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HomeMy WebLinkAboutJOHNSON DRIVE APARTMENTS - FDP190021 - SUBMITTAL DOCUMENTS - ROUND 1 - DRAINAGE REPORTFINAL DRAINAGE REPORT Johnson Drive Apartments Fort Collins, Colorado October 09, 2019 Prepared for: Next Chapter Properties 217 S. Neil Street, Suite B Champaign IL, 61820 Prepared by: 301 North Howes Street, Suite 100 Fort Collins, Colorado 80521 Phone: 970.221.4158 Fax: 970.221.4159 www.northernengineering.com Project Number: 1285-001  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 absolutely necessary, we recommend double-sided printing. October 09, 2019 City of Fort Collins Stormwater Utility 700 Wood Street Fort Collins, Colorado 80521 RE: Final Drainage Report for Johnson Drive Apartments Dear Staff: Northern Engineering is pleased to submit this Final Drainage Report for your review. This report has been prepared in accordance with the City of Fort Collins Stormwater Criteria Manual (FCSCM) and the Urban Drainage and Flood Control District (UDFCD) Urban Storm Drainage Criteria Manual and serves to document the stormwater impacts associated with the proposed Johnson Drive Apartments project. We understand that review by the City of Fort Collins is to assure general compliance with standardized criteria. 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 Blaine Mathisen Project Manager Project Engineer Johnson Drive Apartments Final Drainage Report TABLE OF CONTENTS I. GENERAL LOCATION AND DESCRIPTION ................................................................... 1 A. Location ............................................................................................................................................. 1 B. Description of Property ..................................................................................................................... 2 C. Floodplain.......................................................................................................................................... 3 II. DRAINAGE BASINS AND SUB-BASINS ....................................................................... 5 A. Major Basin Description .................................................................................................................... 5 B. Sub-Basin Description ....................................................................................................................... 5 III. DRAINAGE DESIGN CRITERIA ................................................................................... 7 A. Regulations........................................................................................................................................ 7 B. Four Step Process .............................................................................................................................. 7 C. Development Criteria Reference and Constraints ............................................................................ 8 D. Hydrological Criteria ......................................................................................................................... 8 E. Hydraulic Criteria .............................................................................................................................. 8 F. Floodplain Regulations Compliance .................................................................................................. 9 G. Modifications of Criteria ................................................................................................................... 9 IV. DRAINAGE FACILITY DESIGN .................................................................................... 9 A. General Concept ............................................................................................................................... 9 B. Specific Details ................................................................................................................................ 10 V. CONCLUSIONS ...................................................................................................... 11 A. Compliance with Standards ............................................................................................................ 11 B. Drainage Concept ............................................................................................................................ 12 References ....................................................................................................................... 13 APPENDICES: APPENDIX A – Hydrologic Computations APPENDIX B – Hydraulic Computations B.1 – Storm Sewers (Future) B.2 – Inlets (Future) B.3 – Detention Facilities APPENDIX C – Water Quality Design Computations APPENDIX D – Erosion Control Report APPENDIX E – Soils Resource Report APPENDIX F - FEMA Mapping Johnson Drive Apartments Final Drainage Report LIST OF TABLES AND FIGURES: Figure 1 Vicinity Map .......................................................................................................... 1 Figure 2 Aerial Photograph ................................................................................................... 2 Figure 3 Proposed Site Plan ................................................................................................. 3 Figure 4 FEMA Map ............................................................................................................ 4 Figure 5 City Floodplain Mapping .......................................................................................... 5 MAP POCKET: C6.00 – Proposed Drainage Exhibit C6.01 – Floodplain Exhibit Historic Drainage Exhibit Johnson Drive Apartments Final Drainage Report 1 I. GENERAL LOCATION AND DESCRIPTION A. Location 1. Vicinity Map Figure 1 Vicinity Map 2. Johnson Drive Apartments project site is located in the replat of lots 13, 14, 15, 16, and 17 Spring Court Subdivision which is located in the northeast quarter of Section 23, Township 7 North, Range 69 West of the 6th Principal Meridian, City of Fort Collins, County of Larimer, State of Colorado. 3. The project site is located at 255 Johnson Drive at southwest corner of the intersection of Johnson Drive and Spring Court. The property is bounded to the north by Johnson Drive and further north by Spring Creek, to the east by Spring Court, to the south by and irrigation lateral and to the west by BNSF Railway and the Max route. 4. The project site lies within the Spring Creek Basin. The project site has historically drained towards Spring Court and Johnson Drive via overland flow from south to northeast. The site must provide current City Low-Impact Design (LID) requirements and water quality treatment as well. Water quality treatment methods are described Johnson Drive Apartments Final Drainage Report 2 in further detail below. 5. As this is an in-fill site, the area surrounding the property is fully developed. 6. There are no off-site flows that enter the project area. B. Description of Property 1. Johnson Drive Apartments project is approximately 2.80 net acres. Figure 2 Aerial Photograph 2. There are currently five properties being utilized for this project; one commercial lot (Self-Storage) and four residential lots. The existing commercial lot routes stormwater via overland and gutter flow and releases undetained into Johnson Drive. Once in Johnson Drive, stormwater travels via gutter flow to the east where it is intercepted by an existing inlet and conveyed directly to Spring Creek. The four residential lots route stormwater via overland flow and releases undetained into Spring Court. Once in Spring Court, stormwater travel via gutter flow to the north to Johnson Drive, with the ultimate destination being Spring Court. The overall existing impervious area located within in the four properties is 76,857 sq. ft. and was released undetained. There are currently no water quality measures located on-site. 3. According to the United States Department of Agriculture (USDA) Natural Resources Conservation Service (NRCS) Soil Survey, the site consists of Altvan-Satanta and Kim loams, which fall into Hydrologic Soil Groups B. The NRCS soils report is provided in Appendix E. 4. The proposed development is primarily composed of a proposed student housing building. Associated site work that will be constructed with this project include water services, sanitary sewer services, storm sewer, landscaped swales and walls, and sidewalks along the north, south and east side of the building. Current City Low- Impact Design (LID) requirements will be implemented with the project, and will consist of sand filter, which is further discussed in Section IV, below. Johnson Drive Apartments Final Drainage Report 3 Figure 3 Proposed Site Plan 5. There are no known irrigation laterals crossing the site. There is an irrigation lateral bordering the south side of the property. 