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HomeMy WebLinkAboutMOUNTAIN VIEW COMMUNITY CHURCH - FDP200020 - SUBMITTAL DOCUMENTS - ROUND 1 - DRAINAGE REPORTFINAL DRAINAGE REPORT 1501 ACADEMY CT. STE 203 | FORT COLLINS, CO 80524 | 970-530-4044 | www.unitedcivil.com MOUNTAIN VIEW COMMUNITY CHURCH A Portion of Tract A Seven Lakes Business Park P.U.D Fort Collins, CO Prepared for: Mountain View Community Church 2330 East Prospect Road Fort Collins, CO 80525 Date: October 7, 2020 FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO i U20004_Drainage Report.docx October 7, 2020 City of Fort Collins Stormwater Utility 700 Wood Street Fort Collins, Colorado 80521 RE: Mountain View Community Church Improvements Fort Collins, Colorado Project Number: U20004 Dear Staff: United Civil Design Group, LLC. is pleased to submit this Final Drainage Report for the Mountain View Community Church site in Fort Collins, Colorado. In general, this report serves to document the stormwater impacts associated with the proposed improvements related to the existing site. We understand that review by the City of Fort Collins is to assure general compliance with standardized criteria contained in the Fort Collins Stormwater Criteria Manual (FCSCM). This report was prepared in compliance with technical criteria set forth in both the Urban Drainage and Flood Control District (UDFCD) Urban Storm Drainage Criteria Manual and the Fort Collins Stormwater Criteria Manual. If you should have any questions or comments as you review this report, please feel free to contact us at your convenience. Sincerely, United Civil Design Group Colton Beck, PE Sam Eliason, PE Project Engineer Principal FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO ii U20004_Drainage Report.docx TABLE OF CONTENTS I. General Location and Description ......................................................................................................................1 A. Location and Project Description ................................................................................................. 1 B. Description of Property ................................................................................................................ 2 C. Floodplains ................................................................................................................................... 2 II. Drainage Basins and Sub-Basins .........................................................................................................................3 A. Major Basin Description ............................................................................................................... 3 B. Sub-Basin Description .................................................................................................................. 3 III. Drainage Design Criteria ....................................................................................................................................3 A. Regulations ................................................................................................................................... 3 B. Directly Connected Impervious Area (DCIA) ................................................................................ 3 C. Hydrological Criteria ..................................................................................................................... 4 D. Hydraulic Criteria.......................................................................................................................... 4 E. Modifications of Criteria .............................................................................................................. 4 IV. Drainage Facility Design .....................................................................................................................................4 A. General Concept ........................................................................................................................... 4 B. Specific Details ............................................................................................................................. 4 V. Erosion Control ...................................................................................................................................................7 VI. Conclusions ........................................................................................................................................................8 A. Compliance with Standards ......................................................................................................... 8 B. Drainage Concept ......................................................................................................................... 8 C. Stormwater Quality ...................................................................................................................... 8 VII. References ......................................................................................................................................................9 APPENDICES APPENDIX A – Hydrology Calculations APPENDIX B – Hydraulic Calculations B.1 – Low Impact Development Calculations B.2 – Water Quality Calculations B.3 – Inlet Sizing Calculations (Reserved for Final Submittal) B.4 – Storm Pipe Calculations (Reserved for Final Submittal) B.5 – Curb Channel Calculations (Reserved for Final Submittal) B.6 – Weir Calculation (Reserved for Final Submittal) APPENDIX C – Referenced Materials APPENDIX D – Drainage Exhibits FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 1 U20004_Drainage Report.docx I. GENERAL LOCATION AND DESCRIPTION A. LOCATION AND PROJECT DESCRIPTION The Mountain View Community Church site (referred herein as “the site”) exists as a portion of Tract A, Seven Lakes Business Park P.U.D, located in the southwest quarter of Section 17, T7N, R698W of the 6th P.M., City of Fort Collins, Larimer County, Colorado. The property, consisting of approximately 2.90 acres, is located north of East Prospect Road and east of South Timberline Road. The site currently exists as a commercial property with adjacent parking. The proposed Mountain View Community Church modified site improvements are limited to 0.56 acres of disturbed area. The property is bounded by the Spring Creek Trail to the north and west, and commercial properties to the south and east. Stormwater on the site currently drains in several directions away from the existing building, however, all runoff is ultimately collected by storm sewer infrastructure and conveyed to the Cattail Chorus Natural Area ponds to the north or a drainage channel to the east of the site. Ultimately both areas drain to the Cache La Poudre River, which is approximately 2000 feet east of the site. The proposed improvements to the site consist of reconstructing a portion of the building along with associated landscaping, walks, and parking around the perimeter of the building. Additionally, water quality measures are proposed with the reconstruction to improve drainage function and water quality. FIGURE 1: SITE VICINITY MAP This drainage report presents the overall drainage plan for the development. In general, this report serves to provide an analysis of the drainage impacts associated with the development of site as it relates to existing and proposed drainage facilities on-site. E Prospect Rd FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 2 U20004_Drainage Report.docx B. DESCRIPTION OF PROPERTY The project site currently exists as a fully developed commercial lot, including concrete and asphalt pavement, sidewalks, rooftop, and landscaping, comprising of an existing imperviousness of 65.3%. In its existing condition, by means of sheet flow, concrete pans, curb and gutter, inlets, and storm sewer, the site ultimately drains off-site to Cattail Chorus Natural Area ponds north the site or to a drainage channel to the east. Below are summaries of key components of the site in its existing conditions. Land