HomeMy WebLinkAbout821085002 Drainage Report
DRAINAGE & EROSION CONTROL REPORT
FOR
PARCEL 10# 821085002
JEFFERSON COUNTY, WASHINGTON
MLA #: MLA04-00401; CASE #: BL004-00446
LOCATEOIN
SECTION 8, TOWNSHIP 28 NORTH, RANGE 1 EAST, W.M.
Prepared for
Todd & Cindy Colebrook.
". 0/
APPROVED
STORMW A TER PLAN
Prepared by
SEP 1 0 2004
Robert A. Leach, P.E.
NTI Engineering & Land Surveying
717 South Peabody
Port Angeles, WA 98362
(360) 452-8491 Voice (360) 452-8498 Fax
www.nti4u.com
f5) [E(ClEOWre 1m
ru SEP - 7 2004 lW
August, 2004
JEFFERSON COUNTY
DEPT. OF COMMUNITY DEVELOPMENT
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North.western Territ~ries, Inc. (NTI) was hired by !odd and Cind~ COI~b_~!~~~~f~~~~rro 1;'1
a drainage and erosion control plan for the of their proposed residential home site 6n-----~---~-~
Parcel #821-085-002 at lot 2, Section B of Port Ludlow #6 (revised) in Section 8,
Township 28 North, Range 1 East. As part of this analysis, a storm water collection and
dispersion system has been designed and a temporary / permanent erosion and
sediment control plan has been prepared for the construction of a private single family
residence and driveway.
I. INTRODUCTION
II. PROJECT OVERVIEW
Proposal: This project proposes the construction of a single family home upon
an "l" shaped wooded 5.1 acre site (221,067 sf). The home and ancillary
buildings will have approximately 7409 sf of roof area (home, garage and shop)
with 565 sf wood deck at the house, approximately 1197 net sf in concrete
aprons for the garage and shop (note that approximately 171 sf is under the
structure's eave line) and approximately 12,900 sf of 15' wide gravel driveway
and parking (recommend a narrower, 12' wide drive where possible). A small
yard area of approximately 1065 sf is envisioned along with an allocation of
about 500 sf of site disturbance for the installation of a well and sewer line. The
total disturbed area will be approximately 23,636 sf and the total impervious
surface (post restoration) will be 7409 + 12,900 +1200 +65 = 22,071 = 9.98% of
the site.
A preliminary analysis of this proposal by Jefferson County (July 2, 2004 -see
appendix) has indicated that a "Medium Project Storm Water Plan" is required.
With the total site impervious area being less than 10%, full dispersion disposal
is allowed without triggering flow control facility requirements. This will be
accomplished by use of BMP T5.30 (dispersion) in accordance with BMPs T5.1 0,
T5.11 and T5.12 which are included in total in Appendix 3 for reference.
Drainage dispersion per BMP T5.1 0 will be used for the roof/deck/cone pad
drainage and BMP T5.12 will be used for the gravel driveway drainage.
III. EXISTING CONDITIONS SUMMARY
1. Existing Topography: The property slopes to the south and has a slight
ridge line running in a north south direction along the west property which
causes the contours to be curved convex to the south and to shed water
both easterly and westerly from the crown of the ridge (westerly flow is on
the adjacent property with little or no runoff from this property). The
slopes along the N-S ridge line begin at about 2% at the north for about
1/4 of the site and then moderate to about 5% - 6% for the majority of the
site (through the building zone). The E-W slope from the ridge line is
Page 1 of 12
approximately 5% for the majority of the site until reaching the base of the
site's "L" shape when the slope steepens and varies from approximately
15% to over 25% indicating the change in soil type from AIC to AID. No
off-site runoff enters this property from the east, west or south and the
Walden Lane access intercepts runoff from the north.
2. Existing Vegetation: The site is partially treed per the County's web site
photo of 2000 (see Appendix 2) and the Architect's site plan shows a tree
line to the southwest of the home site. On-site observations reveal that
the shallow slope upland area is predominantly grass with treed areas
while the steeper slope downhill areas is treed. The Jefferson County
Drainage Regulations (DOE 2001) require that the storm drainage plan
consider the site to be vegetated as it was before European contact
(early-mid 1800s) which would, likely, have been totally forested. All
calculations for project related disturbances have been made with a
forested condition. No significant removal of trees is required for this
home's construction.
3. Existing Soils: The site soils are mapped by the USDA Soil
Conservation Service (SCS) at AIC or Alderwood Gravelly, Sandy, Loam
(0% - 15% slope) which is a hydrologic type "C" family of soils. Further
inspection resulting from an analysis of the site topographic information
obtained from the Jefferson County web site indicates that portion of the
site are AID or Alderwood Gravelly, Sandy, Loam (15% - 30% slope).
This is significant only in that the potential for erosion is greater in the AID
soils than in the AIC soils. All work on-site is confined to the AIC soil area
and 50' setbacks for storm drainage dispersion facilities is required by
BMP T5.10, T5.11, T5.12 and T5.30
4. Existing Site Hydrology: A site contour map and a regional contour map
obtained from the Jefferson County web site (see appendix) indicated the
general lay of the land for approximately 500' east and south of the site
and clearly show the drainage way that exists approximately 250' east of
this site's east property line. The dominant grade leads to this drainage
way and suggests that natural drainage leaves the site in a southwesterly
direction. The Alderwood soils are gravelly but shallow and drain
moderately well for their depth with infiltration rates ranging from 2.0 - 6.0
in/hr in the upper strata and less than 0.6 in/hr in the deeper strata.
5. Noise Production: Once construction is completed, there will be no
significant sources of noise at this site.
6. Significant Geological Features or Critical Areas: The portion of the
property located in the base of the "L" (southeast of property) where the
slope increases beyond 15% is classified as a "type one landslide hazard
area. A minimum buffer of 30' is required by the landsl'~~Bat~Q~--~~~_~~..
and a minimum of 50' setback is required by the storm I "I~rl!lis~~/Jio~ Wi [; rn)<)
Page 2 of 12 ~[~~p <~-;-~o~JllJ I
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regulations from a steep slope (40%+) which may include any buffers.
This site's slopes do not reach 40% and only the 30' buffer is required.
Note that the 30' buffer can be reduced to a minimum of 15' if supported
by the recommendation of a geo-technical analysis and report. A
geological site evaluation was prepared by NTl's staff Geologist, Bill
Payton, and is included in Appendix 2 for reference.
7. Description of General Vicinity: The general vicinity is characterized by
larger parcels (5+ acre) for secluded residential development. This
subdivision is a part of the overall Port Ludlow development.
IV. PERMANENT STORM WATER CONTROL PLAN
1. Developed Site Hydrology: The developed parcel will behave much like
the undeveloped parcel in that drainage will flow down hill to the southeast
following the full dispersion of all collected runoff.
2. Storm Water Treatment: The water from the composition roofs of the
three buildings will not require any treatment. The water from the gravel
driveway upstream of the home site will be controlled and diverted into the
area east of the driveway for sheet flow vegetation treatment and
adsorption in accordance with BMP T5.30which references BMP 5.10,
BMP 5.11 and BMP T5.12 (see appendix)
3. Performance Goals & Standards: Not applicable.
4. Flow Control System: None required since this is a rural residential site
with less than 10% total impervious surface.
5. Water Quality System: Full dispersion filtration in forest and/or native
vegetation per BMP T5.30
6. Conveyance System: The conveyance system(s) will vary across the
site depending upon where you are.
a.
The downhill driveway will have two dispersion units to serve its
approximately 475 lineal feet. periodic dispersion units. The
driveway will be sloped transversely at 2% in addition to its
longitudinal slope (2% - 6%) and a shallow ditch will be installed to
collect the runoff after 3500 SF of surface. This 3500 SF will be
piped to a dispersion unit of 3500/700 = 50' in length located such
that downstream building development is not in the direct path of
the resulting surface flow. Although the current plan is for a 15'
wide driveway, a recommendation has been madert9_-GO~id~r-a._,lZ~-;--~~_
facility to reduce the runoff. I rr)~ !L!;L a~_ u ~.7 ffio r ~..~;\ 1
lru L SEP - ;-;o4--j~1
JEFFEf1S0N COUN1Y I
DEPT. OF COMMUNI1Y DEVELOPMENT
Page 3 of 12
7.
8.
9.
10.
11.
12.
13.
b. The parking area from the last catch basin along to the parking
area and up to the two concrete pads will sheet flow to the
southeast and filter through the native vegetation. The 60' of width
will require 25' for the first 20' and 5' each for the second and third
20' for a total of 30' minimum distance; several times this distance
is available.
c. The roof, deck and concrete pads will be connected through a
series of down spouts, pipes and catch basins (with SC oil/water
separators) and transport the collected storm water to three (3)
dispersion units located downstream of the collected facilities. A
maximum of 3500 SF is allowed in each of these units. The area
calculations show that the two units serving the home, deck and
garage will serve slightly more area than this by approximately 100
SF, but, the 565 SF of deck will likely not be impervious and not
need to be included. The deck is included in these calculations to
provide a contingency.
d. Landscaped yard will filter through native vegetation. A maximum
of 150' of landscaping flow length is allowed. More space exists
than this maximum but less space will actually be required.
Source of Fill Material: Unknown
Soil Placement: Minimal import soil will be needed. The building site will
be "balanced" to the degree possible and landscaped areas may have
imported topsoil. The most critical soil to be placed is the backfill in utility
trenches which should be compacted to 95% of optimum and bedded with
sand per the manufacturer's recommendation.
Surfacing: The paving surfaces planned for this project include a gravel
access driveway and parking area and a concrete access pad for the
garage and for the shop. All other surfaces will be vegetative with the
exception of the home roof (composition) and two wooden decks.
Site Restoration: Disturbed areas will be either paved, roofed,
landscaped or restored to natural vegetation. Hydro-seeding of cut slopes
and fills as soon as possible is highly recommended even if the area is to
be fully restored to native vegetation at a later date
Operations Manuals: None required
Special Reports Generated: A site evaluation of the landslide hazard
area was made by Bill Payton, NTl's staff Geologist. His letterrr;.eRe~~~--=--
included in Appendix 2 of this report forreference < i I D) ,Jt rc; ~ u WiJ~ I
Other Permits or Approvals; Jefferson County Building per~'ni I SEP -] 200411
Page 4 of 12 I L~,".",_._..~_ ---.J
r:: . JEf-FEf1S0N COUNTY
_.0.~P1 OF COMMUNITY DEVELOPMI
V. CONSTRUCTION STORM WATER POLLUTION PREVENTION PLAN (SWPPP)
A. Required 12 Elements
1. Clearing Limits: No additional clearing is needed to construct the
home beyond the removal of site grasses for the site grading
necessary to construct the home and driveway. Construction limits
are shown on the plans and will be marked in the field with orange
construction and/or silt fencing to provide a strong visual reference
for equipment operators.
2. Construction Access: Construction access will be provided along
the driveway leading from Walden Lane. Walden Lane is a private
road and not subject to the County's regulation. However, site
access roads should be protected from the effects of mud being
tracked off-site on tires. This is, typically, vehicle accomplished
with a crushed rock or quarry spall paved section of driveway to
help knock any mud from the vehicle's tires. (see appendix for
DOE's recommended BMP)
3. Control Flow Rates: Full dispersion disposal requires no flow
control.
4. Install Sediment Controls: Erosion and sediment control facilities
should be among the first activities on site to ensure that a sudden
storm event will not catch the project by surprise.
5. Stabilize Soils: Stabilization of site soils can be accomplished by
minimizing the area of clearing to that area being actively worked
upon and by expediting the restoration process upon completion.
Proper scheduling of the tasks to be performed for sequence as
well as for time of year is essential.
To minimize the soil erosion forces of raindrop impact, flowing
water and wind erosion during construction, the contractor will
follow the exposed and unworked soil schedule set by DOE for all
soils on site. From October 1 through April 30, no soils shall
remain exposed and unworked for more than 2 days, and from May
1 to September 30, no soils shall remain exposed and unworked
for more than 7 days.
6.
All exposed soils shall be stabilized and hydroseeded or sodded
upon completion of the project. "~..,____.._.~_~
Protect Slopes: Slopes are, typically, protected by ) i1~stf~e ([; .} fi~=rr::
setbacks and by sediment control/filtering from silt fe ~e'p1]\1 straw . 111 !
U L/ SEP - 7 2004 IlL.!
Page 5 of 12 L__~. . r '''<'
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bale barriers or straw mulch. The use of silt fencing is
recommended for this project down stream of all construction
activities because the site impact is small and they can be easily
removed and recycled upon project completion.
7. Protect Drain Inlets: Drain inlets are, typically, protected in a
construction area by wrapping with silt fence filter material or by
lining the inside of the unit with filter fabric if a barrier fence is an
obstruction. Other techniques are available including gravel filters
which are equally as effective an provide the owner and/or
contractor with options.
8. Stabilize Channels and Outlets: The existing drainage path upon
this property beyond disturbed areas will be maintained during and
after construction with native vegetation.
9. Control Pollutants: All chemicals, liquid products, petroleum
products and non-inert wastes present on site shall be covered,
contained and protected from vandalism and handled in a manner
to minimize contamination of storm water.
To minimize pollutants generated by heavy equipment and
vehicles, all maintenance and repairs shall be conducted using spill
prevention measures such as drip pans.
10. Control De-Watering: If de-watering is required during
construction and the de-watering water has similar characteristics
to storm water runoff, it is to be directed across the nature
vegetative buffer at a minimal velocity.
If the de-watering water contains contaminants, the de-watering
water should be directed to a sanitary sewer as permitted by the
sewer utility.
11. Maintain Best Management Practices (BMPs): It is the
contractor's responsibility to maintain the temporary erosion and
sediment control measures and to install the permanent erosion
and sediment control measures set forth in this report and plan.
After construction is complete, maintenance of permanent erosion
and sediment control measures are the owner's responsibility.
All temporary erosion and sediment control measures shall be
removed within 30 days after final site stabilization is achieved or
as needed if longer.) If[":)"') -r~'~<(f;:;-~if~::,.'"'11~\\,-,:,-j-'rr~;-'r"':'::.:.~1,'
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Page 6 of 12 Ilflll SEP - 7 2004 Ill)')!
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JEHERSO!-J COUNTY
DEPT or COMMIItJI1Y [\1:\"", rom w..~
12. Manage the Project: Management of this project can best be
conducted in accordance with DOE if the guidelines set forth in this
report and plan are followed to ensure that the long term goals of
environmental protection and site stability are achieved.
B. Adjacent Areas
1. Adjacent Areas Description: The immediate adjacent area is the
downhill property to the southeast which contains the local
drainage route.
2. Downstream Drainage Path: The downstream drainage path is a
forested depression (see photo in appendix)
C. Environmentally Sensitive Areas: The portion of the property located in
the base of the "L" (southeast of property) where the slope increases
beyond 15% is classified as a "type one landslide hazard area. A
minimum buffer of 30' is required by the landslide designation and a
minimum of 50' setback is required by the storm water dispersion
regulations from a steep slope (40%+) which may include any buffers.
This site's slopes do not reach 40% and only the 30' buffer is required.
Note that the 30' buffer can be reduced to a minimum of 15' if supported
by the recommendation of a geo-technical analysis and report. A
geological site evaluation was prepared by NTl's staff Geologist, Bill
Payton, and is included in Appendix 2 for reference.
D. Erosion Problem Areas: The only potential erosion problem is the
relatively steep slope below the home site. Full dispersion techniques
should insure that the runoff is fully spread and adsorbed. It is prudent
site stewardship to periodically inspect the downstream conditions to
ensure that the facilities are working as designed and that the site remains
stable for the structures above.
E. Construction Phasing:
1. Construction Sequence: Specific plans for construction phasing
are not known. It is likely that the complete access will be
constructed along with the home and garage and the shop
deferred. Another possibility is to build the access and shop, live in
the shop during home/garage construction.
The plan developed is modular and can be adapted to cover any
phasing plan developed.
Page70f 12
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2. Phasing (if proposed): Not applicable at this ti
F.
Construction Schedule: None exists at this time
G. Financial/Ownership Responsibilities: The contractor is responsible
for the maintenance of all temporary drainage, erosion and sediment
control features during construction and, possibly, through the
construction warranty period. Following construction and final restoration,
the owner is responsible for all permanent drainage, erosion and sediment
control features.
H. Engineering Calculations
1. Sediment Ponds & Traps: Not applicable
2. Diversions: Not applicable
3. Waterways: Not applicable
4. Runoff/Storm Water Detention Calculations: None required
I. Monitoring Locations: Not applicable
VI. EROSION & SEDIMENT CONTROL PLAN REQUIREMENTS (a check list)
1. General
a.
b.
c.
2. Site Plan
a.
b.
c.
d.
e.
f.
g.
Vicinity Map: See narrative
Jefferson County Approval Block: On drawings
Erosion & Sediment Control Notes: On drawings
Legal Description of Property: See Appendix 2
North Arrow: On drawings
Boundary of Existing Vegetation: On drawings
Label Potential Erosion Problems: On drawings
Show FEMA Flood or Shorelines Management Boundaries (if
applicable): Not applicable
I~~~ ..._~~-~-._~'.....~- .....'~~~~CL~~~~_~____ _
Show Existing & Proposed Contours: On draWiHt:)) r.l~~~~~...J~_.n~\~~:j~~~'rrS]
Indicate Drainage Basins & Direction of Flow: ~I' fl~tawipg,$ 7 20r! I i.IJ i I
I J ll, j vEr"~ UI'I '.,..l..J. I I'
.- .4'1 '.~
Page 8 of 12 ! L_~,...,"....~..~_.:_~,,~.~._._~..__J I
JUFf:);SiJi'! COUN1Y J
L DEPT. OF COfY':iViUi~ny'~ DE~ELOfJM~!~
h. Label Final Grade Contours & Show Developed Condition
Drainage Basins: On drawings
I. Delineate Clearing & Grading Limits: On drawings, see narrative
j. Show Cut & Fill Slopes (Top & Bottom): See note on drawings
3. Conveyance Systems
a. Designate Swales, Interceptor Trenches & Ditches: On
drawings
b. Show Temporary & Permanent Pipes, Ditches & Trenches: On
drawings
c. Provide Minimum Slope & Cover Data For Pipes: On drawings
d. Show Grades, Dimensions & Direction of Slope: On drawings
e. Provide Details of By-passing Off-Site Runoff: Not applicable
f. Indicate Locations of Outlets & De-Watering Systems: Not
applicable
4. Location of Detention BMPs: Not applicable
5. Erosion & Sediment Control Facilities
a.
Dimensions of Traps, Ponds & Pipes: On drawing
b.
Dimensions of Pond Berms: Not applicable
c.
Pond Volume and Dimensions: Not applicable
d.
Typical Pond Cross-sections: Not applicable
e.
tails of Filter Facilities: Not applicable
f.
Outlet Stabilization Techniques: Not applicable
g.
Control I Restriction Details: Not applicable
h.
Mulch Specifications & Check Dam Details:!~r:.:::\~-~:;~~; .,~~~-.,.~.,--~"-.-._--.--."
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Rock Specifications for Check Dams: Not a :~tf9~5Te~:'."""
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Check Dam Spacing: Not applicable " "I '
Page 9 of 12
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k. Front & Side Cross-sections of Check Dams: Not applicable
I. Locations for Silt Fencing: On drawings
m. Construction Entrance Details: On drawings
6. Detailed Drawings: See the end of the narrative section of this report and
BMP details in Appendix 3
7. Other Pollutant BMPs: A variety of BMPs apply to this project including
construction barrier fence, silt fence, catch basin protection, straw bales for
ditches, construction access and full dispersion techniques for both roofs and
driveways. All BMPs are detailed Appendix 3.
8. Monitoring Locations: Not applicable
VII. METHODOLOGY
As of December 20, 2002, Jefferson County requires the use of the Department of
Ecology (DOE) August 2001 Storm Water Management Manual for Western
Washington. Based an analysis of this site's characteristics made by Jefferson County
and noted in their July 2, 2004 letter, has been determined that a "medium" plan is
needed where the first five of the ten minimum requirements for new and replaced
impervious surfaces apply to this property.
. ~/.
To support runoff volume amounts for energy dissipation method determination, an
analysis was performed using the SBUH technique as allowed by the DOE 2001
manual. This exercise was performed to estimate the amount of runoff in cfs produced
by the 15' driveway per 100' length (0.02 cfs) and 200' length (0.04 cfs) and to estimate
the amount of runoff produced by the roof/deck/concrete pad system per 1500 SF unit
(0.03 cfs).
VIII. CONCLUSIONS
The development and implementation of the storm water drainage system and erosion
and sediment control plan are both a temporary and permanent part of the construction
phase and the long term maintenance of the completed project.
The first step in implementing this plan is readying the site in accordance with DOE
guidelines. A temporary construction fence shall be placed marking the clearing limits,
and trees within the clearing limits that are to remain shall be clearly marlre:Gi..n~S-i':\E-f'l~-;,'~:-"~'-~~"-::::"~'--:::--'
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for locati?n of fence. In addition prior to sta~ing land disturbing activities,! !~})litlf~n~~..~~'-_l!....~'l_~.X;'.II'\
shall be I~stalled down sl~pe of all constru.ctlon and a quarry spall or cru1~~Pi f?ck 1- i i
access dnveway shall be Installed at the site entrance. The 50 foot long'lr)5L~ldeSEP = 7 2004 IlL
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: Jl:iFEHSIJN COUNTl
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Page100f 12
..,--
access driveway should provide the necessary debris and sediment trap for protecting
the private roadway from the construction equipment leaving the site. It is the
contractor's responsibility to maintain a clean roadway in accordance with the county
Public Works Department regulations. The standard silt fence, catch basin filter and
access driveway details are provided with the drawings at the end of this section of this
document and again in this document's Appendix 3 in full BMP format.
