HomeMy WebLinkAboutWell Water Adequacy AnalysisJohn Plano
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Eric Mangeot <eric.mangeot@lrewater.com>
Monday, March 24,2025 9:03 AM
Kara Byrne; Brett Smith
John Plano
Tiny Homes
fi to, don't often get email from eric.mangeot@lrewater.com. Learn why this is important
Kara and Brett,
I just got off the phone with John Ptano with the Garfiel,d County ptanning department who is currentty
reviewing your BWCD water attotment contract for the issuance of buitding permits for the two tiny
homes. John woutd tike to see a copy of LRE Water's water adequacy report that inctuded the resutts of
the pump test and water quatity. lwoutd send this report to him mysetf, but because I am wearing
muttipte hats for this project (al,so as BWCD's Engineer), it woutd be better for you to send him this report
directl,y. I woutd send him the version dated 03-19-2025 that was revised for up to 10 tiny homes that I
sent to you [ast Wednesday.
Ptease feel free to contact me if you have any questions.
Best Regards,
Eric F. Mangeot, P.E.
Senior Project Manager
Office: 970-945-6777
E ric. Ma ngeot@LREwate r. com
CONHECTINC WA1EN TO LIFE
LREWATER.COM
909 Cotorado Avenue, Gtenwood Springs, CO 81601
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WATER
1
WATER
CONNECTINC WATER TO LIFE
KBBS Holdings, LLC
c/o Kara Byrne
248 Skipper Drive
Carbondale, CO 81623
kara@vou ra I ohawed d i nq. com
March 19,2025
Via Email
RE: Well Water Adequacy Analysis
Dear Kara,
At your request, LRE Water analyzed the water quantity and water quality associated with the
newly constructed well, Well Permit No. 334958 ("Well"), located on the KBBS Holdings, LLC
property located in the Lookout Mountain Ranches subdivision near Glenwood Springs, Colorado
(Garfield County Parcel No. 218512402034). A location map is included as Figure 1.
LRE Water conducted a24-hour constant-discharge pumping test on the Well. The pumping test
was performed to evaluate the well yield under current aquifer conditions. The test was performed
during the time of the year when groundwater is seasonally lower due to minimal recharge. The
well water is produced from an unconfined aquifer, which largely recharges from snowmelt run-
off and precipitation. ln addition to the pump test, water quality samples were collected and
analyzed. This letter report summarizes the opinion and findings of LRE Water regarding the
adequacy of the physical water supply for the proposed development on the property.
WATER DEMAND
LRE Water recently applied for a Basalt Water Conservancy District (BWCD) water allotment
contract which is the legal water supply for the proposed domestic water uses. The contract
covers ten tiny homes and up to 3,500 square feet of irrigation on the property. Proposed annual
demands are 2.94 acre-feet (AF) for indoor use and 0.146 AF for irrigation for a total of 3.086 AF.
WATER SUPPLY
WELL CONSTRUCTION
The Well was constructed on October 28,2024, by Shelton Drilling Company. The total depth of
the well is 555 feet and it was constructed with 7-inch diameter steel surface casing with
perforated steel casing installed in the water producing zone from 507 feet to 547 feet. At the time
of the well construction, static water level was 470 feet from the top of casing ("TOC") and the
well produced 8+ gallons per minute ("gpm") during a 2-hour test.
909 Colorado Averrue Glenwood Sprinus, CO 81601 | Ofl'ice: 970-945-6777 | LREWATER.COM
ROCKY MOUNTATN I MTDWEST I SOUTHWEST I TEXAS
Page 2 of 3
PUMPING TEST ANALYSIS
On December 12,2024, LRE Water met Samuelson Pump Company (Well pump installer) at the
well site, The test pump was installed near the bottom of the Well at 520 feet. A vented pressure
transducer was deployed in the Well and was set to record pressure and temperature readings
every minute during the test.
The static water level prior to the test was measured tobe 262.2 feet below the TOC. An average
pumping rate of approximately 8,7 gpm was calculated over the Z4-hour pumping period, with a
maximum pumping rate of 10.0 gpm and a minimum pumping rate of 7.85 gpm.
