HomeMy WebLinkAboutEngineer's Design Plan129 CAINS LANE
CRneor.¡oRLE, CO 816,23
970.309.5259
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November 27,2022 Project No. C1674
Chris Hjorth
norskbuilders@qmail.com
Subsurface lnvestigation and Onsíte Wastewater Treatment System Design
G-Bedroom Main Residence + 2-Bedroom ADU
Lot 23, Stirling Ranch
Garfield County, Colorado
Chris,
CBO lnc. performed a subsurface investigation and completed an onsite wastewater treatment system
(OWTS) design for the subject residence. The 8.168-acre property is located outside of Carbondale, in
an area where OWTSs are necessary.
Legal Description: Section: 29 Township: 7 Range: 87 Subdivision: STIRLING RANCH PUD Lot: 23
Parcel lD: 2391 -292-05-023
SITE CONDITIONS
The property is currently undeveloped. A 6-bedroom Main Residence and 2-bedroom Accessory
Dwelling Unit (ADU) are proposed.
The residences will be served potable water from the community water system serving Stirling Ranch
The water lines may not come within 1O-feet of the proposed septic tanks or within 2S-feet of the
proposed soil treatment area (STA).
The proposed soil treatment area (STA) location has an approximate 10 to 1 1 percent slope to the west
The proposed area vegetated with sage and native grasses.
There should be no traffic or staging of material over the future STA site to avoid compaction of soils
prior to construction of the STA.
SUBSURFACE
The subsurface was investigated on October 24,2022 by digging two soil profile test pit excavation (Test
Pit). A visual and tactile soil analysis was completed by Carla Ostberg.l A previous subsoil study and
percolation testing was performed by HP-Kumar and results documented in a repoft dated December 1 1,
2017, Proled 17 -7 -7 B7 (enclosed).
The materials encountered in Test Pit #1 consisted of dark brown clay loam topsoil to 1.S-feet, underlain by
tan calcareous clay matrix explored to a maximum depth explored of 8.O-feet. No bedrock or groundwater
was encountered.
' Carla Ostberg holds a Certificate of Attendance and Examination from the CPOWVisualand Tactile
Evaluation of Soils Training.
Page2
The materials encountered in Test Pit #2 were consistent with those encountered in Test Pit #1. Test Pit #2
was excavated to a maximum depth explored of 8.O-feet. No bedrock or groundwater was encountered.
A sample of the soils was taken from Test Pit #1 at 3-feet below grade. Soil structure grade was
moderate. The soilformed a ball and a ribbon approximately 1-inch in length before breaking. Soil
structure shape was blocky and consistence was friable to firm. Soiltexture was both gritty and smooth.
STA sizing is based on SoilType 2 with weak structure grade. A long term acceptance rate (LTAR) of
0.6 gallons per square foot.
View of Test Pit #1
Test Pit #1 Backfill
Page 3
Test Pit #2
DESIGN SPECIFICATIONS
Desiqn Calculations:
MainResidence=TSGPDx2people/bedroomx3Bedrooms+225GPD(4th,sthand6thBedrooms)=675
GPD
ADU = 75 GPD x2 people/bedroom x 2 Bedrooms = 300 GPD
Average Design Flow = 675 GPD + 300 GPD = 975 GPD
LTAR = 0.6 GPD/SF
975 GPD / 0.6 GPD/SF x 0.8 (pressure dosed trenches) x 0.7 (chambers) = 910 SF
The new OWTS design is based on 6-bedrooms in the Main Residence and 2-bedrooms in the ADU. An
average daily wastewater flow of 975 GPD will be used.
For the purposes of this OWTS design, Benchmark Elevation has been established as 100' as the
Finished Floor (FF) of the Main Residence (Approx. 7075'). The ADU FF elevation appears to be at
approximately 7081'. CBO lnc. should be notified of any discrepancies or problems with grade elevations
of proposed components during installation of the OWTS.
OWTS Gomponent Minimum Elevation
Primary ïank lnlet lnvert ADU Tank
Primary Tank lnlet Invert Main Residence
ADU Tank to Pump Chamber
Main Residence Tank to Pump Chamber (or tie into
ADU sewer line)
Approximate horizontal distance 29' I min.2o/o fall I
min.7.25" fall
Approximate horizontal distance 11' I min.2o/o fall I
min. 2.75" fall
Approximate horizontal distance 188' / min. 1o/o fall
/ min. 23.5" fall
Approximate horizontal distance 14' I min. 1o/o fall I
min. 1.75" fall
Automatic Distributing Valve Approximate horizontal distance 57' I min. 1% rise
for drain back / min. 7.125" rise
lnfiltrative Surface Approximate horizontal distance to furthest trench
35' / min. 1o/o fall / min. 4.375" fall
Page 4
*Elevations are based upon standard OWTS installation practices. Component elevations may change during
installation due to site conditions. Minimum grade refers to piping between components.
The sewer lines exiting the ADU and Main Residence must be 4-inch diameter SDR-35 with double-
sweep clean outs and a minimum 2o/o grade to the septic tank. There must be an additional clean out at
least every 1OO-feet on the ADU sewer line.
The system installation will include a 1OO0-gallon, two-compartment septic tank with an Orenco@ Biotube
Effluent filter on the outlet to serve the ADU. An additional 2000-gallon, two-compartment septic tank with an
Orenco Biotube Effluent filter must be installed to serve the Main Residence. A 5OO-gallon, single-
compartment pump chamber must be installed with an Orenco@ Pump Vault and an Orenco@ PF3005
pump. Any state-approved poly or concrete septic tanks may be used, although we have provided preferred
components as part of this design packet. The floats should be set to dose approximately 75 gallons each
pump cycle, allowing approximately 6 gallons of drain back after each pump cycle. The control panel for
the pump must be located within line of sight of the septic tank. We recommend Valley Precast out of Buena
Vista be contracted for start-up of the pumping system.