The next steps are installation and minimizing erosion caused by the construction. This
can be minimized by sustaining the access driveway, silt fence, natural vegetative
buffer, limiting the exposure of soils and installing check dams, as needed, in sloped
trenches. The drainage system is limited to collection and disposal, no detention or
treatment is required. The system consists of a 12" ADS or equivalent traffic bearing
catch basins in the concrete pads for the garage and shop, WSDOT type 1 catch
basins along the driveway entrance, gutters and downspouts to collect roof runoff,
underground 6" diameter ADS or equivalent PVC or HOPE pipe collection lines and a
discharge via dispersion trenches meeting the BMP T5.1 0 and BMP T5.12 designs in
Appendix 3. Since grading of the site will cause runoff to collect in the drainage
system, filter fabric should be placed over or around all drains and/or catch basins until
the driveway is stabilized.
The final steps are stabilizing the site and long term maintenance. Before leaving the
site the contractor is responsible for stabilizing all soils disturbed during construction,
hydro-seeding or landscaping exposed soils. All temporary erosion and sediment
control measures shall be removed from the site and the drainage system shall be
cleaned of debris and sediment to allow runoff to flow freely. Long term maintenance of
the system is the owner's responsibility. All ditches, drains, catch basins and down
spouts should be checked regularly for debris and/or blockages and cleaned out if
necessary. Long term erosion control on the site can be controlled by minimizing
exposed soils and maintaining a vegetative buffer between this property and its
neighbors!. The site geo-tech report has specific recommendations for the long term
stability of the bluff and is included in the appendix for reference.
IX. LIMITATIONS
This report has been prepared for the exclusive use of Todd and Cindy Colebrook for
their proposed construction of a private home. The recommendations in the report
apply only to the property that was examined and they are not applicable to other
locations. The investigation and recommendations contained in this report are based
upon site conditions as they existed at the time of our site inspections. During
construction, if subsurface or other conditions are discovered that are significantly
different from those described in the report, NTI should be advised at once so that we
can review the conditions and reconsider our recommendations, where necessary.
Unanticipated soil conditions are commonly encountered on const .~. '~Frfil \VI. [f \~
especially when the topography has been altered years ago. Sue . _ e~~__u... Ll ~
Page 11 of 12 nJ SEP -- 7 20011 ...J
L___.._____-
JEFFERSOI~ COUNTY
nFPT OF CmJJMU:~:TY DEVELOPMENT
conditions frequently require that additional expenditures be made to attain a properly
constructed project. We recommend that a contingency be established in the project
budget and schedule to cover unexpected conditions.
Within the limitations of scope, schedule and budget, our services have been executed
in accordance with generally accepted professional engineering principles and practice.
This warranty is in lieu of all others, either expressed or implied.
Sincerely
NTI Engineering & Land Surveying
Robert A. Leach, P.E.
Principal Engineer
08-23-04
attachment: appendicies
EXPIRES
12/30/2004
E:\Colebrook\Colebrook drainage plan 2.wpd
Page 12 of 12
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717 SOUTH PEABODY. PORT ANGELES, WASHINGTON 98362. (360) 452.8491
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NT I 717 SOUTH PEABODY. PORT ANGELES. WASHINGTON 98362. (360) 452-8491
ONE IJ BAR HOOP FOR 6"
TWO J BAR HOOP FOR 12"
FRAME AND VANED GRA TE
(SEE STANDARD PLAN
FOR DETAIL)
12"
RISER SECTION
(RECTANGULAR ADJUSTMENT
SECTION)
6" REDUCING SECTION
#J BAR EACH WAY
,
~
~
PRECAST BASE SECTION
(MEASUREMENT A T THE TOP)
OF THE BASE
#J BAR EACH CORNER
#J BAR EACH SIDE
SCALE:
DRAWN BY:
PROJECT: DRA 1 N 1\6 f plJ\p
FOR: -rODD (OLEBROo
FINAL REVIEW: Robert A. Leach, PE
SHEET 3 or 10
DATE:
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CA TCH ~~~~CAL'!PE 1 tfi\l_<~f:~-:___J1l
JLr-f-l:f~SOr~ COUN-IY
l_;.~._.:._~__~:.~.":~~~i~',i I '( UiVi:UWMHn
ft NORTHWESTERN TERRITORlrS",-'-lflc-.~
Engineers - Land Surveyors - Geologists
. Construction Inspection - Materials Testing
NT I 717 SOUTH PEABODY, PORT ANGELES. WASHINGTON 98362. (360) 452.8491
G: \ Prod \ DelaH. \Munic;pol\ NTI\REPORT DETAlLS\
PLOTTED:
iD NORTHWf:STERN TERRITORIES. INC. 2004
~~
4-" pEri piP3
-j Iii' . '3lf"'!iashed rock
TRENCH X-SECTION
flITS
slcpe -
:3 me<. II catch basin or '1arel clrai n
! -
2' ~; 10'
IfNEi trench-::s
:5 700 sq. ft.
:> 700 sq. ft.
Typ~ I CB
/ st3Jlchn:J
di3p~r:3ion tn:.nch
wi n:rtct-ed '=-lmre bo&d
lerryh I [j pEr 700 sq ft
of mof atea.
Figure 5.1 Typical Dispersion Trench
, ~ S~P~. :04~1~
I f
L__~_.~.~__~___ J
J FH Hi eJ) N (' () ;I"':'Y~'
DEPT OF f~)~~;/"~~,;il:ri'~';"~!.OPMENT
PLAN VIEW OF ROOF
NTS
G: \Prod\Oeloils \Municipol\NTI\REPORT OETAlLS\
PLOTTED:
lid NORTHWESTERN TERRITORIES. INC. 2004
SCALE: DATE:
DRAWN BY:
PROJECT: D RA I fJ " G t Pl11 f-I
FOR: TOb D COLE BROOK
FINAL REVIEW: Roberl A. Leach, P.E.
SHEET 1 OF Ie,
fj NORTHWESTERN TERRITORIES, INC.
Engineers - Land Surveyors -- Geologists
Construction Inspection - Materials Testing
NTI
717 SOUTH PEABODY, PORT ANGELES, WASHINGTON 98362. (360) 452-8491
noo:hed
gra::le board
2"x 2' nm) tel>
1S"0.C.
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p'pe 0 [!
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'7" ~ cean ou~w~ flDm pipe
t
........
inflU2nl pipe (ma:x: desgn
tbw ~. 0.5 G FS per trenc h)
PLAN
NTS
9i:>h8.nired bolts \
x 15% B"R'\fcr 11m' ccrrtro['wcler q.1Blily
treatrrert in rural areas.
SECTION A-A
NTS
[5) liE CG [i; U[rrrr~1
I Ii j I I: i
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DEPl or CO\!,r,~l';'J:iY iY\TlCH vi[in-
flON 10 second
dispersal ~rero::h
it necessary
t
....-
.
fb.vtootrer
brar,)hing CB's
as necessary
I 18' 0.(; I
-~~~ --i 4-2"
T- .----~/"':.'---':t:
v~
2" grade
board rc.~tes
NOTES:
i. This tremh shan b: construct:d 'SO
as b prevent point discha'ge and.or
elOsbn.
2. Trencres n"\=o/ be pieced no cb=~r
than 50 fee~ bone an:ltter. (100 feet
abrg fbwlir.:)
3. Trench ard grad; beaId mlJst be
P-~1. Align to to/bo.... cori1oursoi si~.
4. SuProrl post spacing ilS required by
soil oorditbns to ensure gl<l.de boOfd
remains level.
Figure 5.2 Standard Dispersion Trench with Notched Grade Board
G: \Prod\Oelo;ls \Mun;c;pal\Nn\REPORT OETAlLS\
PLOTTED:
lid NORTHWESTERN TERRITORIES. INC. 2004
SCAlE: DATE:
DRAWN BY:
PROJECT: DRA uJ /\ G ~ pLl1 W
FOR: TOCt> cOU:. BRC\OK
FINAL REVIEW: Robert A. Leach, P.E.
SHEET 5 OF /b
fj NORTHWESTERN TERRITORIES, INC.
EngineeTs - Land SurveyoTs - Geologists
Construction Inspection - MateTials Testing
NTI
717 SOUTH PEABODY, PORT ANGELES. WASHINGTON 98362. (360) 452.8491
REPLACE WITH EXISTING SURFACE
COVER OR REPAIR W/ CDF BACKFILL
~) [E_~]fif)r ~l
I' II
.J j SEP --. 7 200!!. I!
r , n
L_.--:;:;:"::,:,._,,: ._--~-~...~_J
. .JllrUiSON CUUNTY
..Q~.c'~:.2.~.~!?~~)~~~~l!!l.i~~~~:~r~~!.'!!.
RESEED, REPLACE EXISTING ~ - -
SOD, OR RE-LANDSCAPE AS
NECESSARY
ASPHALT OR GRAVEL
AS APPROPRIA TE
.,.c- .
.; ~ . ///g
:::~ 1I1t-:/fl,t' =//// .
:. . !(/liSi: m ~
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TRACER TAPE WITH
WIRE TRACER
<:
~
COMPACT SELECT SITE BACKFILL
(SEE NOTE BELOW)
..;.:..:..".:.
.
a
"1
# 12 DETECTOR WIRE AND
BL UE TAPE @ WA TERLlNES
BRING UP INTO VAL VE BOXES
. ...;:... :wi;;: ~. ,.
>j/!i~j!l: >:.
!/I!!!IJ.'I.~ fA t.:>
PIPE BEDDING PER WSDOT/APWA
9-03.16 FOR FLEX AND 9-03.15
FOR RIGID PIPE
(Q
.
"I'
SEWER/WA TER PIPE PER PLANS
24" MAX.
NOTE:
BACKFILL TO BE COMPACTED TO 95% MODIFIED PROCTOR DENSITY IN
12" LIFTS IN ALL AREAS REQUIRING PAVING. COMPACTION SHALL BE 90
% ELSEWHERE.
TYPICAL PIPE TRENCH DETAIL
NO SCALE
G: \ Prod \ De/oils \Municipal\ NTI\ REPORT DETAlLS\
PLDTrED:
10 NORTHWESTERN TERRITORIES. INC. 2004
SCALE: NOT TO SCALE DATE:
DRAWN BY:
PROJECT: D RA I JAG E ?lh"j
FOR: TOi)~) e.o LE ?"PJ)OI<,
FINAL REVIEW: Robert A. Leach, PE
SHEET ~ OF I 0
~ NORTHWESTERN TERRITORIES, INC.
Engineers - Land Surveyors - Geologists
Construction Inspection - Materials Testing
NTI
717 SOUTH PEABODY, PORT ANGELES, WASHINGTON 98362. (36G) 452-8491
[E T~ LE ~J~ \VI IE ---
-"---=""-'~~~O=-----'~_~~T
SEP ", 7 2004
l__._...~.~..~_._~
JEfTEfiSON COWi1Y
DEPT. OF COMf"'1UNI1Y Di:VEl.OPMENT
------------~,~-~--
NOTE:
PROVIDE A CLEAN, HARD SURFACE TO
ELlMINA TE TRACKING OF SOIL ONTO STREET.
SURFACE MATERIALS MAY INCLUDE QUARRY
SPALLS, CRUSHED ROCK, OR OTHER
NON-SOIL OR NON-SOUND MATERIALS.
/
/
,/
/
,/ ~OP'
~\~G
/<(,-j.\J
,/
4" TO 8" QUARRY SPALLS
OR APPROVED EQUAL
MAINTENANCE:
THE ENTRANCE SHALL BE MAINTAINED IN A CONDITION WHICH WILL PREVENT
TRACKING OR FLOW OF MUD ONTO PUBLIC RIGHTS-OF-WAY. THIS MAY REQUIRE
PERIODIC TOP DRESSING WITH 2-INCH STONE OR OTHER APPROVED MATERIAL AS
CONDITIONS DEMAND, AND REPAIR AND/OR CLEANOUT OF ANY STRUCTURES USED
TO TRAP SEDIMENT. ALL MATERIALS SPILLED, DROPPED, WASHED, OR TRACKED
FROM VEHICLES ONTO ROADWA YS OR INTO STORM DRAINS MUST BE REMOVED
IMMEDIA TEL Y.
PROVIDE FULL WIDTH
OF INGRESS/EGRESS
AREA
SITE ACCESS DETAIL
G: \ Prod\ De/oils \ Mun;c;pol\ N17\ REPORT OErAlLS\ SlrtAGGESS.OWG
PLD rrED:
q;) NORTHWESTERN TERRITORIES. INC. 2004
SCALE: NOT TO SCALE DATE:
DRAWN BY:
PROJECT: 0 R fll [.J 1\ G t PLI\1J
FOR: 10DP CuLE- ,R\:lOK
FINAL REVIEW: Robert A. Leach, PE
SHEET 7 OF 10
O NORTHWESTERN TERRITORIES, INC.
[ngineers - Land Surveyors - Geologists
Construction Inspection - Materials Testing
NTI
717 SOUTH PEABODY, PORT ANGELES, WASHINGTON 98382. (380) 452-8491
STAKES ------......
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INLET FIL TER DETAIL
NOT TO SCALE
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SCALE: NOT TO SCALE DATE:
DRAWN BY:
PROJECT: 0 1< f\ ! rJ A., G 1-::: PL'V}
FOR: TOD D COL", 1::00\<
FINAL REVIEW: Robert A. Leach, P.E.
SHEET 8 OF ID
ft NORTHWESTERN TERRITORIES, INC.
Engineers - Land Surveyors - Geologists
Construction Inspection - Materials Testing
NTI
717 SOUTH PEABODY, PORT ANGELES, WASHINGTON 98362, (360) 452-8491
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SCALE: NOT TO SCALE DATE:
DRAWN BY:
PROJECT: D R A I 10 ""G E- f.; Lf') iJ
FOR: \0 DD CO\...L 81->00\<
FINAL REVIEW: Robert A. Leach, P.E.
SHEET q OF 10
O NORTHWESTERN TERRITORIES, INC.
Engineers - Land Surveyors - Geologists
Construction Inspection- Materials Testing
NTI
717 SOUTH PEABODY, PORT ANGELES. WASHINGTON 98362, (360) 452-8491
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SILTATION FENCE STANDARD NOTES
,. THE FlL TER FABRIC SHALL BE PURCHASED IN A CONTINUOUS ROLL
CUT TO THE LENGTH OF THE BARRIER TO AVOID USE OF JOINTS.
WHEN JOINTS ARE NECESSARY, FlL TER CLOTH SHALL BE SPLICED
TOGUHER ONLY AT A SUPPORT POST, WITH A MINIMUM 6 INCH
OVERLAP, AND BOTH ENDS SECUREL Y FASTENED TO THE POST.
2. THE FILTER FABRIC SHALL BE INSTALLED TO FOLLOW THE CONTOURS
(WHERE FEASIBLE). THE FENCE POSTS SHALL BE SPACED A MAXIMUM
OF 5 FEU APART AND DRIVEN SECUREL Y INTO THE GROUND (MINIMUM
OF 18 INCHES).
3. A TRENCH SHALL BE EXCA VA TED, ROUGHL Y 6 INCHES WIDE AND 6
INCHES DEEP, UPSLOPE AND ADJACENT TO THE WOOD POST TO
ALLOW THE FILTER FABRIC TO BE BURIED.
4. SILTATION FENCES SHALL BE INSPECTED IMMEDIATELY AFTER EACH
RAINFALL AND AT LEAST DAILY DURING PROLONGED RAINFALL. ANY
REQUIRED REPAIRS SHALL BE MADE IMMEDIA TEL Y.
5. SILTATION FENCES SHALL BE REMOVED WHEN THEY HAVE SERVED
THEIR USEFUL PURPOSE, BUT NOT BEFORE THE UPSLOPE AREA HAS
BEEN PERMANENTL Y STABILIZED.
STIL FENCE DETAIL
NOT TO SCALE
G: \ Prod\Delo;!s \ Mun;c;pol\ NTI\ Reporl delo;ls \ C8 -FF.dw'l
PLOrTEO:
<Id NORrHWf:STERN rERRlroRIES. INC. 2004
SCALE: NOT TO SCALEI DATE:
DRAWN BY:
PROJECT: oRA [rJ PI (:> E fLl\lJ
FOR: TO 1)\) CO LE B1?OO 1<
FINAL REVIEW: Robert A. Leach, PE
SHEET 10 OF 10
fJ NORTHWESTERN TERRITORIES, INC.
Engineers - Land Surveyors - Geologists
Construction Inspection - Materials Testing
NTI
717 SOUTH PEABODY, PORT ANGELES, WASHINGTON 98362, (360) 452-8491
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Appendices
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APPENDIX 1 - Jefferson County Strom Water Forms & Communications
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DE, T. qr COfl'ir"lili~.1~!,~:i:'l.i~~i!~~r1.d
JEFFERSON COUNTY
DEPARTMENT OF COMMUNITY DEVELOPMENT
621 Sheridan Street
Port Townsend, WA 98368
AI Scalf, Director
July 2, 2004
TODD N COLEBROOK
CYNTHIA F COLEBROOK
21 BARQUE LN
PORT LUDLOW WA 98365-9729
RE: SITE ADDRESS: WALDEN LN
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MLA #: MLA04-00401
CASE #: BLD04-00446
Dear TODD N COLEBROOK:
The Department of Community Development is in the process of reviewing your application. The
following information is needed to continue review of your project.
Consistent with the Department of Ecology 2001 Stormwater Management Manual, the proposal is
subject to a Medium Project stormwater plan due to the proposed 6141 square feet of impervious
surface and 7700 square feet of land disturbing activity.
Enclosed is a Stormwater Site Plan. Please fill it out completely and submit original to me for
review.
1 can be reached at 360-379-4457 if you have any questions or concerns.
Please submit the above information to the Department of Community Development by
September 30,2004. Pursuant to Unified Development Code Section 8.2.3.c and f., if the
applicant refuses to submit the additional information or does not request additional time to submit
the
required information within the ninety (90) calendar day period, the application will be mnsidered
abandoned and therefore withdrawn and the applicant shall forfeit the application fee. The
Department of Community Development shall not be responsible for notifying the applicant of an
impending expiration.
c: File
LINDBERG & SMITH ARCHITECTS
Building Permits/Inspections
Development Review Division
Long Range Planning
FAX: (360) 379-4451
(360) 379-4450
JEFFERSON COUNTY
DEPARTMENT OF COMMUNITY DEVELOPMENT
621 Sheridan Street
Port Townsend, WA 98368
AI Scalf, Director
July 2, 2004
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I <r ~ J[?TE~SON'COUN1Y
CASE #: MLA04-G0401 L.~~:.~~9L~:.Q!~~~~ifY DfVEl.OPMENT
LOCATION: Parcel Number 821 085002 Port Ludlow No 6, Lot 2, in Section 8, Township 28,
Range 01 East, WM, Located on Walden Ln, Port Ludlow, WA 98365-9729
TODD N COLEBROOK
CYNTHIA F COLEBROOK
21 BARQUE LN
PORT LUDLOW W A 98365-9729
RE:
Dear TODD N COLEBROOK:
Jefferson County Department of Community Development staff have received the
application materials for the above project proposal and have assigned your case to:
Michelle Farfan
(360) 379-4457
E-mail: mfarfan@Co.jefferson.wa.us
Fax: (360) 379-4473
Please direct all questions to Michelle Farfan and refer to MLA04-00401. If you
need to speak with Michelle Farfan in person, please call to schedule an appointment in
order to ensure availability.
Review times vary depending on the type of application and how complete the
application is upon submittal. For more information, please visit the Jefferson County
Department of Community Development web page at
www.co.iefferson.wa.us/commdevelopment/.
Thank you.
mmunity Development Staff
c: File
LINDBERG & SMITH ARCHITECTS 319 S PEABODY ST STE B PORT ANGELES WA 98362
. . LIND-BERG. & SMITH ARCHITECTS 31.9 S PEABODY ST SIE B PORI fflGELES WA 9836?
BUilding fJermrts/ Inspections uevelopment Heview ulvision Long Range Planning
(360) 379-4450
FAX: (360) 379-4451
JEFFERSON COUNTY
DEPARTMENT OF COMMUNITY DEVELOPMENT
~lEa:IEOWIE
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621 Sheridan Street. Port Townsend' Washington 98368
360/379-4450.360/379-4451 Fax
http://wwvv.co.jefferson.wa.us/commdevelopment/
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STORMWATER SITE PLAN SUBMITTAL TEMPLATE
I MLA# N'\LALl4 '~l PROJECT/APPLlCANTNAME: ~ Todd Coltb[QQJ(
Please answer all of the following questions to the best of your ability. Where the question calls for depiction on a site map, the
applicant may choose to either incorporate the elements into the general plot plan for the Master Land Use Application or to submit a
separate stonnwater site plan map.
Project Overview
1. Describe the proposed developed conditions of the site. Indicate position and relative size of proposed improvements on the
site map.
..
Existing Conditions Summary
2. Describe the existing topography. Indicate contours on the site map.
3. Describe the existing vegetation. Indicate native vegetation areas on the site map.
4. Describe the existing soils. Indicate soil type on the site map.
.
