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HomeMy WebLinkAboutOshkosh-Campbell_Creek_SWMP_Addendum_1-Feb_2008 Report Campbell Creek Stormwater Management Plan– Addendum No. 1 City of Oshkosh, WI February 2008 Report for City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Prepared by: STRAND ASSOCIATES, INC.® 910 West Wingra Drive Madison, WI53715 www.strand.com February 2008 TABLE OF CONTENTS Page No. or Following EXECUTIVE SUMMARY SECTION 1–INTRODUCTION 1.01 Introduction................................................................................................ 1-1 1.02 Scope of Study........................................................................................... 1-1 1.03 Location of Study Area............................................................................... 1-3 1.04 Other Similar Studies................................................................................. 1-3 1.05 Applicable Standards and Design Criteria................................................. 1-4 1.06 Phase II Stormwater Permit....................................................................... 1-4 1.07 Definitions and Abbreviations.................................................................... 1-4 SECTION 2–CONTRIBUTING WATERSHED CHARACTERISTICS 2.01 Basin Characteristics Affecting Stormwater Runoff................................... 2-1 2.02 Expected Precipitation Depths................................................................... 2-4 2.03 Fox River and Lake Winnebago Regulatory Levels................................... 2-5 2.04 Gauging Station on Fox River and Lake Winnebago................................. 2-5 2.05 Lake Winnebago 2004-2005 Regulation Strategy..................................... 2-6 2.06 Rainfall Gauges in Oshkosh...................................................................... 2-6 2.07 Locations of Existing Flooding Problems................................................... 2-7 SECTION 3–ENGINEERING ANALYSIS 3.01 Hydrologic Analysis.................................................................................... 3-1 3.02 Hydraulic Analysis...................................................................................... 3-2 SECTION 4–ALTERNATIVE ANALYSIS 4.01 General...................................................................................................... 4-1 4.02 Alternative 12 (Formerly Alternative 7)...................................................... 4-4 4.03 Alternative 13............................................................................................. 4-8 4.04 Alternative 13 B.......................................................................................... 4-12 4.05 Alternative 14............................................................................................. 4-15 4.06 Alternative 15 ............................................................................................. 4-16 4.07 Alternative 16............................................................................................. 4-19 4.08 Summary of Alternatives and Alternatives Analysis .................................. 4-22 4.09 Storm Sewer Capacity Analysis Under Future Land Use Conditions for Modeled Storm Sewers with Recommended Alternative In-Place............. 4-25 4.10 Storm Sewer Capacity Analysis Under Future Land Use Conditions for Modeled Storm Sewers with Alternative 16 In Place............................ 4-26 4.11 Storm Sewer Sizing for Main Branch to Convey 10-Year Flow with Recommended Alternative In-Place ......................................................... 4-26 4.12 Changes in Diversion at Diversion Points 1, 2, and 3 with Recommended Alternative In-Place .................................................................................... 4-26 4.13 Off-Line Stormwater Ponds (NR 116)........................................................ 4-26 TABLE OF CONTENTS (Continued) Page No. or following SECTION 5–CONCLUSIONS AND RECOMMENDATIONS 5.01 General...................................................................................................... 5-1 5.02 Recommendations for Achieving Stormwater Management Goals........... 5-1 5.03 Implementation Plan.................................................................................. 5-3 5.04 Funding Opportunities................................................................................ 5-3 5.05 Conclusion................................................................................................. 5-4 APPENDICES APPENDIX A–FLOODING PHOTOGRAPHS APPENDIX B–STORMWATER FUNDING BROCHURE TABLES ES.04-1 Summary of Alternatives............................................................................ ES-6 ES.05-1 Stormwater Plan Components and Implementation Plan.......................... ES-7 2.01-1 Hydrologic Soils Groups ............................................................................. 2-2 2.01-2 Campbell Creek Watershed Soils..................................................... 2-3 2.01-3 Existing Conditions and Hydrologic Parameters........................................ 2-4 2.01-4 Future Conditions and Hydrologic Parameters.......................................... 2-4 2.02-1 Design Storm Rainfall Depths, Bulletin 71................................................. 2-5 2.03-1 Regulatory Levels–Lake Winnebago (National Geodetic Vertical Datum of 1929–NGVD 1929)......................... 2-5 2.03-2 Regulatory Levels–Confluence with Campbell Creek and Sawyer Creek (NGVD 1929)...................................................................... 2-5 2.05-1 Lake Winnebago 2004-2006 Regulation Strategy..................................... 2-6 2.07-1 Locations of Existing Flooding................................................................... 2-9 3.01-1 Existing Conditions Peak Discharge Rates................................................ 3-2 3.01-2 Future Conditions Peak Discharge Rates (2-Hour Duration)..................... 3-2 3.02-1 Boundary Conditions at Sawyer Creek/Westfield Outfall (NGVD 1929).... 3-3 3.02-2 Boundary Conditions at Sawyer Creek/Washburn Street Outfall (NGVD 1929)............................................................................................. 3-3 3.02-3 Storm System Characteristics Existing Conditions.................................... 3-5 4.01-1 Existing Available Detention...................................................................... 4-1 4.01-2 Proposed Alternatives Detention Availability–Future Conditions............... 4-1 4.01-3 Alternative Components............................................................................. 4-2 4.02-1 Vacant Parcel Information–Component 1c................................................ 4-5 4.02-2 Alternative 12 (Formerly Alternative 7) Opinion of Probable Cost............. 4-7 4.02-3 Future Conditions Effects–Alternative 12 (Formerly Alternative 7)............ 4-8 4.03-1 Alternative 13–Opinion of Probable Cost................................................... 4-11 4.03-2 Future Conditions Effects–Alternative 13................................................... 4-12 4.04-1 Alternative 13 B–Opinion of Probable Cost............................................... 4-14 4.04-2 Future Conditions Effects–Alternative 13 B............................................... 4-15 4.05-1 Alternative 14–Opinion of Probable Cost................................................... 4-16 4.05-2 Future Condition Effects-Alternative 14..................................................... 4-17 4.06-1 Alternative 15–Opinion of Probable Cost .................................................. 4-18 4.06-2 Future Conditions Effects–Alternative 15................................................... 4-19 TABLE OF CONTENTS (Continued) Page No. or following TABLES (Continued) 4.07-1 Alternative 16–Opinion of Probable Cost................................................... 4-21 4.06-2 Future Conditions Effects–Alternative 16................................................... 4-22 4.08-1 Summary of Alternatives (Including Land Acquisition Costs and 25 Percent Engineering and Contingency................................................. 4-22 4.08-2 Summary of Effects–Ranking Data............................................................ 4-22 4.08-3 Summary of Effects–Rankings................................................................... 4-22 4.08-4 Watershedwide Storage Provided (City-Provided Detention).................... 4-23 4.08-5 Least Amount of Increase in 100-Year, 12-Hour Duration Volume at Tom Sawyer Creek/USH 41 Outfall Ranking in Acre-Feet........................ 4-23 4.08-6 Least Amount of Increase in 100-Year, 12-Hour Duration Flow Rates in Cubic Feet/Second at Sawyer Creek/USH 41 Outfall Ranking.................. 4-24 4.08-7 Sawyer Creek Watershed Peak Discharge Effects.................................... 4-24 5.03-1 Stormwater Plan Components and Implementation Plan (Cost Includes 25 Percent Engineering and Contingencies)..................... 5-3 FIGURES 1.03-1 Study Area Location Relative to DNR Watersheds.................................... 1-3 2.01-1 Drainage Area Map..........................................................................Pocket Folder 2.01-2 Soils Map................................................................................................... 2-2 2.01-3 Existing Land Use–Impervious Area Map.................................................. 2-4 2.01-4 Future Land Use–Impervious Area Map.................................................... 2-4 2.01-5 Existing Land Use–Smart Growth Plan...................................................... 2-4 2.01-6 20-Year Land Use Plan–Smart Growth Plan ............................................ 2-4 2.01-7 Zoning Map–Smart Growth Plan................................................................ 2-4 2.06-1 June 10/11, 2004 Storm Event–USACE Gauge in Oshkosh, Wisconsin... 2-7 2.07-1 Problem Areas........................................................................................... 2-8 3.02-1 Existing Conditions Pipe Network.............................................. Pocket Folder 3.02-2 Existing Survey Data at Landmark Plaza and Tippler................................ 3-4 3.02-3 Existing Conditions Diversion Analysis...................................................... 3-6 4.02-1 Alternative 12–Components....................................................................... 4-4 4.02-2 Alternative 12–Components 12A and 12D Tippler Detention and Landmark Plaza to Tippler Improvements Expanded Tippler Detention.... 4-4 4.02-3 Alternative 12–Components 12B Armory Detention.................................. 4-5 4.02-4 Alternative 12–Components 12C Detention at Vacant Lot Southeast of 9th/Washburn Street Intersection.............................................................. 4-5 4.02-5 WisDOT 50-Year Design........................................................................... 4-6 4.03-1 Alternative 13–Westhaven Golf Course Detention and Upstream Diversion Component................................................................................ 4-8 4.03-2 Alternative 13–Component 13B Partially Expanded Armory Detention Basin 4-8 4.04-1 Alternative 13 B–Westhaven Golf Course Detention and Upstream Diversion Component 13B4....................................................................... 4-12 4.04-2 Alternative 13 B–Components................................................................... 4-12 4.05-1 Alternative 14–STH 44/West Waukau Avenue Detention Component...... 4-15 TABLE OF CONTENTS (Continued) Page No. or following FIGURES (Continued) 4.06-1 Alternative 15–Expanded Detention Basin SE of STH 44/ N. Clay Road Intersection Component............................................................................. 4-17 4.07-1 Alternative 16–Westhaven Golf Course Detention Upstream Diversion Component................................................................................................ 4-19 4.08-1 Alternative 13 B-Sawyer Creek Hydrograph at USH 41 Outfall................. 4-25 4.08-2 Sawyer Creek/USH 41 Outfall Hydrograph North Branch Campbell Creek Stormwater Management Plant................................................................. 4-24 4.09-1 Pipe Capacity Analysis–With Alternative 13 B In-Place............. Pocket Folder 4.10-1 Pipe Capacity Analysis–With Alternative 16 In-Place................ Pocket Folder 4.11-1 Downstream Pipe Upsizing to Convey the 10-Year Flow with Alternative 13B In-Place............................................................ 4-26 4.12-1 Diversion Analysis–With Alternative 13B In-Place..................... 4-26 EXECUTIVE SUMMARY City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-1 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 ES.01 INTRODUCTION This report is an addendum to the North Branch Campbell Creek Stormwater Management Plan, City of Oshkosh, Wisconsin, May 2006, which summarized the methodology and results of a study done by Strand Associates, Inc. to develop a stormwater management plan for the North Branch of Campbell Creek Watershed in the City of Oshkosh. The North Branch Campbell Creek Watershed is predominantly a fully developed urban watershed that comes together at West 4th Avenue and Sawyer Street with the South Branch of Campbell Creek. The North Branch of Campbell Creek and specifically the Landmark Plaza have experienced recent flooding. A sampling of photographs taken by City staff on June 11, 2004, documenting the flooding that occurred as a result of a June 10/11, 2004, storm event is included in Appendix A. Much of the development in this watershed occurred prior to the advent and implementation of strong guidelines on stormwater management, resulting in several areas with stormwater system capacity issues. This stormwater management plan addendum, in conjunction with the May 2006 study, will address ways to mitigate the existing stormwater flooding problems in the North Branch of Campbell Creek watershed and suggest ways to decrease the impacts of future development. This addendum builds upon the previous study that looked at eleven alternatives. The previous study recommended the implementation of Alternative 7. One of the Alternative 7 components was a wet detention basin at the intersection of 9th Avenue and South Washburn Street. The location of this detention has met with opposition because of its potential value as commercial property. At the November 14, 2006, City Council meeting, the Council adopted an ordinance to officially map the 9th and Washburn detention basin site contingent upon further study to explore other upstream detention options. As part of the addendum, Strand has updated the stormwater models to account for proposed Wisconsin Department of Transportation (WisDOT) USH 41 impervious area additions and have added more detail to the stormwater models upstream of the Dickinson Avenue and South Washburn Street intersection. Alternative 7 was remodeled in the new stormwater model as Alternative 12. Five additional alternatives (Alternatives 13, 13B, 14, 15, and 16) were also modeled in search of an alternative to the detention basin at the 9th/Washburn detention site. ES.02 CONTRIBUTING WATERSHED CHARACTERISTICS The Campbell Creek watershed is a highly developed watershed with large amounts of impervious surfaces such as streets, parking lots, and rooftops. The high level of impervious surface results in high peak discharge rates and runoff volumes during storm events. The soils in the Campbell Creek watershed are predominantly Type C soils (Kewaunee Silt Loam underlain by clay subsoil). Thus, there is little infiltration potential in the underlying soils. Nine flooding locations in the Campbell Creek watershed were identified. Apparent causes of the flooding and type of damage incurred are listed in Table 2.07-1. The June 10 and 11, 2004, storm event that prompted this study compares to a 20-year, 12-hour storm event (cumulative 3.63 inches of rainfall). City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-2 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 The lower reaches of the Campbell Creek storm sewer system (and adjacent linked Sawyer Creek storm sewer system) are affected by the Lake Winnebago pool elevation. When lake levels are high, the storm sewer capacity is reduced because the pipe is partially full of water at the start of a storm event. ES.03 HYDROLOGIC ANALYSIS Hydrologic models were developed for the Campbell Creek drainage area using the RUNOFF module of the computer model XP-SWMMTM Version 9.51. XP-SWMMTM estimates peak stormwater discharges and volumes based on mathematical input parameters representing precipitation depth and time distribution, drainage area, land use, and time of concentration for each subbasin. This model was used to determine drainage system capacities and analyze performance of the proposed alternatives. Computer modeling results appear to closely match observed locations, depths, and durations of flooding in the Campbell Creek watershed. However, modeling also indicates that severity of flooding in the lower reaches of the Campbell Creek watershed is strongly tied to the water surface elevation of Lake Winnebago during the storm. Hydrologic analysis was run to assess the effect of the 10-year and 100-year storm events under existing and future land use conditions as well as the effect of the June 10/11, 2004, storm event (under land use and moisture conditions existing at the start of that storm) on Landmark Plaza flooding. This analysis indicates the following: 1. In certain areas, the existing storm sewer system has less than a recommended 10-year design storm capacity under existing conditions. The modeled existing storm sewer system in the Campbell Creek watershed has capacities ranging from 1-year to 100-year. However, certain downstream capacities are realized only because of upstream ponding that attenuates flows getting downstream. 