Table
Effluent will be pumped through a 1.S-inch diameter pump line from the pump chamber to an Orenco@
automatic distributing valve (ADV), model6404. This pump line must have a minimum 1o/o grade for proper
drain back into the tank after each pump cycle. The ADV must be placed at a high point in the system in an
insulated riser with access from grade. Screened rock must be placed below the ADV to support the ADV
and to assure the clear pipes exiting the ADV remain visible for future inspection and maintenance.
Effluent will be pressure dosed through 1.5-inch diameter pipes to four gravelless chamber trenches,
each 19 'Quick 4' Plus Standard lnfiltrator@ chambers, for a total of 76 chambers and 912 square feet of
infiltrative area. There must be at least 4-feet of undisturbed soil between each trench.
Effluent will be pressure dosed to 1.S-inch diameter laterals, which must be hung with zip ties from the
underside of the chambers. Laterals will have 5/32-inch diameter orifices facing up, with the exception of
the first and last orifices facing down for drainage. Orenco@ Orifice Shields may be placed under each
downward-facing orifice. The orifices must be placed 3-feet on center. Each lateral must end in a 90
degree ellfacing up with a ball valve for ffushing. Valves may be placed in a valve box, accessible from
grade, for access. lnspection ports must be placed at the beginning and end of each trench. Ports may
be cut to grade and covered with a valve box for access.
Dose Range Max = 249.75 gal. (975 GPD x
25o/o + 6 qal drain back)
Min. 54 gal. (12 galx 4) + 6 gal
drain back
Dose Setting 75 gallons/dose 6 gallons drain back (57' I 1.5"
diameter pump line)
500 gallon, single-compartment
Valley Precast concrete pump
chamber
7" onloff float separationFloat Separation
Pump Criteria 17.8 gallons per minute (GPM)19.4 feet totaldynamic head
fiDH)
Page 5
COMPONENT SPECIFICATIONS
The component manufacturers are typical of applications used by contractors and engineers in this area.
GBO lnc. must approve alternative components prior to installation of the OWTS. Requests must
be submitted, in writing, to our office for approval prior to installation. Component technical data
sheets are available upon request.
Construction must be according to Garfield County On-Site Wastewater Treatment System Regulations, the
OWTS Permit provided by Garfield County Building Department, and this design.
¡NSTALLATION CONTRACTOR
CBO lnc. expects that the installer be experienced and qualified to perform the scope of work outlined in this
design. The installer must review this design thoroughly and coordinate with our office in advance of
installation. Any additional conditions in this design or county permit must be completed and documented
prior to final approval of the OWTS installation. Communication between the installer and this office is
expected throughout the installation.
INSTALLATION OBSERVATIONS
CBO lnc. must view the OWTS during construction. ïhe OWïS observation should be performed before
backfill, after placement of OWTS components. Septic tanks, distribution devices, pumps, dosing
siphons, and other plumbing, as applicable, must also be observed. CBO lnc. should be notified 48 hours
in advance to observe the installation.
ln an effort to improve the accuracy of the record drawing, we request that the installer provide a
sketch of the installation, including path of the sewer lines, water line installation (if applicable),
septic tank location, STA location, and measurements from building corners or another fixed
objects on the property. This sketch is most easily provided on Sheet W2.0 of the OWTS Design
Packet. Photographs of the installation and final cover are also requested to supplement our installation
documentation.
COMPONENT MANUFAGTURER MODEL NO.COMMENTS
Septic Tanks lnfiltrator@
Valley Precast
f nfiltrator@
Item # lM-1060
Item # 2000T-2CP
Item # lMl-540-HH
1 000-gallon, 2-comp poly
septic tank
2000-9allon, 2-comp
:oncrete septic tank
500-gallon, single-comp
ooly pump chamber with
{H oumo
Pump Orenco@ PF300511%HP
120 Volt
Biotube ProPak Pump
Packaqe
Orenco(Ð BPP3ODD y'ault, Filter, Control Panel
idemand dose)
Tank Risers and Lids Orenco@ Double-walled PVC Risers and
Lids (24" diameter)
ADV OrencoG)V64U4A 1.5" lnlet and Outlets
ADV Riser and Lid OrencoG)Double-walled PVC Risers
and Lids (30" diameter)
Orifice Shields Orenco(Ð OS150 1.5 inch diameter (8 total)
Flush¡ng Assembly Orenco(Ð 1.5" diameter (2) 45" or 90" long sweep only
(4 total)
chambers lnfiltrator@ Plus Standard 76 'Quick 4' Chambers
Page 6
REVEGETATION REQUIREMENTS
An adequate layer of good quality topsoil capable of supporting revegetation shall be placed over the entire
disturbed area of the OWTS installation. A mixture of native grass seed that has good soil stabilizing
characteristics (but without taproots), provides a maximum transpiration rate, and competes well with
successional species. No trees or shrubs, or any vegetation requiring regular irrigation shall be placed over
the STA. Until vegetation is reestablished, erosion and sediment control measures shall be implemented
and maintained on site. The owner of the OWTS shall be responsible for maintaining proper vegetation
cover.
OPERATION INFORMATION AND MAINTENANCE
The property owner shall be responsible for the operation and maintenance of each OWTS servicing the
propefi. The property owner is responsible for maintaining service contracts for manufactured units,
alternating STAs, and any other components needing maintenance.