5. Describe the existing site hydrology (Le., drainage; behavior of water on the site-above, below, and on the ground). Indicate
existing stonnwater drainage to and from the site on the site map. Depict separate drainage basins on the site map, if
applicable, and indicate acreage of each.
6. Describe any excess levels of noise generated by the proposed use or activity:
slormwnl&' aHa plonl&rrplale - '0_. Hl'll2003
5
Project Overview
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JEFFEflSON COUNTY
DEPT. OF corv1MUi~ir::~)_i:~~~~~pr,.~[~~~~
Proposal (MLA #: MLA04-00401; CASE #: BLD04-00446): This project
proposes the construction of a single family home upon an "L" shaped wooded
5.1 acre site (221,067 sf). The home and ancillary buildings will have
approximately 7409 sf of roof area (home, garage and shop) with 565 sf wood
deck at the house, approximately 1197 net sf in concrete aprons for the garage
and shop (note that approximately 171 sf is under the structure's eave line) and
approximately 12,900 sf of 15' wide gravel driveway and parking (recommend a
narrower, 12' wide drive where possible). A small yard area of approximately
1065 sf is envisioned along with an allocation of about 500 sf of site disturbance
for the installation of a well and sewer line. The total disturbed area will be
approximately 23,636 sf and the total impervious surface (post restoration) will
be 7409 + 12,900 +1200 +65 = 22,071 = 9.98% of the site.
General Project Information
1.
A preliminary analysis of this proposal by Jefferson County (July 2, 2004 -see
appendix) has indicated that a "Medium Project Storm Water Plan" is required.
With the total site impervious area being less than 10%, full dispersion disposal
is allowed without triggering flow control facility requirements. This will be
accomplished by use of BMP T5.30 (dispersion) in accordance with BMPs T5.1 0,
T5.11 and T5.12.
Drainage dispersion per BMP T5.1 0 will be used for the roof/deck/cone pad
drainage and BMP T5.12 will be used for the gravel driveway drainage.
Existing Conditions Summary
2. Existing Topography: The property slopes to the south and has a slight ridge
line running in a north south direction along the west property which causes the
contours to be curved convex to the south and to shed water both easterly and
westerly from the crown of the ridge (westerly flow is on the adjacent property
with little or no runoff from this property). The slopes along the N-S ridge line
begin at about 2% at the north for about 1/4 of the site and then moderate to
about 5% - 6% for the majority of the site (through the building zone). The E-W
slope from the ridge line is approximately 5% for the majority of the site until
reaching the base of the site's "L" shape when the slope steepens and varies
from approximately 15% to over 25% indicating the change in soil type from AIC
to AID. No off-site runoff enters this property from the east, west or south and
the Walden Lane access intercepts runoff from the north.
3. Existing Vegetation: The site is partially treed per the County's web site photo
of 2000 (see Appendix 2) and the Architect's site plan shows a tree line to the
southwest of the home site. On-site observations reveal that the shallow slope
Page 1 of 9
upland area is predominantly grass with treed areas while the steeper slope
downhill areas is treed. The Jefferson County Drainage Regulations (DOE 2001)
require that the storm drainage plan consider the site to be vegetated as it was
before European contact (early-mid 1800s) which would, likely, have been totally
forested. All calculations for project related disturbances have been made with a
forested condition. No significant removal of trees is required for this home's
construction.
4.
Existing Soils: The site soils are mapped by the USDA Soil Conservation
Service (SCS) at AIC or Alderwood Gravelly, Sandy, Loam (0% - 15% slope)
which is a hydrologic type "C" family of soils. Further inspection resulting from an
analysis of the site topographic information obtained from the Jefferson County
web site indicates that portion of the site are AID or Alderwood Gravelly, Sandy,
Loam (15% - 30% slope). This is significant only in that the potential for erosion
is greater in the AID soils than in the AIC soils. All work on-site is confined to the
AIC soil area and 50' setbacks for storm drainage dispersion facilities is required
by BMP T5.10, T5.11, T5.12 and T5.30
5.
Existing Site Hydrology: A site contour map and a regional contour map
obtained from the Jefferson County web site (see appendix) indicated the
general lay of the land for approximately 500' east and south of the site and
clearly show the drainage way that exists approximately 250' east of this site's
east property line. The dominant grade leads to this drainage way and suggests
that natural drainage leaves the site in a southwesterly direction. The Alderwood
soils are gravelly but shallow and drain moderately well for their depth with
infiltration rates ranging from 2.0 - 6.0 in/hr in the upper strata and less than 0.6
in/hr in the deeper strata.
6.
Noise Production: Once construction is completed, there will be no significant
sources of noise at this site.
7.
Significant Geological Features or Critical Areas: The portion of the property
located in the base of the "L" (southeast of property) where the slope increases
beyond 15% is classified as a "type one landslide hazard area. A minimum
buffer of 30' is required by the landslide designation and a minimum of 50'
setback is required by the storm water dispersion regulations from a steep slope
(40%+) which may include any buffers. This site's slopes do not reach 40% and
only the 30' buffer is required. Note that the 30' buffer can be reduced to a
minimum of 15' if supported by the recommendation of a geo-technical analysis
and report. A geological site evaluation was prepared by NTI's staff Geologist,
Bill Payton, and is included in Appendix 2 for reference.
8.
Description of General Vicinity: The general vicinity is characterized by larger
parcels (5+ acre) for secluded residential development. ThiS"'~~~: d~S}. /.~: f1..~[~-'tt.-..'jcf1.-.a....,.lr. ...-.-[i~~I'[-~:"-
of the overall Port Ludlow development IJ lhc<.lc~,,-~~.'.'.~.~. fli
U uL S!:[1 - i iilu4 1.0
-~-------1
JEFFEnSON COUN'lY
DEPT. OF COMMUNITY DEVELOPMENT
Page 2 of 9
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Permanent Storm Water Control Plan L, ____ :
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9. Developed Site Hydrology: The developed parcel will behave muchlike-the " i
undeveloped parcel in that drainage will flow down hill to the southeast following
the full dispersion of all collected runoff.
10. Storm Water Treatment: The water from the composition roofs of the three
buildings will not require any treatment. The water from the gravel driveway
upstream of the home site will be controlled and diverted into the area east of the
driveway for sheet flow vegetation treatment and adsorption in accordance with
BMP T5.30 which references BMP 5.10, BMP 5.11 and BMP T5.12.
11. Performance Goals & Standards: Not applicable.
12. Flow Control System: None required since this is a rural residential site with
less than 10% total impervious surface
13. Water Quality System: Full dispersion filtration in forest and/or native
vegetation per BMP T5.30
14. Conveyance System: The conveyance system(s) will vary across the site
depending upon where you are.
a.
The downhill driveway will have two dispersion units to serve its
approximately 475 lineal feet. periodic dispersion units. The
driveway will be sloped transversely at 2% in addition to its
longitudinal slope (2% - 6%) and a shallow ditch will be installed to
collect the runoff after 3500 SF of surface. This 3500 SF will be
piped to a dispersion unit of 3500/700 = 50' in length located such
that downstream building development is not in the direct path of
the resulting surface flow. Although the current plan is for a 15'
wide driveway, a recommendation has been made to consider a 12'
facility to reduce the runoff.
., ,./
b. The parking area from the last catch basin along to the parking
area and up to the two concrete pads will sheet flow to the
southeast and filter through the native vegetation. The 60' of width
will require 25' for the first 20' and 5' each for the second and third
20' for a total of 30' minimum distance; several times this distance
is available.
c. The roof, deck and concrete pads will be connected through a
series of down spouts, pipes and catch basins (with SC oil/water
separators) and transport the collected storm water to three (3)
dispersion units located downstream of the collected facilities. A
maximum of 3500 SF is allowed in each of these units. The area
calculations show that the two units serving the home, deck and
Page 3 of 9
garage will seNe slightly more area than this by approximately 100
SF, but, the 565 SF of deck will likely not be impervious and not
need to be included. The deck is included in these calculations to
provide a contingency.
d. Landscaped yard will filter through native vegetation. A maximum
of 150' of landscaping flow length is allowed. More space exists
than this maximum but less space will actually be required.
15. Source of Fill Material: Unknown
16. Soil Placement: Minimal import soil will be needed. The building site will be
"balanced" to the degree possible and landscaped areas may have imported
topsoil. The most critical soil to be placed is the backfill in utility trenches which
should be compacted to 95% of optimum and bedded with sand per the
manufacturer's recommendation.
17. Surfacing: The paving surfaces planned for this project include a gravel access
driveway and parking area and a concrete access pad for the garage and for the
shop. All other surfaces will be vegetative with the exception of the home roof
(composition) and two wooden decks.
18. Site Restoration: Disturbed areas will be either paved, roofed, landscaped or
restored to natural vegetation. Hydro-seeding of cut slopes and fills as soon as
possible is highly recommended even if the area is to be fully restored to native
vegetation at a later date
19. Operations Manuals: None required
20. Special Reports Generated: None
21. Other Permits or Approvals: Jefferson County Building Permit
Construction Storm Water Pollution Prevention Plan (SWPPP)
Section I - Construction SWPPP Narrative
1. Required 12 Elements
1. Clearing Limits: No additional clearing is needed to construct the home
beyond the removal of site grasses for the site grading necessary to
construct the home and driveway. Construction limits are shown on the
plan~ and will ~e marked in t~e field with orange co.nst ~:fe~aAq+e~m'~~\'t7'f;-'~i;:;.:~:;'l
fencing to provide a strong visual reference for equlpm ~j)~ ~r~r~; U \\/ .h~ II i.,...\.... '.'.
Page 4 of 9 ~l8_~~7-~0~~-1~!\
____ _)Ef~~~.~9,t,L~fllLt~.l'r M. "'''T I
2. Construction Access: Construction access will be provided along the
driveway leading from Walden Lane. Walden Lane is a private road and
not subject to the County's regulation. However, site access roads should
be protected from the effects of mud being tracked off-site on tires. This
is, typically, vehicle accomplished with a crushed rock or quarry spall
paved section of driveway to help knock any mud from the vehicle's tires.
(see appendix for DOE's recommended BMP)
3. Control Flow Rates: Full dispersion disposal requires no flow control.
4. Install Sediment Controls: Erosion and sediment control facilities
should be among the first activities on site to ensure that a sudden storm
event will not catch the project by surprise.
5. Stabilize Soils: Stabilization of site soils can be accomplished by
minimizing the area of clearing to that area being actively worked upon
and by expediting the restoration process upon completion. Proper
scheduling of the tasks to be performed for sequence as well as for time
of year is essential.
To minimize the soil erosion forces of raindrop impact, flowing water and
wind erosion during construction, the contractor will follow the exposed
and unworked soil schedule set by DOE for all soils on site. From
October 1 through April 30, no soils shall remain exposed and unworked
for more than 2 days, and from May 1 to September 30, no soils shall
remain exposed and unworked for more than 7 days.
All exposed soils shall be stabilized and hydroseeded or sodded upon
completion of the project.
6. Protect Slopes: Slopes are, typically, protected by vegetative setbacks
and by sediment control/filtering from silt fences, straw bale barriers or
straw mulch. The use of silt fencing is recommended for this project down
stream of all construction activities because the site impact is small and
they can be easily removed and recycled upon project completion. All
sloped trenches shall include check dams placed at 50 foot intervals
7. Protect Drain Inlets: Drain inlets are, typically, protected in a
construction area by wrapping with silt fence filter material or by lining the
inside of the unit with filter fabric if a barrier fence is an obstruction. Other
techniques are available including gravel filters which are equally as
effective an provide the owner and/or contractor with options.
8. Stabilize Channels and Outlets: The existing drainage ~.9Jb__ld_QQllJb_i~__~_~~~x__
property ?eyo~d dist~rbed area~ will be maintained during 'i'~QJi~ f~e~~ lG II WI It:
constructIon with natIve vegetation. b>~[~-'-' ~_d__~.__._... - i
lnl SEP ~ 7 200~- !
Page 5 of 9 L__~~__~_._J
JEFFEfiSON cournv
OEPT. OF COMMUNI1Y DEVELOPMHFr
9.
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Control ~ollutants: All chemical~. liquid products, JI:trolbu.1f1.['[f.7f.l:~..,ttt~iN"r~"-".J
and non-Inert wastes present on sIte shall be covereql.1'~~hr~If-l5l9!9.~'di
protected from vandalism and handled in a manner to minimize -.. "'--'-"~"-_.
contamination of storm water.
To minimize pollutants generated by heavy equipment and vehicles, all
maintenance and repairs shall be conducted using spill prevention
measures such as drip pans.
10. Control De-Watering: If de-watering is required during construction and
the de-watering water has similar characteristics to storm water runoff, it is
to be directed across the nature vegetative buffer at a minimal velocity.
If the de-watering water contains contaminants, the de-watering water
should be directed to a sanitary sewer as permitted by the sewer utility.
11. Maintain Best Management Practices (BMPs): It is the contractor's
responsibility to maintain the temporary erosion and sediment control
measures and to install the permanent erosion and sediment control
measures set forth in this report and plan.
After construction is complete, maintenance of permanent erosion and
sediment control measures are the owner's responsibility.
All temporary erosion and sediment control measures shall be removed
within 30 days after final site stabilization is achieved or as needed if
longer.
12. Manage the Project: Management of this project can best be conducted
in accordance with DOE if the guidelines set forth in this report and plan
are followed to ensure that the long term goals of environmental
protection and site stability are achieved.
2. Adjacent Areas
a. Adjacent Areas Description: The immediate adjacent area is the
downhill property to the southeast which contains the local drainage route.
b. Downstream Drainage Path: The downstream drainage path is a
forested depression (see photo in appendix)
3. Environmentally Sensitive Areas: The portion of the property located in the base of
the "L" (southeast of property) where the slope increases beyond 15% is classified as a
"type one landslide hazard area. A minimum buffer of 30' is required by the landslide
designation and a minimum of 50' setback is required by the storm water dispersion
Page 6 of 9
',~
regulations from a steep slope (40%+) which may include any buffers. This site's
slopes do not reach 40% and only the 30' buffer is required. Note that the 30' buffer
can be reduced to a minimum of 15' if supported by the recommendation of a geo-
technical analysis and report. A geological site evaluation was prepared by NTl's staff
Geologist, Bill Payton, and is included in Appendix 2 for reference.
4. Erosion Problem Areas: The only potential erosion problem is the relatively steep
slope below the home site. Full dispersion techniques should insure that the runoff is
fully spread and adsorbed. It is prudent site stewardship to periodically inspect the
downstream conditions to ensure that the facilities are working as designed and that the
site remains stable for the structures above.
5. Construction Phasing:
a. Construction Sequence: Specific plans for construction phasing are
not known. It is likely that the complete access will be constructed along
with the home and garage and the shop deferred. Another possibility is to
build the access and shop, live in the shop during home/garage
construction.
The plan developed is modular and can be adapted to cover any phasing
plan developed.
b. Phasing (if proposed): Not applicable at this time.
6. Construction Schedule: None exists at this time
7. Financial/Ownership Responsibilities: The contractor is responsible for the
maintenance of all temporary drainage, erosion and sediment control features during
construction and, possibly, through the construction warranty period. Following
construction and final restoration, the owner is responsible for all permanent drainage,
erosion and sediment control features.
a. Sediment Ponds & Traps: Not applicable
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8. Engineering Calculations
b. Diversions: Not applicable
c. Waterways: Not applicable
d. Runoff/Storm WaterDetention Calculations: None required
Page 7 of 9
Section II - Erosion and Sediment Control Plan Requirements
1. General
a.
b.
c.
2. Site Plan
a.
b.
c.
d.
e.
Vicinity Map: See narrative
Jefferson County Approval Block: On drawings
Erosion & Sediment Control Notes: On drawings
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L2~!~~.~~~ r.crYl~NITY DEVELOPM~~
Legal Description of Property: See narrative
North Arrow: On drawings
Boundary of Existing Vegetation: On drawings
Label Potential Erosion Problems: On drawings
Show FEMA Flood or Shorelines Management Boundaries (if
applicable): Not applicable
/
f.
Show Existing & Proposed Contours: On drawings
g. Indicate Drainage Basins & Direction of Flow: On drawings
h. Label Final Grade Contours & Show Developed Condition Drainage
Basins: On drawings
I. Delineate Clearing & Grading Limits: On drawings, see narrative
J. Show Cut & Fill Slopes (Top & Bottom): See note on drawings
3. Conveyance Systems
a. Designate Swales, Interceptor Trenches &Ditches: On drawings
b. Show Temporary & Permanent Pipes, Ditches & Trenches: On
drawings
c. Provide Minimum Slope & Cover Data For Pipes: On drawings
d. Show Grades, Dimensions & Direction of Slope: On drawings
". ..-/
e.
Provide Details of By-passing Off-Site Runoff: Not applicable
Page 8 of 9
f. Indicate Locations of Outlets & De-Watering Systems: Not applicable
'. -~
4. Location of Detention BMPs: Not applicable
5. Erosion & Sediment Control Facilities
a. Dimensions of Traps, Ponds & Pipes: On drawings
b. Dimensions of Pond Berm: Not applicable
c. Pond Volume and Dimensions: Not applicable
d. Typical Pond Cross-sections: Not applicable
e. Details of Filter Facilities: Not applicable
f. Outlet Stabilization Techniques: Not applicable
g. Control I Restriction Details: Not applicable
h. Mulch Specifications & Check Dam Details: Not applicable
'--_./ I. Rock Specifications for Check Dams: Not applicable
j. Check Dam Spacing: Not applicable
k. Front & Side Cross-sections of Check Dams: Not applicable
I. Locations for Silt Fencing: On drawings
m. Construction Entrance Details: On drawings
6. Detailed Drawings: See report and appendicles
7. Other Pollutant BMPs: A variety of BMPs apply to this project including silt fence,
catch basin protection, straw bales for ditches, construction access and full dispersion,
All BMPs are detailed in the report and appendicies.
8. Monitoring Locations: Not applicable
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DEPT. OF COM MUf'H1Y DE\jEl.O~,./1ENT I
Page 9 of 9
$tormwater SIte Plan Changes
Ii the designer wishes to make changes or revisions to the originally approved Stormwater Site Plan, the proposed revisions shall be
"- -' submitted to OeD prior to construction. The submittal shall include substitute pages that Include all proposed changes, revised
drawings showing any structural changes, and any other supporting Information that explains and supports the reason for the change.
FInal Corrected Plan SubmIttal
If the project included construction of conveyance systems, treatment facilities, flow control facilities, or structural source control BMPs
(not standard on-site stormwater management BMPs), the applicant shall submit a final corrected plan {"as-buiUsj when the project is
completed. These should be engineering drawings (stamped by a licensed civil engineer) that accurately represent the project as
constructed.
APPLICANT SIGNATURE
By signing the Construction SWPPP worksheet, , as the applicanVowner atlest that the information provided herein is true and
correct to the best of my knowledge. I also certify that this application is being made with the full knowledge and consent of all
owners of the affected property.
(lANDOWNER OR AUTHORIZED REPRESENTATIVE SIGNATURE)
(DATE)
THIS SPACE MAY BE USED FOR ADDITIONAL NOTES, IF NEEDED:
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APPENDIX 2 - Calculations, Etc.
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NORTHWESTERN TERRITORIES, INC.
717 SOUTH PEABODY STREET, PORT ANGELES, WA 98362
Engineers. Land Surveyors. Geologisls
Construction Inspection. Materials Testing
(360) 452.8491 1.800.654-5545 FAX 452.8498 E-Mail: info@nli4u.com
H'WW.IJ{j-lll.C()1JI
August 27, 2004
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JEFFUiS()l>J COUNTY
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Todd and Cindy Colebrook
21 Barque Ln
Port Ludlow, W A 98365
Subject:
Geotechnical Assessment of Lot 2, Port Ludlow #6, Tax Parcel #821085002,
Located in Section 8, Township 28 North, Range 1 East, W.M., Jefferson County,
Washington
Dear Mr. And Mrs. Cole brook:
Bill Payton of NTI Engineering and Surveying completed a geotechnical assessment of the
above referenced property consisting of research of available literature and geologic maps of
the area, and a site visit for visual observations. This assessment was in response to the
eastern portion of the parcel being listed as a landslide hazard area 1 by the Jefferson County
Department of Community Development, specifically a ravine that runs southward along the
eastern side of the property.
The USDA Soil Survey maps the soils in the area of the property as the Alderwood gravelly
sandy loam (0%-15% slopes), a silty sand or silty gravel soil that formed in glacial till. The
Washington State Department of Ecology's Geology and Ground-Water Resources of Eastern
Jefferson County, Washington maps the soils in the area of the subject property as Lodgement
till (Qvt), a glacially derived soil. This same soil is mapped by Ecology's Coastal Zone Atlas as
Vashon Lodgement till (Qvt1). For comparison purposes, this is the same soil that comprises
the steep bluffs along Water Street in Port Townsend. The Atlas states that this soil stands in
steep natural and cut slopes for long periods (as evidenced by the vertical cliffs in Port
Townsend). Visual observations of the surface soils at the property match the above soil
descriptions.
The property is well vegetated predominantly in grass with young to mature native trees and
shrubs along the gully. No springs or seeps observed, and it appears that no water flows in the
gully except storm runoff. Likewise, no water loving plants such as horsetail ferns were present
in the gully. There was no evidence of past slide activity observed in the gully or elsewhere on
the property. A few of the trees in the west side of the gully had slightly curved trunks indicating
that minor down slope creep of the surface soils is occurring.