2. Modeling results indicate that the existing 36-inch x 58-inch CMP downstream from Landmark Plaza has limited conveyance capacity because of the high Manning’s “n” values, minimal or reverse slope, and shallow cover. This limited downstream capacity creates a “bottleneck” causing flows to surcharge and inundate upstream areas including Landmark Plaza and appears to be a major factor in the flooding occurring at the Landmark Plaza. Any measures to increase flow rates from Landmark Plaza must also include either improved downstream conveyance or detention to maintain the system capacity. The challenge to upsizing this portion of the storm sewer will be dealing with cover issues and utility conflicts. 3. It appears that the low elevation at which Landmark Plaza was built is a major contributing factor to the flooding problems that are presently occurring. This is evidenced by the fact that the first floor elevation of the eastern Landmark Plaza building (762.28) is only approximately 0.41 feet above the lowest overflow elevation of 761.87 City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-3 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 (located on the east side of Westfield Drive) that would allow stormwater from the Landmark Property to discharge into the Tippler Athletic Field. As described in more detail in Section 4.01, we would recommend a minimum of 1.5 feet of freeboard (with 2 feet being desirable) from the first floor elevation of a building to the computed 100-year water surface elevation adjacent to the building. 4. Modeling results indicate that Sawyer Creek did not back up into Landmark Plaza as was originally theorized during the June 10/11, 2004, storm event. 5. There are four diversion/cross connection points along Washburn Street that allow flows to move into and out of adjacent basins as shown in Figure 3.02-3. These three diversion/cross connection points appear to have been naturally occurring drainage routes prior to development occurring in these locations. This analysis indicates that the capacity of the culvert beneath USH 41 south of Dickinson Avenue is less than the peak discharge coming to that point (Diversion Point 1). This causes flows exceeding the capacity of the culvert to divert to the north along Washburn Street until that flow reaches Diversion Point 4. Diversion Point 4 allows very little flow (15.5 cfs during the existing conditions June 10/11, 2004 storm event) to cross easterly across USH 41 thus causing flows exceeding its capacity to flow north toward Diversion Point 2. The culvert that creates Diversion Point 4 is sloped from east to west. However, before the flows get to the north side of 9th Avenue, they are attenuated by surface ponding between Diversion Point 1 and Diversion Point 4 (south of West 9th Avenue); therefore the flows at Diversion Point 2 are not as high as at Diversion Point 1 or Diversion Point 4. Diverting additional flows toward Sawyer Creek and thus away from the Landmark Plaza at Diversion Point 2 appears feasible only if the storm sewer leading from just north of Witzel Avenue to the Sawyer Creek/Washburn Street outfall is upsized to maintain the existing 100-year capacity of that segment of storm sewer. Diversion of additional flow to the east to reduce flooding along Washburn Street at Diversion Point 1 appears to be feasible, provided it is routed to the proposed Armory detention pond. Diversion of additional flow to the east at Diversion Point 4 does not appear to be feasible with the proposed reconstruction of USH 41. 6. The capacity of the existing ditch and connecting storm sewer culvert through Landmark Plaza are currently limited by backwater caused by the downstream drainage system. In general, if the downstream “bottleneck” and associated backwater are reduced/relieved, then modeling results indicate that these ditch segments and connecting storm sewer culvert appear to be able to pass the 100-year 2-hour duration storm event flows around the west and south sides of the southern Landmark Plaza building and the movie theater building without inundating these buildings. 7. Modeling results indicate that the areas west and southwest of the eastern Landmark Plaza building have adequate overland flow routes that would convey flows around the north and south sides of the building rather than flood the building if the downstream drainage system capacity is increased. However, the three stormwater inlets on the west City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-4 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 and southwest sides of the eastern Landmark Plaza building would experience parking lot surface ponding ranging in depth from 11.8 inches up to 15.5 inches before overflowing along these routes. We would normally recommend no more than 6 to 9 inches of ponding to avoid damage to vehicles at low points. We recommend that the owner of Landmark Plaza perform a study to determine how to reduce potential ponding at the three stormwater inlets to an acceptable level considering that downstream backwater effects are alleviated. ES.04 ALTERNATIVES ANALYSIS To identify the most cost-effective solution to address the goals of this study, six individual alternatives described in Table ES 04-1 were evaluated as Alternatives 12, 13, 13B, 14, 15, and 16. Alternative 7 from the original study was remodeled in the new stormwater model as Alternative 12. In assessing/ranking each Alternative, we have focused on not only alleviating flooding in the Landmark Plaza area but also have assessed each alternative in terms of the watershed-wide benefit. The following criteria were used to arrive at a recommendation after assessment of these six alternatives. This included selection of the most cost alternative that meets the following criteria: 1. Meets Landmark Plaza Flooding Criteria (2 feet or greater freeboard) for the 2-hour and 12-hour duration, 100-year storm events. All options meet this criteria. 2. Meets Tippler Flooding Criteria (2 feet or greater freeboard) for the 2-hour and 12-hour duration, 100-year storm events. All options meet this criteria. 3. Is in the top three for watershed-wide benefit ranking. Alternatives 16, 13 B, and 13 are in the top three for watershed-wide ranking. 4. Is in the top three for storage considered under these alternatives. See Table 4.08-5. Alternatives 13, 13 B, and 16 are in the top three for watershed-wide ranking. 5. Is in the top three for least amount of volume discharging to the Sawyer Creek/USH 41 outfall over a 4 day period under 100-year, 12 hour storm with proposed conditions. See Table 4.08-6. Alternatives 13, 13 B, and 16 are in the top three. Additionally, Alternatives 13 B and 16 appear to closely mimic the volume of stormwater discharging to the Sawyer Creek/USH 41 outfall when compared to existing conditions. 6. Is in the top three for least amount of total minutes of flooding in the modeled system under the 100-year, 12 hour storm event under proposed conditions. See Table 4.08-6. All alternatives significantly improve the storm sewer system compared to existing conditions. However, the top three are Alternatives 13, 13 B and 16. 7. Keeps the increased peak discharge at USH 41 to a minimum. See Table 4.08-4 and Figure 4.08-1. All options are relatively equivalent for this criteria. City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-5 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 8. Has the least effect on the Sawyer Creek 100-year, 12-hour peak discharge rate under existing conditions at the USH 41/Sawyer Creek outfall. We have inserted the Campbell Creek watershed proposed conditions USH 41/Sawyer Creek outfall hydrographs the Sawyer Creek existing conditions HEC-HMS model to see the impact in peak discharge at the Sawyer Creek/USH 41 outfall as shown in Table 4.08-7. As the table shows, there are negligible effects on the Sawyer Creek peak discharge under existing conditions. This means that while all alternatives increase the peak discharge outfalling to Sawyer Creek from the 1,841 acre Campbell Creek watershed, the timing and routing of flows through the 10,026 acre Sawyer Creek watershed seem to mitigate the effects of the peak discharge increase coming from the Campbell Creek watershed. Figure 4.08-1 shows the Sawyer Creek watershed hydrograph in comparison to the USH 41/Sawyer Creek hydrograph entering from the Campbell Creek watershed with Alternative 13 B in place. As can be seen, the Campbell Creek hydrograph peaks much sooner than the Sawyer Creek watershed hydrograph. The above discussion supports the recommendation of Alternative 13 B as the most cost- effective alternative for providing flooding relief in the Campbell Creek watershed. For the purposes of this assessment, all alternatives are considered feasible. However, the charge of the Common Council was to find an alternative that performs similar to the original Alternative 7 (Alternative 12, herein). Our analysis shows that Alternative 13 performs similar to Alternative 7 (Alternative 12, herein) and at a lower cost. For this reason, Alternative 13 would normally be recommended. However, it is obvious that Alternative 13 B and 16 provide the most benefit to the City for both quantity and quality control but at a higher cost and would actually help out flooding in the Sawyer Creek watershed. It is thus our recommendation the City proceed with Alternative 13 B as the most cost-effective in assisting the City address flooding issues in the watershed as well as assist the City in meeting their WPDES stormwater quality permit. City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-6 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 Alt. Alternative Description Watershed- wide Benefit Rank Meets Landmark Plaza Criteria City Storage Provided (Acre-Feet) Opinion of Probable Cost* Cost per Acre- Foot of Storage Provided 12 Alternative 12 (Formerly Alternative 7) 4 Yes 101.1 $18,311,700 $181,100 13 Alternative 13-Incl/Partially Expanded Westhaven Golf Course Detention and Partially Expanded Armory Pond 3 Yes 113.9 $12,095,200 $106,200 13 B Alt. 13 B – Incl/Fully Expanded Westhaven Golf Course and Partially Expanded Armory Pond 2 Yes 215.1 $16,609,700 $77,200 14 Alternative 14- Incl/STH44/Waukau Detention 5 Yes 98.5 $14,003,500 $142,200 15 Alternative 15-Incl/STH 44/Gray Road Detention 6 Yes 110.2 $11,067,900 $100,400 16 Alternative 16-Fully Expanded Westhaven Golf Course Detention and Fully Expanded Armory Pond 1 Yes 221.5 $21,060,500 $95,100 ƒ Costs do not include stormwater quality component costs. See individual Alternative paragraphs in Section 4 for stormwater quality component cost breakdowns. ƒ Alternative 7 originally didn’t account for the proposed 50-year Design WisDOT Storm Sewer/Ditch along USH 41. ƒ All Alternatives are considered equal (within 0.05 feet) for freeboard at Landmark Plaza with all Alternatives having between 2.72 feet and 2.77 feet of freeboard as modeled under the 2-hour duration, 100-year storm event. Table ES.04-1 Summary of Alternatives (Including Land Acquisition Costs and 25 Percent Engineering and Contingency) City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-7 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 ES.05 CONCLUSIONS AND RECOMMENDATIONS The recommended stormwater management plan is described in Table ES.05-1. In addition to our recommended stormwater management plan, we suggest these recommendations be followed during implementation of the plan: 1. The City should complete soils investigation to determine soil characteristics in locations where detention ponds are proposed. 2. The City should adopt the Policies and Practices identified in Section 5.05 of the original report and the Drainage Evaluation Form in Appendix B of the original report. 3. The City should coordinate detention basins recommended in this study with detention basins recommended in the water quality study being performed by another consultant. 4. The City should investigate funding opportunities for the detention basins through the DNR Municipal Flood Control Grant Program. The DNR Lake Protection Grant program, River Protection Grant program, and Stewardship Grant program should also be explored. 5. The City should update City stormwater facility maps using the field survey forms and survey information provided by Strand Associates. Component Description Opinion of Probable Cost Implementation Schedule and Funding Source 13 B 1 Expanded Detention at Tippler Junior High property (see component 12a) $2,251,600 Priority 1-Municipal Flood Control Grant and Stormwater Utility 13 B 2 Partially Expanded Detention at Armory Site (see component 13b) $2,495,400 Priority 4-Municipal Flood Control Grant and Stormwater Utility 13 B 3 Storm Sewer System Improvements from Landmark Plaza to Tippler (see component 12d) $479,900 Priority 2-Municipal Flood Control Grant and Stormwater Utility 13 B 4 Fully Expanded Westhaven Golf Course Detention and Upstream Diversion $11,382,800 Priority 3-Municipal Flood Control Grant, UNPS Grant, Stormwater Utility, Stewardship Grant Total $16,609,700 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 13d. All other component costs include excavation below the normal WSEL. Table ES.05-1 Stormwater Plan Components and Implementation Plan (Costs include 25 Percent Engineering and Contingencies) City of Oshkosh, Wisconsin Campbell Creek Stormwater Management Plan Addendum No. 1 Executive Summary Prepared by Strand Associates, Inc.® ES-8 JHL:pll\\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\ES.doc\022508 6. The City should further explore the regulatory requirements with the DNR regarding permitting of off-line ponds. 7. The City should further explore the regulatory requirements regarding the diversion of the navigable Campbell Creek to the Westhaven Golf Course ponds. 8. The City should investigate possible utility conflicts and space availability for each component of the recommended Alternative. 9. The owner of Landmark Plaza should perform a study to determine how to reduce potential ponding at nodes 06-846, 06,847, and 06-1293.2 to an acceptable level considering that downstream backwater effects are alleviated as discussed in Section 3.02 C. 7 of the original report. 10. We recommend that the City assess inlet capacity in conjunction with future street improvement projects to evaluate the benefits of adding inlets to fully realize the capacities shown in Figure 4.09-1 11. The City should consider upsizing the storm conveyance facilities shown in Figure 4.11-1 as funds become available, as reconstruction becomes necessary and as feasible after implementation of the recommended Alternative. 12. The topographic surveys completed for each of the recommended projects should include survey of the properties (including the structure 1st floor elevation) surrounding each pond location. It is recommended that an acceptable pond overflow route be incorporated into the final design of each pond for flows potentially exceeding the 100- year storm event and/or for potential blockages of outlet structures. In addition, during design, it is recommended the berms at the ponds have 2 feet of freeboard between the modeled 100-year WSEL in the pond and the top of the berm to provide an added measure of protection to structures surrounding the recommended ponds (or to a height that would not invoke NR 333 as described below in item 14). The figures, herein, contemplate an approximate 1 foot of freeboard. 13. During design, we recommend running the XP-SWMM model to maximize the use of the Tippler, Armory, and Westhaven ponds after detailed topographic surveys are completed of the project sites, of the surrounding topography and 1st floor building elevations, and of the existing utility elevation information. After design is complete for all components of Alternative 13 B, we recommend that the XP-SWMM model be re-run with all changes to revise Figure 4.09-1 Storm Sewer Capacity Analysis Under Future Land Use Conditions For Modeled Storm Sewers With Alternative 13 B In-Place. 