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HomeMy WebLinkAboutTAPESTRY - PDP240001 - SUBMITTAL DOCUMENTS - ROUND 1 - Drainage Related Document PRELIMINARY DRAINAGE REPORT TAPESTRY FORT COLLINS, COLORADO APRIL 24, 2024 EPSGROUPINC.COM NORTHERNENGINEERING.COM 970.221.4158 FORT COLLINS GREELEY This Drainage Report is consciously provided as a PDF. Please consider the environment before printing this document in its entirety. When a hard copy is necessary, we recommend double-sided printing. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth April 24, 2024 City of Fort Collins Stormwater Utility 700 Wood Street Fort Collins, CO 80521 RE: PRELIMINARY DRAINAGE REPORT FOR TAPESTRY Dear Staff: Northern Engineering/EPS Group is pleased to submit this Preliminary Drainage Report for your review. This report accompanies the preliminary submittal for the proposed Tapestry project. This report has been prepared in accordance with the Fort Collins Stormwater Criteria Manual (FCSCM) and serves to document the stormwater impacts associated with the project. We understand that review by the City of Fort Collins is to assure general compliance with standardized criteria contained in the FCSCM. If you should have any questions as you review this report, please feel free to contact us. Sincerely, NORTHERN ENGINEERING SERVICES, INC. STEPHANIE THOMAS, PE JACOB O’BANION, EIT Project Manager Project Engineer Compliance Statement I hereby attest that this report for the final drainage design for Tapestry was prepared by me or under my direct supervision, in accordance with the provisions of the Fort Collins Stormwater Criteria Manual. I understand that the City of Fort Collins does not and will not assume liability for drainage facilities designed by others. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth TABLE OF CONTENTS GENERAL LOCATION AND DESCRIPTION ................................................................. 1 DRAIN BASINS AND SUB-BASINS ............................................................................. 3 DRAINAGE DESIGN CRITERIA ................................................................................... 4 DRAINAGE FACILITY DESIGN .................................................................................... 6 CONCLUSIONS ......................................................................................................... 12 REFERENCES ............................................................................................................ 13 TABLES AND FIGURES FIGURE 1 – AERIAL PHOTOGRAPH ...................................................................................1 FIGURE 2 – FEMA FIRMETTE .............................................................................................3 FIGURE 3 – EXISTING CITY FLOODPLAINS .......................................................................3 TABLE 1 – RATIONAL CALCULATIONS SUMMARY ......................................................... 11 TABLE 2 - DETENTION SUMMARY .................................................................................. 12 APPENDICES APPENDIX A – HYDROLOGIC COMPUTATIONS APPENDIX B – HYDRAULIC CALCULATIONS APPENDIX C –WATER QUALITY/LID COMPUTATIONS APPENDIX D – EROSION CONTROL REPORT APPENDIX E – USDA SOILS REPORT APPENDIX F – SIGNED VARIANCE APPLICATION MAP POCKET DR1 – DRAINAGE EXHIBIT EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth GENERAL LOCATION AND DESCRIPTION A. LOCATION Vicinity Map The Tapestry project site is a parcel of land being a portion of the northeast ¼ of Section 12, Township 7 north, range 69 west of the 6th P.M. City of Fort Collins, County of Larimer, State of Colorado. The project site (refer to Figure 1) is bordered to the north by Buckingham Street and the New Belgium Brewery property; to the west by 3rd Street and an existing single-family residential area (Buckingham Neighborhood); to the south by Odell Brewing Company; and to the east by Colorado Iron and Metal. B. DESCRIPTION OF PROPERTY The project site is a ± 11.1-acre tract. The site is currently undeveloped and zoned as Industrial District (I). The existing groundcover consists of grass, dirt, and beet tailings with a few trees along the outer edge of the subject property. The existing topography is characterized by Loveland clay loam soil overlaid with a layer of beet tailings. The beet tailings consist of the residual material left behind from sugar beet processing, resulting in irregular mounds, depressions and ridges across the Figure 1 – Aerial Photograph EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth landscape. The presence of beet tailings adds an additional layer of complexity to the site’s drainage dynamics. In order to avoid considering the presence of the beet tailings when assessing the existing drainage conditions, a new surface was designed and approved by The City of Fort Collins with the beet tailings removed. This plan set is called “Utility Plans for Odell – North” and was approved on 01/09/2022. The topography from the approved design is the topography used to assess the existing drainage conditions for the subject property. Therefore the approved surface design of the beet tailing removal will be referred to as the existing surface throughout the the remainder of this report. The plans for the beet tailing removal surface are included as an attachment with this report. The existing on-site runoff generally drains from north to south across flat grades (e.g., < 1.00%). The site drains to an existing 6” pvc just north of the Odell Brewing Company parking lot and south of the subject property. The existing storm drain discharges to Lincoln Avenue. A geotechnical investigation was conducted on the project site in March of 2021 and ground water was found to be between 10-14 feet below the existing surface (prior to beet tailing removal). It was estimated that the general flow of the groundwater on site is to the southeast. According to the United States Department of Agriculture (USDA) Natural Resources Conservation Service (NRCS) Soil Survey, the site consists primarily of Loveland clay loams which fall into Hydrologic Soil Group C. The proposed development consists of 7 – 20-unit condominiums, open space, private alleys, and a connector local street that is a continuance of Logan Avenue from the west side of the site at 3 rd Street and ties into Buckingham Street as 4th Street, a connector local street. The proposed land use is Multi-Family Residential and two future development tracts. C. FLOODPLAIN The entirety of the subject property is located within the FEMA 500-yr floodplain (Zone X), LOMR 20-08-0643P effective 06/25/2021. FEMA has designated 3rd street (west of the subject property) and a large portion of the Odell site (south of the property as Reduced Flood Risk due to Levee (Zone X), LOMR 06-08B336P effective 04/19/2007. The entirety of the subject property is located within a City of Fort Collins Moderate Risk 100-yr floodplain. a) As per section 10-103 (9), Critical Facilities are prohibited in the floodplain. The definition of Critical Facilities includes facilities for at-risk populations (daycares, schools, nursing homes, etc.), facilities utilizing hazardous materials (gas stations, auto repair, laboratories), emergency services facilities (urgent care, hospitals, fire, police) and government services (municipal offices, library). A floodplain use permit is required prior to building permit issuance. b) Development within the floodplain must comply with Chapter 10 of the Municipal Code. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth Figure 2 – FEMA FIRMette Figure 3 – Existing City Floodplains EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth DRAIN BASINS AND SUB-BASINS A. MAJOR BASIN DESCRIPTION a) The Tapestry project is located within the Dry Creek Basin. The Dry Creek Basin is a tributary of the Cache la Poudre River. The basin begins near the Wyoming border, has a drainage area of about 62 square miles with a series of irrigation canals and reservoirs dominating the upper basin. The majority of the lower basin is developed and includes commercial, industrial and residential uses. Dry Creek enters Fort Collins near Willox Lane and College Avenue and flows through small remnants of ditches and channels until it joins the Cache la Poudre River near Mulberry Street and Timberline Road. The runoff from the Tapestry project generally flows from north to south and ultimately ends up within the Cache la Poudre River south of Lincoln Avenue. B. SUB-BASIN DESCRIPTION The project site is broken up into fifteen sub-basins. The B, C and D basins are captured by on-site inlets and conveyed through storm drains and are treated via Stormtech isolator chambers throughout the site and ultimately discharged to the proposed detention pond. The A, E, F, G and P basins are captured by on-site inlets and conveyed through storm drains or flow via concrete pans or sheet flow to the proposed detention pond. The project site has one outfall location which is the outfall structure on the southern end of the proposed detention pond. The flows from the site are conveyed from the proposed detention pond via storm sewer that ties into an existing storm drain in the northeast corner of the Odell property. The project site does not receive notable runoff from contiguous off-site properties. DRAINAGE DESIGN CRITERIA A. STORMWATER MANAGEMENT STRATEGY The overall stormwater management strategy employed with the Tapestry project utilizes the “Four Step Process” to minimize adverse impacts of urbanization on receiving waters. The following is a description of how the proposed development has incorporated each step. Step 1 – Employ Runoff Reduction Practices. The Tapestry project aims to reduce runoff peaks, volumes and pollutant loads from frequently occurring storm events (i.e., water quality (i.e., 80th percentile) and 2-year storm events) by implementing Low Impact Development (LID) strategies. Wherever practical, runoff will be routed across landscaped areas. The project has also implemented Stormtech isolator chambers throughout the site that serve to capture, treat and release runoff from new impervious areas. The project has also made an effort to increase the amount of open space wherever feasible on site in order to minimize imperviousness on-site. These LID practices reduce the overall amount of impervious area, while at the same time Minimizing Directly Connected Impervious Areas (MDCIA). The combined LID/MDCIA techniques will be implemented, where practical, throughout the development, thereby slowing runoff and increasing opportunities for infiltration. Step 2 – Implement BMPs that Provide a Water Quality Capture Volume (WQCV) with Slow Release. The efforts taken in Step 1 will help to minimize excess runoff from frequently occurring storm events; however, urban development of this intensity will still have stormwater runoff leaving the site. The primary water quality treatment will occur via Stormtech isolator chambers that will ultimately discharge to the proposed detention pond. In addition to LID treatment, traditional water quality treatment will be provided within the lower stages of the detention pond. Step 3 – Stabilize Drainageways. The Tapestry project aims to protect the existing Cache La Poudre River by limiting any increases beyond historical flow rates within the river. By utilizing a combination EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth of LID, traditional water quality treatment, and a detention pond. As such, the peak discharge from the Tapestry project will not be compounded with peak flow in the river. Furthermore, this project will pay a one-time stormwater development fee, as well as ongoing monthly utility fees, both of which help achieve citywide drainage stability. Step 4 – Implement Site Specific and Other Source Control BMPs. This step typically applies to industrial and commercial developments. This does not apply to this site. B. DEVELOPMENT CRITERIA REFERENCE AND CONSTRAINTS The site plan is constrained topographically on the north and west by Buckingham Street and 3 rd Street respectively, on the east side by the Colorado Iron and Metal property, and to the south by the Odell property. The site is constrained by the amount of beet tailing remediation that is required. Beet remediation will lower the existing site topography creating a sumped site. A substantial amount of fill will be required in order to allow the site to drain and to allow for detention and water quality treatment. C. HYDROLOGICAL CRITERIA The City of Fort Collins