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STORMWATER DRAINAGE REPORT
Stites Office Building
I M EG #24006341 .00
PLNAPP #24637
SUBMITTEDJULY2025
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1143 Stoneridge Drive, Suite 1, Bozeman, MT
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TABLE OF CONTENTS
1. Introduction......................................................................................................................................3
2. Hydrology and Hydrogeology...........................................................................................................3
3. Existing Stormwater Drainage Conditions.......................................................................................4
4. Proposed Stormwater Drainage System .........................................................................................5
5. Evaluation of Major Storm Flood Risks............................................................................................7
6. Operation, Inspection, and Maintenance Considerations................................................................7
7. References.......................................................................................................................................8
8. Appendix A- Amended Plat
9. Appendix B - Baxter Meadows, Phase II Storm Drain Design Report
10. Appendix C- The Modified Rational Method Calculations
11. Appendix D - Drainage Area Map
12. Appendix E - Operation, Maintenance, and Inspection Plan
13. Appendix F- Geotechnical Investigation Report
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 2 May 27, 2025
Stormwater Drainage Report
For the
Stites Office Building
Prepared for:
City of Bozeman, MT
I M EG #24006341.00
July 8, 2025
1. Introduction
The Stites Office Building involves the development of a 5,100-square-foot office building and associated
site features on the eastern half three adjacent parcels legally described as Lots 4—6, Block 20, Baxter
Meadows Subdivision Phase 2A (Plat J-383) City of Bozeman, Gallatin County, MT. The project
necessitates an amendment to the existing plat from three lots (Lot 4-6) into two (Lot 4A and 5A). The
subject property, Lot 5A, is a 0.19-acre site situated north of Baxter Lane and west of Caballo Avenue.
The amended plat is included in Appendix A.
The existing ground cover is bare soil with little vegetative cover. According to historic satellite data from
Google Earth, the surrounding lots began subdividing and developing from agricultural farmland to
commercial development in 2004. Lot 5A is zoned for community business district use (B-2) and has
remained an undeveloped, empty lot bordered by existing arterial streets. The ground cover condition
changed from short vegetation to bare soil in 2023 based on aerial imaging. The topography is generally
flat with a 1-2% slope toward the north. The site elevation is higher than the bordering paved areas and
does not take on any additional offsite run-on. There are no existing watercourses on or adjacent to the
site.
This report provides background on the underlying stormwater system, presents runoff volume and flow
rate calculations, and outlines the integration of the proposed storm drainage features. It details how the
proposed stormwater facilities will adequately store, infiltrate, or convey runoff generated by the
development.
The development incorporates site grading and swales to convey stormwater to the proposed and existing
detention and retention facilities. It is proposed to utilize a subsurface retention basin to capture the post-
development runoff volume for the full range of storm events.
The stormwater runoff (CFS) was determined by the Rational Method. The analysis follows the
methodology and standards established by the City of Bozeman Design and Construction Standards
(October 2024), Montana DEQ Circular 8 (2024), and the Federal Highway Administration HEC-22 Manual
(4th Edition).
2. Hydrology and Hydrogeology
The hydrology for Lot 5A is based on NRCS Type II temporal rainfall distribution data. The City of Bozeman
precipitation depths for the post-development major storm duration and return interval are listed below
(DCP Table 6.5.1).
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 3 May 27, 2025
Table 6.5.1 - Precipitation Depth - Duration
(Depth in Inches)
Duration 2-year 5-year 10-year 25-year 50-year 100-year
24 hr 1.18 1.49 1.70 1.96 2.15 2.34
Precipitation intensity values (COB DCP Table 6.5.2) at the post-development major storm duration are
below.
Table 6.5.2- Precipitation Intensity- Duration
(Intensity in Inches per Hour�
Time (min) Time (hr) 2-year 5-year 10-year 25-year 50-year 100-year
1440 24 0.049 0.062 0.071 0.082 0.090 0.098
Runoff flow rates and runoff volumes were determined using The Rational Method by multiplying the major
storm duration (24 hrs) by the post-development runoff flowrates. The Rational Method was selected due
to the small lot area (under 5 acres) and homogeneous drainage area (DA).
Soils on Lots 4A and 5A consist of undocumented clayey fill over an organic soil horizon, followed by lean
clay soil, and pit run gravel. The depth to the pit run gravel horizon is 54 - 60 inches. The aquifer was
observed approximately 6.5-7.33 feet below ground surface, with signs of seasonal groundwater depth at
approximately 3 feet below grade, as recorded in the IMEG Geotechnical Investigation Report conducted
on October 24, 2024. This report is included in the submittal documents for the City of Bozeman Site Plan
Application #24637. The Baxter Meadows Phase 2A Plat J-383 recommends no basement to be
constructed below 3 feet from the top of curb. Due to the seasonal shallow depth of the aquifer, storm
facilities should be shallow or above ground to maximize recharge distance and minimize the surface water
interaction with the aquifer.
3. Existing Stormwater Drainage Conditions
Lots 4—6 are currently unimproved open lots within the Baxter Meadows Subdivision. The Phase II
Baxter Meadows Subdivision Storm Drain Design Report by Robert Peccia &Associates (Appendix B)
designed conveyance and storage systems to accommodate the known pre-development and estimated
post-development runoff for the subdivision. The current general runoff pattern on the property is sheet
flow. Stormwater runoff flows offsite northwest along the gutter in the right-of-way, then enters inlets at
the corner of Trakker Trail and Vaquero Parkway before being conveyed to a manhole that directs flow to
an offsite detention pond on the west side of Vaquero Parkway. The proposed development is within
Basin 1, as defined on pages 7,14, 17, 18, and 19 in the underlying subdivision report; a summary of the
contents is provided in Table 4-1.
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 4 May 27, 2025
Table 4-1. Basin 1 Characteristics (from RPA Storm Drain Report)
100-year
Basin 1 Area Rational Time of Intensity, i Peak Flow Runoff Volume,
(Ac) Coefficient, C Concentration, Tc(min) (in/hr) Rate, q (CFS) Q (FT3)
Pre-Development 2.9 0.2 29 1.03 0.6 893
Post-Development 2.9 0.5 25 1.64 1.64 2459
The Bain 1 subdivision infrastructure is not equipped to detain any runoff from Lot 5A. It is documented
that the subdivision experiences challenges with high groundwater and surcharging inlets at the
intersection of Trakker Trail and Vaquero Parkway per correspondence on January 17, 2025 with Russel
Smith in the stormwater department. On-site mitigation must be provided to store generated runoff from
development regardless of the underlying subdivision's plan. The following section will detail the accurate
land use proposed for the site.
4. Proposed Stormwater Drainage System
Per the City of Bozeman DCP's, the stormwater mitigated onsite by Lot 5A is the greater volume of two
scenarios: (1) retention of total runoff from the post-development 100-year storm event or (2) the water
quality design storm. The 100-year, 24-hour storm event exceeds the runoff reduction volume (RRV1.
4.1. Retention of Post- Development 100-year Storm Event
The proposed land use includes asphalt/concrete, roof area, and landscaping. The post-development
weighted runoff coefficient is 0.75. Pursuant to Section 6.8.1 of the Bozeman Design and Construction
Standards, the storm design duration for the 100-year event retention is 24 hours. The peak runoff
flowrate was calculated using the Rational Method, Q= Cr*C*I*A, where Q is the peak runoff flowrate
(CFS), C is the runoff coefficient (0.75), I is the rainfall intensity (in/hr) for the 100-year 24-hour storm
event, and A is the drainage area (acres). The rainfall intensity for the 100-year, 24-hour storm is 0.098
in/hr as listed in Table 6.5.2 in the Bozeman Design and Construction Standards. The rational method
yields a peak runoff flowrate of 0.017 CFS for the 100-year, 24-hour storm. The runoff volume was
calculated by multiplying the peak runoff flowrate (0.017 CFS) by the design duration (24 hours,
converted to 86,400 seconds) resulting in a volume of 1,491 cubic feet (CF), per Rational Methodology
following the guidance section 6.5.3 in the Design and Construction Standards. Calculations were done
at each timestep duration for each storm event to produce peak runoff flowrates and volumes. Detailed
calculations for the full range of storm events (2-year through 100-year) are provided in Appendix C. Table
4-3 below summarizes the runoff values for the 100-year, 24-hour event.
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 5 May 27, 2025
Table 4-3. Summary of Post-Development 100-year Storm Runoff
100-year
Rational Runoff
Area Area Design Duration, D Intensity, i Peak Flow
Basin 1 (Ac) (ft2) Coefficient, (min) (in/hr) Rate, q (CFS) Volume, Q
C (FT3)
Post- 0.193 8407.08 0.73 1440 0.098 0.017 1491
Development
4.2. Runoff Reduction Volume
The runoff reduction volume (RRV) was calculated using post-development site conditions according to
the Montana Post-Construction Storm Water BMP Design Manual. These calculations are in Appendix C.
The water quality design storm generates a runoff volume of 238 ft3.
4.3. Proposed Stormwater Facility
The proposed subsurface retention basin wraps around the building to the north, east, and west. The
proposed capacity is 1502 CF. The basin consists of an 191.5 LF, 36-inch HDPE perforated pipe encased
in 2" of gravel on either side, wrapped in geotextile filter fabric to provide screening, prevent migration of
fines and mitigate blockages to the pipe perforations. The retention volume within the pipe is 1354 CF
and the retention volume within the gravel is 151 CF. A recent Physical Properties of Aggregate Report
by Rimrock Engineering (included in Appendix C) for 3/a" bedding was used a sample to determine a
porosity value. The void content of the sample, e, is recorded as 37%. The porosity of the sample, n, was
calculated using the following equation: n = e/(1+e), resulting in 27% porosity. This value was used for
sizing the gravel storage area per Section 6.8.3.B.e of the City of Bozeman Design and Construction
Standards. Vegetated landscape depressions convey runoff into five catch basin inlets with 10-inch
sumps to capture sediments before entry into the buried pipe. The pipe invert will be buried shallower
than seasonal high groundwater, found at 3 ft bgs, to minimize interaction. A drainage area map is
provided in Appendix D showing the proposed runoff pattern and location of the retention facility on the
site.
To meet the 72-hour maximum drain-down time requirement, lean clay, located 2 to 5 feet below the
ground surface across the site, must be excavated from the retention basin footprint and replaced with
well-draining material. The 3-foot by 191.5-foot basin area should be excavated to the depth of poorly-
graded gravel (approximately 5 ft bgs) and backfilled with materials having an infiltration rate of 1 in/hr or
higher. Excavation beyond 3 feet below the ground surface may encounter saturated soils or
groundwater. Please reference Appendix C for maximum drain down time calculations and Appendix F
for the geotechnical investigation report.
There are two areas of the subject property comprised of 747 ftz of landscaped area and 641 ftz of
hardscaped area, that are not retained on-site. They are marked purple on the drainage area map. Runoff
from these areas flows directly offsite into the curb inlet at the intersection of Cabello Ave and Trakker
Trail, connecting to Basin 3 as outlined in the RPA Baxter Meadows Subdivision report. For a 100-year,
24-hour storm event, a peak runoff flowrate of 0.002 cfs and total runoff volume of 188 cu-ft is
contributed to the subdivision's stormwater infrastructure as calculated according to the Rational
Method. Runoff passes through landscaped filter strips before leaving the site. Refer to the table below
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 6 May 27, 2025
for a summary of these drainage areas and Appendix C for calculations covering the full range of storm
events. Please note that the peak runoff flowrate and retention volume calculated for the entire site is
stored in the retention basin located in drainage area 1 and therefore there is no analysis on DA 1.
Table 4-4. Summary of Drainage Areas
Total Area 100-year 24-hr
(acres) Total Impervious Area Pervious Rational 100-year 24-hr
DA Area (sf) (sf)/% Area (sf)/ % Coefficient, C Runoff Volume Runoff (cfs)
(cu ft)
1 0.161 7,039 5,227 1,812 0.73 See total See total
2 0.032 1,388 641 747 0.53 3.05 0.002
Total 0.193 8,427 5,868 2,559 0.73 1491 0.017
5. Evaluation of Minor& Major Storm Flood Risks
Table 4-5. Summary of Post-Development Runoff by Storm Event for 24-hour duration
Outputs: Post-Development
2-yr 5-yr 10-yr 25-yr 50-yr 100-yr
Intensit 0.05 0.06 0.07 0.08 0.09 0.10
Flow cfs 0.007 0.009 0.010 0.013 0.015 0.017
Volume cf 597 755 864 1098 1315 1491
The runoff from the 10-year, minor storm, is 864 ft3 and will be fully stored by the 1502 ft3 retention
basin. The total runoff volume in the 100-year return interval storm is 1491 ft3 and will be retained onsite
in the retention basin. If a storm larger than the 100-year return interval is to occur, the retention system
will first fill as designed then as the system exceeds the designed capacity, three inlets are connected to
6-inch horizontal pipes that are designed to convey water offsite. Two pipes discharge to the north and
one pipe discharges to the east, through the retaining wall, sheet flowing over the sidewalk, into the
gutter, and enter the inlets at Vaquero Parkway &Trakker Trail, and Caballo Avenue &Trakker Trail.
Runoff from drainage area 2 will be intercepted by Basin 3 (per RPA's subdivision stormwater report) if
the storm event exceeds the 100-year return interval. There is no conveyance or connection to any
existing storm infrastructure proposed during the major event as part of this lot development. The major
storm is retained onsite and does not inundate buildings or roads.
6. Operation, Inspection, and Maintenance Considerations
Please see OIM Plan in Appendix E.
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 7 May 27, 2025
7. References
City of Bozeman. (2024, October). City of Bozeman Design and Construction Standards.
https://www.bozeman.net/home/showpublisheddocument/14823/638724483537270000.
City of Bozeman. (2024, October). City of Bozeman Modifications to Montana Pu.blic Works Standard
Specifications, �`' Edition.
https://www.bozeman.net/home/showpublisheddocument/14824/638724489684800000.
HDR, & Montana Department of Environmental Quality. (2017, September). Montana Post-Const�uction
Storm WaterBMPDesign Guidance Manual. Montana.
U.S. Department of Transportation, Federal Highway Administration. (2024, February). Hydraulic
Engineering Circu/ar No. 22— Ur.ban Drainage Design, Fourth Edition.
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 8 May 27, 2025
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APPENDIX A
SURVEY REQUESTED BY OWNER TO CREATE TWO LOTS FROM THREE AMENDED PLAT OF LOTS 4, �J, AND 6
EXISTING LOTS AND RELOCATE THE COMMON BOUNDARY BETWEEN THE
REMAINING EXISTING LOTS WITHIN A PLATTED SUBDIVISION, AND EXEMPT BAXT E R M EA D OWS S U B D I V I S I O N P H AS E 2A
FROM REVIEW AS A SUBDIVISION PURSUANT TO 76-3-207 (1)(d) MCA. '
OWNER OF LOTS 4, 5, & 6 BLOCK 20: CYCLONE DEVELOPMENT, LLC
DEED REF.: DOC N0. 2842351 LOCATED IN THE SE1/4 OF SECTION 34, T.1S., R.5E., P.M.M., CITY OF BOZEMAN, GALLATIN COUNTY, MONTANA
� I
TRAKKER TRAIL I CERTIFICATE o � CONSENT
(90� R.�.W.� DETAIL 1 I, the undersigned property owner, do hereby certify that we have caused to be surveyed, aggregated, and
FOUND MONUMENT 0.64' I platted into lots, as shown by this plat hereunto included, the following described tract of land, to wit:
N89�24'53"E (R1) � BEARING N13°51'E FROM
CALCULATED POINT I LEGAL D ESC R I PTI O N
S89'06'45"E (F) 329.30' (R1&F) ,
- - - - _ _ _ 156.40 (R1&F) I
��6.9�' R1&F T Lots 4, 5, and 6, Block 20, Baxter Meadows Subdivision, Phase 2A, according to the plat thereof, on file
C � 66.�0' (R1&F) , and of record in the office of the Clerk and Recorder, Gallatin County, Montana, and located in the SE1/4
I I � 73.�J3 82.87' I of Section 34, T. 1 S., R. 5 E. P.M.M., Gallatin County, Montana.
I „ �� � �� i. r- �
� , ,� , �� i � � "� � Area = 15,905 square feet, 0.365 acres, more or less, and subject to all easements and rights-of-way as
�` '� '� � shown, existing or of record.
I I 15' UTILITY EASEMENT� i � i i i '�� ��� , `- " -+ ` � ��
G PER PLAT [J-383] �� " "I' � � NEW BOUNDARY I
� � We hereby certify that the purpose of this survey is to depict the relocation and aggregation of lots within
� I I ^ I a platted subdivision, therefore this division of land is exempt from review as a subdivision pursuant to
r, � � � I � I V- section 76-3-207(1)(d), MCA to wit: "for five or fewer lots within a platted subdivision, the relocation of
� � � � �, -�- � , ,� _,_ ��_ � common boundaries" and 76-3-207(1)(f), MCA, to wit: "aggregation of parcels or lots when a certificate of
� I \ � I � � � � � � � � � � � �-, ' '` -'- '' � I survey or subdivision plat shows that the boundaries of the original parcels have been eliminated and the
L_ \J I -t I I I I V\
� � J � v �- " ' �" I �_ .� � .. � boundaries of a larger aggregate parcel are established. a restriction or requirement on the original platted
�� I I � � � � I lot or original unplatted parcel continues to apply to those areas ,
� � � I
� O � t�p I � � further this plat is to be known and designated as: AMENDED PLAT OF LOTS 4, 5, AND 6, BLOCK 20,
� I I r- � � O I BAXTER MEADOWS SUBDIVISION PHASE 2A.