Use - The site’s current land use is commercial. Ground Cover - The site exists as a commercial development with concrete and asphalt pavement, sidewalk, rooftop, and surrounding grass landscaping. The grass cover is good (ie., heavy or dense cover with nearly all ground surfaces protected by vegetation). Existing Topography – The site slopes in a multitude of directions away from the existing on-site building, however, runoff ultimately drains north to an existing downstream pond associated with the Cattail Chorus Natural Area. Grades – In general, the western portion of the site is sloped westerly and northerly at approximately 1.0% to 5.0%; the southern and eastern portions of the site are sloped easterly and northerly at approximately 1.0% to 5.0%. The northern portion of the side drains northerly off-site. Soil Type - The USDA’s Web Soil Survey shows that the site consists largely of a “Type C” soil, namely Loveland clay loam (0 to 1% slopes). The Web Soil Survey also indicates the site is comprised of Table Mountain loam (0 to 1% slopes), a “Type B” soil. The on-site soils provide moderate infiltration and are suitable for development. Utilities – The following dry utility lines run along the south side of the site: gas, electric, cable TV, fiber optic. Water mains are also present on the south side of the site within West Prospect Road. A recently constructed sanitary sewer service exists at the northwest portion of the site. Drainage Features and Storm Sewer – An off-site pond exists north of the site. On-site and off-site storm sewer infrastructure conveys runoff to the mentioned downstream pond. C. FLOODPLAINS The existing site is within the Spring Creek Floodplain which is a FEMA designated 100- year floodplain and floodway. In addition, the existing site and building is located within the limits of Poudre River 500-year floodplain. The FEMA FIRM Panel # is 08069C0983H effective 5/2/2012. A Letter of Map Amendment (LOMA) Determination Document #19-08- 0473A dated 3/27/2019 removed the building from the 100-year floodplain. The current FEMA FIRM Map along with the LOMA is included in the appendix. The proposed building will be used as a place of Worship. This is not a critical facility, which are not allowed within the Poudre River 500-year floodplain. FIGURE 2: FLOODPLAIN MAP Existing Building FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 3 U20004_Drainage Report.docx II. DRAINAGE BASINS AND SUB-BASINS A. MAJOR BASIN DESCRIPTION The existing site is located within both the Spring Creek and Cache La Poudre River master drainage basins. The northern portion of the site drains downstream within the Spring Creek Basin, while the southern portion of the site drains east, ultimately conveyed to the Cache La Poudre River. No known master planning improvements are associated with or adjacent to the site. B. SUB-BASIN DESCRIPTION The site, along with the rest of Tract A, is included within the Seven Lakes Business Park P.U.D completed by Parsons & Associates in January 1982. A Site Drainage and Grading Plan associated with this P.U.D is included in the Appendix. A drainage report could not be located. The approved P.U.D provides context for how the overall Tract A portion of the Seven Lakes Business Park was designed to drain and is somewhat similar to existing drainage patterns. The site exists within Basins A3 and B of the mentioned Site Drainage and Grading Plan. Basin A3 drains north within the Spring Creek drainage basin; Basin B drains south and east within the Cache La Poudre drainage basin. More recent drainage reports and letters related to the Seven Lakes Business Park are recorded with the City of Fort Collins, however, documents specifically related to this site are not recorded. III. DRAINAGE DESIGN CRITERIA A. REGULATIONS The design criteria for this study are directly from the City of Fort Collins Storm Drainage Design Criteria and Construction Standards Manual and the Urban Storm Drainage Criteria Manuals Volumes 2, and 3 (referred to herein as USDCM). B. DIRECTLY CONNECTED IMPERVIOUS AREA (DCIA) With the adoption of the USDCM, the City has also adopted the “Four Step Process” that is recommended in Volume 3 of the USDCM in selecting structural BMPs for the redeveloping urban areas. The following portions of this summary describe each step and how it has been utilized for this project: Step 1 – Employ Runoff Reduction Practices The objective of this step is to reduce runoff peaks and volumes and to employ the technique of “minimizing directly connected impervious areas” (MDCIA). This project accomplishes this by: Routing the roof and pavement flows through bioretention facilities and vegetated buffers to increase the time of concentration, promote infiltration and provide water quality. Step 2 – Provide Water Quality Capture Volume (WQCV) The objective of providing WQCV is to reduce the sediment load and other pollutants that exit the site. For this project WQCV is provided within the bioretention facilities. Step 3 – Stabilize Drainageways The site is adjacent to Spring Creek and the use of LID will help slow runoff from the site and benefit the stabilization of the Spring Creek drainageway. In addition, this project will pay stormwater development and stormwater utility fees which the City uses, in part, to maintain the stability of the City drainageway systems. Step 4 – Consider Need for Site Specific and Source Control BMPs Site specific and source control BMPs are generally considered for large industrial and commercial sites. The redevelopment of the existing site will include multiple site specific and source controls, including: • Dedicated maintenance personnel providing landscape maintenance and snow and ice management. FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 4 U20004_Drainage Report.docx C. HYDROLOGICAL CRITERIA City of Fort Collins Rainfall Intensity-Duration-Frequency Curves, provided by Figure RA-16 of the Fort Collins Stormwater Criteria Manual, are utilized for all hydrologic computations related to the site in its existing/historic and proposed conditions. Since this site is relatively small and does not have complex drainage basins, the peak flow rates for design points have been calculated based on the Rational Method as described in the USDCM and the City of Fort Collins Stormwater Criteria Manual (FCSCM) with storm duration set equal to the time of concentration for each sub-basin. This method was used to analyze the developed runoff from the 10-year (minor) and the 100-year (major) storm events. The Rational Method is widely accepted for drainage design involving small drainage areas (less than 160 acres) and short time of concentrations. Runoff coefficients are assumed based on impervious area and are given in the Appendices. D. HYDRAULIC CRITERIA The developed site will convey runoff to existing design points via swales, concrete pans, and pipes. The City of Fort Collins Stormwater Criteria Manual (FCSCM) and USDCM are referenced for all hydraulic calculations. In addition, the following computer programs are utilized: • Storm Sewer Extension for AutoCAD Civil3D • Hydraflow Express Extension for AutoCAD Civil3D • UD-Inlet by UDFCD Drainage conveyance facility capacities proposed with the development project, including swales and bioretention ponds, are designed in accordance with criteria outlined in the FCSCM and/or the Urban Drainage and Flood Control District’s Urban Storm Drainage Criteria Manual (UDFCD). E. MODIFICATIONS OF CRITERIA The drainage design of the MVCC improvements does not vary from City of Fort Collins criteria. IV. DRAINAGE FACILITY DESIGN A. GENERAL CONCEPT Developed runoff is designed to largely maintain existing drainage patterns. Existing conveyance methods include sheet flow, concrete pans, curb and gutter, inlets, and storm sewer that ultimately drain runoff off-site to Cattail Chorus Natural Area ponds north the site. Runoff that drains off-site to the east is ultimately conveyed to the