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HomeMy WebLinkAboutPACIFIC COAST SUPPLY WAREHOUSE - FDP200019 - SUBMITTAL DOCUMENTS - ROUND 1 - DRAINAGE REPORTFINAL DRAINAGE AND EROSION CONTROL REPORT FOR PACIFIC COAST SUPPLY A TRACT OF LAND LOCATED IN THE SOUTHWEST QUARTER OF SECTION 3, TOWNSHIP 7 NORTH, RANGE 68 WEST OF THE 6TH P.M., CITY OF FORT COLLINS, COUNTY OF LARIMER, STATE OF COLORADO ZP#: Z19-050 September 2, 2020 FINAL DRAINAGE AND EROSION CONTROL REPORT FOR PACIFIC COAST SUPPLY A TRACT OF LAND LOCATED IN THE SOUTHWEST QUARTER OF SECTION 3, TOWNSHIP 7 NORTH, RANGE 68 WEST OF THE 6TH P.M., CITY OF FORT COLLINS, COUNTY OF LARIMER, STATE OF COLORADO ZP#: Z19-050 September 2, 2020 Prepared for: Pacific Coast 12860 W. Cedar Dr. lakewood, CO 80228 Contact: Stuart Nielson 303-659-2313 Prepared by: ZP Architects Engineers, Inc. 2727 Bryant Street, Suite 610 Denver, CO 80211 (303) 455-3322 William J. Logan, P.E. Project Engineer i Engineers Certification Statement “I hereby attest that this report for the final drainage design for the Pacific Coast Supply 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.” Registered Professional Engineer Date State of Colorado No.31705 ii TABLE OF CONTENTS PHASE II DRAINAGE REPORT I. GENERAL LOCATION AND DESCRIPTION A. Location ................................................................................................................. 1 B. Description of Property .......................................................................................... 2 II. DRAINAGE BASINS AND SUB-BASINS A. Major Basin Description ......................................................................................... 2 B. Sub-Basin Description ........................................................................................... 2 III. DRAINAGE DESIGN CRITERIA A. Regulations............................................................................................................ 3 B. Development Criteria Reference and Constraints ................................................. 3 C. Hydrological Criteria .............................................................................................. 3 D. Hydraulic Criteria ................................................................................................... 3 E. Waivers from the Criteria ....................................................................................... 4 IV. DRAINAGE FACILITY DESIGN A. General Concept ................................................................................................... 5 B. Specific Details ...................................................................................................... 6 V. EROSION and SEDIMENT CONTROL…………………………………………………...6 VI. CONCLUSIONS A. Compliance with Standards ................................................................................... 7 B. Drainage Concept .................................................................................................. 7 VI. LIST OF REFERENCES ............................................................................................ 8 APPENDIX A ................................................................................................................... 9 Hydrologic & Hydraulic Computations APPENDIX B ................................................................................................................. 24 Charts and Tables APPENDIX C ................................................................................................................ 33 FIRM Map, Drainage Plan iii I. GENERAL LOCATION AND DESCRIPTION A. Location The proposed Pacific Coast Supply building is located in a Tract of land located in the Southwest Quarter of Section 3, Township 7 North, Range 68 West of the 6th Principal Meridian, City of Fort Collins, County of Larimer, State of Colorado. The site is specifically located at 1012 NE I-25 Frontage Road. Vicinity Map A new structure is to be located north of the existing Pacific Coast Supply buildings. Site access is off Northeast I-25 Frontage Road to the west. To the north and east is cultivated land with further development beyond the boundary of the proposed site. To the south the property is separated from the cultivated property by an existing 30-feet public access right-of-way. A private irrigation ditch lies along the easterly boundary. The Larimer and Weld Canal also lies to the north and east of the property, (Reference 4). A number of easements exist within the proposed property improvements. The easements consist of a 20’ water line easement, and two 15’ and 10’ easements per the plate from the K-2 Industrial Park; no description of the last two is given. 