HomeMy WebLinkAboutOWTS PlansProposed 3-BR Main Single-Family Dwelling
&
2-BR Plumbed Shop
Onsite Wastewater Treatment System Design
897 County Roa d 231
sitro co 81652
Parcel No. 2L79-041-00-184
Prepared for:
Joaquin Bianco
897 CR 231
silr, co 81652
November 2422
Prepared By:
ôNest Water En g i n eeri n g
ê consulting Engineers & Scientisis
2516 FORESIGHT CtRCtÊ, #r GRAND JUNCTION, COLORADO 81 505 1970)241-7076 * FAX (970) 241-7097
I.O OWTS SUMMERY
The onsite wastewater treatment system (OWTS) will serve multiple dwellings including a
proposed 3-BR main single-family residence and 2-BR living space plumbed shop on avacanf
8.O2-acre parcel located at897 CR 231 Silt, Colorado (Figure A1). The new OWTS will use a
common 1,500 gallon septic tank and a total of 44 ADS ARC 36@ Standard chamber units
configured in four (4) trenches each comprised of eleven (11) ARC 36 units. The trenches must
be separated by at least four feet of undisturbed soil for a minimum 24' x 58' total disturbed area
with chamber endcaps (Figure A2). Soil treatment area (STA)/leachfield is south of proposed
main and plumbed shop residences in an area sloping approximately lYo south.
Soils and percolation data were collected by WestWater Engineering November 18, 2022in
accordance with Garfield County On-Site Wastewater Treatment System (OWTS) Regulations
(Regulations). Soil profile in vicinity of proposed STA shows yellowish red silty sand loam
occurring from 0 to 0-1.0 feet overlying brown silty sand down to 8.5 feet maximum depth of the
excavation (Appendix A). Groundwater was not encountered in the 8.5-foot soils observation
hole. Depth to high seasonal groundwater table is estimated to be greater than 8.5 feet below
ground surface (bgs).
Percolation rates for the 6 percolation test holes completed in the silty sand loam and silty sand
range from 5 to 17 minutes per inch (min/in). Average percolation rate for all 6 test holes is 8
min/in. Site soils are classified as Soil Type 1 in accordance with Table l0-1 of the Regulations
based on sandy silt loam textures and percolation rates faster and within the 16-25 mirVin range.
Long-term acceptance rate (LTAR) used to design the OWTS (Table 10-1 Regulations) is 0.80
gallons per day per square foot area (gpdfff).
2.O WASTEWATERFLOWS
Average Flow
Maximum Daily Wastewater Flow (gpd): 3-BR main dwelling + 2-BR Plumbed Shop
5 x 150 gpd/bedroom : 750 gpd
Septic Tank
Individual septic tank capacity required to serve the 3-BR main and 2-BR plumbed shop
living space is a minimum volume of 1,500 gallon common septic tank per Table 9-1
Regulations.
Use a 1,500 gallon, two-compartment septic tank approved for use in
Garfìeld County to serve both dwellings. Internal effluent fìlter screen must
be installed on septic tank outlet and a tee for the inlet compartment per
Regulations.
Page 1
3.0 OWTS DESIGN
Silty sand occurring at the 2.0 to 4.0 feet depth interval will be used for upper infiltrative surface
for proposed STA (Figure A3). High seasonal groundwater table is estimated to be > 8.5 feet,
maximum depth of STA/leachfield shall not exceed 4 feet in accordance with the Regulations.
The maximum 4.O-foot soil depth promotes optimal secondary effluent treatment using oxygen,
bacteria and fungi processes. Trench excavation will remove approximately 2.0 to 4.0 feet of
soil and upper root mass to prepare a level surface for installing the chamber units in the five
trenches. Soil should not be wet at time of excavation. A minimum I -foot of final cover (10-
inches per Regulations) using the silty sand and silty sand will be slightly crowned over
proposed trenches or match existing grade so water runs off, and is not ponded over any area of
STA/leachfïeld. Prior to backfilling, cover the trenches with non-woven geotextile fabric or
similar permeable material to prohibit soil intrusion into the chamber louver vents.