Geo-fabrics or plastics should not be used over the STA. No heavy equipment, machinery, or materials
should be placed on the backfilled STA. Machines with tracks (not wheels) should be used during
construction of the STA for better weight distribution. Livestock should not graze on the STA. Plumbing
fixtures should be checked to ensure that no additional water is being discharged to OWTS. For example, a
running toilet or leaky faucet can discharge hundreds of gallons of water a day and harm a STA.
lf an effluent filter or screen has been installed in the OWTS, we recommend this filter or screen be cleaned
annually, or as needed. lf the OWTS consists of a pressurized pump system, we recommend the laterals be
flushed annually, or as needed.
The homeowner should pump the septic tank every two years, or as needed gauged by measurement of
solids in the tank. Garbage disposal use should be minimized, and non-biodegradable materials should not
be placed into the OWTS. Grease should not be placed in household drains. Loading from a water softener
should not be discharged into the OWTS. No hazardous wastes should be directed into the OWTS.
Mechanical room drains should not discharge into the OWTS. The OWTS is engineered for domestic waste
only.
ADDITIONAL CONSTRUCTION NOTES
lf design includes a pump, weep holes must be installed to allow pump lines to drain to minimize risk of
freezing. The pump shall have an audible and visual alarm notification in the event of excessively high-
water conditions and shall be connected to a control breaker separate from the high-water alarm breaker
and from any other control system circuits. The pump system shall have a switch so the pump can be
manually operated.
Excavation equipment must not drive in the excavation of the STA due to the potential to compact soil.
Extensions should be placed on all septic tank components to allow access to them from existing grade.
Backfill over the STA must be uniform and granular with no material greater than minus 3-inch.
LIMITS:
The design is based on information submitted. lf soil conditions encountered are different from conditions
described in report, CBO lnc. should be notified. All OWTS construction must be according to the county
regulations. Requirements not specified in this report must follow applicable county regulations. The
contractor should have documented and demonstrated knowledge of the requirements and regulations of
the county in which they are working. Licensing of Systems Contractors may be required by county
regulation.
Page 7
Pleaee call with quêst¡ons.
Sinoerely,
CIBO lnc.
Garla Ostberg, MPH, REI-IS
tw-be+elu'e
Reviewed By:
RomeoA. Baylosis, PE
Pump Selection for a Pressurized System - Singte Famity Residence Project
Norsk Builders I C1674
Parameters
300Discharge Assembly Size
Transport Length Before Valve
Transport P¡pe Class
Transport L¡ne Size
Distributing Valve Model
Transport Length After Valve
Transport Pipe Class
Transport Pipe Size
Max Elevation Lift
Manifold Length
Manifold Pipe Class
Manifold Pipe Size
Number of Laterals per Cell
Lateral Length
Lateral Pipe Class
Lateral Pipe Size
Or¡fice Size
Or¡fice Spacing
Res¡dual Head
Flow Meter
'Add-on' Friction Losses
Calculations
't.25
57
40
1.50
6404
40
1.50
6
0
40
1.50
4
76
40
1.50
5132
3
5
None
0
inches
feet
inches
feet
inches
feet
feet
inches
feet
inches
inches
feet
feet
inches
feet
o
ü
Io
tt
IEo
.9
E(!g
ê
aú
Ê
250
200
150
100
50
PumpData
0510 15 20 25
Net Discharge (gpm)
30 35 40
Minimum Flow Rate per Or¡fice
Number of Orifices per Zone
Total Flow Rate per Zone
Number of Laterals per Zone
o/o Flow Differential lsvLast Orifice
Transport Veloc¡ty Before Valve
Transport Velocity After Valve
Frictional Head Losses
0.68
zo
17.8
1
4.9
2.8
2.4
gpm
gpm
o/o
fps
fps
Loss through Discharge
Loss in Transport Before Valve
Loss through Valve
Loss in Transport after Valve
Loss in Manifold
Loss in Laterals
Loss through Flowmeter
'Add-on' Fr¡ction Losses
Pipe Volumes
2.2
1.1
3.7
0.7
0_0
0.6
0.0
0.0
feet
feet
feet
feet
feet
feet
feet
feet
0
Vol of Transport Line Before Valve
Vol of Transport Line After Valve
Vol of Manifold
Vol of Laterals per Zone
Total Vol Before Valve
Total Vol After Valve
6.0
3.7
0.0
8.0
6.0
11.7
gals
gals
gals
gals
gals
gals
PF3005 High Head Effluent Pump
30 GPM, ,I/2HP
1151230V 1Ø 60H2, 200V 3ø 60Hz
PF3007 High Head Effluent Pump
30 GPM, 3/4HP
23OV 1Ø 6OHz,2OO|46OV 3Ø 60Hz
PF30l0 High Head Effluent Pump
30 GPM, 1 HP
23OV 1ø 60H2, 200/460V 3ø 60Hz
PF3015 H¡gh Head Effluent Pump
30 GPM. 1-1l2HP
gpm
feet
\
System Curve: -
Pump Curve:"" "
HUmp ()ptrmal Kange:
operating Po¡nt, G
o
Design Point:
23OV 1Ø 6OHz,2OOl230l460V 3Ø 60Hz
N
DRAWINGS MUST BE USED IN
CONJUNCTION WITH DESIGN
LETTER DATED 1 1 127 12022
SCÀLE: I = 50'=0"
1O.O'TYP, ESMT ?-4',VSEt ESMT. NITT /
23 P
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R/ST
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THE LOCATION OF PROPOSED IMPROVEMENTS SHOWN ARE
NOT THE RESULT OF A PROPERry SURVEY, fHE LOCAÎIONS
ARE APPROXIMATE. IT IS THE HOMEOWNERS'DUry TO
ENSURE ALL CONSTRUCTION AND IMPROVEMENT LOCATIONS
ARE ACCURATE. PROPERTY LINÊS ANÞ SETBACK DISTANCES
SHOULD BE CONFIR¡,iED PRIOR TO EXCAVATION, SCALED
FOR PRINTING ON 1'I" X 17' PAPER.
k J
\(
Oo \.o
C\\Êr()
ADU
SEPTIC
TANK
ô-BEDROOM
RESIDENCE
LINE
Iul
É,
¿f
TP1
TP2
SEPTIC
TANKS
SCHOONER LANE
VAULT
J
CBO lnc.