Rainfall Intensity-Duration-Frequency Curves, as depicted in Figure 3.4-1 of the FCSCM, serve as the source for all hydrologic computations associated with the Tapestry development. Data contained in Table 3.4-1 has been utilized for Rational Method runoff calculations. The Rational Method has been employed to compute stormwater runoff utilizing coefficients contained in Tables 4.1-2 and 4.1-3 of the FCSCM. Three separate design storms have been utilized to address distinct drainage scenarios. The first event analyzed is the “Minor,” or “Initial” Storm, which has a 2-year recurrence interval. The second event considered is the “Major Storm,” which has a 100-year recurrence interval. The final event analyzed was the 10-year recurrence interval for comparative analysis only. D. HYDRAULIC CRITERIA The drainage facilities proposed with the Tapestry development project are designed in accordance with criteria outlined in the Mile High Flood District’s “Urban Storm Drainage Criteria Manual” (UDFCD) and the Fort Collins Stormwater Criteria Manual (FCSCM). As stated in Section I.C, above, the subject property is located within the FEMA 500-yr floodplain and within the City moderate risk 100-yr floodplain. Therefore a floodplain use permit is required prior to building permit issuance and development within the floodplain must comply with Chapter 10 of the Municipal Code. E. CONFORMANCE WITH WATER QUALITY TREATMENT CRITERIA City Code requires that 100% of runoff from a project site receive some sort of water quality treatment. This project proposes to provide water quality treatment using underground Stormtech isolator chambers and traditional water quality within the lower stages of the detention pond. Through these methods 100% of the on-site area will be treated for water quality. F. CONFORMANCE WITH LOW IMPACT DEVELOPMENT (LID) The project site will conform with the requirement to treat a minimum of 75% of the proposed impervious surfaces using LID treatment from Stormtech isolator chambers. Please see Appendix C for LID design information, table, and exhibit(s). This project proposes to provide LID treatment by using EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth an underground infiltration gallery (aka – underground chambers) located throughout the project site. Stormtech isolator chambers are considered a LID treatment method. Due to the physical constraints associated with the project some areas cannot be captured and adequately routed to the Stormtech chambers. However, these areas are designated to receive water quality treatment within the proposed detention pond. G. SIZING OF WATER QUALITY AND LID FACILITIES Stormtech Isolator Chambers The Stormtech isolator chambers were sized by first determining the required water quality capture volume (WQCV) for each Stormtech isolator chamber. A 12-Hour drain time was used in these calculations. Once the WQCV was identified, the minimum number of chambers needed to achieve this volume was calculated. Using the FAA method, another volume calculation was performed utilizing the WQ flow rate into the chamber and calculated release rate through the fabric. The number of chambers has been increased as needed to confirm the resulting FAA volume is provided within the empty volume of the underground chambers. This is intended to ensure the chambers do not become overwhelmed in the water quality storm event before “discharging” flows into surrounding aggregates. A summary of these calculations and volumes can be found in Appendix C. While the purpose of these LID systems is to treat the water quality storm event, the Stormtech isolator chambers were designed to bypass flows from the major storm event. Each isolator row will have an inspection port and a Nyloplast basin at the end for easy maintenance and cleanout. Water Quality Extended Detention Traditional water quality treatment is provided for all areas not treated by LID or expected to be treated by LID in the future. The water quality extended detention volume was determined by first determining the tributary area that needs to be treated and its percent imperviousness. The tributary area used for determining the WQCV in the detention pond consists of basins A1, A2, E1, 25% of fully developed F1, 25% of fully developed G1, and P. A 40-hour drain time was used in this calculation. The WQCV was then multiplied by 1.2 per FCSCM. It is expected that the future developments within basins F1 and G1 will be required to treat the remaining 75% of their impervious area through an approved LID treatment. DRAINAGE FACILITY DESIGN A. GENERAL CONCEPT The main objective of the Tapestry project drainage design is to bring the project site into compliance with the Mile High Flood District’s “Urban Storm Drainage Criteria Manual” (UDFCD) and the Fort Collins Stormwater Criteria Manual (FCSCM). A list of tables and figures used within this report can be found in the Table of Contents at the front of the document. The tables and figures are located within the sections to which the content best applies. Drainage for the project site has been analyzed using fifteen (15) major storm event drainage sub- basins. Within those basins there are five (5) minor storm event drainage sub-basins. The minor storm event drainage sub-basins consist of only roofs. During major storm events the roof drains are assumed to be overwhelmed therefore the runoff from the roofs would be directed to the inlet EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth within the major basin. A small percentage of the flow would continue to the stormwater infrastructure for which the minor event subbasin is designated. During minor storm events these basins are assumed to drain to roof drains that are routed to storm infrastructure outside of the major basin. The drainage patterns anticipated for the sub-basins are further described below. Proposed Basins Basin A1 Basin A1 encompasses streets, buildings, landscape, and walks internal to the site. Runoff from Basin A1 is captured by inlets within Basin A1 and is conveyed to the proposed Detention Pond. The runoff from Basin A1 is accounted for in the detention volume and the extended water quality detention volume. Basin A2 Basin A2 encompasses streets, landscape, and walks internal to the site. Runoff from Basin A2 is captured by inlets within Basin A2 and is conveyed to the proposed Detention Pond. The runoff from Basin A2 is accounted for in the detention volume and the extended water quality detention volume. Basin B1 Basin B1 encompasses parking lots, buildings, landscape, and walks internal to the site. Runoff from Basin B1 is captured by inlets within Basin B1 and is conveyed to Underground Chambers 1 for water quality treatment. During a major storm event, the runoff from Basin B1 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin B1 is accounted for in the detention volume. Basin B2 Basin B2 encompasses parking lots, buildings, landscape, and walks internal to the site. Runoff from Basin B2 is captured by inlets within Basin B2 and is conveyed to Underground Chambers 1 for water quality treatment. During a major storm event, the runoff from Basin B2 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin B2 is accounted for in the detention volume. A small portion of Basin B2 is rerouted to storm infrastructure in Basin D1 during a water quality/minor storm event. Please see Basins D1.1 and D1.2 for more details. Basin C1 Basin C1 encompasses a portion of 3rd street, as well as, buildings, landscape, and walks internal to the site. Runoff from Basin C1 is captured by inlets within Basin C1 and is conveyed to Underground Chambers 2 for water quality treatment. During a major storm event, the runoff from Basin C1 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin C1 is accounted for in the detention volume. Basin C2 Basin C2 encompasses parking lots, buildings, landscape, and walks internal to the site. Runoff from Basin C2 is captured by inlets within Basin C2 and is conveyed to Underground Chambers 2 for water quality treatment. During a major storm event, the runoff from Basin C2 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin C2 is accounted for in the detention volume. Basin D1 Basin D1 encompasses parking lots, buildings, landscape, and walks internal to the site. Runoff from Basin D1 is captured by inlets within Basin D1 and is conveyed to Underground Chambers 3 for water quality treatment. During a major storm event, the runoff from Basin D1 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin D1 is accounted for in the detention volume. A small portion of Basin D1 is EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth rerouted to storm infrastructure in Basin C2 during a water quality/minor storm event. Please see Basin C2.1 for more details. Basin D2 Basin D2 encompasses parking lots, buildings, landscape, and walks internal to the site. Runoff from Basin D2 is captured by inlets within Basin D2 and is conveyed to Underground Chambers 4 for water quality treatment. During a major storm event, the runoff from Basin D2 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin D2 is accounted for in the detention volume. A small portion of Basin D2 is rerouted to storm infrastructure in Basin D1 during a water quality/minor storm event. Please see Basin D1.4 for more details. Basin D3 Basin D3 encompasses a park, buildings, landscape, and walks internal to the site. Runoff from Basin D3 is captured by inlets within Basin D3 and is conveyed to Underground Chambers 4 for water quality treatment. During a major storm event, the runoff from Basin D3 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin D3 is accounted for in the detention volume. A small portion of Basin D3 is rerouted to storm infrastructure in Basin D2 during a water quality/minor storm event. Please see Basin D1.3 for more details. Basin D4 Basin D4 encompasses streets, walks and landscape. Runoff from Basin D4 is captured by inlets within Basin D4 and is conveyed to Underground Chambers 4 for water quality treatment. During a major storm event, the runoff from Basin D4 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin D4 is accounted for in the detention volume. Basin D5 Basin D5 encompasses streets, walks and landscape. Runoff from Basin D5 is captured by inlets within Basin D5 and is conveyed to Underground Chambers 4 for water quality treatment. During a major storm event, the runoff from Basin D5 is routed over a weir that directs the flow through the downstream storm infrastructure to the Detention Pond. The runoff from Basin D5 is accounted for in the detention volume. Basin E1 Basin E1 encompasses a portion of Buckingham Street, as well as buildings, landscape, and walks internal to the site. Runoff from Basin E1 is captured by a sidewalk culvert within Basin E1 and is conveyed to the proposed Detention Pond. The runoff from Basin E1 is accounted for in the detention volume and the extended water quality detention volume. Basin F1 Basin F1 is considered undeveloped for the interim condition. In the interim condition, runoff will flow from west to east to a proposed drainage pan where it will be conveyed to the proposed Detention Pond. See Basin Future F1 for more information. Basin G1 Basin G1 is considered undeveloped for the interim condition. In the interim condition, runoff will continue, as historically, to flow off-site to storm infrastructure in the Odell parking lot. See Basin Future G1 for more information. Basin P Basin P is comprised of the detention pond. Runoff stored in the pond is discharged through an outlet structure and storm drain that ties into an existing storm drain southeast of the project site. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth Future Development Basins Basin Future F1 Basin Future F1 is considered to be commercial land use in the future condition. Runoff from this future developed basin is accounted for in the detention volume. Basin Future G1 Basin Future G1 is considered to be commercial land use in the future condition. Runoff from this future developed basin is accounted for in the detention volume. Minor Storm Event Basins Basin C2.1 Basin C2.1 is comprised entirely of a portion of roof within Basin D1. The runoff within this basin is expected to drain to the stormwater infrastructure in Basin D1 during a major event, but is expected to be directed to the stormwater infrastructure in Basin C2 during a water quality/minor event. Basin D1.1 Basin D1.1 is comprised entirely of a portion of roof within Basin B2. The runoff within this basin is expected to drain to the stormwater infrastructure in Basin B2 during a major event, but is expected to be directed to the stormwater infrastructure in Basin D1 during a water quality/minor event. Basin D1.2 Basin D1.2 is comprised entirely of a portion of roof within Basin B2. The runoff within this basin is expected to drain to the stormwater infrastructure in Basin B2 during a major event, but is expected to be directed to the stormwater infrastructure in Basin D1 during a water quality/minor event. Basin D1.3 Basin D1.3 is comprised entirely of a portion of roof within Basin D3. The runoff within this basin is expected to drain to the stormwater infrastructure in Basin D3 during a major event, but is expected to be directed to the stormwater infrastructure in Basin D1 during a water quality/minor event. Basin D1.4 Basin D1.4 is comprised entirely of a portion of roof within Basin D2. The runoff within this basin is expected to drain to the stormwater infrastructure in Basin D2 during a major event, but is expected to be directed to the stormwater infrastructure in Basin D1 during a water quality/minor event. Combined Basins Future The FUTURE basin consists of basins A1, A2, B1, B2, C1, C2, D1, D2, D3, D4, D5, E1, F1 FUTURE, G1 FUTURE, and P. This combined basin was used to determine the volume of the detention pond. WQCV The WQCV basin consists of basins A1, A2, E1, F1 FUTURE, G1 FUTURE, and P. This combined basin was used to determine the WQCV volume within the detention pond. Note that only 25% of F1 FUTURE and 25% of G1 FUTURE were used in determining the WQCV. UG1 The UG1 basin consists of basins B1 and B2. The runoff from this basin is conveyed to Underground Chambers 1 and was used in determining the size of Underground Chambers 1. UG2 The UG2 basin consists of basins C1 and C2. The runoff from this basin is conveyed to Underground Chambers 2. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth UG3 The UG3 basin consists of basin D1. The runoff from this basin is conveyed to Underground Chambers 3. UG4 The UG4 basin consists of basins D2, D3, D4 and D5. The runoff from this basin is conveyed to Underground Chambers 4 and was used in determining the size of Underground Chambers 4. UG1* The UG1* basin consists of basins B1 and B2. Note that Minor Basins D1.1 and D1.2 were subtracted from calculations of Basin B2. The runoff from this basin is conveyed to Underground Chambers 1 during the minor storm event. UG2* The UG2* basin consists of basins C1, C2 and C2.1. The runoff from this basin is conveyed to Underground Chambers 2 during the minor storm event. The runoff from this basin was used to determine the size of Underground Chambers 2. UG3* The UG3* basin consists of basins D1, D1.1, D1.2, D1.3, and D1.4. Note that Minor Basin C2.1 was subtracted from calculations of Basin D1. The runoff from this basin is conveyed to Underground Chambers 3 during the minor storm event. The runoff from this basin was used to determine the size of Underground Chambers 3. UG4* The UG4* basin consists of basins D2, D3, D4 and D5. Note that Minor Basin D1.3 was subtracted from the calculations of Basin D3 and Minor Basin D1.4 was subtracted from the calculations of D2. The runoff from this basin is conveyed to Underground Chambers 4 during the minor storm event. The underground chambers were sized to account for the most conservative scenario between the UG and UG* basins. Basin ID Design Point Total Area (acres) C2 C100 2-Yr Tc (min) 100-Yr Tc (min) Q2 (cfs) Q100 (cfs) Proposed Basins A1 a1 0.50 0.76 0.95 5.00 5.00 1.07 4.67 A2 a2 0.33 0.80 1.00 5.00 5.00 0.76 3.31 B1 b1 0.66 0.82 1.00 5.00 5.00 1.55 6.59 B2 b2 0.97 0.88 1.00 5.00 5.00 2.46 9.69 C1 c1 1.29 0.74 0.92 5.53 5.00 2.61 11.77 C2 c2 0.61 0.86 1.00 5.00 5.00 1.49 6.05 D1 d1 0.73 0.89 1.00 5.00 5.00 1.85 7.22 D2 d2 0.23 0.90 1.00 5.00 5.00 0.59 2.30 D3 d3 1.11 0.50 0.62 10.89 8.88 1.20 5.69 D4 d4 0.21 0.77 0.96 5.00 5.00 0.45 1.96 D5 d5 0.21 0.79 0.98 5.00 5.00 0.46 2.01 E1 e1 1.24 0.77 0.96 6.16 5.00 2.55 11.87 F1 f1 1.15 0.21 0.26 12.17 12.17 0.50 2.17 G1 g1 1.26 0.20 0.25 11.67 11.67 0.53 2.29 P p 1.49 0.21 0.26 10.67 10.09 0.67 3.00 Future Development Basins EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth Basin ID Design Point Total Area (acres) C2 C100 2-Yr Tc (min) 100-Yr Tc (min) Q2 (cfs) Q100 (cfs) F1 FUTURE f1 future 1.15 0.85 1.00 5.00 5.00 2.79 11.46 G1 FUTURE g1 future 1.26 0.85 1.00 5.00 5.00 3.05 12.51 Minor Storm Event Sub-Basins C2.1 c2.1 0.04 0.95 n/a 5.00 5.00 0.11 n/a D1.1 d1.1 0.01 0.95 n/a 5.00 5.00 0.04 n/a D1.2 d1.2 0.04 0.95 n/a 5.00 5.00 0.10 n/a D1.3 d1.3 0.16 0.95 n/a 5.00 5.00 0.43 n/a Combined Basins FUTURE future 11.98 0.71 0.89 11.13 7.80 18.23 91.89 WQCV wqcv 5.97 0.41 0.51 11.65 10.53 5.06 22.89 UG1 ug1 1.64 0.86 1.00 5.00 5.00 4.01 16.28 UG2 ug2 1.89 0.78 0.97 5.85 5.00 4.05 18.26 UG3 ug3 0.73 0.89 1.00 5.00 5.00 1.85 7.22 UG4 ug4 1.75 0.62 0.77 10.51 7.64 2.35 11.61 Combined Basins Minor Storm Event UG1* ug1* 1.59 0.86 n/a 5.00 N/A 3.87 n/a UG2* ug2* 1.94 0.78 n/a 5.82 N/A 4.16 n/a UG3* ug3* 0.97 0.91 n/a 5.00 N/A 2.50 n/a UG4* ug4* 1.52 0.57 n/a 11.46 N/A 1.83 n/a Table 1 – Rational Calculations Summary A full-size copy of the Drainage Exhibit can be found in the Map Pocket at the end of this report. B. SPECIFIC DETAILS The Tapestry project plan is constrained on the north and west by Buckingham Street and 3rd Street respectively, on the east side by the Colorado Iron and Metal property, and to the south by the Odell property. The site will be discharging from the proposed detention pond to an existing storm drain southeast of the project site. In order to reduce runoff peaks, volumes and pollutant loads from urbanizing areas, LID strategies and a detention pond are proposed. The Tapestry project proposes providing 100-year detention at a specified release rate of 0.20 cfs/acre and utilizing extended detention for water quality. Stormtech isolator chambers are proposed to treat on-site runoff and conform with LID practices established in the UDFCD and Fort Collins Stormwater Criteria Manual. Detention Pond Calculations: a) Detention Pond Calculations were done via FAA Modified method as described in Chapter 6, Section 2.3 in the City of Fort Collins Stormwater Criteria Manual. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth Pond ID Tributary Area (ac) Weighted Percent Imperviousness (%) Extended Detention WQCV (ac- ft) 100-Yr Detention Vol. (ac-ft) Total Pond Volume (ac-ft) 100-Yr Detention WSEL (ft) Final Release Rate (cfs) Detention Pond 11.98 66 0.10 2.85 2.95 4,949.44 2.40 Table 2 - Detention Summary CONCLUSIONS A. COMPLIANCE WITH STANDARDS The detention design proposed with the Tapestry project does comply with the City of Fort Collins’ Stormwater Criteria Manual. The drainage plan and stormwater management measures proposed with the Tapestry project are compliant with all applicable State and Federal regulations governing stormwater discharge. B. DRAINAGE CONCEPT The drainage design proposed with this project will effectively limit potential damage associated with its stormwater runoff. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth REFERENCES 1. City of Fort Collins Landscape Design Guidelines for Stormwater and Detention Facilities, November 5, 2009, BHA Design, Inc. with City of Fort Collins Utility Services. 2. Fort Collins Stormwater Criteria Manual, City of Fort Collins, Colorado, as adopted by Ordinance No. 159, 2018, and referenced in Section 26-500 of the City of Fort Collins Municipal Code. 3. Soils Resource Report for Larimer County Area, Colorado, Natural Resources Conservation Service, United States Department of Agriculture. 4. Urban Storm Drainage Criteria Manual, Volumes 1-3, Urban Drainage and Flood Control District, Wright-McLaughlin Engineers, Denver, Colorado, Revised January 2016. Mile High Flood District, Updated March 2024. 5. Phase 1 Environmental Site Assessment Odell Townhomes Corner of Buckingham and 3 rd Street Fort Collins, Colorado, Project No. FC10679-200 January 12, 2023, Fort Collins, Colorado. 6. Utility Plans for Odell -North, Northern Engineering, Approved January 9, 2022. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth APPENDIX A HYDROLOGIC COMPUTATIONS Runoff Coefficient1 Percent Impervious1 Project: Location: 0.95 100%Calc. By: 0.95 90%Date: 0.85 80% 0.80 80% 0.50 40% 0.50 40% 0.20 2% Basin ID Basin Area (sq.ft.) Basin Area (acres) Asphalt, Concrete (acres)Rooftop (acres)Commercial (acres)Gravel (acres)Recycled Asphalt (acres)Pavers (acres) Lawns, Clayey Soil, Flat Slope < 2% (acres) Percent Impervious C2*Cf Cf = 1.00 C5*Cf Cf = 1.00 C10*Cf Cf = 1.00 C100*Cf Cf = 1.25 A1 21,615 0.50 0.21 0.16 0.00 0.00 0.00 0.00 0.13 72% 0.76 0.76 0.76 0.95 A2 14,521 0.33 0.27 0.00 0.00 0.00 0.00 0.00 0.07 80% 0.80 0.80 0.80 1.00 B1 28,844 0.66 0.34 0.20 0.00 0.00 0.00 0.00 0.11 80% 0.82 0.82 0.82 1.00 B2 42,425 0.97 0.51 0.38 0.00 0.00 0.00 0.00 0.08 88% 0.88 0.88 0.88 1.00 C1 56,052 1.29 0.60 0.31 0.00 0.00 0.00 0.00 0.37 69% 0.74 0.74 0.74 0.92 C2 26,477 0.61 0.33 0.20 0.00 0.00 0.00 0.00 0.07 85% 0.86 0.86 0.86 1.00 D1 31,612 0.73 0.45 0.22 0.00 0.00 0.00 0.00 0.06 89% 0.89 0.89 0.89 1.00 D2 10,089 0.23 0.14 0.07 0.00 0.00 0.00 0.00 0.02 90% 0.90 0.90 0.90 1.00 D3 48,426 1.11 0.10 0.30 0.00 0.03 0.04 0.01 0.64 38% 0.50 0.50 0.50 0.62 D4 8,968 0.21 0.16 0.00 0.00 0.00 0.00 0.00 0.05 76% 0.77 0.77 0.77 0.96 D5 8,933 0.21 0.16 0.00 0.00 0.00 0.00 0.00 0.04 79% 0.79 0.79 0.79 0.98 E1 53,951 1.24 0.64 0.31 0.00 0.00 0.00 0.00 0.30 74% 0.77 0.77 0.77 0.96 F1 50,150 1.15 0.02 0.00 0.00 0.00 0.00 0.00 1.13 3% 0.21 0.21 0.21 0.26 G1 54,755 1.26 0.00 0.00 0.00 0.00 0.00 0.00 1.26 2% 0.20 0.20 0.20 0.25 P 64,852 1.49 0.02 0.00 0.00 0.00 0.00 0.00 1.47 3% 0.21 0.21 0.21 0.26 Total 521,669 11.98 3.94 2.16 0.00 0.03 0.04 0.01 5.80 50% 0.58 0.58 0.58 0.73 F1 FUTURE 50,150 1.15 0.00 0.00 1.15 0.00 0.00 0.00 0.00 80% 0.85 0.85 0.85 1.00 G1 FUTURE 54,755 1.26 0.00 0.00 1.26 0.00 0.00 0.00 0.00 80% 0.85 0.85 0.85 1.00 Total 104,905 2.41 0.00 0.00 2.41 0.00 0.00 0.00 0.00 80% 0.85 0.85 0.85 1.00 C2.1 1,794 0.04 0.00 0.04 0.00 0.00 0.00 0.00 0.00 90% 0.95 n/a n/a n/a D1.1 604 0.01 0.00 0.01 0.00 0.00 0.00 0.00 0.00 90% 0.95 n/a n/a n/a D1.2 1,554 0.04 0.00 0.04 0.00 0.00 0.00 0.00 0.00 90% 0.95 n/a n/a n/a D1.3 6,899 0.16 0.00 0.16 0.00 0.00 0.00 0.00 0.00 90% 0.95 n/a n/a n/a D1.4 3,221 0.07 0.00 0.07 0.00 0.00 0.00 0.00 0.00 90% 0.95 n/a n/a n/a Total 14,072 0.32 0.00 0.32 0.00 0.00 0.00 0.00 0.00 90% 0.95 0.95 0.95 1.00 FUTURE 521,669 11.98 3.92 2.16 2.41 0.03 0.04 0.01 3.41 66% 0.71 0.71 0.71 0.89 WQCV 259,845 5.97 1.13 0.47 0.60 0.00 0.00 0.00 1.96 35% 0.41 0.41 0.41 0.51 UG1 71,269 1.64 0.85 0.59 0.00 0.00 0.00 0.00 0.20 85% 0.86 0.86 0.86 1.00 UG2 82,529 1.89 0.94 0.51 0.00 0.00 0.00 0.00 0.44 74% 0.78 0.78 0.78 0.97 UG3 31,612 0.73 0.45 0.22 0.00 0.00 0.00 0.00 0.06 89% 0.89 0.89 0.89 1.00 UG4 76,415 1.75 0.55 0.37 0.00 0.03 0.04 0.01 0.75 54% 0.62 0.62 0.62 0.77 UG1* 69,110 1.59 0.85 0.54 0.00 0.00 0.00 0.00 0.20 84% 0.86 n/a n/a n/a UG2* 84,323 1.94 0.94 0.56 0.00 0.00 0.00 0.00 0.44 75% 0.78 n/a n/a n/a UG3* 42,096 0.97 0.45 0.46 0.00 0.00 0.00 0.00 0.06 90% 0.91 n/a n/a n/a UG4* 66,295 1.52 0.55 0.14 0.00 0.03 0.04 0.01 0.75 49% 0.57 n/a n/a n/a DEVELOPED RUNOFF COEFFICIENT CALCULATIONS Asphalt, Concrete Rooftop Commercial Recycled Asphalt Streets, Parking Lots, Roofs, Alleys, and Drives: Character of Surface:Tapestry Fort Collins J. Obanion April 23, 2024 Pavers Composite Runoff Coefficient2 1) Runoff coefficients per Tables 3.2-1 & 3.2 of the FCSM. Percent impervious per Tables 4.1-2 & 4.1-3 of the FCSM. Gravel Future Development Basins Proposed Basins Lawns and Landscaping: Combined Basins Minor Storm Event 7,8,9,10 Combined Basins 1,2,3,4,5,6 2) Composite Runoff Coefficient adjusted per Table 3.2-3 of the Fort Collins Stormwater Manual (FCSM). Lawns, Clayey Soil, Flat Slope < 2% USDA SOIL TYPE: C Minor Storm Event Sub-Basins Notes: 1) The FUTURE Basin consists of all the proposed basins and the two future developments in basins F1 and G1. This basin is a combinantion of Basins A1, A2, B1, B2, C1, C2, D1, D3, D4, D5, E1, F1 FUTURE, G1 FUTURE, & P. 2) The WQCV Basin consists of all the basins that will be treated for water quality via extended detention. This basin is a combination of Basins A1, A2, E1, 25% of F1 FUTURE,25% of G1 FUTURE, & P. 3) The UG1 Basin consists of basins B1 & B2 that will be treated through Stormtech Chambers. 4) The UG2 Basin consists of basins C1 & C2 that will be treated through Stormtech Chambers. 5) The UG3 Basin consists of basin D1 that will be treated through Stormtech Chambes. 