�, I o LOT 4A o LOT 5A � � , �
� v � �'�� -�- � ,�, � ,, -�- ,, � 7 477 S Ft. �� � 4 5 4 5' �
�,,� w I �- �� � � �-� I L ���� � < I + q• 8,427 S q.Ft. ^p C E R T I �I C A T E O F E X E M P T I O N
� � W _0.172 AC � � +0.193 AC �� I AGGREGATION OF LOTS AND RELOCATION OF COMMON BOUNDARY
Z �. I � � � �, � o . I ( )
I � / � I � Z � We certify that the purpose of this survey is to relocate the common boundary between adjoining properties
� I � � and aggregate three existing lots into two new lot and being Lots 4, 5, and 6, BAXTER MEADOWS
M
O � � � �-- I SUBDIVISON PH2A, GALLATIN COUNTY, MONTANA, and that this exemption complies with all conditions imposed
� p 0 JI O I � > on its use. Therefore, this survey is exempt from review as a subdivision pursuant to Section
� Z I I � Z PREVIOUs BOUNDARY � PREVIOUS BOUNDARY � a I 76-3-207(1)(d) and 76-3-207(1)(f), MCA, and the Gallatin County Subdivision Regulations.
� � I' O �
� I I N O � �'�. I Dated this day of . 2025. Cyclone Development, LLC,
� � I I J O a Montana Limited Liability Company
� I I � ---� p I STATE OF MONTANA
� , I I w � COUNTY OF GALLATIN By: Jon Stites, Registered Agent
Q � _ _ _ _ 106.90 (R1&F) _ _ _ _ � _ _ 66.00' (R1&F) � 73.53' M
- -L _ 82•$7� W I This instrument was signed or acknowledged before me on this day of , 2025,
� O :^ � I I by Jon Stites, Registered Agent of Cyclone Development, LLC, a Montana Limited Liability Company.
� � : � N89'06'45"W (F) 329.30' (R1&F) 156.40' (R1&F) � U
^ I Notary Public for the State of Montana
N89'24'S3"E (R1) �- �
� `� �� � : Printed Name:
w :� ALLEY �
Residing at:
� : rp �v: I My commission expires:
� N89'24'S3"E (R1) �
� � - - - - - - - - - - _S89'06'45"E F 329.30 R1&F) � � I I `\1� ��,,,u���������••••.,,,��,
_ - - - - - - ! ! �� N T q � CERTI �ICATE O � SUR�/EYOR
Q � ` `
i , � � - - - - - - - - _ _ _ _ � ���� ������..��d"""��""""���.,,,,���= I, Matthew Jacobson, Professional Land Surveyor No. 13748LS, do hereby certify that between December 19,
� O
> 164.66 (R1&F� � - \� �: :,9 \ 2024 and March . 2025, this survey was made by me or under my direct supervision and that this
I I 164.64' (R1&F) � � = MATTHEW =;
FOUND 5/8" REBAR W/ � I �.* � JACOBSON � .�� ActP Sect ons 76 P3 S101S through 76 3 n625h M.0 A.c�andr he tBozeman rMunic paltCodeSubdivision and Platting
� =- 13748 LS � �
2" ALUMINUM CAP ' "'��" ����`��� Dated this da of 2025.
I (14535/13601 LS) � I � I � I
� I I � =�q��q,,,p��F,�, O`\��� y Matthew Jacobson
� ''�o� SUFZv�I���� Montana License No. 13748LS
� i���� ����I
I I I I I � i//////////llll
� I CERTIFICATE O � GO�/ERNING BODY
B � OCI� 20 � �
� � � . . . . .
I � I I � � I I I, Director of Community Development, City of Bozeman, Montana, do hereby certify that the exemption
J
� � 15' UTILITY EASEMENT � v claimed on the accompanying plat has been duly examined, and has found the same to conform to law,
I � I � & PEDESTRIAN �� I
I approves it.
WALKWAY PER PLAT I � �
I � I � [J-383] I ��1j I Dated this day of . 2025.
O I Director of Community Development
I � I � W �' I City of Bozeman, Montana
� �. -�- �� � � ., -�- .. � �
�_ �..� � �' ,'-�� I I �_ '„ ; ! ;; �_ ���� � � ^ ��� � � I CERTI �ICATE OF EXCLUSION FROM MONTANA
I � I � I ;� � I � I DEPARTMENT OF EN�/IRONMENTAL QUALITY RE�/IEW
�� � O �
I N � I I i I w� p r- I The accompany'ing plat is within the City of Bozeman, Montana, a first-class municipality, and within the
� ao (n � I planning area of the Bozeman growth policy which was adopted pursuant to Section 76-1-601 et seq.,
� � ;n M.C.A., and can be provided with adequate storm water drainage and adequate municipal facilities. Therefore,
I � � � I � I „Q� O I under the provisions of Section 76-4-125(2)(d)(iii) M.C.A., this subdivision is excluded from the requirement
I Q � I I I � J N I for Montana Department of Environmental Quality review.
�z w � � � � � I Dated this day of 2025.
- � � w Director of Transportation and Engineering
� - - - - - - - - - - - - - - - - - - - - - - - - - - - - - � - I- � - - - I � � I I City of Bozeman, Montana
I --� I + - - - - - - - - - � - - - - - - - - - - - - - - - - - �
_- _- _- - - - � � I I
- - - - - - - - - CERTIFICATE O � COUNTY TREASURER
� -� �� I- � - - - - _  _  _  _ _� I I, Maureen Horton, Treasurer of Gallatin County, Montana, do hereby certify that the accompanying
Certificate of Survey has been duly examined and that all real property taxes and special assessments
' . I assessed and levied on the land to be divided have been paid.
DETAIL 1 VICINITY MAP � Dated this day of . 2025.
SCALE: 1" = 1' NOT TO SCALE SUBJECT PROPERTY � I Deputy Treasurer of Gallatin County
c� .
� .
� � . I CLERK AND RECORDER
� � I, Eric Semerad, Clerk and Recorder of Gallatin County, Montana, do hereby certify that the foregoing
o L E G E N D . I instrument was filed in my office at o'clock _.M. this day of
o � � A.D., 2025, and recorded in Book of Plats, on Page , records of the Clerk and Recorder,
z (R�) RECORD OR ADDITIVE PER AMENDED PLAT J-383B �R�� . Gallatin County, Montana.
'1' FOUND 5/8" REBAR I
Q (F) FOUND THIS SURVEY BENT, NO CAP ��.�
� 00 SET 5/8" REBAR W/ 1-1/4"YELLOW PLASTIC CAP, IMEG #13748LS � �R>>�, I Deputy Clerk and Recorder
� �
"� � FOUND MONUMENT AS NOTED �
o �� , � R�,,�iC�
N 0 5/8" REBAR WITH 2"ALUMINUM CAP#12249LS, FOUND S89'06'45"E (F) � N13°51 E � �jJ; . I
O 0.64' (TIE) �
w � 5/8" REBAR WITH 2"ALUMINUM CAP#14535LS, FOUND 82.g7' � � R� . I Note:
BAXTER LANE
� PROPERTY BOUNDARY LINE ��� ) ' Pursuant to A.R.M. 24.183.1104 UNIFORM STANDARDS FOR CERTIFICATES OF SURVEY: Section (1)(f)(iii)(C) "The area that is
� J being removed from one tract of record and joined with another tract of record is not itself a tract of record. Said
j - - - - - SURROUNDING PROPERTY LINE j � � �� I area shall not be available as a reference legal description in any subsequent real property transfer after the initial
�-' � transfer associated with the [certificate of survey or amended plat] on which said area is described, unless said area is
� - - - - - - - EASEMENT LINE � z � J
�J LOT 5A � � � Q • I included with or excluded from adjoining tracts of record."
� > � � .
"� U � CO � Q � .
/ I
r,� z , Q '
N o 20 0 20 40 0 0 / � �
FOUND 5 8" REBAR W I
/ RED PLASTIC CAP .
0 0 (ILLEG) �
N � SCALE IN FEET
� SHEET 1 OF 1
N o BASIS OF BEARING: BOZEMAN, MONTANA
� � MTSTATEPLANE AMENDED PLAT OF LOTS 4, 5, AND 6
�j 1143 STONERIDGE DR PH: ZONE 25001/4 S E C. T. R.
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�% BOZEMAN,MT 59718 � 34 �s. 5E. AN AMENDED PLAT OF GALLATIN COUNTY
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APPENDIX B
PHASE II
BAXTER MEADOWS
DESIGN REPORT
Revised April 2004
TABLE OF CONTENTS
City of Bozeman—Plans and Speci�cations Certified Checklist
Response to Comments on Preliminary Design Report Review (M-M 1/19I04)
Response to Comments on Preliminary Plat Submittal (M-M 12/12/03)
Water System Design Report
Revised Water Modeling
Water Main DEQ Certified Checklist
Sanitary Sewer System Design Report
Sewer Main DEQ Certified Checklist
Storm Drain Design Report
Revised Storm Drainage Modeling
Storm Drainage Maintenance Plan
Traffic Impact Study Update
PHASE II
BAXTER MEADOWS
STORM DRAIN DESIGN REPORT
OCTOBER 2003
By:
ROBERT PECCIA AND ASSOCIATES
P.O. Box 5653
HELENA, MT 59604
�D�ERT PF�C'0
1 1
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�qssOC1A'�`�
For:
CITY OF BOZEMAN
BAXTER MEADOWS DEVELOPMENT
Design Report— Storm Drain System
A. GENERAL DESIGN CRITERIA
1. The storm water drainage plan was designed to limit storm water runoff from the
developed sites to pre-developed runoff rates. There are seven drainage basins
contained in Baxter Meadows - Phase II. Calculations of pre and post development
runoff are included in this report. The calculations are used to determine the volume
and area of the seven detention basins. The basins are designed to be self-draining
and are therefore gradually sloped from inlet to outlet at which point the basin reaches
a depth of eighteen inches.
2. Vegetation and settling action will help remove solids, silts, oils, grease, and other
pollutants contained in storm drainage water that flows into the detention basins.
3. Storm Sewer design meets the City of Bozeman requirements:
a. Alignment between manholes is straight.
b. Pipe slopes are uniform. Design velocities are at least 3-ft/sec.
c. Pond inlet and outlet piping is designed to protect against and prevent erosion.
d. All storm drain pipe is RCP. Inlet laterals are 12-inch and mains are at least 15-
inch diameter.
e. Storm sewer pipe is designed to handle a 25-year storm event.
f. Nine-inch sumps are used for sediment collection in inlets and manholes.
B. STORM DRAIN PLAN
A storm drain plan for the Baxter Meadows subdivision has been approved by the City of
Bozeman. Components of the storm drain system (detention basins,pipes, and inlets) for
Phase II have been designed according to the general guidelines contained in the storm
drain plan.
1. The approved storm drainage plan included drawings showing the development's
drainage features, ground surfaces, etc.
2. Topographic contours (one-foot intervals) and spot elevation data are included in the
plans.
3. Storm water runoff from the Phase II sites drains into detention ponds. Settling
removes suspended solids and other pollutants. The ultimate destination of storm water
runoff from the site is Spring Ditch. Discharge from the detention ponds is limited to the
pre-developed runoff rate by the pond outlet structures thereby minimizing impacts on
down slope drainage facilities and water quality.
4. Design calculations showing runoff quantities and storage requirements are included in
this report.
5. The approved storm drainage facilities maintenance plan a. identifies ownership of all
facilities., b. establishes a schedule for maintenance activities, and c. identifies the
responsible party in charge of the specific maintenance duties.
6. Details and specifications (including invert and other pertinent elevation information)
for all stortn drainage improvements are included in the plans.
C. STORAGE/TREATMENT FACILITIES
The detention ponds for Phase II were sized based on a 10-year, 2-hour storm intensity.
1. Detention Basins
The detention basins were designed for water storage. Outlet-discharge is controlled by a
designed outlet structure.
2. Basin Sizing
The detention basins were designed to hold the difference between the pre-developed and
developed runoff volumes. The final design of the ponds meets or exceeds the City of
Bozeman minimum basin area of 145-square feet per 1-cfs release rate used for sediment
control. Likewise the detention ponds meets the City of Bozeman depth requirements of
no more than 2.5-feet deep with 1.5-feet maximum water depth.
3. Basin Location
The detention basins are located in open areas as shown on the attached drawings.
4. Additional Requirements
Above ground earth formed detention basins not used in the project.
D. DISCHARGE STRUCTURES
1. Orifice controlled discharge structures were designed to restrict detention pond
discharge to pre-developed rates. Design calculations are included in this report.
2. Orifice calculations for controlling discharge to pre-development rate are included this
report.
3. Fail/safe features are part of the design. They include:
a. Emergency free-flowing overflow for rates exceeding design storm events.
b. Discharge piping is at least six inches in diameter capable of conveying a 25-year
storm event.
c. Ponds are designed to avoid long-term standing water by sloping the basin floors
toward the outlet structure.
E. ESTIMATION OF RUNOFF
1. GENERAL The rational method was used to estimate runoff. The basic assumptions
that apply are:
a. Rainfall is uniformly distributed over area for duration of the storm.
b. Peak runoff occurs when duration of storm equals time of concentration.
c. Runoff coefficient for particular watershed is constant for a similar land use.
Rational formula used to determine runoff coefficients: Q =CiA.
2. RUNOFF COEFFICIENTS
Runoff coefficients used for the Phase II design are as follows:
a. Open land--0.20
b. Low to medium density residential--0.35
c. Dense residential--0.50
d. Commercial neighborhood--0.60
e. Commercial downtown--0.80
f. Industrial--0.80
3. TIME OF CONCENTRATION
The time of concentration is the flow time from the most remote point in the drainage to
the point in question. It consists of overland flow time and the channel flow time. The
overland flow time was estimated with the use of ineasured distances and figure I-1
included in part I of Appendix C. The channel flow time in pipes was determined by
estimating the velocities with the Manning equation.
V = (1.486*R^2/3*S^1/2)/n
V=mean velocity(ft/sec)
n=Manning roughness coefficient
R=Hydraulic radius=cross sectional area/wetted perimeter
The following typical "n"values from table I-2 were used for time of
concentration calculations and are included in part I of Appendix C.
a. Open unlined channels--0.035
b. Concrete and RCP pipe--0.013
4. STORM INTENSITY
The intensity of the storm was determined form Figure I-2, I-3, and the City of Bozeman
Design Frequencies for rainfall. Assuming equal to time of concentration.
a. Open land, 2-year
b. Residential, 10-year
c. Commercial or industrial, 10-year
5. RLJNOFF RATES AND VOLUMES
Values for peak runoff rates were computed using the rational formula. This rate occurs
at the time of concentration. Values for runoff volume were calculated using the modified
rational method. This method assumes the maximum runoff rate begins at the time of
concentration and continues to the end of the storm. Maximum runoff rates are less than
the peak runoff rate for durations greater than the time of concentration due to the
decrease in storm intensity as duration increases. By multiplying the duration of the
storm by the runoff rate the volume is computed.