The slope of the gully at the subject property is approximately 14 to 16 degrees (25%-28%), and
is approximately 40 to 50 feet high. The typical angle of repose for loose cohensionless material
ranges from 33 to 37 degrees. The angle of repose is considered the maximum slope that a
loose cohesionless material remains stable. The slopes at the subject property are well below
this angle.
This office is providing an engineered drainage and erosion control plan for the development. As
part of the development, a series of infiltration/dispersion units are proposed along the southern
portion of the property and along the eastern portion of the property at least 30 feet west of the
top of the gully.
Based upon our assessment of the property, we anticipate that the proposed drainage system
will not destabilize the gully slope and further that the ravine does not pose a landslide risk to
the development.
If you have any questions regarding this matter or need further assistance, please feel free to
contact us.
Sincerely,
NORTHWESTERN TERRITORIES, INC.
Bill Payton, L.E.G.
Engineering Geologist
G:\Gen\Bill\Reports\Colebrook.8(28.1 E). Geolech review. PI Ludlow.doc
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i .. .,1 UTi: fi S or~ COiTr~1Y
! (if!'! or CGr,,1MUNIT'{ DEVELOPMr-NT
.- >.. .._'-~--..~~-.._"------~...-.-.~~-------..:~~~
~ b"LCk/_ -=- j?b5: S~
() CurJG PM)~ - 777 + 42.0 - t !97 s c
Cl D C2./ VE'w J\'! - 12..\ cr uu ~ p
q IUT^- L t IA P~vL Ovts' -::: 74-0Q +- ~ bS +-1 [q 7,( f2{ Croo ::::: 1..2; Or {
'J S T R I DATE:
L
~ DESIGNED BY:
:i
w
g PROJECT:
Q,
"
8 FOR:
w
~ SHT OF
~
NT'
NORTHWESTERN TERRITORIES, INC.
a JLS Group Company
Engineers. Land Surveyors. Geologists. Materials Testing
717 SOUTH PEABODY. PORT ANGElES, WASHINGTON 98362. (360) 452.8491
www.nli4u.cominfo@nti4u.com
8/24/04 6:59:25 am Shareware Release
Colebrook Drainage
Incremental Flow Approximation
For Dispersion Unit Sizing
page
1
==============~=========================================~===~========
BASIN ID: 100a
SBUH METHODOLOGY
TOTAL AREA. . . . . . . :
RAINFALL TyPE....:
PRECIPITATION.... :
TIME INTERVAL....:
BASIN SUMMARY
NAME: 100yr post - runoff (200'dwy)
0.09 Acres
TYPE1A
3.50 inches
10.00 min
BASEFLOWS:
AREA.. :
CN.... :
TC.... :
0.00 cfs
PERV
0.02 Acres
86.00
17.27 min
IMP
0.07 Acres
89.00
5.00 min
ABSTRACTION COEFF: 0.20
TcReach - Sheet L: 200.00 ns:0.1500 p2yr: 1.50 s:0.0500
impTcReach - Sheet L: 200.00 ns:0.0110 p2yr: 1.50 s:0.0500
PEAK RATE: 0.04 cfs VOL: 0.02 Ac-ft TIME: 480 min
BASIN ID: 100b
SBUH METHODOLOGY
TOTAL AREA... ....:
RAINFALL TyPE....:
PRECIPITATION. . . . :
TIME INTERVAL....:
NAME: 100yr post - runoff (lOO'dwy)
0.04 Acres
TYPE1A
3.50 inches
10.00 min
BASEFLOWS:
AREA. . :
CN.... :
TC.... :
0.00 cfs
PERV
0.01 Acres
86.00
9.92 min
IMP
0.04 Acres
89.00
5.00 min
ABSTRACTION COEFF: 0.20
TcReach - Sheet L: 100.00 ns:0.1500 p2yr: 1.50 s:0.0500
impTcReach - Sheet L: 100.00 ns:0.0110 p2yr: 1.50 s:0.0500
PEAK RATE: 0.02 cfs VOL: 0.01 Ac-ft TIME: 480 min
BASIN ID: 100c
SBUH METHODOLOGY
TOTAL AREA.......:
RAINFALL TYPE. . . . :
PRECIPITATION. . . . :
TIME INTERVAL....:
NAME: 100yr - roof/cone (1500sf)
0.03 Acres
TYPE1A
3.50 inches
10.00 min
BASEFLOWS:
AREA. . :
CN. . . . :
TC.... :
0.00 cfs
PERV
0.00 Acres
86.00
5.00 min
IMP
0.03 Acres
98.00
5.00 min
ABSTRACTION COEFF: 0.20
TcReach - Sheet L: 200.00 ns:0.1500 p2yr: 1.50 s:0.0500
impTcReach - Sheet L: 200.00 ns:0.0110 p2yr: 1.50 s:0.0500
PEAK RATE: 0.03 cfs VOL: 0.01 Ac-ft TIME: 480 min
5' U M1 vyta I-'VJ
Dnve~ =? C).OLC{'S 1/0-0 !f/1ea./ ~+
f2uor; leo-nc. =t 0.0"3 c.fs I / SO 0 sf
!!~.:~Y"~ ~. [[~fW~'n~"Ji:~:~'.'..'
1,1) J l---~'~'-~~'~'" I'
I ;,,<, I :
II \ Ii'
,ll U, SEP = 7 2004 11 )
I I . '"c.,_"
I J i
! L._-~._~__~.~-l
r , JfYFEf1S0N COUN"IY
LDEPT OF COMMUNITY D[VELOfJMEN~
Sizes of 24-hour design storms for selected locations in the Puget Sound Basin
Rainfall in inches
LOCATION 6 Month 2 Year 10 Year 25 Year 100 Year
Event Event Event Event Event
Port Angeles 1.34 2.10 3.25 3.75 4.60
Sequim 0.99 1.55 2.45 2.95 3.25
Forks 3.19 5.00 7.00 10.00 11.00
Port Townsend 0.70 1.10 1.75 2.00 2.40
Port Hadlock 0.89 1.40 2.20 2.60 3.00
Port Ludlow 1.00 1.50 2.20 3.00 3.50
Source: NOAA Precipitation Atlas (Received @ NTI on 4/13/93)
F:\Document Prep\24 hour rainfall in inches.wpd
.__.....-..........,.,..-~"'---~-".....=-.==.--~-=~~."~=='~~"'--...1
r~1 r...7~-- =l~' .(F':.. r.~ 1.1 \V7 rr~ r~r~.\\
1 .~ !_~-!; L~.l __j l.J tL . ~ \
i l)" r-~'--~~~.~~.~-~llll
I ['II I \' J J
\, i.\ll SEP.. .'.~'...7. 2.-".0.0.4 I L!j
lJ Ll ~.~-
L-J'EFfEf1-sorTco'uN"lY I
DEPT or COMMur~.l"rj'Y~2~~~~!.~_~~~
DATA rot<. FLQAJ G CAJeidA 7/0AJ s 1).1 U Ut T ION S
I] D ~/()-Cwt\ y
eN -= 'i?~ GRAvEL~) ()t\u {S r Wf DC:;
(N~ 8& Gl?.~S;: S'-I\OU LOI":: 1'2 S" C))(oG
/0 0 Y R r<..P'J t fi.) ~ s, <:; / A.J I :L yl~ RAt Ai::::. /, ~ / N
S I M \A lA,T/U".J LE:-AJeoff
1000. - 200' ~
too b - (GO'-==t
0.. 00Cf fie D~/;)EC/J/I')' O,OIl -Ac. Sl-+OuLOEI~
o 0"3 SAC Dr2/UEcvf\ Y ) o. OOCZ 1\ C :; H OctL-D [;r2
SH~b-T FLcJw E2 S % OD GRA-~s; OR S H(} 0 Tt-{
Nt IJ T7 f1G Of- 0!JIVC2"A./TI2A-TrOAJ -= S; H oj pE:A. sorrw/'cRG
sSUH )/.hULATIO~ ' 7YPE lA SrOi<-H
)
2) RODF / CO'A) G
eN = 9f? ROUP"& C0NC 'PA v E
\' CJ () YR f2A OJ - 3,S; /.x...J) 2- '-fT<. l2Ar -'J - LI C;;; / k)
S';fptU/Jt--t;u;..J Me::A::: ISQOsF- O,O?SAC
MIU rrMG: Of- (O,vctMTN.j,-t/o/J -- J;;' H/J-..J Pc'(( SOr-:-rcJA~6
rr.'~-'[E~'~-'~~]-\\lrr[~:s
II, rr?~ l~---. --~~-"-'~"""'--~---ll.ll.i
! Ii 'I - ", I J;
III t\ S t: p", I 2004 ! l<~,:')
I I \
: ii, "(_~iTT;,t~~:~i;~(~?l~}~~UOi~;"':.. ~
S T R I DATE:
_J
DESIGNED BY:
PROJECT:
FOR:
~ SH~ OF
~
NT'
NORTHWESTERN TERRITORIES, INC.
a JLS Group Company
Engineers' Land Surveyors' Geologists' Materials Testing
717 SOUTH PEABODY. PORT ANGELES, WASHINGTON 98362. (360) 452.8491
www.nti4u.cominfo@nti4u.com
STORHWATER MANAGEMENT MANUAL FOR THE PUGET SOUND BASIN
"
Table III-1.3 SCS Western Washington Runoff Curve Numbers
(Published by SCS in 1982) Runoff curve numbers for selected agricultural,
suburban and urban
land use for Type 1A rainfall distribution, 24-hour storm duration.
LAND USE DESCRIPTION
Cultivated land(l):
Mountain open areas:
Meadow or pasture:
Wood or forest land:
Wood or forest land:
Orchard:
.winter condition
CURVE NUMBERS BY
HYDROLOGIC SOIL GROUP
A B C D
86 91 94 95
74 82 89 92
65 78 85 89
42 64 76 81
55 72 81 86
81 88 92 94
low growing brush & grasslands
undisturbed
young second growth or brush
with cover crop
Open spaces, lawns, parks, golf courses,
landscaping.
Good condition:
Fair condition:
Gravel roads & parking lots:
Dirt roads & parkinq lots:
cemeteries,
grass cover on c75% of the
area
grass cover on 50-75% of
the area
68
80
86
90
77
85
90
92
76
85
89
91
72
98
82
98
87
89
98
Impervious surfaces, pavement, roofs etc.
100 100
,
Open water bodies:
Single family residential(2):
Dwelling UnitjGross Acre
1.0 DUjGA
1. 5 DUjGA
2.0 DUjGA
2.5 DUjGA
3.0 DUjGA
3.5 DUjGA
4.0 DUjGA
4.5 DUjGA
5.0 DUjGA
5.5 DUjGA
6.0 DUjGA
6.5 DUjGA
7.0 DUjGA
PUD's, condos, apartments,
commercial bus'inesses &
industrial areas
98
. lakes, wetlands, ponds etc.
100
100
%Impervious(3)
15
20
25
30
34
38
42
46
48
50
52
54
56
Separate curve number
shall be selected for
pervious & impervious
portions of the site
or basin
t~~'---~~ ~.'~'-~.=-"-~~'~-.~--~--<"-~.~., ,., ..-=,----~"....-~ ~._r."C_-.<_'
i fF:\ [E ~ t~~ [I \V/ l
IllJ ) r--'~~'-'----------~-~'
',I r~'> 1
I ,'!
11.1 tJI SEP ~ 7 2004
! c'c~~;')~',;!Il~~'~SS'FTY r~~E!iT I
...........-... ...-n..-_.......___....Ch. .....__~___~
~:"'~.>l
Wil
L I:
L:J;
% impervious
must be
computed
(1 )
(2 )
(3 )
For a more detailed description of agricultural land use curve numbers refer
to Na~ional Engineering Handbook, Sec. 4, Hydrology, Chapter 9, August 1972.
Assumes roof and driveway runoff is directed into streetjstorm system.
The remaining pervious areas (lawn) are considered to be in good
condition for these curve numbers.
......
Irr-1-12
FEBRUARY, 1992
Agnew
Ahl
Aits
Alderwood
Arents, Alderwood
Arents, Everett
Ashoe
BaldhiJ/
BameslOn
Baumgarc;
Beausite
Belfast
Bellingham
Bellingham variant
Boistfon
Bow
Briscot
Buckley
Bunker
Cagey
Carlsborg
Casey
Cassolary
Cathcart
Centralia
Chehalis
Chesaw
Cinebar
Clallalll
Clayton
Coastal beaches
Colter
Custer
Custer, Drained
Dabob
Delphi
Dick
Dimal
Dupont
Earlmont
Edgewick
Eld
Elwell
Esquatzel
E verelt
Everson
Galvin
Getchell
Giles
Godfrey
Greenwater
Grove
Harstine
Hannit
Hoh
August 2001
Hoko
Hoodsport
Hoogdal
Hoypus
Huel
lndianola
Jonas
Jumpe
Kalaloch
Kapowsin
Katula
Kilchis
Kitsap
Klaus
Klone
Lates
Lebam
Lummi
Lynnwood
Lystair
Mal
Manley
Mashel
Maytown
McKenna
McMurray
Melbourne
Menzel
Mixed Alluvial
Molson
Mukilteo
Naff
Nargar
National
Neilton
Newberg
Nisqually
Nooksack
Nonna
Ogarty
Olete
Olomount
Olympic
Orcas
Oridia
Orting
Oso
Ovall
Pastik
Pheeney
Phelan
Pilchuck
Potchub
Poulsbo
Prather
i-:;=:~~'~:-~fO"~:;:';'-""-" ""~""-'
I r' I~ fr~: WI U::
,,' ~ 1-' -~ :::..~. '; .,~ .
'I t fl [I Gr:J:J(l(lI!
-l _.,
i
, L.,
[ _'._ _ __j~~',',_r<:.~.:'i _" ,~,
Volume 1/1 - Hydrologic Analysis and Flow Control BMPsLl!~!:~~).i,:'.CJ.'."2~19 ~_;.~.
s
no iTld\('~. 'I'll(' soilltold:'l 10 or Illore iudll'S of \mtl~r available
for plant.e;. 1(lInoff is slow, :llId t1\(~ hnzard of watl'r ('I'osioll
,light.. A s('aSlJlI:d \\,a(N fable is :d. a d(~pth of I to 2 feet..
,bout fiO to 70 r)(~ITc'.nt. of (.Ill: a<T('a~(~ is us(:d for crops.
.-,(sture, Itay, and sil:tl!:c~ frolll lllixcd grasses alld Iegum"/i are
t.he principal ('I"ol's. A varil'!.y (,f gard('1I vq!,"elahl(~s, berri('s,
alld tl'(~(' frui!., filay 1)(' grown. Capahility unit. JIl\\'-l; \\"()od-
lalld group :1d2.
Ag;.cw !:-lilt loalll, :W 10 ~O perecnt slop.~!:< (AgE),.u
This soil iR mailllv along oce:Ul bluffs or canyon sidemdls.
Tile subsoil in lll'allY plae(~s eOlltains strata of silt.y day
loam, filiI' sandy loam, silty day, and sandy day loam.
H.\lllofT is ra pid. :lnd t.lll) hazard {,f watcrl'rosioTl is severe.
Most an~ls of this soil are wooded. When used for building
sites, t.he soil oft.cn slides \\'h(,1I sa.turated. Capability unit
VIe-1; woodland group :kJ2.
Ahl Sel"ies
The Ahl s"ries eonsiRts of wdl-draineu, very gravelly loam
soils underlain bv basalt Iwdroek at. a depth of 24 to 40
inches. Tlwse soil:s are on mountainous terrain. Slopes range
from fiO to 00 IlC'reenL Elevat.ion ranges from 800 to about
:~,OOO f(~et. These /ioils formed ill \\'eut.hercd basalt under a.
dominantly conifcrow-; forest of Douglas-fir, wcstern hemlock,
and wcstem redeednr. Allnual precipitation is 60 to 80 inches.
The llV('r:ll(e annual air temrwraturc is about 4H"P. The
above :~2"J'; groll'illg; Si~asnn ranges from 150 to HIO days.
and t.lw above ~soF ~rowing season ranges from ISO to 2:m
days. These soils aTe associated mainly with Grove. Lystair,
Ol~~tc, and Tritun soils.
In a r(~presclltativ(: profile a thin layer of organic litter
1~(WCl'f; the smfnee. The upper :3 inches of the soil is dark
fish-browll vcry gravelly loam. Below this, to a depth of
IJdles is V(~ry grave II V loam that is dark red in tile upper
i)m.t and 'I'lxldisll Grown III t.he lower purt. Beneath this, and
extending to a depth of :i8 inehc~s, is mostly angular basalt
pebble.s and fracture'd, \w~ather('d basalt. Bas-'llt bedrock is
at a depth of 38 inches.
A.hl soils are used mainly for tree pl'Oduct.ion and for wild-
life habitat. and rccrentioll areas.
Ahl \'(~ry gnl\'elly loam, 50 lo 70 percent slopes
(AhF).-This very steep soil is in the mOllntains.
. Repres('lItative profile in SE3-'4NW;;,{SE~i sec. 34, T. 27
N., It. 2 \V.. 1.2 mill~S south of U.s. Highway 101 along
i\Jt. Walker ]load, 15 feet cast of road.
01-3 inches to I inch, needles, leaves, t.wigs, bark, moss, and fmg-
ments of wood.
02-[ inl"h to 0, df'c"Jmpnsing organic lil.t{>r.
B2Iir-.0 to ;: inchf'S, dark reddish-hrown (iiYR ;3/-1.1 very gravelly
loam reddish brown (2.ii Y It 5/-1) dry; weak, fine and very
fUlIJ, 'graulll:ir strudllre; soft;, ,'cry friable, slightly sticky,
pln.stie, stne,uT; many line, medium, and large roots; 55 per-
cent a1\glllar I n':'a I t pebbl<'>l; medium acid; c1w.Lr, wavy bound-
nry. (2 to Ii ilH:hc., thicki
B22iru -:1 10 20 inches, dark-red (:2.iiYR :ljl;.l VCI'y gravelly loam,
reddish hrown (2.fiY[t 51-I) dry; weak, tine, I!;ranular anet suh-
nngular hlocky sl rtlelme; soft, very f riahle, slightly sticky.
plastic, slIwar}'; nUlIlY tille, nH.'diUI11, IInd lurge roots; !i!i per-
,'en!. lIngular b'L~alt, pebblf'S 1\nd 5 percent rounded pebbles;
medium aeid; gradual, wavy houndary. (10 to IS illehcs !.hick)
B3..-20 t.o:lO indH~~, rc.'ddi~h-hl'Owll (5Ylt 4/4) very gravellj' [oalll,
light reddish hrowll (5 \'H 6/4) dry; massive; soft., friable,
nOllsLi,~ky, 1I(H1pJ,L~t.iC, smeary; common tine rooLs; 70 percent
angular hn0al[, pebbles; slightly acid; gradual, wavy boulldary.
(8 to 12 illche.~ thick) .
C---30 to ;Jf; inehe.~, ~lO percent. fmeLun.,,1 bnsalt. hedroek. j\falcnal
in voids is reddish-hrown (5YE -1/4) very graveUy loam, light
.'lOlL flllHVIGY
reddiHh bro\\'1I (!i \' H till) dl')'; 1l\II><.s;ve; Hli/l;hlly IIcid; /l;l'IIdllnl,
.wa.vy. 1)(1l1l1:j,~.'"y. (I to .I.~ inehe,:; I.hie")
l1-n.1K IlldH~, b"".1I I, I ll'd 1Il<. "-
Dept.h t.o ImolalL bedrock ran!,;,,,, fr'lIIl 2.1 [0 .(() inc.he,". The Bir
horizollol are very grllvelly loalll "I' vcrI' ).(l'ILvcll~' Hilt. 1ll/L1n, The C
horiwll iH more illllll SO ,;,'rcenL fl'll<:l.'l\:,'d hasalt: hcdl'llck.
Tncluded with t.hi::; soil in mapping al'(, small awns of
Roek outerop and of Triton soils.
This soil is well dmincd. Pel'llwabilit.v is modcmte. Roots
p(met.mte to the lwdnwk. This soil !r(;lds 2 to 4 illdlelJ of
water a.vailable for planLe;. H Ilnolf is vI:ry rapid, mid t.he
hazard of erosion is vel'Y sl'ven~.
This soil is IIscd m:tin'ly for trc'c prodlldion and for wildlife
habita.t and recreatiull an:as. Capabilit.y unit VIIe-1; wood-
land group :~d2.
Ahl-Rock ollterop cOlnplex, 50 to <)0 percent slopes
(AkF).-This mapping: unit is made tip of about. 50 to 70
percent Ahl very gravelly loam. It. is :30 to 50 pereent Rock
outcrop and stony areas. The AIlI soil is 2.1 t.o 30 inches deep
in most places.
Almost all the acreage of the mmplex is used for tree
production and for wildlife habitat and recrc.at.ion areJ\s.
Capability unit VIIs-I; wocxllRnd group 4x2.
Alderwo(){l Series
The AJdenHlod Reri{~s consistR of modera.tely w,,11 drained
soils that. have a very sl()\\']y pernH'<lhl(~ cemented layer at a
depth of 20 to 40 inches. Slopes r:wge from 0 to 50 percent.