Cache La Poudre River by means of existing storm sewer infrastructure and drainage swales related to Tract B and Tract C of the Seven Lakes Business Park. Per City standards, stormwater detention is not being provided because the increase in impervious surfaces is less than 1,000 square-feet. Per City standards, water quality and low impact development (LID) is being proposed with project to mitigate the impervious areas that are being modified with the development. This includes a proposed bioretention pond on the north side of the building and a new storm drain system that conveys runoff to the vegetative buffer on the west side of the property. B. SPECIFIC DETAILS Hydrology Site improvements include an increase of approximately 601-sf of additional impervious area relative to existing conditions. Due to the minimal impacts related to the site’s overall imperviousness (i.e. less than 1,000 sf), the proposed improvements are not expected to negatively impact the existing nearby hydraulic features. The table on the following page summarizes the hydrologic impact associated with the proposed site improvements relative to existing conditions. Refer to the drainage exhibits and hydrology calculations attached for additional information. FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 5 U20004_Drainage Report.docx MVCC Site Existing Proposed Overall Area (acre) 2.90 2.90 *Roof (sf) 36,667 37,606 *Asphalt (sf) 36,862 34,709 *Concrete (sf) 13,123 14,482 *Gravel (sf) - 536 *Landscape (sf) 39,608 38,927 % Imperviousness 66.4% 66.6% Composite C2 0.73 0.73 Composite C100 0.91 0.92 TABLE 1 - HYDROLOGIC SUMMARY For purposes of Low Impact Development (LID) calculations, hydrology calculations related to the “modified” site area (limited to 0.56 acres of site modifications) are included in Appendix B. On-site Basins The following basins provide drainage delineations for the site in its improved condition. Note that basin designations are not bound by property lines; the site receives additional off-site runoff in its existing condition. Refer to Appendix A for hydrology computations and Appendix B for calculations related to Water Quality, Low Impact Development, and other hydraulic features. Basin A Sub-basins A1-A3 (see Drainage Plan attached) are generally located around the north and northwest region of the site. These basins consist of roofs, retaining walls and landscaping. Runoff within these Basins is conveyed to a proposed bioretention pond via sheet flow and roof drains. Runoff conveyed to the bioretention pond system is ultimately discharged to an existing on-site inlet on the north side of the existing building. This inlet currently conveys runoff off-site to the north, downstream within the Spring Creek drainage basin. Basin B Sub-basins B1-B2 represent on-site and off-site drainage basins where runoff is captured and conveyed to an on-site vegetative buffer area. These basins consist of roofs, concrete and asphalt paving, and landscaping. Sub-basin B1 largely consists of a parking lot, and Basin B2 consists solely of roof area. Runoff within sub-basin B1 is conveyed to the vegetative buffer via pans, curb and storm sewer infrastructure, while runoff within sub-basin B2 is conveyed to the vegetative buffer via roof drains/storm sewer. Basin C Sub-basin C1 is an on-site basin that consists of modified roof area. Similar to existing conditions, runoff is conveyed to the access drive immediately south of the existing building. This runoff drains east to an existing, off-site inlet, and ultimately to the Cache La Poudre River. Stormwater Quality Stormwater quality is required to be provided for the total new or modified impervious area on the site. The scope of the MVCC site improvements do not include extensive parking lot work. City staff determined that the permeable paver requirement does not apply to this project. The project is required to provide a minimum of 50% LID treatment, for all new or modified impervious areas, using any approved LID method. The remaining 50% can be treated with LID or ‘standard’ water quality methods. FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 6 U20004_Drainage Report.docx WATER QUALITY REQUIRED: TOTAL NEW OR MODIFIED IMPERVIOUS AREA = 18,850 SF REQUIRED LID WQ TREATMENT = 9,425 SF (50% MIN) WATER QUALITY PROVIDED: BIORETENTION (LID) FOR BASINS A1, A2, & A3 = 9,780 SF (52%) VEGETATIVE BUFFER (STANDARD WQ) FOR BASINS B1 & B2 = 29,332 SF TOTAL IMPERVIOUS AREA TREATED = 39,112 SF I. Bioretention Bioretention is designed to remove sediment and pollution from stormwater runoff via infiltration through an engineered sand media. This slows the conveyance rate of storm water runoff, reduces runoff and provides a flow path across a vegetated surface. A bioretention pond is proposed with the site improvements and is utilized to convey and treat stormwater prior to release to an existing inlet that drains off-site to the north. The proposed bioretention ponds are located immediately north of the existing building. Provided 12-inches of depth, the ponds are hydraulically connected by a 6” pipe and they are designed to provide a water quality capture volume of 351-cf – this volume exceeds the required WQCV for Basins A1-A3 (317-cf). Below is a summary of the bioretention pond: Bottom of Bioretention Pond Elevation Bioretention WSEL Bioretention Volume Required (cf) Bioretention Volume Provided (cf) 4907.20 4908.20 317 343 II. Vegetated Buffer A vegetated buffer with an approximate area of 6,605-sf is utilized for water quality purposes with the site improvements. This buffer treats basins B1 and B2 (see drainage plan attached) which has a total impervious area of 29,332 sf. This buffer is designed to improve stormwater runoff quality by straining sediment and promoting infiltration. To distribute the concentrated flows of this buffer, an 84 lf level spreader is being provided downstream of the concentrated flows. Refer to Appendix B for Grass Buffer calculations and minimum length of the level spreader. Low Impact Development (LID) In December of 2015, Fort Collins City Council adopted the revised Low Impact Development (LID) policy and criteria which requires developments within City limits to meet certain enhanced stormwater treatment requirements in addition to more standard treatment techniques. The scope of the MVCC site improvements do not include extensive parking lot disturbance or construction. City of Fort Collins staff determined that the permeable paver requirement does not apply to this project. The project is required to provide a minimum 50% LID treatment, for all new or modified impervious area, using any approved LID method. The remaining 50% can be treated with LID or standard water quality methods. The following measures are implemented with this proposed development: I. Bioretention Basins A1-A3, with an impervious area of 9,780, are designed to be conveyed to the bioretention ponds associated with the site improvements. The proposed impervious area treated through bioretention includes existing roof and landscape areas. Refer to Appendix B for additional information. The inclusion of bioretention measures support that more than 50% of the modified site area requiring the use of LID treatment is provided with the site improvements. Refer to Appendix B for calculations. FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 7 U20004_Drainage Report.docx Detention Detention is not being provided with the redevelopment of the site because the net increase in impervious surfaces is less than 1,000 square-feet. Standard Operating Procedures (SOPs) In order for physical stormwater Best Management Practices (BMPs) to be effective, proper maintenance is essential. Maintenance includes both routinely scheduled activities, as well as non-routine repairs that may be required after large storms, or as a result of other unforeseen problems. Standard Operating Procedures should clearly identify BMP maintenance responsibility. BMP maintenance