech Engineering, PLLC
PO Box 984 43045 q�
Belfair, Washington 98528 �� �FCIsTER��G���
Phone: 360-275-9374 �810NALE�
Envirotech Engineering,PLLC(Envirotech)has completed this construction stormwater pollution
prevention plan (SWPPP) in conjunction with the stormwater management plan for a residential
property located at 401 NE Timberline Drive, identified as parcel number 12320-34-00030 in
Mason County,Washington.
The following sections in this SWPPP includes Project Description, Existing Site Conditions,
Adjacent Areas, Critical Areas, Soils, Erosion Problem Areas, Construction Phasing/ Schedule,
Engineering Calculations, and the twelve (12) required SWPPP elements per the 2005
Department of Ecology Stormwater Management Manual.
Project Description
Information pertaining to the Project was provided by the property owner, and observations from
a field visit by Envirotech. The proposed development is expected to consist of a new single
family residence,driveway and other ancillary features typical of this type of development.
The size of the property is 13.78 acres. It is anticipated that the residential structures will cover
approximately 6200 square feet (sf), and the driveways will encompass an additional 7050 sf in
size.The total proposed impervious surface area is 13,250 sf. The total land area that has already
been disturbed due to logging is approximately 3.00 acres. It is anticipated that additional land
disturbance will not result from the proposed development. Cut and fill quantities were
approximated to be 200 cubic yards (cy) and 200 cy, respectively. See the accompanying
stormwater management plans for an illustration of current and proposed site features.
Existing Site Conditions
The Project is currently vacant land with few improvements such as a road. Clearing and light
grading is apparent. This includes past logging and stumping. The property is surrounded by rural
residential development. Timberline Drive extends along the north side of the property, and the
Union River and other water features on the south portion of the property.Vegetation on and near
the property consists primarily of 2"d growth firs, alders, and other trees and shrubbery common
to this area of the Pacific Northwest.
Descending slopes exceeding 15% are located on and beyond the property. Average slope grades
are up to approximately 23%with a vertical relief of approximately 15 feet. Some steeper slopes
were observed, but negligible vertical height and influence on the project. Ascending grades are
generally located to the northwest of the planned development. This slope is relatively minor
within 300 feet of the Project,with no apparent slope grades of at least 15%. The upland area of
the property is situated on a gentle hillside. Landforms are primarily of glacial origin with
centuries of weathering overburden.Most of the property consists of alluvium.
The majority of the stormwater runoff originating upslope from the anticipated development is
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December 21,2017
expected to be minimal to moderate. Significant scour, erosion and sediment transport was not
apparent near the planned development. The Union River, stream and wetland on the property
have drainage issues,and is distant from the proposed project. There are no apparent water bodies
or wetlands located upslope from the planned development that would significantly influence the
Project. It appears that development will be at least 25 feet above the ordinary high water mark of
the Union River.
Adjacent Areas
Adjacent areas include vacant land,waterways, and rural residential development. A rock quarry
is also nearby. Site disturbance is not expected to disturb adjacent areas if all provisions in the
stormwater management plan are followed.However,the aforementioned areas have the potential
to be affected by the site disturbance.
Downstream drainage appears to follow the Union River in a southerly direction for at least 2
miles.This project is within the Hood Canal watershed.
Critical Areas
Critical areas on this property include moderately hazard slopes, wetland stream and the Union
P Pert3' Y P >
river.A critical aquifer is not known to exist beneath the property.
This project is not anticipated to disturb any critical area, and special requirements are limited to
environmental buffers from the surface water and wetland.
Soils
Information on infiltration rates and soil conditions pertaining to the Project was accomplished by
Envirotech. For complete details, see the Geological Assessment prepared for the Shearer
Logging and Single Family Residential Property,dated December 21,2017. Selected information
pertaining to the drainage aspect of the project is provided below.
The following subsurface conditions are estimated descriptions of the Project subgrade utilizing
information from the depth of penetration at all testing, sampling, observed and investigated
locations. Soils for this project were described utilizing the Unified Soil Classification System
(USCS). Using the USCS in conjunction with estimated relative densities and other anticipated
engineering properties of the soil, susceptibility for potential landslides, erosion and seismic
hazards may be assessed.