1 B. Description of Property The site consists of two tracts for an approximate area of 4.263 acres. The existing southern tract is currently developed, and includes the three buildings used by Pacific Coast Supply. The recently obtained north tract is undeveloped and will contain most of the new improvements. The plan is to construct a new 20,000 square-foot metal building with approximately 42,955 square-feet of hard surfaces on both tracts. The proposed development will provide additional storage space for the Pacific Coast Supply operations. The existing topography of the site slopes over a combination of native and gravel yards from the east to the west at an average slope of 1.2%. New detention and access easements for detention, maintenance and fire access are proposed. The web soil survey describes the site soils primarily as Longmont Clay and Nunn Clay Loam to Satanta Loam with a Hydrologic Soil Group C and D. Group C/D soils have a slow infiltration rate when thoroughly wet, and consist chiefly of layers that impedes the downward movement of water or soils of moderately fine to fine texture (Reference appendix B for Soil Survey Map Information). The site also has a high water table per the Geotechnical Evaluation Report by American Geoservices (Reference 6). The Larimer and Weld Canal to the east and north flows easterly under I-25 to the west. An irrigation ditch lies along the easterly most boundary and will not be affected by the proposed improvements. II. DRAINAGE BASINS AND SUB-BASINS A. Major Basin Description The site is located within the Cooper Slough/Box Elder Basin Master Drainage Study. (Reference 3 and hereafter called Master). This site is located within a 100-year floodplain as defined by the Federal Emergency Management Agency Community Panel numbers 08069C1001F, (Reference 4) and 08069C0982F, (Reference 5), both dated December 19, 2006. B. Sub-Basin Description Both tracts currently surface drain to the west into the ditch along NE I-25 Frontage Road. Runoff into the ditch drains south and crosses under I-25 through a culvert leading to the west. Offsite runoff to the site is limited from the east basins labeled OS1 and OS2. 2 The proposed site improvements will collect and surface drain the majority of the site to a water quality Bioretention pond in the middle of the site. Stormwater, along with most of the site’s proposed improvements will be directed to the detention pond located at the northwest corner of the property. The runoff collected in the pond will be directed to the west into the frontage ditch. An existing sump condition exists along the frontage ditch near the northwest corner of the property. The low spot has been identified and corrected in the proposed plans. In order to correct the low spot, some minor over lot grading is needed at the northern neighbor’s southwest corner. III. DRAINAGE DESIGN CRITERIA A. Regulations The primary criteria for this development is the “Fort Collins Stormwater Criteria Manual”, (Reference 1 and hereafter called Criteria), and the Urban Drainage Flood Control District’s Urban Storm Drainage Criteria Manuals (Reference 2 and hereafter called Manual). B. Development Criteria References and Constraints The subject area is identified within the Master drainage study. In addition to the Criteria, additional physical site restraints are realized due to this property being partially developed with three buildings already on site. See waivers below. C. Hydrological Criteria The design rainfall for the runoff generated on-site was based on the Rational Method for the 2 and 100-year rainfall events for developed conditions as established in the Criteria and Manual. The runoff results are summarized on the Drainage Plan and in Appendix A. Rainfall intensities were determined from the Criteria by using the 1-hour point rainfall values of 0.82 in/hr for the 2-year storm event and 2.86 in/hr for the 100-year storm event. The detention and discharge limits are based on the 2-year historic runoff. D. Hydraulic Criteria The capacity of the detention facility is based on the FAA method outlined in the Criteria. The proposed Bioretention pond and Extended Drainage Basin water quality volumes are per the Manual. 3 E. Waivers from the Criteria The site contains unique conditions that make development per the Criteria with LID features extremely difficult. Within the proposed site, three existing buildings exist with floor elevations surveyed at 4973.00 feet, establishing an upper limit to design. At the other end, the need to eliminate the existing sump condition and still drain to the ditch establishes the lower design elevation at 4968.40 feet. The combination of full detention, an Extended Detention Basin, a Bioretention pond, an emergency overflow, and a free board forces the drainage facility within a vertical design limit of 4.6 feet. This is further reduced to 3.0 feet once a connection to the ditch is made and a freeboard is established. Due to the existing site limitations, five (5) variances are requested from the Criteria and Manual. 1. Section 3.1: “Minimum freeboard of 12” above 100-yr WSEL.” Variance: 9” of freeboard above 100-year water surface elevation will allow the Bioretention pond to drain directly to the detention pond in the event of flooding. 2. Section 3.1: “…maximum side slopes of four feet horizontal to one foot vertical (4:1) and stabilized…” Variance: The detention pond slopes are set at 3.5:1, interior only. This is in part due to the proposed building and its location to the existing water line easement on the east, and the requirements for landscaping along the frontage road. 3. Section 3.1: “…Detention basin bottoms shall have a minimum cross-slope … of two percent (2%) for vegetated surfaces …” Variance: The bottom of the pond is reduced to 1.60% slope to accommodate the required detention volumes. 