Throughout the pumping test, manual data was also collected in the field to determine if changes
to the flow rate were necessary. The test began with an initial rate of approximately 8.0 gpm and
was increased to 10.0 gpm after 19 hours of pumping. The 10.0 gpm pumping rate was
maintained throughout the remainder of the pumping test. The 1.0.0 gpm pumping rate was the
maximum rate the test pump was able to produce.
The water level reached a maximum drawdown depth of 463.09 feet below TOC (0.89 feet of
drawdown compared to static water levels) at the end of the test. Figure 2 graphically shows the
manual water depth measurements that were recorded during the test and Figure 3 shows the
drawdown in greater detail. The Well experienced minimal drawdown (-0.6 ft) in the first 19 hours
of pumping; therefore, the pumping rate was increased to 10 gpm. After approximately 1.5 hours
of pumping at 10 gpm the aquifer reached a steady state. ln a pumping test, reaching a steady
state means that the drawdown in the aquifer has stabilized and the water level and cone of
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indicative of a healthy aquifer. Over the 24-hour pumping period, approximately 12,535 gallons of
water were pumped from the Well.
ln addition to monitoring the water level during the pumping test, it is equally important to monitor
the recovery process. Therefore, the pump and pressure transducer were kept in place at the
conclusion of the test. The water level in the Well experienced 100% recovery within the first
minute. Figure 4 depicts the water level recovery in the Well.
ln Figure 5, T represents the totaltime since the pumping test started and T' represents the time
since pumping stopped. The Well reaches complete recovery at Tff' greater than 2 (48 hours /
24 hours), which means the Well recovered faster than the rate at which the Well was pumped.
This indicates that, at the time of the test, the Well completely recharged at a rate equal to or
more than the 8.7 gpm average pumping rate. ln other words, the recovery data indicates that the
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WATER QUALITY
The Well was sampled for a standard suite of parameters in accordance with CDPHE Regulation
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Page 3 of 3
Testing Laboratories, Ltd. The water quality results are tabulatedin Table 1 and a copy of the lab
results are also attached. Overall, results indicate that the Well has good water quality for potable
consumption and use.
The water quality results indicated the presence of coliform, but E. coli was not present. The lab
results only indicate that coliform was present and did not detail the type. While most coliform
bacteria are not harmful, some strains can cause gastrointestinal illness. The presence of coliform
could have been a result of field contamination from equipment used for testing or during
construction. To address this, LRE Water recommends using shock chlorination to disinfect the
Well prior to using the well as a potable water source.
Water quality results also indicated hard water at a value of 190 mg CaCOs/L, which is typical for
wells in the area. While there is no CDPHE standard for elevated hardness and no treatment is
required, LRE Water recommends that you consider utilizing a water softener as hard water can
lead to considerable scale buildup and staining.
CONCL USION
The results from the pumping tests indicate that the Well has more than sufficient yield to serve
the proposed domestic water uses. The aquifer drawdown during the pumping test was minimal
compared to the available drawdown, and the aquifer recharged by 100% within one minute after
pumping ceased indicating a healthy aquifer capable of producing at a rate of at least 10 gpm.
The water quality results indicated good water quality for potable consumption. However, LRE
Water does recommend using shock chlorination to disinfect the well prior to use. ln addition,
LRE Water also recommends that you also consider the use of a water softener.
Should you have any questions, or require additional information, please do not hesitate to contact
me by email at anqela.schenk@lrewater.com or by phone at (970) 945-6777.
Sincerely,
LRE WATER
Proj Manager
Hydrogeologist
Project Number 217 21KBBS01 (1 )
WATER
Test Well
Permit No. 334958
KBBS PROPERTIES LLC
BOUNDARY
SE114 SE1/4 Section 12, Township 6 South, Range 89 West, 6th P.M
I
'1,000
Scale:1"=2,000'
Figure 1: KBBS Holdings Test Well Location Map
Job No.21KBBS Holdings, tte
460,0
460.5
461.0
461".5
462.O
462.5
463.0
463.5
464.CI
464.5
455.0
L
Note: Exponential smoothing was used
on the depth of water dataset.