6) The UG4 Basin consists of basins D2, D3, D4, & D5 that will be treated through Stormtech Chambers. 7) The UG1* Basin consists of basins B1 & B2 that will be treated through Stormtech Chambers. Note that Minor Basin D1.1 & D1.2 were subracted from basin B2 for this calculation. 8) The UG2* Basin consists of basins C1, C2 & Minor Basin C2.1 that will be treated through Stormtech Chambers. 9) The UG3* Basin consists of basins D1, Minor Basin D1.1, Minor Basin D1.2, Minor Basin D1.3 & Minor Basin D1.4 that will be treated through Stormtech Chambers. Note that Minor Basin C2.1 was subtracted from basin D1 for this calculation. 10) The UG4* Basin consists of basins D2, D3, D4, & D5 that will be treated through Stormtech Chambers. Note that Minor Basin D1.3 was subracted from basin D3 for this calculation. Page 1 of 1 Where: Length (ft) Elev Up Elev Down Slope (%) Ti 2-Yr (min) Ti 10-Yr (min) Ti 100-Yr (min) Length (ft) Slope (%)Surface n Flow Area3 (sq.ft.) WP3 (ft)R (ft)V (ft/s) Tt (min) Max. Tc (min) Comp. Tc 2-Yr (min) Tc 2-Yr (min) Comp. Tc 10-Yr (min) Tc 10-Yr (min) Comp. Tc 100-Yr (min) Tc 100-Yr (min) A1 a1 7 52.25 52.10 2.14%1.32 1.32 0.59 270 0.60% Gutter 0.012 3.61 19.18 0.19 3.16 1.42 11.54 2.74 5.00 2.74 5.00 2.02 5.00 A2 a2 26 53.40 51.82 6.08%1.57 1.57 0.53 220 0.60% Gutter 0.012 3.61 19.18 0.19 3.16 1.16 11.37 2.74 5.00 2.74 5.00 1.69 5.00 B1 b1 33 53.31 52.51 2.42%2.23 2.23 0.80 170 0.50% Valley Pan 0.012 6.00 10.25 0.59 6.14 0.46 11.13 2.69 5.00 2.69 5.00 1.26 5.00 B2 b2 17 53.42 53.01 2.41%1.24 1.24 0.57 295 0.50% Valley Pan 0.012 6.00 10.25 0.59 6.14 0.80 11.73 2.04 5.00 2.04 5.00 1.38 5.00 C1 c1 34 53.66 52.42 3.65%2.58 2.58 1.28 510 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 2.95 13.02 5.53 5.53 5.53 5.53 4.23 5.00 C2 c2 30 52.85 52.10 2.50%1.81 1.81 0.75 290 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 1.68 11.78 3.49 5.00 3.49 5.00 2.43 5.00 D1 d1 25 52.66 51.93 2.92%1.36 1.36 0.65 225 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 1.30 11.39 2.66 5.00 2.66 5.00 1.95 5.00 D2 d2 62 52 50.92 2.10%2.32 2.32 1.15 45 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 0.26 10.59 2.58 5.00 2.58 5.00 1.41 5.00 D3 d3 160 53.11 49.84 2.04%11.21 11.21 8.88 0 N/A 0.035 #N/A #N/A N/A N/A 0.00 10.89 11.21 10.89 11.21 10.89 8.88 8.88 D4 d4 10 53.51 53.20 3.10%1.36 1.36 0.58 280 0.60% Gutter 0.012 3.61 19.18 0.19 3.16 1.48 11.61 2.83 5.00 2.83 5.00 2.06 5.00 D5 d5 10 53.51 53.20 3.10%1.27 1.27 0.47 285 0.60% Gutter 0.012 3.61 19.18 0.19 3.16 1.50 11.64 2.77 5.00 2.77 5.00 1.97 5.00 E1 e1 32 53.67 52.43 3.88%2.22 2.22 0.92 611 0.40% Gutter 0.012 3.61 19.18 0.19 2.58 3.95 13.57 6.16 6.16 6.16 6.16 4.87 5.00 F1 f1 100 51.80 49.42 2.38%12.46 12.46 11.72 290 0.50% Valley Pan 0.012 6.00 10.25 0.59 6.14 0.79 12.17 13.24 12.17 13.24 12.17 12.51 12.17 G1 g1 300 51.00 49.00 0.67%33.37 33.37 31.52 0 N/A 0.035 #N/A #N/A N/A N/A 0.00 11.67 33.37 11.67 33.37 11.67 31.52 11.67 P p 115 52.39 45.60 5.90% 9.89 9.89 9.31 290 0.50% Valley Pan 0.012 6.00 10.25 0.59 6.14 0.79 12.25 10.67 10.67 10.67 10.67 10.09 10.09 F1 FUTURE f1 future 50 51.80 49.42 4.76%1.97 1.97 0.79 340 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 1.96 12.17 3.93 5.00 3.93 5.00 2.75 5.00 G1 FUTURE g1 future 100 56.60 52.17 4.43%2.85 2.85 1.14 200 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 1.16 11.67 4.00 5.00 4.00 5.00 2.29 5.00 C2.1 c2.1 45 - -33.00%0.59 N/A N/A 0 N/A 0.000 #N/A #N/A N/A N/A 0.00 10.25 5.00 5.00 5.00 5.00 5.00 5.00 D1.1 d1.1 45 - -33.00%0.59 N/A N/A 0 N/A 0.000 #N/A #N/A N/A N/A 0.00 10.25 5.00 5.00 5.00 5.00 5.00 5.00 D1.2 d1.2 45 - -33.00%0.59 N/A N/A 0 N/A 0.000 #N/A #N/A N/A N/A 0.00 10.25 5.00 5.00 5.00 5.00 5.00 5.00 D1.3 d1.3 45 - -33.00%0.59 N/A N/A 0 N/A 0.000 #N/A #N/A N/A N/A 0.00 10.25 5.00 5.00 5.00 5.00 5.00 5.00 D1.4 d1.4 45 - - 33.00%0.59 N/A N/A 0 N/A 0.000 #N/A #N/A N/A N/A 0.00 10.25 5.00 5.00 5.00 5.00 5.00 5.00 FUTURE future 160 53.11 49.84 2.04%7.18 7.18 3.85 611 0.40% Gutter 0.012 3.61 19.18 0.19 2.58 3.95 14.28 11.13 11.13 11.13 11.13 7.80 7.80 WQCV wqcv 115 52.39 45.60 5.90%7.71 7.71 6.58 611 0.40% Gutter 0.012 3.61 19.18 0.19 2.58 3.95 14.03 11.65 11.65 11.65 11.65 10.53 10.53 UG1 ug1 33 53.31 52.51 2.42%1.93 1.93 0.80 295 0.50% Valley Pan 0.012 6.00 10.25 0.59 6.14 0.80 11.82 2.73 5.00 2.73 5.00 1.60 5.00 UG2 ug2 45 53.66 52.42 2.76%2.91 2.91 1.17 510 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 2.95 13.08 5.85 5.85 5.85 5.85 4.12 5.00 UG3 ug3 25 52.66 51.93 2.92%1.36 1.36 0.65 225 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 1.30 11.39 2.66 5.00 2.66 5.00 1.95 5.00 UG4 ug4 160 53.11 49.84 2.04%9.01 9.01 6.14 285 0.60% Gutter 0.012 3.61 19.18 0.19 3.16 1.50 12.47 10.51 10.51 10.51 10.51 7.64 7.64 UG1* ug1*33 53.31 52.51 2.42%1.95 N/A N/A 295 0.50% Valley Pan 0.012 6.00 10.25 0.59 6.14 0.80 11.82 2.75 5.00 N/A N/A N/A N/A UG2* ug2*45 53.66 52.42 2.76%2.87 N/A N/A 510 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 2.95 13.08 5.82 5.82 N/A N/A N/A N/A UG3* ug3*25 52.66 51.93 2.92%1.26 N/A N/A 225 0.50% Gutter 0.012 3.61 19.18 0.19 2.88 1.30 11.39 2.56 5.00 N/A N/A N/A N/A UG4* ug4*160 53.11 49.84 2.04%9.96 N/A N/A 285 0.60% Gutter 0.012 3.61 19.18 0.19 3.16 1.50 12.47 11.46 11.46 N/A N/A N/A N/A Notes S = Longitudinal Slope, feet/feet R = Hydraulic Radius (feet) n = Roughness Coefficient V = Velocity (ft/sec) WP = Wetted Perimeter (ft) DEVELOPED TIME OF CONCENTRATION COMPUTATIONS Location: Maximum Tc:Overland Flow, Time of Concentration: Channelized Flow, Velocity: Channelized Flow, Time of Concentration: Tapestry Fort Collins J. Obanion April 23, 2024 Project: Calculations By: Date: Combined Basins Minor Storm Event Combined Basins Basin ID Design Point Overland Flow Channelized Flow Time of Concentration Future Development Basins Minor Storm Event Sub-Basins Proposed Basins (Equation 3.3-2 per Fort Collins Stormwater Manual)𝑇௜ =1.87 1.1−𝐶∗𝐶𝑓𝐿 𝑆ଵ ଷൗ 𝑉=1.49 𝑛∗𝑅ଶ/ଷ ∗𝑆(Equation 5-4 per Fort Collins Stormwater Manual) 𝑇𝑐=𝐿 180 + 10 (Equation 3.3-5 per Fort Collins Stormwater Manual) 𝑇𝑡=𝐿 𝑉∗ 60 (Equation 5-5 per Fort Collins 1) Add 4900 to all elevations. 2) Per Fort Collins Stormwater Manual, minimum Tc = 5 min. 3) Assume a water depth of 6" and a typical curb and gutter per Larimer County Urban Street Standard Detail 701 for curb and gutter channelized flow. Assume a water depth of 1', fixed side slopes, and a triangular swale section for grass channelized flow. Assume a water depth of 1', 4:1 side slopes, and a 2' wide valley pan for channelized flow in a valley pan. Page 1 of 1 Tc2 Tc10 Tc100 C2 C10 C100 I2 I10 I100 Q2 Q10 Q100 A1 a1 0.50 5.0 5.0 5.0 0.8 0.8 0.9 2.9 4.9 10.0 1.1 1.8 4.7 A2 a2 0.33 5.0 5.0 5.0 0.8 0.8 1.0 2.9 4.9 10.0 0.8 1.3 3.3 B1 b1 0.66 5.0 5.0 5.0 0.8 0.8 1.0 2.9 4.9 10.0 1.6 2.6 6.6 B2 b2 0.97 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 2.5 4.2 9.7 C1 c1 1.29 5.5 5.5 5.0 0.7 0.7 0.9 2.8 4.7 10.0 2.6 4.5 11.8 C2 c2 0.61 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 1.5 2.5 6.0 D1 d1 0.73 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 1.8 3.2 7.2 D2 d2 0.23 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 0.6 1.0 2.3 D3 d3 1.11 10.9 10.9 8.9 0.5 0.5 0.6 2.2 3.7 8.2 1.2 2.1 5.7 D4 d4 0.21 5.0 5.0 5.0 0.8 0.8 1.0 2.9 4.9 10.0 0.4 0.8 2.0 D5 d5 0.21 5.0 5.0 5.0 0.8 0.8 1.0 2.9 4.9 10.0 0.5 0.8 2.0 E1 e1 1.24 6.2 6.2 5.0 0.8 0.8 1.0 2.7 4.6 10.0 2.5 4.4 11.9 F1 f1 1.15 12.2 12.2 12.2 0.2 0.2 0.3 2.1 3.5 7.2 0.5 0.8 2.2 G1 g1 1.26 11.7 11.7 11.7 0.2 0.2 0.3 2.1 3.6 7.3 0.5 0.9 2.3 P p 1.49 10.7 10.7 10.1 0.2 0.2 0.3 2.2 3.7 7.7 0.7 1.2 3.0 F1 FUTURE f1 future 1.15 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 2.8 4.8 11.5 G1 FUTURE g1 future 1.26 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 3.0 5.2 12.5 C2.1 c2.1 0.04 5.0 5.0 5.0 1.0 n/a n/a 2.9 N/A N/A 0.1 n/a n/a D1.1 d1.1 0.01 5.0 5.0 5.0 1.0 n/a n/a 2.9 N/A N/A 0.0 n/a n/a D1.2 d1.2 0.04 5.0 5.0 5.0 1.0 n/a n/a 2.9 N/A N/A 0.1 n/a n/a D1.3 d1.3 0.16 5.0 5.0 5.0 1.0 n/a n/a 2.9 N/A N/A 0.4 n/a n/a D1.4 d1.4 0.07 5.0 5.0 5.0 1.0 n/a n/a 2.9 N/A N/A 0.2 n/a n/a FUTURE future 11.98 11.1 11.1 7.8 0.7 0.7 0.9 2.1 3.6 8.6 18.2 31.1 91.9 WQCV wqcv 5.97 11.7 11.7 10.5 0.4 0.4 0.5 2.1 3.6 7.6 5.1 8.6 22.9 UG1 ug1 1.64 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 4.0 6.8 16.3 UG2 ug2 1.89 5.9 5.9 5.0 0.8 0.8 1.0 2.8 4.7 10.0 4.1 6.9 18.3 UG3 ug3 0.73 5.0 5.0 5.0 0.9 0.9 1.0 2.9 4.9 10.0 1.8 3.2 7.2 UG4 ug4 1.75 10.5 10.5 7.6 0.6 0.6 0.8 2.2 3.7 8.6 2.3 4.0 11.6 UG1* ug1* 1.59 5.0 N/A N/A 0.9 n/a n/a 2.9 N/A N/A 3.9 n/a n/a UG2* ug2* 1.94 5.8 N/A N/A 0.8 n/a n/a 2.8 N/A N/A 4.2 n/a n/a UG3* ug3* 0.97 5.0 N/A N/A 0.9 n/a n/a 2.9 N/A N/A 2.5 n/a n/a UG4*ug4*1.52 11.5 N/A N/A 0.57 n/a n/a 2.1 N/A N/A 1.83 n/a n/a Proposed Basins Minor Storm Event Sub-Basins Date: Fort Collins Project: Location: Calc. By: Combined Basins Minor Storm Event DEVELOPED DIRECT RUNOFF COMPUTATIONS Intensity Flow (cfs) Tapestry J. Obanion April 23, 2024 Basin Design Point Intensity, I, from Fig. 3.4.1 Fort Collins Stormwater Manual. Rational Equation: Q = CiA (Equation 6-1 per MHFD) Area (acres) Runoff CTc (Min) Combined Basins Future Development Basins EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth APPENDIX B HYDRAULIC CALCULATIONS Pond No : P 100-yr 0.89 9.20 min 124002 ft3 11.98 acres 2.847 ac-ft Max Release Rate =2.40 cfs Time (min) Ft Collins 100-yr Intensity (in/hr) Inflow Volume (ft3) Outflow Adjustment Factor Qav (cfs) Outflow Volume (ft3) Storage Volume (ft3) 5 9.950 31827 1.00 2.40 719 31108 10 7.720 49387 1.00 2.40 1438 47950 15 6.520 62566 1.00 2.40 2156 60409 20 5.600 71650 1.00 2.40 2875 68775 25 4.980 79647 1.00 2.40 3594 76053 30 4.520 86748 1.00 2.40 4313 82435 35 4.080 91354 1.00 2.40 5032 86322 40 3.740 95704 1.00 2.40 5750 89954 45 3.460 99606 1.00 2.40 6469 93137 50 3.230 103317 1.00 2.40 7188 96129 55 3.030 106611 1.00 2.40 7907 98705 60 2.860 109778 1.00 2.40 8626 101152 65 2.720 113105 1.00 2.40 9344 103760 70 2.590 115983 1.00 2.40 10063 105920 75 2.480 118990 1.00 2.40 10782 108208 80 2.380 121805 1.00 2.40 11501 110304 85 2.290 124524 1.00 2.40 12220 112304 90 2.210 127243 1.00 2.40 12938 114304 95 2.130 129450 1.00 2.40 13657 115793 100 2.060 131785 1.00 2.40 14376 117409 105 2.000 134344 1.00 2.40 15095 119249 110 1.940 136519 1.00 2.40 15814 120705 115 1.890 139046 1.00 2.40 16532 122513 120 1.840 141253 1.00 2.40 17251 124002 *Note: Using the method described in FCSCM Chapter 6 Section 2.3 DETENTION POND CALCULATION; MODIFIED FAA METHOD w/ Ft Collins IDF Input Variables Results Required Detention Volume Fort Collins, Colorado 473-010 - Conceptual Tapestry Project Number : Project Name : Detention Pond A = Tc = Project Location : Design Point C = Design Storm Page 1 of 1 473-010_FAAModified Method Pond Stage-Storage Curve Proposed Detention Pond 437-010 Tapestry By: J. Obanion 4/18/2024 Stage (FT) Contour Area (SF) Volume (CU.FT.) Volume (AC-FT) 4,944.200 287.30 0.00 0.00 4,944.400 1,255.10 154.24 0.00 4,944.600 2,805.77 560.33 0.01 4,944.800 5,442.80 1385.18 0.03 4,945.000 8,527.89 2782.25 0.06 4,945.15 17,200.40 4330.00 0.10 WQV 4,945.200 12,178.27 4852.87 0.11 4,945.400 15,545.77 7625.27 0.18 4,945.600 18,869.08 11066.76 0.25 4,945.800 21,161.65 15069.83 0.35 4,946.000 22,924.85 19478.48 0.45 4,946.200 24,375.10 24208.48 0.56 4,946.400 25,576.80 29203.67 0.67 4,946.600 26,527.49 34414.09 0.79 4,946.800 27,433.93 39810.24 0.91 4,947.000 28,347.20 45388.35 1.04 4,947.200 29,267.29 51149.80 1.17 4,947.400 30,194.09 57095.94 1.31 4,947.600 31,127.72 63228.12 1.45 4,947.800 32,069.49 69547.84 1.60 4,948.000 33,019.80 76056.77 1.75 4,948.200 33,978.63 82756.61 1.90 4,948.400 34,945.98 89649.07 2.06 4,948.600 35,955.88 96739.26 2.22 4,948.800 37,088.20 104043.67 2.39 4,949.000 38,326.16 111585.10 2.56 4,949.200 39,667.93 119384.51 2.74 4,949.400 41,112.18 127462.52 2.93 4,949.44 41,297.36 128332.00 2.95 100-YR DETENTION 4,949.500 41,873.49 131611.80 3.02 EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth APPENDIX C WATER QUALITY/LID COMPUTATIONS Project Title Date: Project Number Calcs By: City Basins Facility ID 1 WQCV = Watershed inches of Runoff (inches)35% a = Runoff Volume Reduction (constant) i = Total imperviousness Ratio (i = Iwq/100)0.166 in 5.98 ac 0.0828 ac-ft 3609 cu. ft. 0.0994 ac-ft 4330 cu. ft. V = Water Quality Design Volume (ac-ft) WQCV = Water Quality Capture Volume (inches) A = Watershed Area (acres) V = V (120%) = A = Tapestry April 23, 2024 473-010 J. Obanion Fort Collins A1, A2, E1,F1,G1,P Drain Time a = i = WQCV = Figure EDB-2 - Water Quality Capture Volume (WQCV), 80th Percentile Runoff Event Detention Pond WQCV 0.212 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0 0. 