Baxter Meadows-Phase II
Detention Basin 1
Design Storm Frequency 10 yr
Basin Area(Ac) 2.90
Pre-Development Ccefficient C Post-Development Coefficient C
Area(Ac) C Area(Ac) �
Open Space 2.9 0.20 Open Space 0.20
Med. Res. 0.35 Med.Res. 0.35
Dense Res. 0.50 Dense Res. 2.9 0.50
Comm. Neigh. 0.60 Comm.Neigh. 0.60
Comm.Down 0.80 Comm.Down 0.80
Industrial 0.80 Industrial 0.80
Total Area: 2.9 Composite C: 0.2 Total Area: 2.9 Composite C: 0.5
Pre-Development Post-Development
Runoff Distance 400 ft Runoff Distance 550 ft
Average Slope 1.75% Average Slope 1.30%
Time of Concentration 29 min Time of Concentration 25 min
Average Rainfall Intensity 1.03 in/hr Average Rainfall Intensity 1.13 in/hr
Maximum Runoff 0.60 cfs Maximum Runoff 1.64 cfs
Storm Intensity Developed Developed Undeveloped Required
Duration 10 Yr Flow Runoff Runoff Storage
(min) (in/hr) (cfs) (c� (cf) (cfl
5 3.22 4.67 1400 179 1221
10 2.05 2.97 1784 357 1427
15 1.58 2.29 2057 536 1521
20 1.31 1.90 2274 715 1560
25;, ' t:13 ; 1.6d" 2459 893°. 15G6
30 1.00 1.46 2621 1072 1549
35 0.91 1.32 2766 1250 1516
40 0.83 1.21 2899 1429 1470
45 0.77 1.12 3021 1608 1413
50 0.72 1.04 3134 1786 1348
55 0.68 0.98 3241 1965 1276
60 0.64 0.93 3341 2144 1197
65 0.61 0.88 3436 2322 1113
70 0.58 0.84 3526 2501 1025
75 0.55 0.80 3612 2680 933
80 0.53 0.77 3695 2858 837
85 0.51 0.74 3774 3037 737
90 0.49 0.71 3850 3215 635
95 0.47 0.69 3924 3394 530
Minimum Basin Area
Minimum Volume= 1566 cf
Minimum Area(18"basin depth) 1044 sf Actual Area(shaped to drain)= 2088 sf
Minimum Area for Sediment Control-->145 sf per 1 cfs
Peak Developed Flow-> 1.64 cfs
Minimum Area= 238 sf
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Baxter Meadows-Phase II
Detention Basin 2
Design Storm Frequency 10 yr
Basin Area(Ac) 2.17
Pre-Development Coefficient C Post-Development Coe�cient C
Area(Ac) C Area(Ac) �
Open Space 2.17 0.20 Open Space 0.20
Med.Res. 0.35 Med.Res. 0.35
Dense Res. 0.50 Dense Res. 2.17 0.50
Comm.Neigh. 0.60 Comm.Neigh. 0.60
Comm.Down 0.80 Comm.Down 0.80
Industrial 0.80 Industrial 0.80
Total Area: 2.17 Composite C: 0.2 Totai Area: 2.17 Composite C: 0.5
Pre•Development Post-Development
Runoff Distance 500 ft Runoff Distance 650 ft
Average Slope 1.20% Average Slope p,gp�/,
Time of Concentration 36 min Time of Concentration 32 min
Average Rainfall Intensity 0.89 in/hr Average Rainfall Intensity 0.96 in/hr
Maximum Runoff 0.39 cfs Maximum Runoff 1.04 cfs
Storm Intensity Developed Developed Undeveloped Required
Duration 10 Yr Flow Runoff Runoff Storage
(min) (in/hr) (cfs) !c� (c� (c�
5 3.22 3.49 1048 116 931
10 2.05 2.23 1335 232 1103
15 1.58 1.71 1539 348 11 gp
20 1.31 1.42 1702 465 1237
25 1.13 1.23 1840 581 1259
30 : "t.Od 1.09 1961 897 `'` ° ; 1284 , "
35 0.91 0.99 2070 813 1257
40 0.83 0.90 2169 929 1240
45 0.77 0.84 2260 1045 1275
50 0.72 0.78 2345 1161 1184
55 0.68 0.73 2425 1278 1147
60 0.64 0.69 2500 1394 1106
65 0.61 0.66 2571 1510 1061
70 0.58 0.63 2638 1626 1012
75 0.55 0.60 2703 1742 961
80 0.53 0.58 2765 1858 906
85 0.51 0.55 2824 1974 850
90 0.49 0.53 2881 2091 790
95 0.47 0.52 2936 2207 729
100 0.46 0.50 2989 2323 666
105 0.44 0.48 3041 2439 602
110 0.43 0.47 3091 2555 535
115 0.42 0.45 3139 2671 468
120 0.41 0.44 3186 2787 399
125 0.40 0.43 3232 2904 328
130 0.39 0.42 3277 3020 257
135 0.38 0.41 3320 3136 184
140 0.37 0.40 3363 3252 111
145 0.36 0.39 3404 3368 36
150 0.35 0.38 3445 3484 -39
Minimum Basin Area
Minimum Volume= 1264 cf
Minimum Area(18"basin depth) 843 sf Actual Area(shaped to drain)= 1685 sf
Minimum Area for Sediment Control->145 sf per 1 cfs
Peak Developed F�ow-> 1.09 cfs
Minimum Area= 158 sf
Baxter Meadows -Phase II
Detention Basin 3
Design Storm Frequency 10 yr
Basin Area(Ac) 12.15
Pre-Development Coe�cient C Post-Development Coefficient C
Area(Ac) C Area(Ac) C
Open Space 12.15 0.20 Open Space 0.20
Med.Res. 0.35 Med.Res. 0.35
Dense Res. 0.50 Dense Res. 3.15 0.50
Comm.Neigh. 0.60 Comm.Neigh. 9 0.60
Comm.Down 0.80 Comm.Down 0.80
Industrial 0.80 Industrial 0.80
Totai Area: 12.15 Composite C: 0.2 Total Area: 12.15 Composite C: 0.57
Pre-Development Post-Development
Runoff Distance 1300 ft Runoff Distance 1900 ft
Average Slope 0.80 % Average Slope 0.50 %
Time of Concentration 67 min Time of Concentration 38 min
Average Rainfall Inte�sity 0.60 in/hr Average Rainfall Intensiry 0.86 in/hr
Maximum Runoff 1.45 cfs Maximum Runoff 6.01 cfs
Stortn Intensity Developed Developed Undeveloped Required
Duration 10 Yr Flow Runoff Runoff Storage
(min) (in/hr) (cfs) (c� (c� (c�
5 3.22 22.45 6735 434 6300
10 2.05 14.31 8584 869 7715
15 1.58 10.99 9892 1303 8590
20 1.31 9.12 10940 1737 9203
25 1.13 7.89 11829 2171 9658
30 1.00 7.00 12609 2606 10003
35 0.91 6.34 13308 3040 10268
40 0.83 5.81 13944 3474 10470
45 0.77 5.38 14531 3908 10623
50 0.72 5.03 15077 4343 10734
55 0.68 4.72 15588 4777 10811
60 0.64 4.46 16070 5211 10859
65 ; ' 0.61 4.24 76527 ' S645 ::1fl882 .
70 0.58 4.04 16961 6080 10882
75 0.55 3.86 17376 6514 10862
80 0.53 3.70 17773 6948 10824
85 0.51 3.56 18154 7383 10771
90 0.49 3.43 18521 7817 10704
95 0.47 3.31 18875 8251 10623
100 0.46 3.20 19216 8685 10531
105 0.44 3.10 19547 9120 10428
110 0.43 3.01 19868 9554 10314
115 0.42 2.92 20180 9988 10192
720 0.41 2.84 20483 10422 10060
125 0.40 2.77 20777 10857 9921
130 0.39 2.70 21065 11291 9774
135 0.38 2.64 21345 11725 9620
140 0.37 2.57 21618 12159 9459
145 0.36 2.52 21885 12594 9292
150 0.35 2.46 22147 13028 9119
Minimum Basin Area
Minimum Volume= 10882 cf
Minimum Area(18"basin depth) 7255 sf Actual Area(shaped to drein)= 14509 sf
Minimum Area for Sediment Control->145 sf per t cfs
Peak Developed Flow-> 4.24 cfs
Minimum Area= 615 sf
Baxter Meadows-Phase II
Detention Basin 4
Design Storm Frequency 10 yr
Basin Area(Ac) 3.18
Pre-Development Coefficient C Post-Development Coefficient C
Area(Ac) C Area(Ac) C
Open Space 3.18 0.20 Open Space 0.20
Med.Res. 0.35 Med.Res. 1.06 0.35
Dense Res. 0.50 Dense Res. 2.12 0.50
Comm.Neigh. 0.60 Comm.Neigh. 0.60
Comm.Down 0.80 Comm.Down 0.80
Industrial 0.80 Industrial 0.80
Total Area: 3.18 Composite C: 0.2 Total Area: 3.18 Composite C: 0.45
Pre-Development Post-Development
Runoff Distance 500 ft Runoff Distance 600 ft
Average Slope 1.60 % Average Slope 1.06 %
Time of Concentration 33 min Time of Concentration 32 min
Average Rainfall Intensity 0.94 in/hr Average Rainfall Intensity 0.96 in/hr
Maximum Runoff 0.60 cfs Maximum Runoff 1.38 cfs
Stortn Intensiry Developed Developed Undeveloped Required
Duration 10 Yr Fiow Runoff Runoff Storage
(min) (in/hr) (cfs) (c� (cf) (c�
5 3.22 4.61 1382 180 1202
10 2.05 2.94 1761 360 1401
15 1.58 2.26 2030 540 1489
20 1.31 1.87 2245 720 1524
25; 1.13 ' 1:82.' 2427 .` 901 1526"'"`
30 1.00 1.44 2587 1081 1506
35 0.91 1.30 2730 1261 1469
40 0.83 1.19 2861 1441 1420
45 0.77 1.10 2981 1621 1360
50 0.72 1.03 3093 1801 1292
55 0.68 0.97 3198 1981 1217
60 0.64 0.92 3297 2161 1136
65 0.61 0.87 3391 2341 1049
70 0.58 0.83 3480 2521 958
75 0.55 0.79 3565 2702 863
80 0.53 0.76 3646 2882 765
85 0.51 0.73 3724 3062 663
90 0.49 0.70 3800 3242 558
95 0.47 0.68 3872 3422 450
Minimum Basin Area
Minimum Volume= 1526 cf
Minimum Area(18"basin depth; 1017 sf Actuai Area(shaped to drein)= 2035 sf
Minimum Area for Sediment Control-->145 sf per 1 cfs
Peak Developed Flow-> 1.62 cfs
Minimum Area= 235 sf
Baxter Meadows-Phase II
Detention Basin 5
Design Storm Frequency 10 yr
Basin Area(Ac) 16.16
Pre-Development Coefficient C Post-Development Coefficient C
Area(Ac) C Area(Ac) �
Open Space 16.16 0.20 Open Space
0.20
Med.Res. 0.35 Med.Res. 16.16 0.35
Dense Res. 0.50 Dense Res. 0.50
Comm.Neigh. 0.60 Comm.Neigh. 0.60
Comm.Down 0.80 Comm.Down 0.80
Industrial 0.80 Industrial 0.80
Total Area: 16.16 Composite C: 0.2 Total Area: 16.16 Composite C: 0.35
Pre-Development Post-Development
Runoff Distance 1200 ft Runoff Distance 1500 ft
Average Slope 1.10 % Average Slope p,�z %
Time of Concentration 58 min Time of Concentration 62 min
Average Rainfall Intensity 0.65 in/hr Average Rainfall Intensity 0.63 in/hr
Maximum Runoff 2.11 cfs Maximum Runoff 3.54 cFs
Storm Intensity Developed DevelopedJndevelope Required
Duration 10 Yr Flow Runoff Runoff Storage
(min) (in/hr) (cfs) (cf) (c� (�
5 3.22 18.20 5461 634 4827
10 2.05 11.60 6960 1269 5692
15 1.58 8.91 8022 1903 6119
20 1.31 7.39 8872 2537 6334
25 " 1.13 fi.39, 9592. 3472 ` 8420..; ,
30 1.00 5.68 10224 3806 6418
35 0.91 5.14 10791 4441 6350
40 0.83 4.71 11307 5075 6232
45 0.77 4.36 11783 5709 6074
50 0.72 4.08 12226 6344 5882
55 0.68 3.83 12641 6978 5662
60 0.64 3.62 13031 7612 5419
65 0.61 3.44 13402 8247 5155
70 0.58 3.27 13754 8881 4873
75 0.55 3.13 14090 9516 4574
SO 0.53 3.00 14412 10150 4262
85 0.51 2.89 14721 10784 3937
90 0.49 2.78 15018 11419 3600
95 0.47 2.69 15305 12053 3252
100 0.46 2.60 15583 12687 2895
105 0.44 2.52 15851 13322 2529
110 0.43 2.44 16111 13956 2155
Minimum Basin Area
Minimum Volume= 6420 cf
Minimum Area(18"basin dep� 4280 sf Actual Area(shaped to drein)= 8560 sf
Minimum Area for Sediment Control-->145 sf per 1 cfs
Peak Developed Fiow--> 6.39 cfs
Minimum Area= 927 sf
Baxter Meadows-Phase II
Detention Basin B
Design Stortn Frequency 10 yr
Basin Area(Ac) 9.00
Pre-Development Coefficient C Post-Development Coefficient C
Area(Ac) C Area(Ac) C
Open Space 9 0.20 Open Space 0.20
Med.Res. 0.35 Med.Res. 0.35
Dense Res. 0.50 Dense Res. 2.56 0.50
Comm.Neigh. 0.60 Comm.Neigh. 6.14 0.60
Comm.Down 0.80 Comm.Down 0.80
Industrial 0.80 Industrial 0.80
Total Area: 9 Composite C: 0.2 Total Area: 9 Composite C: 0.5682222
Pre-Development Post-Development
Runoff Distance 1000 ft Runoff Distance 7200 fl
Average Slope 1.10 % Average Stope 0.80 %
Time of Concentration 51 min Time of Concentration 40 min
Average Rainfall Intensity 0.71 in/hr Average Rainfall Intensity 0.83 in/hr
Maximum Runoff 1.28 cfs Maximum Runoff 4.26 cfs
Storm intensity Developed Developed Jndevelope Required
Duration 10 Yr Flow Runoff Runoff Storage
(min) (in/hr) (cfs) (c� (c� (c�
5 3.22 16.46 4938 384 4554
10 2.05 10.49 6293 768 5525
15 1.58 S.O6 7253 1152 6101
20 1.31 6.68 8021 1536 6485
25 1.13 5.78 8673 1921 6752
30 1.00 5.14 9244 2305 6940
35 0.91 4.65 9757 2689 7068
40 0.83 4.26 10224 3073 7151
45 0.77 3.95 10654 3457 71 g7
54 ;- 0 72 3.68 Y 1£154; � 38d1"":.` 7243"
55 0.65 3.46 11429 4225 7204
60 0.64 3.27 11783 4609 7173
65 0.61 3.11 12117 4993 7124
70 0.58 2.96 12436 5377 7058
75 0.55 2.83 12740 5762 6978
80 0.53 2.71 13031 6146 6885
85 0.51 2.61 13310 6530 6780
90 0.49 2.51 13579 6914 6665
95 0.47 2.43 13839 7298 6541
100 0.46 2.35 14089 7682 6407
105 0.44 2.27 14332 8066 6266
110 0.43 2.21 14567 8450 6117
115 0.42 2.14 14796 8834 5961
120 0.41 2.09 15018 9219 5799
125 0.40 2.03 15234 9603 5631
130 0.39 1.98 15444 9987 5458
135 0.38 1.93 15650 10371 5279
140 0.37 1.89 15850 10755 5095
145 0.36 1.84 16046 11139 4907
150 0.35 1.80 16238 11523 4714
Minimum Basin Area
Minimum Volume= 7213 cf
Minimum Area(18"basin depth 4809 sf Actual Area(shaped to drain)= 9617 sf
Minimum Area for Sediment Control->745 sf per 1 ds
Peak Developed Flow-> 3.68 cfs
Minimum Area= 534 sf
Baxter Meadows-Phase II
Detention Basin 7
Design Storm Frequency 10 yr
Basin Area(Ac) 12.45
Pre-Development Coefficient C Post-Development Coefficient C
Area(Ac) C Area(Ac) C
Open Space 12.45 0.20 Open Space 0.20
Med.Res. 0.35 Med.Res. 0.35