Figure 2: Depth from Top of Gasing (TOC)
Monitoring Well Permit No. 334942
Notes 1.) lnitial Water Level =
2.) FinalWater Level =
3.) Pump lntake Depth =
100
Pumping Time (minutes)
.A.
Static Water Level (ft)
Depth of Water from TOC
Manual Measurements
Flow Rate (gpm)
462.2ft.
463.09 ft.
520 ft.
below Top of Well Casing
below Top of Well Casing
from Top of Well Casing
:3o
€
7cl
o
EqT'
3
oo
(Jo
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10.0
8.0
6.0
4.0
2.O
0.0
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l
,A i
i
-i - - - q - -
--a =
L
j
'i^'[-"
A
A
n-
L
1*
.--l
Static Water Level = 462.2fL
Average Pumping Rate = 8.7 gpm
I WATER
10 1000
ozt03t2025
L
Note: Exponential smoothing was used
on the drawdown dataset.
Figure 3: Drawdown Analysis
Monitoring Well Permit No. 334942
Drawdown (ft)
Flow Rate (gpm)
6-
€voao
&T'
3
oo
g
3oTI
3l!
a
0.0
0.1
0.2
0.3
o.4
0.5
0.6
o.7
0.8
0.9
1-.0
11.0
9.0
7.O
5.0
3.0
1.0
-1.0
./-.
Average Drawdown
Minute 100 to 1000 = 0.79 ft.
wil
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\\ftrr
)
h
tr
J
10
Pumping Time (minutes)
100 1000
02n312025
^4.
Static Water Level (ft)
Residual Drawdown (ft)
Manual Measurements
Figure 4: Recovery Analysis
Monitoring Well Permit No. 334942
456
RecoveryTime (minutes)
462.O
oo
uo
Eo.! 463.0
-g
o.o6
460.0
461.0
464.4
\
10987321
I WATER
465.0
0
02t03t2025
oo
o
o(,o
cE,
0,0
0.L
0.2
0.3
o.4
0.5
0.5
0.7
0.8
+ ResidualDrawdown (ft)
T = TotalTime (Pumping & Recover)
T'= RecoveryTime
Figure 5: Recovery Analysis
Monitoring Well Permit No.334942
Notes:1.) The recharge rate of the well is equal to or greater than the
average pumping rate ( gpm), when recovery occurs
at or before T lT' = 2 (48 hrs I 24 hrs)
2.)Tn'= - lMl mins (1441 minutes / 1 minute),
Aquifer had recovered 100%.
1
l
I
l
l
10
T/T'(minutes)
100 1000
02!03t2025
Table 1
Regulated Water Quality Parameters
Well Permit No. 334958
ND = Not Detected
* National Standard, which is not an EPA enforcable MCL
Units 1211112024
PresentTotal Coliform
Parameter MCL
MPN/100mL
mg/L
Absent
0.007
E.coli
Arsenic 0.01
0.74Barium2mg/L
NDCadmium0.005 mg/L
Chromium 0.1 mg/L ND
Fluoride 4 mg/L ND
Mercury 0.002 mg/L ND
Nickel N/A mg/L ND
0.05 mg/L NDSelenium
10 mg/L NDNitrate - N
0.05 - 0.2
1 mg/L
mg/L
ND
ND
Nitrite - N
Aluminum
250 mg/L NDChloride
1.3 mg/L NDCopper
2 mg/L NDFluoride
mg/L 0.024lron0.3
mg/L NDLead0.015
mg/L NDManganese0.05
7.7pH6.5 - 8.5
mg/L NDSilver0.1
NDSulfate250mg/L
230TDS500mg/L
ND
ND
No detected VOCs or SOCs
mg/L as CaCO3Total Alkalinity
5Zinc mg/L
Uranium 0.03 mg/L
200
mg/L as CaCO3 190Total Hardness*100
mS/L 71.5Calcium
mg/L
NTU
3.77
0.2
Magnesium
Turbidity
mg/L NDOrtho Phosphate
VOCs & SOCs (only noting detected compounds)
Radlonucllcles
Total Coliform
Primary MCLs
Secondary MCLs
Corrosivity and Hardness
Additiolral WQ Pararrrters
W@ 0210312025