4. Ground Cover of drainage pipe: Variance: Due to insufficient ground cover across the drive lane, a structural concrete box culvert is proposed to accommodate drainage between the Bioretention too the detention pond. 5. Section 2.3.7: “75% of all newly added or modified impervious area must be treated by LID techniques.” Variance: 72.6% of the new hard surfaces are directed to the Bioretention pond. Other new hard surfaces cannot be directed to the Bioretention pond 4 due to the vertical site constraints, and the inability to drain the southern side of the property around the existing buildings to the north. IV. DRAINAGE FACILITY DESIGN A. General Concept Currently the surface drains primarily over native vegetation and existing gravel from the east to west onto the frontage drainage ditch. The proposed improvements will maintain the same drainage patterns by collecting the majority of the improvements into the detention pond along the frontage road. Minor offsite runoff will contribute to the detention pond from basin OS1. Appendix B contains the tables and charts from the Criteria and the Manual. Rainfall is based on the rational method and the City’s rainfall intensities with the site grading divided into seven onsite drainage basins. Basins A through C and OS1 define the areas directly tributary to the detention pond. Basins of direct runoff are designated DRS, DRE, DRN, DRW and OS2 are limited to the perimeter areas about the site. Basin A: Basin A comprises of the center of the property and the east storage yard area. Water collected along with basin OS1 will drain first to the Bioretention pond before transferring to the detention pond. Basin B: Basin B consists of the north roof of the building. Water off the north roof is collected in underground drain lines and discharged in the detention near the northeast corner of the building. Basin C: Basin C contains the detention pond area. Water collected in basin C is combined with basins A, B and OS1 for design point DET, the emergency overflow weir. Basin DRS: The area of Direct Runoff South (DRS) represents the existing surfaces on the south side of the property. This runoff is existing and is not changed due to the proposed improvements. Basin DRE: Direct Runoff East (DRE) represents the small area of runoff intercepted by the existing irrigation ditch. The proposed improvements due not change the ditch are the surrounding banks along the easterly property line. 5 Basin DRN: The area of Direct Runoff North (DRN) represents the surface behind the building. The surface runoff to the north is over native vegetation and is insignificant. Basin DRW: The area of Direct Runoff West (DRW) represents the surface tributary to the frontage road. This are is the result of the berm created for the detention pond and the existing landscaped are south of the access drive lane. The detention facility is made up of four volumes. Two water quality volumes, and the 2-year and 100-year detention volumes. As part of the LID criteria, a Bioretention pond is proposed in the middle of basin A. 72.6% of the new hard surfaces are collected in the Bioretention pond. Water through the Bioretention pond is directed through a discharge box into a structural box culvert that leads to the detention pond. The detention pond consists of an Extended Detention Basin volume and the 2-year and 100-year detention volumes. The Extended Detention Basin is reduced by the Bioretention volume. A Forebay is established at the entrance to the Bioretention pond, and is based on the total detention area tributary to the detention pond. Specific volumes and elevations are tabulated in appendix A and on the drainage plan. The detention ponds outlet box uses a water quality plate to restrict runoff to a 40- hour discharge limit. The 2-year stormwater volume is in turn discharged through the water quality plate for a significant reduction in discharge. The 100-year volume is then controlled by a 5.625” inside diameter pipe at the bottom of the drainage box. Both storm release rates are based on the Criteria’s limit that the site shall not be drained faster than the 2-year historic limit. In the event the outlet box is blocked by debris, an emergency overflow weir is set at the 100-year water elevation of 4972.00 feet. This weir is designed to discharge the 100-year runoff (15.85 cfs) to the ditch along the frontage road. In addition, flood control from the Bioretention pond is managed both through the concrete box culvert, and over and through the drainage swale set across the drive lane. B. Specific Details Access and maintenance to the outlet structures and to the detention features is obtained from an access and drainage easement located off the frontage road. The area of access and detention is contained in the designated easement. V. EROSION and SEDIMENT CONTROL An erosion and sediment control plan has been provided in the final construction set. The plan addresses both temporary measures during construction during construction, as well as permanent erosion control protection. Best Management Practices (BMPs) from the UDFCD and the City Criteria have been utilized. The 6 following erosion control devices have been implemented for the project site: silt fencing along downstream perimeters, wattle protection along drainage ditch culverts, and at the outlet from the pond, a vehicle tracking control pad at the construction entrance, and