1 0. 2 0. 3 0. 4 0. 5 0. 6 0. 7 0. 8 0. 9 1 WQ C V ( w a t e r s h e d i n c h e s ) Total Imperviousness Ratio (i = Iwq/100) Water Quality Capture Volume 6 hr 12 hr 24 hr 40 hr iii78.019.10.91aWQCV 23  iii78.019.10.91aWQCV 23  AV*12 WQCV    40 hr Project Title Date: Project Number Calcs By: City Basins Facility ID 0.8 WQCV = Watershed inches of Runoff (inches)84% a = Runoff Volume Reduction (constant) i = Total imperviousness Ratio (i = Iwq/100)0.303 in 1.64 ac 0.0414 ac-ft 1803 cu-ft 0.0497 ac-ft 2164 cu-ft V = Water Quality Design Volume (ac-ft) WQCV = Water Quality Capture Volume (inches) A = Watershed Area (acres) V = V (120%) = A = Figure EDB-2 - Water Quality Capture Volume (WQCV), 80th Percentile Runoff Event Tapestry April 23, 2024 473-010 J. Obanion Fort Collins B1 & B2 Drain Time a = i = WQCV = Underground Chamber 1 0.231 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0 0. 1 0. 2 0. 3 0. 4 0. 5 0. 6 0. 7 0. 8 0. 9 1 WQ C V ( w a t e r s h e d i n c h e s ) Total Imperviousness Ratio (i = Iwq/100) Water Quality Capture Volume 6 hr 12 hr 24 hr 40 hr iii78.019.10.91aWQCV 23  AV*12 WQCV    12 hrWQCV=(a 0.91𝑖ଷ − 1.19𝑖 ଶ + 0.78𝑖)1.067 Page 1 of 8 473-010 Stormtech Chambers Facility ID : B1 WQ 0.86 5.00 min 840 ft3 1.64 acres 0.02 ac-ft Max Release Rate =0.45 cfs Time (min)Fort Collins WQ Intensity (in/hr) Inflow Volume (ft3) Outflow Adjustment Factor QWQ (cfs) Outflow Volume (ft3) Storage Volume (ft3) 5 1.425 603 1.00 0.45 135 468 10 1.105 935 1.00 0.45 270 665 15 0.935 1187 1.00 0.45 405 782 20 0.805 1362 1.00 0.45 540 822 25 0.715 1513 1.00 0.45 675 838 30 0.650 1650 1.00 0.45 810 840 35 0.585 1733 1.00 0.45 945 788 40 0.535 1811 1.00 0.45 1080 731 45 0.495 1885 1.00 0.45 1215 670 50 0.460 1946 1.00 0.45 1350 596 55 0.435 2025 1.00 0.45 1485 540 60 0.410 2082 1.00 0.45 1620 462 65 0.385 2118 1.00 0.45 1755 363 70 0.365 2162 1.00 0.45 1890 272 75 0.345 2190 1.00 0.45 2025 165 80 0.330 2234 1.00 0.45 2160 74 85 0.315 2266 1.00 0.45 2295 -29 90 0.305 2323 1.00 0.45 2430 -107 95 0.290 2331 1.00 0.45 2565 -234 100 0.280 2369 1.00 0.45 2700 -331 105 0.270 2399 1.00 0.45 2835 -436 110 0.260 2420 1.00 0.45 2970 -550 115 0.255 2482 1.00 0.45 3105 -623 120 0.245 2488 1.00 0.45 3240 -752 DETENTION POND CALCULATION; MODIFIED FAA METHOD w/ Ft Collins IDF Input Variables Results ` Fort Collins, CO 473-010 Tapestry Project Number : Project Name : Underground Chamber 1 A = Tc = Project Location : Design Point C = Design Storm Page 2 of 8 473-010 Stormtech Chambers Project Title Date: Project Number Calcs By: City Basins Facility ID 0.8 WQCV = Watershed inches of Runoff (inches)75% a = Runoff Volume Reduction (constant) i = Total imperviousness Ratio (i = Iwq/100)0.256 in 1.94 ac 0.0413 ac-ft 1801 cu-ft 0.0496 ac-ft 2161 cu-ft V = Water Quality Design Volume (ac-ft) WQCV = Water Quality Capture Volume (inches) A = Watershed Area (acres) A = V = V (120%) = Drain Time a = i = WQCV = Figure EDB-2 - Water Quality Capture Volume (WQCV), 80th Percentile Runoff Event Tapestry April 23, 2024 473-010 J. Obanion Fort Collins C1, C2, C2.1 Underground Chamber 2 0.231 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0 0. 1 0. 2 0. 3 0. 4 0. 5 0. 6 0. 7 0. 8 0. 9 1 WQ C V ( w a t e r s h e d i n c h e s ) Total Imperviousness Ratio (i = Iwq/100) Water Quality Capture Volume 6 hr 12 hr 24 hr 40 hr iii78.019.10.91aWQCV 23  AV*12 WQCV    12 hrWQCV=(a 0.91𝑖ଷ − 1.19𝑖 ଶ + 0.78𝑖)1.067 Page 3 of 8 473-010 Stormtech Chambers Facility ID : C2 WQ 0.78 5.00 min 906 ft3 1.94 acres 0.02 ac-ft Max Release Rate =0.48 cfs Time (min)Fort Collins WQ Intensity (in/hr) Inflow Volume (ft3) Outflow Adjustment Factor QWQ (cfs) Outflow Volume (ft3) Storage Volume (ft3) 5 1.425 647 1.00 0.48 144 503 10 1.105 1003 1.00 0.48 288 715 15 0.935 1273 1.00 0.48 432 841 20 0.805 1462 1.00 0.48 576 886 25 0.715 1623 1.00 0.48 720 903 30 0.650 1770 1.00 0.48 864 906 35 0.585 1859 1.00 0.48 1008 851 40 0.535 1943 1.00 0.48 1152 791 45 0.495 2022 1.00 0.48 1296 726 50 0.460 2088 1.00 0.48 1440 648 55 0.435 2172 1.00 0.48 1584 588 60 0.410 2233 1.00 0.48 1728 505 65 0.385 2272 1.00 0.48 1872 400 70 0.365 2320 1.00 0.48 2016 304 75 0.345 2349 1.00 0.48 2160 189 80 0.330 2397 1.00 0.48 2304 93 85 0.315 2431 1.00 0.48 2448 -17 90 0.305 2492 1.00 0.48 2592 -100 95 0.290 2501 1.00 0.48 2736 -235 100 0.280 2542 1.00 0.48 2880 -338 105 0.270 2574 1.00 0.48 3024 -450 110 0.260 2597 1.00 0.48 3168 -571 115 0.255 2662 1.00 0.48 3312 -650 120 0.245 2669 1.00 0.48 3456 -787 C = Tc = A = Underground Chamber 2 Input Variables Results Design Point Design Storm ` Project Location : Fort Collins, CO DETENTION POND CALCULATION; MODIFIED FAA METHOD w/ Ft Collins IDF Project Number : 473-010 Project Name : Tapestry Page 4 of 8 473-010 Stormtech Chambers Project Title Date: Project Number Calcs By: City Basins Facility ID 0.8 WQCV = Watershed inches of Runoff (inches)90% a = Runoff Volume Reduction (constant) i = Total imperviousness Ratio (i = Iwq/100)0.343 in 0.97 ac 0.0277 ac-ft 1207 cu-ft 0.0332 ac-ft 1448 cu-ft V = Water Quality Design Volume (ac-ft) WQCV = Water Quality Capture Volume (inches) A = Watershed Area (acres) A = V = V (120%) = Drain Time a = i = WQCV = Figure EDB-2 - Water Quality Capture Volume (WQCV), 80th Percentile Runoff Event Tapestry April 23, 2024 473-010 J. Obanion Fort Collins D1, D1.1, D1.3, D1.4 Underground Chamber 3 0.231 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0 0. 1 0. 2 0. 3 0. 4 0. 5 0. 6 0. 7 0. 8 0. 9 1 WQ C V ( w a t e r s h e d i n c h e s ) Total Imperviousness Ratio (i = Iwq/100) Water Quality Capture Volume 6 hr 12 hr 24 hr 40 hr iii78.019.10.91aWQCV 23  AV*12 WQCV    12 hrWQCV=(a 0.91𝑖ଷ − 1.19𝑖 ଶ + 0.78𝑖)1.067 Page 5 of 8 473-010 Stormtech Chambers Facility ID : D1 WQ 0.91 5.00 min 529 ft3 0.97 acres 0.01 ac-ft Max Release Rate =0.28 cfs Time (min)Fort Collins WQ Intensity (in/hr) Inflow Volume (ft3) Outflow Adjustment Factor QWQ (cfs) Outflow Volume (ft3) Storage Volume (ft3) 5 1.425 377 1.00 0.28 84 293 10 1.105 585 1.00 0.28 168 417 15 0.935 743 1.00 0.28 252 491 20 0.805 853 1.00 0.28 336 517 25 0.715 947 1.00 0.28 420 527 30 0.650 1033 1.00 0.28 504 529 35 0.585 1084 1.00 0.28 588 496 40 0.535 1133 1.00 0.28 672 461 45 0.495 1180 1.00 0.28 756 424 50 0.460 1218 1.00 0.28 840 378 55 0.435 1267 1.00 0.28 924 343 60 0.410 1303 1.00 0.28 1008 295 65 0.385 1325 1.00 0.28 1092 233 70 0.365 1353 1.00 0.28 1176 177 75 0.345 1370 1.00 0.28 1260 110 80 0.330 1398 1.00 0.28 1344 54 85 0.315 1418 1.00 0.28 1428 -10 90 0.305 1454 1.00 0.28 1512 -58 95 0.290 1459 1.00 0.28 1596 -137 100 0.280 1483 1.00 0.28 1680 -197 105 0.270 1501 1.00 0.28 1764 -263 110 0.260 1515 1.00 0.28 1848 -333 115 0.255 1553 1.00 0.28 1932 -379 120 0.245 1557 1.00 0.28 2016 -459 C = Tc = A = Underground Chamber 3 Input Variables Results Design Point Design Storm ` Project Location : Fort Collins, CO DETENTION POND CALCULATION; MODIFIED FAA METHOD w/ Ft Collins IDF Project Number : 473-010 Project Name : Tapestry Page 6 of 8 473-010 Stormtech Chambers Project Title Date: Project Number Calcs By: City Basins Facility ID 0.8 WQCV = Watershed inches of Runoff (inches)54% a = Runoff Volume Reduction (constant) i = Total imperviousness Ratio (i = Iwq/100)0.186 in 1.75 ac 0.0271 ac-ft 1179 cu-ft 0.0325 ac-ft 1415 cu-ft V = Water Quality Design Volume (ac-ft) WQCV = Water Quality Capture Volume (inches) A = Watershed Area (acres) Figure EDB-2 - Water Quality Capture Volume (WQCV), 80th Percentile Runoff Event Tapestry April 23, 2024 473-010 J. Obanion Fort Collins D2, D3, D4, D5 Underground Chamber 4 A = V = V (120%) = Drain Time a = i = WQCV = 0.231 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0 0. 1 0. 2 0. 3 0. 4 0. 5 0. 6 0. 7 0. 8 0. 9 1 WQ C V ( w a t e r s h e d i n c h e s ) Total Imperviousness Ratio (i = Iwq/100) Water Quality Capture Volume 6 hr 12 hr 24 hr 40 hr iii78.019.10.91aWQCV 23  AV*12 WQCV    12 hrWQCV=(a 0.91𝑖ଷ − 1.19𝑖 ଶ + 0.78𝑖)1.067 Page 7 of 8 473-010 Stormtech Chambers Facility ID : D1 WQ 0.62 9.92 min 657 ft3 1.75 acres 0.02 ac-ft Max Release Rate =0.34 cfs Time (min)Fort Collins WQ Intensity (in/hr) Inflow Volume (ft3) Outflow Adjustment Factor QWQ (cfs) Outflow Volume (ft3) Storage Volume (ft3) 5 1.425 464 1.00 0.34 102 362 10 1.105 719 1.00 0.34 204 515 15 0.935 913 1.00 0.34 306 607 20 0.805 1048 1.00 0.34 408 640 25 0.715 1164 1.00 0.34 510 654 30 0.650 1269 1.00 0.34 612 657 35 0.585 1333 1.00 0.34 714 619 40 0.535 1393 1.00 0.34 816 577 45 0.495 1450 1.00 0.34 918 532 50 0.460 1497 1.00 0.34 1020 477 55 0.435 1558 1.00 0.34 1122 436 60 0.410 1601 1.00 0.34 1224 377 65 0.385 1629 1.00 0.34 1326 303 70 0.365 1663 1.00 0.34 1428 235 75 0.345 1684 1.00 0.34 1530 154 80 0.330 1719 1.00 0.34 1632 87 85 0.315 1743 1.00 0.34 1734 9 90 0.305 1787 1.00 0.34 1836 -49 95 0.290 1794 1.00 0.34 1938 -144 100 0.280 1823 1.00 0.34 2040 -217 105 0.270 1846 1.00 0.34 2142 -296 110 0.260 1862 1.00 0.34 2244 -382 115 0.255 1909 1.00 0.34 2346 -437 120 0.245 1914 1.00 0.34 2448 -534 Project Location : Fort Collins, CO DETENTION POND CALCULATION; MODIFIED FAA METHOD w/ Ft Collins IDF Project Number : 473-010 Project Name : Tapestry C = Tc = A = Underground Chamber 4 Input Variables Results Design Point Design Storm ` Page 8 of 8 473-010 Stormtech Chambers Vault ID Total Required WQ Volume (cf) Flow, WQ (cfs) Chamber Type Chamber Release Ratea (cfs) Chamber Volumeb (cf) Installed Chamber w/ Aggregatec (cf) Minimum No. of Chambersd Total Release Ratee (cfs) Required Storage Volume by FAA Method (cf) Minimum No. of Chambersf Provided Number of Chambers Provided Release Rate (cfs) Storage Provided within the Chambersg (cf) Total Installed System WQ Volumeh (cf) Chamber 1 2164 0.00 SC-740 0.024 45.90 67.65 32 0.45 840 19 32 0.75 1469 2165 Chamber 2 2161 0.00 SC-740 0.024 45.90 67.65 32 0.47 906 20 32 0.75 1469 2165 Chamber 3 1448 0.00 SC-740 0.024 45.90 67.65 22 0.28 529 12 22 0.52 1010 1488 Chamber 4 1415 0.00 SC-740 0.024 45.90 67.65 21 0.35 657 15 21 0.50 964 1421 a. Release rate per chamber, limited by flow through geotextile with accumulated sediment. b. Volume within chamber only, not accounting for void spaces in surrounding aggregate. c. Volume includes chamber and void spaces (30%) in surrounding aggregate, per chamber unit. d. Number of chambers required to provide full WQCV within total installed system, including aggregate. e. Release rate per chamber times number of chambers. f. Number of chambers required to provide required FAA storage volume stored within the chamber only (no aggregate storage). g. Volume provided in chambers only (no aggregate storage). This number must meet or exceed the required FAA storage volume. h. System volume includes total number of chambers, plus surrounding aggregate. This number must meet or exceed the required WQCV. Chamber Configuration Summary Page 1 of 1 473-010 Stormtech Chambers Flow Rate* 0.35 gpm/sf 1 cf =7.48052 gal 1 gallon =0.133680546 cf 1 GPM = 0.002228009 cfs *Flow rate based on 1/2 of Nov 07 QMAX in Figure 17 of UNH Testing Report Width (in)Length (in)Height (in)Floor Area (sf)Chamber Volume (cf)Chamber/Aggregate Volume (cf)Chamber Flow Rate SC-160 34.0 85.4 16.0 20.2 6.9 23.7 0.015723865 SC-310 34.0 85.4 16.0 20.2 14.7 25.7 0.015723865 SC-740 51.0 85.4 30.0 30.2 45.9 67.7 0.023585797 MC-3500 77.0 90.0 45.0 48.1 109.9 158.7 0.037528028 MC-4500 100.0 52.0 60.0 36.1 106.5 148.6 0.028158693 Chamber Dimensions Chamber Flow Rate Conversion (gpm/sf to cfs) Page 1 of 1 473-010 Stormtech Chambers Project Number:Project:Tapestry Project Location: Calculations By:Date:4/23/2024 Sq. Ft. Acres A1 21,615 0.50 72%n/a Traditional 15,472 A2 14,521 0.33 80%n/a Traditional 11,649 B1 28,844 0.66 80%Underground Chambers 1 Underground Detention 23,104 B2 42,425 0.97 88%Underground Chambers 1 Underground Detention 37,152 C1 56,052 1.29 69%Underground Chambers 2 Underground Detention 38,950 C2 26,477 0.61 85%Underground Chambers 2 Underground Detention 22,477 D1 31,612 0.73 89%Underground Chambers 3 Underground Detention 28,274 D2 10,089 0.23 90%Underground Chambers 4 Underground Detention 9,092 D3 48,426 1.11 38%Underground Chambers 4 Underground Detention 18,536 D4 8,968 0.21 76%Underground Chambers 4 Underground Detention 6,808 D5 8,933 0.21 79%Underground Chambers 4 Underground Detention 7,032 E1 53,951 1.24 74%n/a Traditional 31,777 F1 50,150 1.15 3%n/a Traditional 1,699 G1 54,755 1.26 2%n/a Traditional 1,095 P 64,852 1.49 3%n/a Traditional 2,048 Total 521,669 11.98 255,163 Sq. Ft. Acres Underground Chambers 1 71,269 1.64 85% 60,257 B1 & B2 Underground Detention Underground Chambers 