6. The project site is within a General Commercial District (CG). The proposed use is permitted within this zone district. C. Floodplain 1. The project site is encroached by the FEMA designated 100- Year High Risk Flood Fringe according to FIRM Panel 08069C87G for Larimer County, effective February 26, 2018. 2. Development is allowed within the flood fringe. It should be noted that the portion of the structure that will be constructed within the floodplain with the development of Johnson Drive Apartments. Commercial and Residential spaces will be elevated 18” above the Base Flood Elevation at all openings (Regulatory Flood Protection Elevation RFPE). The garage will be located lower than the RFPE and hydraulic venting will be Johnson Drive Apartments Final Drainage Report 4 provided. Floodproofing of portions of the structure below the RFPE will be floodproofed. 3. A no-rise certification will be required for the storm sewer outfall into the floodway. 4. The building foundation is proposed to be concrete spread footings under perimeter walls and columns. All being supported by structural piers. 5. 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, et.), 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. 6. Development within the floodplain must comply with Chapter 10 of the Municipal Code. 7. Please see appendix for a Floodplain Exhibit and all regulatory notes regarding development within the floodplain. Figure 4 FEMA Map Johnson Drive Apartments Final Drainage Report 5 Figure 5 City Floodplain Mapping II. DRAINAGE BASINS AND SUB-BASINS A. Major Basin Description 1. The project site lies within the Spring Creek Basin. Detention requirements for this site are to detain the difference between the 100-yr developed flow rate and the historic 100-yr release of all existing impervious area and 2-yr release rate from the existing landscaping areas. The project is composed of five different lots, one is a commercial lot and the other four are single-family residential lots. Historically, the lots sheet flow into the surrounding streets undetained. However, Johnson Drive Apartments will release at a reduced historic rate and will also provide water quality. The proposed release rate will be reduced to summation of the historic 2-year event within the existing landscape areas and the historic 100-year event within all the existing impervious areas. Water quality will be provided for all the paved areas via a sand filter within the building. All other water quality will be provided by sheet flowing across landscape areas. 2. There are no previous drainage studies for the area associated with Johnson Drive Apartments project site. B. Sub-Basin Description Johnson Drive Apartments historically drains overland from south to north except for the southwest corner of the site which is picked up by an irrigation lateral running west to east. Runoff from the site has historically flowed overland north towards Spring Creek and eventually enters the Cache La Poudre. Johnson Drive Apartments Final Drainage Report 6 Basin HW1 Pervious Historic Basin HW1 Pervious is 0.18 acres and is roughly the western 2/3 of the property, and it is only comprised of landscaping area. Runoff generated in this basin historically sheet flows north into Johnson Drive. Once in Johnson Drive runoff will be conveyed west to east via curb and gutter until it enters a curb inlet and is further conveyed to Spring Creek. Basin HW1 Pervious has a 2-yr runoff of 0.06 cfs. Basin HW1 Impervious Historic Basin HW1 Impervious is 1.56 acres and is roughly the western 2/3 of the property, and it is only comprised of the paved and roof areas associated with Johnson Drive Storage. Runoff generated in this basin historically sheet flows north into Johnson Drive. Once in Johnson Drive runoff will be conveyed west to east via curb and gutter until it enters a curb inlet and is further conveyed to Spring Creek. Basin HW1 Impervious has a 100-yr runoff of 15.48 cfs. Overall Basin HW is 1.73 acres and has a combined release rate of 15.54 cfs (0.06 cfs + 15.48 cfs) from Basins HW1 Pervious 2-year event and HE1 Impervious 100- year event. Basin HE1 Pervious Historic Basin HE1 Pervious is 0.60 acres and is roughly the eastern 1/3 of the property, and it is only comprised of landscaping area. Runoff generated in this basin historically sheet flows directly into Spring Court and is then conveyed north via curb and gutter until it enters a curb inlet and is conveyed to Spring Creek. Basin HE1 Pervious has a 2-yr runoff of 0.15 cfs. Basin HE1 Impervious Historic Basin HE1 Impervious is 0.21 acres and is roughly the eastern 1/3 of the property, and it is comprised of the paved sidewalks and roof areas. Runoff generated in this basin historically sheet flows directly into Spring Court and is then conveyed north via curb and gutter until it enters a curb inlet and is conveyed to Spring Creek. Basin HE1 Impervious has a 100-yr runoff of 2.08 cfs. Overall Basin HE is 0.20 acres and has a combined release rate of 2.22 cfs (0.15 cfs + 2.08 cfs) from Basins HE1 Pervious 2-year event and HE1 Impervious 100-year event. Basin HS1 Pervious Historic Basin HS1 Pervious is 0.27 acres and is situated in the southwest corner of the project site. Runoff generated in this area will sheet flow into an existing irrigation lateral that runs west to east. There is also a small detention pond in this area that is serving the property to the south of the project site. This area will remain untouched during the development of Johnson Drive Apartments. Basin HW1 Pervious has a 2-yr runoff of 0.11 cfs. Basin HS1 Impervious Historic Basin HS1 Impervious is 0 acres because it is all vegetated. Basin HW1 Impervious has a 100-yr runoff of 0 cfs. Overall Basin HS1 is 0.27 acres and has a combined release rate of 0.11 cfs (0.11 cfs + 0 cfs) from Basins HS1 Pervious and HS1 Impervious. Therefore, the overall historic release rate from the site is 17.88 cfs (15.54 cfs + 2.22 cfs + 0.11 cfs). However, due to uncapturable flows from Johnson Drive Apartments, which is Johnson Drive Apartments Final Drainage Report 7 discussed in Section IV.A, the allowable release rate is reduced to 13.09 cfs. 1. A more detailed description of the project’s proposed drainage patterns follows in Section IV.A.4. A full-size copy of the Historic and Proposed Drainage Exhibits can be found in the Map Pocket at the end of this report. III. DRAINAGE DESIGN CRITERIA A. Regulations There are no optional provisions outside of the FCSCM proposed with the Johnson Drive Apartments project. B. Four Step Process The overall stormwater management strategy employed with the Johnson Drive Apartments 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 Several techniques have been utilized with the proposed development to facilitate the reduction of runoff peaks, volumes, and pollutant loads as the site is redeveloped from the current use by implementing multiple Low-Impact Development (LID) strategies including: Providing as much vegetated open areas as possible along the east, west and south portion of the site to reduce the overall impervious area and to minimize directly connected impervious areas (MDCIA). Selecting a site that has been previously developed to reduce development impacts. Routing flows, to the extent feasible, through a stormwater detention vault located internal to the building for water quality purposes. Stormwater will be routed through a sand filter to increase filtration. Providing on-site detention to increase time of concentration, and reduce loads on downstream storm infrastructure. Routing runoff from the roof directly into the sand filter. Step 2 – Implement BMPs That Provide a Water Quality Capture Volume (WQCV) with Slow Release The efforts taken in Step 1 will facilitate the reduction of runoff; however, urban development of this intensity will still generate stormwater runoff that will require additional BMPs and water quality. The stormwater runoff from the site will be intercepted and treated using an internal stormwater vault with a water quality capture volume. Step 3 – Stabilize Drainageways There is one major drainageway within the subject property, Sherwood Lateral. While this step may not seem applicable to proposed development, the project indirectly helps achieve stabilized drainageways nonetheless. By providing detention and water quality treatment where none previously existed, sediment and flash flows with erosion potential are removed from downstream drainageway systems. Furthermore, this project will pay Johnson Drive Apartments Final Drainage Report 8 one-time stormwater development fees, as well as ongoing monthly stormwater utility fees, both of which help achieve City-wide drainageway stability. Additionally, Johnson Drive Apartments does not intend to alter the south side of the north bank stabilizing the Sherwood Lateral. Also, Johnson Drive Apartments will be maintaining the North side slope of the lateral by tying in at the same elevations as the top of the bank Step 4 – Implement Site Specific and Other Source Control BMPs. The proposed project includes one multi-story building, covered parking areas within the structure, retaining walls, and pedestrian sidewalks, all of which will require the need for site specific source controls including: A localized trash enclosure placed within the building. The proposed development will provide LID features within the stormwater vault internal to the building to provide enhanced water quality. The Sand Filter is designed to capture the first flush storm event; thus, eliminating sources of potential pollution previously left exposed to weathering and runoff processes. C. Development Criteria Reference and Constraints 1. There are no known drainage studies for the existing property. 