a concrete washout location. Permanent erosion control is established with rip-rap at outfall points into and from the detention, and with the establishment of erosion control. VI. CONCLUSIONS A. Compliance with Standards The runoff calculations are based on the Criteria and Manual for the 2-year and 100-year storm recurrences. In addition, water quality volumes are provided in the form of a Bioretention pond and an Extended Detention Basin per the Manual. The storm detention volumes are based on the Modified FAA method for the 2-year and 100-year storm events. The emergency overflow and storm outlet pipe drain to the right-of-way and are sized for the 100-year storm event. B. Drainage Concept The drainage system has been designed to convey the developed runoff to the designated detention pond in a safe and effective manner. In addition, all on site flows as well as the detention pond and its components have been sized to transfer stormwater to the drainage ditch. The proposed release rates from the detention pond will reduce the peak runoff to the 2-year historic limit. In its current condition, runoff from the site runs un-detained. The improvements being made will detain a large amount of stormwater and reduce runoff from the site so that the 100-year storm event can be conveyed safely downstream. As a result, no negative impacts are anticipated to any downstream stormwater facilities. 7 VI. REFERENCES 1. “Fort Collins Stormwater Criteria Manual”, dated revised November 2017. 2. "Urban Storm Drainage Criteria Manual", by Urban Drainage and Flood Control District, Vol. 1 and 2 dated January 2016, and Vol. 3 dated November 2010. 3. “Cooper Slough/Box Elder Basin Master Drainage Study” 4. Federal Emergency Management Agency Community Panel Number 08069C1001F, dated December 19, 2006. 5. Federal Emergency Management Agency Community Panel Number 08069C0982F, dated December 19, 2006. 6. Geotechnical Evaluation Report, Project No. 0281-D20, by American Geoservices, dated June 30, 2020 8 APPENDIX A Hydrologic & Hydraulic Computations 9 Fort Collins Stormwater Rational Method Project Name: Pacific Coast Supply Coefficent Impervious Basin Surface Types C (%) Hard Surfaces Asphalt, Conc 0.95 100 Rooftops 0.95 90 Recycled Asphalt 0.80 80 Gravel or Pavers 0.50 40 Landscape (Lawns) Playgrounds 25 Lawns, Sandy Soil, Flat Slope < 2% 0.10 2 Lawns, Sandy Soil, Avg Slope 2-7% 0.15 2 Lawns, Sandy Soil, Steep Slope > 7% 0.20 2 Lawns, Clayey Soil, Flat Slope < 2% 0.20 2 Lawns, Clayey Soil, Avg Slope 2-7% 0.25 2 Lawns, Clayey Soil, Steep Slope >7% 0.35 2 Dominant Predevelopement NRCS Soils Group: C/D Asphalt Recycled Gravel or Lawns, Sandy Lawns, Clayey Area Area Total & Conc. Rooftops Asphalt Pavers Playgrnds Flat Average Steep Flat Average Steep Average Average Total Area Area Areas Areas Area Area Area Area Area Area Area Area Area Coeff. 1.00 1.00 1.00 1.10 1.20 1.25 Impervs Area Basin Description (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (sq.ft.) (C) C 2 C 5 C 10 C 25 C 50 C 100 (%) (acre) Basin A Center/Storage 86902 34883 16285 0 26657 0 0 0 0 9077 0 0 0.73 0.73 0.73 0.73 0.81 0.88 0.91 69.5 1.995 A B North Roof 10000 0 10000 0 0 0 0 0 0 0 0 0 0.95 0.95 0.95 0.95 1.00 1.00 1.00 90.0 0.230 B C West Front Area 21377 4415 0 0 0 0 0 0 0 16962 0 0 0.35 0.35 0.35 0.35 0.39 0.43 0.44 22.2 0.491 C DRS Direct Runoff South 39853 5773 4915 0 20108 0 0 0 0 9057 0 0 0.55 0.55 0.55 0.55 0.61 0.66 0.69 46.2 0.915 DRS DRE Direct Runoff East 2302 0 0 0 391 0 0 0 0 1911 0 0 0.25 0.25 0.25 0.25 0.28 0.30 0.31 8.5 0.053 DRE DRN Direct Runoff North 16484 0 0 0 11200 0 0 0 0 5284 0 0 0.40 0.40 0.40 0.40 0.44 0.48 0.50 27.8 0.378 DRN DRW Direct Runoff West 8757 697 0 0 0 0 0 0 0 8060 0 0 0.26 0.26 0.26 0.26 0.29 0.31 0.32 9.8 0.201 DRW OS1 Offsite 1 5329 0 0 0 0 0 0 0 0 5329 0 0 0.20 0.20 0.20 0.20 0.22 0.24 0.25 2.0 0.122 OS1 OS2 Offsite 2 15754 0 0 0 0 0 0 0 0 15754 0 0 0.20 0.20 0.20 0.20 0.22 0.24 0.25 2.0 0.362 OS2 Det Detention+EDB 118279 39298 26285 0 26657 0 0 0 0 26039 0 0 0.68 0.68 0.68 0.68 0.75 0.82 0.85 62.7 2.715 Det RG A+OS1 Rain Garden 92231 34883 16285 0 26657 0 0 0 0 14406 0 0 0.70 0.70 0.70 0.70 0.77 0.84 0.87 65.6 2.117 RG H Trib Historic 151151 0 0 0 0 0 0 0 0 151151 0 0 0.20 0.20 0.20 0.20 0.22 0.24 0.25 2.0 3.470 H Trib Sec. 6.0 Low Impact Development (LID) Option 2 Impervious Surfaces Pavement Roof Pavement Roof A Center/Storage 34883 13000 34883 13000 B North Roof 0 10000 0 0 C West Front Area 4415 0 0 0 DRS Direct Runoff South 2960 0 0 0 DRE Direct Runoff East 0 0 0 0 DRN Direct Runoff North 0 0 0 0 DRW Direct Runoff West 697 0 0 0 Sub-Totals = 42955 23000 34883 13000 Total New = 65955 sq.ft. Total Captured = 47883 sq.ft. Percent of New Hard Surfaces Tributary to RG = 72.6% Runoff Coefficients Frequency Adjustment Factor Cf Total New Hardsurfaces RG Cature Area 10 TIME OF CONCENTRATION Project Name: Pacific Coast Supply Calculated By: WJL DATE: 8/26/2020 SUB-BASIN INITIAL/OVERLAND INITIAL FINAL DATA TIME (t i ) TIME tc TOTAL t c ;t i +t t DESIGN C*Cf = AREA LENGTH SLOPE t i LENGTH SLOPE CHANNEL VEL. t t t i +t t LENGTH t c =(L/180)+10 minimum C5 (Ac) (ft) (ft/ft) (min) (ft) (ft/ft) CONSTANT (fps) (min) (min) (ft) (min) (min) (1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (12) (13) (14) A 0.73 1.99 204 0.014 40.51 143 0.007 20 1.69 1.41 41.93 