Elevation ranges from 100 to 800 fed. These soils formed in
glacial till under a forest of mixed eoniferouE and broad-
leaNed vegetation. Annual pre('ipiblt.ion ranges from 25 to
50 indH~'3. Tho average annual air temperature is abont
49"F. The above 32010' growing season ranges from 160 to
260 days, and t.h(' above 2S"F growing season ranges from
220 to 320 davs. These soils are assodatcd mainly with
Beausitc, Case);, Clallam, Dick, Everett, Hoypus, In{iianoh,
Sinclair, and Whidb(~y soils.
In a repr{'.scnt~tt.i \'0 profile a thin layer of organic litter
covers the surface. The top 1 iuth of the soil is very dark
grayish-brown gravdly fino sandy loam. Below this, to a
dept.h of 12 inell(~S. is dark Yl'llowish-brown gravelly sandy
loam. Benc.ath this layer, and continuing to a. depth of 30
inches, is gravelly :Jandy loam th:tt is brown in the upper
part and dark grayish hrO\HI and prominently mottled in
the lower part. The next layer is a dark gmyish-brown
cemented la.yer t.hat formed in very compact glacial till.
Rounded pebbles, cobblestones, ancl stones arc on the surface
and throughout the profile.
Alderwood soils are used mainly for tree production and
for wildlife habita I. and reereatio!l :lrC.fJ.S. u'ss than 30 percent
of the acreage is used for growing pasture plnnts, hay plants,
and diversified farm crops.
:'\Jdcrwood gravelly salHI)' loam, 0 to L5 pel"cenl
slopes (AIC)..--This nearly level t.o rolling soil is on glacial
terraces. In most places t.he stope is 5 to 10 percent..
Reprcscubttivc profile 100 yards \\"(:st of house, southwest
side of Beausite Lake; SE!iNE};{SEy.{ sec. 28, '1'. 29 N.,
R.I W.:
01-1~~ inches to .1.;1 inch, needles, leaves, bark, and frugment.~ of
wood.
02-!..~ inch to 0, hlack (!iYlt 2,11) part.ly deell.ycd leave;;, uecdle.~,
bark. and fr'lgmenL~ of w"r,d; !l1c."lium acid; abrupt, wavy
boundary. CY:i I") I !.-:! inch('_~ thick) r
A2--0 t.o I inch, very dark Rrayi"!..bro,,,u (10' II 3/2) grav:-lIy
line >landy 10al1l, pale brown nU:l{tur}Jd,t~..;",:cl+k;'yefrJlO~;:;'
Ii) ,Ji~,. lI,,; u~: U Wi E::
I' ./ I
fr'I"I!
I, t} i
u \.\1
)M'__~_..'_.''''''
"1
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.1rFF,~n~:(]k (~{':i jU"J-Y
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!
'DOli
,mIW1W~ON COHN'I'Y J\lmA, WM;fllNn'I'ON
gr:llIlIl:tr sl.rlldllre; ~(Ifl., very friable, lIollsticky !Lnd IIlIn-
pla.'li(~; 11I:l11.\' fino alld IlIedilllll rnol.~; :!:, pcrc~('.1\1. pohhlt,.~;
lI\t'dilllll ,,,,id; dear, XIIIIIOth IHllllHlarr. (!'; 10 II.~ illche:J Ihide)
112Ii""1I I 10 Ii ill(.it<,., dad, ydlowixit.llI:own-(IOYlt -trt) ~I'll\'ol\y
xlllldy 10/lnl, (lal,' hrowlI (ItlYll.li/:ll drr; weak, fillo, p;ranullll'
~tl'l"'(.IIf1'; slightly hard, friahle, ..lifdlf.ly Htieky /lnd slighlly
plllxtic; lIlallY tine '''HI nll"lilllll rool.~; COllllllon hard iron-
Illllng;:llll"''' r'OI"~r,,1 i'\II~; .10 per<.'olll. gravel; medillm Hcid;
gr:ldll:d, \I'IlVY (Jollndar.\'. U lo (i inehCH thick)
1122irollu'-ll t., 12 illdles. dllrk yellowi.'ih-hrown (IOY It 4i4) I!;mvelly
~andy Inam, Pille brown (11IYlt li;:l) dry; weak, fine, slIbangll-
IIlr blo"ky slntdllre; t<lighlly IHtr.-l, friable, Hlightly stieky alld
sli~hll.\' pl,c'ili...; ""'n)' line IllHl nwdillm reinl:;: commOn hard
irlln-lllHlIg:lII(~~e (~lIn"ret.ionH; .W percent pehbles; slightly aeid;
dellI', wavy l.lfHIIHbry. (5 to 7 in"hos (.hick)
In ..12 III 21 ill(~h<,:<, brown (IOYlt 'l/:!) ~mvcll.\' sandy luam, Pltle
1"'OWll (IOYH. Ii!:!) dry; lVeak, linc, slIbanJ!;lIlar blocky st.rllc-
I.lll'('; slighlly hard, friable, Hlip;htl.\, sticky, slig;hlly plnstie;
Illany fille :llHIIIH'd illm I'on!.~; 45 pereent grnvel; ;;lightly acid;
('Ielll'. slTloolh hOllll(hry. (li (.0 12 indies thick)
CI.~J 1.0 :\0 incl,,~., dark grayi"h-brown (LIIYH. ,1/2) gmvelly
::and)' loam, li/{ht gm.v (IOYll. 7/2) dry; many medium, p,,,..ni-
111m I., yellowish-red (.'; Y H 4/U) TlIol.lle;;; massive; hard, firm,
~Iighfly sl i"ky, slightly plast.ic; few line find medium 1'00t.~;
.\.~ perr'.en(. gmvel; medilllll aeid; gradual, wuvy bouudrrry.
(-I 10 III indIP_~ Ihil:k)
C:!Si[Il--~;1O (.0 48 illches, d,u'k grayish-brown (IOYR .i/2) weakly
('l~lllellf.ed ~l'avclly sandy Inrrm, lip;ht. gruy (lOYlt 7/2) dl')';
'llall.\' ('oars", prolllilH'nt" yellowish-red (5YR 4fG) mol.He;;;
1I1:L"...ive; extn~rncly hard, extremely finn; no 1'001:;; slighl.!y
'lO'id. (HIt" IX iuehc,.; thick)
C:l.-..IX in!:h".':, very compact gravelly sandy loam glacial t.iIl. (;'.Inn)'
feet tbiel()
The depth In (.he cemented layer ranj!;e.~ from 20 to .W inches.
Tlw A:! :md B:liren horizons nllll!;e from velT dark gnwish brown
I" dark yellowish browll. Their c<ml.ent of '~(;arse fragments ranges
frolll 20 t.) :j\) percent. and avel'll.gc,; marc than ;Ii) percent,. In p1ne(,1~
ihe lippeI' parI of t.he CI horiuHl is eompaet gra\'eHy loamy fmud.
Few tn fn:lny hard iron-mangane.>e L'Ollcretions arc in the A2,
B2il'en, '\llll B22irc:n horizolls.
Small :u'cas of sandy, vcry gravelly, or eobbly soils are
induded \\'it.1l lhis ::;oil ill mapping. .
This soil i,; mod(~ratelv well drained. I\~l'meability above
the c:enwlltcd layer is moderately rapid. Roots pctll~trate to
th(.~ l'(,lllcntcd layer and flatten out 011 top of it. A pcrched
water table is above the cemented layer during the winter
months. This soil holds 2 to 4 inches of water available for
plant.<;. Runoff is slow to medium, and the hazard of water
erosion is sli~ht tD moderate.
This soil is used for permanent past.ure of mixed grasses
and legul\ws. Both hay and silage are commonly produced.
Small grains, vegdablcs, berrie.s, and fruit trees are also
grown. Capability unit IVe-l; woodland group 3d2.
Aldcrwood gravelly sandy IOllJu, 15 to 30 percent
slopes (AID).--.This moderately steep soil is in places where
the rolling glacial upland terraces converge toward raviup.s
and ..,tccp dminageways.
RUllOff is medium to rapid, and thc hazard of water
('rosion is ll1olkrat.c to R(:vcre. This soil is used mainl\' for
t.l'<_'C produd.il.ln and for wildlife habitat and recreat.ion :;reI13.
rt is also :mited to permanent hay and pasture erops. Capa-
bility unit V [e-l; woodland group 3d2.
Alderwood gravclly sandy loan1, 30 to 50 percent
slopes (AIE)..--This :;tC(:p soil is on glaciated upland.."
generally in slllall an'IiS along Rteop morainal margins or
mllyon sidewalls. On t.he upper third of the KlopeR, the
surface bver and subsoil are often 20 to 2,-1 inches thick
over the c~nwnkd layer. Alon?; the bottom slopes, dept.h to
the eenwnled I:wer is :W t.o 4.0 inches.
Jncluckd wit.it t.his soil in mapping :tre small areas of
Aldcr\\'ood gravelly sandy loam ilnd Alderwood gravelly
D
loalll, LS (n :\0 p(~rccllt slop(\,;, as wdl fi:-; slllall ILrC:lS of
Jt:vcn~t(., Illdiallola, lIoypus, Nillelll.i1', and Whidbcy soils,
15 f.o :\0 percl'lll. slop(,,;.
Itulloff is rapid, !llld Ul(~ har,iLl'd of \\'al,el' (~roKi()n iK scvc('(~.
Thii:' soil is us(~d for tn'l) pl'Odudioll alld for wildlife' habif.at
and ('('l'['catiol\ :tr('~I.<;. Capability unit VJc-l; \\.ooelland gl'lHlp
:-ld2.
Alden~o()(l gravelly IOUlll, 0 lo 15 percenl slopes
(AmC)...-This ncarly Icvd to rolling; soil is 011 glacial (.('rrace'..,.
The surfacc bYl~r alld subsoil are gra.velly loam.
Ineluckd with t.his soil in mapping are small traets having
shain or sandstonn at a d(~pl.h of 20 Lo 3G inelle'S.
P,,-rmcabilit.y is IlIod(~ra.t.e. ThiR soil holds :{ t.o G inches of
waLcr available for plants.
This soil is use'c! mainly for tree production and for wildlife
habi t.at a.nd rccreation awas. Capability unit I Ve-l; \\'ood-
land group ~~d:2.
Alrlel'wo(ul gravell..,. IOatll, 15 to 30 percellt slopes
(AmD)..-This lIloderatdy steep soil is in area..,; where the
rolling upla.nd glacia.l terraces converge with the steep
drainagmvay ravines. TIH) surf:tce layer and subsoil are
gravelly loam,
This soil holds :3 to G inches of wat.C'r available for plant.':;.
Pcrmeability is moderate. llulloff is medium to rapid, and
the hazard of (~rosjoll is moderate t.o s(~v('.re.
This soil is used mainly for tree produd.ion and for wildlife
habitat and reercation areas. Capabilit.y unit VIe-I; woodland
group 3d2.
Alderwood-Quilecnc ('omplcx, () t.o 15 percell l slopes
(AuC).--.This nmppill~ unit is made tip of about GO percent
Alderwood gravdly sandy loam, 0 to 15 percent slopes, and
about ~30 pe)'(~cnt, Qnileellesilt, loam, 0 to 15 perccnt slopes.
The mostly rolling Alderwood soil is on glacia.l moraines.
The nearly level to strongly sloping Quilcene soil is mostly
in arC:1S adjacent. to the moraines. About 10 percent of t.he
acreage is Everett, Hoypus, a11<l Indianola soils.
lIto:-;t of this acreage is wooded. A small acreage has beell
cleared and planted to pasture. Capability unit IVe~l;
woodland group :3d2.
Beausite Series
The Hl'ausite series l:onsists of well-drained soils underlain
by strongly cemented s:mdstone conglomerate at. a depth of
20 to 3G inches. They arc on the sich" of valleys, mostly
south :lIld southeast of Discovery Bay in the northeastern
part of Jefferson Count.y. Slopes range from 0 to 50 percent.
Elevat.ion mngeH from 50 to 1,500 feet. These soils formed
under a dominantly coniferous forest. in weat.hered con-
glomerat.e consisting of mixed acid n,nd baslc roekH. Annual
precipit.ation ranges from :m to '10 inches. The l1vemge
annual air temperature is about 500F. The above :no1"
growing season range's from about 220 to 250 da.ys. and the
a.bove lSDI<' growing sea.'''HlIl ranges from about, 270 (0 300
d:tys. The.se soils arc as:-;oeiakd mainly wit.h Alderwood,
Everett., lndia.nola, Quilc('[w, and Sinclair soils.
III a representative profile a thin layer of organie litter
eov(~rs the surface. The upper 22 inches of t.he soil is gravelly
sandy loam that is dark brown in t.he upper part and dark
ydlowish brown in the lowC'r part. Below this, t.o a depth of
;n in(~hesJ is brown and grayish-browll very gravelly sandy
loam. lkneath.this layer i::; stroll!!;ly ('('men led, very gravelly
mUldst.011C (,ollgl()l11(~rate. ..~...--"". .............,..,... ...-........".... .... ....-. .__._~.._...,..~.".l
BculIsite soils arc lIsud nht.iXly filL tif~.c nt.(ld~lct..l9(1 :IT.J;d I'0t.\
'Idl" I b' 1 .." 'I J' I", '. ,I \'" " 1'i; \
WI lie la rlat. llIH recreation ~~re,r& ','., ,," ",',' ;.,::, I' \ II
! i ~:::;-:! "'''-1111 i :
I. !! \ ~ !.; I,,!, "I ,1 t.
! -~! -,
: I j .j I I j ;.,j'; t
1 L.! 1 L.~~,1 I
i \ i
", ."..~~ i,
JE~:f.En~Ul,: C:nUNTY
I [\C-T~T OF cn~/:[,,~~__n\LrY UFVELOFf,~~ttr!- ;
(i.[
HOIL SUHVEY
TAIl['I'; S.---!j'stiJllaletl soi! /Im/i-'
i.l" Ilslt~r'isk ill the first eoll1l11n indicat."s t.hat. lIt b~<;t OIl(' mllpping nnit in that serics is made lip of two or II10re killds of soil. Th(, soils ill slIl.I,
other s"nes that ILppclLrin the first colllll1n of this ta"I". ,\"SI:IICe of dala illdical('" II,aL
Dcpth t.o-
13cdl'Ock I
Scasonal
high
water
tablc I
Dcpth
from
surfacc
of
t.ypical
prolile 1
Chl.<;sificalion
Ullified
AM.;r 10
Coarsc
f rnet.i(Jl1
greaicr
Ihall
:l
illehes
Soil serics alld map symbols
USDA tcxturc
Inches Feet Inches Percent
..\gncw: AgB, AgE,uuhu,u"u >60 1-2 0-9 Silt loam n n. n.. __ U l'vfL 01' CL 1\-'1
9-52 Silty clay loamn__uu CL A-7
52-60 Gravclly silty clay CL A-7 - - - - - - - - --
loam.
'..\hl: AhF, AkFn'h.n_uuuu. 24-40 >5 0-30 Very gravclly loam_h' GI\f, SI\f A-I or 1\-2 0-20
Rock outcrop part of AkF too 30 Basalt.
variablc for valid estimatcs.
. .-\ldcrll'ood:
AIC, AID, AlE, AuCuuuuuu >60 22-3 0-30 Gravelly sandy loam___ S:\1 A.1 01' .-\.2 10-25
For Quilrcnc part of AuC, 30-48 'Vcakly cemcntcd and GI\for S\f A-lor A-2 0-25
sec Quilccnc scrics. vcry compact gravel-
ly sandy loam,
AmC, AmD.n__uu'hun.u glacial till.
>60 22-3 0--33 Gravclly loamnn___.. GM A-4 0-20
33-45 Weakly cemented and G:\1 or 8:\1 A-2 or A.l 0-25
very compact gravel-
ly loam, glacial till.
*Beausite:
BaD, 8aE, BdD, BdE, BeE__.._ 20-36 >5 0-33 Gravelly sandy loam 8M A-lor A-2 25-35
For Alderll'ood part of BdD, and very gravelly
sec Alderwood series, unit sandy loam.
AIC. For Alderwood part of 33 Sandstone con-
BdE, see Alderwood scries, glomerate.
unit AlE. Rock outcrop
part of BeE too variable for
valid estimates.
Bclfast:
Bf_.._.._.._.....___._..___.. >60 3 >5 0-60 Stratified sandy loam, SM or j\1L A.4 0-20
sandy loam, and
loam with sand,
pebbles, and cobbles. ML
Bg..._......__.._._._._.._... >60 3 >5 0-60 Stratificd silt loam, A-4 100
fine sandy loam, and
loam.
Bh..........___.___._.._._... >60 32-4 (}-GO Stratified silt loam and Iv1L or CL A-4 or A-6 100
silty clay loam. i'I'1L or CL
Bk_..........._....._._...._. >60 3 Yz-l 0-60 Stratified silt loam, A.4 or A-6 100
fine sandy loam,
loam and clay loam.
Bm.. __u.. 'U__'n_'_hn'h >60 3 Yz-l 0-20 Silty clay loam and CL A-6 0
sandy clay loam. SM or ML
20-60 Stratified silt loam, A.4 0
finc sandy loam, and
clay loam.
*Calawah: CGB, CND, CVBuuu. >60 2-3 0-40 Silt loam and silty clay [\1L or CL .-\.4 or 1\.6 0
For Snahopish part of eND, loam.
scc Snahopish scries, unit Heavy silty clay loam CL A-7 0
SPD. For Tcalwhit part of 40--60
CVB, sec Tcalwhit scrics, and silty clay.
unit TEB.
Carlsborg: CaC, CaD"__hu,,,,, >60 >5 0-60 Gravclly loamy sandn_ 8Ivf A.l or :\.2 0-10
Casey: SiI[ I "
CdB................_._._._... >60 1-2 0-17 Fine sandy loam. _....
17-60 Clay (with thin layer CH -" ~;-T--~.\-l.~/ -~ -:E .=-~-;-.~~;,:_.L_
of loamy line sand). !i '<i I., I'"' \ I
H ~~} iL.l \ f
. -." II i j I
~. ;J lUll
L,~.J I
I
~-~'FF' ) ,<\P I
ut- I
.-.-- ._-_._---~.._~._-_._.-. --~.-. .._-~~.--"=~- I
JIWFlmSON COUN'l'Y AHI~A, WASIllNGl'ON
(i;')
crties si!/mjicant in en!lincr:rin!l
nlnppini; units may Illlv(, different properties nnd limitntiolls, and for this reHson it is Il(~ecssnry to folio\\' clln.fldly the instrlldions to!' rderrini; [0
;he soil is too variablc 01' thnt no estimate was lllade. > means more than; <, less tlmn]
-_._--------~--~------------------
Pcrccn(Ui;e plLHsinJ,: sieve~'
No.4 No. 10 No. 40 No. 200
(4.7 mm) (2.0 mm) (0.42 mm) (0.074 mill)
PCl'IllCa-
bility
Availuble
wuter
capueity
Reuetion
Shrillk.
swell
paten tinl
Corrosivity tn-
Uncoated
st.eel
Concret.e
Fro,;t-
aelion
potential
11lches per Inches per inch
huur of 80il pll
100 100 90-100 70-80 0.li-2.0 0.16-0.18 5.6-6.5 Low or Iligh__..... I\Ioderate. .. Slight.
moderate.
100 lOa 90-100 80-90 0.2-0.6 O. 18-0.20 6.1-6.5 Modemte.... . High.__.... Low.
80-90 75-85 70.-80 liO-70 0.2-0.6 0.15-0.17 6.6-7.3 Modemte.... . High....... Low.
40-60 30-40 20-35 15-25 0.6-2.0 0.08-0.10 5.6-6.5 Low _ _ .. __ .. . I\-Ioderate.. _ Moderate .. None.
60-70 55-65 25-35 20-30 2.0-6.0 0.07-0.09 5.6-6.5 Low. . ... . . . . :\[odcmte.. . Moderate.. . Slight.
40-70 35-65 20-45 10-30 <0.06 ------------ ---------- Low. . . . . .. . . Moderate.. . ;\Ioderate.
60-70 55-65 45-55 35-45 0.6-2.0 0.12-0.14 - 6.1-6.5 Low... u ----I ]\[oderate.. . Low. . . . u . Slight.
40-70 35-65 30-55 20-35 <0.06 ------------ ---------- Low. . __ .. u . I\Iodemte___ Low. I
60-70 50-65
25-35
15-2;j
2.0-6.0
0.06-0.08 5.6-6.5 Low.. __.. u. l\Iodemte... I\Iodemtc. __ ::\ one.
80-100 70-100
65-80
35-65
0.6-2.0
0.12-0.14 5.6-6. 5 Low.. __ u... Moderate... Moderate.. . None.
100 100 70-8:j 50-80 0.6-2.0 0.15-0.17 5.6-6.5 Low _ _ _. .. . . . Moderate._. Low or ' None.
, g5-100 gO-lOO 80-90 70-85 0.2-0.6 0,19-0.21 6.1-7.3 Low or Moderate... LO:~~~r~.t~~ I Slight.
moderate. r~LI
100 90-100 60-75 50-70 0,2-0,6 0.18-0.20 6.1-7.3 Low or High....... Slight.
moderat.e.
100 9.'HOO 8,j-90 55-85 0.2-0.6 0.17-0.19 6.1-7.3 Moderate. __.. High...... . Low. . . . . . . Sligh t.
100 95-100 70-85 45-65 0.6-2.0 0.14-0.16 6.1-7.3 Low _ _ _ . . '. _ . High.._____ Low.