is typically the responsibility of the entity owning the BMP. Identifying who is responsible for maintenance of BMPs and ensuring that an adequate budget is allocated for maintenance is critical to the long-term success of BMPs. Maintenance responsibility may be assigned either publicly or privately. For this project, the privately owned BMPs including grass swales and the bioretention pond, are to be maintained by the property owner. Storm Sewer There are multiple storm sewers, roof drains and underdrains for the bioretention ponds proposed with the site improvements. All storm sewers will be private and are sized to accommodate the flows from the 100-year storm event. Hydraulic computations of these systems are included in Appendix B. Inlets There are multiple inlets proposed with the site improvements. Inlets are utilized to support the proposed site modifications in addition to existing site drainage insufficiencies. A Type 13 inlet associated with Basin B1 is proposed with site improvements. Due to existing site constraints and the desire to only capture minor flows for water quality purposes, this inlet is limited to capturing 1.5-cfs – additional runoff related to Basin B1 will continue to drain downstream in accordance with existing drainage patterns. Other proposed inlets are designed to convey the 100-year storm event. Hydraulic computations of these systems are included in Appendix B. V. EROSION CONTROL Erosion control, both temporary and permanent, is a vital part of any development project. For this project, the site disturbance is less than 1 acre; therefore, a CDPHE Stormwater Management Plan (SWMP) is not required. However, comprehensive erosion control measures are included with the site improvements. Refer to the Utility Plans for additional information. At a minimum, the following temporary BMP’s will be installed and maintained to control on-site erosion and prevent sediment from traveling off-site during construction: • Silt Fence – a woven synthetic fabric that filters runoff. The silt fence is a temporary barrier that is placed at the base of a disturbed area. • Vehicle Tracking Control – a stabilized stone pad located at points of ingress and egress on a construction site. The stone pad is designed to reduce the amount of mud transported onto public roads by construction traffic. • Inlet Protection – acts as a sediment filter. It is a temporary BMP and requires proper installation and maintenance to ensure their performance. • Straw Wattles – wattles act as a sediment filter in swales around inlets. They are a temporary BMP and require proper installation and maintenance to ensure their performance. The contractor shall store all construction materials and equipment and shall provide maintenance and fueling of equipment in confined areas on-site from which runoff will be contained and filtered. Temporary Best Management Practices (BMP’s) will be inspected by the contractor at a minimum of once every two weeks and after each significant storm event. FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 8 U20004_Drainage Report.docx VI. CONCLUSIONS A. COMPLIANCE WITH STANDARDS Storm drainage calculations have followed the guidelines provided by the Urban Storm Drainage Criteria Manuals Volumes 1, 2 and 3 and the City of Fort Collins Stormwater Criteria Manual. B. DRAINAGE CONCEPT The drainage system has been designed to convey the runoff to the designated design points and the existing public infrastructure in an effective, safe manner. No negative impacts are anticipated to the City of Fort Collins Master Drainage Plan or to downstream properties or infrastructure due to the proposed improvements. C. STORMWATER QUALITY Multiple long-term stormwater quality measures have been selected for the site that will provide treatment of stormwater prior it to being discharged from the site. For this site this includes a bioretention pond and vegetated buffers. FINAL DRAINAGE REPORT MOUNTAIN VIEW COMMUNITY CHURCH FORT COLLINS, CO 9 U20004_Drainage Report.docx VII. REFERENCES 1. City of Fort Collins Stormwater Criteria Manual, City of Fort Collins, Colorado, November 2017. 2. Urban Storm Drainage Criteria Manual Volume 1 and 2, Urban Drainage and Flood Control District, Denver, Colorado, June 2001, Revised April 2008. 3. Site Drainage and Grading Plan, Parsons & Associates, Fort Collins, Colorado, last revised 8/5/1985. 4. Natural Resources Conservation Service Web Soil Survey at: websoilsurvey.nrcs.usda.gov/app 5. Flood Insurance Rate Map, FEMA, Panel 08069C0983H, https://hazards.fema.gov/femaportal/ 6. Stormwater Discharges Associated with Construction Activity, Stormwater Management Plan Preparation Guides, State of Colorado, www.colorado.com APPENDIX A HYDROLOGY CALCULATIONS APPENDIX B HYDRAULIC CALCULATIONS APPENDIX C REFERENCED MATERIALS APPENDIX D DRAINAGE EXHIBITS APPENDIX A HYDROLOGY CALCULATIONS RUNOFF COEFFICIENTS AND % IMPERVIOUS Mountain View Community Church, Fort Collins, CO Basin Design Pt. Total Total Roof (1) Asphalt Concrete (1) Gravel (1) Lawns (10(3) Composite Effective C2 C 100 %I = 90% %I = 100% %I = 100% %I =40% %I=2% Imperviousness Impervious C=0.95 C=0.95 C=0.95 C=0.50 C=0.25 Areas acres sf sf sf sf sf sf (%) sf EX-MA Modified Area 0.56 24,441 8,010 3,369 7,112 5,950 72.9% 17,809 0.78 0.97 EX-Site Site 2.90 126,260 36,667 36,862 13,123 39,608 66.4% 83,777 0.73 0.91 Basin Design Pt. Total Total Roof (1) Asphalt Concrete (1) Gravel (1) Lawns (10(3) Composite Effective C2 C 100 acres sf %I = 90% %I = 100% %I = 100% %I =40% %I=2% Imperviousness Impervious C=0.95 C=0.95 C=0.95 C=0.50 C=0.25 Areas sf sf sf sf sf (%) sf PR-MA Modified Area 0.56 24,441 8,949 1,216 8,471 536 5,269 73.9% 18,061 0.79 0.99 PR-Site Site 2.90 126,260 37,606 34,709 14,482 536 38,927 66.6% 84,029 0.73 0.92 A1 A1 0.03 1,206 50 1,156 6.1% 0.28 0.35 A2 A2 0.06 2,592 2,592 - 90.0% 0.95 1.00 A3 A3 0.16 7,138 7,138 - 90.0% 0.95 1.00 B1 B1 0.60 26,000 20,750 2,150 3,100 88.3% 0.87 1.00 B2 B2 0.15 6,432 6,432 - 90.0% 0.95 1.00 C1 C1 0.16 6,927 6,927 - 90.0% 0.95 1.00 939 (2,153) 1,359 536 (681) 1.0% 252 939 (2,153) 1,359 536 (681) 0.2% 252 Notes: (1) Recommended % Imperviousness Values per Table 4.1-3 Surface Type - Percent Impervious in Fort Collins Stormwater Criteria Manual (2) Runoff C is based Table 3.2-2. Surface Type - Runoff Coefficients and Table 3.2-3. Frequency Adjustment Factors in Fort Collins Stormwater Manual (3) Runoff C for Lawns based off of Lawns, Clayey Soil, Avg Slope 2-7% Difference between Proposed and Existing Modified Areas Difference between Proposed and Existing Site Composite Runoff Coefficients Areas (2) Existing Basins Proposed Basins Areas Composite Runoff Coefficients (2) Date: 10/6/2020 C:\United Civil Dropbox\Projects\U20004 - Mountain View Community Church\Reports\Drainage\Calculations\U20004-Drain Calcs.xlsm RATIONAL METHOD PEAK RUNOFF Mountain View Community Church, Fort Collins, CO Basin Design Pt. Area Final acre tc (6) C2 C5 C100 I2 I5 I100 Q2 Q5 Q100 min in/hr in/hr in/hr cfs cfs cfs A1 A1 0.03 5.0 0.28 0.28 0.35 2.85 3.97 9.95 0.02 0.03 0.10 A2 A2 0.06 5.0 0.95 0.95 1.00 2.85 3.97 9.95 0.16 0.22 0.59 A3 A3 0.16 5.0 0.95 0.95 1.00 2.85 3.97 9.95 0.44 0.62 1.63 B1 B1 0.60 5.0 0.87 0.87 1.00 2.85 3.97 9.95 1.47 2.05 5.94 B2 B2 0.15 5.0 0.95 0.95 1.00 2.85 3.97 9.95 0.40 0.56 1.47 C1 C1 0.16 5.0 0.95 0.95 1.00 2.85 3.97 9.95 0.43 0.60 1.58 Notes: 2 year runoff rate Basins B1 and B2 used for calculating level spreader length. Proposed Basins Runoff Coefficients Rainfall Intensity Peak Discharge Date: 10/6/2020 C:\United Civil Dropbox\Projects\U20004 - Mountain View Community Church\Reports\Drainage\Calculations\U20004-Drain Calcs.xlsm APPENDIX B HYDRAULIC CALCULATIONS WATER QUALITY - LOW IMPACT DEVELOPMENT Mountain View CommunityChurch, Fort Collins, CO Water Quality & LID Requirements Basin Area Area Roof Asphalt Concrete Gravel (sf) (acres) (sf) (sf) (sf) (sf) PR-MA 24,441 0.561 8,949 1,216 8,471 536 Total New or Modified Impervious Area