347 11.93 11.93 B 0.95 0.23 50 0.020 7.31 7.31 50 10.28 7.31 C 0.35 0.49 183 0.029 61.57 61.57 183 11.02 11.02 DRS 0.55 0.91 198 0.015 58.22 58.22 198 11.10 11.10 DRE 0.25 0.05 25 0.060 20.28 20.28 25 10.14 10.14 DRN 0.40 0.38 55 0.073 23.13 23.13 55 10.31 10.31 DRW 0.26 0.20 27 0.040 23.87 23.87 27 10.15 10.15 OS1 0.20 0.12 183 0.011 102.59 102.59 183 11.02 11.02 OS2 0.20 0.36 102 0.010 79.42 79.42 102 10.57 10.57 Det 0.68 2.72 204 0.014 46.06 367 0.005 20 1.41 4.33 50.38 571 13.17 13.17 RG 0.70 2.12 204 0.014 43.92 142 0.006 20 1.55 1.53 45.45 346 11.92 11.92 H Trib 0.20 4.26 300 0.012 126.25 228 0.012 10 1.11 3.42 129.67 528 12.93 12.93 t i =1.87(1.1-CxCf)(L^0.5)/S^1/3 t t =L/(60V) t c CHECK (URBANIZED BASINS) TRAVEL TIME (t t ) 11 STANDARD FORM SF-3 Calculated By: WJL JOB NO: Z19-050 DATE: STORM DRAINAGE SYSTEM DESIGN PROJECT : Name CHECKED BY:______________ (RATIONAL METHOD PROCEDURE) DESIGN STORM: 2 Year AREA DESIGN AREA (AC) RUNOFF COEFF tc (MIN) C*A (AC) I (IN/HR) Q (CFS) tc (MIN) SUM(C*A) (AC) I (IN/HR) Q (CFS) SLOPE (%) STREET FLOW(CFS) DESIGN FLOW (CFS) SLOPE (%) PIPE SIZE (IN) LENGTH (FT) VELOCITY (FPS) tt (MIN) (1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (13) (14) (15) (16) (17) (18) (19) (20) (21) (22) 1 AAA 1.99 0.73 11.9 1.46 2.05 3.01 11.0 1.49 2.12 3.16 2 BBB 0.23 0.95 7.3 0.22 2.48 0.54 3 CCC 0.49 0.35 11.0 0.17 2.12 0.37 4 5 DRS DRS DRS 0.91 0.55 11.1 0.51 2.12 1.07 6 DRE DRE DRE 0.05 0.25 10.1 0.01 2.20 0.03 7 DRN DRN DRN 0.38 0.40 10.3 0.15 2.18 0.33 8 DRW DRW DRW 0.20 0.26 10.2 0.05 2.20 0.11 9 OS1 OS1 OS1 0.12 0.20 11.0 0.02 2.12 0.05 10 OS2 OS2 OS2 0.36 0.20 10.6 0.07 2.16 0.16 11 Det Det Det 2.72 0.68 13.2 1.86 1.97 3.65 12 RG RG RG 2.12 0.70 11.9 1.49 2.06 3.06 13 14 H Trib H Trib H Trib 3.47 0.20 12.9 0.69 1.98 1.38 STREET DESIGN POINT STANDARD FORM SF-3 Calculated By: WJL JOB NO: Z19-050 DATE: STORM DRAINAGE SYSTEM DESIGN PROJECT : Name CHECKED BY:______________ (RATIONAL METHOD PROCEDURE) DESIGN STORM: 100 Year AREA DESIGN AREA (AC) RUNOFF COEFF tc (MIN) C*A (AC) I (IN/HR) Q (CFS) tc (MIN) SUM(C*A) (AC) I (IN/HR) Q (CFS) SLOPE (%) STREET FLOW(CFS) DESIGN FLOW (CFS) SLOPE (%) PIPE SIZE (IN) LENGTH (FT) VELOCITY (FPS) tt (MIN) (1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (13) (14) (15) (16) (17) (18) (19) (20) (21) (22) 1 AAA 1.99 0.91 11.9 1.82 7.17 13.1 11.9 1.85 7.17 13.3 2 BBB 0.23 1.00 7.3 0.23 8.63 2.0 3 CCC 0.49 0.44 11.0 0.22 7.41 1.6 4 5 DRS DRS DRS 0.91 0.69 11.1 0.63 7.39 4.6 6 DRE DRE DRE 0.05 0.31 10.1 0.02 7.66 0.1 7 DRN DRN DRN 0.38 0.50 10.3 0.19 7.61 1.4 8 DRW DRW DRW 0.20 0.32 10.2 0.06 7.66 0.5 9 OS1 OS1 OS1 0.12 0.25 11.0 0.03 7.41 0.2 10 OS2 OS2 OS2 0.36 0.25 10.6 0.09 7.54 0.7 11 Det Det Det 2.72 0.85 13.2 2.31 6.86 15.9 12 RG RG RG 2.12 0.87 11.9 1.85 7.17 13.3 13 12 H Trib H Trib H Trib 3.47 0.25 12.9 0.86 6.92 6.0 STREET PIPE TRAVEL TIME STREET REMARKS DESIGN Fort Collins Modified FAA Detention Project Name: Pacific Coast Supply Design Informtion (Input): Tributary Area: 2.72 sq.ft. Imperviousness: 62.68 % Tc: 1.38 min. Allowable Release Rate Qout: 1.38 cfs (2-year Historic) Allowable Release Rate Qout: 1.38 cfs (2-year Historic) 2-Year Minor Detention 100-Year Major Detention Runoff Coefficient C2: 0.68 Runoff Coefficient C100: 0.85 Inflow Peak Runoff Qin: 3.65 cfs Inflow Peak Runoff Qin: 15.85 Duration Duration Results: (cu.ft.) (acre-ft) (min.) Results: (cu.ft.) (acre-ft) (min.) Max. Minor Storage Vol: 1934 0.044 20 Max. Major Storage Vol: 21505 0.494 180 WQCV (EDB): 748 0.017 WQCV (EDB): 748 0.017 Total Minor Storm Vol: 2682 0.062 Total Major Storm Vol: 22253 0.511 1 (min) Duration Interval 5 (min) Duration Interval Rainfall Rainfall Inflow Outflow Storage Storage Rainfall Rainfall Inflow Outflow Storage Storage Duration Intensity Volume Volume Volume Volume Duration Intensity Volume Volume Volume Volume minutes inches / hr cubic feet cubic feet cubic feet acre feet minutes inches / hr cubic feet cubic feet cubic feet acre feet (input) (output) (output) (output) (output) (output) (input) (output) (output) (output) (output) (output) 5 2.85 1587 413 1174 0.0269 5 9.95 6897 413 6484 0.1489 6 2.67 1784 496 1288 0.0296 10 7.72 10702 826 9876 0.2267 7 2.52 1964 578 1386 0.0318 15 6.52 13558 1239 12319 0.2828 8 2.40 2138 661 1477 0.0339 20 5.60 15527 1652 13875 0.3185 9 2.30 2305 743 1562 0.0359 25 4.98 17260 2065 15195 0.3488 10 2.21 2461 826 1635 0.0375 30 4.52 18798 2478 16321 0.3747 11 2.13 2609 908 1700 0.0390 35 4.08 19796 2891 16906 0.3881 12 2.05 2739 991 1748 0.0401 40 3.74 20739 3304 17436 0.4003 13 1.98 2866 1074 1792 0.0411 45 3.46 21585 3717 17868 0.4102 14 1.92 2993 1156 1837 0.0422 50 3.23 22389 4130 18259 0.4192 15 1.87 3123 1239 1885 0.0433 55 3.03 23103 4542 18560 0.4261 16 1.81 3225 1321 1903 0.0437 60 2.86 23789 4955 18834 0.4324 17 1.75 3313 1404 1909 0.0438 65 2.71 24420 5368 19051 0.4374 18 1.70 3407 1487 1921 0.0441 70 2.59 25134 5781 19352 0.4443 19 1.65 3491 1569 1922 0.0441 75 2.48 25785 6194 19591 0.4497 20 1.61 3585 1652 1934 0.0444 80 2.38 26395 6607 19788 0.4543 21 1.56 3648 1734 1913 0.0439 85 2.29 26984 7020 19964 0.4583 22 1.53 3748 1817 1931 0.0443 90 2.21 27574 7433 20141 0.4624 23 1.49 3816 1900 1916 0.0440 95 2.13 28052 7846 20206 0.4639 24 1.46 3902 1982 1920 0.0441 100 2.06 28558 8259 20299 0.4660 25 1.43 3981 2065 1916 0.0440 105 2.00 29112 8672 