14. For the Westhaven ponds, we recommend that the City consult Chapter NR 333 Dam Design and Construction and the local DNR dam engineer to determine if these pond berms would fall under the applicability of this code section. The main requirement that would make these berms apply to this code section is if the berm has a structural height of more than 6 feet and a maximum storage capacity of 50-acre-feet or more of water. If they do, during design a dam breach analysis may be required as well as a Small Dam Safety Permit. SECTION 1 INTRODUCTION City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 1–Introduction Prepared by Strand Associates, Inc.® 1-1 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S1.doc\022508 1.01 INTRODUCTION This report is an addendum to the North Branch Campbell Creek Stormwater Management Plan, City of Oshkosh, Wisconsin, May 2006, which summarized the methodology and results of a study done by Strand Associates, Inc. to develop a stormwater management plan for the North Branch of Campbell Creek Watershed in the City of Oshkosh. The North Branch Campbell Creek Watershed is predominantly a fully developed urban watershed that comes together at West 4th Avenue and Sawyer Street with the South Branch of Campbell Creek. The North Branch of Campbell Creek and specifically the Landmark Plaza have experienced recent flooding. A sampling of photographs taken by City staff on June 11, 2004, documenting the flooding that occurred as a result of a June 10/11, 2004, storm event is included in Appendix A. Much of the development in this watershed occurred prior to the advent and implementation of strong guidelines on stormwater management, resulting in several areas with stormwater system capacity issues. This stormwater management plan addendum, in conjunction with the May 2006 study, will address ways to mitigate the existing stormwater flooding problems in the North Branch of Campbell Creek watershed and suggest ways to decrease the impacts of future development. This addendum builds upon the previous study that looked at eleven alternatives. The previous study recommended the implementation of Alternative 7. One of the Alternative 7 components was a wet detention basin at the intersection of 9th Avenue and South Washburn Street. The location of this detention has met with opposition due to its potential value as commercial property. At the November 14, 2006, City Council meeting, the Council adopted an ordinance to officially map the 9th and Washburn detention basin site contingent upon further study to explore other upstream detention options. As part of the addendum, Strand has updated the stormwater models to account for proposed WisDOT USH 41 impervious area additions and have added more detail to the stormwater models upstream of the Dickinson Avenue and South Washburn Street intersection. Alternative 7 was remodeled in the new stormwater model as Alternative 12. Five additional alternatives (Alternatives 13, 13B, 14, 15, and 16) were also modeled in search of an alternative to the detention basin at the 9th/Washburn detention site. 1.02 SCOPE OF STUDY This study included the following key elements: A. Topographic Survey A field survey was completed to provide vertical elevation and horizontal location of various portions of the storm sewer system including storm sewer and ditches from south of the Dickinson Avenue and South Washburn Street intersection southeasterly to south of the STH 44 and Waukau Avenue intersection. In addition, mapping data was obtained from previous work in the watershed. Mapping used for this study is discussed in Section 2 and shown in Figure 2.01-1. The field survey forms and survey information have been provided to the City of Oshkosh for use in updating the City’s Geographical Information System (GIS). City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 1–Introduction Prepared by Strand Associates, Inc.® 1-2 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S1.doc\022508 B. Storm Sewer System Map The storm sewer system map was revised to include additional detail in previous subbasin SBB 60. This map is shown in Figure 2.01-1 enclosed at the back of this report C. Analysis of Existing Drainage System The existing stormwater drainage system was analyzed with the XP-SWMMTM computer model. This addendum expands upon the previous model from south of the Dickinson Avenue and South Washburn Street intersection southeasterly to south of the STH 44 and Waukau Avenue intersection. This model was developed to estimate the peak discharge rates and runoff volumes during storm events under existing land use conditions. The model was also used to identify available capacities of existing storm sewers and detention basins. This analysis identified areas currently vulnerable to flooding during extreme storm events. D. Analysis of Potential Impacts of Future Development on Existing Drainage Systems The XP-SWWMTM model was used to determine locations where improvements to the existing drainage system will accommodate future development and mitigate the associated stormwater impacts under future land use conditions. This addendum expands upon the previous model to: ƒ Evaluate alternatives to reduce flooding in the North Branch Campbell Creek Watershed to a similar extent as originally provided by Alternative 7. ƒ Evaluate specific alternatives to reduce flooding at the Landmark Plaza shopping center to a similar extent as originally provided by Alternative 7. E. Stormwater Management Plan This project report includes recommendations based on an alternatives analysis. Discussion of project components is also included in the report. Opinions of Probable Cost for each conceptual alternative are included. All costs are presented in 4th quarter 2007 dollars. Future construction costs should be adjusted for inflation when final project schedules are determined. F. Implementation Plan The implementation plan includes the development of a schedule for completion of recommended improvements and a discussion of financing options for the recommended stormwater improvements. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 1–Introduction Prepared by Strand Associates, Inc.® 1-3 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S1.doc\022508 Figure 1.03-1 Study Area Location Relative to DNR Watersheds 1.03 LOCATION OF STUDY AREA The Campbell Creek watershed is in general located in an area east of South Oakwood Road, north of STH 44, west of the Fox River, and south of Taft Avenue. The location of the study area, which is in the Upper Fox River Basin, is shown in Figure 1.03-1. 1.04 OTHER SIMILAR STUDIES The following reports/plans are applicable to portions of the North Branch Campbell Creek planning area. Stormwater Management Plan–Campbell Creek Watershed, Prepared for City of Oshkosh, HNTB, December 1994. Citywide Storm Water Management Study, Prepared for City of Oshkosh, Mead & Hunt, March 2000. Stormwater Management Revenue Alternatives Phase I Feasibility Analysis, Tetra Tech MPS/Mead & Hunt, August 2000. Winnebago County Land and Water Resource Management Plan, 1998. The State of the Upper Fox River Basin, Wisconsin Department of Natural Resources (DNR), WT-665-2001, October 2001. North Branch Campbell Creek Stormwater Management Plan, City of Oshkosh, Wisconsin, May 2006, Strand Associates. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 1–Introduction Prepared by Strand Associates, Inc.® 1-4 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S1.doc\022508 1.05 APPLICABLE STANDARDS AND DESIGN CRITERIA See May 2006 Study. 1.06 PHASE II STORMWATER PERMIT See May 2006 Study. 1.07 DEFINITIONS AND ABBREVIATIONS The following definitions and abbreviations are presented as an aid to the reader. A. Definitions Average Sediment Depth–The average depth of deposited sediment measured over the entire pond area. Average Current Normal Pool Depth–The average depth of water measured over the entire pond area. This is the difference between the water surface and the top of sediment. Average Current Total Pond Depth–The average depth of the pond if all deposited sediment were removed. This is the difference between the water surface and the existing bottom of the pond. Control Structure–The manmade structure that controls the water released from a stormwater facility to the outfall. Curve Number–The Soil Conservation Service has devised a method of computing the runoff from an area based on a system of curve numbers. The curve number for an area of land is obtained by examining the land use and soil type of the land area. Flume–The structure or channel upstream of the stormwater facility used to convey stormwater to the facility. Forebay–The area of the pond near the inlet where heavy sediments are encouraged to settle out of the stormwater that enters a facility. Outfall–The piping, channel, or other equipment downstream of the control structure used to transfer water out of the control structure to the surrounding environment. Recurrence Interval–The probability that a given rainfall event will occur in a given year. For example, a 100-year rainfall event has a 1 percent chance of occurring in a given year (1/100 = 0.01 = 1 percent), a 5-year rainfall event has a 20 percent chance of occurring in a given year (1/5 = 0.20 = 20 percent). Subbasin–The parts of a drainage basin that, when combined, create the entire drainage basin for a facility. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 1–Introduction Prepared by Strand Associates, Inc.® 1-5 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S1.doc\022508 Time of Concentration (Tc)–“…the time for runoff to travel from the hydraulically most distant point of the watershed to a point of interest within the watershed,” SCS, 1986. Time Distribution of Rainfall–The amount of rainfall that has fallen during a storm event versus the amount of time that has elapsed during a storm event. Weir–A wall spanning the control structure. When the water level of the pond reaches the top of the weir, water flows over the weir and out of the pond. B. Abbreviations ac - acres ac-ft - acre feet BMP - Best Management Practices cfs - cubic feet per second CMP - corrugated metal pipe DNR - Wisconsin Department of Natural Resources FDM - Facilities Development Manual FEMA - Federal Emergency Management Agency HSG - Hydrologic Soils Groups ft - feet GIS - Geographic Information System MRCC - Midwestern Regional Climate Center NGVD - National Geodetic Vertical Datum NHI - National Heritage Inventory NOI - Notice of Intent NRCS - National Resource Conservation Service RCP - reinforced concrete pipe RCN - runoff curve number SCS - Soil Conservation Service sq mi - square miles Tc - time of concentration TIN - triangulated irregular network TSS - total suspended solids USACE - United States Army Corps of Engineers USGS - United States Geological Survey WisDOT - Wisconsin Department of Transportation WPDES - Wisconsin Pollutant Discharge Elimination System WWTP - wastewater treatment plant SECTION 2 CONTRIBUTING WATERSHED CHARACTERISTICS City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-1 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 2.01 BASIN CHARACTERISTICS AFFECTING STORMWATER RUNOFF A. General The amount of stormwater discharging from a watershed depends on a number of individual characteristics. Watershed size and topography, land use, soil types and degree of saturation, type of drainage system (storm sewers, open channels), and amount of watershed storage available all affect stormwater discharge. To quantify stormwater flows and volumes, an inventory of watershed physical characteristics in the Campbell Creek watershed was completed. This section describes physical land characteristics in the Campbell Creek watershed that impact stormwater runoff. B. Drainage Patterns Existing drainage patterns, watershed designations, and locations and sizes of storm sewer and other water features are identified in Figure 2.01-1 (enclosed the pocket folder at the back of this report). The Campbell Creek watershed, draining approximately 1,840 acres, is located west of the Fox River and south of Lake Butte des Morts and includes lands currently in the City of Oshkosh, Town of Algoma, and Town of Nekimi. The portion of the City being studied with this plan drains in four general manners. The northernmost portion, referred to as the North Branch of Campbell Creek (NBB-xx basin id designations), drains an area of approximately 140 acres east of USH 41 including Landmark Plaza prior to draining east through the storm sewer system. The southernmost portion referred to as the South Branch of Campbell Creek (SBB-xx basin id designations) drains a total of 1,000 acres. Of this total, approximately 665 acres of land west of USH 41 then drains either northerly towards Sawyer Creek via a WisDOT ditch or easterly through the Armory area before joining up with the North Branch near the intersection of Glen Avenue and Mason Street. The joined North and South Branch systems continue easterly to a backwater of the Fox River through the Main Stem watershed (CCB-xx basin id designations) that drains approximately 225 acres. The Fox River then discharges into Lake Winnebago prior to draining northeasterly to Green Bay and Lake Michigan. A portion of the Sawyer Creek watershed (SCB-xx basin id designations) is interconnected with the North Branch and South Branch systems allowing approximately 475 acres of drainage to impact drainage patterns in the Campbell Creek watershed. Upstream stormwater flows are able to enter Landmark Plaza through a 3-foot x 4.5-foot reinforced concrete pipe (RCP) Box starting in the ditch at the west side of USH 41 that discharges into the ditch that runs on the south side of Landmark Plaza. At the southeast corner of Landmark Plaza, the ditch enters the storm sewer system and heads north toward the center of the east side of Landmark Plaza before heading east to the Campbell Creek outfall in a 36-inch x 58-inch corrugated metal pipe (CMP) at an approximate average slope of 0.232 percent. The Fox River through Oshkosh and Lake Winnebago are both identified by the DNR as impaired waters and are on the Federal Clean Water Act Section 303(d) list. Impaired waters are those that are not meeting the state’s water quality standards. More information on the 303 (d) list can be found on the DNR’s Web site at: http://dnr.wi.gov/org/water/wm/wqs/303d/303d.html City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 HSG Percent of Watershed A 0.5 B 0.4 B/D 2.0 C 95.2 D 1.8 Table 2.01-1 Hydrologic Soil Groups C. Soils The amount of stormwater runoff produced by a storm event is impacted by the types of soil underlying the watershed. Soils having a high percentage of sand and gravel will absorb a higher percentage of stormwater runoff than will soils having high clay content. This means that sandy soil generally produces less runoff than clay soil. The Natural Resource Conservation Service (NRCS) classifies soil types in categories known as Hydrologic Soil Groups (HSG). Group A soils consist of sandy soils having high infiltration rates and low runoff potential. Group B soils have moderately fine to moderately coarse textures and moderate runoff potential. Group C soils are typically silty clay loam soils having moderately fine to fine textures and a low infiltration capacity. Examples of Group D soils are clays, soils with a permanent high water table, and shallow soils over nearly impervious material. Group D soils have a very low infiltration capacity and have high runoff potential. Soil types, hydrologic soil group, and expected soil permeability at 36-inch depth in the Campbell Creek Watershed are identified in Table 2.01-2 and illustrated in Figure 2.01-2. According to the Winnebago County, Wisconsin, Soils Survey, published by the U.S. Department of Agriculture in cooperation with the Research Division of the College of Agricultural and Life Sciences, University of Wisconsin, local soils are primarily silt loams and silty clay loams. These soils are classified by the NRCS as mainly HSG Group C soils. Infiltration rates for the Group B soils range from 0.15 to 0.30 inches per hour. Infiltration rates for the Group C soils range from 0.05 to 0.15 inches per hour. Infiltration rates for Group A soils are generally greater than 0.30 inches per hour. The percentages of each hydrologic soil group in the watershed are shown in Table 2.01-1. According to the NRCS Soil Survey for Winnebago County, the predominant soil type in the Campbell Creek watershed belongs to the Kewaunee Silt Loam series. These are well drained and moderately well-drained soils on convex hills and lower side slopes with a silt loam surface layer, a firm clay subsoil, and a firm silty clay loam substratum. SOILS MAP NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 2 . 0 1 - 2 1- 382 . 