2. The subject property is a redevelopment project and is surrounded by currently developed properties. As such, several constraints have been identified during the course of this analysis that will impact the proposed drainage system including: Existing elevations along the north, south, east, and west property lines will be maintained. Overall drainage patterns of the existing site will be maintained. Release rates can not adversely impact existing infrastructure. D. Hydrological Criteria 1. The City of Fort Collins Rainfall Intensity-Duration-Frequency Curves, as depicted in Figure RA-16 of the FCSCM, serve as the source for all hydrologic computations associated with this development. Tabulated data contained in Table RA-7 has been utilized for Rational Method runoff calculations. 2. The Rational Method has been employed to compute stormwater runoff utilizing coefficients contained in Tables RO-11 and RO-12 of the FCSCM. 3. The Rational Formula-based Modified Federal Aviation Administration (FAA) procedure has been utilized for detention storage calculations. 4. Two 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-yr recurrence interval. The second event considered is the “Major Storm,” which has a 100-yr recurrence interval. 5. No other assumptions or calculation methods have been used with this development that are not referenced by current City of Fort Collins criteria. E. Hydraulic Criteria 1. As previously noted, the subject property maintains historic drainage patterns. 2. All drainage facilities proposed with the Johnson Drive Apartments project are designed in accordance with criteria outlined in the FCSCM and/or the Urban Drainage and Flood Control District’s (UDFCD) Urban Storm Drainage Criteria Johnson Drive Apartments Final Drainage Report 9 Manual. 3. As stated in Section I.C.1, above, the subject property is encroaching a FEMA 100- Year High Risk Flood Fringe. F. Floodplain Regulations Compliance As previously mentioned, the project site is encroaching a FEMA 100-Year High Risk Flood Fringe along the northwest corner of the property. Development is allowed within the flood fringe pursuant to Chapter 10 of the City of Fort Collins Municipal Code. It should be noted that no structures will be constructed within the floodway with the development of Johnson Drive Apartments. However, the building and all the landscaping walls do fall within the 100- year moderate floodplain. G. Modifications of Criteria The proposed Johnson Drive Apartments development is not requesting any modifications. IV. DRAINAGE FACILITY DESIGN A. General Concept 1. The main objectives of the Johnson Drive Apartments drainage design are to maintain existing drainage patterns and ensure no adverse impacts to any adjacent properties or existing infrastructure. 2. As previously mentioned, there are no off-site flows draining onto the existing property. Additionally, on-site LID feature will be provided which will enhance downstream water quality. These measures are discussed further below. 3. 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. 4. The proposed Johnson Drive Apartments project is has been divided into five (5) major drainage basins, designated as Basins A1, OW1, OS1, OS2, and ON1. Drainage patterns for basins shown on the Proposed Drainage Exhibit are described below. Basin A1 Basin A1 has a net area of 1.668 acres, which corresponds to the entire building footprint. Runoff generated in Basin A1 will be generated by the roof which will then convey the runoff to an internal storm vault via roof leaders. The internal storm vault will also be a sand filter therefore, 100% of the treatable runoff is treated via LID. Basin A1 will provide onsite detention that is required for the runoff volume difference between the 100-year developed inflow rate and the 2-year historic release rate for any net new impervious area. After Basin A1 is detained and treated, it will be conveyed to Spring Creek via ADS pipe. The 100-year flow rate for Basin A1 is 16.59 cfs. Basin OW1 Basin OW1 is located between the proposed apartment building and the Mason Street corridor retaining wall and has a net area of 0.093 acres. This area is all landscaping but due to existing grades this area will be getting free released into Spring Creek via a Johnson Drive Apartments Final Drainage Report 10 Nyloplast inline drain that is connected to the outfall pipe of Basin A1. Since Basin OW1 is leaving the site undetained and untreated the overall release rate will be modified to reflect this. The 100-year release rate for Basin OW1 is 0.17 cfs. Basin OS1 Basin OS1 has a net area of 0.301 acre, and is associated with the Sherwood Irrigation lateral and detention pond that occupy the southwest corner of the site. This area has historically bypassed the site flowing east via the irrigation lateral. Johnson Drive apartments will not be developing anything in this area therefore this runoff will continue to flow east via the irrigation lateral. Because Johnson Drive Apartments is not able to capture and treat this area runoff the max allowable release rate will be reduced to reflect this. The 100-year release rate for Basin OS1 is 1.03 cfs. Basin OS2 Basin OS2 has a net area of 0.30 acres, and is located along the southern edge of the proposed apartment building and northern side of the irrigation lateral. All the runoff generated in Basin OS2 will flow east towards Spring Court via a swale. Runoff generated in Basin OS2 will freely discharge into Spring Court via a concrete chase. Therefore, the max allowable release rate will be reduced to reflect that Basin OS2 is not being detained or treated. The 100-year release rate for Basin OS2 is 0.41 cfs. Basin ON1 Basin ON1 has a net area of 0.48 acres, and is located along the eastern and northern edge of the proposed apartment building. All the flow generated in Basin ON1 will leave the site undetained and untreated via overland flow. The runoff will either enter Spring Court or Johnson Drive. Once in the public right of way the runoff will make its way to an existing inlet near the northeast corner of the intersection of Johnson Drive and Spring Court. From there the runoff will be conveyed to Spring Creek via pipe. The 100-year release rate for Basin ON1 is 3.18 cfs. Max Allowable Release Rate The max allowable release rate for Johnson Drive Apartments is 13.09 cfs. This was calculated by summing up the historic release rates from Basins HW1, HE1, and HS1 2-year pervious and 100-year impervious rates. Following the calculations laid out in Section II.B yields a historic release rate of 17.88 cfs. Due to the Basins OS1, OS2, ON1, and OW1 free releasing off the site the 17.88 cfs was reduced by summation of the aforementioned basins 100-year release rates which is 4.79 cfs. Therefore, the max allowable release rate is 17.88 cfs – 4.79 cfs = 13.09 cfs. B. Specific Details 1. The main drainage problems associated with this project site are the deficiency of existing stormwater infrastructure present, steep existing grades, an existing irrigation lateral running across the site, and FEMA floodplain. Currently the site drains to the northeast. The proposed site will mitigate these issues by instituting the following water quality and detention facilities: Johnson Drive Apartments Final Drainage Report 11 Johnson Drive Apartments will be utilizing a sand filter to treat all the runoff generated by Basin A1. The sand filter will be incorporated into the internal storm chamber within the apartment building. All the free released runoff will be generated by landscaping areas which will provide minimal water quality via grass buffers. 2. Detention Pond Calculations Using the FAA Method to detain Basin A1 with a reduced release rate of 13.09 cfs yields an overall detention volume of 1946 cu. ft. This required volume will be stored in conjunction with the WQCV within the internal storm chamber. 