100 100 95-100 80-95 0,2-0.6 0.17-0.20 4,5-5.0 Low or High.__..__ High..... --I Slight.
moderate. I
100 100 95-100 85-95 0.06-0.2 o . 18-0 . 20 4.5-5.0 Moderate.... . High...____ High.
70-80 45-55
:~0-'1O
10-20
6,0-20.0
0.05-0.07 5,6-6.5 Low...______ Moderate__. i\Ioclerate__. None.
100
100
100
100
li5-80
!l0-100
:1:j-.'iO
80-85
o fl-2.0
<O,(JG
O. ] 3-0. l;i
0.14-0.16
6 . 1-6 . 5
G.6-7,3
Low. . . _ . . . . ./
High".....u
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Legend
To.....ns
@ Co.J~"S::s.:r.
"'" q\..r~ CO'"r.crs
f""</~ Road System
0 Parcefs-H
Boundaries
D ~",",,.,,m
0 't'V&~
0 Co.rr.-~
FOR INFORMATIONAL PURPOSES ONLY-
efferson County does not attest to the accuracy of the data contained herein and makes no warranty with
espect to its correctness or validity. Data contained in this map is limited by the method and accuracy of its
lIection. Mon Au 16 18:36:442004
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@ Co.rr.y s"",
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Li Parcels-H
Contours
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OR INFORMATIONAL PURPOSES ONLY-
efferson County does not attest to the accuracy of the data contained herein and makes no warranty with
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Page I of 1
Parcel Number: 821085002
06/11/2004
Owner Mailing Address:
TODD N COLEBROOK
CYNTHIA F COLEBROOK
21 BARQUE LN
PORT LUDLOW WA 983659729
Site Address:
Section:
Qtr Section:
Township:
Range:
Planning area:
Sub Division:
Land Use Code:
8
SW1j4
28N
lE
Port Ludlow (7)
PORT LUDLOW NO 6
9100 - VACANT LAND
School District:
Rre Dist:
Tax Status:
Tax Code:
Chimacum (49)
Port Ludlow (3)
Taxable
231
Property Description:
PORT LUDLOW NO 6 I LOT 2(REV)V9jPG40-41 8j17-28N-R1E I REVISION V13jP107 I I
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APPENDIX 3 - Storm Water Manual BMPs
for
Erosion, Sediment Control & Drainage Dispersion
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aMP C103: High Visibility Plastic or Metal Fence
Purpose
Conditions of Use
Design and
Installation
Specifications
jl1aintemmce
Standards
..
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Fencing is intended to: (1) restrict clearing to approved limits; (2) prevent
diShlrbance of sensitive areas, their buffers, and other areas required to be
left undisturbed; (3) limit construction traffic to designated construction
entrances or roads; and, (4) protect arcas where marking with survey tape
may not provide adequate protection.
To establish clearing limits, plastic or metal fence may be used:
. At the boundary of sensitive areas. their buffers, and other areas
required to be left uncleared.
. As necessary to control vehicle access to and on the site.
. High visibility plastic fence shall be composed ofa high-density
polyethylene material and shall be at least four feet in height. Posts
for the fencing shall be steel or wood and placed every 6 feet on
center (maximum) or as needed to ensure rigidity. The fencing shall
be fastened to the post every six inches with a polyethylene tie. On
long continuous lengths of fencing, a tension wire or rope soan be
used as a top stringer to prevent sagging between posts. The fence
color shall be high visibility orange. The fence tensile strength shall
be 360 lbs.lft. using the ASTM 04595 testing method.
. Metal fences shall be designed and installed according to the
manufacturer's specifications.
. Metal fences shall be at least 3 feet high and must be highly visible.
. Fences shall not be wired or st<:lpled to trees.
. If the fence has been damaged or visibility reduced, it shall be
repaired or replaced immediately and visibility restored.
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4-6
Volume /I - Construction Storm water Pollution Prevention
August 2001
BMP C105: Stabilized Construction Entrance
Purpose Construction entrances are stabilized to reduce the amount of sediment
transported onto paved roads by vel1icles or equipment by constructing a
stabilized pad of quarry spalls at entrances to construction sites.
Conditions of Use Construction entrances shall be stabilized wherever traffic will be leaving
a construction site and traveling on paved roads or other paved areas
within 1,000 feet of the site.
On large commercial, highway, and road projects, the designer should
include enough extra materials in the contract to allow for additional
stabilized entrances not shown in the initial Construction SWPPP. It is
difficult to detemline exactly where access to these projects will take
place; additional materials will enable the contractor to install them where
needed.
Design and
installation
Specifications
.
See Figure 4.2 for details.
A separation geotextile shall be placed under the spalls to prevent
fine sediment from pumping up into the rock pad. The geotextile
shall meet the following standards:
.
Grab Tensile Strength (ASTM 04751) 200 psi min.
Grab Tensile Elongation (ASTM 04632) 30% max.
Mullen Burst Strength (ASTM 03786-80a) 400 psi min.
AOS (ASTM 04751) 20-45 (U.S. standard sieve size)
.
Consider early instaIlation of the first lift of asphalt in area,> that wiU
paved; this can be used as a stabilized entrance. Also consider the
installation of excess concrete as a stabilized entrance. During large
concrete pours, excess concrete is often available for this purpose.
Hog fuel (wood-based mulch) may be substituted for or combined with
quarry spalls in areas that wiIJ not be used for permanent roads. Hog
fuel is generally less effective at stabilizing construction entrances and
should be used only at sites where the amount of tratlic is very limited.
Hog fuel is not recommended for entrance stabilization in urban areas.
The effectiveness of hog fuel is highly variable and it generally
requires more maintenance than qunny spalls. The inspector may at
any time require the use of quarry spaBs if the hog fuel is not
preventing sediment from being tracked onto pavement or if the hog
fuel is being carried onto pavement. Hog fuel is prohibited in
pcmlanenl roadbeds because organics in the subgrade soils cause
degradation of the subgrade support over time. 1~~--~fi;-:<"~::-:;"<,::"'::]c'::::'~>~-::;::'1
Fencing (see BMPs Cl 03 and, Cl 04) shall be installed fr1\e9f1;s<<ty t~ 11 ~\'l tE fr'\'\ I
restrict traffic to the constructIon entrance. I LJ~ r-~'-----"'''_P'''''~''lll i: i
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4-8
Volume /I - Construction Slormwater Pollution Prevention
DEPTAWgu~~'~QQ1~Y
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/J.laintenallce
Standards
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August 2001
· Whenever possible, the entrance shall be constructed on a fim1,
compacted sub grade. This can substantiaHy increase the effectiveness
of the pad and reduce the need for maintenance.
· Quarry spaBs (or hog fuel) shall be added if the pad is no longer in
accordance with the specifications.
· If the entrance is not preventing sediment from being tracked onto
pavement, then alternative measures to keep the streets free of
sediment shaH be used. This may include street sweeping, an increase
in the dimensions of the entrance, orthe installation ofa wheel wash.
· Any sediment tbat is tracked onto pavement shall be removed by
shoveling or street sweeping. The sediment collected by sweeping
shall be removed or stabilized on site. The pavement shall not be
cleaned by washing down the street, except when sweeping is
ineffective and there is a threat to public safety. U'it is necessary to
wash the streets, the construction of a small sump shall be considered.
The sediment would then be washed into the sump where it can be
controlled.
· Any quarry spalls that are loosened from the pad, which end up on the
roadway shall be removed immediately.
· If vehicles are entering or exiting the site at points other tban the
construction entrance(s), fencing (see BMPs CI03 and el04) shall be
installed to control traffic.
· Upon project completion and site stabilization, all construction
accesses intended as pennanent access tor maintenance shaH be
pennanently stabilized.
Driveway shaN meellhe
requirements of the
pennitting agency
It is recommended that
the entrance be
crowned so that runoff
draIns off the pad
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FI ure 4.2 - Stabilized Construction Entrance -'-.-.. , ,
GeotexUlo
Volume 1/ - Construction Stormw8ter Pollution Proventlon
4-9
BMP C233: Silt Fence
Purpose
Conditions of Use
Design and
Installation
Specifications
'"
Use of a silt fence reduces the transport of coarse sediment from a
construction site by providing a temporary physical barrier to sediment
and reducing the runoff velocities of overland flow. See Figure 4.20 for
details on silt fence construction.
· Silt fence may be used downslope of all disturbed areas.
· Silt fence is not intended to treat concentrated flows, nor is it intended
to treat substantial amounts of overland flow, Any concentrated flows
must be conveyed through the drainage system to a sediment pond.
The only circumstance in which overland flow can be tre<lted solely by
a silt fence, rather than by a sediment pond, is when the area draining
to the fence is one acre or less and flow rates are less than 0.5 cfs.
· Silt fences should not be constructed in streams or used in V-shaped
ditches. They are not an adequate method of silt control for anything
deeper than sheet or overland flow.
Joints in filter fabric shall be splicEKi at
posts. Use staples, wire rings or
equivale~tlo attach fabric to posts
2"x2" by 14 Ga. wire or
equivalent, if standard
strength fabric used ~
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L. /' ~8ackfill.trenSh with native sol /
Post spacing may be increased or 3/4 -1.5 washed gravel
to 8' if wire backing is used. /
2"x2" wood posts, steel fence
posts, or equivalent
Figure 4.20 - Silt Fence
· Drainage area of I acre or less or in combination with sediment basin
in a larger site.
· Maximum slope steepness (normal (perpendicular) to fence line) I: l.
· Maximum sheet or overland flow path length to the fence of 100 feet.
.
No flows greater than 0.5 cis.
The geotextile used shall meet the 1ollowing standards. All geotextile
properties listed below are minimum average roll values (i.c., the test
result for any sampled roll in a lot shall meet or excee9:Jhe~y.~lu~s~::~,"'~"'-"
. . bl. 4 0) ! i '''\\ Is f'J I,; if \\;7
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U.OPMENT
August 2001
Volume II - Construction Slormwater Pollution Preven/lon
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Polymeric Mesh AOS
(ASTM 04751)
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Geote:~~~eS~~dards i If u! s ~ ?iJ04')/
0.60 Olm maximum for slit film wovenS (#30.sicve). o3()' , .-
mm maximum for all other geotextilc types (#50 isiivtiJ:;n;:~', :';'".;,L:'..!.~\'~/!7.'.::Y-'-.J
0.15 mm minimum for all fabric types (#IOOsieveJ//;':C!i;Jr: ' .
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0.02 see-I minilnunl - o.~.~_':_-.:.- r y c!\;
Water Permittivity
(ASTM D4491)
--
Grab Tensile Strength
(ASTM D4632)
180 Ibs. Minimum tor cxtm strength fabric.
100 Ibs minimum for standard strength fabric.
30% maximum
Grab Tensile Strength
(ASTM 04632)
---
Ultraviolet Resistance
(ASTM 04355)
70% minimum
. Standard strength fabrics shall be supported with wire mesh, chicken
wire, 2-inch x 2-inch wire, safety fence, or jute mesh to increase the
strength of the fabric. Silt fence materials are available that have
synthetic mesh backing attached.
. Fitter fabric material shall contain ultraviolet ray inhibitors and
stabilizers to provide a minimum of six months of expected usable
construction life at a temperature range of OOF. to ] 20oF.
. ] 00 percent biodegradable silt fence is available that is strong, long
lasting, and can be left in place after the project is completed, if
pelmitted by local regulations.
. Standard Notes for construction plans and specifications follow. Refer
to Figure 4.20 for standard silt fence details.
The contractor shall install and maintain temporary silt fences at the
locations shown in the Plans. The silt fences shall be constructed in
the areas of clearing, grading, or drainage prior to starting those
activities. A silt fence shall not be considered tempor3lY if the silt
fence must function beyond the life of the contract. The silt fence
shall prevent soil carried by runoff water from going beneath, through,
or over the top of the silt fence, but shall allow the water to pass
through the fence.
The minimum height of the top of silt fence shall be 2 feet and the
maximum height shall be 2Y2 feet above the original ground surface.
The geotextile shall be sewn together at the point of manufacture, or at
an approved location as detennined by the Engineer, to form geotextilc
lengths as required. All sewn seams shall be located at a support post.
Altematively, two sections of silt fence cun be overlapped, provided
the Contractor can demonstrate, to the satist~lction of the Engineer, that
the overlap is long enough and that the adjacent fence sections are
close enough together to prevent silt laden water from escaping
through the fence at the overlap.
Volume /I - Construction Stormwater Pollution Prevention
August 2001
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The geotextile shall be attached on the up-slope side of the posts and
support system with staples, wire, or in accordance with the '. i.
manufacturer's recommendations. The geotextile shall be attached to
the posts in a manner that reduces the potential for geotextile tearing at
the staples, wire, or other connection device. Silt fence back-up
support for the geotextile in the form of a wire or plastic mesh is
dependent on the properties of the geotextile selected for use. Ifwire
or plastic back-up mesh is used, the mesh shall be fastened securely to
the up-slope of the posts with the gcotextile being up-slope of the
mesh back-up support.
The geotextile at the bottom of the fence shall be buried in a trench to
a minimum depth of 4 inches below the ground surface. The trench
shall be baclcfilled and the soil tamped in place over the buried pOltion
of the geotextile, such that no flow can pass beneath the fence and
scouring can not occur. When wire or polymeric back-up support
mesh is used, the wire or polymeric mesh shall extend into the trench a
minimum of 3 inches.
The fence posts shall be placed or driven a minimum of 18 inches. A
minimum depth of 12 inches is allowed if topsoil or other soft
subgrade soil is not present and a minimum depth of 18 inches cannot
be reached. Fence post depths shall be increased by 6 inches ifthe
fence is located on slopes of 3: I or steeper and the slope is
perpendicular to the fence. Ifrequired post deptbs cannot be obtained,
the posts shall be adequately secured by bracing or guying to prevent
overturning of the fence due to sediment loading.
Silt fences shall be located on contour as much as possible, except at
the ends of the fence, where the fence shall be turned uphill such that
the silt fence captures the runoff water and prevents water from
flowing around the end of the fence.
If the fence must cross contours, with the exception of the ends of the
fence, gravel check dams placed perpendicular to the back of the fence
shall be used to minimize concentrated flow and erosion along the
back of the fence. The gravel check dams shalJ be approximately 1-
foot deep at the back of the fence. It shalJ be continued perpendicular
to the fence at the same elevation until the top of the check dam
intercepts the ground surface behind the fence. The gravel check dams
shall consist of crushed surfacing base course, gravel backfiH for
walls, or shoulder ballast. The gravel check dams shall be located
every 10 feet along the fence where the fence must cross contours.
The slope of the fence line where contours must be crossed shall not
be steeper than 3: 1.
Wood, steel or equivalent posts shall be used. Wood posts shall havc
minimum dimensions of 2 inches by 2 inches by 3 feet minimum
length, and shall be free of defects such as knots, splits, or gouges.
August 2001
4-91
Volume 1/ - Construction Slormwater Pollution Prevention
_ ~_ i
"
~r;;~ :1~lrl
Steel post,> shall consist of either size No.6 rebar or IJrger)ASTMA ...... .. j'
120 steel pipe with a mini1l1um diameter of I-inch, UJ '[HL, ,Q1'JErsh~pe(;l)i;,';'TY
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steel posts with a minimum weight of 1.35 Ibs.lft. or 6t1fers-recfpost's;'~) .....~.
having equivalent strength and bending resistance to the post sizes
listed. The spacing of the support posts shall be a maximum of 6 feet.
Fence back-up support, if used, shall consist of steel wire with a
maximum mesh spacing of 2 inches, or a prefabricated polymeric
mesh. The strength of the wire or polymeric mesh shall be equivalent
to or greater than 180 lbs. grab tensile strength. The polymeric mesh
must be as resistant to ultraviolet radiation as the geotextile it supports.
. Silt fence installation using the slicing method specification details
follow. Refer to Figure 4.21 for sl1cing method detalls.
The base ofbotb end posts must be at least 2 to 4 inches above the top
of the silt fence fabric on the middle posts for ditch checks to drain
properly. Use a hand level or string level, if necessary, to mark base
points before installation.
Install posts 3 to 4 feet apart in critical retention areas and 6 to 7 feet
apart in standard applications.
Install posts 24 inches deep on the downstream side of the silt fence,
and as close as possible to the fabric, enabling posts to support the
fabric from upstream water pressure.
Install posts with the nipples facing away from the silt fence fabric.
Attach the fabric to each post with three ties, all spaced within tbe top
8 inches of the fabric. Attach each tie diagonally 45 degrees through
the fabric, with each puncture at least I inch vertically apart. In
addition, each tie should be positioned to hang on a post nipple when
tightening to prevent sagging.
Wrap approximately 6 inches of fabric around the end posts and secure
with 3 ties.
No more than 24 inches of a 36-inch fabric is allowed above ground
level.
The rope lock system must be used in all ditch check applications.
The installation should be checked and corrected for any deviation
before compaction. Use a flat-bladed shovel to tuck fabric deeper into
the ground if necessary.
Compaction is vitally important for effective results. Compact the soil
immediately next to the silt fence fabric with the front wheel of the
tractor, skid steer, or roller exerting at least 60 pounds per square inch.
Compact the upstream side first and then each side twice for a total of
four trips.
,..-.......
'~
4.92
Volume /I - Construction Stormwater Pollution Prevention
August 2001
Maintenance
Standard,'
'""
August 2001
~(s~ ~7" 7: i@
; I''''
!
· Any damage shall be repaired immediateIY'~~::;-:'~\1-crUNTyJ
· [[concentrated flows are evident uphill of the fence, they must be " "'!f:L~~,~~'....J
intercepted and conveyed to a sediment pond.
· H is important to eheck the uphill side of the fence for signs of the
fence clogging and acting as a barrier to flow and then causing
channelization of flows parallel to the fence. If this occurs, replace the
fence or remove the trapped sediment.
· Sediment deposits shall either be removed when the deposit reaches
approximately one-third the height of the silt fence, or a second silt
fence shall be installed.
· If the filter fabric (geotextile) has deteriorated due to ultraviolet
breakdown, it shall be replaced.
......dl... "-19M
........2....
POST SPACING:
r taIIX.. .. ..... "'-II
FLO_
~ -.ax. .n ~ ......
----.-:aFDt.Ic f
1~
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1oIfI. b'..... .tct. of p-est
1Ut..,.. *........ ea.c:h ...... ~
am ~ 2... "......~ ~'.
with IIfhk..~
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~
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POST DUTH.
.... - - FO-.I
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.,~ c...........
~.uac_
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~~~ :-;:~~~/~
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/-~~~J ~ ~~~~
'/,/ '/,/ ~ ' ~ {.(? ".1-' '/,/ '-7
/.~~~1e ~ ~%~~
::v '/,/ -0 'fl <<q- ~ '/,/
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/.~:0~ ~~'\~':.~~
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~~~ ~~~~ ~
4/// 0- 0] :4~~4
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No more than 24- of a 36" fabric
Is aftOW&d above ground.
ATlACIMEHr DEtMS:
. Gaoh.l8bfk:... _.__
. -.. - - pel' poot. aI_ top 8- of labric.
*""->n "ad'llledaoonaly. ~_~
It ........... d yo ..~
. tIang - .. an .. pool "'PPI- and ~-=uely.
Uoe~ _ (5abol Of _.......
RoI 01 sill fence
Post
inoslaIO<I
aIWf
compacllon
SiIIIF~
c~ ..........lIon
Vlbfll!ofy plow II not IllCO!Iptabkl because of hortrontal compaction
Figure 4.21 - Slit Fence Installation by Slicing Method
Volume 1/ - Construction Stormwater Pollution Prevent/on
4-93
1})I-l~ (~11~rll=\Yr-tEF;~:-7
III:!~ ---',11 '
ill ~J J,
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5.3<3 other Practices I ur-~- ,2004 It.
The BMPs described in this section are other gene I pdGtice;s..:fo~~~
treatment of storm water. [.D"pT 0 JE/"F~RS,~)N ~o.ur{fY .1
~::. ' r CO~IMlJ!m'r DEVELOPMENT i
. ~- ---~j
8MP T5.30 Full Dispersion
Purpose and Definition
This BMP allows for "fully dispersing" runoff from impervious surfaces
and cleared areas of development sites that protect at least 65% of the site
(or a threshold discharge area on the site) in a forest or native condition.
Applications and Limitations
· Rural single family residential developments should use these
dispersion BMPs wherever possible to minimize effective impe~ous
surface to less than 10% of the development site.
· Other types of development that retain 65% of the site (or a threshold
discharge area on the site) in a forested or native condition may also
use these BMPs to avoid triggering the flow control facility
requirement
Design Guidelines
· Roof Downspouts
Roof surfaces that comply with the downspout infiltration
requirements in Vol~lme III> Chapter 3> are considered to be "fully
dispersed" (i.e., zero percent effective imperviousness). All other roof
surfaces are considered to be "fully disp~rsed" (i.e., at or approaching
zero percent effective imperviousness) only if they are within a
thrCshold discharge area that is or will be more than 65% forested (or
native vegetative cover) and lesS than 10% impervious (total), AND if
they comply with the downspout dispersion requirements ofBMP
T5.10, and have vegetated flow paths through native vegetation
exceeding 100 feet
· Driveway Dispersion.