for Water Quality Treatment* 18850 sf 50% to be treated by LID WQ 9425 sf *Impervious Areas calculated based on all of the new or modified asphalt, concrete, and roof areas and 40% of new or modified gravel areas LID -Bioretention Water Quality Provided Basin Area Area Imperviousness Watershed WQCV* (sf) (acres) (%) (inches) (cf) A1 1,206 0.028 6% 0.03 4 A2 2,592 0.060 90% 0.32 83 A3 7,138 0.164 90% 0.32 229 Total WQCV Required for Bioretention 317 Total WQCV Provided In Bioretention Pond 343 * Water quality provided by bioretention and based on 12-hour drain time Impervious Area Treated by LID (Basins A1, A2, & A3) 9780 sf (meets requirements, more than 9425 sf) *Impervious Areas calculated based on asphalt, concrete, and roof areas and 40% of gravel areas draining to LID feature Non LID - Vegetative Buffer Water Quality Provided Basin Area Area Roof Asphalt Concrete Gravel (sf) (acres) (sf) (sf) (sf) (sf) B1 26,000 0.597 0 20,750 2,150 0 B2 6,432 0.148 6,432 0 0 0 Impervious Area to Vegetative Buffer 29332 sf 9070 Total Water Quality Provided Total Impervious Areas Treated 39112 sf (meets requirements, more than 18,850 sf) Date: 8/21/2020 E:\United Civil Dropbox\Projects\U20004 - Mountain View Community Church\Reports\Drainage\Calculations\U20004-Drain Calcs.xlsm Bioretention Stage Storage Volumes Mountain View CommunityChurch, Fort Collins, CO Stage Storage Volumes Delta Volume = (d/3)(A1+A2+(A1*A2) 0.5 ) Elevation delta West Pond Elev. Area East Pond Elev. Area Total Pond Elev. Area Delta Volume Cumulative Volume ft ft ft 2 ft 2 ft 2 ft 3 ft 3 4907.20 100 146 246 0 0 4907.40 0.20 121 164 285 53 53 4907.60 0.20 142 182 324 61 114 4907.80 0.20 164 200 364 69 183 4908.00 0.20 186 219 405 77 260 4908.20 0.20 208 238 446 84 343 Total 343 Date: 8/19/2020 P:\U20004 - Mountain View Community Church\Reports\Drainage\Calculations\U20004-Drain Calcs.xlsm Sheet 1 of 1 Designer: Company: Date: Project: Location: 1. Design Discharge A) 2-Year Peak Flow Rate of the Area Draining to the Grass Buffer Q2 = 2.0 cfs 2. Minimum Width of Grass Buffer WG= 40 ft 3. Length of Grass Buffer (14' or greater recommended) LG = 45 ft 4. Buffer Slope (in the direction of flow, not to exceed 0.1 ft / ft) SG = 0.010 ft / ft 5. Flow Characteristics (sheet or concentrated) A) Does runoff flow into the grass buffer across the entire width of the buffer? B) Watershed Flow Length FL= ft C) Interface Slope (normal to flow) SI= ft / ft D) Type of Flow CONCENTRATED FLOW Sheet Flow: FL * S I < 1 Concentrated Flow: FL * S I > 1 6. Flow Distribution for Concentrated Flows 7 Soil Preparation (Describe soil amendment) 8 Vegetation (Check the type used or describe "Other") 9. Irrigation (*Select None if existing buffer area has 80% vegetation AND will not be disturbed during construction.) 10. Outflow Collection (Check the type used or describe "Other") Notes: Continues to sheet flow to Spring Creek Fort Collins, CO Design Procedure Form: Grass Buffer (GB) Sam Eliason United Civil Design Group Mountain View Community Church August 19, 2020 UD-BMP (Version 3.07, March 2018) Existing Xeric Turf Grass Irrigated Turf Grass Other (Explain): Choose One Choose One Grass Swale Street Gutter Storm Sewer Inlet Other (Explain): None (sheet flow) Slotted Curbing Level Spreader Choose One Other (Explain): Choose One Yes No Choose One Permanent None* Temporary UD-BMP_v3.07 (2).xlsm, GB 8/19/2020, 5:47 PM IINLET CAPACITY Mountain View Community Church, Fort Collins, CO INLET ID: Type 13 Governing Equations: Inlet capacity equation at low flows (weir calculation): Where: P = 2(L + W) H = depth of water above the flowline Inlet capacity equation at higher flows (orifice calculation): Where: A = open area of the inlet grate H = depth of water above the centroid of the cross-sectional area (A) Input Parameters: Grate: Type 13 Wier Perimeter: 8.0 Open Area of Grate (ft2): 3.8 Grate Centroid Elevation (ft): 4906.45 Allowable Capacity: 50% Depth vs. Flow: Depth Elevation Shallow Orifice Actual Above Inlet Weir Flow Flow Flow (ft) (ft) (cfs) (cfs) (cfs) 0.00 4906.45 0.00 0.00 0.00 0.05 4906.50 0.13 2.28 0.13 0.10 4906.55 0.38 3.23 0.38 0.15 4906.60 0.70 3.95 0.70 0.20 4906.65 1.07 4.57 1.07 0.25 4906.70 1.50 5.11 1.50 <---- Maximum Depth 0.30 4906.75 1.97 5.59 1.97 0.35 4906.80 2.48 6.04 2.48 0.40 4906.85 3.04 6.46 3.04 0.45 4906.90 3.62 6.85 3.62 0.50 4906.95 4.24 7.22 4.24 Q  3 . 0 P H 1 . 5 Q  0 .67A ( 2 gH ) 0 . 5 Date: 10/6/2020 C:\United Civil Dropbox\Projects\U20004 - Mountain View Community Church\Reports\Drainage\Calculations\U20004-Drain Calcs.xlsm APPENDIX C REFERENCED MATERIALS 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°2'22.10"W 40°34'20.14"N 105°1'44.65"W 40°33'52.81"N SEE FIS REPORT FOR DETAILED LEGEND AND INDEX MAP FOR FIRM PANEL LAYOUT HAZARDFLOOD SPECIAL AREAS Without Zone A, V, Base A99 Flood Elevation (BFE) With BFE or Depth Zone AE, AO, AH, VE, AR Regulatory Floodway 0.ofAreas 2% 1% Annual annual Chance chance Flood flood with Hazard, average 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. with See Reduced Notes. Flood Risk due to 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 authoritativethe flood hazard NFHL information web services is derived provided directly by FEMA. from This map was reflect exported changes on or 2/amendments 5/2020 at 10:subsequent 10:59 PM to and this does date not 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 FLOODOF AREAS HAZARD OTHER AREAS STRGUECNTUERRAESL 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. LAG 4908.7' 4909 4904 4906 4907 4908 4910 4907 4913 4907 4911 4907 4906 4907 4909 4910 4903 4904 4904 4906 4910 4913 4906 4904 4910 4910 4906 4909 4905 4907 4909 4905 4912 4905 4907 4911 4905 4903 4907 4905 4905 4904 4904 4911 4904 4913 4905 4910 4904 4909 4903 4904 4904 4910 4906 4903 4908 4905 4908 4906 Federal Emergency Management Agency Washington, D.C. 20472 Page 1 of 5 Date: March 27, 2019 Case No.: 19-08-0473A LOMA COMMUNITY AND MAP PANEL INFORMATION LEGAL PROPERTY DESCRIPTION DETERMINATION APPROXIMATE LATITUDE & LONGITUDE OF PROPERTY: 40.568580, -105.034568 SOURCE OF LAT & LONG: GOOGLE EARTH DATUM: NAD 83 FLOODING SOURCE: SPRING CREEK AFFECTED MAP PANEL COMMUNITY CITY OF FORT COLLINS, LARIMER COUNTY, COLORADO NUMBER: 08069C0983H DATE: 5/2/2012 COMMUNITY NO: 080102 A portion of Tract A, Seven Lakes Business Park P.U.D, as described in the Special Warranty Deed recorded as Document No. 20060013344, in the Office of the Clerk and Recorder, Larimer County, Colorado LETTER OF MAP AMENDMENT DETERMINATION DOCUMENT (REMOVAL) LOT SUBDIVISION STREET BLOCK/ SECTION FLOOD ZONE OUTCOME WHAT IS REMOVED FROM THE SFHA LOWEST LOT ELEVATION (NAVD 88) LOWEST ADJACENT GRADE ELEVATION (NAVD 88) 1% ANNUAL CHANCE FLOOD ELEVATION (NAVD 88) X -- 4908.7 feet -- (unshaded) 2330 East Prospect Structure Road Seven Lakes Business Park P.U.D. Tract A -- -- Special Flood Hazard Area (SFHA) - The SFHA is an area that would be inundated by the flood having a 1-percent chance of being equaled or exceeded in any given year (base flood). ADDITIONAL CONSIDERATIONS (Please refer to the appropriate section on Attachment 1 for the additional considerations listed below.) PORTIONS REMAIN IN THE SFHA/FLOODWAY eLOMA DETERMINATION This document provides the Federal Emergency Management Agency's determination regarding a request for a Letter of Map Amendment for the property described above. Using the information submitted and the effective National Flood Insurance Program (NFIP) map, we have determined that the structure(s) on the property(ies) is/are not located in the SFHA, an area inundated by the flood having a 1-percent chance of being equaled or exceeded in any given year LETTER OF MAP AMENDMENT DETERMINATION DOCUMENT (REMOVAL) ATTACHMENT 1 (ADDITIONAL CONSIDERATIONS) Page 2 of 5 Date: 3/27/2019 Case No : 19-08-0473A LOMA Federal Emergency Management Agency Washington, D.C. 20472 Structure Removal: The following considerations may or may not apply to the determination for your Structure: PORTIONS OF THE PROPERTY REMAIN IN THE SFHA and/or FLOODWAY - Portions of this property, but not the subject of the Determination document, may remain in the Special Flood Hazard Area (SFHA) and/or the regulatory floodway for the flooding source indicated on the Determination Document. The NFIP regulatory floodway is the area that must remain unobstructed in order to prevent unacceptable increases in base flood elevations. Therefore, no construction may take place in an NFIP regulatory floodway that may cause an increase in the base flood elevation. Therefore, any future construction or substantial improvement on the property remains subject to Federal, State/Commonwealth, and local regulations for floodplain management. The NFIP regulatory floodway is provided to the community as a tool to regulate floodplain development. Modifications to the NFIP regulatory floodway must be accepted by both the Federal Emergency Management Agency (FEMA) and the community involved. Appropriate community actions are defined in Paragraph 60.3(d) of the NFIP regulations. Any proposed revision to the NFIP regulatory floodway must be submitted to FEMA by community officials. The community should contact either the Regional Director (for those communities in Regions I-IV, and VI-X), or the Regional Engineer (for those communities in Region V) for guidance on the data which must be submitted for a revision to the NFIP regulatory floodway. Contact information for each regional office can be obtained by calling the FEMA Map Assistance Center toll free at (877) 336-2627 (877-FEMA MAP) or from our web site at https://www.fema.gov/regional-contact-information STUDY UNDERWAY - This determination is based on the flood data presently available. However, the Federal Emergency Management Agency may be currently revising the National Flood Insurance Program (NFIP) map for the community. New flood data could be generated that may affect this property. If a new NFIP map is issued it will supersede this determination. The Federal requirement for the purchase of flood insurance will then be based on the newly revised NFIP map. EXTRATERRITORIAL JURISDICTION - The subject of the determination is shown on the National Flood Insurance Program map and may be located in an Extraterritorial Jurisdiction area for the community indicated on the Determination Document. This attachment provides additional information regarding this request. If you have any questions about this attachment, please contact the FEMA Map Assistance Center toll free at (877) 336-2627 (877-FEMA MAP) or by letter addressed to the Federal Emergency Management Agency, Attn: North Wind Resource Partners (NWRP) eLOMA Coordinator, NWRP eLOMA Coordinator, 3601 Eisenhower Ave., Alexandria, VA 22304-6439, Fax: 703-751-7415 Luis V. Rodriguez, P.E., Director Engineering and Modeling Division Federal Insurance and Mitigation Administration eLOMA LETTER OF MAP AMENDMENT DETERMINATION DOCUMENT (REMOVAL) ATTACHMENT 1 (ADDITIONAL CONSIDERATIONS) Page 3 of 5 Date: 3/27/2019 Case No : 19-08-0473A LOMA Federal Emergency Management Agency Washington, D.C. 20472 GREAT LAKES - The Federal Emergency Management Agency (FEMA) has based this determination on elevation data which is published in the current Flood Insurance Study for the community. However, the elevations established in the U.S. Army Corps of Engineers (USACE) reports on the Great Lakes are the best available data known to us. If in the future there are any subsequent map revisions to the National Flood Insurance Program map and the USACE reports remain the best available data known, FEMA will use those elevations for any such revisions. Further, be advised that the elevations on the Flood Insurance Rate Map (FIRM) may only reflect the Stillwater elevation for the lake and may not account for the effects of wind driven waves or wave run-up. On-site conditions such as wind speed, wind direction, fetch distance, water depth and the slope of the beach or bluff may result in significant increases to the base flood elevation. Therefore, it is strongly recommended that the requestor be aware of these circumstances and, if warranted, evaluate the effects of wind driven waves along the shoreline of the property. STATE AND LOCAL CONSIDERATIONS - Please note that this document does not override or supersede any State or local procedural or substantive provisions which may apply to floodplain management requirements associated with amendments to State or local floodplain zoning ordinances, maps, or State or local procedures adopted under the National Flood Insurance Program. COASTAL BARRIER RESOURCE SYSTEM - Based upon information provided to FEMA by the U.S. Fish and Wildlife Service (USFWS), the subject property may be within a System Unit or an Otherwise Protected Area (OPA) of the John H. Chafee Coastal Barrier Resource System (CBRS). Federal flood insurance is generally not available within the CBRS for new construction or substantial improvements occurring after the flood insurance prohibition date (which is generally tied to the date that the area was first established as either a System Unit or OPA, but may differ in some cases). Other federal expenditures and financial assistance (including certain types of disaster assistance) are also restricted within System Units of the CBRS. The USFWS is the authoritative source for information regarding the CBRS. Additional information, including the CBRS Mapper, can be found on the USFWS website at: https://www.fws.gov/cbra. This attachment provides additional information regarding this request. If you have any questions about this attachment, please contact the FEMA Map Assistance Center toll free at (877) 336-2627 (877-FEMA MAP) or by letter addressed to the Federal Emergency Management Agency, Attn: North Wind Resource Partners (NWRP) eLOMA Coordinator, NWRP eLOMA Coordinator, 3601 Eisenhower Ave., Alexandria, VA 22304-6439, Fax: 703-751-7415 Luis V. Rodriguez, P.E., Director Engineering and Modeling Division Federal Insurance and Mitigation Administration eLOMA 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 Mountain View Community Church Natural Resources Conservation Service March 23, 2020 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 42—Gravel pits............................................................................................13 64—Loveland clay loam, 0 to 1 percent slopes...........................................13 105—Table Mountain loam, 0 to 1 percent slopes...................................... 15 References............................................................................................................17 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 4490790 4490810 4490830 4490850 4490870 4490890 4490910 4490930 4490790 4490810 4490830 4490850 4490870 4490890 4490910 4490930 496950 496970 496990 497010 497030 497050 497070 497090 497110 497130 497150 497170 497190 496950 496970 496990 497010 497030 497050 497070 497090 497110 497130 497150 497170 497190 40° 34' 9'' N 105° 2' 10'' W 40° 34' 9'' N 105° 1' 59'' W 40° 34' 4'' N 105° 2' 10'' W 40° 34' 4'' N 105° 1' 59'' W N Map projection: Web Mercator Corner coordinates: WGS84 Edge tics: UTM Zone 13N WGS84 0 50 100 200 300 Feet 0 15 30 60 90 Meters Map Scale: 1:1,140 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 Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI 42 Gravel pits 0.5 9.2% 64 Loveland clay loam, 0 to 1 percent slopes 3.9 72.8% 105 Table Mountain loam, 0 to 1 percent slopes 1.0 18.0% Totals for Area of Interest 5.3 100.0% Map Unit Descriptions The map units delineated on the detailed soil maps in a soil survey represent the soils or miscellaneous areas in the survey area. The map unit descriptions, along with the maps, can be used to determine the composition and properties of a unit. A map unit delineation on a soil map represents an area dominated by one or more major kinds of soil or miscellaneous areas. A map unit is identified and named