3. Water Quality Results Following UDFCD criteria and using the characteristics from Basin A1 wields an overall water quality capture volume (WQCV) of 2,187 cu. ft. This water quality will be getting provided via sand filter. With the current configuration of the internal stomr chamber the actual WQCV is 2,250 cu. ft. The treated runoff will be conveyed to Spring Creek via HDPE pipe. 4. Below is a breakdown of the LID treatment of the proposed project site. V. CONCLUSIONS A. Compliance with Standards 1. The drainage design proposed with the Johnson Drive Apartments project complies with the City of Fort Collins’ Stormwater Criteria Manual. 2. The drainage design proposed with the Johnson Drive Apartments project complies with the City of Fort Collins’ Master Drainage Plan for the Spring Creek Basin. 3. The project site is encroached by a 100-Year High Floodplain Fringe along the northwest corner of the property. However, the development will not adversely impact any of the downstream infrastructure, as this floodplain is caused by the obstruction of the College Avenue bridge. 4. The drainage plan and stormwater management measures proposed with the Johnson Drive Apartments development are compliant with all applicable State and Federal regulations governing stormwater discharge. Basin ID Basin Impervious Area Treatment Type LID System Area Treated by Percent of Impervious Area A1 1.668 ac. Sand Filter Yes 1.668 ac. 84% OW1 0.000 ac. Grass Buffer No N/A 0% OS1 0.047 ac. Grass Buffer No N/A 0% OS2 0.002 ac. Grass Buffer No N/A 0% ON1 0.271 ac. Grass Buffer No N/A 0% Total 1.988 ac. 1.668 ac. 84% Johnson Drive Apartments Final Drainage Report 12 B. Drainage Concept 1. The drainage design proposed with this project will effectively limit potential damage associated with its stormwater runoff. The total difference in impervious area between historic and proposed conditions is only 9,801 sq. ft., which is only 8,801 sq. ft. above the maximum threshold for detention according to the City of Fort Collins Stormwater Criteria Manual. 2. Johnson Drive Apartments will be releasing at reduced runoff rates from the historic condition to both Johnson Drive and Spring Court; therefore, there will be no downstream impacts from this development. 3. Johnson Drive Apartments will provide water quality for a majority of the site (1.668 acres out of 2.80 acreas) with accepted LID treatments. The remaining portion of the project site will receive water quality by crossing over landscaped areas. The areas receiving water quality via landscaping were uncatchable and only include the perimeter areas along the north, south, east, and west. 4. The proposed Johnson Drive Apartments development will not impact the Master Drainage Plan recommendations for the Spring Creek major drainage basin. Johnson Drive Apartments Final Drainage Report 13 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. 174, 2011, and referenced in Section 26-500 (c) of the City of Fort Collins Municipal Code. 3. Larimer County Urban Area Street Standards, Adopted January 2, 2001, Repealed and Reenacted, Effective October 1, 2002, Repealed and Reenacted, Effective April 1, 2007. 4. Soils Resource Report for Larimer County Area, Colorado, Natural Resources Conservation Service, United States Department of Agriculture. 5. Urban Storm Drainage Criteria Manual, Volumes 1-3, Urban Drainage and Flood Control District, Wright-McLaughlin Engineers, Denver, Colorado, Revised April 2008. APPENDIX A HYDROLOGIC COMPUTATIONS CHARACTER OF SURFACE: Runoff Coefficient Percentage Impervious Project: Johnson Drive Apartments Streets, Parking Lots, Roofs, Alleys, and Drives: Calculations By: C. Snowdon Asphalt ……....……………...……….....…...……………….………………………………….. 0.95 100% Date: Concrete …….......……………….….……….………………..….………………………………… 0.95 90% Gravel ……….…………………….….…………………………..……………………………….0.15 . 0.50 40% Roofs …….…….………………..……………….…………………………………………….. 0.95 90% Pavers…………………………...………………..…………………………………………….. 0.40 22% Lawns and Landscaping Sandy Soil ……..……………..……………….…………………………………………….. 0.15 0% Clayey Soil ….….………….…….…………..………………………………………………. 0.25 0% 2-year Cf = 1.00 100-year Cf = 1.25 Basin ID Basin Area (s.f.) Basin Area (ac) Area of Asphalt (ac) Area of Concrete (ac) Area of Roofs (ac) Area of Gravel (ac) Area of Lawns and Landscaping (ac) 2-year Composite Runoff Coefficient 10-year Composite Runoff Coefficient 100-year Composite Runoff Coefficient Composite % Imperv. HW1 75478 1.73 0.86 0.01 0.69 0.00 0.18 0.87 0.87 1.00 86% HE1 35074 0.81 0.00 0.07 0.14 0.00 0.60 0.36 0.36 0.45 23% HS1 11546 0.27 0.00 0.00 0.00 0.00 0.27 0.15 0.15 0.19 0% Total 122098 2.80 0.86 0.09 0.82 0.00 1.04 0.65 0.65 0.82 60% HW1 (Impervious) 67772 1.56 0.86 0.01 0.69 0.00 0.00 0.95 0.95 1.00 96% HW1 (Pervious) 7706 0.18 0.00 0.00 0.00 0.00 0.18 0.15 0.15 0.19 0% HE1 (Impervious) 9085 0.21 0.00 0.07 0.14 0.00 0.00 0.95 0.95 1.00 90% HE1 (Pervious) 25989 0.60 0.00 0.00 0.00 0.00 0.60 0.15 0.15 0.19 0% HS1 (Impervious) 0 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0% HS1 (Pervious) 11546 0.27 0.00 0.00 0.00 0.00 0.27 0.15 0.15 0.19 0% Overland Flow, Time of Concentration: Project: Johnson Drive Apartments Calculations By: Date: Gutter/Swale Flow, Time of Concentration: 0.15 0 Tt = L / 60V Tc = T i + Tt (Equation RO-2) Velocity (Gutter Flow), V = 20·S ½ Velocity (Swale Flow), V = 15·S ½ NOTE: C-value for overland flows over grassy surfaces; C = 0.25 Is Length >500' ? C*Cf (2-yr Cf=1.00) C*Cf (10-yr Cf=1.00) C*Cf (100-yr Cf=1.25) Length, L (ft) Slope, S (%) Ti 2-yr (min) Ti 10-yr (min) Ti 100-yr (min) Length, L (ft) Slope, S (%) Velocity, V (ft/s) Tt (min) Length, L (ft) Slope, S (%) Velocity, V (ft/s) Rational Method Equation: Project: Johnson Drive Apartments Calculations By: Date: From Section 3.2.1 of the CFCSDDC Rainfall Intensity: hw1 HW1 1.73 5 5 5 0.87 0.87 1.00 2.85 4.87 9.95 4.29 7.33 17.24 he1 HE1 0.81 16 16 15 0.36 0.36 0.45 1.81 3.08 6.62 0.52 0.89 2.38 hs1 HS1 0.27 5 5 5 0.15 0.15 0.19 2.85 4.87 9.95 0.11 0.19 0.49 N/A HW1 (Impervious) 1.56 5 5 5 0.95 0.95 1.00 2.85 4.87 9.95 4.21 7.20 15.48 N/A HW1 (Pervious) 0.18 10 10 10 0.15 0.15 0.19 2.26 3.86 7.88 0.06 0.10 0.26 N/A HE1 (Impervious) 0.21 6 6 5 0.95 0.95 1.00 2.67 4.56 9.95 0.53 0.90 2.08 N/A HE1 (Pervious) 0.60 19 19 18 0.15 0.15 0.19 1.65 2.82 5.92 0.15 0.25 0.66 N/A HS1 (Impervious) 0.00 5 5 5 0.00 0.00 0.00 2.85 4.87 9.95 0.00 0.00 0.00 N/A HS1 (Pervious) 0.27 5 5 5 0.15 0.15 0.19 2.85 4.87 9.95 0.11 0.19 0.49 Total allowable release from Basin Hs1 = 0.11 C2 Total allowable release from Basin Hs1 = 2.22 Total allowable release from Basin HN1 = 15.54 Flow, Q10 (cfs) Flow, Q100 (cfs) C10 C 100 Total Release = 17.88 HISTORIC RUNOFF COMPUTATIONS Intensity, i2 (in/hr) Intensity, i10 (in/hr) Intensity, i100 (in/hr) Notes C. Snowdon October 3, 2019 Rainfall Intensity taken from the City of Fort Collins Storm Drainage Design Criteria (CFCSDDC), Figure 3.1 Design Point Basin(s) Area, A (acres) 2-yr Tc (min) 10-yr Tc (min) 100-yr Tc (min) Flow, Q2 CHARACTER OF SURFACE: Runoff Coefficient Percentage Impervious Project: Johnson Drive Apartments Streets, Parking Lots, Roofs, Alleys, and Drives: Calculations By: Asphalt ……....……………...……….....…...……………….………………………………….0.. 95 100% Date: Concrete …….......……………….….……….………………..….………………………………… 0.95 90% Gravel ……….…………………….….………………………….0.15 .……………………………….0.. 50 40% Roofs …….…….………………..……………….…………………………………………….. 0.95 90% Pavers…………………………...………………..……………………………………………..0.40 22% Lawns and Landscaping Sandy Soil ……..……………..……………….…………………………………………….. 0.15 0% Clayey Soil ….….………….…….…………..………………………………………………. 0.25 0% 2-year Cf = 1.00 100-year Cf = 1.25 Basin ID Basin Area (s.f.) Basin Area (ac) Area of Asphalt (ac) Area of Concrete (ac) Area of Roofs (ac) Area of Gravel (ac) Area of Pavers (ac) Area of Lawns and Landscaping (ac) 2-year Composite Runoff Coefficient 10-year Composite Runoff Coefficient 100-year Composite Runoff Coefficient Composite % Imperv. A1 72641 1.668 0.000 0.000 1.668 0.000 0.000 0.000 0.95 0.95 1.00 90% OW1 4061 0.093 0.000 0.000 0.000 0.000 0.000 0.093 0.15 0.15 0.19 0% OS1 13093 0.301 0.000 0.047 0.000 0.000 0.000 0.254 0.27 0.27 0.34 14% OS2 11338 0.260 0.000 0.000 0.000 0.000 0.000 0.260 0.15 0.15 0.19 0% ON1 20964 0.481 0.105 0.166 0.000 0.000 0.000 0.210 0.60 0.60 0.75 53% TOTAL 122097 2.80 0.105 0.213 1.668 0.000 0.000 0.818 0.72 0.72 0.90 64% DEVELOPED COMPOSITE % IMPERVIOUSNESS AND RUNOFF COEFFICIENT CALCULATIONS Runoff Coefficients are taken from the City of Fort Collins Storm Drainage Design Criteria and Construction Standards, Table 3-3. % Impervious taken from UDFCD USDCM, Volume I. Overland Flow, Time of Concentration: Project: Johnson Drive Apartments Calculations By: Date: Gutter/Swale Flow, Time of Concentration: Tt = L / 60V Tc = Ti + Tt (Equation RO-2) Velocity (Gutter Flow), V = 20·S½ Velocity (Swale Flow), V = 15·S½ NOTE: C-value for overland flows over grassy surfaces; C = 0.25 Is Length >500' ? C*Cf (2-yr