20440 0.4692 26 1.40 4053 2147 1906 0.0438 110 1.94 29584 9085 20499 0.4706 27 1.37 4119 2230 1889 0.0434 115 1.88 29972 9498 20474 0.4700 28 1.34 4178 2313 1865 0.0428 120 1.84 30610 9911 20699 0.4752 29 1.32 4262 2395 1867 0.0429 125 1.79 30969 10324 20645 0.4739 30 1.30 4343 2478 1865 0.0428 130 1.75 31452 10737 20715 0.4756 31 1.27 4384 2560 1824 0.0419 135 1.71 31935 11150 20786 0.4772 32 1.24 4418 2643 1775 0.0408 140 1.67 32420 11563 20857 0.4788 33 1.22 4483 2725 1757 0.0403 145 1.64 32905 11976 20930 0.4805 34 1.19 4505 2808 1697 0.0390 150 1.61 33393 12389 21004 0.4822 35 1.17 4560 2891 1669 0.0383 155 1.58 33882 12802 21081 0.4840 36 1.15 4610 2973 1637 0.0376 160 1.55 34375 13215 21160 0.4858 37 1.13 4656 3056 1600 0.0367 165 1.52 34869 13627 21242 0.4876 38 1.11 4697 3138 1558 0.0358 170 1.50 35367 14040 21326 0.4896 39 1.09 4733 3221 1512 0.0347 175 1.48 35867 14453 21414 0.4916 40 1.07 4766 3304 1462 0.0336 180 1.46 36371 14866 21505 0.4937 41 1.05 4794 3386 1407 0.0323 42 1.04 4864 3469 1395 0.0320 43 1.02 4884 3551 1332 0.0306 44 1.01 4948 3634 1314 0.0302 0 1000 2000 3000 4000 5000 6000 5 10 15 20 25 30 35 40 45 50 55 60 Volume (Cubic Feet) Duration (Minutes) 2-Year Modified FAA Storm Detention 2-Vol 2-Inflow 2-Outflow 15 0 5000 10000 15000 20000 25000 30000 35000 40000 45000 50000 55000 5 15 25 35 45 55 65 75 85 95 105 115 125 135 145 155 165 175 Volume (Cubic Feet) Duration (Minutes) 100-Year Modified FAA Stom Detention 100-Vol 100-Inflow 100-Outflow 16 Sheet 1 of 2 Designer: Company: Date: Project: Location: 1. Basin Storage Volume A) Effective Imperviousness of Tributary Area, Ia Ia = 65.6 % (100% if all paved and roofed areas upstream of rain garden) B) Tributary Area's Imperviousness Ratio (i = Ia/100) i = 0.656 C) Water Quality Capture Volume (WQCV) for a 12-hour Drain Time WQCV = 0.21 watershed inches (WQCV= 0.8 * (0.91* i3 - 1.19 * i2 + 0.78 * i) D) Contributing Watershed Area (including rain garden area) Area = 92,231 sq ft E) Water Quality Capture Volume (WQCV) Design Volume VWQCV = 1,577 cu ft Vol = (WQCV / 12) * Area F) For Watersheds Outside of the Denver Region, Depth of d6 = in Average Runoff Producing Storm G) For Watersheds Outside of the Denver Region, VWQCV OTHER = cu ft Water Quality Capture Volume (WQCV) Design Volume H) User Input of Water Quality Capture Volume (WQCV) Design Volume VWQCV USER = cu ft (Only if a different WQCV Design Volume is desired) 2. Basin Geometry A) WQCV Depth (12-inch maximum) DWQCV = 6.00 in B) Rain Garden Side Slopes (Z = 4 min., horiz. dist per unit vertical) Z = 0.00 ft / ft (Use "0" if rain garden has vertical walls) C) Mimimum Flat Surface Area AMin = 1210 sq ft D) Actual Flat Surface Area AActual = 3344 sq ft E) Area at Design Depth (Top Surface Area) ATop = 3344 sq ft F) Rain Garden Total Volume VT= 1,672 cu ft (VT= ((ATop + AActual) / 2) * Depth) 3. Growing Media 88 88.00 0.00 38 38.00 0.00 4. Underdrain System A) Are underdrains provided? 1 B) Underdrain system orifice diameter for 12 hour drain time i) Distance From Lowest Elevation of the Storage y = 0.948 ft Volume to the Center of the Orifice ii) Volume to Drain in 12 Hours Vol12 = 1,577 cu ft iii) Orifice Diameter, 3/8" Minimum DO = 1 1/16 in Design Procedure Form: Rain Garden (RG) W. Logan ZP Architects Engineers September 8, 2020 Pacific Coast Supply Fort Collins Bioretention UD-BMP (Version 3.07, March 2018) Choose One Choose One 18" Rain Garden Growing Media Other (Explain): YES NO UD-BMP_v3.07.xlsm, RG 17 9/8/2020, 8:40 PM Sheet 2 of 2 Designer: Company: Date: Project: Location: 5. Impermeable Geomembrane Liner and Geotextile Separator Fabric A) Is an impermeable liner provided due to proximity of structures or groundwater contamination? PROVIDE A 30 MIL (MIN) PVC LINER WITH CDOT CLASS B GEOTEXTILE ABOVE IT. USE THE SAME GEOTEXTILE BELOW THE LINER IF THE SUBGRADE IS ANGULAR 6. Inlet / Outlet Control A) Inlet Control 7. Vegetation 8. Irrigation A) Will the rain garden be irrigated? Notes: Design Procedure Form: Rain Garden (RG) W. Logan ZP Architects Engineers September 8, 2020 Pacific Coast Supply Fort Collins Bioretention Choose One Choose One Choose One Sheet Flow- No Energy Dissipation Required Concentrated Flow- Energy Dissipation Provided Plantings Seed (Plan for frequent weed control) Sand Grown or Other High Infiltration Sod Choose One YES NO YES NO UD-BMP_v3.07.xlsm, RG 18 9/8/2020, 8:40 PM Sheet 1 of 3 Designer: Company: Date: Project: Location: 1. Basin Storage Volume A) Effective Imperviousness of Tributary Area, Ia Ia = 62.7 % B) Tributary Area's Imperviousness Ratio (i = Ia / 100 ) i = 0.627 C) Contributing Watershed Area Area = 2.715 ac D) For Watersheds Outside of the Denver Region, Depth of Average d6 = in Runoff Producing Storm E) Design Concept (Select EURV when also designing for flood control) 1 F) Design Volume (WQCV) Based on 40-hour Drain Time VDESIGN= ac-ft (VDESIGN = (1.0 * (0.91 * i3 - 1.19 * i2 + 0.78 * i) / 12 * Area ) G) For Watersheds Outside of the Denver Region, VDESIGN OTHER= ac-ft Water Quality Capture Volume (WQCV) Design Volume (VWQCV OTHER = (d6*(VDESIGN/0.43)) H) User Input of Water Quality Capture Volume (WQCV) Design Volume VDESIGN USER= 0.017 ac-ft (Only if a different WQCV Design Volume is desired) I) NRCS Hydrologic Soil Groups of Tributary Watershed i) Percentage of Watershed consisting of Type A Soils HSG A = % ii) Percentage of Watershed consisting of Type B Soils HSG B = % iii) Percentage of Watershed consisting of Type C/D Soils HSG C/D = % J) Excess Urban Runoff Volume (EURV) Design Volume For HSG A: EURVA = 1.68 * i1.28 EURVDESIGN = ac-f t For HSG B: EURVB = 1.36 * i1.08 For HSG C/D: EURVC/D = 1.20 * i1.08 K) User Input of Excess Urban Runoff Volume (EURV) Design Volume EURVDESIGN USER= ac-f t (Only if a different EURV Design Volume is desired) 2. Basin Shape: Length to Width Ratio L : W = 2.0 : 1 (A basin length to width ratio of at least 2:1 will improve TSS reduction.) 