0 3 0 Taft Ave Kn a p p S t W. So u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S K o e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma SAWYER CREEK 60 20 27 15 8 21 18 1930 40 6 5 2438 3658 3622 36 3150 51 3 1 54 30 3843 6 48 7244 3654 5031 9 2918 24 4327 58 3 6 42 12 2633 2945 4472 10 2516 1423 6540 3453 0 18 24 21 12 24 24 8 15 12 15 3658 8 12 21 24 12 0 15 12 31 5 0 12 15 48 36 15 18 12 0 12 15 15 12 12 18 12 24 12 12 18 15 15 3658 18 8 8 15 18 8 18 21 21 12 12 15 12 48 12 21 26 3 3 36 18 24 24 15 12 36 21 8 15 0 18 0 18 24 12 18 24 15 12 24 18 8 12 12 8 12 12 15 8 21 18 24 8 24 24 8 21 10 8 18 30 24 48 24 8 12 36 6 8 21 15 827 8 15 12 8 36 8 18 12 12 30 12 12 18 12 24 42 15 8 8 30 8 15 12 8 24 8 8 12 18 12 42 8 12 24 18 12 36 15 24 12 12 1212 18 12 12 12 8 18 8 12 18 18 15 15 10 18 15 8 24 30 12 8 12 0 12 15 12 18 10 36 12 18 12 2438 12 21 8 21 42 8 15 2945 12 10 12 12 12 8 36 15 18 12 3658 24 12 12 15 18 18 12 15 15 24 21 44 7 2 15 18 24 0 18 0 12 12 8 8 8 12 12 24 36 12 18 12 0 15 12 2945 15 12 6 8 0 18 24 24 15 36 8 36 5 8 12 24 12 24 15 12 12 15 42 8 30 12 20 12 10 6 12 6 8 36 12 12 12 3658 12 15 30 12 12 24 15 8 18 12 8 12 15 15 30 12 12 12 12 12 21 8 12 8 15 42 8 15 18 12 12 8 30 6 24 2945 15 12 12 8 12 8 8 8 15 42 8 18 12 12 8 12 12 30 0 12 12 0 21 12 21 24 8 36 12 24 30 18 36 12 12 12 0 8 42 6 12 18 12 12 27 18 2438 0 30 3658 12 18 12 42 30 36 60 48 12 12 12 21 2427 18 30 18 18 15 18 15 8 6 8 15 18 21 15 12 2516 48 24 12 12 0 48 3658 24 15 12 12 24 21 8 48 8 27 12 8 15 21 8 15 48 8 15 24 18 24 15 3658 0 12 12 15 8 30 15 15 12 12 12 1821 12 18 24 10 21 24 36 12 8 8 18 24 15 15 12 8 12 21 12 24 12 12 0 6540 18 30 1212 12 8 18 8 12 18 18 5836 21 12 12 42 8 42 15 12 18 36 21 21 12 36 15 15 15 15 0 8 15 5836 8 18 8 15 15 24 15 12 3658 24 12 12 12 12 8 21 21 0 3622 21 3658 12 42 21 36 8 12 12 12 12 15 8 12 0 12 30 27 12 12 24 0 12 12 12 12 6 12 30 18 0 0 024 24 48 18 15 12 0 30 18 42 8 8 24 12 18 24 18 36 15 8 19 3 0 8 42 18 12 18 15 12 8 12 15 0 12 48 18 18 15 24 12 12 21 12 12 18 18 24 15 10 36 24 0 15 8 24 8 12 5836 12 42 24 12 15 12 12 42 15 12 24 0 15 8 15 8 24 12 12 8 8 21 24 12 12 18 30 36 10 0 12 27 21 8 15 48 24 12 18 15 12 48 30 15 36 12 15 24 12 12 24 8 12 15 15 30 15 24 12 30 24 12 30 18 8 54 24 12 48 12 24 18 15 15 15 8 15 30 18 12 15 21 8 24 12 15 12 8 24 8 18 24 36 24 21 2945 18 8 8 24 15 12 0 4815 12 21 15 12 24 36 0 15 18 8 12 36 15 27 15 15 42 18 15 21 12 21 60 36 8 0 12 8 10 0 18 18 8 12 12 30 30 48 15 12 18 30 8 15 12 48 12 8 15 21 21 30 15 27 12 24 48 12 12 18 15 24 12 15 27 36 15 21 36 8 12 15 8 12 27 24 24 15 12 5836 12 24 18 0 18 0 12 29 1 8 12 8 6 24 12 36 36 8 30 21 15 24 30 12 12 12 8 30 12 8 24 18 5836 12 8 12 10 24 12 12 24 15 15 21 42 0 21 21 12 8 12 18 12 12 18 15 12 18 48 21 15 36 21 24 21 36 8 18 30 12 21 18 24 30 12 15 8 12 8 24 27 12 15 12 1515 12 8 12 42 12 30 12 8 12 12 12 8 12 24 8 42 18 15 0 21 42 12 15 0 20 1815 42 30 12 8 12 8 24 58 3 6 12 12 12 12 5031 12 12 12 15 8 12 15 15 12 15 24 24 12 12 18 24 6 15 18 12 12 12 21 15 24 24 18 15 30 12 8 12 12 12 15 12 12 30 12 18 0 12 15 0 12 15 15 12 15 12 15 42 8 18 30 18 21 24 30 15 8 15 12 30 12 21 12 12 15 15 15 27 10 10 6 12 12 42 15 15 8 8 15 30 12 12 12 15 24 24 12 18 18 15 36 24 36 36 1827 12 12 21 30 15 8 12 8 12 42 18 15 12 12 10 18 12 15 15 27 42 12 58 3 6 12 50 3 1 60 18 30 12 8 15 15 24 10 18 12 15 30 24 18 12 12 30 12 18 48 36 42 0 3012 18 21 29 4 5 21 18 12 18 12 15 10 24 60 18 24 12 12 30 42 10 12 8 15 15 48 18 48 15 24 12 12 30 12 21 48 15 10 30 12 18 12 12 12 15 18 21 15 48 18 12 10 24 18 12 12 12 24 0 30 12 15 24 2516 30 15 12 8 12 12 12 21 15 8 21 12 36 5836 15 12 8 8 24 21 12 12 15 12 8 12 8 18 12 12 18 18 12 48 21 8 18 18 15 18 12 15 21 12 15 12 6 27 18 0 8 12 18 15 12 12 15 20 15 0 21 18 18 27 18 18 24 18 8 27 30 24 12 18 8 42 10 24 12 8 0 12 24 15 27 12 12 15 15 8 18 42 8 48 12 18 48 0 12 24 30 12 18 12 8 12 12 36 8 6 15 42 6 12 48 21 12 12 12 36 18 8 18 18 30 36 15 48 0 36 12 12 8 12 18 18 36 12 18 18 18 SBB-190 CCB-10 SBB-15 SCB-100 SCB-35 SCB-85 SBB-75 SBB-175 SCB-75 SBB-76 SCB-70 SBB-95 SBB-85 SCB-50 SCB-10 SBB-60 CCB-20 SBB-55 NBB-20 SBB-140 SBB-45 SCB-15 SBB-25.A SBB-50 SBB-176 SBB-30 SBB-90 NBB-15 SBB-10 SCB-30 SCB-55 SBB-20 SCB-20 NBB-55 SBB-41 SBB-61 SCB-95 NBB-10 SBB-40 SCB-40 SBB-135 SBB-185 SBB-180 NBB-45 CCB-05 SBB-65 SBB-70 NBB-30 SBB-141 SBB-115 SBB-05 SCB-90 CCB-15 SBB-25.D SCB-25 SBB-71 SCB-80 SCB-60 SBB-80 SCB-65 NBB-25 SBB-42 NBB-05 SCB-05 NBB-40 SBB-25.F SBB-25.B SBB-25.E SBB-170 SBB-35 NBB-35 SBB-25.C SBB-145 SBB-155 NBB-50 SBB-105 SBB-120 SCB-45 SBB-165 SBB-130 SBB-150 SBB-110 SBB-100 SBB-160 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 2 . 01 - 2 - So il s . m x d 0 1,500 3,000750 Feet ³ Legend Municipal Boundary Drainage Basin Boundary Sub Drainage Basin Boundary Updated Basin Boundary Hydrologic Soils Group A B B/D C D Witzel Ave US H W Y 4 1 60 30 27 18 8 24 20 21 12 10 1423 15 19 3 0 24 18 27 18 12 10 12 24 24 12 12 12 12 10 12 12 60 15 30 18 12 15 12 18 12 30 15 12 12 30 12 12 12 24 12 12 15 18 12 60 12 12 15 30 15 15 12 24 12 60 18 18 24 12 8 20 18 SCB-35 SCB-30 SCB-10 SCB-25 SCB-40 SCB-20 SCB-15 CCB-10 NBB-40 SCB-50 SCB-E NBB-45 NBB-50 NBB-55 SCB-B SCB-C SCB-D NBB-35 SCB-A SCB-45 Hwy 41 Updated Basins 0 300 600150 Feet City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-3 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 Symbol Soil Description Permeability at 36 inches (in/hr) HSG1 Percent of Watershed HmB Hochheim loam, 2 to 6% slopes Gently sloping, well drained soils on broad crests of hills and ridges on till plains; loam surface layer; friable loam subsoil; gravelly fine, sandy loam substratum. 0.2-2.0 B 0.4% HrB Hortonville silt loam, 2 to 6% slopes Gently sloping, well drained soils on convex hills and lower side slopes on till plains; silt loam surface layer; friable loam subsoil; friable loam substratum. 0.2-2.0 C 0.5% KnB Kewaunee silt loam, 2 to 6% slopes Gently sloping, well drained and moderately well drained soil is on convex hills and lower side slopes; silt loam surface layer; firm clay subsoil; firm silty clay loam substratum. 0.06-0.6 C 54.1% KoC2 Kewaunee silt loam, 6 to 12% slopes Sloping, well drained soil on sides of moraines and hills; silty clay loam surface layer; firm clay subsoil; firm silty clay loam substratum. 0.06-0.6 C 2.3% LzB Lorenzo Variant loam, 2 to 8% slopes Gently sloping, moderately well drained soil on till plains; loam surface layer; upper part of subsoil is friable caly loam; lower part of subsoil is friable gravelly sandy loam; very gravelly loamy sand substratum. 0.06-0.6 C 3.1% MaA Manawa silty clay loam, 0 to 3% slopes Nearly level to gently sloping, somewhat poorly drained soil in drainageways and depressional areas; silty clay loam surface layer; upper part of subsoil is firm silty clay loam; lower part of subsoil and substratum is firm silty clay. 0.06-0.2 C 21.4% MtA Mosel silt loam, 0 to 3% slopes Nearly level to gently sloping, somewhat poorly drained soil on valley terraces and in drainageways and swales in uplands; silt loam surface layer; friable silt loam subsurface layer; upper part subsoil is friable clay loam; lower part subsoil is firm silty clay; firm silty clay substratum. 0.06-0.6 C 2.9% Na Navan silt loam Nearly level, poorly drained soil in drainageways and swales in the uplands; silt loam surface layer; upper subsoil is friable silt loam; lower subsoil is firm clay loam; firm silty clay substratum. 0.6-2.0 D 0.7% OmB Omro clay loam, 2 to 6% slopes Gently sloping, well drained soil is on crests and sides of broad hills; clay loam surface layer; upper subsoil is firm clay; lower subsoil is firm silty clay; friable gravelly fine sandy loam substratum. 0.06-0.6 C 4.5% Pg Pits, gravel Excavation pits from which sand and gravel have been removed. NA A 0.5% Pu Poygan silty clay loam Nearly level, poorly drained soil in drainageways and depressional areas; silty clay loam surface area; firm silty clay subsoil; firm silty clay substratum. 0.06-0.2 D 1.2% UoA Udorthents, 0 to 3% slopes Nearly level to gently sloping, moderately well drained to somewhat poorly drained soils adjacent to major drainageways and lakes; 1 to 4 feet of fill material over poorly drained soils; fill material is commonly clay, silty clay, silty clay loam and clay loam containing pebbles and stones; buried soil is mineral or organic. NA C 6.5% We Wauseon silt loam Nearly level, poorly drained soil in drainageways and swales in the uplands; silt loam surface layer; upper subsoil is friable silt loam; middle and lower subsoil is friable fine sandy loam; firm silty clay loam substratum. <0.6 B/D 2.0% 1 HSG = Hydrologic soils group Table 2.01-2 Campbell Creek Watershed Soils City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-4 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 E. Land Use Land use is another factor that affects the amount of stormwater runoff that will be produced by a rainstorm. Urbanization and development reduce the ability of the ground to absorb stormwater, typically causing peak discharges and runoff volumes to increase. The time from the beginning of the storm event to the occurrence of the peak runoff may also be significantly shortened. Existing and future land use in the Campbell Creek watershed is shown in Figures 2.01-3 and 2.01-4. Existing land use is based on the City’s impervious area GIS layer supplemented with review of aerial information provided by Winnebago County. See Figure 2.01-5 for a graphic of the different types of existing landuse according to the City’s Smart Growth Plan. Future land use is also based on the City’s impervious area GIS layer as shown in Figure 2.01-4 and is supplemented with land use from the 20-Year Land Use Plan (Smart Growth Plan) shown in Figure 2.01-6 for areas currently not developed. Wisconsin Department of Transportation (WisDOT) proposed improvements (to the best of our knowledge as of August 15, 2007) have also been incorporated into the future land use shown in Figure 2.01-4. This investigation indicates that the watershed is currently almost entirely built out except for agricultural lands in the southwestern portion of the watershed and various vacant parcels of land in the urbanized central portion of the watershed. The City of Oshkosh Stormwater Ordinance (Chapter 24) in conjunction with NR 151 regulates future development (over 1 acre in size). Future land use will likely increase future stormwater volumes due to the increase in impervious area. We have also included a zoning map from the City Smart Growth Plan in Figure 2.01-7. Tables 2.01-3 and 2.01-4 summarize the existing and future hydrologic parameters for each drainage basin, respectively. These tables show that the impervious area increases approximately 30.9 percent between existing and future land use conditions. 2.02 EXPECTED PRECIPITATION DEPTHS According to the Midwestern Regional Climate Center (MRCC) Web site, the City of Oshkosh receives an average annual precipitation of 31.57 inches. Significant runoff-producing events typically occur during spring and summer thunderstorms as a result of stormwater runoff from short-duration, intense storm events. The depth and duration of rainfall in a watershed for a given storm event has a major impact on the amount of stormwater runoff produced. Table 2.02-1 summarizes expected rainfall depths for the 1-year through 100-year storm frequencies for the region (Bulletin 71, Rainfall Atlas of the Midwest, Floyd A. Huff and James R. Angel–Climatic Section 6). These rainfall totals are used in conjunction with the Huff distribution to estimate peak storm discharges. EXISTING LAND USE - IMPERVIOUS AREA MAP NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 2 . 0 1 - 3 1- 382 . 0 3 0 Taft Ave Kn a p p S t W. So u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S K o e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma SAWYER CREEK SBB-190 CCB-10 SBB-15 SCB-100 SCB-35 CCB-05 SCB-85 SBB-75 SBB-65 SBB-175 SCB-75 SBB-76 SCB-70 SBB-95 SBB-85 SBB-70 SCB-50 SCB-10 NBB-30 SBB-60 CCB-20 SBB-55 SBB-141 NBB-20 SBB-140 SBB-45 SCB-15 SBB-25.A SBB-50 SBB-115 SBB-176 SBB-30 SBB-90 NBB-15 SBB-10 SCB-30 SCB-55 SBB-20 SCB-20 NBB-55 SBB-05 SBB-41 SCB-90 SBB-61 CCB-15 SCB-95 NBB-10 SCB-25 SBB-71 SCB-80 SBB-40 SCB-40 SBB-135 SCB-60 SCB-65 NBB-40 SBB-25.B SBB-185 SBB-35 SBB-180 NBB-45 SBB-25.D SBB-80 NBB-25 SBB-42 NBB-05 SCB-05 SBB-25.F SBB-25.E SBB-170 NBB-35 SBB-145 SBB-25.C SBB-155 NBB-50 SBB-105 SBB-120 SCB-45 SBB-165 SBB-130 SBB-150 SBB-110 SBB-100 SBB-160 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 2 . 01 - 3 - Im pe rvi ou s Areas . mx d 0 1,500 3,000750 Feet ³ Legend Municipal Boundary Drainage Basin Boundary Sub Drainage Basin Boundary Impervious Area Pervious Area (Non-Agriculture) Pervious Area (Agriculture) Minor ROW Major ROW DOT ROW FUTURE LAND USE - IMPERVIOUS AREA MAP NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 2 . 0 1 - 4 1- 382 . 0 3 0 Taft Ave Kn a p p S t W. So u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S Ko e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma SAWYER CREEK SBB-190 CCB-10 SBB-15 SCB-100 SCB-35 CCB-05 SCB-85 SBB-75 SBB-65 SBB-175 SCB-75 SBB-76 SCB-70 SBB-95 SBB-85 SBB-70 SCB-50 SCB-10 NBB-30 SBB-60 CCB-20 SBB-55 SBB-141 NBB-20 SBB-140 SBB-45 SCB-15 SBB-25.A SBB-50 SBB-115 SBB-176 SBB-30 SBB-90 NBB-15 SBB-10 SCB-30 SCB-55 SBB-20 SCB-20 NBB-55 SBB-05 SBB-41 SCB-90 SBB-61 CCB-15 SCB-95 NBB-10 SCB-25 SBB-71 SCB-80 SBB-40 SCB-40 SBB-135 SCB-60 SCB-65 NBB-40 SBB-25.B SBB-185 SBB-35 SBB-180 NBB-45 SBB-25.D SBB-80 NBB-25 SBB-42 NBB-05 SCB-05 SBB-25.F SBB-25.E SBB-170 NBB-35 SBB-145 SBB-25.C SBB-155 NBB-50 SBB-105 SBB-120 SCB-45 SBB-165 SBB-130 SBB-150 SBB-110 SBB-100 SBB-160 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 2 . 01 - 4 - Fu t u r e Im p e r v i o u s A r e a s . m xd 0 1,500 3,000750 Feet ³ Legend Municipal Boundary Drainage Basin Boundary Sub Drainage Basin Boundary Updated Basins Impervious Area Pervious Area (Non-Agriculture) Pervious Area (Agriculture) Minor ROW Major ROW DOT ROW Industrial Residential Commercial Witzel Ave US H W Y 4 1 SCB-35 SCB-30 SCB-10 SCB-25 SCB-40 SCB-20 SCB-15 CCB-10 NBB-40 SCB-50 SCB-E NBB-45 NBB-50 NBB-55 SCB-B SCB-C SCB-D NBB-35 SCB-A SCB-45 Hwy 41 Updated Basins 0 600300 Feet EXISTING LAND USE MAP - SMART GROWTH PLAN NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 2 . 0 1 - 5 1- 382 . 0 3 0 Taft Ave Kn a p p S t W. So u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S Ko e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma City of Oshkosh SAWYER CREEK SBB-190 CCB-10 SBB-15 SCB-100 SCB-35 CCB-05 SCB-85 SBB-75 SBB-65 SBB-175 SCB-75 SBB-76 SCB-70 SBB-95 SBB-85 SBB-70 SCB-50 SCB-10 NBB-30 SBB-60 CCB-20 SBB-55 SBB-141 NBB-20 SBB-140 SBB-45 SCB-15 SBB-25.A SBB-50 SBB-115 SBB-176 SBB-30 SBB-90 NBB-15 SBB-10 SCB-30 SCB-55 SBB-20 SCB-20 NBB-55 SBB-05 SBB-41 SCB-90 SBB-61 CCB-15 SCB-95 NBB-10 SCB-25 SBB-71 SCB-80 SBB-40 SCB-40 SBB-135 SCB-60 SCB-65 NBB-40 SBB-25.B SBB-185 SBB-35 SBB-180 NBB-45 SBB-25.D SBB-80 NBB-25 SBB-42 NBB-05 SCB-05 SBB-25.F SBB-25.E SBB-170 NBB-35 SBB-145 SBB-25.C SBB-155 NBB-50 SBB-105 SBB-120 SCB-45 SBB-165 SBB-130 SBB-150 SBB-110 SBB-100 SBB-160 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 2 . 01 - 5 - Ex i st ing L a n d U s e . m xd 0 1,500 3,000750 Feet ³ Legend Land Use Commercial Industrial Residential Agriculture Government Infill Non-Res Municipal Boundary Landfill-Quarry Mixed Use Parking Lot Public Park Rec-Open Space School Vacant Land Infrastructure InstitutionalDrainage Basin Boundary Sub Drainage Basin Boundary 20 YEAR LAND USE PLAN - SMART GROWTH PLAN NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 2 . 0 1 - 6 1- 382 . 0 3 0 Taft Ave Kn a p p S t W. So u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S Ko e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma SAWYER CREEK SBB-190 CCB-10 SBB-15 SCB-100 SCB-35 CCB-05 SCB-85 SBB-75 SBB-65 SBB-175 SCB-75 SBB-76 SCB-70 SBB-95 SBB-85 SBB-70 SCB-50 SCB-10 NBB-30 SBB-60 CCB-20 SBB-55 SBB-141 NBB-20 SBB-140 SBB-45 SCB-15 SBB-25.A SBB-50 SBB-115 SBB-176 SBB-30 SBB-90 NBB-15 SBB-10 SCB-30 SCB-55 SBB-20 SCB-20 NBB-55 SBB-05 SBB-41 SCB-90 SBB-61 CCB-15 SCB-95 NBB-10 SCB-25 SBB-71 SCB-80 SBB-40 SCB-40 SBB-135 SCB-60 SCB-65 NBB-40 SBB-25.B SBB-185 SBB-35 SBB-180 NBB-45 SBB-25.D SBB-80 NBB-25 SBB-42 NBB-05 SCB-05 SBB-25.F SBB-25.E SBB-170 NBB-35 SBB-145 SBB-25.C SBB-155 NBB-50 SBB-105 SBB-120 SCB-45 SBB-165 SBB-130 SBB-150 SBB-110 SBB-100 SBB-160 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 2 . 01 - 6 - 20 Y e a r L a n d U s e P l an . mx d 0 1,500 3,000750 Feet ³ Legend Municipal Boundary Drainage Basin Boundary Sub Drainage Basin Boundary Updated Basins 20-Year Land Use Plan Commercial Industrial Pro Public Institution Residential Witzel Ave US H W Y 4 1 SCB-35 SCB-30 SCB-10 SCB-25 SCB-40 SCB-20 SCB-15 CCB-10 NBB-40 SCB-50 SCB-E NBB-45 NBB-50 NBB-55 SCB-B SCB-C SCB-D NBB-35 SCB-A SCB-45 Hwy 41 Updated Basins 0 600300 Feet ZONING MAP - SMART GROWTH PLAN NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 2 . 0 1 - 7 1- 382 . 0 3 0 Taft Ave Kn a p p S t W. So u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S Ko e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma City of Oshkosh SAWYER CREEK SBB-190 CCB-10 SBB-15 SCB-100 SCB-35 CCB-05 SCB-85 SBB-75 SBB-65 SBB-175 SCB-75 SBB-76 SCB-70 SBB-95 SBB-85 SBB-70 SCB-50 SCB-10 NBB-30 SBB-60 CCB-20 SBB-55 SBB-141 NBB-20 SBB-140 SBB-45 SCB-15 SBB-25.A SBB-50 SBB-115 SBB-176 SBB-30 SBB-90 NBB-15 SBB-10 SCB-30 SCB-55 SBB-20 SCB-20 NBB-55 SBB-05 SBB-41 SCB-90 SBB-61 CCB-15 SCB-95 NBB-10 SCB-25 SBB-71 SCB-80 SBB-40 SCB-40 SBB-135 SCB-60 SCB-65 NBB-40 SBB-25.B SBB-185 SBB-35 SBB-180 NBB-45 SBB-25.D SBB-80 NBB-25 SBB-42 NBB-05 SCB-05 SBB-25.F SBB-25.E SBB-170 NBB-35 SBB-145 SBB-25.C SBB-155 NBB-50 SBB-105 SBB-120 SCB-45 SBB-165 SBB-130 SBB-150 SBB-110 SBB-100 SBB-160 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 2 . 