according to the taxonomic classification of the dominant soils. Within a taxonomic class there are precisely defined limits for the properties of the soils. On the landscape, however, the soils are natural phenomena, and they have the characteristic variability of all natural phenomena. Thus, the range of some observed properties may extend beyond the limits defined for a taxonomic class. Areas of soils of a single taxonomic class rarely, if ever, can be mapped without including areas of other taxonomic classes. Consequently, every map unit is made up of the soils or miscellaneous areas for which it is named and some minor components that belong to taxonomic classes other than those of the major soils. Most minor soils have properties similar to those of the dominant soil or soils in the map unit, and thus they do not affect use and management. These are called noncontrasting, or similar, components. They may or may not be mentioned in a particular map unit description. Other minor components, however, have properties and behavioral characteristics divergent enough to affect use or to require different management. These are called contrasting, or dissimilar, components. They generally are in small areas and could not be mapped separately because of the scale used. Some small areas of strongly contrasting soils or miscellaneous areas are identified by a special symbol on the maps. If included in the database for a given area, the contrasting minor components are identified in the map unit descriptions along with some characteristics of each. A few areas of minor components may not have been observed, and consequently they are not mentioned in the descriptions, especially where the pattern was so complex that it was impractical to make enough observations to identify all the soils and miscellaneous areas on the landscape. The presence of minor components in a map unit in no way diminishes the usefulness or accuracy of the data. The objective of mapping is not to delineate pure taxonomic classes but rather to separate the landscape into landforms or landform segments that have similar use and management requirements. The Custom Soil Resource Report 11 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, 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 42—Gravel pits Map Unit Composition Gravel pits: 95 percent Minor components: 5 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Gravel Pits Setting Parent material: Gravel pits Typical profile H1 - 0 to 6 inches: extremely gravelly sand H2 - 6 to 60 inches: extremely gravelly sand, extremely gravelly coarse sand, very gravelly coarse sand H2 - 6 to 60 inches: H2 - 6 to 60 inches: Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 8s Hydrologic Soil Group: A Hydric soil rating: No Minor Components Aquents Percent of map unit: 5 percent Landform: Marshes Hydric soil rating: Yes 64—Loveland clay loam, 0 to 1 percent slopes Map Unit Setting National map unit symbol: jpx9 Elevation: 4,800 to 5,500 feet Mean annual precipitation: 13 to 15 inches Mean annual air temperature: 48 to 50 degrees F Frost-free period: 135 to 150 days Farmland classification: Prime farmland if irrigated Map Unit Composition Loveland and similar soils: 90 percent Minor components: 10 percent Estimates are based on observations, descriptions, and transects of the mapunit. Custom Soil Resource Report 13 Description of Loveland Setting Landform: Flood plains, stream terraces Landform position (three-dimensional): Tread Down-slope shape: Linear Across-slope shape: Linear Parent material: Alluvium Typical profile H1 - 0 to 15 inches: clay loam H2 - 15 to 32 inches: clay loam, silty clay loam, loam H2 - 15 to 32 inches: very gravelly sand, gravelly sand, gravelly coarse sand H2 - 15 to 32 inches: H3 - 32 to 60 inches: H3 - 32 to 60 inches: H3 - 32 to 60 inches: Properties and qualities Slope: 0 to 1 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Poorly drained Runoff class: Medium Capacity of the most limiting layer to transmit water (Ksat): Moderately high (0.20 to 0.60 in/hr) Depth to water table: About 18 to 36 inches Frequency of flooding: Occasional Frequency of ponding: None Calcium carbonate, maximum in profile: 15 percent Salinity, maximum in profile: Very slightly saline to slightly saline (2.0 to 4.0 mmhos/cm) Available water storage in profile: Very high (about 16.7 inches) Interpretive groups Land capability classification (irrigated): 3w Land capability classification (nonirrigated): 3w Hydrologic Soil Group: C Hydric soil rating: No Minor Components Aquolls Percent of map unit: 5 percent Landform: Swales Hydric soil rating: Yes Poudre Percent of map unit: 5 percent Hydric soil rating: No Custom Soil Resource Report 14 105—Table Mountain loam, 0 to 1 percent slopes Map Unit Setting National map unit symbol: jpty 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 Table mountain and similar soils: 85 percent Minor components: 15 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Table Mountain Setting Landform: Flood plains, stream terraces Landform position (three-dimensional): Tread Down-slope shape: Linear Across-slope shape: Linear Parent material: Alluvium Typical profile H1 - 0 to 36 inches: loam H2 - 36 to 60 inches: loam, clay loam, silt loam H2 - 36 to 60 inches: H2 - 36 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: 15 percent Salinity, maximum in profile: Nonsaline to very slightly saline (0.0 to 2.0 mmhos/cm) Sodium adsorption ratio, maximum in profile: 5.0 Available water storage in profile: Very high (about 18.0 inches) Interpretive groups Land capability classification (irrigated): 1 Land capability classification (nonirrigated): 3c Hydrologic Soil Group: B Custom Soil Resource Report 15 Ecological site: Overflow (R049XY036CO) Hydric soil rating: No Minor Components Caruso Percent of map unit: 7 percent Hydric soil rating: No Fluvaquentic haplustolls Percent of map unit: 4 percent Landform: Terraces Hydric soil rating: Yes Paoli Percent of map unit: 4 percent Hydric soil rating: No Custom Soil Resource Report 16 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 17 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 18 This unofficial copy was downloaded on Dec-04-2019 from the City of Fort Collins Public Records Website: http://citydocs.fcgov.com For additional information or an official copy, please contact Engineering Office 281 North College Fort Collins, CO 80521 USA APPENDIX D DRAINAGE EXHIBITS MOUNTAIN VIEW COMMUNITY CHURCH BUILDING LEGEND BUILDING/ROOF AREA ASPHALT CONCRETE PROPERTY BOUNDARY LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (BASED ON PHASE 2 ADDITION) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) PATH: 0' 50' 100' SCALE: 1" = 50' 25' P:\U20004 - MOUNTAIN VIEW COMMUNITY CHURCH\CADD\ET\EXISTING IMPERVIOUS EXHIBIT.DWG DRAWING NAME: EXISTING IMPERVIOUS EXHIBIT SHEET SIZE: 11 x 17 MOUNTAIN VIEW COMMUNITY CHURCH EXISTING IMPERVIOUS AREAS EXHIBIT DATE: July 28, 2020 PREPARED FOR: MOUNTAIN VIEW COMMUNITY CHURCHJOB NUMBER: U20004 NOTE: THIS EXHIBIT WAS PREPARED FOR INFORMATION ONLY AND THE ENGINEER PREPARING THESE PLANS WILL NOT BE RESPONSIBLE FOR UNAUTHORIZED USE OF THEM. 1501 ACADEMY COURT, SUITE 203 FORT COLLINS, CO 80524 (970) 530-4044 WWW.UNITEDCIVIL.COM SHEET 1 OF 2 UNITED CIVIL Design Group LLC NORTH BASIN AREAS COMPOSITE EFFECTIVE COMPOSITE FRUNOFF COEFFICIENTS TOTAL TOTAL ROOF ASPHALT CONCRETE GRAVEL LAWNS IMPERVIOUSNESS IMPERVIOUS %I = 0% %I = 100% %I = 0% %I =0% %I=2% (%I) AREAS C2 C100 (ACRES) sf sf sf sf sf sf EX-SITE 2.90 126,260 36,667 36,862 13,123 39,608 66.4% 83,777 0.73 0.91 UD W MOUNTAIN VIEW COMMUNITY CHURCH BUILDING LEGEND BUILDING/ROOF AREA ASPHALT CONCRETE PROPERTY BOUNDARY GRAVEL LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (BASED ON PHASE 2 ADDITION) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) LIMITS OF MODIFIED IMPERVIOUS AREA (TYP) PATH: 0' 50' 100' SCALE: 1" = 50' 25' P:\U20004 - MOUNTAIN VIEW COMMUNITY CHURCH\CADD\ET\PROPOSED IMPERVIOUS