The Project is primarily composed of undisturbed, native soils, without indications of substantial
fill. However, some fill could be present. Competent bearing soils were encountered at 18 inches
below the existing ground surface in locations where the ground was probed. For engineering
purposes,these native soils consist of distinguishable layers,as presented below.
Soils within the upper 6 feet of natural ground were observed to be primarily moist, brown silty
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sand with gravel (SM). Soils below the upper SM layer could be a conglomerate of sand, silt and
clay. This is based on nearby well reports,site geology,and/or knowledge of the general area.
According to the USDA Textural Classification System, the site soils are primarily classified as
sandy loam. Some pockets of gravelly soils was also observed. Soil structure may be described as
granular.
According to the "Soil Survey of Mason County," by the United States Department of
Agriculture, Soil Conservation Service (SCS), the site soils are described as Everett gravelly
loamy sand, with 5% - 15% slopes, Belfast silt loam, with 0 — 3% slopes, and Indianola loamy
sand,with 5%to 15%slopes.
From the water well report(s) and knowledge of the general area, permanent groundwater is at
least 50 feet directly below the property at the building pad location. Surface seepage or perched
groundwater at shallow depths was not observed on-site,nor indicated on the well reports.
The soil samples obtained at the Project site during the field investigation were preserved and
transported for possible laboratory testing. Visual classification of soils was performed in the
field at all observed soil profiles. Visual classifications were performed in accordance with the
American Standards for Testing and Materials(ASTM D2488).
The general results from the visual classification are presented above in the Subsurface
Conditions Section. Specifically, soils within the upper 4 feet in one testing location consisted of
approximately 12% gravel, 55% sand-sized soils, and 33% fines with no plasticity indicating a
very low content of clay within the fine fraction. Minor variations observed during the visual
classification of particle size content(i.e. gravel, sand, fines), or isolated pockets within the soil
stratification were insignificant in relation to the overall engineering properties of the soil.
Based on the fines content, erodibility of the site soils is considered to be moderate. However,
soils on disturbed slopes are more apt to erode than disturbed soils on flat ground. Based on the
fines content and fraction of clay within the fines content, settleability of the site soils is expected
to be moderate to fast. Permeability is expected to be high for this site due significance of
moderate density,poorly graded granular soils.
According to the 2005 Stormwater Management Manual for Western Washington prepared by the
Washington State Department of Ecology Water Quality Program, infiltration rates are
determined per the USDA Textural Classification of the soils, and an appropriate factor of safety.
Based on the soils consisting predominantly of sandy loam, and utilizing a factor of safety of 2,
site infiltration for stormwater facilities should be 0.33 inches/hour.
Water quality for this project is achieved by the soil subgrade beneath the sub-base water storage
area. The Cation-Exchange Capacity (CEC) of the soils, based on soil texture and testing as
provided above,the CEC ranges from a minimum of 15 to 40 meq/100g. Based on the abundance
of organic matter in the top soil,the CEC values may be much higher.
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Erosion Problem Areas
There are no identified or mapped erosion hazard areas for this property where development is
expected to occur.
Construction Phasing
Construction phasing for this project may occur, such as developing the second house sometime
after the initial development is complete. The following includes the recommended construction
sequence and procedure for project development:
1. Delineate clearing and easement limits.
2. Construct all required temporary erosion control features.
3. Clear vegetation required for site development.
4. Perform initial earthwork and rough grading for constructing the roadway, driveways,
building pads, stormwater management facilities, etc. If necessary, exposed soils in stock
piles must be protected with plastic covering or County approved method.
5. Complete final grading of the subgrade, and materials placement per the plans and
specifications. This includes dredging sediments from temporary sediment facilities, if
necessary.
6. Maintain all temporary erosion and sediment control facilities, as needed, in order to
provide the required protection of downstream water quality. Additional temporary
erosion control shall be rendered throughout the duration of the project, if necessary.