All setback distances in accordance with the Regulations are applicable to septic system
installation. The septic tank must be at least 5 feet, and STA at least 20 feet from plumbed
structure(s) with basement, crawl space, and or footing drains. STA's must be outside of any
easements and at least 10 feet from property lines and 100 feet from existing shared water supply
well located on the north abutting parcel. Setback distances also apply to natural and artificial
waterways, including a S0-foot setback from STA/leachfield to open irrigation ditches and
ponds. Potable water lines serving the residences must be 25 feet from the STA/leachfield.
Designated leachfield repair area must be retained per Regulations as idle land set aside for
future use once primary fields fail and no longer accepts wastewater.
Proposed 1,500 gallon septic tank will be maintained to provide at least 48 hours detention time
for received wastewater flow from the structures they serve. Internal septic tank inlet and outlet
tees must be installed per Regulations. An effluent filter must be installed instead of tee on the
septic tank outlet. Use the Orenco Systems Biotube Effluent Filter OSI Model FTW0444-36 or
equivalent. Effluent flrlters typically require cleaning and maintenance every 6 months.
The following design calculations propose to discharge septic tank effluent to four (4) ARC 36
trenches each with eleven (1 1) chamber units in a disturb ed area approximately 24 feet by 58
feet. This includes 4 feet of undisturbed soil separating the trenches. A total of 44 ADS ARC 36
Standard chamber units will be used in the trenches generally configured east to west.
Soil Absorption Area Calculations
Absorption Area (A) : Design Flow (Q)/LTAR
Field percolation rate (t): 5-17 minlin
Leachfield Area:A:QILTAR,
Where:
A: Leachfield area square feet
Page 2
Q : Design Flodmaximum daily wastewater flow
: max. daily wastewater flow from 3-BR main and 2-BR Shop
: 5 x 150 gpd/bedroom:750 (gpd)
LTAR: Long Term Acceptance Rate (max. hydraulic loading rate)
:0.80 gallons per daylff
A:750 gpdl0.80 gpdlf:2 :937 .5 ff
ADS ARC 36 Trench Configuration:
937 .5 ft2 x 1.0 (appl. method adjustmentr) x 0.7 (distribution media adjustmentz): 656.25 ft2;
656.25 ft ll5 ft : 43.75 ARC 36 chamber units; Use 44 units.
1 Regulations Table l0-2 size adjustment factor for Methods of Application in STA
2 Regulations Table 10-3 size adjustment factor for Types of Media in STA
Note: County and State approved bottom chamber area for ARC 36 Standard ADS
Unit: T5 f(.
The Four-Trench System will use atotal of forty-four (\ chamber units. Each trench will have
eleven (11) ARC 36 chamber units. Wastewater flow into the trenches will be equally
distributed using a distribution box.
4.0 SYSTEMINSTALLATIONREOUIREMENT
Minimum setback requirements must be in accordance with the Regulations. All sewer pipe
couplings must be completed with primed and glued or bell and spigot joints using -inch SDR
35 PVC pipe. Schedule 40 PVC 4-inch pipe with a minimum l-foot soil cover must be used if
pipe is installed in a vehicular traffic crossing. Drain-waste-vent (DWV) rated Schedule 40 PVC
pipe is specified for crossings but may also be used instead of SDR 35 PVC pipe.
Building sewer pipe must be set at a slope between Vs-inch and t4-inch per foot slope (1 to 2Yo),
preferably using theYq-inch per foot slope as recommended by the International Plumbing Code
(IPC) administered by the County. Fittings should use sweep 9O-degee curves or two (2) 45-
degree elbows at all influent pipe tums. Fittings must be DWV for Schedule 40 PVC pipe.