Cf=1.00) C*Cf (10-yr Cf=1.00) C*Cf (100-yr Cf=1.25) Length, L (ft) Slope, S (%) Ti 2-yr (min) Ti 10-yr (min) Ti 100-yr (min) Length, L (ft) Slope, S (%) Velocity, V (ft/s) Tt (min) Length, L (ft) Slope, S (%) Velocity, V (ft/s) Tt (min) 2-yr Tc Rational Method Equation: Project: Johnson Drive Apartments Calculations By: Date: From Section 3.2.1 of the CFCSDDC Rainfall Intensity: a1 A1 1.67 5 5 5 0.95 0.95 1.00 2.85 4.87 9.95 4.52 7.72 16.59 13.09 ow1 OW1 0.09 5 5 5 0.15 0.15 0.19 2.85 4.87 9.95 0.04 0.07 0.17 0.17 os1 OS1 0.30 5 5 5 0.27 0.27 0.34 2.85 4.87 9.95 0.24 0.40 1.03 1.03 os2 OS2 0.26 9 9 8 0.15 0.15 0.19 2.35 4.02 8.38 0.09 0.16 0.41 0.41 on1 ON1 0.48 9 9 7 0.60 0.60 0.75 2.30 3.93 8.80 0.66 1.14 3.18 3.18 Total 17.88 Area, A (acres) Intensity, i2 (in/hr) 100-yr Tc (min) 100-year Release Rate DEVELOPED RUNOFF COMPUTATIONS C100 Design Point Flow, Q100 (cfs) Flow, Q2 (cfs) 10-yr Tc (min) 2-yr Tc (min) C2 Flow, Q10 (cfs) Intensity, i100 (in/hr) Basin(s) C. Snowdon October 3, 2019 Intensity, i10 (in/hr) Rainfall Intensity taken from the City of Fort Collins Storm Drainage Design Criteria (CFCSDDC), Figure 3.1 C10 Q  C f  C  i  A  Page 6 of 6 D:\Projects\1285-001\Drainage\Hydrology\1285-001_Rational-Calcs.xlsx\Direct-Runoff APPENDIX B HYDRAULIC COMPUTATIONS B.1 – Storm Sewers B.2 – Inlets B.3 – Detention Facilities APPENDIX B.1 STORM SEWERS Johnson Apartments Project: 1285-001 Date: Calculation by: SJT Circular D or Da, Pipe Diameter (ft) H or Ha, Culvert Height (ft) W, Culvert Width (ft) Yt/D Q/D1.5 Q/D2.5 Yt/H Q/WH0.5 Storm A 13.09 1 13.26 2.00 0.80 0.40 4.69 2.34 N/A N/A 5.31 2.34 2.41 5.38 Type L 6.00 9.00 1.5 Culvert Parameters Spec Length of Riprap (ft) Urban Drainage pg MD-107 Design Discharge (cfs) INPUT CALCULATE October 8, 2019 OUTPUT Storm Line/Culvert Label At=Q/V (ft2) Number of Barrels Yt, Tailwater Depth (ft) Riprap Type (From Figure MD-21 or MD-22) Box Culvert Flow through each Barrel (cfs) L= 1/(2tanq)* [At/Yt)-W] (ft) CALCULATIONS FOR RIPRAP PROTECTION AT PIPE OUTLETS Circular Pipe APPENDIX B.2 INLETS Area Inlet Performance Curve: Design Point OW1 - Inline Drain A2.1 Governing Equations: At low flow depths, the inlet will act like a weir governed by the following equation: * where P = 2(L + W) * where H corresponds to the depth of water above the flowline At higher flow depths, the inlet will act like an orifice governed by the following equation: * where A equals the open area of the inlet grate * where H corresponds to the depth of water above the centroid of the cross-sectional area (A) The exact depth at which the inlet ceases to act like a weir, and begins to act like an orifice is unknown. However, what is known, is that the stage-discharge curves of the weir equation and the orifice equation will cross at a certain flow depth. The two curves can be found below: If H > 1.792 (A/P), then the grate operates like an orifice; otherwise it operates like a weir. Input Parameters: Type of Grate: 15" ADS Drop In Grate 1599CGD Shape Circular Length of Grate (ft): 1.25 Width of Grate (ft): 1.25 Open Area of Grate (ft2): 0.85 Flowline Elevation (ft): 4987.910 Allowable Capacity: 50% Depth vs. Flow: Depth Above Inlet (ft) Elevation (ft) Shallow Weir Flow (cfs) Orifice Flow (cfs) Actual Flow (cfs) 0.00 4987.91 0.00 0.00 0.00 0.10 4988.01 0.19 0.72 0.19 Q100 0.20 4988.11 0.53 1.02 0.53 0.30 4988.21 0.97 1.25 0.97 0.40 4988.31 1.49 1.44 1.44 0.50 4988.410 2.08 1.62 1.62 0.60 4988.51 2.74 1.77 1.77 0.70 4988.61 3.45 1.91 1.91 0.80 4988.71 4.21 2.04 2.04 0.90 4988.81 5.03 2.17 2.17 1.00 4988.910 5.89 2.28 2.28 Inlet at Design Point A2.1 is designed to intercept the full 100-yr flow of 0.17 cfs at the elevation 4988.01 0.00 1.00 2.00 3.00 4.00 5.00 6.00 0.00 0.10 0.20 0.30 0.40 0.50 0.60 0.70 0.80 0.90 1.00 Discharge (cfs) Stage (ft) Stage - Discharge Curves Weir Flow Orifice Flow Q  3 . 0 P H 1 . 5 APPENDIX B.3 DETENTION FACILITIES Pond No : A1 100-yr 1.00 5.00 min 1946 ft3 1.67 acres 0.045 ac-ft Max Release Rate = 13.09 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 4985 1.00 13.09 3927 1058 10 7.720 7735 0.75 9.82 5891 1845 15 6.520 9800 0.67 8.73 7854 1946 20 5.600 11222 0.63 8.18 9818 1405 25 4.980 12475 0.60 7.85 11781 694 30 4.520 13587 0.58 7.64 13745 -157 35 4.080 14309 0.57 7.48 15708 -1399 40 3.740 14990 0.56 7.36 17672 -2682 45 3.460 15601 0.56 7.27 19635 -4034 50 3.230 16182 0.55 7.20 21599 -5416 55 3.030 16698 0.55 7.14 23562 -6864 60 2.860 17194 0.54 7.09 25526 -8331 65 2.720 17715 0.54 7.05 27489 -9774 70 2.590 18166 0.54 7.01 29453 -11286 75 2.480 18637 0.53 6.98 31416 -12779 80 2.380 19078 0.53 6.95 33380 -14301 85 2.290 19504 0.53 6.93 35343 -15839 90 2.210 19930 0.53 6.91 37307 -17377 95 2.130 20275 0.53 6.89 39270 -18995 100 2.060 20641 0.53 6.87 41234 -20592 105 2.000 21042 0.52 6.86 43197 -22155 110 1.940 21383 0.52 6.84 45161 -23778 115 1.890 21778 0.52 6.83 47124 -25346 120 1.840 22124 0.52 6.82 49088 -26963 *Note: Using the method described in Urban Storm Drainage Criteria Manual Volume 2. DETENTION POND CALCULATION; MODIFIED FAA METHOD w/ Ft Collins IDF Input Variables Results Required Detention Volume Fort Collins, Colorado 1285-001 Johnson Drive Apartments Project Number : Project Name : Pond A1 A = Johnson Drive Apartments ORIFICE RATING CURVE 100-yr Detention in Building 100-yr Orifice Project: Johnson Drive Date: 10/4/2019 By: S. Thomas 100-yr WSEL= 4990.8 Orifice Plate Outflow Q 13.09 cfs Orifice Coefficient Cd 0.65 Gravity Constant g 32.2 ft/s^2 100-year head H 7.02 ft Orifice Area Ao 0.95 ft^2 Orifice Area Ao 136.39 in^2 Radius r 6.6 in Diameter d 13.2 in Orifice Curve Stage (ft) H (ft) Q (cfs) SWMM Stage Note 4983.80 0.02 0.70 0.00 Pond Invert 4984.30 0.52 3.56 0.50 4984.80 1.02 4.99 1.00 4985.30 1.52 6.09 1.50 4985.80 2.02 7.02 2.00 4986.30 2.52 7.84 2.50 4986.80 3.02 8.59 3.00 4987.30 3.52 9.27 3.50 4987.80 4.02 9.91 4.00 4988.30 4.52 10.50 4.50 4988.80 5.02 11.07 5.00 4989.30 5.52 11.61 5.50 4989.80 6.02 12.12 6.00 4990.30 6.52 12.62 6.50 4990.80 7.02 13.09 7.00 100-yr WSEL 4991.20 7.42 13.46 7.40 Overflow 10/4/2019 12:18 PM D:\Projects\1285-001\Drainage\Detention\1285-001_Pond A1 - 100 yr Restrictor.xlsx\Orifice Size APPENDIX C WATER QUALITY DESIGN COMPUTATIONS Sheet 1 of 2 Designer: Company: Date: Project: Location: 1. Basin Storage Volume A) Effective Imperviousness of Tributary Area, Ia Ia = 90.0 % (100% if all paved and roofed areas upstream of sand filter) B) Tributary Area's Imperviousness Ratio (i = Ia/100) i = 0.900 C) Water Quality Capture Volume (WQCV) Based on 12-hour Drain Time WQCV = 0.36 watershed inches WQCV= 0.9 * (0.91* i3 - 1.19 * i2 + 0.78 * i) D) Contributing Watershed Area (including sand filter area) Area = 72,641 sq ft E) Water Quality Capture Volume (WQCV) Design Volume VWQCV = 2,187 cu ft VWQCV = WQCV / 12 * Area F) For Watersheds Outside of the Denver Region, Depth of d6 = 0.43 in Average Runoff Producing Storm G) For Watersheds Outside of the Denver Region, VWQCV OTHER = 2,187 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 DWQCV = 1.5 ft B) Sand Filter Side Slopes (Horizontal distance per unit vertical, Z = 0.00 ft / ft 4:1 or flatter preferred). Use "0" if sand filter has vertical walls. C) Mimimum Filter Area (Flat Surface Area) AMin = 486 sq ft D) Actual Filter Area AActual = 1500 sq ft E) Volume Provided VT = 2250 cu ft 3. Filter Material 4. Underdrain System A) Are underdrains provided? B) Underdrain system orifice diameter for 12 hour drain time i) Distance From Lowest Elevation of the Storage y = 1.0 ft Volume to the Center of the Orifice ii) Volume to Drain in 12 Hours Vol12 = 2,187 cu ft iii) Orifice Diameter, 3/8" Minimum DO = 1 - 3 / 16 in Johnson Drive Apartments - Basin A1 Fort Collins, CO Design Procedure Form: Sand Filter (SF) Cody Snowdon Northern Engineering October 3, 2019 Choose One Choose One 18" CDOT Class C Filter Material Other (Explain): YES NO WQ - Basin A1 - UD-BMP_v3.03.xlsm, SF 10/3/2019, 1:17 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 GEOMEMBRANE PER TABLE SF-4 WITH SEPARATOR FABRIC (PER TABLE SF-3) ABOVE IT. PROVIDE SEPARATOR FABRIC BELOW THE GEOMEMBRANE AS WELL IF SUBGRADE IS ANGULAR OR COULD OTHERWISE PUNCTURE THE GEOMEMBRANE. 6-7. Inlet / Outlet Works A) Describe the type of energy dissipation at inlet points and means of conveying flows in excess of the WQCV through the outlet Notes: Design Procedure Form: Sand Filter (SF) Cody Snowdon Northern Engineering October 3, 2019 Johnson Drive Apartments - Basin A1 Fort Collins, CO Choose One YES NO WQ - Basin A1 - UD-BMP_v3.03.xlsm, SF 10/3/2019, 1:17 PM APPENDIX D EROSION CONTROL REPORT A comprehensive Erosion and Sediment Control Plan (along with associated details) will be included with the final construction drawings. It should be noted, however, that 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 along the disturbed perimeter, gutter protection in the adjacent roadways and inlet protection at 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 C0.01 and C3.00 of the Utility Plans. The 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 will 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 StormWater 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. APPENDIX E SOIL RESOURCE 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, Colorado Next Chapter Student Housing Natural Resources Conservation Service August 24, 2017 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 3—Altvan-Satanta loams, 0 to 3 percent slopes......................................... 