129 Ca¡ns Lane
Carbondale, Colorado 81623
Phone 970.309.5259
carla.ostberg@gmail.com
Norsk Builders, LTD
Lot 23, Stirling Ranch
Garfield county, colorado
PrcjectNumber; C1674
Date:1112712022
Designed by: CBO
Reviewed by: RB
Drawn by: DD
w1 .0
Sheet 'l 0F 4
N ?
SCALE: 1 = 30'=0"
OOO-GALLON, TWO-COMPARTMENT
SEPTIC TANK WITH EFFLUENT
SCREEN
3
tS
U
À
4'DIA SDR-35 SEWER
LINE (1 % FALL TO PUMP
CHAMBER)
CLEAN OUT MIN. EVERY 1
4' DIA SDR-35 SEWER PIPE WITH CLEANOUT
MIN 2% FALL TO TANK
I
2OOO-GALLON 2-COIVIPARTMENT SËPTIC TANK
WITH EFFLUENT SCREEN,
RISERS AND LIDS TO GRADE.
SINGLE.COMPARTMENT PUMP
CHAMBER WTH ORENCO
PUMPING SYSTEM. RISERS AND
LIDS TO GRADE.
ð
1.5' DIA SCH*40 PUMP LINE.
(MIN 1% DRAIN BACK TO TANK)
1.5- DIA SCH-40 DISTRIBUTION
LINES TO EACH TRENCH (MIN.
1olo FALL)
/t rP1 +
4 TRENCHES EACH WITH 19'QUICK 4'CHAMBERS
76 CHAMBERS = 912 SF. 1.5" DIA SCH-40 PVC
SUSPENDED LATERALS WITH 5/32'DIA ORIFICES
3' O.C- FACING UP. FIRST AND LAST ORIFICES
FAC¡NG ÐOWN FOR DRAINAGE, COVERED WITH
ORIFICE SHIELDS
4' DIA SDR-35 INSPECTION PORT AT
BEGINNING AND END OF EACH TRENCH +
TP2
PROPERTY LIN R E
O
CBO lnc.
I 29 Ca¡ns Lane
Carbondale, Colorado 8'l 623
Phone 970.309.5259
carla.ostberg@gmail.com
Norsk Builders, LTD
Lot 23, St¡rling Rênch
Garfield County, Colorado
ProjectNumberj C1674
Dale: 1'112712022
Designed by: CBO
Reviewed by: RB
Drawn by: DD
w2.0
Sheet 2 0F 4
CBO lnc.
129 Ca¡ns Lane
Carbondale, Colorâdo 81623
Phone 970.309.s2s9
carla.ostberg@9mail. com
INFILTRATOR
END PLATE
\IUICK¿'
CHAI,IBER (4'x 3')1,5' DtA SCH{o
DISTRIBUTION LINE TÒ
EACH TRENCH
1.5" DtA SDR-35
EFFLUENT PIPE FROM
PUMP CHNBER
DIASDR-35 SLIP.ON PVC
ADV WIÎH ACCESS AT INSPÊCTION
PORT
DO NOT GLUE
GRAOE INSULATED
PUCED IN TOP POffi 4'ñax
I
L
TRACÊR WIRE FINISHED GRADE
OF CHAMBER END PLATES sotL
_lLINE TO 4" DIA
4TH TRENCH (4 fot[)LIMIT SEWER L¡NE
4' DIA SDR.35 INSPECTION
PORT A1 EEGINNING ANÞ
ÊND OF ÊACH TRENCH
EXCAVATION
SUSPEND LATERALS WTH
ZIP.TIES TO UNDERSIDE
OF CHAMBERS
GRAVELLESS'QUICK4'
CHAMBER {4' x 3')
SCARIFY SURFACE TO TANK
END ÊACH LATERAL IN A 90" LONG
SWÊÊPING ËLL FACING UP WITH A BALL
VALVE IN A VALVE BOX ACCESSIBLE AT
GRADË
1.5'DIA SCH"4O PVC SUSPENDED UTERAL
wlH s/32" DrA ORtFICES AT 3'O.C. FACTNG
UP. FIRST AND LAST ORIFICES FACE DOWN
WTH AN ORIFICÊ SHIÊLD FOR DMINAGE.
r;.\-C!¿i,EEE-IEEI.çH-SLCTON\:)
/I CLEANOUT DETAIL
L,l----j-ffi
/ÀCHAMBER]RENCH PLAN\r,-ffiæ
INSTALL FLUSHING
VALVE ECCENTRIC TO
CENTER OF VALVÉ
BOX
10" DIA VALVE BOX
W|TH SECURED LID
SMALL VALVE COVER
BOX OR ìRRIGATION
VALVE BOX AT GMDE
30" DIAMEÏER PVC
1.5" PVC SLIP X MALE
PIPÉ THREAD
ADAPTERWCAP
1.5" DIA BALL
VALVE
RISER
CAP ORTHREADED
CLEANOUT ASSEMBLY
1.5'DtA SCH-40 PVC
LONG SWEEP 90" ELBOW
Trc
COMPACT SOIL BASE
fO SUPPORT BOX PVC PIPE CUITO FI.l-
DISTRIBUTING
VALVE ASSÊMBLY END CAP
FROM
USE HOLE SAW TO
CUT THRU TOP OF
PUMPING DIA SCH40 1.5'DIA SCH4O PVC
SUSPENDED TATERAL
END
PVC INLET AND
OUTLETS
AINSPECTON PORT iN CHAMBERÉ/r-frræ /À AUTOMAÏC DISIRIBUTING\9r---"---'--"- ffiæ VALVE DÊTAIL
/I FLL'SHING VALVE DETAIL\9¡-----rñæ
Norsk Builders, LTD
Lot 23, Stirling Ranch
Gârfield County, Colorado
ProjectNumber: C1674
llan,:11tz7t2o2z
lDesigned by: CBO
lReviewed by: RB
lDrawn
bv: DD
w3.0
Sheet 3 0F 4
CBO lnc.