01 - 7 - Zo n in g . m xd 0 1,500 3,000750 Feet ³ Witzel Ave US H W Y 4 1 SCB-35 SCB-10 SCB-30 SCB-25 SCB-20 SCB-15 NBB-55 SCB-40 CCB-10 SCB-50 NBB-40 SCB-E NBB-45 NBB-35 NBB-50 SCB-B SCB-C SCB-45 SCB-D NBB-25 SCB-A Hwy 41 Updated Basins 0 600300 Feet Legend Municipal Boundary Drainage Basin Boundary Updated Basins Sub Drainage Basin Boundary Zoning Commercial (Includes - C-1, C-1PD, C-2,C-2PD, C-3, C-3DO, C-3PD) Manufacturing (Includes - M-1, M-1PD, M-2,M-2DO, M-2PD, M-3, M-3PD) Residential (Includes - R-1, R-1C, R-1LO,R-1PD, R-2, R-2PD, R-3, R-3PD,R-4, R-4PD, R-5, R-5PD) City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® Page 1 of 1 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 2.01-3.doc\022508 TABLE 2.01-3 EXISTING CONDITIONS AND HYDROLOGIC PARAMETERS Basin ID Structure ID Tc (hrs) Tc (min) Drainage Basin Area (ac) Total Impervious Area (ac) Total Pervious Area (ac) Total Pervious Ag. (ac) Pervious (%) Impervious (%) Pervious RCN Composite RCN CCB-05 D-OF-3 0.47 28.20 46.68 21.15 25.52 0.00 55 45 74 85 CCB-10 Outfall 1 0.75 45.00 134.37 66.46 67.91 0.00 51 49 75 86 CCB-15 06-462 0.32 19.20 15.97 5.94 10.03 0.00 63 37 74 83 CCB-20 06-602 0.89 53.40 27.78 11.55 16.22 0.00 58 42 74 84 Total 224.80 105.11 119.69 0.00 NBB-05 06-469 0.56 33.60 7.00 2.87 4.14 0.00 59 41 74 84 NBB-10 06-552 0.44 26.40 14.29 6.73 7.57 0.00 53 47 75 86 NBB-15 06-653 0.70 42.00 21.75 8.75 13.00 0.00 60 40 74 84 NBB-20 06-770 0.70 42.00 26.03 5.51 20.52 0.00 79 21 74 79 NBB-25 06-1062 0.39 23.40 7.08 3.61 3.48 0.00 49 51 74 86 NBB-30 06-688 0.34 20.40 29.72 17.25 12.47 0.00 42 58 76 88 NBB-35 06-843 0.30 18.00 3.98 3.03 0.95 0.00 24 76 75 92 NBB-40 06-846 0.09 5.40 6.08 5.02 1.07 0.00 18 82 74 94 NBB-45 06-847 0.08 4.80 4.25 4.03 0.22 0.00 5 95 74 97 NBB-50 06-1293.2 0.09 5.40 2.31 2.25 0.06 0.00 3 97 74 97 NBB-55 LP-5 0.30 18.00 18.43 6.92 11.51 0.00 62 38 76 84 Total 140.93 65.96 74.97 0.00 SBB-05 06-471 0.31 18.60 16.64 7.04 9.60 0.00 58 42 74 84 SBB-10 06-474 0.62 37.20 20.38 7.19 13.20 0.00 65 35 74 83 SBB-15 06-473 0.77 46.20 73.71 23.88 49.83 0.00 68 32 68 78 SBB-20 AEW-1 0.54 32.40 19.10 7.61 11.50 0.00 60 40 74 84 SBB-25A 13-420 0.71 42.60 29.91 11.09 18.82 0.00 63 37 74 83 SBB-25B 13-660 0.44 26.40 6.27 2.56 3.71 0.00 59 41 75 84 SBB-25C 13-454 0.38 22.80 4.43 2.48 1.95 0.00 44 56 75 88 SBB-25D 13-1190 0.29 17.40 18.21 14.36 3.85 0.00 21 79 78 95 SBB-25E AEW-36 0.08 5.00 5.72 2.56 3.17 0.00 55 45 79 92 SBB-25F AEW-37 0.16 9.60 6.62 3.81 2.81 0.00 42 58 78 93 SBB-30 13-457 0.19 11.40 21.87 12.62 9.25 0.00 42 58 74 88 SBB-35 13-460 0.33 19.80 4.34 2.40 1.94 0.00 45 55 75 88 SBB-40 AD-4 0.63 37.80 9.89 0.28 9.61 0.00 97 3 74 75 SBB-41 AP-1 0.36 21.60 16.30 4.44 11.87 0.00 73 27 74 81 SBB-42 AD-3 0.13 7.80 6.93 2.47 4.45 0.00 64 36 74 83 SBB-45 13-1217 0.18 10.80 24.46 20.17 4.29 0.00 18 82 74 94 SBB-50 13-1221 0.13 7.80 23.81 18.71 5.11 0.00 21 79 75 93 SBB-55 AEW-15 0.44 26.40 26.46 14.84 11.62 0.00 44 56 75 88 SBB-60 STR-10 1.05 63.00 28.83 13.96 14.87 0.00 52 48 77 87 SBB-61 AEW-32 0.41 24.60 15.54 6.72 8.82 0.00 57 43 74 84 SBB-65 13-874 0.53 31.80 39.84 15.31 24.53 0.00 62 38 74 83 SBB-70 13-983 0.42 25.20 32.10 10.60 21.51 0.00 67 33 74 82 SBB-71 13-1033 0.35 21.00 12.80 4.82 7.98 0.00 62 38 74 83 SBB-75 AEW-22 0.49 29.40 44.54 15.11 29.43 0.00 66 34 75 83 SBB-76 AEW-19 0.68 40.80 38.46 14.81 23.66 0.00 62 38 75 83 SBB-80 2125-2175 0.49 29.40 8.24 1.73 6.52 0.00 79 21 74 79 SBB-85 13-1003 0.39 23.40 32.55 14.34 18.21 0.00 56 44 75 85 SBB-90 2690 B. AV 0.15 9.00 21.72 12.11 9.61 0.00 44 56 78 89 SBB-95 13-4 0.68 40.80 34.19 8.17 26.03 0.00 76 24 75 80 SBB-100 2301-UA-2.1 0.08 5.00 0.94 0.52 0.42 0.00 45 55 79 90 SBB-105 2301-UA-1.1 0.22 13.20 2.59 0.35 2.23 0.00 86 14 74 77 SBB-110 2301-UA-3 0.20 12.00 1.53 0.45 1.07 0.00 70 30 75 82 SBB-115 AEW-25 0.36 21.60 25.17 11.41 13.76 0.00 55 45 76 86 SBB-120 2751-2 0.42 25.20 2.32 1.04 1.28 0.00 55 45 74 85 SBB-125 2751-4 0.08 5.00 1.01 1.01 0.00 0.00 0 100 74 98 SBB-130 2751-3 0.34 20.40 2.07 1.14 0.93 0.00 45 55 74 87 SBB-135 2980-1.5 0.08 5.00 10.44 1.57 8.87 0.00 85 15 75 79 SBB-140 AEW-26 0.43 25.80 28.12 7.87 20.25 0.00 72 28 76 82 SBB-141 AEW-26 0.42 25.20 29.64 8.41 21.23 0.00 72 28 74 81 SBB-145 2980-1.4 0.08 5.00 3.98 3.25 0.73 0.00 18 82 75 94 SBB-150 4000-91.4 0.21 12.60 1.77 0.64 1.12 0.00 64 36 74 83 SBB-155 2449-1.5 0.14 8.40 2.71 1.85 0.86 0.00 32 68 74 90 SBB-160 4000-91.3 0.08 5.00 0.89 0.33 0.56 0.00 63 37 74 83 SBB-165 4000-91.2 0.27 16.20 2.22 1.14 1.07 0.00 48 52 74 86 SBB-170 2449-1.3 0.21 12.60 5.02 0.97 4.04 0.00 81 19 74 79 SBB-175 AEW-28 0.94 56.40 44.87 5.07 16.91 22.89 89 11 82 83 SBB-176 AEW-40 0.73 43.80 25.08 7.20 17.87 0.00 71 29 75 81 SBB-180 2531-1 0.13 7.80 4.90 2.41 2.48 0.01 51 49 75 86 SBB-185 2531-3 0.46 27.60 5.18 0.96 4.20 0.02 82 18 74 78 SBB-190 44D-9 0.53 31.80 156.49 6.03 5.60 144.86 96 4 83 83 Total 1000.79 339.82 493.19 167.78 SCB-05 16-430 0.29 17.40 6.18 2.89 3.29 0.00 53 47 74 85 SCB-10 16-428 0.53 31.80 30.35 15.20 15.15 0.00 50 50 74 86 SCB-15 06-640 0.40 24.00 24.37 12.35 12.02 0.00 49 51 74 86 SCB-20 06-678 0.73 43.80 18.95 8.81 10.14 0.00 54 46 74 85 SCB-25 06-1355 0.11 6.60 13.72 7.53 6.19 0.00 45 55 78 89 SCB-30 16-647 0.83 49.80 20.27 5.53 8.52 6.21 73 27 79 84 SCB-35 06-773 0.79 47.40 51.20 26.23 24.96 0.00 49 51 75 87 SCB-40 40D-19 1.07 64.20 9.30 4.61 4.69 0.00 50 50 76 87 SCB-45 40D-17 0.14 8.40 2.04 0.74 1.29 0.00 64 36 80 86 SCB-50 WP-1 0.21 12.60 31.38 19.57 11.80 0.00 38 62 75 89 SCB-55 40D-12 0.30 18.00 20.19 10.16 10.03 0.00 50 50 77 87 SCB-60 13-2371 0.25 15.00 9.19 5.60 3.58 0.00 39 61 78 90 SCB-65 40D-7 0.67 40.20 7.97 3.25 4.72 0.00 59 41 75 84 SCB-70 13-792 0.66 39.60 34.92 13.95 20.97 0.00 60 40 74 84 SCB-75 13-764 0.71 42.60 39.65 14.31 25.33 0.00 64 36 74 83 SCB-80 13-549 0.68 40.80 11.92 5.68 6.25 0.00 52 48 75 86 SCB-85 13-550 0.89 53.40 45.77 1.65 44.12 0.00 96 4 74 75 SCB-90 13-561 0.52 31.20 16.03 5.36 10.69 0.00 67 33 74 82 SCB-95 13-550 0.49 29.40 14.35 0.38 13.90 0.00 97 3 74 75 SCB-100 13-571 0.52 31.20 66.92 21.35 45.65 0.00 68 32 74 82 Total 474.65 185.14 283.32 6.21 Grand Total 1841.17 696.03 971.18 173.99 62 38 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® Page 1 of 1 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 2.01-4.doc\022508 TABLE 2.01-4 FUTURE CONDITIONS AND HYDROLOGIC PARAMETERS Basin ID Structure ID Tc (hrs) Tc (min) Drainage Basin Area (ac) Total Impervious Area (ac) Total Pervious Area (ac) Total Pervious Ag. (ac) Pervious (%) Impervious (%) Pervious Composite RCN All Composite RCN CCB-05 D-OF-3 0.47 28.20 46.68 21.15 25.52 0.00 55 45 74 85 CCB-10 Outfall 1 0.75 45.00 134.37 66.71 67.66 0.00 50 50 75 86 CCB-15 06-462 0.32 19.20 15.97 5.94 10.03 0.00 63 37 74 83 CCB-20 06-602 0.89 53.40 27.78 11.55 16.22 0.00 58 42 74 84 Total 224.80 105.37 119.43 0.00 NBB-05 06-469 0.56 33.60 7.00 2.87 4.14 0.00 59 41 74 84 NBB-10 06-552 0.44 26.40 14.29 6.73 7.57 0.00 53 47 75 86 NBB-15 06-653 0.70 42.00 21.75 8.75 13.00 0.00 60 40 74 84 NBB-20 06-770 0.70 42.00 26.03 5.51 20.52 0.00 79 21 74 79 NBB-25 06-1062 0.39 23.40 7.08 3.61 3.48 0.00 49 51 74 86 NBB-30 06-688 0.34 20.40 29.72 18.54 11.18 0.00 38 62 75 89 NBB-35 06-843 0.30 18.00 3.98 3.04 0.94 0.00 24 76 75 92 NBB-40 06-846 0.09 5.40 6.08 5.02 1.06 0.00 17 83 74 94 NBB-45 06-847 0.08 4.80 4.25 4.03 0.22 0.00 5 95 74 97 NBB-50 06-1293.2 0.09 5.40 2.31 2.25 0.06 0.00 3 97 74 97 NBB-55 LP-5 0.30 18.00 18.43 8.63 9.80 0.00 53 47 75 86 Total 140.93 68.97 71.96 0.00 SBB-05 06-471 0.31 18.60 16.64 7.04 9.60 0.00 58 42 74 84 SBB-10 06-474 0.62 37.20 20.38 7.19 13.20 0.00 65 35 74 83 SBB-15 06-473 0.77 46.20 73.71 28.71 45.00 0.00 61 39 70 81 SBB-20 AEW-1 0.54 32.40 19.10 7.61 11.50 0.00 60 40 74 84 SBB-25A 13-420 0.71 42.60 29.91 11.09 18.82 0.00 63 37 74 83 SBB-25B 13-660 0.44 26.40 6.27 2.56 3.71 0.00 59 41 75 84 SBB-25C 13-454 0.38 22.80 4.43 2.48 1.95 0.00 44 56 75 88 SBB-25D 13-1190 0.29 17.40 18.21 14.36 3.85 0.00 21 79 78 95 SBB-25E AEW-36 0.08 5.00 5.72 2.56 3.17 0.00 55 45 79 92 SBB-25F AEW-37 0.16 9.60 6.62 3.81 2.81 0.00 42 58 78 93 SBB-30 13-457 0.19 11.40 21.87 12.62 9.25 0.00 42 58 74 88 SBB-35 13-460 0.33 19.80 4.34 2.40 1.94 0.00 45 55 75 88 SBB-40 AD-4 0.63 37.80 9.89 0.28 9.61 0.00 97 3 74 75 SBB-41 SBD 0.36 21.60 16.30 4.49 11.81 0.00 72 28 74 81 SBB-42 AD-3 0.13 7.80 6.93 4.78 2.14 0.00 31 69 74 91 SBB-45 13-1217 0.18 10.80 24.46 21.27 3.18 0.00 13 87 74 95 SBB-50 13-1221 0.13 7.80 23.81 19.15 4.67 0.00 20 80 75 93 SBB-55 AEW-15 0.44 26.40 26.46 16.80 9.66 0.00 36 64 74 89 SBB-60 PR-27 1.05 63.00 28.83 20.46 8.37 0.00 29 71 77 92 SBB-61 AEW-32 0.41 24.60 15.54 7.53 8.00 0.00 52 48 74 86 SBB-65 13-874 0.53 31.80 39.84 15.14 24.71 0.00 62 38 74 83 SBB-70 13-983 0.42 25.20 32.10 10.47 21.63 0.00 67 33 74 82 SBB-71 13-1033 0.35 21.00 12.80 4.77 8.03 0.00 63 37 74 83 SBB-75 AEW-22 0.49 29.40 44.54 24.78 19.76 0.00 44 56 75 88 SBB-76 AEW-19 0.68 40.80 38.46 20.80 17.66 0.00 46 54 75 87 SBB-80 2125-2175 0.49 29.40 8.24 3.88 4.37 0.00 53 47 74 85 SBB-85 13-1003/N312 0.39 23.40 32.55 16.86 15.70 0.00 48 52 75 87 SBB-90 2690 B. AV 0.15 9.00 21.72 14.08 7.64 0.00 35 65 77 91 SBB-95 13-4 0.68 40.80 34.19 17.05 17.14 0.00 50 50 75 87 SBB-100 2301-UA-2.1 0.08 5.00 0.94 0.52 0.43 0.00 45 55 79 90 SBB-105 2301-UA-1.1 0.22 13.20 2.59 0.35 2.24 0.00 87 13 74 77 SBB-110 2301-UA-3 0.20 12.00 1.53 0.45 1.08 0.00 71 29 75 82 SBB-115 AEW-25 0.36 21.60 25.17 13.50 11.67 0.00 46 54 76 88 SBB-120 2751-2 0.42 25.20 2.32 1.04 1.28 0.00 55 45 74 85 SBB-125 2751-4 0.08 5.00 1.01 1.00 0.01 0.00 1 99 74 98 SBB-130 2751-3 0.34 20.40 2.07 1.40 0.68 0.00 33 67 74 90 SBB-135 2980-1.5 0.08 5.00 10.44 5.31 5.13 0.00 49 51 74 86 SBB-140 AEW-26 0.43 25.80 28.12 17.72 10.40 0.00 37 63 76 90 SBB-141 AEW-26 0.42 25.20 29.64 19.14 10.50 0.00 35 65 75 90 SBB-145 2980-4 0.08 5.00 3.98 3.38 0.61 0.00 15 85 74 94 SBB-150 4000-94 0.21 12.60 1.77 0.63 1.13 0.00 64 36 74 83 SBB-155 2449-1.5 0.14 8.40 2.71 2.01 0.70 0.00 26 74 74 92 SBB-160 4000-93 0.08 5.00 0.89 0.32 0.57 0.00 64 36 74 83 SBB-165 4000-92 0.27 16.20 2.22 1.13 1.09 0.00 49 51 74 86 SBB-170 2449-1.3 0.21 12.60 5.02 3.56 1.45 0.00 29 71 75 91 SBB-175 AEW-28 0.94 56.40 44.87 19.09 24.60 1.18 57 43 76 86 SBB-176 AEW-40 0.73 43.80 25.08 14.63 10.45 0.00 42 58 75 88 SBB-180 2531-1 0.13 7.80 4.90 2.39 2.50 0.01 51 49 75 86 SBB-185 2531-3 0.46 27.60 5.18 0.94 4.22 0.02 82 18 74 78 SBB-190 MOON 0.44 26.50 156.49 77.55 74.48 4.45 50 50 75 86 Total 1000.79 511.04 484.10 5.66 SCB-A PR-1 0.08 5.00 1.03 0.71 0.32 0.00 31 69 79 92 SCB-B PR-2 0.08 5.00 2.52 1.74 0.78 0.00 31 69 79 92 SCB-C PR-3 0.08 5.00 2.49 1.72 0.77 0.00 31 69 79 92 SCB-D PR-4 0.08 5.00 1.56 1.08 0.48 0.00 31 69 79 92 SCB-E PR-6 0.08 5.00 4.09 2.82 1.27 0.00 31 69 79 92 SCB-05 16-430 0.29 17.40 6.18 2.89 3.29 0.00 53 47 74 85 SCB-10 16-428 0.53 31.80 30.35 15.20 15.15 0.00 50 50 74 86 SCB-15 06-640 0.40 24.00 24.37 12.35 12.02 0.00 49 51 74 86 SCB-20 06-678 0.73 43.80 18.95 8.81 10.14 0.00 54 46 74 85 SCB-25 06-1355 0.11 6.60 10.29 7.31 2.98 0.00 29 71 78 92 SCB-30 222 0.83 49.80 18.92 12.02 6.85 0.05 36 64 75 90 SCB-35 215 0.79 47.40 48.62 36.16 12.46 0.00 26 74 75 92 SCB-40 PR-8 1.07 64.20 9.30 5.40 3.91 0.00 42 58 75 88 SCB-45 PR-11 0.14 8.40 2.04 1.12 0.91 0.00 45 55 79 90 SCB-50 WP-1 0.21 12.60 31.38 19.85 11.52 0.00 37 63 75 89 SCB-55 PR-14 0.30 18.00 20.19 13.05 7.14 0.00 35 65 77 90 SCB-60 PR-19 0.25 15.00 9.19 6.61 2.58 0.00 28 72 77 92 SCB-65 PR-22 0.67 40.20 7.97 5.28 2.69 0.00 34 66 75 90 SCB-70 13-792 0.66 39.60 34.92 23.06 11.86 0.00 34 66 74 90 SCB-75 13-764 0.71 42.60 39.65 14.31 25.33 0.00 64 36 74 83 SCB-80 13-549 0.68 40.80 11.92 6.03 5.89 0.00 49 51 75 86 SCB-85 WNWPOND 0.89 53.40 45.77 1.65 44.12 0.00 96 4 74 75 SCB-90 13-562 0.52 31.20 16.03 5.28 10.76 0.00 67 33 74 82 SCB-95 WNWPOND 0.49 29.40 14.35 0.37 13.98 0.00 97 3 74 75 SCB-100 13-571 0.52 31.20 66.92 21.01 45.91 0.00 69 31 74 82 Total 478.99 225.82 253.12 0.05 Grand Total 1845.51 911.19 928.61 5.71 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-5 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 Return Frequency Elevation (ft) Summer Target Maximum 747.55 10-year 747.56 50-year 748.26 100-year 748.36 500-year 748.96 Table 2.03-1 Regulatory Still Water Levels–Lake Winnebago (National Geodetic Vertical Datum of 1929–NGVD 1929) Return Frequency Campbell Creek Elevation (ft) Sawyer Creek Elevation (ft) 10-year 748.65 748.80 50-year 749.20 749.45 100-year 749.55 749.65 500-year 750.10 750.20 Table 2.03-2 Regulatory Levels–Fox River Confluence with Campbell Creek and Sawyer Creek (NGVD 1929) Storm Duration (hours) Frequency (yr) 1 2 3 6 12 18 24 1 0.92 1.14 1.25 1.47 1.71 1.84 1.96 2 1.13 1.39 1.54 1.80 2.09 2.26 2.40 5 1.41 1.74 1.92 2.25 2.61 2.82 3.00 10 1.67 2.06 2.28 2.67 3.10 3.35 3.56 25 2.10 2.59 2.85 3.35 3.88 4.19 4.46 50 2.50 3.09 3.40 3.99 4.63 5.00 5.32 100 2.98 3.68 4.06 4.76 5.52 5.97 6.35 Table 2.02-1 Design Storm Rainfall Depths, Bulletin 71 2.03 FOX RIVER AND LAKE WINNEBAGO REGULATORY LEVELS A Flood Insurance Study was completed for the Fox River and Lake Winnebago on June 6, 1995, by Carl Crane, Inc. (now Foth and Van Dyke). This study has been updated as the Flood Insurance Study, Winnebago County, Wisconsin, and Incorporated Areas, Federal Emergency Management Agency (FEMA), March 17, 2003. The regulatory highwater elevations (still water level) for Lake Winnebago based on the updated study are shown in Table 2.03-1. Copies of the flood profiles for the Fox River and Sawyer Creek are included as Figure 2.03-1, and Figure 2.03-2 in the May 2006 report. The regulatory elevations at the confluence of Campbell Creek/Fox River and Sawyer Creek/Fox River are shown in Table 2.03-2. 2.04 GAUGING STATIONS ON FOX RIVER AND LAKE WINNEBAGO There is a rainfall gauging station (United States Geological Survey (USGS) 04082400) located on the Fox River and 400 feet downstream of the USH 45 (Main Street) bridge in Oshkosh. In addition, there is a stage gage (USGS 04082500) on Lake Winnebago located at 905 Bay Shore Drive, 800 feet east of the mouth of the upper Fox River. Both of these gages are operated in cooperation with United States Army Corps of Engineers (USACE) and information regarding them can be found at the following two Web sites. http://waterdata.usgs.gov/wi/nwis/uv/?site_no=04082400&PARAmeter_cd=00045 http://waterdata.usgs.gov/wi/nwis/dv/?site_no=04082500&PARAmeter_cd=00065 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-6 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022608 Date Elevation (ft) Early Spring–Starting at Ice Break-up Fill To Elevation Range By May 1 2.4 to 2.7 (746.95 to 747.25) Early Summer–By June 1 2.7 to 3.0 (747.25 to 747.55) Mid Summer–by July 1 Minimum of 3.0 (747.55) Winter Drawdown 2.5 (747.05) from mid- Oct. to early Jan. 1.62 (745.77) by end February Notes: 1. Navigation season is considered Ice Breakup to Oct. 10. 2. Stage = FT above Oshkosh Datum (0 = 744.35 IGLD 85) according to USACE Web site. 3. Conversion from stage to NGVD29 = +744.55 per correspondence from City 4. Record Low = 0.33 = 744.88 (March 9). 5. Record High = 3.81 = 748.36 (July 10). Table 2.05-1 Lake Winnebago 2004-2006 Regulation Strategy 2.05 LAKE WINNEBAGO 2004-2005 REGULATION STRATEGY According to the following two USACE Web sites, the following information relative to the regulation of Lake Winnebago dated November 24, 2004, is presented. All elevations from this Web site were reported as being in City of Oshkosh datum. (http://www.lre.usace.army.mil/_kd/Items/actions.cfm?action=Show&item_id=4144&destination=ShowItem) (http://www.lre.usace.army.mil/_kd/Items/actions.cfm?action=Show&item_id=4207&destination=ShowItem) Table 2.05-1 lists Lake Winnebago regulatory elevations as documented by the USACE. This table uses a conversion factor of adding 744.55 to the gage height reading in feet to convert the gage reading to NGVD 1929 datum. This differs from the USACE conversion stated on the Web site but matches information received by the USACE via e-mail for a similar project in the City. 2.06 RAINFALL GAGES IN OSHKOSH The City of Oshkosh operates a tipping bucket rain gauge at the wastewater treatment plant (WWTP). We have obtained data regarding a June 11, 2004, rainfall event from the City to help in calibrating our model. The format of this rainfall data is in daily rainfall totals. The National Weather Service maintains a climatological data station at the Oshkosh Wittman Regional Airport. Hourly precipitation data was available for the June 11, 2004, storm event and the month preceding it. The USGS in cooperation with USACE has a precipitation gage on the Fox River in Oshkosh (USGS 04082400). We have obtained data regarding the June 10/11, 2004, rainfall event from the USACE. The total precipitation for June 10 and June 11, 2004 according to this gage was 3.97 inches of rainfall. For the period from 1 P.M. on June 10, 2004 to 12 P.M. on June 11, 2004 (the bulk of the June 10/11, 2004, rainfall event), this gage showed 3.92 inches of rainfall. We used the rainfall data from the USACE gage in our modeling of the June 10/11, 2004 storm. The rainfall totals from the Oshkosh WWTP gage and the National Weather Service gage at the Oshkosh Airport closely match the USACE data used in our model. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0.55 0.6 0.65 Ra i n f a l l ( I n c h e s ) 1: 0 0 P M 2: 0 0 P M 3: 0 0 P M 4: 0 0 P M 5: 0 0 P M 6: 0 0 P M 7: 0 0 P M 8: 0 0 P M 9: 0 0 P M 10 : 0 0 P M 11 : 0 0 P M 12 : 0 0 A M 1: 0 0 A M 2: 0 0 A M 3: 0 0 A M 4: 0 0 A M 5: 0 0 A M 6: 0 0 A M 7: 0 0 A M 8: 0 0 A M 9: 0 0 A M 10 : 0 0 A M 11 : 0 0 A M 12 : 0 0 P M Hours June 10 & 11, 2004 Storm Event USACE Gage in Oshkosh, WI Figure 2.06-1 June 10/11, 2004, Storm Event–USACE Gauge in Oshkosh, Wisconsin The June 10/11, 2004 storm event using USACE gage data is illustrated in Figure 2.06-1 and corresponds to about a 15-year, 18-hour storm event (cumulative 3.61 inches of rainfall) or about a 16-year, 24-hour event (cumulative 3.92 inches of rainfall) when comparing to Huff rainfall amounts and durations and starting the rainfall event at 1 P.M. on June 10, 2004. If the storm is considered to start at 7 P.M. on June 10 and continue through 9 A.M. on June 11, then the storm would be considered about a 20-year, 12-hour storm (cumulative 3.63 inches of rainfall) when comparing to Huff rainfall amounts and durations. 2.07 LOCATIONS OF EXISTING FLOODING PROBLEMS A. Apparent Contributions to Flooding Flooding in the City of Oshkosh occurs most commonly after short, intense thunderstorm events in the spring and summer months. In general, flooding appears to be because of one, or a combination, of several factors: 1. Lack of positive drainage: The flat surface topography in certain areas of the City discourages positive drainage of stormwater. In certain cases, the stormwater drainage is in a saw-tooth pattern whereby storm sewer handles smaller storm flows but numerous depressional areas are created to accomplish surface drainage. As a result, stormwater accumulates in the depressional areas with larger storm events, causing flooding of adjacent land. An example of this is along Reichow Street and Crystal Springs Avenue. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-8 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 2. Insufficient storage capacity: The capacity of depressional areas at many locations is exceeded by the volume of stormwater runoff discharging to the depressional area. This causes water levels in the depressional area to back up onto adjacent streets or yards. Previous flooding at the intersection of E. Murdock Avenue and Harrison Street in the Anchorage Basin is an example of this condition. 3. Insufficient outlet capacity: Constructed drainage structures have insufficient capacities to convey the peak discharge from intense storm events. Backups upstream of the culvert beneath South Washburn Street south of Dickinson Avenue may be an example of this condition. The culvert downstream of Landmark Plaza is also an example of insufficient outlet capacity. 4. Insufficient inlet capacity: Drainage from streets and other surface areas may be restricted by the limited capacity of street or low point inlets at several locations in the Campbell Creek watershed including at the Landmark Plaza. 5. High lake/river/creek levels: High lake and river levels reduce the outlet capacity of the trunk storm sewer line located upstream of the Campbell Creek discharge at the Fox River as well as at the two outfalls on Sawyer Creek. 6. Drainage Basin Cross Connections: Cross connections allow water from another stormwater drainage basin or subbasin to enter into an adjacent basin, which may overwhelm drainage facilities in the adjacent basin. The drainage basin cross connections under USH 41 in the Campbell Creek drainage basin appear to have been the natural/original route of stormwater conveyance. In this report, we refer to these as cross connections or diversions simply because stormwater can go two directions at these locations. 7. First Floor Elevation Built Too Low With Insufficient Overflow Route: This appears to be the case at Landmark Plaza. Historically, flooding has caused extensive property damage in the Campbell Creek watershed. In addition, nuisance flooding involving water accumulation in yards and streets is common. B. Flooding Locations Seven locations of recurrent flooding have been identified in the Campbell Creek watershed based on discussions with City staff and shown on the City of Oshkosh’s Stormwater Management Projects Map which identifies Drainage Problem Areas. In addition, Map 2 of the December 1994 stormwater plan identifies a number of residences in the watershed that reported flooding during a June 1993 storm event. These locations are identified in Figure 2.07-1 and described in Table 2.07-1 PROBLEM AREAS NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 2 . 0 7 - 1 1- 382 . 0 3 0 !( !( !( !( !( !( !( !( Taft Ave Kn a p p S t W. So u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S Ko e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma City of Oshkosh Bank Full Within BanksWithin Banks US R o u t e 4 1 State R o a d 4 4 State R o a d 9 1 Un i v e r s a l S t . Oa k w o o d R d . W 20th Ave. Marico p a D r . Dickinson Ave. Cu m b e r l a n d T r l . S W a s h b u r n S t . Crystal Springs Ave. Mo r e l a n d S t . Re i c h o w S t . W 9th Ave. Ma s o n S t . W 4th Ave. Witzel Ave. N S a w y e r S t . Jo s s l y n S t . N W e s t f i e l d S t . SAW Y E R C R E E K 42" RCP IE = 775.25 3' x 4.5' RCP Box IE = 762.54 6/11/04 High Water Mark 748.43 (per city) 6/10/04 Fox River Gage ELEV. = 747.66 6/11/04 High Water Mark 762.75 6/11/04 High Water Mark 756.61 (per city) Diversion PT 1 High PT = 776.35 SAWYER CREEK 30" RCP IE = 760.27 36" RCP IE = 769.53 SCB-E SCB-D SCB-C SCB-B SCB-A SBB-25.F SBB-25.E SBB-25.C SBB-25.B SBB-25.A SBB-61 SBB-71 SBB-76 SBB-140 SBB-176 SCB-95 SCB-90 SBB-85 SBB-60 SBB-70 SCB-75 SBB-75 SBB-80 SBB-95 SBB-90 SBB-100 SBB- 105 SBB-115 SBB- 110 SBB-120 SBB-135 SBB-130SBB-125 SBB-141 SBB- 145 SBB-150 SBB-160 SBB-165 SBB- 170 SBB-155 SBB-175 SBB-180 SBB-185 SBB-190 SBB- 42 SBB-41 NBB-45 SCB-35 SCB-40 NBB-50 SCB-85 SCB-15 SCB-10 SCB-05 SCB-20 SCB-25 CCB-05 CCB-10 CCB-15 CCB-20 NBB-35 NBB-40 NBB-55 NBB-25 NBB-20 NBB- 05NBB-10 NBB-15 NBB-30 SCB-30 SCB-45SCB-50 SBB-05 SBB-10 SBB-20 SBB-15 SBB-25.D SBB-30 SBB-35 SBB-40 SBB-45 SCB-55 SCB-60 SCB-65 SCB-70 SCB-100 SCB-80 SBB-50 SBB-55 SBB-65 8 7 4 6 5 1 3 2 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 2 . 07 - 1 - Pr o b l em Ar e a s . m x d 0 1,500 3,000750 Feet ³ Legend Municipal Boundary Landmark Plaza Navigable Stream June 11, 2004 Flooding June 1993 Reported Flooding Drainage Basin Boundary Sub Drainage Basin Boundary Wetlands 100-year Floodplain Storm Manhole Storm Sewer Culvert !(Drainage Problem Areas2 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 2–Contributing Watershed Characteristics Prepared by Strand Associates, Inc.® 2-9 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S2.doc\022508 ID Location Apparent Causes (See Legend) Type of Damage 1 Landmark Plaza a, b, c, d, e, f, g 1, 2, 4 2 Universal Street near STH 44 b, c 1 3 S. Washburn Street near Dickinson Avenue b, c 1, 4 4 Reichow Street and Crystal Springs Avenue Area a, c, d 1, 2, 4 5 School yard northwest of Mason St./West 9th Ave a,b,c,d 1,2,4 6 Street flooding upstream of Campbell Creek discharge a, b, c, d, e 1, 2, 4 7 Various Residences a, c, d 1, 2, 4 8 Badger Ave./Universal St. Intersection a, c, d 1, 4 9 Allerton Drive c, d, h 1, 2, 3, 4 Legend: Apparent Contribution to Flooding: Type of Damage: a. Lack of positive drainage route. 1. Street/Yard/Field Flooding b. Insufficient storage capacity. 2. Property/Structural Damage c. Insufficient outlet capacity. 3. Erosion d. Insufficient inlet capacity. 4. Safety Issue e. High lake, river, creek levels f. Drainage basin cross connections g. First Floor Elevation Built Too Low With Insufficient Overflow Route h. Breach in railroad embankment. Table 2.07-1 Locations of Existing Flooding SECTION 3 ENGINEERING ANALYSIS City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® 3-1 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S3.doc\022508 3.01 HYDROLOGIC ANALYSIS A. Purpose of Evaluation A watershed model was developed for the Campbell Creek drainage area. This model estimated peak discharges and stormwater runoff volumes from individual drainage subbasins. This data was used to size stormwater detention and conveyance facilities and estimate potential flood depths at critical watershed locations. Stormwater modeling was completed for the following scenarios: 1. Existing conditions peak discharge and stormwater runoff volumes. This analysis estimated where the existing capacities of storm sewer facilities were exceeded and included incorporation of the existing Wal-Mart, golf course, and Armory detention basins into the models. Also, numerous existing detention basins southeast of the Dickinson/S. Washburn Street intersection have been added to the models. 2. June 10/11, 2004, storm event peak discharges and stormwater runoff volumes. This analysis was run to determine stormwater characteristics that occurred with this storm. 3. Future conditions peak discharges and stormwater runoff volumes. Estimating peak discharges and runoff volumes to areas of known flooding allowed potential drainage projects to be developed and properly sized to accommodate future peak discharges. All models incorporated the Alternative 7 improvements the original report at the Armory site (one of two layouts) and the Tippler Junior High and Landmark Plaza sites. B. Methodology For this project, hydrologic models were developed using the RUNOFF module of the computer model XP-SWMMTM Version 9.51. XP-SWMMTM is a proprietary model based on the EPA-developed Stormwater Management Model (SWMMTM). XP-SWMMTM estimates peak stormwater discharges and volumes based on mathematical input parameters representing precipitation depth and time distribution, drainage area, land use, and time of concentration for each subbasin. Primary input parameters include the drainage area, runoff curve number (RCN), and time of concentration (Tc). The RCN considers land use and percentage of impervious area, soil type, and saturation conditions to impact the volume of stormwater runoff generated for a given rainfall depth. The Tc is the time it takes for stormwater to travel from the most hydrologically remote point in the watershed to the subbasin outlet. Parameters representing rainfall depth and distribution and watershed storage are also included in the model. Based on user input coding, XP-SWMMTM generates hydrographs for each subbasin, routes them through storage areas, and combines them at appropriate locations. The result is a rainfall-runoff model of the storm event of interest. For this project, hydrographs were generated for the 1-, 2-, 5-, 10-, 25-, 50- and 100-year storms under existing land use conditions. The Huff rainfall (1st Quartile for storms of duration 6 hours and less and 2nd Quartile for storms of duration of City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® 3-2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S3.doc\022508 6.1- to 12-hour) distribution was analyzed for this project. A sensitivity analysis was performed in the original report to identify the storm duration resulting in the highest probable peak discharges at various watershed locations (typically referred to as the “critical duration”). Our analysis concluded that the critical storm duration creating the greatest peak discharges watershedwide under existing land use conditions is a 2-hour storm. It was further concluded that the critical duration is a 12-hour storm at Landmark Plaza in terms of creating the highest flooding volumes because of the long retention times/flooding upstream of Landmark Plaza under existing land use conditions. We have thus analyzed each of our alternatives for the 10-year and 100-year storm events of 2-hour and 12-hour duration under future land use conditions. C. Modeling Results Table 3.01-1 includes summaries of peak discharges calculated by XP-SWMMTM for each subbasin in the Campbell Creek watershed for existing land use conditions for a 2-hour duration storm. Peak discharges for the June 10/11, 2004 storm are arrived at by using RCNs that are 20 percent higher than existing land use conditions to account for the substantial rainfall in the month preceding the June 10/11, 2004, storm event. Table 3.01-2 includes summaries of peak discharges calculated by XP-SWMMTM for each subbasin in the Campbell Creek watershed for future land use conditions for a 2-hour duration storm. As discussed in Section 2, all new development over 1 acre within the watershed will need to provide detention that will assist in providing peak flow reduction in the watershed under future conditions. Our models do not include this future detention. However, in the alternatives analysis, we provide a detention basin in subbasin SBB-190 where there is substantial agricultural land that is planned for future development. 3.02 HYDRAULIC ANALYSIS A. Methodology The Extended Transport (EXTRAN) module of the XP-SWMMTM computer model was used to calculate the hydraulic capacity of the existing storm sewer system under existing conditions. Figure 3.02-1 (located in the pocket folder of the original report dated May 2006) shows a schematic of the storm sewer network as modeled. EXTRAN is a dynamic flow routing model that routes inflow hydrographs through an open channel and/or closed conduit system, computing the time history of flows and heads throughout the system. Input to EXTRAN includes the following: 1. The physical geometry of the storm sewer system, including culvert sizes and shapes, ground and invert elevations, and culvert connectivity information. For this project, physical information regarding the culvert system was obtained from the City of Oshkosh’s storm sewer GIS layer along with field survey information. 2. Data regarding special hydraulic structures in the system including weirs, check valves, and storage junctions. 3. Roughness coefficients for existing and proposed conduits. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 1 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.01-1.doc\121707 TABLE 3.01-1 EXISTING CONDITIONS PEAK DISCHARGE RATES Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Basin ID Structure ID 1-yr 2-yr 5-yr 10-yr 25-yr 50-yr 100-yr 6/11/2004 CCB-05 D-OF-3 9 14 24 33 51 69 92 27 CCB-10 Outfall 1 26 41 65 90 134 180 236 78 CCB-15 06-462 3 4 7 11 17 23 32 9 CCB-20 06-602 4 6 11 15 23 31 41 16 NBB-05 06-469 1 2 3 4 7 9 12 4 NBB-10 06-552 3 5 8 11 17 23 30 8 NBB-15 06-653 3 5 9 12 19 26 35 12 NBB-20 06-770 2 4 7 11 17 25 34 14 NBB-25 06-1062 2 3 4 6 9 12 16 4 NBB-30 06-688 9 14 22 30 44 58 75 18 NBB-35 06-843 2 3 4 6 8 10 13 2 NBB-40 06-846 4 6 9 12 17 23 29 4 NBB-45 06-847 5 7 10 12 16 20 24 3 NBB-50 06-1293.2 3 4 5 7 9 11 13 1 NBB-55 LP-5 4 6 10 14 22 30 40 11 SBB-05 06-471 3 5 9 12 19 26 35 10 SBB-10 06-474 3 5 8 11 17 24 32 12 SBB-15 06-473 4 9 17 26 43 62 86 37 SBB-20 AEW-1 3 5 8 12 18 25 34 11 SBB-25A 13-420 15 24 38 51 76 101 132 17 SBB-25B 13-660 1 2 3 4 7 9 12 4 SBB-25C 13-454 1 2 3 4 6 8 11 3 SBB-25D 13-1190 11 16 22 28 39 49 62 11 SBB-25E AEW-36 2 3 5 6 9 13 18 3 SBB-25F AEW-37 3 4 6 8 12 15 21 4 SBB-30 13-457 7 11 17 24 35 45 60 13 SBB-35 13-460 1 2 3 4 6 8 11 3 SBB-40 AD-4 0 1 2 3 5 8 11 5 SBB-41 AP-1 2 3 6 9 14 20 28 9 SBB-42 AD-3 1 2 4 5 8 11 15 4 SBB-45 13-1217 16 22 31 40 57 74 95 15 SBB-50 13-1221 15 21 31 41 60 79 101 14 SBB-55 AEW-15 7 11 18 24 35 47 61 16 SBB-60 STR-10 5 8 13 18 26 34 45 17 SBB-61 AEW-32 3 5 8 11 17 23 31 9 SBB-65 13-874 6 10 17 24 38 52 69 23 SBB-70 13-983 4 7 13 19 30 42 57 18 SBB-71 13-1033 2 4 6 9 14 19 25 7 SBB-75 AEW-22 6 11 19 27 42 58 78 26 SBB-76 AEW-19 6 10 16 22 35 47 63 22 SBB-80 2125-2175 1 1 2 4 6 9 12 5 SBB-85 13-1003 7 11 18 25 38 52 68 19 SBB-90 2690 B. AV 9 13 19 26 37 50 67 13 SBB-95 13-4 3 6 11 16 25 35 48 19 SBB-100 2301-UA-2.1 0 1 1 1 2 3 3 1 SBB-105 2301-UA-1.1 0 0 1 1 2 3 4 1 SBB-110 2301-UA-3 0 0 1 1 2 2 3 1 SBB-115 AEW-25 6 9 15 21 31 42 56 15 SBB-120 2751-2 0 1 1 2 3 4 5 1 SBB-125 2751-4 2 2 3 3 4 5 6 1 SBB-130 2751-3 1 1 1 2 3 4 5 1 SBB-135 2980-1.5 1 2 4 6 10 14 19 6 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 2 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.01-1.doc\121707 Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Max Flow (cfs) Basin ID Structure ID 1-yr 2-yr 5-yr 10-yr 25-yr 50-yr 100-yr 6/11/2004 SBB-140 AEW-26 7 13 22 33 52 73 100 33 SBB-145 2980-4 3 4 6 8 12 15 19 2 SBB-150 4000-94 0 1 1 1 2 3 4 1 SBB-155 2449-1.5 1 2 3 3 5 7 9 2 SBB-160 4000-93 0 0 0 1 1 1 2 1 SBB-165 4000-92 1 1 1 2 3 4 5 1 SBB-170 2449-1.3 0 1 2 3 4 6 9 3 SBB-175 AEW-28 6 10 16 23 35 48 64 27 SBB-176 AEW-40 3 5 8 12 19 27 36 14 SBB-180 2531-1 1 2 4 5 7 10 13 3 SBB-185 2531-3 0 1 1 2 4 5 7 3 SBB-190 44D-9 25 41 69 98 152 208 279 97 SCB-05 16-430 1 2 4 5 8 11 14 4 SCB-10 16-428 6 10 