13 53—Kim loam, 1 to 3 percent slopes.......................................................... 15 Soil Information for All Uses...............................................................................17 Soil Properties and Qualities.............................................................................. 17 Soil Erosion Factors........................................................................................17 Wind Erodibility Group (Next Chapter Student Housing)............................ 17 Wind Erodibility Index (Next Chapter Student Housing)..............................20 Soil Qualities and Features.............................................................................23 Hydrologic Soil Group (Next Chapter Student Housing)............................. 23 References............................................................................................................28 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 4490020 4490040 4490060 4490080 4490100 4490120 4490140 4490020 4490040 4490060 4490080 4490100 4490120 4490140 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 40° 33' 43'' N 105° 4' 47'' W 40° 33' 43'' N 105° 4' 38'' W 40° 33' 39'' N 105° 4' 47'' W 40° 33' 39'' N 105° 4' 38'' W N Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84 0 45 90 180 270 Feet 0 10 20 40 60 Meters Map Scale: 1:932 if printed on A landscape (11" x 8.5") 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 Map Unit Legend Larimer County Area, Colorado (CO644) Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI 3 Altvan-Satanta loams, 0 to 3 percent slopes 2.6 99.4% 53 Kim loam, 1 to 3 percent slopes 0.0 0.6% Totals for Area of Interest 2.6 100.0% 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 3—Altvan-Satanta loams, 0 to 3 percent slopes Map Unit Setting National map unit symbol: jpw2 Elevation: 5,200 to 6,200 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 Altvan and similar soils: 45 percent Satanta and similar soils: 30 percent Minor components: 25 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Altvan Setting Landform: Benches, terraces Landform position (three-dimensional): Side slope, tread Down-slope shape: Linear Across-slope shape: Linear Parent material: Mixed alluvium Typical profile H1 - 0 to 10 inches: loam H2 - 10 to 18 inches: clay loam, loam, sandy clay loam H2 - 10 to 18 inches: loam, fine sandy loam, silt loam H2 - 10 to 18 inches: gravelly sand, gravelly coarse sand, coarse sand H3 - 18 to 30 inches: H3 - 18 to 30 inches: H3 - 18 to 30 inches: H4 - 30 to 60 inches: H4 - 30 to 60 inches: H4 - 30 to 60 inches: Properties and qualities Slope: 0 to 3 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Well drained Runoff class: Low Capacity of the most limiting layer to transmit water (Ksat): Moderately high to high (0.60 to 2.00 in/hr) Depth to water table: More than 80 inches Frequency of flooding: None Frequency of ponding: None Calcium carbonate, maximum in profile: 10 percent Available water storage in profile: Very high (about 13.2 inches) Interpretive groups Land capability classification (irrigated): 3e Land capability classification (nonirrigated): 3e Custom Soil Resource Report 13 Hydrologic Soil Group: B Hydric soil rating: No Description of Satanta Setting Landform: Structural benches, terraces Landform position (three-dimensional): Side slope, tread Down-slope shape: Linear Across-slope shape: Linear Parent material: Mixed alluvium and/or eolian deposits Typical profile H1 - 0 to 9 inches: loam H2 - 9 to 18 inches: loam, clay loam, sandy clay loam H2 - 9 to 18 inches: loam, clay loam, fine sandy loam H2 - 9 to 18 inches: H3 - 18 to 60 inches: H3 - 18 to 60 inches: H3 - 18 to 60 inches: Properties and qualities Slope: 0 to 1 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Well drained Runoff class: Low Capacity of the most limiting layer to transmit water (Ksat): Moderately high to high (0.60 to 2.00 in/hr) Depth to water table: More than 80 inches Frequency of flooding: None Frequency of ponding: None Calcium carbonate, maximum in profile: 10 percent Available water storage in profile: Very high (about 27.4 inches) Interpretive groups Land capability classification (irrigated): 1 Land capability classification (nonirrigated): 3c Hydrologic Soil Group: B Hydric soil rating: No Minor Components Nunn Percent of map unit: 10 percent Hydric soil rating: No Larim Percent of map unit: 10 percent Hydric soil rating: No Stoneham Percent of map unit: 5 percent Hydric soil rating: No Custom Soil Resource Report 14 53—Kim loam, 1 to 3 percent slopes Map Unit Setting National map unit symbol: jpwx Elevation: 4,800 to 5,600 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 Kim and similar soils: 90 percent Minor components: 10 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Kim Setting Landform: Fans Landform position (three-dimensional): Base slope Down-slope shape: Linear Across-slope shape: Linear Parent material: Mixed alluvium Typical profile H1 - 0 to 7 inches: loam H2 - 7 to 60 inches: loam, clay loam, sandy clay loam H2 - 7 to 60 inches: H2 - 7 to 60 inches: Properties and qualities Slope: 1 to 3 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Well drained Runoff class: Low Capacity of the most limiting layer to transmit water (Ksat): Moderately high to high (0.60 to 2.00 in/hr) Depth to water table: More than 80 inches Frequency of flooding: None Frequency of ponding: None Calcium carbonate, maximum in profile: 15 percent Salinity, maximum in profile: Nonsaline to slightly saline (0.0 to 4.0 mmhos/cm) Available water storage in profile: Very high (about 26.5 inches) Interpretive groups Land capability classification (irrigated): 2e Land capability classification (nonirrigated): 4e Hydrologic Soil Group: B Ecological site: Loamy Plains (R067XY002CO) Custom Soil Resource Report 15 Hydric soil rating: No Minor Components Fort collins Percent of map unit: 6 percent Hydric soil rating: No Stoneham Percent of map unit: 3 percent Hydric soil rating: No Aquic haplustolls Percent of map unit: 1 percent Landform: Swales Hydric soil rating: Yes Custom Soil Resource Report 16 Soil Information for All Uses Soil Properties and Qualities The Soil Properties and Qualities section includes various soil properties and qualities displayed as thematic maps with a summary table for the soil map units in the selected area of interest. A single value or rating for each map unit is generated by aggregating the interpretive ratings of individual map unit components. This aggregation process is defined for each property or quality. Soil Erosion Factors Soil Erosion Factors are soil properties and interpretations used in evaluating the soil for potential erosion. Example soil erosion factors can include K factor for the whole soil or on a rock free basis, T factor, wind erodibility group and wind erodibility index. Wind Erodibility Group (Next Chapter Student Housing) A wind erodibility group (WEG) consists of soils that have similar properties affecting their susceptibility to wind erosion in cultivated areas. The soils assigned to group 1 are the most susceptible to wind erosion, and those assigned to group 8 are the least susceptible. 