129 Cains Lane
Carbondale, Colorado 81623
Phone 970.309.5259
€rla.ostberg@gma¡l.mm
DESIGN
6.BEDROOM RESIDENCÊ + 2-BEDROOIV ADU
75 GPD X 2 PÊRSONS/BEDROOM X 3 BEDROOMS + 225 GPD (4th, sth ANd 6th
BEDROOMS) = 575
75 GPD x 2 PERSONSßEDROOM x 2 BEDROOMS = 300
WASTEWATER FLOW = 975 GPD
STA TO WATER COURSE 50'N/A
STATO WELL 'f 00'N/A
STA TO HOUSE 20'44
SEPTIC TANK TO WATER COURSE 50'N/A
SEPIIC IANK TO WELL 50'N/A
IVAIN HOUSE TO SEPTIC TANK 25'
ADU TO SEPTIC TANK
OWTS COMPONENTS AND
PHYSICAL FEATURES
MIN¡MUM REOUIRED
SETBACK
APPROXIMATE PROPOSED
SETBACK
TANK:
MIN. I75O GALLONS TO SERVE MAIN RESIDENCE
I\4IN. lOOO GALLONS TO SERVË ADU
SOIL TRËATMENT AREA (STA):
LONG TERM ACCEPTANCE RATE (LTAR) = 0.6 GAU SF
CALCULATED STA = Q/LTAR = 975 / 0.6 = 1 625 SF
PRESSURE DOSED, TRENCHES = 1625 SF X 0-8 = 1300 SF
CHAMBERS = I 300 SF X 0.7 = 91 0 SF / 1 2 SF / CHAMBER = 76 CHAMBERS
FOUR GRAVELLESS CHAMBER TRENCHES
19'QUICK 4'CHAMBERS IN EACH TRENCH
TOTAL 76'QUICK 4' CI1AMBERS
SOIL PROFILE TÊST PIT NO. 1 SOIL PROFILE TEST PIT NO. 2 LEGEND
[= topso¡l
l:rl ælca¡eous
clay matrix
0
1
2
4
5
6
7
I
10
DARK BROWN TOPSOIL DARK BROWN TOPSOIL
FINISHËÞ GRADE
TAN CALCAREOUS CLAY MATRIX TAN CALCAREOUS CLAY MATRIX
24'MtN.
4'DIA SDR.35 SEWER
(MlN 2% SLOPE TO TANK)
SCREENED
OR SAND FOR
BEDDING
3" MtN.
NO GROUNDWATER OR BËDROCK ENCOUNTERED
DURING EXCAVATION 8" MtN.
/:\.IRENCH DETAIL
/ASOILS LOG\v
BACKFILL
Norsk Builders, LTD
Lot 23, Stirling Ranch
Garf¡eld County, Çolorado
Project Number; C1674
Date:1112712022
Designed
Reviewed
Drawn by:
by: CBO
þy: RB
DD
w4.0
Sheet 4 0F 4
H-PryKUMAR
Geotechnlcal Enginaering I EngineErlng Geology
Materlals Testlng I Environmental
5020 County Road 154
Glenwood Springs, C0 81601
Phone: (970) 945.7988
Fax (970) 945-8454
Email: hpkglenwood@kumarusa.com
Office Locations: Denver (HQ), Parker, Colorado Springs, Fort Collins, Glenwood Springs, Summit County, Colorado
December ll,20l7
ay Wright
630 East Hyman Avenuen Suite 101
Aspen, Colorado 8161I
iav.wrisht @elliman.com
projecr No.lT-7-287
Subject: Subsoil Study for Foundation Design and Percolation Testing, Proposed
Residence, Lot23, Stirling Ranch, Skipper Drive and Schooner Lane, Missouri
Heights, Garfield County, Colorado
Dear
As requested, H-PÆ(umar performed a subsoil study and percolation testing for foundation and
septic disposal designs at the subject site. The study was conducted in accordance with our
agreement for geotechnical engineering services to you dated October 20,2017. The data
obtained and our recommendations based on the proposed construction and subsurface
conditions encountered are presented in this report.
Proposed Construction: This report was for the purchase/sale of the property in which the
Clary's are the buyers. Design plans for the residence have not been developed. r#e assume that
the proposed residence will be a one to two story wood frame structure over a basement or
crawlspace and located on the site in the area of Pits I and2, shown on Figure 1. Ground floors
will be slab-on-grade or structural over crawlspace. Cut depths are expected to range between
about 2 to 7 feet. Foundation loadings for this type of construction are assumed to be relatively
light and typical of the proposed type of construction. The septic disposal system is proposed to
be located south of the residence in the area of the profile pits and percolation test holes shown
on Figure 1.
If building conditions or foundation loadings are significantly different from those described
above, we should be notified to re-evaluate the recommendations presented in this report.
Site Conditions: The lot was vacant and the topography appeared to be natural at the time of
our field work. An existing fence line runs north to south through the eastern portion of the lot.