Clean-outs (2-way) are required between dwelling and septic tank and beyond septic tank where
pipe lengths exceed 100 feet from septic tank to STA/leachfield.
Installer must adhere to minimum depth requirements for leachfield and ensure gravity drainage
into all septic system components to avoid using a lift pump. System components must be
placed on native soils or re-stabilized soils in excavated areas.
Page 3
Infiltrator trenches must be excavated level to ensure prepared infiltrative surface is level along
entire length of STA. Solid 4-inch pipe is used in the header network of sanitary tees.
The owner will ultimately be responsible for septic system maintenance including pumping
septic tank once every 3-4 years and cleaning effluent filter every 6 months.
5.0 SYSTEM INSPECTION
WestWater Engineering is responsible for inspecting OWTS to ensure construction conforms to
design plan and meets all aspects of County Regulations to include:
Inspect system prior to backfilling including piping and septic system components.
Complete as-built drawing of system
6.0 DESIGN LINIITATIONS
The OWTS design is based on site specific soil investigation collected in vicinity of proposed
leachfield and local experience of designing OWTS's in Garfield County, Colorado, The design
is only valid for proposed new OV/TS serving proposed residences at referenced location
provided in this report. WestWater Engineering assumes no liability for inaccurate information
or conditions that vary from design assumptions listed above. Notify WestWater Engineering
andlor the Mesa County official immediately if actual site conditions differ from those assumed
here in.
Please do not hesitate to contact us ifyou have any questions regarding this report.
Respectfully,
-Ë{À- r
Dean Goebel, M.S., P.G. Hydrogeologist
Reviewed By
Keith
o
o
/0t,AL
Page 4
APPENDIXA
SOILS AND PERCOLATION DATA
ô\Nest Water En g i neeri ng
ê consulting Engineers & Scientists
25t6 FORESIGHT ClRCtE, #1 GRAND JUI'¡CTION, COLORADO 8t5O5
41. SOILS AND PERCOLATION REPORT
Date: November 18,2022
(9701241-7076 - FAX (970) 241-7097
Consultant:Dean Goebel, M.S., P.G. Hydrogeologist
West\Vater Engineering
2516 Foresight Circle #l
Grand Junction, CO 81505
(e70) 241-7076
Client Joaquin Bianco
897 County Road 231
Silt, CO 81652
Land Parcel: 897 CR 231, Silt, CO 8T652
2179-041-00-184
42. SOILS LOG
Site soils were ìnvestigated at the 8.)Z-acre vacant parcel to collect site specific design criteria
for an onsite wastewater treatment system (OWTS) to serve a proposed 3-BR single-family
dwelling and plumbed shop with 2-BR living space located at897 County Road, Silt, Colorado
Percolation testing and soil evaluation procedures were conducted in accordance with Garfield
County On-Site Wastewater Treatment System (OWTS) Regulations (Regulations). The
Percolation Test Site is located approximately 175 feet south of the north property line and 300
feet east of the west property line (Figure Al).
The proposed OWTS soil treatment area (STA/leachfield is located in the southwestern portion
of the parcel in an area sloping approximately lYo to the south. The excavated soils observation
pit shows a uniform soil profile of silty sand loam topsoil overlying silty sand. Groundwater was
not encountered in the 8.S-foot soils observation pit.
The soils profile log is summarized below and in Table Al Yellowish red (5YR 4/6) silty sand
loam, disturbed from past cultivation from 0.0-1.0 feet, overlying silty sand from 1.0-8.5 feet
maximum depth of excavation. Estimated high seasonal groundwater is estimated to be greater
than 8.5 feet based on the timing near the end of the irrigation season and the lack of soil
moisture or signs of prolonged saturation in the bottom of soil observation pit.