2 82,529 1.89 74% 61,427 C1 & C2 Underground Detention Underground Chambers 3 31,612 0.73 89% 28,274 D1 Underground Detention Underground Chambers 4 76,415 1.75 54% 41,467 D2, D3, D4, & D5 Underground Detention Total 261,825 6.01 191,425 521,669 ft2 255,163 ft2 191,373 ft2 191,425 ft2 75.02%Percent Impervious Treated by LID 473-010 Fort Collins, Colorado J. Obanion Total New or Modified Impervious Area (ft2) Total Impervious Area Treated by LID 75% Required Minimum Area to be Treated by LID Total Area of Current Development Total New or Modified Impervious Area LID Site Summary - New Impervious Area LID ID LID Summary per Basin LID Summary Tributary Area Weighted % Impervious Subbasin ID Treatment TypeWQ Treatment Impervious Area (ft2) Water Quality Treatment via LID AreaBasin ID Percent Impervious WQ Treatment Type D EE D E VAULTCABLE D XX AC ACACAC ACAC D D D X / / / / / / / // / / / / / / // / / / / / / // / / / / / / / / / / / / / / // / / / / / / // / / / / / / // / / / / / / / DN DN DNDN DN DN DNDN DN DN DN DN DNDN D EE D E BUCKINGHAM STREET 3R D S T R E E T LOGAN STREET DETENTION POND LOGAN STREET A1 D4 B1 B2 C1 C2 D1 D2 D5 E1 F1 G1 P D3 A2 D1.2 C2.1 D1.1 D1.3 D1.4 A1 A2 B1 B2 C1 C2 D1 D2 D3 D5 E1 F1 G1 P C2.1 UNDERGROUND CHAMBERS 2 UNDERGROUND CHAMBERS 1 UNDERGROUND CHAMBERS 3 UNDERGROUND CHAMBERS 4 D4 DRAWN BY: SCALE: ISSUED: TAPESTRY SHEET NO: FORT COLLINS: 301 North Howes Street, Suite 100, 80521 GREELEY: 820 8th Street, 80631 E N G I N E E R N GI EHTRON R N 970.221.4158 northernengineering.com LID EXHIBIT J. OBanion 1in=120ft 04/24/2024 PROPOSED STORM SEWER PROPOSED CURB & GUTTER PROPERTY BOUNDARY PROPOSED INLET aDESIGN POINT DRAINAGE BASIN LABEL MAJOR EVENT DRAINAGE BASIN BOUNDARY A LEGEND: ( IN FEET ) 1 inch = ft. Feet0120120 120 AREA TREATED BY UNDERGROUND CHAMBERS 1 FOR DRAINAGE REVIEW ONLY NOT FOR CONSTRUCTION AREA TREATED BY UNDERGROUND CHAMBERS 2 AREA TREATED BY UNDERGROUND CHAMBERS 3 *SEE RATIONAL CALCS FOR IMPERVIOUS AREA CALCULATIONS AREA TREATED BY UNDERGROUND CHAMBERS 4 MINOR EVENT DRAINAGE BASIN BOUNDARY LID Site Summary - New Impervious Area Total Area of Current Development 521,669 ft2 Total New or Modified Impervious Area 255,163 ft2 75% Required Minimum Area to be Treated by LID 191,373 ft2 Total Impervious Area Treated by LID 191,425 ft2 Percent Impervious Treated by LID 75.02% EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth APPENDIX D EROSION CONTROL REPORT EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth EROSION CONTROL REPORT A comprehensive Erosion and Sediment Control Plan (along with associated details) has been included with the final construction drawings. It should be noted; however, any such Erosion and Sediment Control Plan serves only as a general guide to the Contractor. Staging and/or phasing of the BMPs depicted, and additional or different BMPs from those included may be necessary during construction, or as required by the authorities having jurisdiction. It shall be the responsibility of the Contractor to ensure erosion control measures are properly maintained and followed. The Erosion and Sediment Control Plan is intended to be a living document, constantly adapting to site conditions and needs. The Contractor shall update the location of BMPs as they are installed, removed, or modified in conjunction with construction activities. It is imperative to appropriately reflect the current site conditions at all times. The Erosion and Sediment Control Plan shall address both temporary measures to be implemented during construction, as well as permanent erosion control protection. Best Management Practices from the Volume 3, Chapter 7 – Construction BMPs will be utilized. Measures may include, but are not limited to, silt fencing and/or wattles along the disturbed perimeter, gutter protection in the adjacent roadways, and inlet protection at existing and proposed storm inlets. Vehicle tracking control pads, spill containment and clean-up procedures, designated concrete washout areas, dumpsters, and job site restrooms shall also be provided by the Contractor. Grading and Erosion Control Notes can be found on Sheet CS2 of the Utility Plans. The Final Utility Plans will also contain a full-size Erosion Control Plan as well as a separate sheet dedicated to Erosion Control Details. In addition to this report and the referenced plan sheets, the Contractor shall be aware of, and adhere to, the applicable requirements outlined in any existing Development Agreement(s) of record, as well as the Development Agreement, to be recorded prior to issuance of the Development Construction Permit. Also, the Site Contractor for this project may be required to secure a Stormwater Construction General Permit from the Colorado Department of Public Health and Environment (CDPHE), Water Quality Control Division – Stormwater Program, before commencing any earth disturbing activities. Prior to securing said permit, the Site Contractor shall develop a comprehensive Storm Water Management Plan (SWMP) pursuant to CDPHE requirements and guidelines. The SWMP will further describe and document the ongoing activities, inspections, and maintenance of construction BMPs. EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth APPENDIX E USDA SOILS REPORT United States Department of Agriculture A product of the National Cooperative Soil Survey, a joint effort of the United States Department of Agriculture and other Federal agencies, State agencies including the Agricultural Experiment Stations, and local participants Custom Soil Resource Report for Larimer County Area, ColoradoNatural Resources Conservation Service March 29, 2024 Preface Soil surveys contain information that affects land use planning in survey areas. They highlight soil limitations that affect various land uses and provide information about the properties of the soils in the survey areas. Soil surveys are designed for many different users, including farmers, ranchers, foresters, agronomists, urban planners, community officials, engineers, developers, builders, and home buyers. Also, conservationists, teachers, students, and specialists in recreation, waste disposal, and pollution control can use the surveys to help them understand, protect, or enhance the environment. Various land use regulations of Federal, State, and local governments may impose special restrictions on land use or land treatment. Soil surveys identify soil properties that are used in making various land use or land treatment decisions. The information is intended to help the land users identify and reduce the effects of soil limitations on various land uses. The landowner or user is responsible for identifying and complying with existing laws and regulations. Although soil survey information can be used for general farm, local, and wider area planning, onsite investigation is needed to supplement this information in some cases. Examples include soil quality assessments (http://www.nrcs.usda.gov/wps/ portal/nrcs/main/soils/health/) and certain conservation and engineering applications. For more detailed information, contact your local USDA Service Center (https://offices.sc.egov.usda.gov/locator/app?agency=nrcs) or your NRCS State Soil Scientist (http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/contactus/? cid=nrcs142p2_053951). Great differences in soil properties can occur within short distances. Some soils are seasonally wet or subject to flooding. Some are too unstable to be used as a foundation for buildings or roads. Clayey or wet soils are poorly suited to use as septic tank absorption fields. A high water table makes a soil poorly suited to basements or underground installations. The National Cooperative Soil Survey is a joint effort of the United States Department of Agriculture and other Federal agencies, State agencies including the Agricultural Experiment Stations, and local agencies. The Natural Resources Conservation Service (NRCS) has leadership for the Federal part of the National Cooperative Soil Survey. Information about soils is updated periodically. Updated information is available through the NRCS Web Soil Survey, the site for official soil survey information. The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or a part of an individual's income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require 2 alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA's TARGET Center at (202) 720-2600 (voice and TDD). To file a complaint of discrimination, write to USDA, Director, Office of Civil Rights, 1400 Independence Avenue, S.W., Washington, D.C. 20250-9410 or call (800) 795-3272 (voice) or (202) 720-6382 (TDD). USDA is an equal opportunity provider and employer. 3 Contents Preface....................................................................................................................2 How Soil Surveys Are Made..................................................................................5 Soil Map..................................................................................................................8 Soil Map................................................................................................................9 Legend................................................................................................................10 Map Unit Legend................................................................................................11 Map Unit Descriptions.........................................................................................11 Larimer County Area, Colorado......................................................................13 22—Caruso clay loam, 0 to 1 percent slope...............................................13 64—Loveland clay loam, 0 to 1 percent slopes...........................................14 References............................................................................................................16 4 How Soil Surveys Are Made Soil surveys are made to provide information about the soils and miscellaneous areas in a specific area. They include a description of the soils and miscellaneous areas and their location on the landscape and tables that show soil properties and limitations affecting various uses. Soil scientists observed the steepness, length, and shape of the slopes; the general pattern of drainage; the kinds of crops and native plants; and the kinds of bedrock. They observed and described many soil profiles. A soil profile is the sequence of natural layers, or horizons, in a soil. The profile extends from the surface down into the unconsolidated material in which the soil formed or from the surface down to bedrock. The unconsolidated material is devoid of roots and other living organisms and has not been changed by other biological activity. Currently, soils are mapped according to the boundaries of major land resource areas (MLRAs). MLRAs are geographically associated land resource units that share common characteristics related to physiography, geology, climate, water resources, soils, biological resources, and land uses (USDA, 2006). Soil survey areas typically consist of parts of one or more MLRA. The soils and miscellaneous areas in a survey area occur in an orderly pattern that is related to the geology, landforms, relief, climate, and natural vegetation of the area. Each kind of soil and miscellaneous area is associated with a particular kind of landform or with a segment of the landform. By observing the soils and miscellaneous areas in the survey area and relating their position to specific segments of the landform, a soil scientist develops a concept, or model, of how they were formed. Thus, during mapping, this model enables the soil scientist to predict with a considerable degree of accuracy the kind of soil or miscellaneous area at a specific location on the landscape. Commonly, individual soils on the landscape merge into one another as their characteristics gradually change. To construct an accurate soil map, however, soil scientists must determine the boundaries between the soils. They can observe only a limited number of soil profiles. Nevertheless, these observations, supplemented by an understanding of the soil-vegetation-landscape relationship, are sufficient to verify predictions of the kinds of soil in an area and to determine the boundaries. Soil scientists recorded the characteristics of the soil profiles that they studied. They noted soil color, texture, size and shape of soil aggregates, kind and amount of rock fragments, distribution of plant roots, reaction, and other features that enable them to identify soils. After