There are pinon and juniper trees to the west of the fence and sage brush to the east. There is an
-2-
understory of grass and weeds across the lot. The lot slopes gently to moderately down to the
southwest. Scattered basalt cobbles and boulders were observed on the ground surface.
Subsidence Potential: The lot is underlain by Pennsylvania Age Eagle Valley Evaporite
bedrock. The evaporite contains gypsum deposits. Dissolution of the gypsum under certain
conditions can cause sinkholes to develop and can produce areas of localized subsidence.
During previous work in the area, sinkholes were observed in the lower Roaring Fork Valley.
Sinkholes were not observed in the immediate area of the subject lot. The pits were relatively
shallow, for foundation design only. Based on our present knowledge of the site, it cannot be
said for certain that sinkholes will not develop. In our opinion, the risk of ground subsidence at
Lot23 throughout the service life of the residence is low and similar to other lots in the area but
the owner should be aware of the potential for sinkhole development.
Subsurface Conditions: The subsurface conditions at the site were evaluated by excavating two
exploratory pits in the building area and two profile pits in the septic disposal area at the
approximate locations shown on Figure 1. The logs of the pits are presented on Figure 2. The
subsoils encountered, below about I ta Ir/z feet of topsoil, consist mainly of dense, basalt cobbles
and boulders in a sandy clayey silt matrix. About lVzfeet of sandy silty clay with basalt rocks
was encountered between the topsoil and mostly basalt rocks in Profile Pit 2 in the southern part
of the septic area. Results of swell-consolidation testing performed on relatively undisturbed
samples of sandy clayey silt matrix soils, presented on Figures 3 and 4, indicate low
compressibility under existing moisture conditions and light loading and no to low collapse
potential when wetted. The samples were moderately compressible under increased loading after
wetting. Results of a gradation analysis performed on a sample of gravelly sandy loam (minus 3
inch fraction) obtained from the site are presented on Figure 5. The laboratory test results are
summarized in Table 1. No free water was observed in the pits at the time of excavation and the
soils were slightly moist.
Foundation Recommendations: Development of a residence on the lot should be feasible from
a geotechnical point of view. Considering the subsoil conditions encountered in the exploratory
pits and the nature of the proposed construction, we recoûlmend spread footings placed on the
undisturbed natural basalt rock soil designed for an allowable soil bearing pressure of 2,000 psf
for support of the proposed residence. The matrix soils tend to compress after wetting and there
could be some post-construction foundation settlement. Footings should be a minimum width of
16 inches for continuous walls and 2 feet for columns. I-oose and disturbed soils encountered at
the foundation bearing level within the excavation should be removed and the footing bearing
H-PVKUIVIAR
Proiect No 17-7-7A7
-3-
level extended down to the undisturbed natural soils. Exterior footings should be provided with
adequate cover above their bearing elevations for frost protection. Placement of footings at least
36 inches below the exterior grade is typically used in this area. Continuous foundation walls
should be reinforced top and bottom to span local anomalies such as by assuming an unsupported
length of at least l0 feet. Foundation walls acting as retaining structures should be designed to
resist a lateral earth pressure based on an equivalent fluid unit weight ofat least 50 pcffor the
on-site soil as backfill excluding topsoil and rock larger than about 6 inches. Excavation below
about 5 feet at this site will be difficult. Our experience in the Missouri Heights area is that a
typical good-sized trackhoe excavator used for residential construction should be capable of
excavating about 2 feet deeper in a foundation excavation than the depth where refusal to
digging was encountered in our pits. Narrow excavations such as utility trenches and tight
excavation corners may only be able to be excavated to the depth of our pits. Deeper
excavations will likely require rock excavation techniques such as chipping or blasting.
Floor Slabs: The natural on-site soils, exclusive of topsoil, are suitable to support lightly loaded
slab-on-grade construction. To reduce the effects of some differential movement, floor slabs
should be separated from all bearing walls and columns with expansion joints which allow
unrestrained vertical movement. Floor slab control joints should be used to reduce damage due
to shrinkage cracking. The requirements for joint spacing and slab reinforcement should be
established by the designer based on experience and the intended slab use. A minimum 4 inch
layer of free-draining gravel should be placed beneath basement level slabs to facilitate drainage.
This material should consist of minus 2 inch aggregate with less than 5O7o passing the No. 4
sieve and less than ZVo passingthe No. 200 sieve.
All fill materials for support of floor slabs should be compacted to at least 957o of maximum
standard Proctor density at a moisture content near optimum. Required fill can consist of the on-
site soils devoid of vegetation, topsoil and oversized rock.
Underdrain System: Although free water was not encountered during our exploration, it has
been our experience in the area that local perched groundwater can develop during times of
heavy precipitation or seasonal runoff. Frozen ground during spring runoff can also create a
perched condition. V[e recommend below-grade construction, such as retaining walls,
crawlspace and basement areas, be protected from wetting and hydrostatic pressure buildup by
an underdrain system.
The drains should consist of drainpipe placed in the bottom of the wall backfill sunounded above
the invert level with free-draining granular material. The drain should be placed at each level of
H.PèKUMAR
Project No.17-7-787
-4-
excavation and at least I foot below lowest adjacent finish grade and sloped at a minimu m !c/o to
a suitable gravity outlet. Free-draining granular material used in the underdrain system should
contain less than 27o passingthe No. 200 sieve, less than 507o passing the No. 4 sieve and have a
maximum size of 2 inches. The drain gravel backfill should be at least lr/zfeet deep.
Surface Drainage: The following drainage precautions should be observed during construction
and maintained at all times after the residence has been completed:
1) Inundation ofthe foundation excavations and underslab areas should be avoided
during construction.
2) Exterior backfill should be adjusted to near optimum moisture and compacted to
at least 95Vo of the maximum standard Proctor density in pavement and slab areas
and to at least 9A7o of the maximum standard Proctor density in landscape areas.