3. Basin Side Slopes A) Basin Maximum Side Slopes Z = 4.00 ft / ft (Horizontal distance per unit vertical, 4:1 or flatter preferred) 4. Inlet A) Describe means of providing energy dissipation at concentrated inflow locations: Design Procedure Form: Extended Detention Basin (EDB) Pacific Coast Supply ZP Architects Engineers September 8, 2020 W. Logan UD-BMP (Version 3.07, March 2018) Riprap field Choose One Excess Urban Runoff Volume (EURV) Water Quality Capture Volume (WQCV) UD-BMP_v3.07.xlsm, EDB 19 9/8/2020, 8:48 PM Use stainless steel well screen #93 Vee w/ 0.139 " wire opening, # 156 VEE support rods on 3/4" o.c., screen thickness 0.31" w/ 6" wide min. opening. At 0.29 ft 2 At A  ot  77 e     0.124  D Aot 0.004 ft 2 Aot   (0.0417  ft ) 2  4 D  0.625  in   3 Trashrack Opening Area: Provide 2 rows at 4" o.c. vertically in face of drainage box with (1) one 5/8-inch diameter holes per row. Drain_Time  23.7 hr (approxiomatly) Drain_Time WQCV Qwqcv 1hr 3600sec   Approximate WQCV Drain Time: Qwqcv 0.00876 ft 3 sec Qwqcv   d1 2  4 Cd 2g  h 1 d1 2           d2 2  4 Cd 2g  h 2 d2 2      Q100 1.37 ft 3 sec Q100   ID 2  4 Cd 2  32.2 H ID 2           cfs Actual Discharge ID  5.625  in ID  0.469 ft D root D  0.471 ft Use 5 5/8" orfice  d 2  4 Cd 2  32.2 H d 2          Q2  d         ft Q2 1.38 ft 3 sec where Cd  0.60  Q100  D 2  4 Cd 2g  H D 2          Emergency overflow from pond: Use a retangular contracted weir: Qof C w  (L  0.2  H ) H b   where Cw  3.4 b 3 2  H  0.25  ft Detention Flow Through runoff is: QC  15.85  cfs Qof Q  C Qof 15.85 ft 3 sec  Required width of weir for a maximum flow height of 3": Width root Cw  (L  0.2  H ) H b   Qof  L    Width  37.344 ft Use an 40' wide emergency overflow wier from detention pond. 22 WQCV Depth: DWQ  ElevWQCV  20.30  ft D WQ  49.39 ft K40 0.013 D WQ 2   0.22  DWQ  ft 0.10 ft 2    K40 1.153 ft 2  WQCV 748 ft 3  (0.00706  acre  ft ) WQCV  0.0071  acre  ft in 2 Required Area per Row: row Area WQCV K40  Area  268.178 ft Area WQCV K40 in ft   Area  22.35 ft (1/2-in, dia) 23 APPENDIX B Charts and Tables 24                 Hydrologic Soil Group—Larimer County Area, Colorado (Pacific Coast Supply) Natural Resources Conservation Service Web Soil Survey National Cooperative Soil Survey 9/8/2020 Page 1 of 4 4494360 4494380 4494400 4494420 4494440 4494460 4494480 4494500 4494360 4494380 4494400 4494420 4494440 4494460 4494480 4494500 499900 499920 499940 499960 499980 500000 500020 500040 500060 500080 500100 500120 499900 499920 499940 499960 499980 500000 500020 500040 500060 500080 500100 500120 40° 36' 4'' N 105° 0' 4'' W 40° 36' 4'' N 104° 59' 54'' W 40° 35' 59'' N 105° 0' 4'' W 40° 35' 59'' N 104° 59' 54'' W N Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84 0 50 100 200 300 Feet 0 15 30 60 90 Meters Map Scale: 1:1,070 if printed on A landscape (11" x 8.5") sheet. Soil Map may not be valid at this scale. 29 MAP LEGEND MAP INFORMATION Area of Interest (AOI) Area of Interest (AOI) Soils Soil Rating Polygons A A/D B B/D C C/D D Not rated or not available Soil Rating Lines A A/D B B/D C C/D D Not rated or not available Soil Rating Points A A/D B B/D C C/D D Not rated or not available 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 Hydrologic Soil Group Map unit symbol Map unit name Rating Acres in AOI Percent of AOI 53 Kim loam, 1 to 3 percent slopes B 0.0 0.1% 63 Longmont clay, 0 to 3 percent slopes D 1.3 29.3% 74 Nunn clay loam, 1 to 3 percent slopes C 2.2 51.5% 94 Satanta loam, 0 to 1 percent slopes C 0.8 19.1% Totals for Area of Interest 4.3 100.0% Description Hydrologic soil groups are based on estimates of runoff potential. Soils are assigned to one of four groups according to the rate of water infiltration when the soils are not protected by vegetation, are thoroughly wet, and receive precipitation from long-duration storms. The soils in the United States are assigned to four groups (A, B, C, and D) and three dual classes (A/D, B/D, and C/D). The groups are defined as follows: Group A. Soils having a high infiltration rate (low runoff potential) when thoroughly wet. These consist mainly of deep, well drained to excessively drained sands or gravelly sands. These soils have a high rate of water transmission. Group B. Soils having a moderate infiltration rate when thoroughly wet. These consist chiefly of moderately deep or deep, moderately well drained or well drained soils that have moderately fine texture to moderately coarse texture. These soils have a moderate rate of water transmission. Group C. Soils having a slow infiltration rate when thoroughly wet. These consist chiefly of soils having a layer that impedes the downward movement of water or soils of moderately fine texture or fine texture. These soils have