Driveway surfaces are considered to be "fully dispersed" if they are
within a threshold discharge area that is or will be more than 65%
forested (or native vegetative cover) and less than 100.10 impervious
(total), AND if they comply with the driveway dispersion BMPs-
BMP 5.11 and BMP T5.12 - and have flow paths through native
vegetation exceeding 100 feel This also holds true for any driveway
surfaces that comply with the roadway dispersion BMPs described
below.
5-20
Volume V -" RunoffTrestment BMPs
'. '. -" August 2001
.
I!D)~j~]L~!~ [ -,-:-1
i i 1''\ I I
~ l! j t ! I
Roadway Dispersion BMPs I: i ! i I Sfi]". 7 2004 i i"
i 'Jlm~~,"~~.___._~.~__l .i i
R?a~way surfaces a:e considered to b7 Itfull~ disp~rs~fd" An~~*,i~~~)~Y)1:~rr OPiv!H " I
WIthin a threshold dIscharge area that IS or wIll be moredthan'65%-.-~:_'"'.. "'"--'
forested (or native vegetative cover) and, less than 10% impervious
(total), AND if they comply with the following dispersion
requirements:
1. Roadway runoff dispersion is allowed only on rural neighborhood
collectors and local access streets. To the extent feasible,
driveways should be dispersed to the same standards as roadways
to ensure adequate water quaiity protection of downstream
resources.
2. The road section shall be designed to minimize collection and
concentration of roadway runoff. Sheet flow over roadway fill
slopes (i.~., where roadway subgrade is above adjacent right-of-
way) should be used wherever possible to avoid concentration.
3. When it is necessary to collect and concentrate runofffrom the
roadway and adjacent upstream areas (e.g., in a ditch on a cut
slope), concentrated flows shall be incrementally discharged from
the ditch via cross culverts or at the ends of cut sections. These
incremental discharges of newly concentrated flows shall not
exceed 0.5 cfs at anyone discharge point from a ditch for the 100-
year runoff event Where flows at a 'particular ditch discharge
point were already concentrated under existing site conditions
(e.g., in a natural channel that crosses the roadway alignment), the
O.5-cfs limit would be ill addition to the existing concentrated peak
flows.
4. Ditch discharge points with up to 0.2 cfs discharge for the peak.
1 DO-year flow~sliaIl use'rOck pads or disPersion trenches to
disperse flows. Ditch discharge points with between 0.2 and 0.5
cfs discharge for the lOO-year peak flow shall use only dispersion
trenches to disperse flows.
5. Dispersion trenches shall be designed to accept surface flows (free
discharge) from a pipe, culvert, or ditch end, shall be aligned
perpendicular to the flowpath, and shall be minimum 2 feet by 2
feet in section, 50 feet in length, filled with %-inch to 1 %..inch
washed rock, and provided with a level notched grade board (see
Figure 5.2). Manifolds may be used to split flows up to 2 cfs
discharge for the IOO-year peak flow between up to 4 trenches.
Dispersion trenches shall have a minimum spacing of 50 feet.
6. After being dispersed with rock pads or trenches, flows from ditch
discharge points must traverse a minimum of 100 feet of
undisturbed native vegetation before leaving the project site, or
._.';_'~_..:....:..:..-;...'-=-__.::;:c=::::=--. . ___._____.____~._
August 2001
Volume V - Runoff Iroatment.BMP.$.:____...... ..~~..'...,~.. ....... ...6::?L""H'
~I~ 8~o~~:4~1~1
.. Ii
i
~~~~~~r::~:~~;~:~e~el carrying eXiS~g..coIiceiJtraied\~\(.____~J
Note: In order to provide the laO-foot jlowpath length to an
existing channel, some roadway runoff may unavoidably enter the
channel undispersed Also note that water quality treatment may
be waived for roadway runoff dispersed through 100 feet of
undisturbed native vegetation.
7. Flowpaths from adjacent discharge points must not intersect within
the 100- foot flowpath lengths, and dispersed flow from a discharge
point must not be mtercepted by another discharge point. To
enhance the flow control and water quality effects of dispersion,
the flowpath shall not exceed 15% slope, and shall be located
within designated open space.
Note: Runoff may be conveyed to an area meeting these jlowpath
criteria.
./
8. Ditch discharge points shall be located a minimum of 100 feet
upgradient of steep slopes (i.e., slopes steeper than 40%), wetlands,
and streams.
9. Where the Local Plan Approval Authority determines there is a
potential for significant adverse impacts downstream (e.g., erosive
steep slopes or existing downstream drainage problems),
dispersion of roadway runoff may not be allowed, or other
measures may be required.
Cleared Area Dispersion BMPs
.
The runoff from cleared areas that are comprised of bare soil, non-
native landscaping, lawn, and/or pasture is considered to be "fully
dispersed" ifit is dispersed through at least 25 feet of native vegetation
in accordance with the following criteria:
1. The contributing flowpath of cleared area being dispersed must be
no more than 150 feet, AND
2. Slopes within the 25-foot minimum flowpath through native
vegetation should be no steeper than 8%. If this criterion can not
be met due to site constraints, the 25-foot flowpath length must be
increased 1.5 feet for each percent increase in slope above 8%.
5-22
Volume V - Runoff Treatment BMPs
August 2001
15) ~ tC IE n Wi IE ln1l
..nl S FP - 7 ?004. llJ)
BMP T5.1 0 Downspout Dispersion
Purpose and Definition
I I
.!UHRS()N r.O! INTY
; firTT nr r.ryc.l/I}! !~!iT'{ flE\lt!.OP~.,~ENT i
I .-..-___.___~_,......_,~-I
Downspout dispersion BMPs are splashblocks or gravel-filled trenches
that serve to spread roof runoff over vegetated pervious areas. Dispersion
attenuates peak flows by slowing entry of the runoff into the conveyance
system, allows for some infiltration, and provides some water quality
benefits.
Applications and Limitations
· Downspout dispersion is required on all subdivision single family lots
which meet one of the following criteria:
1. Lots greater than or equal to 22,000 square feet where downspout
infiltration is not being provided according to the requirements in
Volume III, Chapter 3.
2. Lots smaller than 22,000 square feet where soils are not suitable
for downspout infiltration as determined in Volume III, Chapter 3
and where the..design criteria below can be met.
· All other projects required to apply Roof Downspout BMPs must
provide downspout dispersion if downspout infiltration is not feasible
or applicable as determined in Volume III, Chapter 3, and if the design
criteria below can be met.
General Design Guidelines
· Dispersion trenches designed as shown in the Figures 5.1 and 5.2 shall
be used for all downspout dispersion applications except where
splashblocks are allowed below. See Figure 5.3 for a typical
splashblock.
· Splashblocks may be used for downspouts discharging to a vegetated
flowpath at least 50 feet in length as measured from the downspout to
the downstream property line, structure, sensitive steep slope, stream,
wetland, or other impervious surface. Sensitive area buffers may
count toward flowpath lengths. The vegetated flowpath must be
covered with well-established lawn or pasture, landscaping with well-
established groundcover, or native vegetation with natural
groundcover. The groundcover shall be dense enough to help disperse
and infiltrate flows and to prevent erosion.
· If the vegetated flowpath (measured as defined above) is less than 25
feet on a subdivision single-family lot, a perforated stub-out
connection may be used in lieu of downspout dispersion (See Volume
III, Chapter 3). A perforated stub-out may also be used where
implementation of downspout dispersion might cause erosion or
flooding problems, either on site or on adjacent lots. This provision
might bc appropriatc, for example, for lots constructcd 011 steep hills
August 2001
5-3
Volume V - Runoff Treatment BMPs
1- -. . ..- .
,~r~ s~p~: :4~ I~
i
,
I i
where downspout discharge could be cumulative and mightposeraIRSON COUNTY
potential hazard for lower lying lots, or where dispersed flows couiCi""'^" nF\'~i~'!""
create problems for adjacent offsite lots. This provision does not apply
to situations where lots are flat and onsite downspout dispersal would
result in saturated yards.
----'
Note: For all other types ofprojects, the use of a peiforated stub-out in lieu
of downspout dispersion shall be as determined by the Local Plan Approval
Authority.
4>> pat pir:e
1 iii' . 8/..," washed rock
TRENCH X-SECTION
NTS
slcpe-
:~ modi catch basin or yard drai n
I
:::; 700 sq. ft.
2' ;~ 1CI
levEl trencl"Bs
:> 700 sq. ft.
Tyr:e I CB
st an d3.rd
disj::ersion trench
wi mtcl"Bd grace board
lergh 1 a per 700 sq ft
of roof area,
PLAN VIEW OF ROOF
NTS
Figure 5.1 Typical Dispersion Trench
5.4
Volume V - Runoff Treatment BMPs
August 2001
Q
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erd caporph.g
llCMI to second
d ispersaJ ~/l2 r-.:; h
if necessary
. c lean ou~ w)Ii! from pipe
. 4" 0 r 6" perbraed pipe lad flatJlevel
t
notched
9 ra:Je board
2'':>:: 2' notches
18'0.C.
t
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inflU2 n~ pipe (max cBs!;) n
fbw ~ 0.5 C FS per ~renc h)
o
type I CB
'hvsold COV2r
.........
t
PLAN
NTS
fl::w to o~t-e r
brar-.:;hing C8's
as necessary
1'.0
min
(pipe 0 D.
,I11'D
min.
I 18'0.C I
-r--~//,..__- ~ ~2"
T~---'~~~v=t
\/---
2"gracE . T
board rDtct",s 2"
SECTION A-A
NTS
rWTES:
i. Th is ~/l2 r~ h st811 t", con5truc~d so
as b pre\o'en~ poi nt di9:: t.=<rge 3nd,Q r
elDsDn.
2. Trenct",s moo! be placed no cbser
~han 50 fee~ b one 3rot~'" r (100 feet
abrg fbwline)
3. TrenchardgracE toad mlJ5tbe
1eV21. A I!;) n to foll:.w con~olJrsofsie.
4. Su P p:> rt post spac ing 3S r-=qlJire::J by
so il co rd nons t.o ensu Ie 9 racE board
remains level.
"15"10 rrox fer 11 0)/ cmtrov\'later qJ8J ity
treat rreti in rural areas.
Figure 5.2 Standard Dispersion Trench with Notched Grade Board
August 2001
Volume V - Runoff Treatment BMPs
5-5
roc(
dO\vl1spoiJ
serves up
to 700 s1.
d ro c(
rr;~:~~~~~~~~e;~<~"--\~'-.:; :;7l
I ~J (;~(~:l~' .:j[lJ) I
,/ [i+ [f1 SON 'COliN'fV
nEPT OF COMMlH~!TY otVELOPMl:NT
-,~._--~-_. --~ - ~---- -- ~---------.:~._"
50'min.
veg elate d
noVl path
\ spas h
_\ ti ock
do\vl1s poli: ex! emi on
NTS
splash
block
Figure 5.3 Typical Downspout
Splashblock Dispersion
Additional Design Criteria For Dispersion Trenches
· A vegetated flowpath of at least 25 feet in length must be maintained
between the outlet of the trench and any property line, structure,
stream, wetland, or impervious surface. A vegetated flowpath of at
least 50 feet in length must be maintained between the outlet of the
trench and any steep slope. Sensitive area buffers may count towards
flowpath lengths.
· Trenches serving up to 700 square feet of roof area may be simple I a-
foot-long by 2-foot wide gravel filled trenches as shown on Figure 5- 1.
For roof areas larger than 700 square feet, a dispersion trench with
notched grade board as shown in Figure 5-2 may be used as approved
by the Local Plan Approval Authority. The total length of this design
must provide at least 10 feet of trench per 700 square feet of roof area
and not exceed 50 feet.
· A setback of at least 5 feet must be maintained between any edge of
the trench and any structure or property line.
· No erosion or flooding of downstream properties may result.
· Runoff discharged towards landslide hazard areas must be evaluated
by a geotechnical engineer or qualified geologist. The discharge point
5-6
Volume V - Runoff Treatment BMPs
August 2001
ImnO)/ fE ~ InlnEl~.1
L ~I SE/' ~ 7 2004 hi i
I L_ I
may not be placed on or above slopes greater than 2P0i or a~ils.~
erosion hazard areas without evaluation by a geotechA;:cfal ~[lgnte'ftr'9l); O~~lJOPMP'
qualified geologist and jurisdiction approval. --------:.
· For sites with septic systems, the discharge point must be
downgradient of the drainfield primary and reserve areas. This
requirement can be waived by the jurisdiction's pennit review staff if
site topography will clearly prohibit flows from intersecting the
drainfield.
Additional Design Criteria For Splash blocks
In general, if the ground is sloped away from the foundation, and there is
adequate vegetation and area for effective dispersion, splashblocks will
adequately disperse storm runoff If the ground is fairly level, if the
structure includes a basement, or if foundation drains are proposed,
splashblocks with downspout extensions may be a better choice because
the discharge point is moved away from the foundation. Downspout
extensions can include piping to a splashblock/discharge point a
considerable distance from the downspout, as long as the runoff can travel
through a well-vegetated area as described below.
The following conditions must be met to lIse splashblocks:
· A vegetated flowpath of at least 50 feet must be maintained between
the discharge point and any property line, structure, steep slope,
stream, wetland, lake, or other impervious surface. Sensitive area
buffers may cOllnt toward flowpath lengths.
· A maximum of 700 square feet of roof area may drain to each
splashblock.
· A splashblock or a pad of crushed rock (2 feet wide by 3 feet long by 6
inches deep) shall be placed at each downspout discharge point.
· No erosion or flooding of downstream properties may result.
· Runoff discharged towards landslide hazard areas must be evaluated
by a geotechnical engineer or qualified geologist. Splashblocks may
not be placed on or above slopes greater than 20% or above erosion
hazard areas without evaluation by a geotechnical engineer or
qualified geologist and approval by the Local Plan Approval
Authority.
· For sites with septic systems, the discharge point must be downslope
of the primary and reserve drain field areas. This requirement can be
waived by the Local Plan Approval Authority if site topography
clearly prohibits flows from intersecting the drainfield.
August 2001
5-7
Volume V - Runoff Treetment BMPs
Ii 0-)'] '-'- !,
I L.: ~ 1,'----....--.-.--.
,r,.1
BMP T5.11 Concentrated Flow Dispersion I U Ui::; 7
Purpose and Definition I I.... ."C,'C"""
Jr-,. ",,",(,
Dispersion of concentrated flows from driveways or othef"p'C:ly~~~~t;';-ii~;~Y
through a vegetated pervious area attenuates peak flows by slowing'entry
of the runoff into the conveyance system, allows for some infiltration, and
provides some water quality benefits. See Figure 5.4.
Applications and Limitations
r->=---
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· Any situation where concentrated flow can be dispersed through
vegetation.
· Dispersion for driveways will generally only be effective for single-
family residences on large lots and in rural short plats. Lots proposed
by short plats in urban areas will generally be too small to provide
effective dispersion of driveway runoff.
· Figure 5.4 shows two possible ways of spreading flows from steep
driveways.
Design Guidelines
· A vegetated flowpath of at least 50 feet should be maintained between
the discharge point and any property line, structure, steep slope,
stream, lake, wetland, lake, or other impervious surface.
· A maximum of 700 square feet of impervious area may drain to each
dispersion BMP.
· A pad of crushed rock (2 feet wide by 3 feet long by 6 inches deep)
shall be placed at each discharge point.
· No erosion or flooding of downstream properties may result.
· Runoff discharged towards landslide hazard areas must be evaluated
by a geotechnical engineer or qualified geologist. The discharge point
shall not be placed on or above slopes greater than 20% or above
erosion hazard areas without evaluation by a geotechnical engineer or
qualified geologist and approval by the Local Plan Approval
Authority.
· For sites with septic systems, the discharge point should be
downgradient of the drainfield primary and reserve areas. This
requirement may be waived by the Local Plan Approval Authority if
site topography clearly prohibits flows from intersecting the drain field.
5-8
Volume V - Runoff Treatment BMPs
August 2001
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:steep Driveway \-liltl1 Diagonal Berms
~/ ~/ ~/ , ~~I .nn-n-H!
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( I 25' from ROW if'f- J
I ) d rhrg....a y sb;:>gSI:r: I
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:Steeo Drivewav Vlitl1 Slotted Drains
Figure 5.4 Typical Concentrated Flow Dispersion for Steep Driveways
August200t
5-9
Volume V - Runoff Treatment BMPs
,0.'''''"''__<,. r""::'..:/ '<<iJ (~~':l P. \1 .,-; i::::J . ';'
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,JEFFEHSON COUNT'! -
Purpose and Definition OEPT. OF COMMUNITY DEVELOPMEW
-------. ._~~-~~~=-~-_._-_!
Sheet flow dispersion is the simplest method of runoff control. This BMP
can be used for any impervious or pervious surface that is graded so as to
avoid concentrating flows. Because flows are already dispersed as they
leave the surface, they need only traverse a narrow band of adjacent
vegetation for effective attenuation and treatment.
Applications and Limitations
Flat or moderately sloping (< 15% slope) impervious surfaces such as
driveways, sport courts, patios, and roofs without gutters; sloping cleared
areas that are comprised of bare soil, non-native landscaping, lawn, and/or
pasture; or any situation where concentration of flows can be avoided.
BMP T5.12
Sheet Flow Dispersion
Design Guidelines
· See Figure 5.5 for details for driveways.
· A 2-foot-wide transition zone to discourage channeling should be
provided between the edge of the driveway pavement and the
downslope vegetation, or under building eaves. This may be an
extension of subgrade material (crushed rock), modular pavement,
drain rock, or other material acceptable to the Local Plan Approval
Authority.
· A vegetated buffer width of 10 feet of vegetation must be provided for
up to 20 feet of width of paved or impervious surface. An additional 5
feet of width must be added for each addition 20 feet of width or
fraction thereof.
· A vegetated buffer width of 25 feet of vegetation must be provided for
up to 150 feet of contributing cleared area (i.e., bare soil, non-native
landscaping, lawn, and/or pasture). Slopes within the 25- foot
minimum flowpath through vegetation should be no steeper than 8
percent. If this criterion cannot be met due to site constraints, the 25-
foot flowpath length must be increased 1.5 feet for each percent
increase in slope above 8%.
· No erosion or flooding of downstream properties may result.
· Runoff discharge toward landslide hazard areas must be evaluated by a
geotechnical engineer or a qualified geologist. The discharge point
may not be placed on or above slopes greater than 20% or above
erosion hazard areas without evaluation by a geotechnical engineer or
qualified geologist and approval by the Local Plan Approval
Authority.
· For sites with septic systems, the discharge point must be
downgradient of the drainfield primary and reserve areas. This
requirement may be waived by the Local Plan Approval Authority if
site topography clearly prohibits flows from intersecting the draintield.
5-10
Volume V - Runoff Treatment BMPs
Augusl 2001
6" m in
BERM DETAIL
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August 2001
Volume V - Runoff Treatment BMPs
5-11
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BMP T5.13 Post-Construction Soil Quality and pepth !
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Purpose and Definition I n )Ef'fERSON COUNTY
: "EP!_ 9~ CO~MUNI!Y DEVEl.OPi',
Naturally occurring (undisturbed) soil and vegetation provide import~ni'---
stonnwater functions including: water infiltration; nutrient, sediment, and
pollutant adsorption; sediment and pollutant biofiltration; water interflow
storage and transmission; and pollutant decomposition. These functions
are largely lost when development strips away native soil and vegetation
and replaces it with minimal topsoil and sod. Not only are these important
stonnwater functions lost, but such landscapes themselves become
pollution- generating pervious surfaces due to increased use of pesticides,
fertilizers and other landscaping and household/industrial chemicals, the
concentration of pet wastes, and pollutants that accompany roadside litter.
Establishing soil quality and depth regains greater stormwater functions in
the post development landscape, provides increased treatment of
pollutants and sediments that result from development and habitation, and
minimizes the need for some landscaping chemicals, thus reducing
pollution through prevention.
Applications and Limitations
Establishing a minimum soil quality and depth is not the same as
preservation of naturally occurring soil and vegetation. It also does not
maximize the stonnwater functions that could be attained through greater
soil depth and more specialized fonnulations as presented in BMP T5.35,
Engineered Soil/Landscape Systems. However, establishing a minimum
soil quality and depth will provide improved on-site management of
stonnwater flow and water quality.
Soil organic matter can be attained through numerous materials such as
compost, composted woody material, biosolids, and forest product
residuals. It is important that the materials used to meet the soil quality
and depth BMP be appropriate and beneficial to the plant cover to be
established. Likewise, it is important that imported topsoils improve soil
conditions and do not have an excessive percent of clay fines.
Design Guidelines
· Soil retention. The duff layer and native topsoil should be retained in
an undisturbed state to the maximum extent practicable. In any areas
requiring grading remove and stockpile the duff layer and topsoil on
site in a designated, controlled area, not adjacent to public resources
and critical areas, to be reapplied to other portions of the site where
feasible.
· Soil quality. All areas subject to clearing and grading that have not
been covercd by imperviolls surface, incorporated into a drainagc
I~lcjlity or engineered as structural filial' slope shall, at project
eomplelion, demonstrate the following:
5-12
Volume V ~ Runoff Treatment BMPs
August 2001
August 2001
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1. Retention or enhancement of the moisture infi!ltratic)ll Hll~-9t}iL~QiL_.____1
moisture holding capacity of the original undisturbedsofJn~'ti\'eto ",,~
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the site. Areas which have been compacted or have removed some
or all of the duff layer or underlying top soil shall be amended to
mitigate for lost moisture infiltration and moisrure holding
capacity; and
2. A topsoil layer with a minimum organic matter content of ten
percent dry weight and a pH from 6.0 to 8.0 or matching the pH of
the original undisturbed soil. The topsoil layer shall have a
minimum depth of eight inches except where tree roots limit the
depth of incorporation of amendments needed to meet the criteria.