16 23 34 46 60 18 SCB-15 06-640 6 9 14 20 30 40 53 14 SCB-20 06-678 3 5 8 12 18 24 32 11 SCB-25 06-1355 6 8 12 16 24 34 46 8 SCB-30 16-647 3 5 8 11 17 23 31 12 SCB-35 06-773 10 16 25 35 52 69 90 30 SCB-40 40D-19 2 3 4 6 8 11 14 5 SCB-45 40D-17 1 1 1 2 3 4 5 1 SCB-50 WP-1 12 18 27 36 52 69 89 19 SCB-55 40D-12 6 9 14 20 29 38 50 12 SCB-60 13-2371 4 6 8 11 16 20 26 6 SCB-65 40D-7 1 2 3 5 7 10 14 5 SCB-70 13-792 5 9 14 20 31 43 57 20 SCB-75 13-764 5 9 15 21 33 45 61 22 SCB-80 13-549 2 4 6 8 12 16 22 7 SCB-85 13-550 2 5 10 16 27 40 58 31 SCB-90 13-561 2 4 6 9 14 20 27 9 SCB-100 13-571 8 14 25 36 58 81 110 38 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 1 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.01-2.doc\022608 TABLE 3.01-2 FUTURE CONDITIONS PEAK DISCHARGE RATES (2 HOUR DURATION) Max Flow (cfs) Basin ID Node 1-yr 2-yr 5-yr 10-yr 25-yr 50-yr 100-yr CCB-05 D-DF-3 9 14 24 33 51 69 92 CCB-10 Outfall 1 27 42 67 91 136 182 238 CCB-15 06-462 3 4 7 11 17 23 32 CCB-20 06-602 4 6 11 15 23 31 41 NBB-05 06-469 1 2 3 4 7 9 12 NBB-10 06-552 3 5 8 11 17 23 30 NBB-15 06-653 3 5 9 12 19 26 35 NBB-20 06-770 2 4 7 11 17 25 34 NBB-25 06-1062 2 3 4 6 9 12 16 NBB-30 06-688 10 16 24 32 46 61 78 NBB-35 06-843 2 3 4 5 8 10 12 NBB-40 06-846 4 6 9 12 18 23 29 NBB-45 06-847 5 7 10 12 16 20 25 NBB-50 06-1293.2 3 4 5 7 9 11 13 NBB-55 LP-5 4 7 11 16 24 32 42 SBB-05 06-471 3 5 9 12 19 26 35 SBB-10 06-474 3 5 8 11 17 24 32 SBB-15 06-473 7 13 23 33 53 74 101 SBB-20 AEW-1 3 5 8 12 18 25 34 SBB-25A 13-420 4 7 11 16 25 35 46 SBB-25B 13-660 1 2 3 4 7 9 12 SBB-25C 13-454 1 2 3 4 6 8 11 SBB-25D 13-1190 11 16 22 28 39 49 62 SBB-25E AEW-36 2 3 5 6 9 13 18 SBB-25F AEW-37 3 4 6 8 12 15 21 SBB-30 13-457 7 11 17 24 35 45 60 SBB-35 13-460 1 2 3 4 6 8 11 SBB-40 AD-4 0 1 2 3 5 8 11 SBB-41 SBD 2 3 6 9 15 21 28 SBB-42 AD-3 3 5 7 9 14 19 25 SBB-45 13-1217 18 25 35 46 64 81 102 SBB-50 13-1221 15 21 32 42 61 80 103 SBB-55 AEW-15 9 13 20 27 39 51 65 SBB-60 PR-27 9 13 19 24 34 43 54 SBB-61 AEW-32 3 5 9 12 18 25 33 SBB-65 13-874 6 10 17 24 38 52 69 SBB-70 13-983 4 7 13 19 30 42 57 SBB-71 13-1033 2 3 6 9 13 19 25 SBB-75 AEW-22 12 18 28 39 57 76 98 SBB-76 AEW-19 9 14 21 29 43 57 74 SBB-80 2125-2175 2 3 4 6 9 12 16 SBB-85 13-1003 4 7 11 15 22 29 38 SBB-85 N312 4 6 10 14 20 27 35 SBB-90 2690 B. AV 10 15 22 29 41 56 74 SBB-95 13-4 7 11 18 24 36 48 63 SBB-100 2301-UA-2.1 0 1 1 1 2 3 3 SBB-105 2301-UA-1.1 0 0 1 1 2 3 4 SBB-110 2301-UA-3 0 0 1 1 2 2 3 SBB-115 AEW-25 7 11 18 24 35 47 61 SBB-120 2751-2 0 1 1 2 3 4 5 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 2 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.01-2.doc\022608 Max Flow (cfs) Basin ID Node 1-yr 2-yr 5-yr 10-yr 25-yr 50-yr 100-yr SBB-125 2751-4 1 2 3 3 4 5 6 SBB-130 2751-3 1 1 2 2 3 4 6 SBB-135 2980-1.5 3 5 7 10 15 21 30 SBB-140/ SBB-141 AEW-26 21 30 46 61 88 114 146 SBB-145 2980-4 3 4 7 9 12 16 20 SBB-150 4000-94 0 1 1 1 2 3 4 SBB-155 2449-1.5 1 2 3 4 6 8 10 SBB-160 4000-93 0 0 0 1 1 1 2 SBB-165 4000-92 1 1 1 2 3 4 5 SBB-170 2449-1.3 2 4 5 7 9 12 16 SBB-175 AEW-28 7 12 19 26 39 52 69 SBB-176 AEW-40 6 10 15 20 29 38 49 SBB-180 2531-1 1 2 4 5 7 10 13 SBB-185 2531-3 0 1 1 2 4 5 7 SBB-190 Moon 37 58 93 128 192 258 339 SCB-A PR-1 1 1 1 2 3 3 4 SCB-B PR-2 1 2 3 4 6 8 11 SCB-C PR-3 1 2 3 4 6 8 11 SCB-D PR-4 1 1 2 3 4 5 7 SCB-E PR-6 2 3 5 7 10 14 18 SCB-05 16-430 1 2 4 5 8 11 14 SCB-10 16-428 6 10 16 23 34 46 60 SCB-15 06-640 6 9 14 20 30 40 53 SCB-20 06-678 3 5 8 12 18 24 32 SCB-25 06-1355 6 8 12 17 25 33 43 SCB-30 222 5 8 12 15 22 29 37 SCB-35 215 18 25 37 47 66 85 107 SCB-40 PR-8 2 3 5 6 9 12 15 SCB-45 PR-11 1 1 2 2 4 5 7 SCB-50 WMP-1 12 18 28 37 53 69 91 SCB-55 PR-14 9 12 19 24 35 45 58 SCB-60 PR-19 5 7 10 13 18 23 29 SCB-65 PR-22 3 4 6 7 10 14 17 SCB-70 13-792 11 16 24 32 45 59 76 SCB-75 13-764 5 9 15 21 33 45 61 SCB-80 13-549 3 4 6 9 13 17 22 SCB-85/ SCB-95 WNWPOND 2 5 10 16 27 40 58 SCB-90 13-562 2 4 6 9 14 20 27 SCB-100 13-571 8 14 25 36 57 80 108 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® 3-3 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S3.doc\022508 Return Frequency Elevation (ft) 6/11/04 WSEL 750.49 1-year 747.55 2-year 747.55 5-year 748.78 10-year 749.57 25-year 750.49 50-year 751.04 100-year 751.04 Table 3.02-1 Boundary Conditions at Sawyer Creek/Westfield Outfall (NGVD 1929) Return Frequency Elevation (ft) 6/11/04 WSEL 754.33 1-year 747.55 2-year 747.55 5-year 751.06 10-year 752.55 25-year 754.33 50-year 755.37 100-year 755.37 Table 3.02-2 Boundary Conditions at Sawyer Creek/Washburn Street Outfall (NGVD 1929) 4. Inflow hydrographs at critical nodes in the system. For this project, hydrographs were computed using the XP-SWMMTM RUNOFF module, as described in Section 3.01B. 5. Boundary conditions defining starting water surface elevations and other inlet and outlet conditions. For this project, the summer target maximum for Lake Winnebago is considered 747.55 NGVD 1929 datum. Critical components of this modeling effort are the “boundary conditions” used at the pipe discharge at Campbell Creek and the two pipe discharges at Sawyer Creek. “Boundary conditions” means the assumed elevation of the water surface at the discharge point of the storm sewer being modeled. The boundary conditions at the Campbell Creek outfall being used are the Lake Winnebago pool elevations reported on the USACE gage. The gage elevation or summer target maximum is always used in our model as the boundary condition at the Campbell Creek outfall because of its proximity to the gage. The Lake Winnebago pool elevation backwater effects (still water elevation) appear to extend up to the Sawyer Creek/Washburn Street outfall and possibly beyond as a relatively flat surface, so the summer target maximum elevations for the lake can be used as boundary conditions for the smaller storms in Sawyer Creek. The boundary conditions at Sawyer Creek/Westfield Drive outfall and Sawyer Creek/Washburn Street outfall are elevations arrived at by running the FIS HEC-2 model for Sawyer Creek starting with an elevation of 747.55 (summer target maximum) at the Fox River/Sawyer Creek confluence (see Tables 3.02-1 and 3.02-2). 6. Stage-storage-outflow data for impoundments in the watershed, including the golf course detention, Wal-Mart detention, and Armory detention. 7. Pump curve data for the analyzed stormwater pumping station. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® 3-4 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S3.doc\022508 Output information from the EXTRAN model includes the following: 1. Time histories of flows and depths through individual storm sewer facility reaches for various storm events. 2. Estimates of cumulative stormwater volumes overflowing the system at various locations for extreme storm events. B. Model Calibration Calibration of the model to reproduce the elevations and flooding volumes that were reported during the June 10/11, 2004, storm event was performed to compare modeled results with observed conditions. We calibrated the model to the elevation surveyed as the high water mark at Landmark Plaza (762.75). Using survey obtained on January 19, 2006, stage versus storage relationships were developed for the Landmark Plaza lands and the Tippler Junior High lands. This survey data is shown in Figure 3.02-2. Each of these two basins (designated Landmark Basin and Tippler Basin) were modeled as detention pond basins with overflow routes that represent what happens in these areas during large storm events. The model shows that during the June 10/11, 2004 storm event, the Landmark Plaza lands (including portions of Westfield Drive and surrounding residences) flood up to a peak elevation of 762.64, which equates to a peak storage volume of 15.57 acre-feet. This is also similar in elevation to the surveyed elevation (762.89) along Westfield Drive (in the cul-de-sac) that was indicated as a high water mark by a resident on Westfield Drive. The Tippler Junior High depressional area is modeled to pond to an elevation of 760.24 with peak storage volume of 10.45 acre-feet. In addition, two other calibration locations were established upstream of Landmark Plaza. These two locations are along South Washburn Street near Domino’s Pizza and at the intersection of Universal Street and Badger Street. At these two points, we were provided (by the City) with pictures of the flooding at these locations on June 11, 2004. We established the flooding elevation at each location based upon survey completed as part of this project (South Washburn Street near Domino’s Pizza = 775.30, Intersection of Universal Street and Badger Street = 818.93). The model shows that during the June 10/11, 2004 storm event, the area along South Washburn Street near Domino’s Pizza floods up to a peak elevation of 775.06. Likewise, the model shows that during the June 10/11, 2004 storm event, the intersection of Universal Street and Badger Street floods up to a peak elevation of 818.77. Modifications made to the model to arrive at this calibration include the following. 1. Change of Manning’s “n” value from 0.026 to 0.028 in the corrugated metal pipe storm sewers downstream of Landmark Plaza (from node P-06-841 to P-06-408.2) to account for likely increased roughness in this section of pipe because of age. According to City storm sewer system maps, this stretch of storm sewer was built between 1958 and 1970, with older sections being on the downstream end of this stretch. EX I S T I N G SU R V EY D A T A AT LA N D MAR K PL A Z A A N D T I P P L E R NORT H B R AN C H CA MP B EL L CRE EK S T O R MW A TE R S T U DY AD D E ND U M N O . 1 CI T Y OF O S H K O SH WI N N E B AG O C O U NT Y , W I S C O NS I N FIGURE 3.02-21-382.030 761 761 761 761 762 762 763 764765 76276 3 761 761 762 763 764 762 762 763 762 76 0 760 76 0 76 0 76 1 76 1 761 76 1 76 2 76 2 762 76 2 76076 176 2 76 3 763 76 3 76 4 764 76 2 76 3 759 759 762 763 764 765766 760 760 761 758 758 761 762 759 759 762 763 760 760 761 760 760 760760 761 761 761 759 759 760 760 761 / Overflow Elevation = 758.70 / Overflow Elevation = 760.00 / Overflow Elevation = 761.87 FFE=766.12 FFE=764.44 FFE=764.35 FFE=764.13 FFE=762.39 FFE=763.74 FFE=762.69 FFE=762.91 FFE=764.64 FFE=763.51 FFE=763.61 FFE=763.84 FFE=763.34 FFE=763.48 FFE=763.66 FFE=763.27 FFE=764.49 FFE=762.28 FFE=763.99 FFE=763.87 FFE=764.39 FFE=763.95 FFE=762.53 FFE=764.26 FFE=762.35 FFE=761.31 Node 06-1293.2 Node 06-847 Node 06-846 WITZEL AVE S E A G L E S T N K O E L L E R S T BISMARCK AVE US H W Y 4 1 S O U T H B O U N D US H W Y 4 1 N O R T H B O U N D S W E S T F I E L D S T S W A S H B U R N S T W 4TH AVE W 2ND AVE W 3RD AVE N E A G L E S T N M E A D O W S T LI L A C S T N W E S T F I E L D S T MO N T I C E L L O D R p v t S:\@SAI\351--400\382\030\Data\GIS\Report Figures\Figure 3.02-2 - Existing Survey Data.mxd 0 200 400100 Feet ³ Legend Existing Contour Survey ShotE Storm Sewer City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® 3-5 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S3.doc\022508 2. Increase of pervious area curve numbers by 20 percent to account for the substantial rainfall in the month preceding the June 10/11, 2004, storm event. The 20 percent increase in pervious area curve numbers increases the composite pervious area curve number from 74 (Antecedent Moisture Conduction II) up to 91. This closely approximates Antecedent Moisture Condition III. 3. Use of a starting water surface elevation at the Campbell Creek outfall recorded by the USACE gage on the Fox River (747.66) on June 10, 2004. Use of a starting water surface elevation of 750.49 at the Sawyer Creek/Westfield outfall and 754.33 at the Sawyer Creek/Washburn outfall, which are the 5-year stormwater surface elevations at these locations, arrived at from modeling Sawyer Creek in HEC-RAS using a starting water surface elevation of 747.66 at the Fox River. 4. Based on these results, we believe the model provides a reasonable representation of flooding that occurred at Landmark Plaza on June 10/11, 2004. 5. Based on these results, we also believe that the model provides a reasonable representation of stormwater storage and conveyance in the Campbell Creek watershed during the June 10/11, 2004 storm event. C. Design-Storm Evaluation Modeling of existing conditions shows that there are numerous areas with undersized stormwater conveyance facilities that frequently exceed their capacities and flood adjacent lands and streets. Table 3.02-3 lists the design capacity and physical characteristics of modeled links in the stormwater conveyance system. Modeling provided the following observations: 1. Modeling results indicate that the existing 36-inch x 58-inch CMP downstream from Landmark Plaza has limited conveyance capacity because of the high Manning’s “n” values, minimal or reverse slope, and shallow cover. The average slope is approximately 0.23 percent. This limited downstream capacity creates a “bottleneck” causing flows to surcharge and inundate upstream areas including Landmark Plaza and appears to be a major factor in the flooding occurring at the Landmark Plaza. Any measures to increase flow rates from Landmark Plaza must also include either improved downstream conveyance or detention to maintain the system capacity. The challenge to upsizing this portion of the storm sewer will be dealing with cover issues and utility conflicts. 2. It appears that the low elevation at which Landmark Plaza was built is a major contributing factor to the flooding problems that are presently occurring. This is evidenced by the fact that the first floor elevation of the eastern Landmark Plaza building (762.28) is only approximately 0.41 feet above the lowest overflow elevation of 761.87 (located on the east side of Westfield Drive) that would allow stormwater from the Landmark Basin to discharge into the Tippler Basin. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 1 of 7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.02-3.doc\121707 TABLE 3.02-3 STORM SYSTEM CHARACTERISTICS EXISTING CONDITIONS Name Diameter (ft) Shape Roughness Conduit Slope (%) Length (ft) Design Flow (cfs) D-13-1283 3.58 Special 0.026 -0.97 44 87 D-2449-1.2 4.00 Natural 0.100 0.18 467 102 D-2449-1.4 3.00 Natural 0.100 2.06 146 120 D-2980-1 2.74 Natural 0.050 0.32 165 45 D-2980-3 2.74 Natural 0.035 0.64 61 64 D-40D-1 3.10 Natural 0.100 0.40 276 114 D-40D-1.1 3.10 Natural 0.100 0.37 237 109 D-40D-10 7.77 Natural 0.100 0.27 172 439 D-40D-11 6.39 Natural 0.100 0.67 196 500 D-40D-12 5.29 Natural 0.100 0.14 181 185 D-40D-13 4.51 Natural 0.100 0.30 187 195 D-40D-14 4.51 Natural 0.100 0.50 196 148 D-40D-15 4.84 Natural 0.100 0.37 193 142 D-40D-16 4.84 Natural 0.100 0.18 131 134 D-40D-16.1 4.90 Natural 0.100 0.18 71 133 D-40D-17 4.90 Natural 0.100 0.48 46 143 D-40D-17.1 4.90 Natural 0.100 0.48 141 144 D-40D-18 5.06 Natural 0.100 0.38 176 148 D-40D-19 5.75 Natural 0.100 0.25 154 187 D-40D-2 3.36 Natural 0.100 0.77 191 178 D-40D-20 5.77 Natural 0.100 0.27 187 384 D-40D-21 6.12 Natural 0.100 1.02 76 749 D-40D-23 8.24 Natural 0.100 0.42 185 732 D-40D-24 4.39 Natural 0.100 0.53 206 156 D-40D-25 3.73 Natural 0.100 0.83 206 180 D-40D-26 2.88 Natural 0.100 0.77 230 104 D-40D-27 2.88 Natural 0.100 0.80 210 43 D-40D-28 4.42 Natural 0.100 1.97 206 206 D-40D-29 5.59 Natural 0.100 2.42 207 243 D-40D-3 3.31 Natural 0.100 0.19 186 59 D-40D-30 5.69 Natural 0.100 3.38 110 546 D-40D-31 4.46 Natural 0.100 1.93 64 231 D-40D-4 3.31 Natural 0.100 0.51 188 89 D-40D-5 3.45 Natural 0.100 0.33 173 51 D-40D-6 3.45 Natural 0.100 0.32 90 53 D-40D-6.1 3.45 Natural 0.100 0.34 113 54 D-40D-7 4.95 Natural 0.100 0.24 177 155 D-40D-8 4.95 Natural 0.100 0.74 166 295 D-40D-9 7.77 Natural 0.100 0.35 195 628 D-44D-1 7.80 Natural 0.100 0.00 43 89 D-44D-2 7.80 Natural 0.100 0.50 131 2749 D-44D-3 7.36 Natural 0.100 -0.79 23 3203 D-44D-4 6.66 Natural 0.100 -0.03 71 188 D-44D-5 7.99 Natural 0.100 -0.10 186 1938 D-44D-6 8.18 Natural 0.014 0.05 175 1371 D-44D-7 9.90 Natural 0.100 0.09 177 3279 D-44D-8 9.90 Natural 0.100 0.00 182 325 D-44D-9 10.56 Natural 0.100 0.21 203 6311 D-AD-1 7.56 Natural 0.075 1.12 209 803 D-AD-2 9.90 Natural 0.075 0.16 167 410 D-AD-3 5.00 Natural 0.075 0.17 237 75 D-AD-4 5.03 Natural 0.075 0.35 169 146 D-AD-5 5.12 Natural 0.075 0.46 200 162 D-AEW-11 3.08 Natural 0.100 0.11 185 23 D-AEW-12 7.85 Natural 0.100 0.10 186 310 D-AEW-17 5.73 Natural 0.100 1.05 205 328 D-AEW-19 4.81 Natural 0.100 -1.06 26 187 D-AEW-2 5.45 Natural 0.050 0.29 191 162 D-AEW-21 3.85 Natural 0.100 -0.74 94 153 D-AEW-23 5.78 Natural 0.100 0.84 71 397 D-AEW-25 7.14 Natural 0.100 -0.52 107 755 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 2 of 7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.02-3.doc\121707 Name Diameter (ft) Shape Roughness Conduit Slope (%) Length (ft) Design Flow (cfs) D-AEW-27 6.74 Natural 0.100 0.25 55 1327 D-AEW-31 5.66 Natural 0.100 -0.67 91 1150 D-AEW-32 2.82 Natural 0.100 0.10 302 6 D-AEW-35 1.59 Natural 0.100 0.11 126 5 D-AEW-37 3.00 Circular 0.016 0.60 219 42 D-AEW-5 2.78 Natural 0.100 0.81 206 113 D-AEW-7 4.79 Natural 0.100 0.16 201 102 D-AEW-9 8.51 Natural 0.100 0.35 152 703 D-DITCH 3.66 Natural 0.050 0.51 187 102 D-DK-1 1.59 Natural 0.100 0.57 124 10 D-DK-2 2.25 Natural 0.100 