A-1
Depth Interval (ft)Soil Description
0-1 0 Yellowish red (5YR alQ srlty sand (vf)'loam Ap horizon disturbed by
past cultivation; low-moderate organic matter (OM); blocky, dry; roots;
sparse native grass vegetation
1.0-8.5 Strong brown (7.5YR 5/6) silty sand (vf); low OM; granular laminar
structure; moderate OM; granular structure, roots; dry
Table 41. Soil Log Description
vf : very fine; f : fine, m : medium and; crs : coarse for sand sized particles
Percolation rates summarized in Table A2 show a range from 5 to 17 minutes per inch (min/in)
with an average of 8 min/in. Based on percolation data, macroscopicltactile soil analysis and
depth to the high seasonal water table at 8.5 feet, bottom of leachfield (top of infiltrative surface)
should be no deeper than 4.0 feet per Regulations. Site soils are categorized as Type I soils
based on silty sandy loam texture, granularJaminar soil structure and percolation rates mainly
faster than the T6-25 min/in range. Soils should not be excavated under wet conditions to avoid
compaction and smearing leading to reduction in permeability
Table A2. Percolation Test Results
ID Depth
(ft)
Time Final
Drop
(in)
Percolation
Rate
(min/in)
10:08
(start)
10:38 11:08 11:38 12:08
(end)
1 2.0-3.0 2.5"7.75"I 1.5"dry dry 9.0 7
)0.0-1.0 4.0"6.75"8.25"9.t5"rr.125"7.r25 r7
5 2.5-3.5 5.0"I 1.5"dry dry dry 6.5 5
4 4.0-5.0 5.5"1r.75"dry dry dry 6.25 5
5 3.0-4.0 7.0"11.875"dry dry dry 4.875 6
6 3.4-4.4 7.0"Tr.625"dry dry dry 4 625 7
A-2
APPENDIX B
FIGURES
897 COUNTY ROAD 231
Ð(STING OTYË SITE PI.AN
FIGURE A1
WestWoter
Englneerlng
2516 Forcslght Clrcle, fl
Grond Junctlon, CO El5O5
(s7o) 211-7076
fra
EXISTING SHARED
WATER SUPPLY WELL
WELL & IRRIGAÏON
EASEMENT
AND PUMP HOUSE 3O-FOOT ACCESS &
UTLITY EASEMENT
SOILS AND PERCOLAÏON
TEST SITE
ïH6
TH4
'rHz STAKED LOCATONS OF
PROPOSED 5-BR DWELLING
AND PLUMBED SHOP
SLOPE 1%
SOUTH EXISÏNG PROPERTY
L¡NE (8.02r ACRES)
1 0
SCALE: 1":150'
150
WestWoter
Englneerlng
2516 Forcolght Clrcl6, fi
Grond Junctlon, C0 E1505
(e7o) 241-7076
fra FIGURE A2
897 COUNTY ROAD 231
PROPOSED OWTS LAY-OT'T
PROPOSED
POTABLE WATER
LINE CORRIDOR
FROM WELL
PROPOSED
CISTERN
NOTE:
ADS ARC 36 TRENCHES
44 UNITS 4 TRENCHES
11 UNITS EACH
PROPOSED
POTABLE WA
LINE CORRIDOR
FROM CISÏERN
_PROPOSED
DRIVEWAY
ACCESS
SOILS AND PERCOLATION
TEST S|TE (r\?)
t:::.)
2-WAY
CLEANour(s)
NEW 1,500
GALLON
SEPÏC TANK
MINIMUM DWELLING SEÏBACK
TO LEACHFIELD 20 FT 2-WAY
CLEANOUT
DISÏRIBUÏON BOX
RISER AÏ GRADE
COVER ADS ARC 36
TRENCHES WTH GEO.
TEXTLE FABRIC
LINE
LEAçHFTELÐ _19_Ff_
40200 0
1
REPAIR
LEACHFIELD
AREA 24' x 58'
PLUMBED
PROPOSED
3-BR
SINGLE-FAMIL
RESIDENCE
SCALE ":4Q'
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