Subsoils below the topsoil layer should be scarified at least 4
inches with some incorporation of the upper material to avoid
stratified layers, where feasible.
· These criteria can be met by using on-site native topsoil, incorporating
amendments into on-site soil, or importing blended topsoil. Ifblended
topsoil is imported, then fines should be limited to twenty-five percent
passing through a 200 sieve.
· The resulting soil should be conducive to the type of vegetation to be
established.
jVf aintenance
· Soil quality and depth should be established toward the end of
construction and once established, should be protected from
compaction, such as from large machinery use, and from erosion.
· Soil should be planted and mulched after installation.
· Plant debris or its equivalent should be left on the soil surface to
replenish organic matter.
· It should be possible to reduce use of irrigation, fertilizers, herbicides
and pesticides. These activities should be adjusted where possible,
rather than continuing to implement formerly established practices.
Volume V - Runoff Treatment BMPs
5-13
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Th~ two BMPs m th~s sectIOn are general practices P~~s.~(!~'lljt,UNnY DEVEL~PMEN~,_
mamtenance at the SIte.
BMP T5.20 Preserving Natural Vegetation
Purpose And Definition
Preserving natural vegetation on-site to the maximum extent practicable
will minimize the impacts of development on stonnwater runoff.
Preferably 65 percent or more of the development site should be protected
for the purposes of retaining or enhancing existing forest cover and
preserving wetlands and stream corridors.
Applications and Limitations
New development often takes place on tracts of forested land. In fact,
building sites are often selected because of the presence of mature trees.
However, unless sufficient care is taken and planning done, in the jnterval
between buying the property and completing construction much of this
resource is likely to be destroyed. The property owner is ultimately
responsible for protecting as many trees as possible, with their understory
and groundcover. This responsibility is usually exercised by agents, the
planners, designers and contractors. It takes 20 to 30 years for newly
planted trees to provide the benefits for which trees are so highly valued.
Forest and native growth areas allow rainwater to naturally percolate into
the soil, recharging ground water for summer stream flows and reducing
surface water runoff that creates erosion and flooding. Conifers can hold
up to about 50 percent of all rain that falls during a stonn. Twenty to 30
percent of this rain may never reach the ground but evaporates or is taken
up by the tree. Forested and native growth areas also may be effective as
stonnwater buffers around smaller developments.
On lots that are one acre or greater, preservation of 65 percent or more of
the site in natural vegetation will allow the use of full dispersion
techniques presented in BMP T5.30. Sites that can fully disperse are not
required to provide runoff treatment or flow control facilities.
Design Guidelines
· The preserved area should be situated to minimize the clearing of
existing forest cover, to maximize the preservation of wetlands, and to
bu frcr stream corridors.
· The preservcd area should bc placed in a scparate tract or protected
through recorded easemcnts for individual lots.
5-14
Volume V - Runoff Troatment BMPs
August 2001
· If feasible, the preserved area should be located downslope from the
building sites, since flow control and water quality are enhanced by
flow dispersion through duff, undisturbed soils, and native vegetation.
· The preserved area should be shown on all property maps and should
be clearly marked during clearing and construction on the site.
Maintenance
· Vegetation and trees should not be removed from the natural growth
retention area, except for approved timber harvest activities and the
removal of dangerous and diseased trees.
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JEFFEf1S0f'.,! COUNTY
DEPT. OF COMMUNiTY DEVELOPMENT
lIugust 2001
Volume V - Runoff Troatment BMPs
5-15
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BMP T5.21 Better Site Design U U I SEP . ;)004 I W
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urpose an eJlmtlOn JUrEf\SUr~C;(llTfiFy'
DEPT. OF COMMUNITY DCVELOPMElfr
Fundamental hydrological concepts and stonnwater management concepts"~-'~.
can be applied at the site design phase that are:
· more integrated with natural topography,
· reinforce the hydrologic cycle,
· more aesthetically pleasing, and
· often less expensive to build.
A few site planning principles help to locate development on the least
sensitive portions of a site and accommodate residential land use while
mitigating its impact on stonnwater quality.
Design Guidelines
· Define Development Envelope and Protected Areas - The first step
in site planning is to define the development envelope. This is done by
identifying protected areas, setbacks, easements and other site features,
and by consulting applicable local standards and requirements. Site
features to be protected may include important existing trees, steep
slopes, erosive soils, riparian areas, or wetlands.
By keeping the development envelope compact, environmental
impacts can be minimized, construction costs can be reduced, and
many of the site's most attractive landscape features can be retained.
In some cases, economics or other factors may not allow avoidance of
all sensitive areas. In these cases, care can be taken to mitigate the
impacts of development through site work and other landscape
treatments.
· Minimize Directly Connected Impervious Areas - Impervious areas
directly connected to the stonn drain system are the greatest
contributors to urban nonpoint source pollution. Any impervious
surface that drains into a catch basin or other conveyance structure is a
"directly connected impervious surface." As stormwater runoff flows
across parking lots, roadways, and other paved areas, the oil, sediment,
metals, and other pollutants are collected and concentrated. If this
runoff is collected by a drainage structure and carried directly along
impervious gutters or in sealed underground pipes, it has no
opportunity for filtering by plant material or infiltration into the soil.
It also increases in velocity and amount, causing increased peak-flows
in the winter and decreased base-flows in the summer.
5-16
Volume V - Runoff Treatment BMPs
August 2001
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minimize these directly connected impervious areas. Ihis d3n-be-dQn.e~.~....... ~'_'
b~ limi~ing overall impervio~s land ~overage or by int~tr~\n~-l~~atITj~~~Wi:~~roP
dlspersmg runoff from these ImpervIOUS areas. ---.---__~___..
· Maximize Permeability - Within the development envelope, many
opportunities are available to maximize the permeability of new
construction. These include minimizing impervious areas, paving with
permeable materials, clustering buildings, and reducing the land
coverage of buildings by smaller footprints. All of these strategies
make more land available for infiltration and dispersion through
natural vegetation.
Clustered driveways, small visitor parking bays and other strategies
can also minimize the impact of transportation-related surfaces while
still providing adequate access.
Once site coverage is minimized through clustering and careful
planning, pavement surfaces can be selected for permeability. A patio
of brick- on-sand, for example, is more permeable than a large concrete
slab. Engineered soil/landscape systems are permeable ground covers
suitable for a wide variety of uses. Permeable/porous pavements can
be used in place of traditional concrete or asphalt pavements in many
low traffic applications.
Maximizing permeability at every possible opportunity requires the
integration of many small strategies. These strategies will be reflected
at all levels of a project, from site planning to materials selection. In
addition to the environmental and aesthetic benefits, a high-
permeability site plan may allow the reduction or elimination of
expensive runoff underground conveyance systems, flow control and
treatment facilities, yielding significant savings in development costs.
· Build Narrower Streets - More than any other single element, street
design has a powerful impact on stormwater quantity and quality. In
residential development, streets and other transportation-related
structures typically can comprise between 60 and 70 percent of the
total impervious area, and, unlike rooftops, streets are almost always
directly connected to the storm water conveyance system.
The combination of large, directly connected impervious areas,
together with the pollutants generated by automobiles, makes the street
network a principal contributor to stonnwater pollution in residential
areas.
Street design is usually mandated by local municipal standards. These
standards have been developed to facilitate efficient automobile traffic
August 2001
5-17
Volume V - Runoff Treatment BMPs
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and maximize parking. Most require large impervious Hmd coverage. I
In recent years, new street standards have been gaihing kcc~pf~QG~"ftlil~F~:'T'/""
meet the access requirements of local residential stteets\.vhi1'e're'duEihg', F!1f'~,"H
impervious land coverage. These standards generally create a new
class of street that is narrower than the current local street standard,
called an "access" street. An access street is intended only to provide
access to a limited number of residences.
Because street design is the greatest factor in a residential
development's impact on stonnwater quality, it is important that
designers, municipalities and developers employ street standards that
reduce impervious land coverage.
· Maximize Choices for Mobility - Given the costs of automobile use,
both in land area consumed and pollutants generated, maximizing
choices for mobility is a basic principle for environmentally
responsible site design. By designing residential developments to
promote alternatives to automobile use, a primary source of
stonnwater pollutien can be mitigated.
Bicycle lanes and paths, secure bicycle parking at community centers
and shops, direct, safe pedestrian connections, and transit facilities are
all site-planning elements that maximize choices for mobility.
· Use Drainage as a Design Element - Unlike conveyance stonn drain
systems that hide water beneath the surface and work independently of
surface topography, a drainage system for stormwater infiltration or
dispersion can work with natural land forms and land uses to become a
major design element of a site plan.
By applying storm water management techniques early in the site plan
development, the drainage system can suggest pathway alignments,
optimum locations for parks and play areas, and potential building
sites. In this way, the drainage system helps to generate urban fonn,
giving the development an integral, more aesthetically pleasing
relationship to the natural features of the site. Not only does the
integrated site plan complement the land, it can also save on
development costs by minimizing earthwork and expensive drainage
features.
5.18
Volume V - Runoff Treatment BMPs
August 2001
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APPENDIX 4 - Storm Water Manual References
Jefferson County Department Of Community Development
STORMWATER MANAGEMENT HANDOUT
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Select definitions from the 2001 Department of ~?:olo~. i IJ\ \ I
Stormwater Management Manual jOr Western W ashi1ig.\!n\:~:;, . \~ \
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2.3 Definitions Related toMinimum Req1~l~~EI~J~:&~Iu~~
A full listing and definition of stonnwater-related words and phrases that
are used in this manual is given in the glossary. A few of the key
definitions are listed here for ease in understanding the requirements that
follow.
· Arterial- A road or street primarily for through traffic. A major
arterial connects an Interstate Highway to cities and counties. A minor
arterial connects major arterials to collectors. A collector connects an
arterial to a neighborhood.. A collector is not an arterial. A local
access road connects individual homes to a collector.
· Effective Impervious surface - Those impervious surfaces that are
connected via sheet flow or discrete conveyance to a drainage system.
Impervious surfaces on residential development sites are considered
ineffective if the runoff is dispersed through at least one hundred feet
of native vegetation in accordance with BMP T5.30 ~ "Full
Dispersion," as described in Chapter 5 of Volume V.
· Highway - A main public road connecting towns and cities
· Impervious surface - A hard surface area that either prevents or
retards the entry of water into the soil mantle as under natural
conditions prior to development. A hard surface area which causes
water to run off the surface in greater quantities or at an increased rate
of flow from the flow present under natural conditions prior to
development. Common impervious surfaces include, but are not
limited to, roof tops, walkways, patios, driveways, parking lots or
storage areas, concrete or asphalt paving, gravel roads, packed earthen
materials, and oiled, macadam or other surfaces which similarly
impede the natural infiltration of stormwater. Open, uncovered
retention/detention facilities shall not be considered a.s impervious
surfaces for purposes of determining whether the thresholds for
application of minimum requirements are exceeded. Open, uncovered
retention/detention facilities shall be considered impervious surfaces
for purposes of runoff modeling.
2-4
Volume 1- MInimum TechnIcal Requirements
August 2001
August 2001
.
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Replaced impen'ilJlIs surface - For structures, the remov' I and!
replacement of any exterior impervious surfaces or found4tion. Lfgril-ij~si}i~-c(ilr7fY.
other impervious surfaces, the removal down to bare soil {rTI!:!rS-eDF COMrv\U~~.I1Y_Dt~ELopr...'EN"r
course and replacement.
.
Site - The area defined by the legal boundaries of a parcel or parcels
of land that is (are) subject to new development or redevelopment. For
road projects, the length of the project site and the right-or-way
boundaries define the site.
.
Source control Bll1P - A structure or operation that is intended to
prevent pollutants from coming into contact with stonmvater through
physical separation of areas or careful management of activities that
are sources ofpolllltants. This manual separates source control BMPs
into two types. Structural Source Control Bl\1Ps are physical,
stmctural, or mechanical devices, or facilities that are intended to
prevent pollutants trom entering stonnwater. Operational Bli-{Ps are
non-stmctural practices that prevent or reduce pollutants trom entering
stonmvatcr. See Volume IV for details.
.
Threshold Discharge Area - An onsite area draining to a single
natural discharge location or multiple natural discharge locations that
combine within one-quarter mile downstream (as detennincd by the
shortest tlowpath). The examples in Figure 2.1 below illustrate this
definition. The purpose of this definition is to clarify how the
thresholds of this manual are applied to project sites with multiple
discharge points.
Exan\jNe of a Project Site
with a Slngkt twuraI
Dlsdmrge and a SIngIQ
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-------_._-~---~------
Volume 1- Minimum Technical Requirements 2-7
.
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LalUJ disturbing activi(J' - Any activity that results in movbnen,trok;,;
earth, or a change in the existing soil cover (both veg ~mfiveQll;~6!ri:op~!:"i'~" "',
vegetative) and/or the existing soil topography. Land disturbIng....
activities include, but are not limited to clearing, grading, filling, and
excavation. Compaction that is associated with stabilization of
structures and road construction shall also be considered a land
disturbing activity. Vegetation maintenance practices are not
considered land-disturbing activity.
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. Jl-{aintenance - Repair and maintenance includes activities conducted
on currently serviceable structures, facilitie.s, and equipment that
involves no expansion or use beyond that previously existing and
results in no significant adverse hydrologic impact. It includes those
usual activities taken to prevent a decline, lapse, or cessation in the use
of structures and systems. Those usual activities may include and
replacement of disfunctioning facilities, including cases \-vhere
environmental permits require replacing an existing structure with a
different type structure, as long as the functioning characteristics of the
original structure are not changed. One example is the replacement of
a collapsed, fish blocking, round culvert with a new box culvert under
the same span, or width, ofroadway. For further details on the
application of this manual to various road management fi.mctions,
please see Section 2.2.
o Native vegetation - Vegetation comprised of plant species, other than
noxious weeds, that are indigenous to the coastal region of the Pacific
Northwest and which reasonably could have been expected to
naturally occur on the site. Examples include trees such as Douglas
Fir, western hemlock, western red cedar, alder, big-leaf maple, and
vine maple; shrubs such as willow, elderberry, salmonberry, and salat
and herbaceous plants such as sword fern, foam flmver, and fire\vecd.
. New development - Land disturbing activities, including Class IV -
gencral forest practices that arc conversions from timber land to other
uses: structural development, including construction or installation of a
building or other stnlcture; creation of impervious surhlces: and
subdivision, short subdivision and binding site plans, as defined and
applied ill Chapter 58.17 RCW. Projects meeting the definition of
redevelopment shall not be considered new development.
. Pollution-generating impervious surface (PGlS) - Those impervious
suri~lces considered to bc a significant source of pollutants ill
storm water runoff. Such surfaces include thosc which (]rc subject to:
vehicular use; industrial activities (as fUlther defined in the glossary):
or slorage of erodible or leachable materials, wastes, or chemicals, and
which receive direct rainfall or the tUn-on or blow-in of rainfall.
Erodible or leachable materials, wastes, or chemicals are those
August 2001
--------------_._--------_._---------~--------
Volume 1- Minimum Technical Requirements
2-5
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substances which, when exposed to rainfall, leasttrnbly.alterJhe _ ...
physical or chemical characteristics of the rai f~l1 n,nkft~;)~x~iririj~s':'U"'!r
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include erodIble salls that are stockpIled, unc prOC"ess-wastes;""-"~--"-
manure, fertilizers, oily substances, ashes, kiln dust, and garbage
dumpster leakage. Metal roots are also considered to be POlS unless
they are coated with an inert, non-leachable material (e.g., baked-on
enamel coating).
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A surface, whether paved or not, shall be considered subject to
vehicular use if it is regularly used by motor vehicles. The following
are considered regularly-used surfaces: roads, unvegetated road
shoulders, bike lanes within the traveled lane of a roadway, driveways,
parking lots, unfenced fire lanes, vehicular equipment storage yards,
and airport runways,
The following are not considered regularly-used surfaces: paved
bicycle pathways separated from and not subject to drainage from
roads for motor vehicles, fenced firelanes, and infrequently used
maintenance access roads.
· Pollution-generating perviolls surfaces (PGPS) - Any non-
impervious surface subject to use of pesticides and fertilizers or loss of
soil. Typical POPS include lawns, landscaped areas, golf courses,
parks, cemeteries, and sports fields.
· Pre-developed condition - The native vegetation and soils that existed
at a site prior to the influence of Euro-American settlement. The pre-
developed condition shall be assumed to be a forested land cover
unless reasonable, historic iofonnation is prov'ided that indicates the
site was prairie prior to settlement.
· Project site - That portion of a property, properties, or right of way
subject to land disturbing activities, new impervious surfaces, or
replaced impervious surfaces.
· Receiving waters - Bodies of water or surface water systems to which
surface runoff is discharged via a point source of stoffi1water or via
sheet flow.
(
· Redevelopment- On a site that is already substantially developed (i.e.,
has 35% or more of existing impervious surface coverage), the
creation or addition of impervious surfaces; the expansion of a
building footprint or addition or replacement of a structure; structural
development including construction, installation or expansion of a
building or other structure;; replacement of impervious surface that is
not part of 11 routine maintenance activity; and land disturbing
activities.
2-6
Volume 1- Minimum Technical Requirements
August 2001
Supplemental Guidelines
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Reduction of flows through infiltration decreases stkRffi!cflwili~f~id1iJA\fC: 1f'\>\jl
and helps to maintain base tlow throughout the summer months.
However, infiltration should only be used where ground water quality is
not threatened by such discharges.
Volume III includes a description of the Western Washington Hydrology
Model. The model provides credits for use of certain downspout designs
and other types of Onsite Stonnwater Management BMPs described in
Volume V. Using those BMPs reduces the size ofthe required flow
control facilities.
Application of sufticient types of Onsite Stomlwater Management BMPs
can result in reducing the effective impervious area and the converted
pervious areas such that a flow control facility is not required.
Application of "Full Dispersion", BMP T5.30, also results in eliminating
the flow control facility requirement for those areas that are "fully
dispersed. "
.* Interim Guideline
Local governments have a choice to make concerning a flow control
standard to use until a now duration standard is adopted and a continuous
rainfalllrunoffmodeJ and flow routing program (for sizing orifices and
ponds) are available for use. They can continue to use the peak flow
standard of the 1992 Puget Sound manual, or use a peak now standard that
approximates the results that the proposed flow duration standard would
achieve.
By adjusting the target peak flow standard, restricting use of variables in
the Santa Barbara Urban Hydrograph (SBUH) hydrologic analysis, and
applying a volume correction factor, one can estimate the orifice sizes and
detention volumes that the proposed flow duration standard would
indicate. The following explains how to adjust the SBUH approach to
obtain results similar to the output from the King County Runoff Time
Series (an application of the Hydrologic Simulation Program _ Fortran)
with the proposed flow duration standard as the target.
/'
"
Adjusted target peak now standard. Limit the peak rate of runoff from
individual development sites to 50 percent or the pre-developed condition
2-year, 24-hour design storm. Limit the peak rate from the 10-year, 24-
hour design stoml to the pre-developed condition peak rate from the 2-
year, 24-hour design storm. Limit the peak rate from the I DO-year, 24-
hour design stann to the pre-developed condition peak rate from the 10-
year, 24-hour design storm.
"
2-32
Volume 1- Minimum Technical Requirements
August 2001
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Restricted variable assumptions. The flow pa~h lerlgtl~i~~~\ltnyqfo.(.
sheet flow runoff in the pre-developed conditiOll (nl:lwlaHonslnust 'notcbe,;;., ."
less than 300 feet..---........ .... .
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The Manning's effective roughness coefficient for pre-developed forested
conditions should be 0.80. For pasture conditions, the coefficient should
be 0.15.
In the table of curve numbers in Volume Ill, Chapter 2, the curve numbers
for pre-developed forest and pasture conditions must be selected from the
"fair" category.
Volume correction factor: In addition to the above, the pond volume
correction factor (applicable to detention and retention facilities) identified
in Volume III, Chapter 2 should be used where the pre-developed
condition is modeled as pasture. When enlarging the pond to
accommodate the volume correction factor, remember to not change the
pond depth or the design of the outlet structure. Thus, a.n increase in the
surface area is necessary.
2.5.8 Minimum Requirement #8: Wetlands Protection
Applicability
The requirements below apply only to projects whose stormwater
discharges into a wetland, either directly or indirectly through a
conveyance system. These requirements must be met in addition to
meeting Minimum Requirement #6, RUlloff Treatment.
Thresholds
The thresholds identified in Minimum Requirement #6 - Runoff
Treatment, and Minimum Requirement #7 - Flow Control shall also
be applied for discharges to wetlands.
Standard Requirement
Discharges to wetlands shall maintain the hydrologic conditions,
hydrophytic vegetation, and substrate characteristics necessary to
support existing and designated uses. A wetland can be considered
for hydrologic modification and/or stormwater treatment in
accordance with Guide Sheet lB in Appendix [-D.
Additional Requirements
The standard requirement does not excuse any discharge from the
obligation to apply whatever technology Is necessary to comply with
stnte water quality standards, Chapter 173-201A WAC, or state
Volume 1- Minimum Technical Requirements
2-33