a slow rate of water transmission. Group D. Soils having a very slow infiltration rate (high runoff potential) when thoroughly wet. These consist chiefly of clays that have a high shrink-swell potential, soils that have a high water table, soils that have a claypan or clay layer at or near the surface, and soils that are shallow over nearly impervious material. These soils have a very slow rate of water transmission. If a soil is assigned to a dual hydrologic group (A/D, B/D, or C/D), the first letter is for drained areas and the second is for undrained areas. Only the soils that in their natural condition are in group D are assigned to dual classes. Hydrologic Soil Group—Larimer County Area, Colorado Pacific Coast Supply Natural Resources Conservation Service Web Soil Survey National Cooperative Soil Survey 9/8/2020 Page 3 of 4 31 Rating Options Aggregation Method: Dominant Condition Aggregation is the process by which a set of component attribute values is reduced to a single value that represents the map unit as a whole. A map unit is typically composed of one or more "components". A component is either some type of soil or some nonsoil entity, e.g., rock outcrop. For the attribute being aggregated, the first step of the aggregation process is to derive one attribute value for each of a map unit's components. From this set of component attributes, the next step of the aggregation process derives a single value that represents the map unit as a whole. Once a single value for each map unit is derived, a thematic map for soil map units can be rendered. Aggregation must be done because, on any soil map, map units are delineated but components are not. For each of a map unit's components, a corresponding percent composition is recorded. A percent composition of 60 indicates that the corresponding component typically makes up approximately 60% of the map unit. Percent composition is a critical factor in some, but not all, aggregation methods. The aggregation method "Dominant Condition" first groups like attribute values for the components in a map unit. For each group, percent composition is set to the sum of the percent composition of all components participating in that group. These groups now represent "conditions" rather than components. The attribute value associated with the group with the highest cumulative percent composition is returned. If more than one group shares the highest cumulative percent composition, the corresponding "tie-break" rule determines which value should be returned. The "tie-break" rule indicates whether the lower or higher group value should be returned in the case of a percent composition tie. The result returned by this aggregation method represents the dominant condition throughout the map unit only when no tie has occurred. Component Percent Cutoff: None Specified Components whose percent composition is below the cutoff value will not be considered. If no cutoff value is specified, all components in the database will be considered. The data for some contrasting soils of minor extent may not be in the database, and therefore are not considered. Tie-break Rule: Higher The tie-break rule indicates which value should be selected from a set of multiple candidate values, or which value should be selected in the event of a percent composition tie. Hydrologic Soil Group—Larimer County Area, Colorado Pacific Coast Supply Natural Resources Conservation Service Web Soil Survey National Cooperative Soil Survey 9/8/2020 Page 4 of 4 32 APPENDIX C FIRM Map, Drainage Plan and Details 33 34 35 36 of the version date(s) listed below. Soil Survey Area: Larimer County Area, Colorado Survey Area Data: Version 15, Jun 9, 2020 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: Jul 19, 2018—Aug 10, 2018 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. Hydrologic Soil Group—Larimer County Area, Colorado (Pacific Coast Supply) Natural Resources Conservation Service Web Soil Survey National Cooperative Soil Survey 9/8/2020 Page 2 of 4 30          !  " #"!$%&!$ "'&"(&)"*! 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H  Elev100  69.00  ft H  2.95 ft 100-year orifice size: Q2 Q  wqcv 1.36 ft 3 sec  Qwqcv 0.020 ft 3 sec Qwqcv   d1 2  4 Cd 2g  h 1 d1 2           d2 2  4 Cd 2g  h 2 d2 2            d h2  0.82917  ft 2  0.052  ft d h1  1.1625  ft Additional Discharge from water quality plate: 1  0.052  ft C Q2  1.38  cfs d  0.60 H Elev2 Elev H  0.41 ft Q2   WQCV  D 2  4 Cd 2g  H D 2          where 2-year vertical orifice size: Detention Outlet Structure: 21       Discharge from water quality plate: d h2  0.081  ft 2  0.052  ft Two 1/2" diameter outlets: h d1 1  0.414  ft  0.052  ft WQCV 748 ft 3 where Cd  0.60  WQCV Release Plate: 20 45 0.99 4961 3717 1244 0.0286 46 0.98 5020 3799 1220 0.0280 47 0.96 5024 3882 1142 0.0262 48 0.95 5078 3964 1113 0.0256 49 0.94 5129 4047 1082 0.0248 50 0.92 5122 4130 993 0.0228 51 0.91 5168 4212 956 0.0219 52 0.90 5211 4295 916 0.0210 53 0.89 5252 4377 875 0.0201 54 0.88 5291 4460 831 0.0191 55 0.87 5328 4542 786 0.0180 56 0.86 5363 4625 738 0.0169 57 0.85 5395 4708 687 0.0158 58 0.84 5425 4790 635 0.0146 59 0.83 5453 4873 580 0.0133 60 0.82 5478 4955 523 0.0120 65 0.78 5645 5368 277 0.0064 14 POINT DIRECT RUNOFF TOTAL RUNOFF 8/26/2020 13 DIRECT RUNOFF TOTAL RUNOFF STREET PIPE TRAVEL TIME REMARKS 8/26/2020 12