17 18 Custom Soil Resource Report Map—Wind Erodibility Group (Next Chapter Student Housing) 4490020 4490040 4490060 4490080 4490100 4490120 4490140 4490020 4490040 4490060 4490080 4490100 4490120 4490140 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 40° 33' 43'' N 105° 4' 47'' W 40° 33' 43'' N 105° 4' 38'' W 40° 33' 39'' N 105° 4' 47'' W 40° 33' 39'' N 105° 4' 38'' W N Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84 0 45 90 180 270 Feet 0 10 20 40 60 Meters Map Scale: 1:932 if printed on A landscape (11" x 8.5") sheet. Soil Map may not be valid at this scale. MAP LEGEND MAP INFORMATION Area of Interest (AOI) Area of Interest (AOI) Soils Soil Rating Polygons 1 2 3 4 4L 5 6 7 8 Not rated or not available Soil Rating Lines 1 2 3 4 4L 5 6 7 8 Not rated or not available Soil Rating Points 1 2 3 4 4L 5 6 7 8 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) Table—Wind Erodibility Group (Next Chapter Student Housing) Wind Erodibility Group— Summary by Map Unit — Larimer County Area, Colorado (CO644) Map unit symbol Map unit name Rating Acres in AOI Percent of AOI 3 Altvan-Satanta loams, 0 to 3 percent slopes 5 2.6 99.4% 53 Kim loam, 1 to 3 percent slopes 4L 0.0 0.6% Totals for Area of Interest 2.6 100.0% Rating Options—Wind Erodibility Group (Next Chapter Student Housing) Aggregation Method: Dominant Condition Component Percent Cutoff: None Specified Tie-break Rule: Lower Wind Erodibility Index (Next Chapter Student Housing) The wind erodibility index is a numerical value indicating the susceptibility of soil to wind erosion, or the tons per acre per year that can be expected to be lost to wind erosion. There is a close correlation between wind erosion and the texture of the surface layer, the size and durability of surface clods, rock fragments, organic matter, and a calcareous reaction. Soil moisture and frozen soil layers also influence wind erosion. Custom Soil Resource Report 20 21 Custom Soil Resource Report Map—Wind Erodibility Index (Next Chapter Student Housing) 4490020 4490040 4490060 4490080 4490100 4490120 4490140 4490020 4490040 4490060 4490080 4490100 4490120 4490140 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 40° 33' 43'' N 105° 4' 47'' W 40° 33' 43'' N 105° 4' 38'' W 40° 33' 39'' N 105° 4' 47'' W 40° 33' 39'' N 105° 4' 38'' W N Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84 0 45 90 180 270 Feet 0 10 20 40 60 Meters Map Scale: 1:932 if printed on A landscape (11" x 8.5") sheet. Soil Map may not be valid at this scale. MAP LEGEND MAP INFORMATION Area of Interest (AOI) Area of Interest (AOI) Soils Soil Rating Polygons 0 38 48 56 86 134 160 180 220 250 310 Not rated or not available Soil Rating Lines 0 38 48 56 86 134 160 180 220 250 310 Not rated or not available Soil Rating Points 0 38 48 56 86 134 160 180 220 250 310 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 Table—Wind Erodibility Index (Next Chapter Student Housing) Wind Erodibility Index— Summary by Map Unit — Larimer County Area, Colorado (CO644) Map unit symbol Map unit name Rating (tons per acre per year) Acres in AOI Percent of AOI 3 Altvan-Satanta loams, 0 to 3 percent slopes 56 2.6 99.4% 53 Kim loam, 1 to 3 percent slopes 86 0.0 0.6% Totals for Area of Interest 2.6 100.0% Rating Options—Wind Erodibility Index (Next Chapter Student Housing) Units of Measure: tons per acre per year Aggregation Method: Dominant Condition Component Percent Cutoff: None Specified Tie-break Rule: Higher Soil Qualities and Features Soil qualities are behavior and performance attributes that are not directly measured, but are inferred from observations of dynamic conditions and from soil properties. Example soil qualities include natural drainage, and frost action. Soil features are attributes that are not directly part of the soil. Example soil features include slope and depth to restrictive layer. These features can greatly impact the use and management of the soil. Hydrologic Soil Group (Next Chapter Student Housing) 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. Custom Soil Resource Report 23 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. Custom Soil Resource Report 24 25 Custom Soil Resource Report Map—Hydrologic Soil Group (Next Chapter Student Housing) 4490020 4490040 4490060 4490080 4490100 4490120 4490140 4490020 4490040 4490060 4490080 4490100 4490120 4490140 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 493240 493260 493280 493300 493320 493340 493360 493380 493400 493420 493440 40° 33' 43'' N 105° 4' 47'' W 40° 33' 43'' N 105° 4' 38'' W 40° 33' 39'' N 105° 4' 47'' W 40° 33' 39'' N 105° 4' 38'' W N Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84 0 45 90 180 270 Feet 0 10 20 40 60 Meters Map Scale: 1:932 if printed on A landscape (11" x 8.5") sheet. Soil Map may not be valid at this scale. 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 Table—Hydrologic Soil Group (Next Chapter Student Housing) Hydrologic Soil Group— Summary by Map Unit — Larimer County Area, Colorado (CO644) Map unit symbol Map unit name Rating Acres in AOI Percent of AOI 3 Altvan-Satanta loams, 0 to 3 percent slopes B 2.6 99.4% 53 Kim loam, 1 to 3 percent slopes B 0.0 0.6% Totals for Area of Interest 2.6 100.0% Rating Options—Hydrologic Soil Group (Next Chapter Student Housing) Aggregation Method: Dominant Condition Component Percent Cutoff: None Specified Tie-break Rule: Higher Custom Soil Resource Report 27 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 28 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 29 APPENDIX F FEMA MAPPING USGS The National Map: Orthoimagery. Data refreshed April, 2019. National Flood Hazard Layer FIRMette 0 250 500 1,000 1,500 2,000 Feet Ü 105°5'1.81"W 40°33'56.85"N 105°4'24.35"W 40°33'29.52"N SEE FIS REPORT FOR DETAILED LEGEND AND INDEX MAP FOR FIRM PANEL LAYOUT HAZARD SPECIAL FLOOD AREAS Without Zone A, V, Base A99 Flood Elevation (BFE) With BFE or Depth Zone AE, AO, AH, VE, AR Regulatory Floodway 0.of 2% 1% Annual annual Chance chance Flood flood with Hazard, average Areas depth areasdrainage of less less than than one one foot square or with mile Zone X Future ChanceAnnual Conditions Flood Hazard 1% Zone X Area Levee.to with See Reduced Notes. Flood Risk due Zone X Area with Flood Risk due to LeveeZone D NO SCREEN Area of Minimal Flood Hazard Zone X Area of Undetermined Flood Hazard Zone D Channel, Culvert, or Storm Sewer Levee, Dike, or Floodwall Cross Sections with 1% Annual Chance 17.5 Water Surface Elevation Coastal Transect Coastal Transect Baseline Profile Baseline Hydrographic Feature Base Flood Elevation Line (BFE) Effective LOMRs Limit of Study Jurisdiction Boundary Digital Data Available No Digital Data Available Unmapped This digital map flood complies maps if with it is FEMA's not void standards as described for the below. use of The accuracy basemap standards shown complies with FEMA's basemap The authoritative flood hazard NFHL information web services is derived provided directly by FEMA. from This the map was reflectnot exported changes on or 10/amendments 3/2019 at 7:subsequent 06:21 PM and to this does date and time. becomeor The superseded NFHL and effective by new data information over time. may change This elementsmap map image do not is appear: void if basemap the one or imagery, more of flood the following zone labels, legend, FIRM panel scale number, bar, map and creation FIRM effective date, community date. Map identifiers,images for unmapped regulatoryfor purposes. and unmodernized areas cannot be used Legend OTHER FLOOD AREAS HAZARD OF OTHER AREAS STRGUECNTUERREASL FEATURES OTHER MAP PANELS 8 1:6,000 B 20.2 The point pin selected displayed by the on the user map and is does an approximate not represent an authoritative property location. SITE LOCATION M D H Y D H Y D B M X X X X X X X VAN VAN LOD LOD LOD LOD LOD LOD LOD LOD LOD LOD 15947 - 4984.8 NAVD 88 16110 - 4985.2 NAVD 88 16451 - 4987.6 NAVD 88 89.38 89.38 89.38 87.19 96.50 89.41 FFE=87.18 FFE=87.18 FFE=87.18 JOHNSON DRIVE SPRING COURT E E G G E E E E E E FDC BURLINGTON NORTHERN RAILWAY AND MAX GUIDEWAY PORTION OF LOT 3, BANK CENTER SQUARE 87.18 87.72 30" VERTICAL CURB AND GUTTER DRAINAGE SWALE FEMA FLOODWAY FEMA 100-YEAR MODERATE RISK FLOODPLAIN DETENTION VAULT MAP PACKET E E E E G G G E E E E E E E E E FDC VAN VAN LOD LOD LOD LOD LOD LOD LOD LOD LOD LOD LOD LOD LOD LOD LOD M D B M D ST X X X X X X X X X X JOHNSON DRIVE SPRING COURT BURLINGTON NORTHERN RAILWAY AND MAX GUIDEWAY PORTION OF LOT 3, BANK CENTER SQUARE a1 FFE=87.18 A1 OS1 OW1 ON1 OS2 ow1 os2 DRAINAGE SWALE SHERWOOD LATERAL EXISTING STORM INLET EXISTING STORM MH EXISTING 12" ADS FEMA 100-YEAR FLOODWAY FEMA 100-YEAR MODERATE RISK FLOODPLAIN INLET A2.1 MH A2 SUMP MH STRM A1 - TIE TO BUILDING OUTFALL APPROXIMATE LOCATION OF SAND FILTER AND 100-YR DETENTION VAULT TO BE OUTFALL TO BE ROUTED UNDER GARAGE FLOOR TO CONNECTION AT NORTHWEST CORNER OF BUILDING No. Revisions: By: Date: REVIEWED BY: S. Thomas DESIGNED BY: DRAWN BY: SCALE: DATE: 10/09/2019 PROJECT: 1285-001 Sheet of 19 JOHNSON DRIVE APARTMENTS These drawings are instruments of service provided by Northern Engineering Services, Inc. and are not to be used for any type of construction unless signed and sealed by a Professional Engineer in the employ of Northern Engineering Services, Inc. NOT FOR CONSTRUCTION REVIEW SET 301 North Howes Street, Suite 100 Fort Collins, Colorado 80521 E NGINEER ING N O R T H E RN PHONE: 970.221.4158 www.northernengineering.com 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. Call before you dig. R NORTH ( IN FEET ) 0 1 INCH = 20 FEET 20 20 40 60 C6.00 DRAINAGE EXHIBIT LEGEND: RUNOFF SUMMARY: PROJECT BOUNDARY DESIGN POINT PROPOSED STORM SEWER EXISTING STORM INLET PROPOSED CURB & GUTTER 1. REFER TO "FINAL DRAINAGE REPORT FOR JOHNSON DRIVE APARTMENTS DATED 10/09/2019" FOR ADDITIONAL INFORMATION 2. THE NATURAL HABITAT BUFFER ZONE IS INTENDED TO BE MAINTAINED IN NATIVE LANDSCAPE. PLEASE SEE SECTION 3.4.1 OF THE LAND