7. Provide permanent erosion control in order to stabilize the project.
8. Remove temporary erosion sedimentation control facilities after construction is complete,
and the site is sufficiently stabilized.
Construction Schedule
Some clearing and grading, including past logging has already occurred. Construction of the
single family residence is expected to commence in March 2018. Successive phases are not
anticipated. Wet season erosion control will most likely be required for this project. However,
wet season construction constraints are not necessary for critical areas.
Engineering Calculations
Standard sediment ponds and traps were not utilized for this project. However, sedimentation due
to construction runoff is anticipated to be retained on site. Significant diversions and waterways
were not utilized for this project.
The drainage report consists of calculations for 100yr-24hr and 6mo-24hr storm events. Runoff
was shown to be contained on-site due to a 100yr-24hr event. Consequently, stormwater
accumulated from a 2yr-24hr temporary erosion storm event will be easily accommodated.
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Operation and Maintenance
An operation and maintenance schedule for construction activities are provided below within the
Specific Construction SWPPP Items. An operation and maintenance schedule for all proposed
permanent stormwater facilities shall be required under a separate cover. If required by the
Agency,an operation and maintenance Declaration of Covenant shall be implemented to cover all
privately owned and maintained stormwater facilities.
Specific Construction SWPPP Items
The following 12 items are addressed herein per the 2005 Department of Ecology Stormwater
Manual.
1.0 Mark Clearing Limits
Clearing limits shall be delineated on-site by the owner/ contractor. Activities are not permitted
beyond the designated clearing limits without prior approval and/or permits. Additional clearing
is not anticipated due to previous logging.
2.0 Establish Construction Access
Construction access shall be limited to a single entrance to access the project during construction.
A stabilized construction access adjacent to Timberline Drive shall be built per the erosion
control plans.
3.0 Control Flow Rates
Properties and waterways located downstream from the construction site is protected from
erosion by adhering to the stormwater management manual by containing all construction runoff
on-site due to the 2yr 24hr storm event. Due to this, a downstream analysis is not necessary for
this project during construction.Temporary retention/detention stormwater facilities, if any, shall
be functional prior to the construction of site improvements. Additional or different stormwater
flow control may be necessary if current designed facilities are not functioning as intended. If
permanent infiltration ponds are used for flow control during construction, these facilities should
be protected from siltation during the construction phase.
4.0 Install Sediment Controls
Sediment controls deemed adequate for this project are naturally vegetated terrain, and silt
fencing. See the stormwater management plan for locations and details.
5.0 Stabilize Soils
Soil stabilization is necessary for this project.Temporary seeding and permanent soil stabilization
requirements are provided in the stormwater management plans. This also includes stabilizing all
exposed and unworked soils from runoff and wind erosion.
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6.0 Protect Slopes
Both natural and fill slopes shall be protected per the stormwater management plans. This
includes stabilizing with vegetation,and maintaining natural vegetation.
7.0 Protect Drain Inlets
There are no existing drain inlets that will be influenced by this project.Proposed inlets should be
protected with fabric or other standard control until the project is stabilized.
8.0 Stabilize Channels and Outlets
All designed channels and outlets, if any, shall be stabilized with vegetation, riprap, or other
appropriate means. See the stormwater management plans for locations and details. A roadside
swale may be warranted in order to divert water away from the development.
9.0 Control Pollutants
Pollution generated from construction must be controlled at all times. Control of pollutants other
than sediments includes the following:
1. All pollutants other than sediments, including waste materials and demolition debris,that
occur on-site shall be handled and disposed of in a manner that does not cause
contamination of stormwater. Woody debris may be chopped and spread on site.
2. Cover, containment and protection from vandalism shall be provided for all chemicals,
liquid products,petroleum products,and non-inert wastes present on the project site.
3. Maintenance and repair of heavy equipment and vehicles involving oil changes,hydraulic
system drain down, solvent and de-greasing cleaning operations, fuel tank drain down
and removal, and other activities which may result in discharge or spillage of pollutants
to the ground or into stormwater runoff must be conducted using spill prevention
measures, such as drip pans. Contaminated surfaces shall be cleaned immediately
following any discharge or spill incident. Emergency repairs may be performed on-site
using temporary plastic placed beneath and,if raining,over the vehicle.