Dense Res. 0.50 Dense Res. 0.50
Comm.Neigh. 0.60 Comm.Neigh. 12.45 0.60
Comm.Down 0.80 Comm.Down 0.80
Industrial 0.80 Industrial 0.80
Total Area: 12.45 Composite C: 0.2 Total Area: 12.45 Composite C: 0.6
Pre•Development Post-Development
Runoff Distance 900 ft Runoff Distance 1300 ft
Average Slope 1.10 % Average Slope 0.77 %
Time of Concentration 49 min Time of Concentration 39 min
Average Rainfail Intensity 0.73 in/hr Average Rainfail Intensity 0.85 in/hr
Maximum Runoff 1.82 cfs Maximum Runoff 6.33 cfs
Storm Intensity Developed Developed Jndevelope Required
Duration 10 Yr Flow Runoff Runoff Storage
(min) (in/hr) (cfs) (c� (c� (c�
5 3.22 24.04 7213 545 6667
10 2.05 15.32 9193 1091 8102
15 1.58 11.77 10595 1636 8959
20 1.31 9.76 11717 2181 9535
25 1.13 8.45 12669 2727 9942
30 1.00 7.50 13503 3272 10231
35 0.91 6.79 14252 3817 10435
40 0.83 6.22 14934 4363 10571
45 0.77 5.76 15562 4908 10654
50 0.72 5.38 16147 5453 10693
55���� ��. 0.68 - 5.Q6� - �16695 �°�� 5999� �- 1Q698
60 0.64 4J8 17211 6544 10667
65 0.61 4.54 17700 7089 10610
70 0.58 4.32 18165 7635 10530
75 0.55 4.14 18609 8180 10429
SO 0.53 3.97 19034 8726 10309
85 0.51 3.81 19442 9271 10171
90 0.49 3.67 19835 9816 10019
95 0.47 3.55 20214 10362 9852
100 0.46 3.43 20580 10907 9673
105 0.44 3.32 20935 11452 9482
110 0.43 3.22 21278 11998 9281
115 0.42 3.13 21612 12543 9069
120 0.41 3.05 21936 13088 8848
125 0.40 2.97 22252 13634 8618
130 0.39 2.89 22560 14179 8381
135 0.38 2.82 22860 14724 8135
140 0.37 2.76 23152 15270 7883
145 0.36 2.69 23438 15815 7623
150 0.35 2.64 23718 16360 7358
Minimum Basin Area
Minimum Volume= 10696 cf
Minimum Area(18"basin depth) 7131 sf Actual Area(shaped to drain)= 14261 sf
Minimum Area for Sediment Control->145 sf per 1 cfs
Peak Developed Flow-> 5.06 cfs
Minimum Area= 734 sf
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28
Baxter Meadows Phase II -Storm Drain Inlet Calcs -Basin 1
Inlet Overland Overland Overland Gutter Gutter Gutter Overland Gutter Total Rainfall 25 Year
Inlet Area Coe�cient Flow Distance Flow Slope Flow Distance Flow Slope Flow Velocity Flow tc Flow tc tc Intensity Flow
(acres) C (ft) (%) (ft) (%) (Ws)Fi .7-1 ) (min)* (in/hr
9 (min)Fig.I-1 (min ) (cfs)
1 0.11 0.50 0 2.00 230 0.60 1.57 0.0 2.4 10.0 2.46 0.14
2 1.70 0.50 360 2.00 200 0.60 1.57 23.0 2.1 25.1 1.36 1.16
3 0.82 0.50 140 2.00 270 0.60 1.57 13.0 2.9 15.9 1.83 0.75
4 0.27 0.50 0 2.00 340 0.60 1.57 0.0 3.6 10.0 2.46 0.33
Total 2.gp
'Minumum tc=10 min
Baxter Meadows Phase II-Stortn Drein Pipe Calculations-Basin 1
Pipe/Gutter Segment Inlet Area Inlet Cumulative Pipe Pipe pipe Flow Pipe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
C (Acre) (Acre) (ft) (cfs) (i�) (i�) (ft/s) (min)
(min) (1Nhr) Point(cfs)
Baxter Parkway Gutter Inlets 1&2 0.50 �,g� p g�
Inlets 1&2 Manhole 1 0.50 z5•1 25.1 1.36 �,23
�.91 60 1.23 15 5.1 3.37 0.3 25.4 1.35 �.22
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Inlets 3&4 Manhole 1 0.50 15.9 15.g �,g2 p gg
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Totals At Manhole 1 2.90 1.45
Discharge Into Basin 25.4 1.35 1.96
1.96 15 6.5 3.83
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Baxter Meadows Phase II -Storm Drain Inlet Calcs-Basin 2
Inlet Overland Overland Overland Gutter Gutter Gutter Overland Gutter Total Rainfall 25 Year
Inlet Area Coefficient Flow Distance Flow Slope Flow Distance Flow Slope Flow Velocity Flow tc Fiow tc tc Intensity Flow
(acres) C (ft) (°/a) (ft)
(%) (ff/s)Fig.7-1 (min)Fig.I-1 (min) (min)• (in/hr) (cfs)
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2 1.71 0.50 340 2.00 235 0.60 1.57 17.0 2.5 19.5 1.60 1.37
3 0.16 0.50 20 2.00 130 1.75 2.68 2.0
4 0.12 0.50 30 2.00 130 1.75 2.68 3.0 0.8 10.0 2.46 0.15
Total 2.17
'Minumum tc=10 min
Baxter Meadows Phase II-Storm Drein Pipe Calculations-Basin 2
Pipe/Gutter Segment Inlet Area Inlet Cumulative Pipe Pipe Pipe Flow Pipe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Veloci tc
� (A��e) 1Acre � tc Intensity At Downstream
� �ft) (��) ('") ('�) (�S) (min) (min) (in/hr) Point(cfs)
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Inlets 1&2 Manhole 1 0.50 19.5 19.5 1.60 1.5�
Trakker Way Gutter Inlets 3&4 0.50 0�95 6� ��51 15 5.7 3.57 0.3
0.28 1.09 19.8 1.59 1.50
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3.39 0.3 19.8 1.59 1.72
Totals At Manhole 1 2��
Discharge Into Basin 1.09
1.72 15 6.1 3.70 18.8 1.59 1.72
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Baxter Meadows Phase II -Storm Drain Inlet Calcs -Basin 3, Including Trakker Site
Inlet Overland Overland Overland Gutter Gutter Gutter Overland Gutter Total Rainfall 25 Year
Inlet Area Coefficient Flow Distance Flow Slope Flow Distance Flow Slope Flow Velocity Flow tc Flow tc tc Intensity Flow
(acres) C (ft) (%) �ft� �a�o�
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3 0.22 0.60 20 2.00 150 0.50 1.43 3.0 1.7 10.0 2.46 0.32
4 0.15 0.60 20 2.00 150 0.50 1.43
5 0.47 0.60 20 2.00 3.0 1.7 10.0 2.46 0.22
6 �•79 0.60 340 0.60 1.57 3.0 3.6 10.0 2.46 0.69
200 2.00 340 0.60 1.57 13.0 3.6 16.6 1.77 1,g1
7 0.76 0.60 20 2.00 360
8 0.98 0.60 0.50 1.43 3.0 4.2 10.0 2.46 1.12
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9 0.26 0.60 10 2.00 230 0.60 1.57 2.0 2.4 10.0 2.46 0.38
10 1.95 0.60 310 2.00 230 0.60 1.57 14.0 2.4 16.4 1.79 2.09
�� 1•15 0.60 130 2.00 190 0.60 1.57 8.0 2.0 10.0 2.45 1.69
12 0.75 0.60 130 2.00 120
13 0.23 0.60 0.60 1.57 8.0 1.3 10.0 2.46 1.10
10 2.00 250 0.60 1.57 2.0 2.7 10.0 2.46 0.34
14 0.29 0.60 20 2.00 250 0.60 1.57 3.0 2.7 10.0 2.46 0.43
15 0.58 0.50 20 2.00 410 0.50 1.43
16 0.96 0.50 60 2.00 410 0.50 1.43 7.0 4.8 11�.8 2.21 1�.06
Total 12.15
'Minumum tc=10 min
Baxter Meadows Phase II-Storm Drein Pipe Calculatio�s-Basin 3
Pipe/Gutter Segment Inlet Area Inlet Gumulative Pipe Pipe Pipe Flow Pipe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
C (Acre) (Acre) (ft) (cfs) (in) (in) (fUs) (min) (min) (in/hr) Point(cfs)
Caspian Brench
Caspian Gutter iniets 1&2 0:6(y 1,s1 ' 4.gj ,
Infefs 1&2 [Nanhole 1 0'5� ;0.81 5Q �� ;�:50 - �'15 ' 6:S_ �- � �. 15.4 154�, � 1:86 1.50
Trakker Gutter intets 3&4 ' 4.60 3.5& �2 � 95 8 �_ 1'.84 :
0.37" �`1.03 - �� � " � 1.48 �
Intets 3 8�4 Manhole 1 0.6Q " 1Q.a 2:46 0.55
� Manhole 1 � inlets 5&6 '� �0:&0 � i.03 80 �' 4.58 �` �15 3.4 � 2.88� ; 0.4� ��,� V.6 ���� �1�.71 � 1J6�
inlet9 5&6 Manhole 2 '_.' _ 0.60 2.25` 2.38 29a ; 1:78 15 8.1. 3.T2.: . . t,3" 18.8 ' 7.63.
2.38 70 '., ,3.�9 '1$ 9.9 4.51 0:3 3.89
Manhole 2 ', inlets T&8: 19.2 . i:62 3.88
" Inlets 7 8�8 ��� �80 1.74�� �-�3.43 400' `� 3.88 �15 � '9.9 4.50 1`5 ��20.6 ' 1:54 �
,_
� Manho►e 3 ��� D;BQ �� '3.43 45.;: 5;29�" ��16 � �� 11.2 � 4.56 i ,.:,0.2 �' ��:� 20 8 .,.'. 1�.54 �' �5.27�
Charolais Gutter Inlets 9&10 0.60 2.21 475
Inlets 9&10 Manhole 3 0.60 16.4 16.4 1 jg Z.g7
4 75 70 2.37 15 7 3 4 02 0.3 20.5 1.55 7.37
Menhole 3 InletS 15&1 B . 0!50 ' 1.54 5 52 �FOA T 37 21
Iniets 15&18 " � 4$4 4 97� 1-S 21.8 -` 1.48 8.23
Manhole 4" Q:SQ '
�X1..'
Alley Brench w- � .. 6&2 _.._.. ' ;�23 , •w�y � . `;. rt34 .� ����T9���� ;;ik:'f � ;;?'21.8' '" 1:48 � 8:2U�
Alley�c�tter . 1Net 11 ,_-. 0.60 � 1 15''.. 0.89
� ;- Inlet 11`� � .°�Inlet 12 . - 4.60 ��� 0 75�� '� � .
; ��:inlett2 �� 114 � 125 � � 1.89 - � ��5 6.0 � �,3.88�
10.0 1Q 0 2.46 1.89
�IMet 13&14;°' tl;60 � � = 0i6 10.6 2'37 �
`1.14 ° '° 170 2.74 � ��16 �:. � �� 7:B�, �� � 0;4 .; ...1t.6 �`,,= 2:�31�� . 2.63
Baxter Pkwy Gutter Inlets 13&14 0.60 \ "���� °
Itll@tS":13&74 MBRhole 4 `. , 0;80, 0.52 1.45 10.0 11.0 2.31 3.35
� � .�_:8.98�� 80 3:35 ,,, 15 �"�,.. ; .90�.: " 43T�`; _�.. -�11:3 - ��� 2t.$. '_`� � �1.�9 _ f6:37
Totals At Manhole 4 12.75 6.98
Discharge Into Basin 21.9 1.49 10.37
10.37 21 14.8 5.72
Baxter Meadows Phase II-Storm Drain Pipe Calculations-Basin 3
Pipe/Gutter Segment Inlet Area Inlet Cumulative Pipe Pipe Pipe Flow Pipe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
C (Acre) (Acre) (ft) (cfs) (in) (in) (ffls) (min) (min) (in/hr) Point(cfs)
Caspian Branch
CaspianGutter inleYst&2 G.�(i 1.61 , tt.8i ` 15.4 i5.4 4.88 1<50
�fnieGs 1&2 . Manhole-�- 0.50 � � ��� � D.81 7< 50 � i.50 � �S� � �� 5.6 < �3.�6..� �A.2. 15.8��� ��1.84.� 1:48
Trak[cer Gutter: �Iniets 3&4 �� 0.6� � 0.37 1.Q3 � � �� � �� �� � � 3Q.0. �� � 2 46 . � p.55
K .lniets 3&4� Ma�hote T �0.60 > = � 9.03 °66� �� � q,65 �- t2`�, �.& ' � �2:74�� � �0.4 17.6�' �� �i.71 � �q.76
Maohflfe 1 - lnlets 5&8 �.Bfl =2.26 r 2.38 29t1 . 1:76 15 B.�E ' 3.�2 4 3 " ; '•�8.8= 1,83 ; , -3,89 �.., .'
Inlets 5&s � � Manhole 2��� ��0.60 � � " °
2.38 -- 7Q 3.85 1b 9,8 - d.59 ' 0.3 19.2 ' i.82 3.86 .
Manhote 2 Inists 7&8 p.60 1<74 ,. ' 3.43 4pU 3:86 15 8.9 ' 4.�Q :1.5 20.& ' 2.54 5.28
��_ r.r. `iniefs 7&.8 ���Man6o(e 3� o.60 � :. �� °: ;: s ._,: 3.43 ex� 4� ��,2v �-., 18_,. . 11.2_�' . � A:58 :U 2„ '� 2CM.&;;,;�� , �1 54 � -. 5,27
Charolais Gutter Inlets 9&10 � 0.60 221 4]5 16.4 16.4 1.79 2.37
Inlets 9&10 Manhole 3 0 60 4 75 70 2.37 15 7.3 4.02 0 3 20 5 1 55 7.37
Manhoie 3 in(ets 15&16 0 50 � �.�•>.,._,�,„y, �, �
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Alley Branch ��
; AligY Gutfgr tniet 91 U st? 1.15 Cr.Bs
9�0 1Q.Q 248 1.89
' � l�tlet 1'i ; tniet 12"" �6� {3.75 1.94 125 1.a9 7S 8.0 ' 9.6� Q 6 10.8 2 37 2.70
, � � �
��� Ba�e�t.�.�.,r� . .,b.�nI4t.13&1� - _ tl$�.���:: .�z �. ,' � � i.9� .�� �.. �ji6 �70. �r 15,.. ,�.; 7.8 �� 4.15, �q4 �7t0" �239 �2,83 ,
Pkwy Gutter Inlets 13&14 0 60 0 52 1 45 90 0 11.0 �2 31 3.35
;�s�r�il��3;$��}+F:� ..,.._.,,���..4„ , a60. ,;. �aa ,
._. .. ._.. . .._.�,� �«w.�.....a"�.wrmf, �.�,.�.��:'..� F..w.i;.;�s��.s' �"'k1..�..-'-�^�'`.'i`�.Q A'� ^,� L'Z3.a"A�"s`�'� �-�..x1� .n::> ti� tfi�'x .
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Totals At Manhole 4 12.15 6.98 21.9 1.49 10.37
Discharge Into Basin 10.37 21 14.6 5.72
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Baxter Meadows Phase II -Storm Drain Inlet Calcs -Basin 4
Inlet Overland Overland Overland Gutter Gutter Gutter Overland Gutter Total Rainfall 25 Year
Inlet Area Coeffcient Flow Distance Flow Slope Flow Distance Flow Slope Flow Velocity Flow tc Flow tc tc Intensity Flow
(acres) C (ft) (%) (ft)
(%) (ft/s)Fig.7-1 (min)Fig. I-1 (min) (min)* (in/hr) (cfs)
� �•�$ 0.35 20 2.00 260 0.60 1.57 4.0 2.8 10.0 2.46 0.15
2 0.27 0.35 35 2.00 260 0.60 1.57 4.0 2.8 10.0 2.46 0.23
3 0.61 0.35 60 2.00 380 0.88 1.90 6.0 3.3 10.0 2.46 0.52
4 1.79 0.50 210 2.00 380 0.88 1.90 16.0 3.3 19.3 1.61 1.44
5 0.12 0.50 25 2.00 190 0.60 1.57 4.0 2.0 10.0 2.46 0.15
6 0.21 0.50 40 2.00 190 0.60 1.57 5.0 2.0 10.0 2.46 0.26
Total 3.18
'Minumum tc=10 min
Baxter Meadows Phase II-Storm Drain Pipe Calculations-Basin 4
Pipe/Gutter Segment Inlet Area Inlet Cumulative Plpe Pipe Pipe Flow Pipe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C z Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
C (Acre) (Acre) (ft) (cfs) (in) (in) (ft/s) (min) (min) (in/hr) Point(cfs)
Rawhide Gutter Inlets 1&2 Q.35 O.AS., 0.16
iniets 1&2 Manhole 1 0.35 , p £ ' F't 1p:d ,10.0� 2.A6 0.39:
Gallatin Green Gutter Inlets 3&4 ���'18 ' �� �`�� 0:���� "�'�' ,�` :'��, x.r� .2.A�..�� �0;$ ��-19.5 1.60�� 02S
0 46 0:33� � 1.26 � � `�
Inlets 3&4 2.40
Manhole 1 0.50 19.3 �g,3 �.g� � 78
Manhple 1 �:. � -�IltleFs 5&8��.; � 1.26 40 1.78 15 6.2 3.73 0.2 19.5 1.60
0.60 "' 2.02
` 1:q3 ,.150, ; : 2.Q2'., . 'l5 `6,�'.;,,. .