USE CODE FOR ALLOWABLE USES WITHIN THE NATURAL HABITAT BUFFER ZONE. 3. DEVELOPMENT MUST COMPLY WITH THE FLOODPLAIN REGULATIONS IN CHAPTER 10 OF THE CITY MUNICIPAL CODE. 4. REFER TO NOTES ON FLOODPLAIN EXHIBIT SHEET C6.01 FOR ALL FLOODPLAIN REGULATIONS, PERMIT REQUIREMENTS, ETC. EXISTING STORM MANHOLE D A2 a3 (4:1) PROPOSED MAJOR CONTOUR EXISTING MAJOR CONTOUR EXISTING MINOR CONTOUR PROPOSED MINOR CONTOUR PROPOSED SLOPE (RISE:RUN) 4:1 DRAINAGE BASIN MINOR/MAJOR COEFF. DRAINAGE BASIN ID EXISTING SLOPE (RISE:RUN) EXISTING CONCENTRATED FLOW PROPOSED CONCENTRATED FLOW PROPOSED OVERLAND FLOW NOTES: EROSION BUFFER ZONE EXISTING STORM SEWER ST BASIN ID TOTAL AREA (acres) C2 C100 Q2 (cfs) Q100 (cfs) A1 1.668 0.95 1.00 4.52 16.59 OW1 0.093 0.15 0.19 0.04 0.17 OS1 0.301 0.27 0.34 0.24 1.03 OS2 0.260 0.15 0.19 0.09 0.41 ON1 0.481 0.72 0.75 0.66 3.18 FOR DRAINAGE REVIEW ONLY NOT FOR CONSTRUCTION 18 OUTFALL SHERWOOD IRRIGATION DITCH NATURAL HABITAT BUFFER ZONE TOP OF BANK LIMITS OF DISTURBANCE SWALE 86.06 86.72 FFE=87.18 FFE=87.18 FFE=89.38 FFE=89.38 FFE=89.38 FFE=87.18 FFE=89.38 ENTRANCE TO SECOND LEVEL APPROXIMATE FLOOD OPENINGS (GREY DASHED LINE) APPROXIMATE FLOOD OPENINGS (GREY DASHED LINE) 16198 - 4985.9 NAVD 88 ELEVATOR SUMP ELEVATION 82.18 (EQUIPMENT TO BE LOCATED ON ROOF) PARKING STRUCTURE BELOW RESIDENTIAL (66,000 SQ. FT.) No. Revisions: By: Date: REVIEWED BY: S. Thomas DESIGNED BY: DRAWN BY: SCALE: DATE: 10/09/2019 PROJECT: 1285-001 Sheet of 19 JOHNSON DRIVE APARTMENTS These drawings are instruments of service provided by Northern Engineering Services, Inc. and are not to be used for any type of construction unless signed and sealed by a Professional Engineer in the employ of Northern Engineering Services, Inc. NOT FOR CONSTRUCTION REVIEW SET 301 North Howes Street, Suite 100 Fort Collins, Colorado 80521 E NGINEER ING N O R T H E RN PHONE: 970.221.4158 www.northernengineering.com 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. Call before you dig. R C6.01 FLOODPLAIN EXHIBIT FOR DRAINAGE REVIEW ONLY NOT FOR CONSTRUCTION NORTH ( IN FEET ) 0 1 INCH = 30 FEET 30 30 60 90 19 LEGEND: PROJECT BOUNDARY PROPOSED STORM SEWER EXISTING STORM INLET PROPOSED CURB & GUTTER BASE FLOOD ELEVATION (BFE) EXISTING STORM MANHOLE D PROPOSED MAJOR CONTOUR EXISTING MAJOR CONTOUR EXISTING MINOR CONTOUR PROPOSED MINOR CONTOUR NOTES: CROSS SECTION (CSL) EXISTING STORM SEWER ST 1. REFER TO THE PLAT FOR LOT AREAS, TRACT SIZES, EASEMENTS, LOT DIMENSIONS, UTILITY EASEMENTS, OTHER EASEMENTS, AND OTHER SURVEY INFORMATION 2. THIS PROJECT IS LOCATED WITHIN A FEMA 100-YEAR FLOODWAY AND FLOOD FRINGE AND MUST COMPLY WITH CHAPTER 10 OF THE CITY CODE. 3. ALL ELEVATIONS DEPICTED IN PLAN VIEW AND BENCHMARKS LISTED HEREON ARE PER NAVD 88 DATUM. 4. ANY ITEMS LOCATED IN THE FLOODWAY THAT CAN FLOAT (E.G., PICNIC TABLES, BIKE RACKS, ETC.) MUST BE ANCHORED. 5. THE LOWEST FLOOR AND THE FINISHED FLOOR FOR ANY BUILDING IN THE FLOODPLAIN SHALL BE FLOODPROOFED UP TO THE REGULATORY FLOOD PROTECTION ELEVATION. 6. A FLOODPLAIN USE PERMIT SHALL BE REQUIRED FOR EACH STRUCTURE AND EACH SITE CONSTRUCTION ELEMENT IN THE FLOODPLAIN. 7. A FLOODPLAIN USE PERMIT AND NO RISE CERTIFICATION IS REQUIRED PRIOR TO PERFORMING ANY WORK WITHIN THE FLOODWAY (I.E., CURB CUT REMOVAL, LANDSCAPING). 8. THE FLOODPLAIN USE PERMIT FOR THE BUILDING WILL BE SUBMITTED AT THE TIME OF THE BUILDING PERMIT APPLICATION. 9. A FLOODPROOFING CERTIFICATE SHALL BE COMPLETED AND APPROVED BEFORE THE CERTIFICATE OF OCCUPANCY IS ISSUED FOR ANY STRUCTURE IN THE FLOODPLAIN. 10. THE FLOODPROOFING REQUIREMENTS OF CHAPTER 10 OF THE CITY CODE WILL BE SATISFIED PRIOR TO ISSUANCE OF A BUILDING PERMIT. 11. NO STORAGE OF MATERIALS OR EQUIPMENT SHALL BE ALLOWED IN THE FLOODWAY, WHETHER TEMPORARY (DURING CONSTRUCTION) OR PERMANENT. LANDSCAPING SHALL ALSO MEET THE REQUIREMENTS FOR NO RISE IN THE FLOODWAY. 12. REFER TO THE FINAL DRAINAGE REPORT FOR JOHNSON DRIVE APARTMENTS DATED 10/09/2019 FOR ADDITIONAL INFORMATION. 13. ALL HVAC EQUIPMENT IS SUBJECT TO CHAPTER 10 FLOOD PROTECTION REQUIREMENTS. 14. REFER TO ARCHITECTURAL DOCUMENTS FOR ADDITIONAL FLOODPROOFING INFORMATION. 15. THE GROUND LEVEL PARKING DECK SHALL SUPPLY 1 SQUARE INCH OF VENTING FOR EVERY 1 SQUARE FOOT OF ENCLOSED AREA. THE OVERALL AREA OF THE GROUND LEVEL PARKING DECK IS 66,000 SQ. FT., RESULTING IN 66,000 SQ. IN. OF THEE GARAGE TO BE VENTED. 16. THE BOTTOM OF THE VENT SHALL NOT BE HIGHER THAN 1 FOOT ABOVE FINISH GRADE. 17. THE VENTING SHALL BE ON TWO SIDES LOCATED ON THE NORTHERN AND EASTERN FACE OF THE GARAGE AREA. 15869 - 4984.50 NAVD 88 FEMA FLOODWAY FEMA 100-YEAR MODERATE RISK PROJECT BENCHMARKS: City of Fort Collins Benchmark S-402 Elevation: 4997.54 (NAVD 88) Elevation: 4994.37 (NVGD 29) City of Fort Collins Benchmark 28-92 Elevation: 5010.65 (NAVD 88) Elevation: 5007.48 (NGVD 29) COMMERCIAL DETAIL BASE FLOOD ELEVATION (COMMERCIAL) BASE FLOOD ELEVATION (RESIDENTIAL) RESIDENTIAL DETAIL of the version date(s) listed below. Soil Survey Area: Larimer County Area, Colorado Survey Area Data: Version 11, Sep 23, 2016 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: Mar 20, 2015—Oct 15, 2016 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 26 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 11, Sep 23, 2016 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: Mar 20, 2015—Oct 15, 2016 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 22 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 11, Sep 23, 2016 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: Mar 20, 2015—Oct 15, 2016 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 19 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 11, Sep 23, 2016 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: Mar 20, 2015—Oct 15, 2016 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 Tc = Project Location : Design Point C = Design Storm Page 1 of 1 1285-001_Pond A1_DetentionVolume_FAAModified Method.xls Q  0 . 67 A ( 2 gH ) 0 . 5 (Figure MD-21) Rectangular Pipe (Figure MD-22) Spec Width of Riprap (ft) 2*d50, Depth of Riprap (ft) for L/2 Froude Parameter Q/D2.5 Max 6.0 or Q/WH1.5 Max 8.0 Expansion Factor 1/(2tanq) (From Figure MD-23 or MD-24) (min) 10-yr Tc (min) 100-yr Tc (min) a1 A1 No 0.95 0.95 1.00 N/A N/A N/A N/A 209 0.50% 1.41 2.5 N/A N/A N/A 5 5 5 ow1 OW1 No 0.15 0.15 0.19 20 25.00% 2.7 2.7 2.6 N/A N/A N/A 171 2.92% 2.56 1.1 5 5 5 os1 OS1 No 0.27 0.27 0.34 24 45.92% 2.1 2.1 1.9 N/A N/A N/A N/A N/A N/A 5 5 5 os2 OS2 No 0.15 0.15 0.19 34 5.11% 6.0 6.0 5.8 N/A N/A N/A 335 2.00% 2.12 2.6 9 9 8 on1 ON1 No 0.60 0.60 0.75 81 2.11% 6.6 6.6 4.6 264 0.59% 1.54 2.9 N/A N/A N/A 9 9 7 DEVELOPED TIME OF CONCENTRATION COMPUTATIONS Gutter/Internal Building Flow Swale Flow Design Point Basin Overland Flow C. Snowdon October 3, 2019 Time of Concentration (Equation RO-4)   3 1 1 . 87 1 . 1 * S C Cf L Ti   Page 5 of 6 D:\Projects\1285-001\Drainage\Hydrology\1285-001_Rational-Calcs.xlsx\Tc-10-yr_&_100-yr 10-year Cf = 1.00 October 3, 2019 **Soil Classification of site is Sandy Loam** C. Snowdon Page 4 of 6 D:\Projects\1285-001\Drainage\Hydrology\1285-001_Rational-Calcs.xlsx\C-Values (cfs) Q  C f  C  i  A  Page 3 of 6 D:\Projects\1285-001\Drainage\Hydrology\1285-001_Rational-Calcs.xlsx\Hist-Direct-Runoff Tt (min) 2-yr Tc (min) 10-yr Tc (min) 100-yr Tc (min) hw1 HW1 No 0.87 0.87 1.00 35 5.00% 1.5 1.5 0.6 425 0.90% 1.90 3.7 N/A N/A N/A 5 5 5 he1 HE1 No 0.36 0.36 0.45 85 1.01% 12.8 12.8 11.2 298 0.50% 1.41 3.5 N/A N/A N/A 16 16 15 hs1 HS1 No 0.15 0.15 0.19 24 45.92% 2.4 2.4 2.3 299 100.50% 20.05 0.2 N/A N/A N/A 5 5 5 N/A HW1 (Impervious) No 0.95 0.95 1.00 35 5.00% 1.0 1.0 0.6 425 0.90% 1.90 3.7 N/A N/A N/A 5 5 5 N/A HW1 (Pervious) No 0.15 0.15 0.19 35 5.00% 6.1 6.1 5.9 425 0.90% 1.90 3.7 N/A N/A N/A 10 10 10 N/A HE1 (Impervious) No 0.95 0.95 1.00 85 1.01% 2.6 2.6 1.7 298 0.50% 1.41 3.5 N/A N/A N/A 6 6 5 N/A HE1 (Pervious) No 0.15 0.15 0.19 85 1.18% 15.5 15.5 14.9 298 0.50% 1.41 3.5 N/A N/A N/A 19 19 18 N/A HS1 (Impervious) No 0.00 0.00 0.00 24 45.92% 2.8 2.8 2.8 N/A N/A N/A N/A N/A N/A 5 5 5 N/A HS1 (Pervious) No 0.15 0.15 0.19 24 45.92% 2.4 2.4 2.3 N/A N/A N/A N/A N/A N/A 5 5 5 HISTORIC TIME OF CONCENTRATION COMPUTATIONS C. Snowdon October 3, 2019 Design Point Basin Overland Flow Gutter Flow Swale Flow Time of Concentration (Equation RO-4)   3 1 1 . 87 1 . 1 * S C Cf L Ti   Page 2 of 6 D:\Projects\1285-001\Drainage\Hydrology\1285-001_Rational-Calcs.xlsx\Hist-Tc-10-yr_&_100-yr Existing Impervious Area Breakdown HISTORIC COMPOSITE % IMPERVIOUSNESS AND RUNOFF COEFFICIENT CALCULATIONS Notes October 3, 2019 10-year Cf = 1.00 **Soil Classification of site is Sandy Loam** Runoff Coefficients are taken from the City of Fort Collins Storm Drainage Design Criteria and Construction Standards, Table 3-3. % Impervious taken from UDFCD USDCM, Volume I. Page 1 of 6 D:\Projects\1285-001\Drainage\Hydrology\1285-001_Rational-Calcs.xlsx\Hist-C-Values