describing the soils in the survey area and determining their properties, the soil scientists assigned the soils to taxonomic classes (units). Taxonomic classes are concepts. Each taxonomic class has a set of soil characteristics with precisely defined limits. The classes are used as a basis for comparison to classify soils systematically. Soil taxonomy, the system of taxonomic classification used in the United States, is based mainly on the kind and character of soil properties and the arrangement of horizons within the profile. After the soil 5 scientists classified and named the soils in the survey area, they compared the individual soils with similar soils in the same taxonomic class in other areas so that they could confirm data and assemble additional data based on experience and research. The objective of soil mapping is not to delineate pure map unit components; the objective is to separate the landscape into landforms or landform segments that have similar use and management requirements. Each map unit is defined by a unique combination of soil components and/or miscellaneous areas in predictable proportions. Some components may be highly contrasting to the other components of the map unit. The presence of minor components in a map unit in no way diminishes the usefulness or accuracy of the data. The delineation of such landforms and landform segments on the map provides sufficient information for the development of resource plans. If intensive use of small areas is planned, onsite investigation is needed to define and locate the soils and miscellaneous areas. Soil scientists make many field observations in the process of producing a soil map. The frequency of observation is dependent upon several factors, including scale of mapping, intensity of mapping, design of map units, complexity of the landscape, and experience of the soil scientist. Observations are made to test and refine the soil-landscape model and predictions and to verify the classification of the soils at specific locations. Once the soil-landscape model is refined, a significantly smaller number of measurements of individual soil properties are made and recorded. These measurements may include field measurements, such as those for color, depth to bedrock, and texture, and laboratory measurements, such as those for content of sand, silt, clay, salt, and other components. Properties of each soil typically vary from one point to another across the landscape. Observations for map unit components are aggregated to develop ranges of characteristics for the components. The aggregated values are presented. Direct measurements do not exist for every property presented for every map unit component. Values for some properties are estimated from combinations of other properties. While a soil survey is in progress, samples of some of the soils in the area generally are collected for laboratory analyses and for engineering tests. Soil scientists interpret the data from these analyses and tests as well as the field-observed characteristics and the soil properties to determine the expected behavior of the soils under different uses. Interpretations for all of the soils are field tested through observation of the soils in different uses and under different levels of management. Some interpretations are modified to fit local conditions, and some new interpretations are developed to meet local needs. Data are assembled from other sources, such as research information, production records, and field experience of specialists. For example, data on crop yields under defined levels of management are assembled from farm records and from field or plot experiments on the same kinds of soil. Predictions about soil behavior are based not only on soil properties but also on such variables as climate and biological activity. Soil conditions are predictable over long periods of time, but they are not predictable from year to year. For example, soil scientists can predict with a fairly high degree of accuracy that a given soil will have a high water table within certain depths in most years, but they cannot predict that a high water table will always be at a specific level in the soil on a specific date. After soil scientists located and identified the significant natural bodies of soil in the survey area, they drew the boundaries of these bodies on aerial photographs and Custom Soil Resource Report 6 identified each as a specific map unit. Aerial photographs show trees, buildings, fields, roads, and rivers, all of which help in locating boundaries accurately. Custom Soil Resource Report 7 Soil Map The soil map section includes the soil map for the defined area of interest, a list of soil map units on the map and extent of each map unit, and cartographic symbols displayed on the map. Also presented are various metadata about data used to produce the map, and a description of each soil map unit. 8 9 Custom Soil Resource Report Soil Map 44 9 3 2 5 0 44 9 3 2 9 0 44 9 3 3 3 0 44 9 3 3 7 0 44 9 3 4 1 0 44 9 3 4 5 0 44 9 3 4 9 0 44 9 3 5 3 0 44 9 3 2 5 0 44 9 3 2 9 0 44 9 3 3 3 0 44 9 3 3 7 0 44 9 3 4 1 0 44 9 3 4 5 0 44 9 3 4 9 0 44 9 3 5 3 0 494510 494550 494590 494630 494670 494710 494510 494550 494590 494630 494670 494710 40° 35' 33'' N 10 5 ° 3 ' 5 4 ' ' W 40° 35' 33'' N 10 5 ° 3 ' 4 4 ' ' W 40° 35' 23'' N 10 5 ° 3 ' 5 4 ' ' W 40° 35' 23'' N 10 5 ° 3 ' 4 4 ' ' W N Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84 0 50 100 200 300 Feet 0 20 40 80 120 Meters Map Scale: 1:1,570 if printed on A portrait (8.5" x 11") sheet. Soil Map may not be valid at this scale. MAP LEGEND MAP INFORMATION Area of Interest (AOI) Area of Interest (AOI) Soils Soil Map Unit Polygons Soil Map Unit Lines Soil Map Unit Points Special Point Features Blowout Borrow Pit Clay Spot Closed Depression Gravel Pit Gravelly Spot Landfill Lava Flow Marsh or swamp Mine or Quarry Miscellaneous Water Perennial Water Rock Outcrop Saline Spot Sandy Spot Severely Eroded Spot Sinkhole Slide or Slip Sodic Spot Spoil Area Stony Spot Very Stony Spot Wet Spot Other Special Line Features Water Features Streams and Canals Transportation Rails Interstate Highways US Routes Major Roads Local Roads Background Aerial Photography The soil surveys that comprise your AOI were mapped at 1:24,000. Warning: Soil Map may not be valid at this scale. Enlargement of maps beyond the scale of mapping can cause misunderstanding of the detail of mapping and accuracy of soil line placement. The maps do not show the small areas of contrasting soils that could have been shown at a more detailed scale. Please rely on the bar scale on each map sheet for map measurements. Source of Map: Natural Resources Conservation Service Web Soil Survey URL: Coordinate System: Web Mercator (EPSG:3857) Maps from the Web Soil Survey are based on the Web Mercator projection, which preserves direction and shape but distorts distance and area. A projection that preserves area, such as the Albers equal-area conic projection, should be used if more accurate calculations of distance or area are required. This product is generated from the USDA-NRCS certified data as of the version date(s) listed below. Soil Survey Area: Larimer County Area, Colorado Survey Area Data: Version 18, Aug 24, 2023 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: Jul 2, 2021—Aug 25, 2021 The orthophoto or other base map on which the soil lines were compiled and digitized probably differs from the background imagery displayed on these maps. As a result, some minor shifting of map unit boundaries may be evident. Custom Soil Resource Report 10 Map Unit Legend Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI 22 Caruso clay loam, 0 to 1 percent slope 2.1 15.9% 64 Loveland clay loam, 0 to 1 percent slopes 11.1 84.1% Totals for Area of Interest 13.3 100.0% Map Unit Descriptions The map units delineated on the detailed soil maps in a soil survey represent the soils or miscellaneous areas in the survey area. The map unit descriptions, along with the maps, can be used to determine the composition and properties of a unit. A map unit delineation on a soil map represents an area dominated by one or more major kinds of soil or miscellaneous areas. A map unit is identified and named according to the taxonomic classification of the dominant soils. Within a taxonomic class there are precisely defined limits for the properties of the soils. On the landscape, however, the soils are natural phenomena, and they have the characteristic variability of all natural phenomena. Thus, the range of some observed properties may extend beyond the limits defined for a taxonomic class. Areas of soils of a single taxonomic class rarely, if ever, can be mapped without including areas of other taxonomic classes. Consequently, every map unit is made up of the soils or miscellaneous areas for which it is named and some minor components that belong to taxonomic classes other than those of the major soils. Most minor soils have properties similar to those of the dominant soil or soils in the map unit, and thus they do not affect use and management. These are called noncontrasting, or similar, components. They may or may not be mentioned in a particular map unit description. Other minor components, however, have properties and behavioral characteristics divergent enough to affect use or to require different management. These are called contrasting, or dissimilar, components. They generally are in small areas and could not be mapped separately because of the scale used. Some small areas of strongly contrasting soils or miscellaneous areas are identified by a special symbol on the maps. If included in the database for a given area, the contrasting minor components are identified in the map unit descriptions along with some characteristics of each. A few areas of minor components may not have been observed, and consequently they are not mentioned in the descriptions, especially where the pattern was so complex that it was impractical to make enough observations to identify all the soils and miscellaneous areas on the landscape. The presence of minor components in a map unit in no way diminishes the usefulness or accuracy of the data. The objective of mapping is not to delineate pure taxonomic classes but rather to separate the landscape into landforms or landform segments that have similar use and management requirements. The delineation of such segments on the map provides sufficient information for the development of resource plans. If intensive use of small areas is planned, however, Custom Soil Resource Report 11 onsite investigation is needed to define and locate the soils and miscellaneous areas. An identifying symbol precedes the map unit name in the map unit descriptions. Each description includes general facts about the unit and gives important soil properties and qualities. Soils that have profiles that are almost alike make up a soil series. Except for differences in texture of the surface layer, all the soils of a series have major horizons that are similar in composition, thickness, and arrangement. Soils of one series can differ in texture of the surface layer, slope, stoniness, salinity, degree of erosion, and other characteristics that affect their use. On the basis of such differences, a soil series is divided into soil phases. Most of the areas shown on the detailed soil maps are phases of soil series. The name of a soil phase commonly indicates a feature that affects use or management. For example, Alpha silt loam, 0 to 2 percent slopes, is a phase of the Alpha series. Some map units are made up of two or more major soils or miscellaneous areas. These map units are complexes, associations, or undifferentiated groups. A complex consists of two or more soils or miscellaneous areas in such an intricate pattern or in such small areas that they cannot be shown separately on the maps. The pattern and proportion of the soils or miscellaneous areas are somewhat similar in all areas. Alpha-Beta complex, 0 to 6 percent slopes, is an example. An association is made up of two or more geographically associated soils or miscellaneous areas that are shown as one unit on the maps. Because of present or anticipated uses of the map units in the survey area, it was not considered practical or necessary to map the soils or miscellaneous areas separately. The pattern and relative proportion of the soils or miscellaneous areas are somewhat similar. Alpha-Beta association, 0 to 2 percent slopes, is an example. An undifferentiated group is made up of two or more soils or miscellaneous areas that could be mapped individually but are mapped as