�.86 :�J �" ,Q1S, �20.1 1.5fi 2.24..._
Totals Atlnlets 5&8 3.18 1.43
Discharge Into Basin 20-1 �.57 2.24
2.24 15 7.0 3.96
Baxter Meadows Phase II-Storm Drain Pipe Calculations-Basin 4
Pipe/Gutter Segment Inlet Area Inlet Cumulative Pipe Pipe Pipe Flow Pipe Segment CumulaUve Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
c (Acre) (,4cre) (ft) (cfs) (In) (in) (tUs) (min) (min
) (in/hr) Point(cfs)
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Gallatin Green Gutter Inlets 3&4 0.46 2.40 1.26 19.3 ^ 19.3 1.61 1.78
Inlets 3 8 4 Manhole 1 0 50 1.26 40 1.78 15 6.2 3.73 0.2 19.5 1.60 2.02
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Totals Atlnlets 5 8 6 3.18 1.43 20.1 1.57 2.24
Discharge Into Basin 2.24 15 7.0 3.96
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Baxter Meadows Phase II-Storm Drain Iniet Calcs-Basin 5
Inlet Overland Overland Overland Gutter Gutter Gutter Overland Gutter Total Rainfall 25 Year
Inlet Area Coefficient Flow Distance Flow Slope Flow Distance Fiow Slope Flow Velocity Flow tc Flow tc tc Intensity Flow
(acres) C (ft) (%) (ft)
(%) (ft/s)Fig.7-1 (min)Fig.I-1 (min) (min)* (in/hr) (cfs)
� 1.05 0.35 110 2.00 380 0.70 1.70 11.0 3.7 14.7 1.92 0.70
2 1.05 0.35 110 2.00 380 0.70 1.70 11.0 3.7 14.7 1.92 0.70
3 1.22 0.35 130 2.00 380 0.80 1.81 12.0 3.5 15.5 1.86 0.79
4 1.40 0.35 150 2.00 380 0.80 1.81 13.0 3.5 16.5 1.78 p.g7
5 1.26 0.35 130 2.00 380 0.60 1.57 12.0 4.0 16.0 1.81 0.80
6 2•2� 0.35 205 2.00 380 0.60 1.57 16.0 4.0 20.0 1.57 1.25
7 0.32 0.35 40 2.00 280 0.50 1.43 4.0 3.3 10.0 2.46 0,27
8 0.13 0.35 5 2.00 280 0.50 1.43 2.0 3.3 10.0 2.46 0.11
9 0.34 0.35 40 2.00 250 0.80 1.81 4.0 2.3 10.0 2.46 0.29
10 0.11 0.35 5 2.00 250 0.80 1.81 2.0 2.3 10.0 2.46 0.09
11 0.93 0.35 110 2.00 340 0.80 1.81 11.0 3.1 14.1 1.97 0.64
12 0.93 0.35 110 2.00 270 0.80 1.81 11.0 2.5 13.5 2.03 0.66
13 0.64 0.35 110 2.00 230 0.50 1.43 11.0 2.7 13.7 2.01 0.45
14 0.63 0.35 110 2.00 230 0.50 1.43 11.0 2.7 13.7 2.01 0.44
15 1.66 0.35 120 2.00 500 0.80 1.81 12.0 4.6 16.6 1.78 1.03
16 1-84 0.35 140 2.00 500 0.80 1.81 13.0 4.6 17.6 1,7'I 1.1 p
17 0.27 0.35 40 2.00 230 0.57 1.53 4.0 2.5 10.0 2.46 0.23
18 0.11 0.35 10 2.00 230 0.57 1.53 2.0 2.5 10.0 2.46 0.09
Total 16.16
*Minumum tc=10 min
Baxter Meadows Phase II-Storm Drein Pipe Calculations-Basin 5
Pipe/Gutter Segment Inlet Area Inlet Cumulative Pipe Pipe Pipe Flow Pipe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
C (Aere) (Acre) (ft) (cfs) (in) (in) (ff/s) (min) (min) (in/hr) Point(cfs)
Milkhouse Branch
Milkhouse Gutter inlets 5&6 0.35 3.53 1,24
� 20.0 2D,0 1.58 1.95
intefs 5&6 InleEs 8&10 Q.3S 0.45 � 1.39 31Q � ; 1,95 -� �1 S-� �6.0 �� �� 4 28 � ��1.2 ��21.2 �� � 1.52� � 2.11
S.Fele�o&Gutter In ets 3&4 �� 0.3� � � � � �
nhole 2 0.3fi , 1.3,� �45•�� `� 2.71.- 15� � 6.3 - 4.34 '� - � 03 �-_21.4 1.5'! 2:?0
9 5 2.62 2.31 16.5 21.4 1.78 1.63
Inlets 3&4 Manhole 2 0.35 2.31 50 1 63 15 5.5 4.05 0.2 21.4 1.51 3.49
Manhole 2 Inlets 7&8 0.35 O.A5 2.47 Z9Q 3.48 18'� "°`8.7 4.74 0:9 ' 22.3 t:47 3;67 '
INets7&8 Manhole 3 0.35 .'` ` 2:47 ., 4a . 3.62 18 8.9 4,18 d:2 22.b 1.49 3.61
Lasso Gutter Inlets 1&2 0.35 2.10 3.20
14.7 22.5 1.92 1.41
Inlets 1 &2 Manhole 3 0.35 3.20 50 1.41 15 5.2 3.70 0.2 22.5 1.46 4.68
Manhole 3 Inlets 11&12 0.35 1.86 3.85 280 4.68 18 10.3 4,44 ' 1.1 23.6 1:42 5.47
Iniets 11&12 Inlets 13&14 0.35 1.27 4.30 230: b.47 21 10.4 4.63 D.8 24.4 1.39 5.97
Iniets�l3&14' Ma�hole5 �� ��:U,3�5. �4.30' � ��SO � � 5.8,7"��. °� 21�� 10,9 � 4.73 � �- ��tl.2 ;�24.8- ��� 1:38� 5.84
Ferguson Brench
N.Ferguson Gutter Inlets 15&16 , 0.35 3.&0 1,23
� � � ..l7;6 `17.8,, � � 1.21 �2.09
Infets 15&16 � inlets 17&18 D.�B - 0.38 �1.38���� �290 �I 2.09 ��� �15 _ ��71 ; �� 3.64 ��� �1.3�, - 18,8 1:83 � 2.2?��
Inlets 17&18 Manhole 5 0-35 1.86 4U 2.22 : 1S 6.7. . 3.78 '' 0.2 ' 19.1 � 1:82 2.20"; :
Totals At Manhole 5 16.16 5.68
24.8 1.38 7.81
Discharge Into Basin 7.81 21 12.9 5.04
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Baxter Meadows Phase II-Storm Drain Inlet Calcs-Basin 6
Inlet Overland Overland Overland Gutter Gutter
Inlet Area Coefficient Flow Distance Flow Slope Flow Distance Flow Slope Flow Veeocity OFlow tc Flowtc Ttcal Intensaty 2 Flow r
(acres) C lft) (%) �ft) �%)
(ft/s)Fig.7-1 (min)Fig.I-1 (min) (min)' (in/hr) (cfs)
1 0.51 0.50 100 2.00 270 0.80 1.81 8.0 2.5 10.5 2.38 0.61
2 1.16 0.60 180 2.00 270 0.80 1.81 13.0 2.5 15.5 1.86 1.29
3 3.64 0.60 400 2.00 300 0.50 1.43 16.0 3.5 19.5 1.60 3.50
4 0.74 0.60 170 2.00 300 0.50 1.43 11.0 3.5 14.5 1.94 0.86
5 1.62 0.50 300 2.00 150 1.35 2.35 17.0 1.1 18.1 1.68 1.36
6 0.45 0.50 50 2.00 310 1.35 2.35 8.0 2.2 10.2 2.43 0.55
7 0.28 0.50 20 2.00 290 0.90 1.92 2.0 2.5 10.0 2.46 0.34
8 0.60 0.60 110 2.00 290 0.90 1.92 10.0 2.5 12.5 2.13 0.77
Total 9.00
'Minumum tc=10 min
Baxter Meadows Phase II-Storm Drain Pipe Calculations-Basin 6
Pipe/Gutter Segment Inlet Area Inlet Cumulative Pipe Pipe Pipe Flow Plpe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
C (Acre) (Acre) (ft) (cfs) (in) (in) (ft/a) (min) (min) (in/hr) Point(cfs)
Rawhide Gutter Inlets 3&4 0.60 4.38 2.63
Inlets 3&4 Manhole 1 0.60 19.5 19.5 1.60 4.21
2.63 35 4.21 15 11.4 4.22 0.1 19.6 1.59 4.19
Charolais Gutter Inlets 1&2 0.57 1.67 3.58
Inlets 1&2 Manhole 1 0.50 15.5 15.5 1.85 1.77
3.58 60 1.77 15 5.7 4.14 0.2 19.6 1.60 5.71
Manhole 1 Inlets 5&6 0.50 2.07 4.61 290 5.71 15 9.8 6.73 0.7 20.3 1.56 �,Zp
Inlets 5&6 Manhole 2 0.50 4.61 45 7.20 18 9.9 7.19 0.1 20.4 1.55 7.�7
Baxter Pkwy Gutter Inlets 7&8 0.50 0.88 5.05
Inlets 7&8 Manhole 2 0.50 10.0 10.0 2.46 �,pg
5.05 70 1.08 15 4.3 3.76 0.3 20.4 1.56 7,gg
Totals At Manhole 2 9.00 5.05
Discharge Into Basin 20.4 �.56 7.86
7.86 18 12.1 6.25
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Baxter Meadows Phase II -Storm Drain Inlet Calcs -Basin 7
Inlet Overland Overland Overland Gutter Gutter Gutter Overland Gutter Total Rainfall 25 Year
Inlet Area Coefficient Flow Distance Flow Slope Flow Distance Flow Slope Flow Velocity Flow tc Flow tc tc Intensity Flow
(acres) C (ft) (%) (ft)
(%) (ft/s)Fig.7-1 (min)Fig. I-1 (min) (min)' (in/hr) (cfs)
� 0.42 0.60 30 2.00 250
2 0.50 0.60 0.55 1.50 2.0 2.8 10.0 2.46 0.62
45 2.00 250 0.55 1.50 3.0 2.8 10.0 2.46 0.74
3 0.42 0.60 25 2.00 250
4 0.51 0.60 0.55 1.50 2.0 2.8 10.0 2.46 0.62
45 2.00 250 0.55 1.50 3.0 2.8 10.0 2.46 0.75
5 0.96 0.60 290 2.00 200
6 2.48 0.60 0.66 1.65 14.0 2.0 16.0 1.82 1.05
25 2•�� 2�� 0.66 1.65 2.0 2.0 10.0 2.46 3.65
7 2.47 0.60 570 2.00 240 0.66 1.65 20.0 2.4 10.0 2.46 3.64
$ 0.33 0.60 20 2.00 240 0.66 1.65 2.0 2.4 10.0 2.46 0.49
9 0.61 0.60 25 2.00 500
�� 3.75 0.60 �•9� 1•92 2.0 4.3 10.0 2.46 0.90
580 2.00 500 0.90 1.92 20.0 4.3 24.3 1.39 3.13
• Total 12.45
*Minumum tc=10 min
Baxter Meadows Phase II-Storm Draln Pipe Calculations-Basin 7
Pipe/Gutter Segment Inlet Area Inlet Cumulative Pipe Pipe Pipe Flow Plpe Segment Cumulative Rainfall 25 Year Flow
From To Coefficient, Area C x Area Length Flow Diameter Depth Velocity tc tc Intensity At Downstream
� (Acre
) (Acre) (ft) (cfs) (in) (in) (it/s) (min) (min) (in/hr) Point(cfs)
Caspian Gutter Inlets 1 &2 0.60 0.92 0.55
Inlets 1 &2 Inlets 3&4 0.60 p,93 � �� 1�.0 10.0 2.46 1.36
Inlets 3&4 Manhole 1 0.60 260 1'36 �5 6 3.36 1.3 11.3 z.27
1.11 290 2.52 15 7.7 3.95 1.2 12.5 2.13 2.52
Manhole 1 Inlets 5&6 0.60 3.44 3.17 2.36
Inlets 5&6 Inlets 7&8 0.60 60 2•36 15 7.4 3.89 0.3 12.g 2.1p
2.80 4.85 290 6.66 18 6.7 4.95 1.0 13.7 2.00 6.66
Inlets 7&8 Manhole 3 0.60 9 72
Baxter Pkwy Gutter Inlets 9&10 0.60 4�85 50 9•72 21 14.6 5.46 0.2 13.9 1.99 9.65
Iniets 9&10 Manhole 3 0.60 4.36 7.47 24.3 24.3 1.39 3.64
7.47 60 3.64 15 7.6 5.03 0.2 24.3 1.39 10.39
Totais At Manhote 3 12.45 7,47
Discharge Into Basin 24•3 7.39 10.39
10.39 21 12.8 6.73
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ALLIED
ENGINEERING
SERVICES, INC.
32 Discover}� Drive . Bozeman, Montana �9718 . Phone: . Fax:
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BAXTER MEADOVVS SUBDIVISION
STOKI��VVATER MASTER PLAN AND
PHASE I STORMWATER FACILITIES DESIGN REPORT
ADDENDUM #1
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Prepared By
Paul J. Sanford,P.E.
Allied Engineering Services, Inc.
Prepared For
Baxter Meadows Development, LP
July 30, 2002
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BAXTER MEADOWS SUBDIVISION
STORMVVATER MASTER PLAN A1VD PHASE I DESIGN REPORT—ADDENDUM #]
� TABLE OF CONTENTS
APPET'DIX DESCRIPTION
A.l Phase 1—Flood Hazard Evaluation and Design Report
Spring Ditch
Output
Input
Baxter-Border Ditch
; Output
Input
B.1 Comparison of 36-inch Arch Pipe to Round Pipe
� Culvert Master: Culvert #1 —Arch Pipe
� Culvert Master: Culvert#1 —Round Pipe
Culvert Master: Culvert#2 —Arch Pipe
' Culvert Master: Culvert#2—Round Pipe
Culvert Master: Culvert#3—Arch Pipe
Culvert Master: Culvert#3 —Round Pipe
� HEC-R.AS: Round Pipe vs. Arch Pipe
D.l Revised Storm Drainage Facilities Maintenance Plan
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June 30,2002 TC-] Project O]-24]
BAXTER MEADOWS SUBD7VISION STORMWATER—ADDENDUM #]
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APPENDIX D.1
�� Revised - Storm Draina e Facilities Maintenance Plan
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. STORM SE�'ER FACILITIES
� MAINTENANCE FLAN
BAXTER ME�iDOV�'S SUBDI�ISION
The storm drainage control facilities for Baxter Meadows Subdivision consists of storm sewer
co]]ection systems which direct storm runoff to on-site detention or retention ponds. The storm
water drainage design limits storm water runoff from the developed site to the pre-development
runoff rates. The storm water drainage design will utilize vegetated swales upstream and
downstream of the detention ponds, whenever possible to remove solids, silt, oils, and other
pollutants prior to discharge to the receiving water body. Storm water runoff from the project
� flows into the Baxter Border Ditch or the Spring Ditch, eventually reaching the East Gallatin
River. Both of these watercourses are considered Stream/Ditches (flow is sowced by both
imgation & natura] drainage). Impacts to water quality are minimized by designing the
detention ponds to settle out at a minimum particles 40 microns (1/635th5 of an inch) and larger.
, Furthermore, detention pond outlet structures are designed to trap oils.
k The City of Bozeman wil] be responsible for maintaining storm sewer facilities located within
$ the publicly maintained public right-of-way. Operation and maintenance responsibilities of the
City should include the following (Thomas, Dean &Hoskins, 1982):
� • Cleaning inlets, manholes, and storm sewer pipes.
• Street sweeping and cleaning to remove debris to reduce the sediment loading to
detention ponds and thereby reduce the amount of particulate discharged to
receiving streams.
• City administration as needed to assure the proper operation of the storm drain
utility.
The I3ome-Owners or Property Owners Association shall be responsible for maintenance of the
detention ponds and other storm drainage facilities not located in the publicly maintained public
right-of-way which includes all facilities located.in the privately maintained streets. Operation
and maintenance responsibilities shall include the following:
• Cleaning, mowing, and maintenance of outfal] ditches/swales.
• Cleaning, mowing, and maintenance of detention ponds.
• Cleaning and maintenance of outlet structures and outlet pipes
To retain the capacity of the detention ponds, the Home-Owners or Property Owners Association
shall remove any fill or other materials placed in the ponds and any accumulated sediment. The
Home-Owners or Property Owners Association should at a minimum, perform bi-annual
inspections of the detention ponds, outfall ditches/swales, and outlet structures and pipes and
maintain them as needed.