EXHIBIT.DWG DRAWING NAME: PROPOSED IMPERVIOUS EXHIBIT SHEET SIZE: 11 x 17 MOUNTAIN VIEW COMMUNITY CHURCH PROPOSED IMPERVIOUS AREAS EXHIBIT DATE: July 28, 2020 PREPARED FOR:MOUNTAIN VIEW COMMUNITY CHURCH JOB NUMBER: U20004 NOTE: THIS EXHIBIT WAS PREPARED FOR INFORMATION ONLY AND THE ENGINEER PREPARING THESE PLANS WILL NOT BE RESPONSIBLE FOR UNAUTHORIZED USE OF THEM. 1501 ACADEMY COURT, SUITE 203 FORT COLLINS, CO 80524 (970) 530-4044 WWW.UNITEDCIVIL.COM SHEET 2 OF 2 UNITED CIVIL Design Group LLC NORTH BASIN AREAS COMPOSITE EFFECTIVE COMPOSITE FRUNOFF COEFFICIENTS TOTAL TOTAL ROOF ASPHALT CONCRETE GRAVEL LAWNS IMPERVIOUSNESS IMPERVIOUS %I = 0% %I = 100% %I = 0% %I =0% %I=2% (%I) AREAS C2 C100 (ACRES) sf sf sf sf sf sf PR-SITE 2.90 126,260 37,606 34,709 14,482 536 38,927 66.6% 84,029 0.73 0.92 2 4 3 1 2 1 3 3 1 2 2 2 1 2 4 3 2 3 2 1 1 2 1 1 2 3 1 1 2 2 1 2 2 1 1 2 2 3 1 2 2 1 2 1 2 3 1 1 2 2 3 2 2 3 2 UD UD UD 3 2 2 2 2 2 1 1 2 2 1 2 1 2 1 4908 4907 4906 4904 SPRING CREEK CROSS SECTION 1335 GM 2290 E PROSPECT ROAD OWNER: DDNH COMMERCIAL INC 2310 E PROSPECT RD OWNER: C AND C HOLDINGS LLC OWNER: GATEWAY MEDICAL SERVICES LLC EXISTING BUILDING LOT LINE (TYP) LIMITS OF 100-YEAR FLOODPLAIN 100-YEAR FLOODPLAIN (BUILDING REMOVED FROM FLOODPLAIN PER LOMA CASE NO. 19-08-0473A DATED 3/27/2019) EXISTING EDGE OF POND EXISTING LIMITS OF WETLANDS LIMITS OF FLOODWAY EXISTING 12" CMP EXISTING 8" ADS ROOF DRAIN B2 0.12 0.95 1.00 A2 0.06 0.95 1.00 A3 0.16 0.95 1.00 A1 0.03 0.28 0.35 B1 0.60 0.87 1.00 C1 0.02 0.31 0.38 2330 E PROSPECT RD OWNER: MOUNTAIN VIEW COMMUNITY CHURCH BASINS LINES SHOWN BASED ON PHASE 2 ROOF DESIGN (NOT SIGNIFICANTLY DIFFERENT THAN PHASE 1) 82 LF - LEVEL SPREADER TO DISTRIBUTE STORMWATER FLOW TO VEGETATIVE BUFFER STORM LINE B STORM LINE A2 STORM LINE A3 STORM LINE C SPRING CREEK TRAIL PROPOSED INLET BIORETENTION UNDERDRAIN OUTFALL EXISTING POND CATTAIL CHORUS NATURAL AREA STORM LINE B BIORETENTION POND WITHIN DRAINAGE EASEMENT BY SEPARATE DOCUMENT MINIMUM FLAT AREA FOR BIOTENTION: 100 SF WEST POND & 146 SF EAST POND OWNER: SEVEN LAKES BUSINESS PARK ASSN SPRING CREEK VEGETATIVE BUFFER (APPROX. 6,605 SF) 44' EXISTING CREEK BANK 1502 S TIMBERLINE RD OWNER: POUDRE SCHOOL DISTRICT R-1 86' OUTLET B MOUNTAIN VIEW COMMUNITY CHURCH 10/7/2020 U20004 1" = 20' 1" = N/A MOUNTAIN VIEW COMMUNITY CHURCH NORTH 10/7/2020 11:10:56 AM E:\UNITED CIVIL DROPBOX\PROJECTS\U20004 - MOUNTAIN VIEW COMMUNITY CHURCH\CADD\CP\C5.00 - DRAINAGE PLAN.DWG C5.00 - DRAINAGE PLAN SME JRS C5.00 15 DRAINAGE PLAN 0 20' 40' SCALE: 1" = 20' 10' PREPARED FOR: JOB NUMBER SHEET NUMBER OF SHEETS DATE SUBMITTED: VERTICAL: HORIZONTAL: SCALE PRELIMINARY PLANS NOT FOR CONSTRUCTION PROJ. MGR: DRAWING NAME: PATH: DATE: TIME: DESIGNER: CIVIL ENGINEERING & CONSULTING UNITED CIVIL Design Group 19 OLD TOWN SQUARE #238 FORT COLLINS, CO 80524 (970) 530-4044 www.unitedcivil.com The engineer preparing these plans will not be responsible for, or liable for, unauthorized changes to or uses of these plans. All changes to the plans must be in writing and must be approved by the preparer of these plans. NO. BY DATE CAUTION REVISIONS: 12 X.XX XX.X X.XX X BASIN DESIGNATION BASIN AREA (ACRE) 5 - YR RUNOFF COEFF. 100 - YR RUNOFF COEFF. DESIGN POINT FLOW DIRECTION DP D1 LEGEND NOTES 1. ONSITE DETENTION NOT REQUIRED SINCE INCREASE IN IMPERVIOUS AREA IS LESS THAN 1000 SQUARE FEET. 2. ONSITE WATER QUALITY AND LID PROVIDED BASED ON MODIFIED IMPERVIOUS AREA FOR PHASE 1 AND PHASE 2 INCLUDING THE NEW SANCTUARY IMPROVEMENTS. CHECKED BY: CHECKED BY: CHECKED BY: CHECKED BY: CHECKED BY: APPROVED: FLOODPLAIN NOTES 1. PORTIONS OF THIS PROJECT ARE LOCATED WITHIN THE FEMA REGULATED 100-YEAR SPRING CREEK FLOODPLAIN AND FLOODWAY. THIS PROPERTY IS ALSO WITHIN THE POUDRE RIVER 500-YEAR FLOODPLAIN AND IS SUBJECT TO THE REQUIREMENTS OF CHAPTER 10 OF THE CITY CODE. 2. ALL DEVELOPMENT (CURB & GUTTER, PAVEMENT, GRADING, FILL, PARKING LOTS, UTILITIES, LANDSCAPING, ETC.) WITHIN THE FEMA REGULATORY FLOODPLAIN MUST BE PRECEDED BY AN APPROVED FLOODPLAIN USE PERMIT AND APPLICABLE FEES. 3. A NO RISE CERTIFICATION IS REQUIRED PRIOR TO PERFORMING ANY WORK WITHIN THE FLOODWAY (I.E. CURB CUT, CURB & GUTTER, UTILITY WORK, LANDSCAPING, ETC.) 4. ALL SPOT ELEVATIONS AND BASE FLOOD ELEVATIONS AS SHOWN ON THIS DRAWING ARE PER VERTICAL CONTROL DATUM NAVD 88. 5. NO STORAGE OF MATERIAL OR EQUIPMENT MAY OCCUR AT ANY TIME IN THE FLOODWAY BEFORE, DURING OR AFTER CONSTRUCTION. 6. ANY ITEMS LOCATED IN THE FLOODWAY THAT CAN FLOAT (E.G. PICNIC TABLE, BIKE RACKS, ETC.) MUST BE ANCHORED. 7. CRITICAL FACILITIES ARE PROHIBITED IN THE POUDRE RIVER 500-YEAR FLOODPLAIN. WATER QUALITY SUMMARY WATER QUALITY REQUIREMENT: TOTAL NEW OR MODIFIED IMPERVIOUS AREA = 18,850 SF REQUIRED LID WQ TREATMENT = 9,425 SF (50% MIN) WATER QUALITY PROVIDED: BIORETENTION (LID) FOR BASINS A1, A2, & A3 = 9,780 SF (52%) VEGETATIVE BUFFER (NON LID) FOR BASINS B1 & B2 = 29,332 SF TOTAL IMPERVIOUS AREA TREATED = 39,112 SF 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 14, Sep 13, 2019 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: Aug 11, 2018—Aug 12, 2018 The orthophoto or other base map on which the soil lines were compiled and digitized probably differs from the background imagery displayed on these maps. As a result, some minor shifting of map unit boundaries may be evident. Custom Soil Resource Report 10 (base flood). This document amends the effective NFIP map to remove the subject property from the SFHA located on the effective NFIP map; therefore, the Federal mandatory flood insurance requirement does not apply. However, the lender has the option to continue the flood insurance requirement to protect its financial risk on the loan. A Preferred Risk Policy (PRP) is available for buildings located outside the SFHA. Information about the PRP and how one can apply is enclosed. This determination is based on the flood data presently available. If there are any errors on this eLOMA Determination Letter that cause FEMA to rescind and/or nullify the determination the property owner should consult the Licensed Professional that submitted this eLOMA. The enclosed documents provide additional information regarding this determination. If you have any questions about this document, please contact the FEMA Map Assistance Center toll free at (877) 336-2627 (877-FEMA MAP) or by letter addressed to the Federal Emergency Management Agency, Attn: North Wind Resource Partners (NWRP) eLOMA Coordinator, 3601 Eisenhower Avenue, Alexandria, VA 22304-4605, Fax: 703-751-7415. Luis V. Rodriguez, P.E., Director Engineering and Modeling Division Federal Insurance and Mitigation Administration eLOMA 4906 4903 4907 4905 4906 4907 4904 4905 4911 4909 4908 4905 4907 4910 4908 4905 4906 4905 4906 4907 4904 4908 4904 4901 4904 4906 4904 4905 4905 4905 4903 4905 4906 4904 4905 4909 4906 4909 4911 4906 4913 4912 4906 4906 4903 4904 4906 4905 4911 4906 4911 4907 4903 4910 4913 4906 4910 4904 4909 4911 4905 4907 4908 4909 4908 4912 4912 4904 4903 4906 4904 4905 4910 4909 4907 4907 4911 4902 4906 4907 4904 4903 4909 4910 4910 4906 4906 4905 4904 4903 4905 4904 4906 4906 4904 4908 4910 4903 4904 4905 4903 4908 4913 4909 4903 4907 4905 4904 4910 4910 4904 4904 4907 4910 4908 4903 4908 4912 4904 4903 4909 4909 4910 4907 4908 4906 4906 4909 4909 4904 4910 4905 4904 4903 4908 4908 4910 4908 4900 4911 4906 4910 4904 4904 4909 4909 4905 4908 4909 4908 4903 4901 4909 4907 4905 4909 4905 4902 4911 4910 4903 4910 4903 4904 4908 4910 4909 4903 4909 4909 4908 4909 4907 4904 4905 4903 4906 4906 4907 4906 4905 4904 4905 4905 4907 4908 4907 4905 4906 4901 4904 4902 4904 4903 ¯ 0 62.5 125 250 375 500 Feet Revised Floodplain Ground Contours Spring Creek Profile Flooding Extents Base Flood Elevations Spring Creek Cross Sections Parcels Fort Collins Buildings Lowest Adjacent Ground Flood Zones . AE, AE,FLOODWAY X,0.2 PCT ANNUAL CHANCE FLOOD HAZARD Legend: LOMA for 2330 E Prospect Rd LAG 4908.7' 4908 4909 4910 4907 4909 4909 4908 4908 SPRING CREEK CROSS SECTION 1335