Free-draining wall backfill should be capped with about 2 feetof the on-site, finer
graded soils to reduce surface water infiltration.
3) The ground surface surounding the exterior of the buitding should be sloped to
drain away from the foundation in all directions. We recommend a minimum
slope of 12 inches in the first l0 feet in unpaved areas and a minimum slope of 3
inches in the first 10 feet in pavement and walkway areas. A swale may be
needed uphill to direct surface runoffaround the residence,
4) Roof downspouts and drains should discharge well beyond the limits of all
backfill.
Percolation Testing: Percolation tests l,vere conducted on November 13, Z0I7,to evaluate the
feasibility of an infiltration septic disposal system at the site. Two profile pits and three
percolation holes were dug at the locations shown on Figure 1. The test holes (nominal 12 inch
diameter by 12 inch deep) were hand dug at the bottom of shallow backhoe pits and were soaked
with water prior to testing. The soils exposed in the percolation holes are similar to those
exposed in the Profile Pits shown on Figure 2 and consist of gravelly sandy loam to sandy loam.
The percolation test results are presented in Table 2. Based on the subsurface conditions
encountered and the percolation test results, the tested area should be suitable for a conventional
infiltration septic disposal system. 'We recommend the infiltration area be oversized due to the
variable percolation rate. A civil engineer should design the infiltration septic disposal system.
Limitltions: This study has been conducted in accordance with generally accepted geotechnical
engineering principles and practices in this area at this time. We make no warranty either
expressed or implied. The conclusions and recommendations submitted in this report are based
H-PryKUMAR
Project Na.'17-7-787
-5-
upon the data obtained from the exploratory pits excavated at the locations indicated on Figure l,
the proposed type of construction and our experience in the area. Our services do not include
determining the presence, prevention or possibility of mold or other biological contaminants
(MOBC) developing in the future. If the client is concerned about MOBC, then aprofessional in
this special field of practice should be consulted. Our findings include interpolation and
extrapolation of the subsurface conditions identified at the exploratory pits and variations in the
subsurface conditions may not become evident until excavation is performed. If conditions
encountered during'construction appear different from those described in this report, we should
be notified at once so re-evaluation of the recommendations may be made.
This report has been prepared for the exclusive use by our client for design purposes. We are not
responsible for technical interpretations by others of our information. As the project evolves, we
should provide continued consultation and field services during construction to review and
monitor the implementation of our recommendations, and to verify that the recommendations
have been appropriately interpreted. Significant design changes may require additional analysis
or modifications to the recommendations presented herein. We recommend on-site observation
ofexcavations and foundation bearing strata and testing of structural fill by a representative of
the geotechnical engineer.
If you have any questions or if we may be of further assistance, please let us know.
Respectfully Submitted,
I.I.P*KUMAR
Daniel E. Hardin, P
Reviewed by:
Steven L. Pawlak, P.E
DEHlkac
attachments Figure I - Location of Exploratory Pits
Figure 2 - Logs of Exploratory Pits
Figures 3 and 4 - Swell-Consolidation Test Results
Figure 5 - USDA Gradation Test Results
Table I - Summary of Laboratory Test Results
Table 2 -Percolation Test Results
H.PæKUMAR
Project No,17-7-787
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17 -7 -787
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PIT 1 PIT 2 PROFILE
PIT 1
PROFILE
PIT ?
0 WC=6.5
-200=76
LL=34
Pl= 14
0
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SILT=29
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LEGEND
TOPSO|L; oRGANlc SANDY OLAY AND slLT, wlTH GRAVEL AND COBBLES, FIRM, MotsT, DARK
BROWN.
BASALT COBBLES AND BOULDERS (GM): IN SANDY CLAYEY SILT MATRIX, DENSE, SLIGHTLY
MOIST, WHITISH BROWN.
CLAY (CL): SANDY, SILTY, WITH BASALT GRAVEL, VERY ST|FF, SL|GHTLY MOIST, BROWN.
þ z-INCH DIAMETER HAND DRIVEN LINER SAMPLE.
F
I
DISTURBED BULK SAMPLE
PRACTICAL DIGGING REFUSAL.
NOTES
2.
3.
THE EXPLORATORY PITS WERE EXCAVATED WITH A BACKHOE ON NOVEMBER 13,2017.
THE LOCATIONS OF THE EXPLORATORY PITS WERE MEASURED APPROXIMATELY BY PACING FROM
FEATURES SHOWN ON THE SITE PLAN PROVIDED.
THE ELEVAÏIONS OF THE EXPLORATORY PIÎS WERE NOT MEASURED AND THE LOGS OF THE
EXPLORATORY PITS ARE PLOTTED TO DEPTH.
4. THE EXPLORATORY PIT LOCATIONS SHOULD BE CONSIDERED ACCURATE ONLY TO THE DEGREE
IMPLIED BY THE METHOD USED.
5. THE LINES BETWEEN MATERIALS SHOWN ON THE EXPLORATORY PIT LOGS REPRESENT THE
APPROXIMATE BOUNDARIES BETWEEN MATERIAL TYPES AND THE TRANSITIONS MAY BE GRADUAL.
6. GROUNDWATER WAS NOT ENCOUNTERED IN THE PITS AT lHE TIME OF DRILLING. PITS WERE
BACKFILLED SUBSEQUENT TO SAMPLING.