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APPENDIX C
PROPOSED POST-DEVELOPMENT CONDITION
Contributing Area C Area(Ac) C'Area
Lawns:sandy soil, 022 0.06 0.01
average,2-7%
Drives,walks,and roofs 0.95 0.13 0.13
Total 0.19 0.14
Runoff Coefficient C 0.73
Area A 0.193 Ac
Time of Concentration T c 1440 min
2-year 5-year 10-year 25-year 50-year 100-year
Storm Duration Intensity Flow Rate Runoff Volume Intensity Flow Rate Runoff Volume Intensity Flow Rate Runoff Volume Intensity Flow Rate Runoff Volume Intensity Flow Rate Runoff Volume Intensity Flow Rate Runoff Volume
(hrs) (min) I (in/hr) Q;�(cfs) (ft') I (in/hr) Q;,,(cfs) (ft') I (in/hr) Q;,,(cfs) (ft') I (in/hr) Q;�(cfs) (ft') I (in/hr) Q;,,(cfs) (ft') I (in/hr) Q;�(cfs) (ft')
0.08 5.00 2.08 0.293 87.9 3.16 0.445 133.6 3.87 0.545 164 4.76 0.738 221.3 5.43 0.765 229.5 6.09 1.073 322
0.17 10.00 1.53 0.216 129.4 2.31 0.325 195.3 2.83 0.399 239 3.48 0.539 323.6 3.97 0.559 335.6 4.45 0.784 470
0.25 15.00 1.24 0.175 157.3 1.87 0.263 237.1 2.29 0.323 290 2.83 0.439 394.8 3.22 0.454 408.3 3.61 0.636 572
0.33 20.00 0.99 0.139 167.4 1.50 0.211 253.6 1.84 0.259 311 2.26 0.350 420.3 2.58 0.364 436.2 2.89 0.509 611
0.42 25.00 0.84 0.118 177.5 1.28 0.180 270.5 1.56 0.220 330 1.93 0.299 448.7 2.20 0.310 465.0 2.46 0.433 650
0.50 30.00 0.75 0.106 190.2 1.13 0.159 286.6 1.38 0.194 350 1.70 0.263 474.3 1.94 0.273 492.0 2.18 0.384 691
0.58 35.00 0.66 0.093 195.3 0.99 0.139 292.9 1.22 0.172 361 1.50 0.232 488.2 1.71 0.241 506.0 1.92 0.338 710
0.67 40.00 0.59 0.083 199.5 p,gg 0.125 301.0 �,pg 0.154 369 1.35 0.209 502.2 1.53 0.216 517.4 �,72 0.303 727
0.75 45.00 0.54 0.076 205.4 0.81 0.114 308.2 1.00 0.141 380 1.23 0.191 514.7 1.40 0.197 532.6 1.57 0.277 747
0.83 50.00 0.49 0.069 207.1 0.74 0.104 312.8 0.91 0.128 385 1.12 0.174 520.8 1.28 0.180 541.1 1.44 0.254 761
0.92 55.00 0.45 0.063 209.2 0.69 0.097 320.8 0.84 0.118 391 1.04 0.161 531.9 1.18 0.166 548.7 1.33 0.234 773
1.00 60.00 0.42 0.059 213.0 0.64 0.090 324.6 p,7g 0.111 401 p,g7 0.150 541.2 1.10 0.155 558.0 �,24 0.218 786
2.00 120.00 0.24 0.034 243.5 0.34 0.048 344.9 0.41 0.058 416 0.49 0.076 546.8 0.55 0.077 558.0 0.61 0.107 774
2.50 150.00 0.19 0.027 240.9 0.25 0.035 317.0 0.29 0.041 368 0.34 0.053 474.3 0.37 0.052 469.2 0.41 0.072 650
6.00 360.00 0.12 0.017 365.2 0.15 0.021 456.5 0.17 0.024 517 0.19 0.029 636.1 0.21 0.030 639.1 0.22 0.039 837
12.00 720.00 0.08 0.011 487.0 0.09 0.013 547.8 0.10 0.014 609 0.12 0.019 803.5 0.13 0.018 791.3 0.14 0.025 1065
24.00 1440.00 0.05 0.007 596.5 0.06 0.009 754.8 0.07 0.010 864 0.08 0.013 1098.1 0.09 0.015 1314.8 0.10 0.017 1491
Table 6.6.3-Frequency Correction Factors
Recurrence Interval Adjustment Factor
(years) Cf
2 through 10-year 1
25-year 1.1
50-year 1.2
100-year 1.25
Pond Report
Hydraflow Hydrographs Extension for Autodesk0 Civil 3D0 by Autodesk, Inc.v2023 Tuesday,07/1 /2025
Pond No. 3 - Retention Syst
Pond Data
UG Chambers-Invert elev. =100.00 ft, Rise x Span=3.00 x 3.00 ft, Barrel Len= 191.50 ft, No. Barrels= 1, Slope=0.00%, Headers=No
Encasement-Invert elev.= 100.00 ft, Width=3.33 ft, Height=3.00 ft, Voids=27.00%
Stage/Storage Table
Stage(ft) Elevation(ft) Contour area(sqft) Incr.Storage(cuft) Total storage(cuft)
0.00 100.00 n/a 0 0
0.30 100.30 n/a 103 103
0.60 100.60 n/a 141 244
0.90 100.90 n/a 160 404
1.20 101.20 n/a 171 576
1.50 101.50 n/a 177 753
1.80 101.80 n/a 177 929
2.10 102.10 n/a 171 1,101
2.40 102.40 n/a 160 1,261
2.70 102.70 n/a 141 1,402
3.00 103.00 n/a 103 1,505
Culvert/Orifice Structures Weir Structures
[A] [B] [C] [PrfRsr] [A] [B] [C] [D]
Rise(in) = 0.00 0.00 0.00 0.00 Crest Len(ft) = 0.00 0.00 0.00 0.00
Span(in) = 0.00 0.00 0.00 0.00 Crest EI.(ft) = 0.00 0.00 0.00 0.00
No.Barrels = 0 0 0 0 Weir Coeff. = 3.33 3.33 3.33 3.33
Invert EI.(ft) = 0.00 0.00 0.00 0.00 Weir Type = --- --- --- ---
Length(ft) = 0.00 0.00 0.00 0.00 Multi-Stage = No No No No
Slope(%) = 0.00 0.00 0.00 n/a
N-Value = .013 .013 .013 n/a
Orifice Coeff. = 0.60 0.60 0.60 0.60 Exfil.(in/hr) = 0.100(by Contour)
Multi-Stage = n/a No No No TW Elev.(ft) = 0.00
Note:Culvert/Orifice outflows are analyzed under inlet(ic)and outlet(oc)control.Weir risers checked for orifice conditions(ic)and submergence(s).
Stage(ft) Stage/Storage Elev(ft)
3.00 103.00
2.00 102.00
1.00 101.00
0.00 100.00
0 200 400 600 800 1,000 1,200 1,400 1,600
Storage Storage(cuft)
Pond Report
Hydraflow Hydrographs Extension for Autodesk0 Civil 3D0 by Autodesk, Inc.v2023 Tuesday,07/1 /2025
Pond No. 3 - Retention Syst
Pond Data
UG Chambers-Invert elev. =100.00 ft, Rise x Span=3.00 x 3.00 ft, Barrel Len= 191.50 ft, No. Barrels= 1, Slope=0.00%, Headers=No
Encasement-Invert elev.= 100.00 ft, Width=3.33 ft, Height=3.00 ft, Voids=27.00%
Stage/Storage Table
Stage(ft) Elevation(ft) Contour area(sqft) Incr.Storage(cuft) Total storage(cuft)
0.00 100.00 n/a 0 0
0.30 100.30 n/a 103 103
0.60 100.60 n/a 141 244
0.90 100.90 n/a 160 404
1.20 101.20 n/a 171 576
1.50 101.50 n/a 177 753
1.80 101.80 n/a 177 929
2.10 102.10 n/a 171 1,101
2.40 102.40 n/a 160 1,261
2.70 102.70 n/a 141 1,402
3.00 103.00 n/a 103 1,505
Culvert/Orifice Structures Weir Structures
[A] [B] [C] [PrfRsr] [A] [B] [C] [D]
Rise(in) = 0.00 0.00 0.00 0.00 Crest Len(ft) = 0.00 0.00 0.00 0.00
Span(in) = 0.00 0.00 0.00 0.00 Crest EI.(ft) = 0.00 0.00 0.00 0.00
No.Barrels = 0 0 0 0 Weir Coeff. = 3.33 3.33 3.33 3.33
Invert EI.(ft) = 0.00 0.00 0.00 0.00 Weir Type = --- --- --- ---
Length(ft) = 0.00 0.00 0.00 0.00 Multi-Stage = No No No No
Slope(%) = 0.00 0.00 0.00 n/a
N-Value = .013 .013 .013 n/a
Orifice Coeff. = 0.60 0.60 0.60 0.60 Exfil.(in/hr) = 0.100(by Contour)
Multi-Stage = n/a No No No TW Elev.(ft) = 0.00
Note:Culvert/Orifice outflows are analyzed under inlet(ic)and outlet(oc)control.Weir risers checked for orifice conditions(ic)and submergence(s).
Stage/Storage/Discharge Table
Stage Storage Elevation Clv A Clv B Clv C PrfRsr Wr A Wr B Wr C Wr D Exfil User Total
ft cuft ft cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs cfs
0.00 0 100.00 --- --- --- --- --- --- --- --- 0.000 --- 0.000
0.30 103 100.30 --- --- --- --- --- --- --- --- 0.001 --- 0.001
0.60 244 100.60 --- --- --- --- --- --- --- --- 0.001 --- 0.001
0.90 404 100.90 --- --- --- --- --- --- --- --- 0.001 --- 0.001
1.20 576 101.20 --- --- --- --- --- --- --- --- 0.001 --- 0.001
1.50 753 101.50 --- --- --- --- --- --- --- --- 0.001 --- 0.001
1.80 929 101.80 --- --- --- --- --- --- --- --- 0.001 --- 0.001
2.10 1,101 102.10 --- --- --- --- --- --- --- --- 0.001 --- 0.001
2.40 1,261 102.40 --- --- --- --- --- --- --- --- 0.001 --- 0.001
2.70 1,402 102.70 --- --- --- --- --- --- --- --- 0.001 --- 0.001
3.00 1,505 103.00 --- --- --- --- --- --- --- --- 0.001 --- 0.001
Runoff Reduction Volume (RRV)
Montana Post-Construction Storm Water BMP Design Manual (2017)
Section 3.2.1
Water Quality Rainfall Depth P 0.5 in
Dimensionless Runoff Coefficient R� 0.677
Percent Impervious Area I 0.696
Site Drainage Area A 0.193 ac
Equations:
PRVA
RRV = 12
Outputs
Runoff Reduction Volume RRV 0.005 ac-ft
238 ft3
Maximum Drain Down Time Calculations
Dimensions
diameter(ft) length (ft) width (ft) depth (ft)
Perforated Pipe 3 191.5 - -
Total (Pipe+Gravel) - 191.5 3.33 3
Gravel Void Ratio 27%
Volume (cu-ft) %Storage
Total 1913 100%
Perforated Pipe 1354 71%
Gravel 559
Gravel Void 151 8%
Total Void 1505 79%
72-hour Maximum Drain Down Time
Surface Area (ft2) 638
Depth of Water(ft) 3.00
Infiltration Rate (in/hr) 1.1
Drain Down Time (hr) 32.73 < 72 hrs
RIMROCK ENGINEERING, INC.
PHYSICAL PROPERTIES OF AGGREGATE
Client Name: Knife River—Billings_ Project No: 03101
Address: P.O. Box 80066 __ Date of Report: __09/27/2018 _________
Billin s, Montana 59108
Project Name: 2018 Aggregate Tests Sample_No:_ See Below
Pro'ect Location: Billin s, Montana Date Received: 09/26/2018
Sampled By__ Client ___ Type of Aggre9ate: _ _ See Below
Submitted B : Client Source of Sam le: Bi erstaff Pit
Bulk Density (Unit igh ) and Voids in gregate ASTM C29
Sam le No. 18-W3057-S1 18-W3057-S2 18-W3057-S3 18-W3069-S1
Descri tion -3/8"Chi s -3/4" Beddin -1"Concrete Rock -1-1/2"Washed Rock
Void Content, % 39 37 38 34
Void Ration = 0.37
Porosity = Void Ratio/(1+Void Ratio)x100
Porosity = 0.37/1.37*100 = 27%
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Reviewed By: .'/U i,(.. /_ C'��i
RIMROCK ENGINEERING, INC. 5440 Holiday Avenue. Billings, MT 59101. Phone: Fax:
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APPENDIX D
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(E) STORM CURB INLET o 0
T R A K K E R T RA 1 L SUBSURFAVPRo oE��ENT1050BAFT3 � �
20 10 0 20 40 a o
VREQUIRED — �49� FT
SCALE: 1�� = 20� (P) 191.5 LF OF 36"
DA #2 BURIED PERFORATED PIPE .
LANDSCAPE = 747 SQ. FT. Z
� ��������������������� ������������������ HARDSCAPE = 641 SQ. FT. S 89'06'45 E 82.87 � �
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LANDSCAPE = 1812 SQAFT1 I � � � (P) INLETS
HARDSCAPE = 5227 SQ. FT. I "E
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APPENDIX E
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OPERATION, MAINTENANCE, AND
INSPECTION PLAN
Stites Office Building
IMEG #24006341 .00
PLNAPP #24637
1143 Stoneridge Drive, Suite 1, Bozeman, MT
: :imegcorp.com
TABLE OF CONTENTS
1. Parties Responsible..........................................................................................................................3
2. Contact Information .........................................................................................................................3
3. Site Plan ...........................................................................................................................................3
4. Maintenance and Inspection Activities ............................................................................................3
4.1. Construction Inspection ......................................................................................................3
4.2. Post-Construction Inspection..............................................................................................4
4.3. Maintenance Activities and Inspection Schedule ...............................................................4
5. Stormwater Facility Inspection Form...............................................................................................4
6. Replacement Schedule....................................................................................................................5
7. Cost Estimate...................................................................................................................................5
8. Financial Plan....................................................................................................................................6
9. References.......................................................................................................................................7
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 2 June 30, 2025
Operation, Inspection, and Maintenance Plan
For the
Stites Office Building
Prepared for:
City of Bozeman, MT
I M EG #24006341.00
June 30, 2025
1. Parties Responsible
Stormwater conveyance systems connected to the site include City of Bozeman infrastructure, such as
curbs, gutters, inlets, manholes, and detention ponds. Facilities within public rights-of-way will be
maintained by the City of Bozeman, while those outside public rights-of-way, such as the off-site pond
are the responsibility of the Homeowners or Property Owners Association, as outlined in the Baxter
Meadows Storm Sewer Facilities Maintenance Plan. Maintenance, inspection, and records-keeping of
the proposed onsite storm facilities are the responsibility of the property owner. Responsibilities will
transfer to successive owners automatically. Each property owner shall ensure that stormwater facilities
remain in compliance with applicable regulations.
2. Contact Information
Responsible Party: Jon Stites— Property Owner
Phone Number: (406) 994-9189
Email Address:
Mailing Address: 3970 Valley Commons Drive
Unit 2
Bozeman, MT 59718
3. Site Plan
Please see the civil site plan associated with City of Bozeman PLN APP#24637, specifically the detailed
site grading and drainage sheet, C5.0.
4. Maintenance and Inspection Activities
4.1. Construction Inspection
The current site entrances are unpaved. Gravel will be placed at the site entrance to minimize sediment
transport during construction. If necessary, tires may be washed on the gravel surface to further reduce
sediment tracking onto city streets. During construction, filter fabric shall be placed between the rim and
frame of existing storm drain inlets, as indicated in the demolition plan, to prevent sediment from
entering the drainage system.
The contractor shall install straw wattles or a silt fence along the west and north sides of the disturbance
area to prevent sediment from entering the adjacent roadway. Permanent BMPs will include landscaping,
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 3 June 30, 2025
hardscape improvements, a subsurface retention basin, and storm drain inlets to minimize sediment
transport.
The contractor is responsible for inspecting and maintaining BMPs during construction. BMPs must be
inspected and maintained at least once every fourteen days and within 24 hours of a rainfall event of 0.5
inches or greater. Any visible erosion or sedimentation must be addressed within 24 hours. Disturbed
soil must be stabilized within 14 days of clearing or inactivity. Soil stockpiles must be stabilized or
covered daily. If wind erosion is observed, soil piles should be watered or covered.
Solid waste and construction debris will be stored in dumpsters and transported to the Bozeman or
Gallatin County Dump as needed. The contractor is responsible for daily site cleanup. Chemicals, paints,
petroleum products, fertilizers, and pesticides must be stored in approved containers in enclosed areas.
Hazardous waste must be disposed of per label instructions. The contractor shall also ensure proper
disposal of concrete washout water and provide portable toilets on-site during construction, with waste
periodically hauled to the local wastewater treatment plant.
4.2. Post-Construction Inspection
Post-construction, the project owner will assume responsibility for stormwater facility inspection and
maintenance. Permanent erosion control measures will include landscaping, finished asphalt, and
concrete surfaces. Stormwater will be collected in on-site subsurface retention basins.
4.3. Maintenance Activities and Inspection Schedule
Catch Basins—At least annually, inspect the inside of each catch basin for a depth of deposits exceeding
one-third the depth from the basin to the invert of the lowest outlet invert (i.e. sump) (Storm Water 0
and M Fact Sheet Catch Basin Cleaning 1999). If deposits exceed this depth, clean out basin either
manually or with a truck equipped with a vacuum pump. If deposits greatly exceed this depth, begin
inspecting more regularly. Given the small size of the proposed catch basins, it may be more economical
to clean out by hand. Test sediments for pollutants if contamination is suspected, debris can typically be
disposed of in the landfill, however hazardous waste disposal may be required if sediment presents
contamination.
Retention Basin—At least annually, inspect the underground basin for sediments. Observe that the
retention basin is draining properly (i.e. no ponding occurring at catch basin inletsl. Maintain pretreatment
structures by removing sediment and debris from catch basins and landscaped depressions. Vacuum and
jet the pipe if sediment is observed and the function of the structure is impaired.
Swales/Landsca,oe Depressions—Inspect and remove debris from drainage swales and retention basins
after storms to ensure rainwater has drained and there is no erosion. Seasonally, mow grass no shorter
than 3 to 6 inches and remove clippings. Monitor health of vegetation and stabilize eroded areas with
new vegetation or reseeding. Maintain original condition of side slopes and minimize use of fertilizer,
pesticides, and herbicides (How to Maintain your Grass Drainage Swale 2019).
5. Stormwater Facility Inspection Form
Record annual inspections, maintenance activities, test results, and follow-up actions. An inspection form
detailing these activities and observations is provided with this application.
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 4 June 30, 2025
6. Replacement Schedule
The following design life of each component is as follows.
24" HDPE Pipe—50- 100 years.
6" HDPE Pipe—50-100 years.
12" Landscape Catch Basin —30 years.
7. Cost Estimate
Retention Basin—The estimated capital cost for an infiltration basin is equal to 13.2*Volume069. Using a
regional cost adjustment factor of 1.04 for Montana, the base capital cost for the proposed basin is
$619.71. The base annual maintenance cost of an infiltration basin is between 1% and 10% of the base
construction cost, resulting in a projected annual maintenance cost between $6.20 and $61.97 (Strassler
et al., 1999). According to the U.S. Bureau of Labor Statistics Consumer Price Index Inflation Calculator,
the equivalent buying power today is $4,178.36 and therefore base annual maintenance present-day is
between $21.35 and $213.55. Table 1-1 and 1-2 summarize the estimated costs for the proposed
infiltration basin.
Table 1-1. Infiltration Basin Annual Base Capital Cost
Storage Cost of Facility Adjusted for Adjusted for
Volume Montana 2025*
Infiltration V C C C
Basin
Capital Cost ft3 C = 13.2Vo.69 1.04C
1502 $ 2,0553.41 $ 2,135.55 $ 4,178.36
Table 1-2. Infiltration Basin Annual Base Maintenance Cost
Infiltration Basin 0.01C 0.1C
Maintenance
Cost $ 21.35 $ 213.55
Swales/Landscape Dep�essions—The vegetative BMPs proposed for the site include swales and
landscape depressions however, the intent is to convey water rather than infiltrate and therefore this
cost analysis is based on filter strips. The estimated capital cost for filter strips are $13,800/acre for seed
and $29,000/acre for sod. The total landscaped area intended to pretreat and convey stormwater is 0.05
acres. The base capital cost for seed is $690 and $1,450 for sod. These projected costs adjusted for
today's buying power is equivalent to between $1,31 1.75 and $2,756.57. The base maintenance cost for
either capital scenario is $320/acre, resulting in total maintenance costs of $30.42 (Strassler et al., 1999).