one unit because similar interpretations can be made for use and management. The pattern and proportion of the soils or miscellaneous areas in a mapped area are not uniform. An area can be made up of only one of the major soils or miscellaneous areas, or it can be made up of all of them. Alpha and Beta soils, 0 to 2 percent slopes, is an example. Some surveys include miscellaneous areas. Such areas have little or no soil material and support little or no vegetation. Rock outcrop is an example. Custom Soil Resource Report 12 Larimer County Area, Colorado 22—Caruso clay loam, 0 to 1 percent slope Map Unit Setting National map unit symbol: jpvt Elevation: 4,800 to 5,500 feet Mean annual precipitation: 13 to 15 inches Mean annual air temperature: 48 to 50 degrees F Frost-free period: 135 to 150 days Farmland classification: Prime farmland if irrigated Map Unit Composition Caruso and similar soils:85 percent Minor components:15 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Caruso Setting Landform:Flood-plain steps, stream terraces Landform position (three-dimensional):Tread Down-slope shape:Linear Across-slope shape:Linear Parent material:Mixed alluvium Typical profile H1 - 0 to 35 inches: clay loam H2 - 35 to 44 inches: fine sandy loam H3 - 44 to 60 inches: gravelly sand Properties and qualities Slope:0 to 1 percent Depth to restrictive feature:More than 80 inches Drainage class:Somewhat poorly drained Runoff class: High Capacity of the most limiting layer to transmit water (Ksat):Moderately low to moderately high (0.06 to 0.20 in/hr) Depth to water table:About 24 to 48 inches Frequency of flooding:Occasional Frequency of ponding:None Calcium carbonate, maximum content:5 percent Maximum salinity:Nonsaline to very slightly saline (0.0 to 2.0 mmhos/cm) Available water supply, 0 to 60 inches: Moderate (about 8.4 inches) Interpretive groups Land capability classification (irrigated): 3w Land capability classification (nonirrigated): 5w Hydrologic Soil Group: D Ecological site: R067BY036CO - Overflow Hydric soil rating: No Minor Components Loveland Percent of map unit:9 percent Custom Soil Resource Report 13 Landform:Terraces Ecological site:R067BY036CO - Overflow Hydric soil rating: Yes Fluvaquents Percent of map unit:6 percent Landform:Terraces Hydric soil rating: Yes 64—Loveland clay loam, 0 to 1 percent slopes Map Unit Setting National map unit symbol: jpx9 Elevation: 4,800 to 5,500 feet Mean annual precipitation: 13 to 15 inches Mean annual air temperature: 48 to 50 degrees F Frost-free period: 135 to 150 days Farmland classification: Prime farmland if irrigated Map Unit Composition Loveland and similar soils:90 percent Minor components:10 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Loveland Setting Landform:Flood plains, stream terraces Landform position (three-dimensional):Tread Down-slope shape:Linear Across-slope shape:Linear Parent material:Alluvium Typical profile H1 - 0 to 15 inches: clay loam H2 - 15 to 32 inches: loam H3 - 32 to 60 inches: very gravelly sand Properties and qualities Slope:0 to 1 percent Depth to restrictive feature:More than 80 inches Drainage class:Poorly drained Runoff class: Medium Capacity of the most limiting layer to transmit water (Ksat):Moderately high (0.20 to 0.60 in/hr) Depth to water table:About 18 to 36 inches Frequency of flooding:Occasional Frequency of ponding:None Calcium carbonate, maximum content:15 percent Maximum salinity:Very slightly saline to slightly saline (2.0 to 4.0 mmhos/cm) Available water supply, 0 to 60 inches: Moderate (about 7.5 inches) Custom Soil Resource Report 14 Interpretive groups Land capability classification (irrigated): 3w Land capability classification (nonirrigated): 3w Hydrologic Soil Group: C Ecological site: R067BY036CO - Overflow Hydric soil rating: No Minor Components Aquolls Percent of map unit:5 percent Landform:Swales Hydric soil rating: Yes Poudre Percent of map unit:5 percent Ecological site:R067BY036CO - Overflow Hydric soil rating: No Custom Soil Resource Report 15 References American Association of State Highway and Transportation Officials (AASHTO). 2004. Standard specifications for transportation materials and methods of sampling and testing. 24th edition. American Society for Testing and Materials (ASTM). 2005. Standard classification of soils for engineering purposes. ASTM Standard D2487-00. Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979. Classification of wetlands and deep-water habitats of the United States. U.S. Fish and Wildlife Service FWS/OBS-79/31. Federal Register. July 13, 1994. Changes in hydric soils of the United States. Federal Register. September 18, 2002. Hydric soils of the United States. Hurt, G.W., and L.M. Vasilas, editors. Version 6.0, 2006. Field indicators of hydric soils in the United States. National Research Council. 1995. Wetlands: Characteristics and boundaries. Soil Survey Division Staff. 1993. Soil survey manual. Soil Conservation Service. U.S. Department of Agriculture Handbook 18. http://www.nrcs.usda.gov/wps/portal/ nrcs/detail/national/soils/?cid=nrcs142p2_054262 Soil Survey Staff. 1999. Soil taxonomy: A basic system of soil classification for making and interpreting soil surveys. 2nd edition. Natural Resources Conservation Service, U.S. Department of Agriculture Handbook 436. http:// www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_053577 Soil Survey Staff. 2010. Keys to soil taxonomy. 11th edition. U.S. Department of Agriculture, Natural Resources Conservation Service. http:// www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_053580 Tiner, R.W., Jr. 1985. Wetlands of Delaware. U.S. Fish and Wildlife Service and Delaware Department of Natural Resources and Environmental Control, Wetlands Section. United States Army Corps of Engineers, Environmental Laboratory. 1987. Corps of Engineers wetlands delineation manual. Waterways Experiment Station Technical Report Y-87-1. United States Department of Agriculture, Natural Resources Conservation Service. National forestry manual. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ home/?cid=nrcs142p2_053374 United States Department of Agriculture, Natural Resources Conservation Service. National range and pasture handbook. http://www.nrcs.usda.gov/wps/portal/nrcs/ detail/national/landuse/rangepasture/?cid=stelprdb1043084 16 United States Department of Agriculture, Natural Resources Conservation Service. National soil survey handbook, title 430-VI. http://www.nrcs.usda.gov/wps/portal/ nrcs/detail/soils/scientists/?cid=nrcs142p2_054242 United States Department of Agriculture, Natural Resources Conservation Service. 2006. Land resource regions and major land resource areas of the United States, the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook 296. http://www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/? cid=nrcs142p2_053624 United States Department of Agriculture, Soil Conservation Service. 1961. Land capability classification. U.S. Department of Agriculture Handbook 210. http:// www.nrcs.usda.gov/Internet/FSE_DOCUMENTS/nrcs142p2_052290.pdf Custom Soil Resource Report 17 EPSGROUPINC.COM | NORTHERNENGINEERING.COM | 970.221.4158 Fort Collins | Greeley | Mesa | Tucson | Goodyear | Phoenix | Fort Worth MAP PACKET DR1 – HISTORIC DRAINAGE EXHIBIT DR2 – DEVELOPED DRAINAGE EXHIBIT S ELEC ELEC VAULT CABLE ELEC ELEC D CS W C S C S C S H Y D C S C S W W W W W W W W W W W W W W W W W FO FO G G G G G G G G G G G G G G G GWWWWWWWWWWWWWWWW G G G G G G G G G G G G G G G G G G W W W W W W W W W W W W W W W W W W W X X X X X X X X W W W W W W W W W W W W W W W W FO FO G G G G G G G G G G G G G G G GWWWWWWWWWWWWWWWW G G G G G G G G G G G G G G G G G G W W W W W W W W W W W W W W W W W W W X X X X X X X X AC ACACAC ACAC ELEC BRKR ELEC BRKR ELEC BRKRELEC BRKR D D ELEC BRKR ELEC BRKR ELEC BRKR ELEC BRKR ELEC BRKR H Y D D X X X X X UD UD UD UD UD DUCTILE IRON NYLOPLAST DUCTILE IRON NYLOPLAST X X D E E E D E E NEW BELGIUM BREWING CO INC 902 BUCKINGHAM STREET ALFREDO LOZANO 128 3RD STREET G AND A INVESTMENTS LLC 903 BUCKINGHAM STREET 20' DRAINAGE EASEMENT BY SEPARATE DOCUMENT REC. NO. ______________ / / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / / / / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / // / / / / / / / DN DN DNDN DN DN DNDN DN DN DN DN DNDN X X D E E E D E E BUCKINGHAM STREET 3R D S T R E E T (E X . 6 0 ' R O W ) LOGAN STREET LOGAN STREET (PRP. 63' ROW) 4T H S T R E E T (P R P . 6 2 ' R O W ) BUILDING 1 BUILDING 2 BUILDING 3 BUILDING 5 BUILDING 6 BUILDING 7 BUILDING 4 GAR. 1 GA R . 2 GAR. 3 A1 D4 B1 B2 C1 C2 D1 D2 D5 E1 F1 G1 P D3 A2 A1 A2 B1 B2 C1 C2 D1 D2 D3 D5 D4 E1 F1 G1 P DETENTION POND D1.2 C2.1 C2.1 D1.1 D1.3 D1.4 TIE INTO EXISTING MANHOLE EX. STORM MANHOLE RIM: 4947.73 INV IN (NE): 4943.26 15" PVC INV OUT: 4943.21 15" PVC EXISTING STORM INLET EXISTING STORM MANHOLE EXISTING STORM INLET TEMPORARY CONSTRUCTION EASEMENT REC. NO. 20090031970 PRIVATE ACCESS & UTILITY EASEMENT REC. NO. 20100026776 PROPOSED INLET PROPOSED INLET PROPOSED INLET PROPOSED INLET COMBINED INLET AND WEIR STRUCTURE PROPOSED INLET PROPOSED INLET PROPOSED INLET WEIR STRUCTURE UNDERGROUND CHAMBERS 2 UNDERGROUND CHAMBERS 1 UNDERGROUND CHAMBERS 3 UNDERGROUND CHAMBERS 4 WEIR STRUCTURE WEIR STRUCTURE SIDEWALK CULVERT PROPOSED DRAINAGE PAN SIDEWALK CULVERT PROPOSED OUTLET STRUCTURE PROPOSED INLET TRACT A OUTLOT Z TRACT B LOT 1 ODELL INVESTMENTS LLC 800 E LINCOLN AVE Sheet TA P E S T R Y Th e s e d r a w i n g s a r e in s t r u m e n t s o f s e r v i c e pr o v i d e d b y N o r t h e r n En g i n e e r i n g S e r v i c e s , I n c . an d a r e n o t t o b e u s e d f o r an y t y p e o f c o n s t r u c t i o n un l e s s s i g n e d a n d s e a l e d b y a P r o f e s s i o n a l E n g i n e e r i n th e e m p l o y o f N o r t h e r n En g i n e e r i n g S e r v i c e s , I n c . N O T F O R C O N S T R U C T I O N R E V I E W S E T of 13 FO R T C O L L I N S | G R E E L E Y | M E S A | G O O D Y E A R | T U C S O N | N O R T H P H O E N I X | F O R T W O R T H no r t h e r n e n g i n e e r i n g . c o m 97 0 . 2 2 1 . 4 1 5 8 C 600 DR A I N A G E E X H I B I T 13 CALL 2 BUSINESS DAYS IN ADVANCE BEFORE YOU DIG, GRADE, OR EXCAVATE FOR THE MARKING OF UNDERGROUND MEMBER UTILITIES. CALL UTILITY NOTIFICATION CENTER OF COLORADO Know what'sbelow. before you dig.Call R NORTH ( IN FEET ) 1 inch = ft. Feet05050 50 100 150 NORTH PROPOSED CONTOUR PROPOSED STORM SEWER PROPOSED SWALE EXISTING CONTOUR PROPOSED CURB & GUTTER PROPERTY BOUNDARY PROPOSED INLET A DESIGN POINT FLOW ARROW DRAINAGE BASIN LABEL MAJOR EVENT DRAINAGE BASIN BOUNDARY PROPOSED SWALE SECTION 11 NOTES: 1.REFER TO THE PRELIMINARY DRAINAGE REPORT FOR TAPESTRY, DATED APRIL 17, 2024 FOR ADDITIONAL INFORMATION. A LEGEND: FOR DRAINAGE REVIEW ONLY NOT FOR CONSTRUCTION MINOR EVENT DRAINAGE BASIN BOUNDARY DEVELOPED DRAINAGE SUMMARY Basin ID Design Point Total Area (acres)C2 C100 2-Yr Tc (min) 100-Yr Tc (min) Q2 (cfs) Q100 (cfs) Proposed Basins A1 a1 0.50 0.76 0.95 5.00 5.00 1.07 4.67 A2 a2 0.33 0.80 1.00 5.00 5.00 0.76 3.31 B1 b1 0.66 0.82 1.00 5.00 5.00 1.55 6.59 B2 b2 0.97 0.88 1.00 5.00 5.00 2.46 9.69 C1 c1 1.29 0.74 0.92 5.53 5.00 2.61 11.77 C2 c2 0.61 0.86 1.00 5.00 5.00 1.49 6.05 D1 d1 0.73 0.89 1.00 5.00 5.00 1.85 7.22 D2 d2 0.23 0.90 1.00 5.00 5.00 0.59 2.30 D3 d3 1.11 0.50 0.62 10.89 8.88 1.20 5.69 D4 d4 0.21 0.77 0.96 5.00 5.00 0.45 1.96 D5 d5 0.21 0.79 0.98 5.00 5.00 0.46 2.01 E1 e1 1.24 0.77 0.96 6.16 5.00 2.55 11.87 F1 f1 1.15 0.21 0.26 12.17 12.17 0.50 2.17 G1 g1 1.26 0.20 0.25 11.67 11.67 0.53 2.29 P p 1.49 0.21 0.26 10.67 10.09 0.67 3.00 Future Development Basins F1 FUTURE f1 future 1.15 0.85 1.00 5.00 5.00 2.79 11.46 G1 FUTURE g1 future 1.26 0.85 1.00 5.00 5.00 3.05 12.51 Minor Storm Event Sub-Basins C2.1 c2.1 0.04 0.95 n/a 5.00 5.00 0.11 n/a D1.1 d1.1 0.01 0.95 n/a 5.00 5.00 0.04 n/a D1.2 d1.2 0.04 0.95 n/a 5.00 5.00 0.10 n/a D1.3 d1.3 0.16 0.95 n/a 5.00 5.00 0.43 n/a Combined Basins FUTURE future 11.98 0.71 0.89 11.13 7.80 18.23 91.89 WQCV wqcv 5.97 0.41 0.51 11.65 10.53 5.06 22.89 UG1 ug1 1.64 0.86 1.00 5.00 5.00 4.01 16.28 UG2 ug2 1.89 0.78 0.97 5.85 5.00 4.05 18.26 UG3 ug3 0.73 0.89 1.00 5.00 5.00 1.85 7.22 UG4 ug4 1.75 0.62 0.77 10.51 7.64 2.35 11.61 Combined Basins Minor Storm Event UG1*ug1*1.59 0.86 n/a 5.00 N/A 3.87 n/a UG2*ug2*1.94 0.78 n/a 5.82 N/A 4.16 n/a UG3*ug3*0.97 0.91 n/a 5.00 N/A 2.50 n/a UG4*ug4*1.52 0.57 n/a 11.46 N/A 1.83 n/a POND SUMMARY TABLE Pond ID Tributary Area (ac) Avg. Percent Imperviousness (%) Extended Detention WQCV (ac-ft) 100-Yr Detention Vol. (ac-ft) 100-Yr Detention WSEL (ft) Peak Release (cfs) Detention Pond 11.98 66 0.10 2.95 4,949.44 2.40