4. Wheel wash or tire bath wastewater shall be discharged to a separate on-site treatment
system or to the sanitary sewer, if available.
5. Application of agricultural chemicals including fertilizers and pesticides shall be
conducted in a manner, and at application rates that will not result in loss of chemical to
stormwater runoff. Manufacturers' recommendations for application rates and procedures
shall be followed.
6. BMP's shall be used to prevent or treat contamination of stormwater runoff by pH
modifying sources. These sources include, but are not limited to, bulk cement, cement
kiln dust, fly ash, new concrete washing and curing waters,waste streams generated from
concrete grinding and sawing, exposed aggregate processes, and concrete pumping and
mixer washout waters. Stormwater discharges shall not cause or contribute to a violation
of the water quality standard for pH in the receiving waters.
7. Construction sites with significant concrete work shall adjust the pH of stormwater if
necessary to prevent violations of water quality standards.
8.
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10.0 Control Dewatering
Although dewatering will not be likely for this project, special provisions are required to be
followed when dewatering. The outlet for dewatering shall be located in a position as to prevent
sediments and pollution from leaving the site.This may be accomplished by pumping water into a
sedimentation pond,or other standard control.
11.0 Maintain BMP's
All temporary BMP's must be inspected and maintained accordingly.This includes the following:
Stabilized Construction Entrance
The stabilized construction entrance shall be inspected at reasonable increments. Increased usage
of the construction entrance warrants more frequent inspections. Additional rock shall be added
periodically to maintain proper function of the pad.
Silt Fence
All silt fencing shall be inspected immediately after each rainfall and at least daily during
prolonged rainfall.Any required repairs shall be made immediately.
Straw
Loose straw is subject to blowing, and should be inspected each day. Keep straw moist or tied
down in order to deter blowing.Add new straw if necessary.
Hay bales shall be bound with wire or appropriate measure. Check for raveling after each major
rainfall event.Bales may need to be stakes to prevent movement.
Permanent Vegetation
Permanent vegetation shall initially be inspected regularly to insure establishment and healthy
growth. Once established, vegetation may need to be periodically fertilized for continuous
growth.Vegetation shall be re-established in areas, if necessary.
While active construction is in process,all temporary erosion and sediment control facilities shall
be inspected and immediately maintained if necessary per the requirements provided above. In
the event that construction activities are discontinued for at least 4 consecutive days, the owner
shall be responsible for the inspection, and immediate maintenance if necessary, of all temporary
erosion and sediment control facilities immediately after storm events, and at least once every 7
days.
In addition to the aforementioned inspection and maintenance schedule, the owner shall install
additional erosion and sediment control facilities if proposed erosion and sediment control
measures prove to be inadequate.
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Preserving Natural Vegetation
Inspect flagged and/or fenced areas regularly to make sure flagging or fencing has not been
removed or damaged. if the flagging or fencing has been damaged or visibility reduced, it shall be
repaired or replaced immediately and visibility restored. If tree roots have been exposed or
injured, "prune" cleanly with an appropriate pruning saw or lopers directly above the damaged
roots and recover with native soils. Treatment of sap flowing trees (fir, hemlock, pine, soft
maples) is not advised as sap forms a natural healing barrier.
Dust Control
Respray area as necessary to keep dust to a minimum.
Concrete Handling
Containers shall be checked for holes in the liner daily during concrete pours and repaired the
same day.
Maintenance Responsibility
Inspection, maintenance, and financial liability of all temporary/ permanent erosion and
sedimentation control facilities shall ultimately be the responsibility of the owner or owner's
representative who is utilizing the facilities. Currently, the following proponent is in charge of
this responsibility:
Tom Shearer
PO Box 1959
Belfair, Washington 98528
12.0 Manage the Project
The designated manager for this project is:
Tom Shearer
PO Box 1959
Belfair, Washington 98528
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December 21,2017