Table 1-3 and 1-4 summarize the estimated costs for the proposed vegetative BMPs.
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 5 June 30, 2025
Table 1-3. Vegetated BMP Annual Base Capital Cost
Vegetative Cost, Sod Cost, Seed Land Area
BMP Capital C C A
Cost C = $29,000 *A C = $13,800 *A ac
Base Cost $ 1,450.00 $ 690.00 0.05
Adjusted for
Montana $ 1,508.00 $ 717.60
Adjusted for
2025* $ 2,756.57 $ 1,311.75
Table 1-4. Vegetated BMP Annual Base Maintenance Cost
Vegetated Cost
BMP
Maintenance
Cost C = $320 *A
Base Cost $ 16.00
Adjusted for
Montana $ 16.64
Adjusted for
2025* $ 31.63
*Value adjusted from August 1999 to January 2025 buying power.
The average cost for vacuum truck services is $75 to $150/ hr hour. Prices may vary with local providers
and the size and extent of sediment deposits.
The average hourly rate of a landscape laborer is $25.00/ hr. Annual observation and inspection, seasonal
site upkeep of vegetated areas including mowing and removal of grass clippings will be assessed as
needed.
The facilities are intended to be low maintenance and have no associated operational costs.
8. Financial Plan
The proposed commercial office building development will generate revenue to fund routine site services
including inspection and maintenance of onsite stormwater facilities.
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 6 June 30, 2025
9. References
Environmental Protection Agency. (1999, September). Storm Wate�O and M Fact Sheet Catch Basin
Cleaning. EPA. https://nepis.epa.gov/Exe/ZyPURL.cgi?Dockey=200044BA.txt
Environmental Protection Agency. (1999, September). Storm Water O and M Fact Sheet Preventive
Maintenance. EPA. https://nepis.epa.gov/Exe/ZyPURL.cgi?Dockey=200044A0.txt
Department of Public Works Watershed Protection & Restoration Program. (2019, March). How to
Maintain you�Grass D�ainage Swale. Anne Arundel County Maryland Department of Public
Works. https://www.aacounty.org/sites/default/files/2023-
04/Grass_Swale_Maintenance_FINAL.pdf
HDR, & Montana Department of Environmental Quality. (2017, September). Montana Post-Construction
Storm WaterBMPDesign Guidance Manual. Montana.
Strassler, E., Pritts, J., & Strellec, K. (1999, August). Prelimina�y Data Summary of Urban Stormwate�
BestManagementPractices. EPA. https://nepis.epa.gov/Exe/ZyPURL.cgi?Dockey=9100PXC1.txt
U.S. Bureau of Labor Statistics. (2025, January). CPl lnf/ation Calculator. U.S. Bureau of Labor Statistics.
https://www.bls.gov/data/inflation_calculator.htm
Engineering Design Report
` Stites Office Building
� Bozeman, MT
. 7 June 30, 2025
`
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ACKNOWLEDGEMENT OF
STORMWATER FACILITY
MAINTENANCE REQUIREMENTS
Stites Office Building
IMEG #24006341 .00
PLNAPP #24637
FEBRUARY 2025
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1143 Stoneridge Drive, Suite 1, Bozeman, MT
: :imegcorp.com
Acknowledgement of Stormwater Facilities Maintenance Requirements
PROPERTY OWNER: Jon Stites
NAME OF PLAN/DEVELOPMENT: Stites Office Building
LOTBLOCK/SUBDIVISION: Lot 6A, Block 20 Baxter Meadows Subdivision
Property Owner hereby acknowledges that they are required to maintain all stormwater
facilities on the Property pursuant to Bozeman Municipal Code sec. 40.04.720. This
requirement is binding on any successor or assign of the Property Owner listed above.
The City requires stormwater facilities be constructed and adequately maintained on
the Property in order to maintain the health, safety and welfare of City residents. Adequate
maintenance is defined as keeping the stormwater facilities and all components thereof in
good working condition so that these stormwater facilities continue to perform in accordance
with the design intent.
Should the Property Owner fail to adequately maintain stormwater facilities, the City
may enter upon the Property and take such steps as are necessary to correct deficiencies. The
City may assess against the Property Owner for the cost of any repairs or necessary
maintenance by any means provided for in the Bozeman Municipal Code.
By signing below Property Owner acknowledges they have read this document and the
applicable provisions of the Bozeman Municipal Code, and they agree to the maintenance
requirements for all stormwater facilities on their Property.
BY:
(Property Owner)
DATE:
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STORMWATER FACILITY INSPECTION
FORM
Stites Office Building
IMEG #24006341 .00
PLNAPP #24637
FEBRUARY 2025
1143 Stoneridge Drive, Suite 1, Bozeman, MT
: :imegcorp.com
Section 1:General Information
Facility ID: Facility Type:Choose an item.
Date/Time:Click or tap to enter a date.
Owner: Contact:
Inspector's Name,contact info: Choose an item.
Location/Access info:
Type oflnspection:
❑ Routine,Dry Weather ❑ Routine,Wet Weather ❑ Complaint Driven ❑ Other:
Section 2:Weather and Discharge Information
Most recent precipitation or melt:
Temperature:
Is a stormwater discharge occurring? ❑Yes ❑ No
If yes,what is the source and quality of discharge?Is an illegal discharge occurring? ❑Yes ❑ No
If yes,what is the source and quality of discharge?
Section 3:Facility Maintenance Priority
❑ Low:Stormwater facility appears to be functioning as designed.Continue scheduled maintenance.
❑ Medium:Stormwater facility requires minor to moderate sediment and vegetation maintenance to mitigate the risk of flooding,
waterway pollution,and infrastructure failure.
❑ High: Stormwater facility requires significant sediment dredging, vegetation removal, and/or infrastructure repairs to restore
function.
Notes,Findinqs&Recommendations:
Inspector's Signature: Date:
Section 4:Qualitative Analysis
Components # Items Conditions Results Notes and Required Actions
1.1 Accessibility Degraded,missing,or inadequate ❑Yes
maintenance access? ❑ No
1.2 Debris Trash,sediment,and waste within and ❑Yes
around the facility? ❑ No
General
1.3 Vegetation Overgrown or dead cattails,woody ❑Yes
shrubs,weeds,grass,and ❑ No
trees?
1.4 Infrastructure Damaged inlet pipe,outlet pipe,outfall ❑Yes
Condition structure,or fencing? ❑ No
2.1 Pretreatment Bay or Clogged,obstructed,or filled ❑Yes
Facility pretreatment forebay or facility? ❑ No
2.2 Storage Bay Clogged or filled storage bay? ❑Yes
❑ No
Groundwater or Stagnant water with infiltration greater ❑Yes
2.3 Standing Water than 48 hours post-rain event? ❑ No
Facility
❑Yes
2.4 Flow Path Clogged or obstructed flow path? ❑ No
2.5 Side Slopes Barren or exposed surfaces on Facility's ❑Yes
side slopes and bottom? ❑ No
3.1 Maintenance Plan or Is there a written plan specific to this ❑Yes
Agreement facility? ❑ No
Maintenance 3.2 Implementation Is there evidence of maintenance? ❑Yes
❑ No
Section 5:Quantitative Analysis
Cover type %Within Notes
facility
Bare ground
Aquatics
Vegetation Grasses/Herbaceou
Trees>3" DBH
Shrubs
Total 100
Location Reading(ft) Elevation(ft) Notes
SRV#CP
Control Point
SRV#1
Inlet
SRV#2
Outlet
SRV#3
Center
SRV#4
North of Center
Elevation
Analysis SRV#5
East of Center
SRV#6
South of Center
SRV#7
West of center
SRV#8
Berm or overflow
SRV#9
Summary
Section 6: Facility Maintenance Inspection Exhibit
Section 7: Photo Log
Photo 1 Photo 2
Date: Date:
Description: Description:
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APPENDIX F
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February 25, 2025
Jonathan Stites
15 Meridian Road
Three Forks, Montana 59752
Email:
RE: Geotechnical Investigation Fieport
Lots 4-6, Block 20
Baxter Meadows Subdivision Phase 2A
Bozeman, Montana
IMEG#24006453.00
Dear Jonathan,
Per your request, IMEG has conducted a subsurface soils investigation for the above referenced property
located in Bozeman, Montana. The scope of services was to conduct a subsurface soils investigation and
provide a soils investigation report for a new commercial structure. The report documents the subsurface
conditions, soil properties, and provides foundation design and general earthwork recommendations.
Proposed Construction
A commercial office building is proposed for construction. The structure will utilize a slab-on-grade with
stem wall foundation. The structure is planned to have a total height of 14.5 feet and will be a single story.
In determining the allowable bearing capacity and settlement estimates, it has been assumed that the
foundation footings will not be subjected to unusual loading conditions such as eccentric loads. A footing
is eccentrically loaded if the load transferred to the footing is not directed through the center of the footing.
If any of the foundation footings will be eccentrically loaded, please contact this office so we can
appropriately revise our allowable bearing capacity and settlement estimates.
Subsurface Soil and Conditions
On October 24, 2024 a member of the staff of IMEG visited the site to conduct a subsurface soils
investigation. The subsurface soils investigation consisted of examining three exploratory test pit
excavations. The exploratory test pits were excavated with tracked excavator provided by Elevation
Excavating. The soil profile revealed by the exploratory excavation was logged and visually classified
according to ASTM D 2488, which utilizes the nomenclature of the Unified Soil Classification System
1143 Stoneridge Drive, Suite 1, Bozeman, MT
: :imegcorp.com
Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 2 of 12
(USCS). The relative density of each soil layer was estimated based on probing of the excavation sidewalls
with a rock hammer and penetration tests performed with a static cone penetrometer. Any evidence of
seepage or other groundwater conditions were also noted. The location of the exploratory test pits are
shown on the included Test Pit Location Map.
The following paragraphs briefly summarize the subsurface soils and conditions observed in the exploratory
test pits excavated for the field investigation. The soil horizons are described as they were encountered in
the test pit excavations, starting with the horizon nearest the surface and proceeding with each additional
horizon encountered with depth. Please refer to the attached test pit logs for more detailed information.
The first soil horizon encountered in each exploratory excavation was undocumented fill, which was
present to depths varying from approximately 0.83 feet below grounds surface (bgs) to 1.25 feet bgs. This
material was a mix of clay, gravel and sand. This material must be removed from beneath all foundation
elements and in any area that will receive asphalt or concrete pavements.
The second soil horizon encountered in each exploratory excavation was an Organic Soil of Low plasticity
(OL). This material was black in color, moist and soft. This material was encountered to depths varying
from 2.0 feet bgs to 2.41 feet bgs. Organic soils are highly compressible and are not suitable for foundation
support. This material must be removed from beneath all foundation elements and in any area that will
receive asphalt or concrete pavement.
Underlying the Organic Soil in each exploratory excavation was a Lean Clay (CL), which was present to
depths varying form 4.0 feet bgs to 4.5 feet bgs. This material was tan to grayish white in color and was
moist to very moist. Penetration tests performed on this material with a static cone penetrometer indicated
it was very soft in consistency. This material is moisture sensitive and not suitable for foundation support
and must be removed from beneath the structure's foundation.
Underlying the Lean Clay in each exploratory excavation was a Poorly Graded Gravel with Sand and Cobbles
(GP), the typical bearing material for most structures within the City of Bozeman. This material was found
to be in a medium dense condition and is suitable for foundation support. Groundwater was encountered
within this material at depths varying from 6.50 feet bgs to 7.33 feet bgs.
Based on the subsurface investigation, it is recommended that the proposed structure bear on the Poorly
Graded Gravel with Sand and Cobbles or on properly placed and compacted structural fill overlying the
Poorly Graded Gravel with Sand and Cobbles.
Groundwater
Groundwater was encountered at depths varying from 6.5 feet bgs to 7.33 feet bgs in the exploratory
excavations. Evidence of seasonally high groundwater (such as a lack of calcium deposits, gleyed soils,
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 3 of 12
increase in moisture content and lack of organic roots) was observed starting at a depth of approximately
3.0 feet bgs, suggesting groundwater may be rising up to near this elevation seasonally.
Seismicity
The general Bozeman area is located in an earthquake zone known as the intermountain seismic belt,
which is a zone of earthquake activity that extends from northwest Montana to southern Arizona. In
general, this zone is expected to experience moderately frequent, potentially damaging earthquakes. With
that in mind, it is important that the structure be designed to withstand horizontal seismic accelerations
that may be induced by such an earthquake, as is required by the International Building Code.
The USGS provides seismic design parameters for the design of buildings and bridges across the United
States.These parameters are based on the 2015 National Earthquake Hazards Reduction Program (NEHRP)
Recommended Seismic Provisions. The primary intent of the NEHRP Recommended Seismic Provisions
is to prevent, for typical buildings and structures, serious injury and life loss caused by damage from
earthquake ground shaking.
The following seismic design parameters were determined for the subject property using the USGS
Seismic Design Application:
Approximate site Location:
Latitude = 45.700° N
Longitude = 111.087°W
Maximum Considered Earthquake (MCE) Spectral Response Acceleration Parameters:
Short Period (Ss) = 0.717g
1-Second Period (S,) = 0.222g
Site Coefficients and Adjusted MCE Spectral Response Acceleration Parameters:
SMs = 0.879g
SM, = 0.479g
Design Spectral Response Acceleration Parameters:
Sps = 0.586g
So, = 0.319g
The seismic site class for this project is D.
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 4 of 12
Foundation Recommendations
Based on the subsurface soils encountered in the exploratory excavations, it will be acceptable to utilize a
slab-on-grade with stem wall foundation as planned. Please find the following as general recommendations
for all foundation elements:
• The foundation footings are to bear on the Poorly Graded Gravel with Sand and Cobbles or on
properly placed and compacted structural fill overlying this material.
• If construction takes place during the colder months of the year, the subgrade must be protected
from freezing. This may require the use of insulating blankets and/or ground heaters
Allowable Bearing Capacity
The bearing capacity of a soil is defined as the ultimate pressure per unit area by the foundation that can
be supported by the soil in excess of the pressure caused by the surrounding soil at the footing level.
Bearing capacity is determined by the physical and chemical properties of the soil located beneath the
proposed structure's footings and can also be influenced by the water table.
It is recommended that the loads from the proposed structure be transmitted to the Poorly Graded Gravel
with Sand and Cobbles or on properly placed and compacted structural fill overlying the Poorly Graded
Gravel with Sand and Cobbles. For this scenario it is recommended that an allowable bearing capacity of
2,500 pounds per square foot be used to dimension the foundation footings.
The allowable bearing capacity may be increased by one third for short term loading conditions such as
those from wind or seismic forces.
Settlement
While the soil at the site may be able to physically support the footings, it is also important to analyze the
possible settlement of the structure.
When a soil deposit is loaded by a structure, deformations within the soil deposit will occur. The total
vertical deformation of the soil at the surface is called total settlement. Total settlement is made up of two
components: elastic settlement and consolidation settlement. Elastic settlement is the result of soil
particles rearranging themselves into a denser configuration due to a load being imposed on them and
usually occurs during the construction process and shortly after. Consolidation settlement occurs more
slowly and over time as water within the pore spaces of a soil are forced out and the soil compresses as
the stress from the load is transferred from the water molecules to the soil particles. Consolidation
settlement is more of a concern with fine-grained soils with low permeability and high in-situ moisture
contents. The degree of settlement is a function of the type of bearing material, the bearing pressure of
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 5 of 12
the foundation elements, local groundwater conditions, and in some cases determines the allowable
bearing capacity for a structures' footings.
In addition to analyzing total settlement, the potential for differential settlement must also be considered.
Differential settlement occurs in soils that are not homogeneous over the length of the foundation or in
situations where the foundation rests on cut and fill surfaces. If the foundation rests on structural fill
overlaying properly compacted gravelly soils, differential settlement is expected to be well within tolerable
limits. Areas that have significantly more fill under the foundation footings (four feet of more)create greater
potential for differential settlement. In these cases the structural fill must be installed properly and tested
frequently. Compaction efforts and structural fill consistence are vital in minimizing differential settlement.
A settlement analysis based on conservative soil parameter estimates, the recommended allowable
bearing capacity, and the assumption that all recommendations made in this report are properly adhered
to, indicates the total and differential settlement are expected to be 1/2-inch or less. Structures of the type
assumed can generally tolerate this amount of movement, however, these values should be checked by a
licensed structural engineer to verify that they are acceptable.
Please note that the settlement estimates are based on loads originating from the proposed structure. If
additional loads are introduced, such as the placement of large quantities of fill, our office should be
contacted to re-evaluate the settlement estimates.
Lateral Pressures
Lateral pressures imposed upon foundation and retaining walls due to wind, seismic forces, and earth
pressures may be resisted by the development of passive earth pressures and/or frictional resistance
between the base of the footings and the supporting soils. If a foundation or retaining wall is restrained
from moving, the lateral earth pressure exerted on the wall is called the at-rest earth pressure. If a
foundation or retaining wall is allowed to tilt away from the retained soil, the lateral earth pressure exerted
on the wall is called the active earth pressure. Passive earth pressure is the resistance pressure the
foundation or retaining wall develops due to the wall being pushed laterally into the earth on the opposite
side of the retained soil. Each of these pressures is proportional to the distance below the earth surface,
the unit weight of the soil, and the shear strength properties of the soil.