7. LABORATORY ÎEST RESULTS:
WC = WATER CONTENT (%) (ASTM D 2216)i
DD = DRY DENSITY (pcf) (ASTM D 2216);
-2OO = PERCENTAGE PASSING NO. 2OO SIEVE (ASTM D 11AO);
LL = LIQUID LIMIT (ASTM D a318);
PI = PLASTICITY INDEX (ASTM D 4318);
GRAVEL = PERCENT RETAINED ON NO. 10 SIEVE
SAND = PERCENT PASSING NO. 10 SIEVE AND RETATNED ON N0. JzS STEVE
SILT = PERCENT PASSING NO. 325 SIEVE TO PARTICLE SIZE .002mm
CLAY = PERCENT SMALLER THAN PARTICLE SIZE .002mm
-.rL
,Z
g
17 -7 -787 H-PVKUMAR LOGS OF TXPLORATORY PITS Fi1. 2
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SAMPLI OFr Sondy Clcyey Silt Motrix
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11 -7 *787 H-PryKUMAR SWTLL-CONSOLIDATION TEST RTSULTS Fig. 3
e
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4
SAMPLE OFr Sondy Clayey Silt Matrïx
FfiOM:Pit2@3'
WC = 13.1 %, DD = 74 pcf
-28Q z 79 %
I
ADDITIONÂL COMFRESSION
UNDTR CONSTANT PRTSSURI
DUE TCI WTTTING
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17 -7 -787 H.PryKUMAR SWELL_CONSOLIDATION TTST RTSULTS Fig. 4
20t7 - lo@dñ
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TABLE 1
SUMMARY OF LABORATORY TEST RESULTS
Project No. l7-7-787
SOILWPE
Sandy Clayey Silt
Matrix
Sandy Clayey Silt
Matrix
Gravelly Sandy Loam
Sandy [.oam
USDASOILTEXruRE
CLAY
(u')
1 7
(LL=34) (PI= 14)
SILT
(vù
29
SANX'
(v")
7A
34
GFAVEL
(vù
20
PERCENT
PASSING
NO.200
SIEVE
79
76
SAND
(T"l
GRAVEL
(hl
NATURAL
DRY
DENSITY
(pcf)
77
74
NATURAL
MOISTURE
CONTENT
e/.)
11.4
I 6J.I
'l.4
6.5
SAIIPLE LOCATION
DEPTH
(fr)
-J
J
1r/*2Vz
Wz-ZVz
PIT
I
2
Profile
Pir 1
Profi.le
Pit2
H:P*KUMAR
TABLE 2
PERCOLATION TEST RESULTS
PROJECT NO. 17-7-787
Note: Percolation test holes were hand dug in the bottom of backhoe pits. percolation
tests were conducted on November 13,2017. The average percolation rates
were based on the lasttwo readings of each test.
HOLE NO.HOLE
DEPTH
(rNcHES)
LENGTH OF
INTERVAL
(MrN)
WATER
DEPTH AT
START OF
INTERVAL
(rNcHES)
WATER
DEPTH AT
ENO OF
INTERVAL
(rNcHES)
DROP IN
WATER
LEVEL
(rNcHES)
AVERAGE
PERCOLATION
RATE
(MrN.fiNCH)
P-1 26 30 7 5Y4 13/o
60
514 4/t 1
4Y4 3Y1 1
g1/4 2%Y.
zsL 2%Y.
P-2 25 30 g%I 13/e
40
I 7Yl %
7lh 61A 1
61/¿íYz %
51h 4r/t '/+
P-3 28 30 81/,7%Y.
34
7%6 1s/c
6 4%1%
4Y¿4 %
4 3 1
ÇqPublb.net* Garfield County, Co
Account
Number
Parcel Number
Acres
Land SqFt
Tax Area
2019 Mill Levy
R008798 Physical
Address
239729205023
I Owner Address
0
011
79.7760
OSKIPPER DR
CARBONDALE
NORSK BUILDERS LTD
79 NAVAJO
CARBONDALECO
81623
2019Total Actual
Value
Overview
Legend
f-l Parcels
' Roads
Parcel/Account
Numbers
Owner Name
f',rî Lakes&Rivers
- CountyBoundary
Line
$250,000 Last2Sales
Date Price
7O/2I/2O2O $2o5,ooo
t2/t/2o77 $O
81623
Date created: LO/ 23/2022
Last Data Uploaded: IO/I3/2A22 !2:05:75 AM
Deveroned bv(Ét) FFtrBFlRt
10123122,3:43PM
Summåry
Account
Percêl
ROO8798
239129205023
OSKIPPERDR,CARBONDALECO S1ó23
qPublic.nêt - Garfisld County, CO - Propêrty Record Card: R008798
GÐqPrlHisneü" Garfield County, CO
Þrcperty
Address
Leg¡l S€ctlon:29 Townshlpr 7 Range:87 suM¡vlslon: STIRLING RANCH PUD Lot:23 EXCEPT A TR oF IAND
ftesrlptlon CONT.035ACASDESC lN ÊOUNÞARYLINEADJ REC#6óó9óó.8.1óSACRES
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CARBONDALE CO81ó23
Land
Unlt lyp6 VACANT RES LOTS - 0100 (VACANT LAND)
SquareFeêt 0
Actual Values
$23s,000.00
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L¿nd Actuâl
2022
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fotal Actual
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Texs B¡lled
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Tot¡lAsssd
$2s0,000.00
2t22
$0.00
$250,000.00
$0.00
$23s,(x)O.00
2024
$72,500-00
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$72,500.00
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$s,783.7ó
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$68,150.00
$0.0o
$7¿5m.(x,
2û79
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?918
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Cl¡ck here to view the tax lnformatlon for thls oarcêl on the Gârtl€ld Corntv Tressurer's website.
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qPublic.nêt ' Garfield County, CO - Properly Record Card: R00ô798
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Bøk- Peæ Sale Prlê
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.alJllclAlM DE€q.
STATEMENT OF AUTHORITY.!up!?9.17
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LETTERS
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