It is recommended that all foundation and retaining walls be backfilled with well-draining granular material.
Well-draining granular backfill has a more predictable behavior in terms of the lateral earth pressure exerted
on the foundation or retaining wall and will not generate expansive related forces. If backfill containing
significant quantities of clayey material is used, the seepage of water into the backfill could potentially
generate horizontal swelling pressures well above at-rest values. Additionally, seepage into a clayey
backfill material will also cause significant hydrostatic pressures to build up against the foundation wall due
to the low permeability of clay soils and will make the backfill susceptible to frost action.
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 6 of 12
Subsurface walls that are restrained from moving at the top are recommended to be designed for an
equivalent fluid pressure of 70 pounds per cubic foot (pcf) (at-rest pressure); the equivalent fluid pressure
is the product of the retained soils unit weight and its coefficient of active or at-rest earth pressure. Any
subsurface walls that are allowed to move away from the restrained soil, such as cantilevered retaining
walls, are recommended to be designed for an equivalent fluid pressure of 55 pcf (active pressure). For
passive pressures, an equivalent fluid pressure of 275 pcf is recommended, and the coefficient of friction
between the cast-in-place concrete and the Poorly Graded Gravel with Sand and Cobbles is 0.5.
These recommended values were calculated assuming a near horizontal backfill and that a mix of the Lean
Clay, Undocumented Fill and Poorly Graded Gravel with Sand and Cobbles will be used as foundation wall
backfill. It is also assumed that the backfill will be compacted as recommended in this report. Also, please
note that these design pressures do not include a factor of safety and are for static conditions, they do not
account for additional forces that may be induced by seismic loading.
Subgrade Preparation and Structural Fill
In general, the excavation for the foundation must be level and uniform and continue down to the Poorly
Graded Gravel with Sand and Cobbles. If any soft spots or undocumented fill are encountered, they will
need to be removed and backfilled with structural fill. The excavation width must extend out from the
footing a minimum distance equal to one footing width or to a distance equal to '/�the height of the required
structural fill; for example, if 6 feet of structural fill is required, the excavation must extend outwards from
the foundation footings a minimum distance of 3 feet.
Structural fill is defined as all fill that will ultimately be subjected to structural loadings, such as those
imposed by footings, floor slabs, pavements, etc. The Poorly Graded Gravel with Sand and Cobbles may
be reused as structural fill, provided any cobbles larger than 6 inches in size are removed. Structural fill
may also be imported for this project, if needed. Imported structural fill is recommended to be a well
graded gravel with sand that contains less than 15 percent of material that will pass a No. 200 sieve and
that has a maximum particle size of 3.0 inches. Also, the fraction of material passing the No. 40 sieve shall
have a liquid limit not exceeding 25 and a plasticity index not exceeding 6. The gravel and sand particles
also need to be made up of durable rock materials that will not degrade due to moisture or the compaction
effort; i.e. no shale or mudstone fragments should be present.
Structural fill must be placed in lifts no greater than 12-inches (uncompacted thickness) and be uniformly
compacted to a minimum of 97 percent of its maximum dry density, as determined by ASTM D698.
Typically, the structural fill must be moisture conditioned to within ± 2 percent of the materials optimum
moisture content to achieve the required density. It is recommended that the structural fill be compacted
with a large vibrating smooth drum roller. Please note that if a moisture-density relationship test
(commonly referred to as a proctor) needs to be performed for a proposed structural fill material to
determine its maximum dry density in accordance with ASTM D698, a sample of the material must be
delivered to this office a minimum of three full working days prior to density testing being needed.
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 7 of 12
At no time should surface water runoff be allowed to flow into and accumulate within the excavation for
the foundation elements. If necessary, a swale or berm should be temporarily constructed to reroute all
surface water runoff away from the excavation. Excavation should not proceed during large precipitation
events.
If any of the foundation footings are found to be located on a test pit, the area will need to be excavated
down to the full depth of the test pit and structural fill be placed and compacted in controlled lifts as
described in this report to bring the area back up to the desired grade.
Foundation Wall Backfill
Approved backfill material should be placed and compacted between the foundation wall and the edge of
the excavation. The organic soil shall not be used as foundation wall backfill. The Lean Clay, Poorly Graded
Gravel with Sand and Cobbles and Undocumented Fill encountered during the field investigation are all
suitable for reuse as foundation wall backfill along the exterior of the foundation in areas that will not have
concrete or asphalt pavements, provided they are not too moist and any cobbles larger than 6 inches in
size are removed. Structural fill is recommended as foundation wall backfill in all areas that will support
concrete slabs-on-grade or asphalt paving improvements.
The foundation wall backfill shall be placed in uniform lifts and be compacted to a minimum of 95 percent
of the material's maximum dry density, as determined by ASTM D698. The foundation wall backfill will
need to be compacted with either walk behind compaction equipment or hand operated compaction
equipment in order to avoid damaging the foundation walls. If walk behind compaction equipment is used
lifts should not exceed 8-inches (loose thickness) and if hand operated compaction equipment is used lifts
should not exceed 4-inches (loose thickness).
Interior Slabs-on-Grade
For any interior slabs-on-grade, it is recommended that the excavation continue down through the
Undocumented fill, Organic soil and Lean Clay to the Poorly Graded Gravel with Sand and Cobbles or to a
depth of 6 inches below the proposed bottom of slab elevation, whichever is deeper. If needed structural
fill can then be placed and compacted to within 6 inches of the bottom of slab elevation.
For all interior concrete slabs-on-grade, preventative measures must be taken to stop moisture from
migrating upwards through the slab. Moisture that migrates upwards through the concrete slab can
damage floor coverings such as carpet, hardwood and vinyl, in addition to causing musty odors and mildew
growth. Moisture barriers will need to be installed to prevent water vapor migration and capillary rise
through the concrete slab.
Capillarity is the result of the liquid property known as surface tension, which arises from an imbalance of
cohesive and adhesive forces near the interface between different materials.With regards to soils, surface
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 8 of 12
tension arises at the interface between groundwater and the mineral grains and air of a soil. The height of
capillary rise within a given soil is controlled by the size of the pores between the soil particles and not the
size of the soil particles directly. Soils that have small pore spaces experience a higher magnitude of
capillary rise than soils with large pore spaces. Typically, soils composed of smaller particles (such as silt
and clay) have smaller pore spaces.
In order to prevent capillary rise through concrete slabs-on-grade it is recommended that 6 inches of 3�4-
inch washed rock (containing less than 10 percent fines) be placed and compacted once the excavation for
the slab is complete. The washed rock has large pore spaces between soil particles and will act as a
capillary break, preventing groundwater from migrating upwards towards the bottom of the slab.
Water vapor is currently understood to act in accordance with the observed physical laws of gases, which
state that the water vapor will travel from an area of higher concentration to that of a lower concentration
until equilibrium is achieved. Because Earth contains large quantities of liquid water, water vapor is
ubiquitous in Earth's atmosphere, and, as a result, also in soils located above the water table (referred to
as the vadose zonel. Typically, the concentration of water vapor in the vadose zone is greater than that
inside the residence. This concentration difference may result in an upward migration of water vapor from
the vadose zone through the concrete slab-on-grade and into the building.
In order to prevent this upward migration of water vapor through the slab, it is recommended that a 15-mil
extruded polyolefin plastic that complies with ASTM E1745 (such as a Stego Wrap 15-mil Vapor Barrier)
be installed.The vapor barrier should be pulled up at the sides and secured to the foundation wall or footing.
Care must be taken during and after the installation of the vapor barrier to avoid puncturing the material,
and all joints are to be sealed per the manufacture's recommendations.
Once the excavation for any interior slabs-on-grade is completed as described in the first paragraph of this
section, and the 3/4 inch washed rock and moisture barriers have been properly installed, it will be
acceptable to form and cast the steel reinforced concrete slab. It is recommended that interior concrete
slabs-on-grade have a minimum thickness of 4 inches, provided the slab reinforcement is designed by a
licensed structural engineer.
Exterior Slabs-on-Grade
For exterior areas to be paved with concrete slabs such as sidewalks and/or patios, it is recommended
that, at a minimum, the Undocumented Fill and Organic Soil be removed. The subgrade then needs to be
compacted to a minimum of 95 percent of its maximum dry density, as determined by ASTM D698. Then
for non-vehicular traffic areas, a minimum of 6 inches of 3/4-inch minus rock needs to be placed, and 4
inches of 4000 pounds per square inch (psi) concrete placed over the 3/4-inch minus rock. For areas with
vehicular traffic, a minimum of 9 inches of 3/4-inch minus rock should be placed, followed by 6 inches of
4000 psi concrete.
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 9 of 12
Exterior slabs that will be located adjacent to the foundation walls need to slope away from the structure
at a minimum grade of 2 percent and should not be physically connected to the foundation walls. If they
are connected, any movement of the exterior slab will be transmitted to the foundation wall, which may
result in damage to the structure.
Site Grading
Surface water should not be allowed to accumulate and infiltrate the soil near the foundation. Proper site
grading will ensure surface water runoff is directed away from the foundation elements and will aid in the
mitigation of excessive settlement. Please find the following as general site grading recommendations:
• Finished grade must slope away from the building a minimum of 5 percent within the first 10 feet,
in order to quickly drain ground surface and roof runoff away from the foundation walls. Please
note that in order to maintain this slope; it is imperative that any backfill placed against the
foundation walls be compacted properly. If the backfill is not compacted properly, it will settle and
positive drainage away from the structure will not be maintained.
• Permanent sprinkler heads for lawn care should be located a sufficient distance from the structure
to prevent water from draining toward the foundation or saturating the soils adjacent to the
foundation or adjacent to any paving improvements.
• Rain gutter down spouts are to be placed in such a manner that surface water runoff drains away
from the structure and any paving improvements.
• All roads, walkways, and architectural land features must properly drain away from all structures
and paving improvements. Special attention should be made during the design of these features
to not create any drainage obstructions that may direct water towards or trap water near the
foundation or paving improvements.
Asphalt Paving Improvements
For areas to be paved with asphalt, it is recommended that, as a minimum, the Undocumented fill and
Organic Soil be removed. The native subgrade then needs to be compacted at ± 2 percent of its optimum
moisture content to 95 percent of its maximum dry density. Following compaction of the native subgrade
a layer of separation geotextile shall be installed (such as a Mirafi 160N), followed by a 12-inch layer of
compacted 6-inch minus gravel, followed by a 6-inch layer of compacted 1-inch minus road mix. Both
gravel courses must be compacted at ± 2 percent of their optimum moisture content to 95 percent of their
maximum dry density. A 3-inch-thick layer of asphalt pavement can then be placed and compacted over
this cross-section.
It is recommended that following compaction of the native subgrade, a loaded dump truck or other heavy
piece of equipment should be driven over it to determine the stability of the subgrade. If any isolated soft
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 10 of 12
spots are found, these areas should be sub-excavated and replaced with compacted fill. If widespread
unstable conditions are present (i.e. significant rutting or pumping is observed) the sub-base component
of the road section will need to be increased and a geotextile may also be required, especially if moisture
related issues are the cause of the instability. In severe cases, geogrid may also be required.
If asphalt paving is to be placed on foundation wall backfill, it is imperative that the backfill be compacted
to a minimum of 95 percent of its maximum dry density, as determined by ASTM D698. The backfill must
be placed in uniform lifts and be compacted as described in the foundation wall backfill section of this
report.
Underground Utilities
We recommend specifying non-corrosive materials or providing corrosion protection due to the presence
of clay soils at the site.
It is recommended that 3/4-inch minus gravel be used as a bedding material, where bedding material is
defined as all material located within 6 inches of the utility pipe(s). The bedding material should be
thoroughly compacted around all utility pipes. Trench backfill shall be compacted to a minimum of 95
percent of its maximum dry density in paved or landscaped areas and a minimum of 97 percent of its
maximum dry density beneath foundation footings. Backfilling around and above utilities should meet the
requirements of Montana Public Works Standard Specifications.
Construction Administration
The foundation is a vital element of a structure; it transfers all of the structure's dead and live loads to the
native soil. It is imperative that the recommendations made in this report are properly adhered to. A
representative from IMEG should observe the construction of any foundation or drainage elements
recommended in this report. The recommendations made in this report are contingent upon our
involvement. If the soils encountered during the excavation differ than those described in this report or any
unusual conditions are encountered, our office should be contacted immediately to examine the conditions,
re-evaluate our recommendations and provide a written response.
If construction and site grading take place during cold weather, it is recommended that appropriate winter
construction practices be observed. All snow and ice shall be removed from cut and fill areas prior to site
grading taking place. No fill should be placed on soils that are frozen or contain frozen material. No frozen
soils can be used as fill under any circumstances. Additionally, Concrete should not be placed on frozen
soils and should meet the temperature requirements of ASTM C 94. Any concrete placed during cold
weather conditions shall be protected from freezing until the necessary compressive strength has been
attained. Once the footings are placed, frost shall not be permitted to extend below the foundation
footings, as this could heave and crack the foundation footings and/or foundation walls.
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Jonathan Stites—Geotechnical Investigation
February 25, 2025 Page 1 1 of 12
It is the responsibility of the contractor to provide a safe working environment with regards to excavations
on the site. All excavations should be sloped or shored in the interest of safety and in accordance with
local and federal regulations, including the excavation and trench safety standards provided by the
Occupational Safety and Health Administration (OSHA).
Report Limitations and Guidelines for Use
This report was prepared to be used exclusively by Jonathan Stites for commercial improvements to be
constructed on Lots 4-6, Block 20 of the Baxter Meadows Subdivision Phase 2A in Bozeman, Montana. All
of the work was performed in accordance with generally accepted principles and practices used by
geotechnical engineers and geologists practicing in this or similar localities. This report should not be used
by anyone it was not prepared for, or for uses it was not intended for. Field investigations and preparation
of this report was conducted in accordance with a specific set of requirements set out by the client, which
may not satisfy the requirements of others. This report should not be used for nearby sites or for structures
on the same site that differ from the structures that were proposed at the time this report was prepared.
Any changes in the structures (type, orientation, size, elevation, etc.) proposed for this site must be
discussed with our company for this report to be valid.
The recommendations made in this report are based upon data obtained from test pits excavated at the
locations indicated on the attached Test Pit Location Map. It is not uncommon that variations will occur
between these locations, the nature and extent of which will not become evident until additional
exploration or construction is conducted. These variations may result in additional construction costs, and
it is suggested that a contingency be provided for this purpose. If the soils encountered during the
excavation differ than those described in this report or any unusual conditions are encountered, our office
should be contacted immediately to examine the conditions and re-evaluate our recommendations and
provide a written response. This report is valid as a complete document only. No portion of this report
should be transmitted to other parties as an incomplete document. Misinterpretation of portions of this
report (i.e. test pit logs) is possible when this information is transmitted to others without the supporting
information presented in other portions of the report.
The scope of our investigation did not include an environmental assessment for determining the presence
or absence of hazardous or toxic materials on the site. If information regarding the potential presence of
hazardous materials on the site is desired, please contact us to discuss your options for obtaining this
information. If any questions arise with regards to any aspects of this report, please contact us at your
convenience to avoid misinterpretation. Costly mistakes due to misinterpretation of geotechnical reports
can usually be avoided by a quick phone call. If you have any questions or if you need further assistance
with your project, please contact the undersigned.
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Jonathan Stites —Geotechnical Investigation
February 25, 2025 Page 12 of 12
Sincerely
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CLIENT Jonathan Stites PROJECT NAME Geotechnical Investiqation
PROJECT NUMBER 24006453.00 PROJECT LOCATION Lots 4-6 Blk 20 Baster Meadows PH 2A
DATE STARTED 10/24/24 COMPLETED 10/24/24 GROUND ELEVATION
EXCAVATION CONTRACTOR Elevation Excavatinq GROUND WATER LEVELS:
EXCAVATION METHOD Bobcat E88 �AT TIME OF EXCAVATION 6.50 ft
LOGGED BY Michael J.Welch, P.E. AT END OF EXCAVATION ---
NOTES AFTER EXCAVATION ---
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CLIENT Jonathan Stites PROJECT NAME Geotechnical Investiqation
PROJECT NUMBER 24006453.00 PROJECT LOCATION Lots 4-6 Blk 20 Baster Meadows PH 2A
DATE STARTED 10/24/24 COMPLETED 10/24/24 GROUND ELEVATION
EXCAVATION CONTRACTOR Elevation Excavatinq GROUND WATER LEVELS:
EXCAVATION METHOD Bobcat E88 �AT TIME OF EXCAVATION 6.83 ft
LOGGED BY Michael J.Welch, P.E. AT END OF EXCAVATION ---
NOTES AFTER EXCAVATION ---
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CLIENT Jonathan Stites PROJECT NAME Geotechnical Investiqation
PROJECT NUMBER 24006453.00 PROJECT LOCATION Lots 4-6 Blk 20 Baster Meadows PH 2A
DATE STARTED 10/24/24 COMPLETED 10/24/24 GROUND ELEVATION
EXCAVATION CONTRACTOR Elevation Excavatinq GROUND WATER LEVELS:
EXCAVATION METHOD Bobcat E88 �AT TIME OF EXCAVATION 7.33 ft
LOGGED BY Michael J.Welch, P.E. AT END OF EXCAVATION ---
NOTES AFTER EXCAVATION ---
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