0.23 107 43 D-DK-3 1.98 Natural 0.100 0.42 170 18 D-DK-4N 1.77 Natural 0.100 0.61 119 20 D-DK-4S 1.77 Natural 0.100 0.22 147 16 D-DK-5 2.19 Natural 0.100 0.43 167 51 D-D-OF-1 5.25 Natural 0.035 0.16 199 255 D-D-OF-2 5.25 Natural 0.035 0.15 190 223 D-D-OF-3 5.01 Natural 0.035 -1.16 133 773 D-LP-2 2.71 Natural 0.035 0.40 184 77 D-LP-3 3.47 Natural 0.035 0.38 245 108 D-LP-4 3.78 Natural 0.100 -0.14 207 37 D-LP-5 3.78 Natural 0.035 0.86 174 490 D-LP-6 2.50 Natural 0.015 3.66 16 284 D-RR-1 4.92 Natural 0.100 1.09 128 150 D-RR-10 3.85 Natural 0.100 0.22 197 84 D-RR-11 5.03 Natural 0.100 0.34 134 156 D-RR-12 3.70 Natural 0.100 0.62 179 114 D-RR-13 3.70 Natural 0.100 0.26 203 76 D-RR-14 5.54 Natural 0.100 0.47 197 263 D-RR-15 5.10 Natural 0.100 0.30 90 126 D-RR-16 6.48 Natural 0.100 0.28 174 185 D-RR-17 7.13 Natural 0.100 0.43 200 211 D-RR-18 6.86 Natural 0.100 0.22 208 189 D-RR-19 6.86 Natural 0.100 0.50 213 375 D-RR-2 4.85 Natural 0.100 0.75 152 191 D-RR-20 7.55 Natural 0.100 0.17 222 176 D-RR-3 4.85 Natural 0.100 0.35 180 86 D-RR-4 4.56 Natural 0.100 0.35 198 107 D-RR-5 4.51 Natural 0.100 0.25 204 118 D-RR-6 4.51 Natural 0.100 0.26 195 174 D-RR-7 3.47 Natural 0.100 0.25 193 38 D-RR-8 3.47 Natural 0.100 0.33 203 61 D-RR-9 3.96 Natural 0.100 0.34 204 56 D-WPSC-1 2.75 Natural 0.100 0.00 252 2 D-WPSC-2 2.75 Natural 0.100 0.13 233 39 L381 1.00 Circular 0.015 1.00 30 3 L383 1.00 Circular 0.015 1.00 28 3 L385 1.00 Circular 0.015 1.00 28 3 O-AEW-13 1.00 Trapezoidal 0.100 0.91 278 35 P-06-1062 4.83 Special 0.028 -1.10 26 41 P-06-1282 5.42 Special 0.015 0.25 24 62 P-06-1293 2.50 Circular 0.015 0.23 220 17 P06-1293.1 1.00 Circular 0.015 0.93 106 3 P-06-1293.2 1.00 Circular 0.015 0.13 180 1 P-06-1353 2.50 Circular 0.015 1.00 81 36 P-06-1354 1.50 Circular 0.015 1.05 10 9 P-06-1355 1.92 Special 0.015 1.00 49 9 P-06-1356 2.50 Special 0.015 1.00 10 20 P-06-1357 2.25 Circular 0.015 0.79 300 24 P-06-1370 5.00 Circular 0.015 0.41 174 144 P-06-1371 5.00 Circular 0.015 0.41 82 145 P-06-1387 1.00 Circular 0.015 1.48 51 4 P-06-1388 1.00 Circular 0.015 0.47 79 2 P-06-1389 1.00 Circular 0.015 1.05 23 3 P-06-1391 3.75 Special 0.015 0.59 51 46 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 3 of 7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.02-3.doc\121707 Name Diameter (ft) Shape Roughness Conduit Slope (%) Length (ft) Design Flow (cfs) P-06-1392 3.75 Special 0.015 1.38 27 70 P-06-462 4.83 Special 0.026 0.41 348 34 P-06-462 4.83 Special 0.026 0.41 349 34 P-06-462 1.00 Trapezoidal 0.014 -0.23 349 123 P-06-467 4.83 Special 0.026 0.22 63 25 P-06-467 4.83 Special 0.026 1.22 63 25 P-06-467 1.00 Trapezoidal 0.014 -0.44 63 225 P-06-468 4.83 Special 0.026 0.34 161 31 P-06-468 4.83 Special 0.026 0.34 160 31 P-06-468 1.00 Trapezoidal 0.014 0.82 160 229 P-06-469 4.83 Special 0.028 0.36 141 30 P-06-469 1.30 Trapezoidal 0.014 0.63 141 312 P-06-470 4.83 Special 0.026 0.24 197 26 P-06-470 4.83 Special 0.026 0.24 197 26 P-06-470 1.50 Trapezoidal 0.014 0.22 197 680 P-06-471 4.83 Special 0.026 0.15 356 21 P-06-471 4.83 Special 0.026 0.15 355 21 P-06-471 1.30 Trapezoidal 0.014 0.15 355 447 P-06-472 4.83 Special 0.026 -0.56 36 40 P-06-472 1.00 Trapezoidal 0.014 0.56 36 252 P-06-473.1 4.83 Special 0.016 0.17 112 36 P-06-473.1 1.00 Trapezoidal 0.014 0.94 112 123 P-06-473.2 4.83 Circular 0.016 0.20 111 86 P-06-473.2 1.00 Trapezoidal 0.014 0.93 111 122 P-06-474 4.83 Special 0.016 0.25 404 44 P-06-474 4.83 Special 0.016 0.28 404 46 P-06-486 4.83 Special 0.028 0.15 338 19 P-06-486 1.00 Trapezoidal 0.014 0.63 338 200 P-06-487 4.83 Special 0.028 0.24 144 24 P-06-487 1.00 Trapezoidal 0.014 -0.16 144 101 P-06-489 6.00 Special 0.026 0.43 257 67 P-06-489 6.00 Special 0.026 0.39 239 63 P-06-489 1.00 Trapezoidal 0.014 0.35 239 199 P-06-490 4.83 Special 0.026 0.39 339 33 P-06-492 4.83 Special 0.026 -0.11 18 18 P-06-492 1.00 Trapezoidal 0.014 -0.45 18 226 P-06-493 4.83 Special 0.026 -0.02 561 7 P-06-493 1.00 Trapezoidal 0.014 0.23 561 122 P-06-494 4.83 Special 0.026 0.37 168 33 P-06-494 1.00 Trapezoidal 0.014 0.39 168 157 P-06-552 4.83 Special 0.028 0.32 296 28 P-06-552 1.30 Trapezoidal 0.014 0.29 296 355 P-06-553 4.83 Special 0.028 0.28 246 26 P-06-553 1.00 Trapezoidal 0.014 0.33 246 146 P-06-602 4.83 Special 0.026 -0.05 518 11 P-06-602 4.83 Special 0.026 -0.05 518 12 P-06-602 1.00 Trapezoidal 0.014 0.24 518 125 P-06-640 4.83 Special 0.026 0.02 102 7 P-06-640 1.00 Trapezoidal 0.014 0.15 102 97 P-06-653 4.83 Special 0.028 0.10 283 16 P-06-653 1.00 Trapezoidal 0.014 0.14 283 94 P-06-677 3.50 Circular 0.015 0.23 327 42 P-06-677 1.00 Trapezoidal 0.014 0.93 327 244 P-06-678 2.50 Circular 0.015 0.51 425 25 P-06-679 2.50 Circular 0.015 0.52 364 26 P-06-680 2.25 Circular 0.015 0.82 241 24 P-06-684 4.83 Special 0.028 0.10 170 16 P-06-685 4.83 Special 0.028 0.21 307 22 P-06-685 1.00 Trapezoidal 0.014 0.03 307 61 P-06-686 4.83 Special 0.028 0.05 165 11 P-06-687 4.83 Special 0.028 8.21 12 142 P-06-687.1 4.83 Special 0.028 -0.04 161 10 P-06-688 4.25 Special 0.026 0.04 302 9 P-06-688 1.00 Trapezoidal 0.014 1.20 302 278 P-06-770 4.83 Special 0.028 0.12 346 17 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 4 of 7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.02-3.doc\121707 Name Diameter (ft) Shape Roughness Conduit Slope (%) Length (ft) Design Flow (cfs) P-06-773 5.00 Circular 0.015 0.33 1092 130 P-06-773 1.30 Trapezoidal 0.014 0.09 1092 120 P-06-836 4.83 Special 0.026 -0.47 47 37 P-06-836 1.00 Trapezoidal 0.014 0.47 47 231 P-06-837 4.83 Special 0.026 0.64 286 43 P-06-837 4.83 Special 0.026 0.64 286 43 P-06-837 1.20 Trapezoidal 0.014 0.31 286 318 P-06-841 4.83 Special 0.028 0.46 37 29 P-06-841.1 4.83 Special 0.028 0.16 189 20 P-06-842 3.00 Circular 0.015 0.20 80 26 P-06-843 2.00 Circular 0.015 0.36 253 12 P-06-844 2.00 Circular 0.015 0.20 213 9 P-06-845 2.00 Circular 0.015 0.38 21 12 P-06-846 2.00 Circular 0.015 0.23 156 9 P-06-847 1.50 Circular 0.015 0.54 267 7 P-06-848 1.50 Circular 0.014 0.60 180 8 P-13-1000 2.00 Circular 0.015 0.64 85 16 P-13-1000 1.00 Trapezoidal 0.015 0.79 85 210 P-13-1001 2.00 Circular 0.015 0.95 110 19 P-13-1001 1.00 Trapezoidal 0.015 1.91 110 349 P-13-1003 2.00 Circular 0.015 0.89 154 19 P-13-1003 1.00 Trapezoidal 0.015 1.24 154 281 P-13-1032 2.50 Circular 0.015 1.33 23 41 P-13-1032 1.00 Trapezoidal 0.015 0.00 23 8 P-13-1033 2.50 Circular 0.015 0.47 156 24 P-13-1035 2.50 Circular 0.015 0.24 341 17 P-13-1036 2.00 Circular 0.015 0.42 129 13 P-13-1038 2.00 Circular 0.015 1.38 66 23 P-13-1041 2.00 Circular 0.015 0.97 202 19 P-13-1041 1.00 Trapezoidal 0.015 -0.12 202 87 P-13-1070 2.50 Circular 0.015 0.22 252 17 P-13-1071 2.50 Circular 0.015 0.21 141 16 P-13-1174 3.17 Special 0.026 -0.15 110 32 P-13-1175 3.17 Special 0.026 0.59 356 63 P-13-1178 3.00 Circular 0.015 0.75 350 50 P-13-1179 3.00 Circular 0.015 0.61 186 45 P-13-1181 3.00 Circular 0.015 0.57 275 44 P-13-1183 3.00 Circular 0.015 0.61 203 45 P-13-1185 3.00 Circular 0.015 0.46 307 39 P-13-1187 3.00 Circular 0.015 0.39 402 36 P-13-1188 3.00 Circular 0.015 0.54 215 42 P-13-1189 3.00 Circular 0.015 0.64 84 46 P-13-1190 4.00 Circular 0.016 0.44 158 78 P-13-1216 3.50 Circular 0.015 0.52 242 63 P-13-1216 1.00 Trapezoidal 0.014 -1.10 242 265 P-13-1217 4.00 Circular 0.015 0.22 133 58 P-13-1218 4.00 Circular 0.015 0.47 96 85 P-13-1219 4.00 Circular 0.015 0.39 139 78 P-13-1220 3.50 Circular 0.015 0.49 273 61 P-13-1221 3.50 Circular 0.015 0.52 250 63 P-13-1221 1.00 Trapezoidal 0.014 1.33 250 292 P-13-1279 3.58 Special 0.026 0.69 35 73 P-13-1280 3.58 Special 0.026 0.22 149 41 P-13-1281 3.58 Special 0.026 0.08 53 24 P-13-1282 3.58 Special 0.026 0.22 32 41 P-13-1292 4.00 Circular 0.016 0.60 58 90 P-13-1362 2.00 Circular 0.015 0.27 210 10 P-13-1362 1.00 Trapezoidal 0.015 0.31 210 141 P-13-1363 2.00 Circular 0.015 0.08 415 6 P-13-1364 1.00 Circular 0.010 0.23 187 2 P-13-1365 1.00 Circular 0.010 0.13 250 2 P-13-1703 2.08 Special 0.026 0.02 96 1 P-13-1703 2.08 Special 0.026 0.02 86 1 P-13-1703 1.00 Trapezoidal 0.014 0.51 86 181 P-13-1704 2.08 Special 0.026 0.35 31 3 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 5 of 7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.02-3.doc\121707 Name Diameter (ft) Shape Roughness Conduit Slope (%) Length (ft) Design Flow (cfs) P-13-1704 2.08 Special 0.026 0.35 31 3 P-13-1844 0.67 Circular 0.010 4.75 30 3 P-13-2 3.00 Circular 0.015 0.05 258 12 P-13-2029 2.00 Circular 0.015 1.20 49 21 P-13-2030 2.00 Circular 0.015 3.89 32 39 P-13-2304 0.67 Circular 0.010 4.20 36 3 P-13-2371 4.50 Circular 0.015 0.14 173 65 P-13-2381 4.42 Special 0.015 0.38 84 57 P-13-2382 4.42 Special 0.015 1.27 21 104 P-13-2411.1 3.17 Special 0.015 1.44 17 44 P-13-2613 3.50 Circular 0.015 -0.46 121 59 P-13-2614 3.50 Circular 0.015 0.83 100 80 P-13-2619 3.50 Circular 0.015 0.26 251 44 P-13-2622 3.50 Circular 0.015 0.09 123 26 P-13-2623 3.50 Circular 0.015 0.06 171 21 P-13-2624 1.00 Circular 0.015 4.29 12 6 P-13-2625 1.00 Circular 0.015 1.09 65 3 P-13-2626 3.50 Circular 0.015 0.33 203 50 P-13-2629 3.50 Circular 0.015 0.08 194 25 P-13-4 3.00 Circular 0.015 0.11 354 19 P-13-4 1.00 Circular 0.015 0.16 354 1 P-13-420 4.83 Special 0.026 0.00 147 36 P-13-452 5.42 Special 0.026 1.02 84 73 P-13-453 4.00 Circular 0.016 0.90 277 111 P-13-454 4.00 Circular 0.016 1.02 174 118 P-13-455 4.00 Circular 0.016 0.44 309 77 P-13-456 4.83 Special 0.026 0.47 322 37 P-13-456 1.00 Trapezoidal 0.014 0.76 322 344 P-13-457 4.00 Circular 0.015 0.32 240 71 P-13-457 1.00 Trapezoidal 0.014 0.66 240 211 P-13-458 4.00 Circular 0.015 0.41 85 80 P-13-458 1.00 Trapezoidal 0.014 -0.59 85 194 P-13-459 4.00 Circular 0.015 0.42 384 81 P-13-459 1.00 Trapezoidal 0.014 0.41 384 162 P-13-460 4.00 Circular 0.015 0.43 350 81 P-13-460 1.00 Trapezoidal 0.014 0.54 350 186 P-13-471 6.33 Special 0.015 0.20 65 79 P-13-546 2.08 Special 0.026 0.63 65 4 P-13-546 2.08 Special 0.026 0.63 65 4 P-13-547 2.08 Special 0.026 0.02 313 1 P-13-547 2.08 Special 0.026 0.02 313 1 P-13-548 2.08 Special 0.026 0.14 91 2 P-13-548 2.08 Special 0.026 0.14 90 2 P-13-548 0.79 Trapezoidal 0.014 0.23 90 124 P-13-549 2.08 Special 0.026 0.14 156 2 P-13-549 2.08 Special 0.026 0.14 155 2 P-13-549 1.00 Trapezoidal 0.014 0.53 155 184 P-13-550 2.08 Special 0.026 0.03 511 1 P-13-550 2.08 Special 0.026 0.03 512 1 P-13-550 1.00 Trapezoidal 0.014 0.12 513 719 P-13-551.1.1 1.00 Circular 0.026 0.23 146 1 P-13-551.2.1 1.00 Circular 0.026 0.76 121 2 P-13-552 2.50 Circular 0.015 0.27 22 19 P-13-552 1.00 Trapezoidal 0.015 0.73 22 215 P-13-554 2.25 Circular 0.015 0.25 215 13 P-13-555 2.25 Circular 0.015 0.30 255 15 P-13-555 1.00 Trapezoidal 0.015 0.19 255 103 P-13-557 2.25 Circular 0.015 0.26 174 14 P-13-558 2.25 Circular 0.015 0.41 66 17 P-13-558 1.00 Trapezoidal 0.015 0.74 66 204 P-13-559 2.00 Circular 0.015 0.31 326 11 P-13-559 1.00 Trapezoidal 0.015 0.55 326 175 P-13-561 2.00 Circular 0.015 0.25 318 10 P-13-561 1.00 Trapezoidal 0.015 0.47 318 161 P-13-562 2.00 Circular 0.015 0.26 185 10 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 6 of 7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.02-3.doc\121707 Name Diameter (ft) Shape Roughness Conduit Slope (%) Length (ft) Design Flow (cfs) P-13-568 1.75 Circular 0.015 0.39 57 9 P-13-569 1.75 Circular 0.015 0.43 155 9 P-13-570 1.75 Circular 0.015 0.39 209 9 P-13-571 1.75 Circular 0.015 0.42 260 9 P-13-6 3.00 Circular 0.015 0.20 180 26 P-13-659 4.00 Circular 0.016 0.89 305 110 P-13-660 4.00 Circular 0.015 0.78 225 110 P-13-764 3.50 Circular 0.015 0.07 505 22 P-13-765 3.50 Circular 0.026 0.09 264 15 P-13-765 1.00 Trapezoidal 0.014 0.66 264 205 P-13-766 3.50 Circular 0.015 0.10 155 27 P-13-766 1.00 Trapezoidal 0.014 0.39 155 158 P-13-791 3.50 Circular 0.015 0.09 295 27 P-13-791 1.00 Trapezoidal 0.014 -0.28 295 135 P-13-792 3.50 Circular 0.015 -0.04 200 16 P-13-792 1.00 Trapezoidal 0.014 0.20 200 113 P-13-793 3.50 Circular 0.015 0.00 262 30 P-13-793 1.00 Trapezoidal 0.014 0.18 262 108 P-13-794 3.50 Circular 0.015 0.13 185 31 P-13-846 2.50 Circular 0.015 0.44 323 24 P-13-847 2.50 Circular 0.015 0.35 151 21 P-13-849 2.50 Circular 0.015 0.93 396 34 P-13-852 2.50 Circular 0.015 0.12 115 12 P-13-852 1.00 Trapezoidal 0.015 0.65 115 191 P-13-853 2.75 Special 0.026 0.39 220 38 P-13-853 1.00 Trapezoidal 0.150 -0.14 195 10 P-13-864 2.75 Special 0.026 0.19 184 26 P-13-864 1.00 Trapezoidal 0.015 0.70 184 211 P-13-866 2.75 Circular 0.026 0.26 196 13 P-13-866 1.00 Trapezoidal 0.015 0.20 196 107 P-13-867 2.75 Special 0.026 0.30 132 33 P-13-867 1.00 Trapezoidal 0.015 0.03 132 41 P-13-869 2.25 Circular 0.015 0.60 33 21 P-13-869 1.00 Trapezoidal 0.015 0.09 33 71 P-13-871 2.25 Circular 0.015 0.14 101 10 P-13-871 1.00 Trapezoidal 0.015 0.22 101 111 P-13-873 2.25 Circular 0.015 0.27 229 14 P-13-873 1.00 Trapezoidal 0.015 0.37 229 143 P-13-874 3.17 Special 0.026 0.11 274 27 P-13-875 3.17 Special 0.026 -1.52 13 101 P-13-875 1.50 Trapezoidal 0.050 0.00 13 4 P-13-983 2.25 Circular 0.015 0.26 214 14 P-13-983 1.00 Trapezoidal 0.015 0.20 214 106 P-13-999 2.00 Circular 0.015 0.74 98 17 P-13-999 1.00 Trapezoidal 0.015 -0.65 98 204 P-16-425 4.83 Special 0.026 0.27 254 28 P-16-425 1.00 Trapezoidal 0.014 0.22 254 118 P-16-426 4.83 Special 0.026 0.19 400 23 P-16-426 1.00 Trapezoidal 0.014 0.25 400 126 P-16-427 4.83 Special 0.026 0.17 401 22 P-16-427 1.00 Trapezoidal 0.014 0.20 401 114 P-16-428 5.42 Special 0.026 0.18 269 31 P-16-428 1.00 Trapezoidal 0.014 0.68 269 349 P-16-429 5.42 Special 0.026 0.18 402 31 P-16-429 1.30 Trapezoidal 0.014 0.22 402 580 P-16-430 6.00 Circular 0.026 0.38 390 131 P-16-469 5.42 Special 0.026 0.29 136 39 P-16-469 1.00 Trapezoidal 0.014 -0.56 136 190 P-16-487 6.00 Special 0.024 -0.05 84 24 P-16-495 4.83 Special 0.026 -0.19 106 23 P-16-495 1.00 Trapezoidal 0.014 0.32 106 144 P-16-646 5.00 Circular 0.015 0.34 471 131 P-16-647 5.00 Circular 0.015 0.33 832 130 P-2125-75 1.00 Circular 0.010 0.22 206 2 P-2301-1 0.50 Circular 0.012 0.51 79 0 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 7 of 7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 3.02-3.doc\121707 Name Diameter (ft) Shape Roughness Conduit Slope (%) Length (ft) Design Flow (cfs) P-2301-1 1.00 Trapezoidal 0.100 25.60 10 207 P-2301-1.1 0.50 Circular 0.012 35.00 10 4 P-2301-1.1 0.33 Circular 0.013 0.00 10 0 P-2301-2 0.16 Circular 0.013 0.54 13 0 P-2301-2 0.25 Trapezoidal 0.100 13.60 10 11 P-2301-2.1 0.67 Circular 0.013 0.00 10 0 P-2301-2.1 0.33 Circular 0.013 0.00 10 0 P-2301-3 0.67 Circular 0.010 0.15 61 1 P-2301-3 1.00 Trapezoidal 0.100 11.40 10 108 P-2449-1.1 1.00 Circular 0.015 10.92 12 10 P-2449-1.3 1.00 Circular 0.015 1.00 48 3 P-2449-1.5 0.83 Circular 0.010 1.00 20 3 P-2449-1.6 2.00 Circular 0.026 0.50 68 8 P-2531-1 1.25 Circular 0.026 1.00 23 3 P-2531-2 1.25 Circular 0.015 0.40 110 4 P-2531-3 1.00 Circular 0.015 0.70 105 3 P-2690-1 0.67 Circular 0.010 3.53 36 3 P-2751-1 1.25 Circular 0.015 11.12 60 19 P-2751-2 1.00 Circular 0.015 1.04 139 3 P-2751-3 1.00 Circular 0.015 1.74 140 4 P-2751-4 0.67 Circular 0.015 0.66 276 1 P-2980-1.5 1.25 Circular 0.010 0.26 681 4 P-2980-2 2.00 Circular 0.026 0.38 65 7 P-2980-4 1.00 Circular 0.010 0.75 26 4 P-4000-91 2.00 Circular 0.015 -2.83 11 33 P-4000-92 1.00 Circular 0.026 3.26 46 3 P-4000-93 0.83 Circular 0.026 0.78 64 1 P-4000-94 0.83 Circular 0.026 0.72 59 1 P-40D-22 5.00 Circular 0.015 0.42 43 146 P-AEW-1 4.83 Special 0.016 0.26 589 44 P-AEW-1 4.83 Special 0.016 0.26 587 44 P-AEW-1 1.00 Trapezoidal 0.024 0.26 587 103 P-AEW-10 3.00 Rectangular 0.015 0.78 195 110 P-AEW-13 5.00 Circular 0.015 0.33 278 130 P-AEW-14.1 3.00 Trapezoidal 0.100 1.28 16 123 P-AEW-15.1 3.17 Special 0.015 2.96 45 63 P-AEW-16 2.50 Circular 0.015 -0.80 71 32 P-AEW-18 2.75 Special 0.026 0.18 50 26 P-AEW-18 2.75 Special 0.026 -0.08 50 17 P-AEW-20 2.75 Special 0.026 0.98 51 60 P-AEW-20 2.75 Special 0.026 1.70 51 79 P-AEW-22 4.00 Circular 0.015 0.61 183 97 P-AEW-22 4.00 Circular 0.015 0.07 191 32 P-AEW-24 3.17 Special 0.026 1.54 61 102 P-AEW-24 3.17 Special 0.026 0.99 61 82 P-AEW-26 4.00 Circular 0.015 0.58 106 95 P-AEW-28 3.50 Circular 0.015 0.29 308 47 P-AEW-3 4.00 Circular 0.015 1.22 166 137 P-AEW-3 1.00 Trapezoidal 0.014 1.19 166 276 P-AEW-30 2.50 Circular 0.026 0.00 43 1 P-AEW-30 2.31 Natural 0.100 0.00 43 87 P-AEW-33 4.00 Circular 0.016 1.65 126 150 P-AEW-34 3.50 Circular 0.026 0.24 54 25 P-AEW-36 3.33 Special 0.026 0.24 25 40 P-AEW-40 2.50 Circular 0.015 2.85 113 60 P-AEW-8 4.50 Circular 0.015 0.16 164 68 P-AP-3 1.25 Circular 0.015 0.40 45 4 P-LP-1 4.25 Special 0.015 0.26 46 39 P-STR-10.1 3.50 Circular 0.015 0.11 74 29 P-STR-5.1 3.50 Circular 0.015 0.12 67 30 p-WM MH-1 1.00 Circular 0.015 0.25 95 2 P-WM P-1 1.00 Circular 0.015 0.10 290 1 P-WM P-2 1.25 Circular 0.015 0.60 82 4 S-13-1033 1.00 Trapezoidal 0.015 0.64 1390 202 S-13-874 1.00 Trapezoidal 0.015 0.23 871 114 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® 3-6 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S3.doc\022508 During the June 10/11, 2004 storm event, modeling results show that the overflow of the Landmark Basin would have had a 0.77-foot depth of stormwater flowing through it. As can be seen, modeling shows that approximately 0.36 feet of flooding of the eastern Landmark Plaza building occurred. According to our survey, the lowest first floor elevation of the homes along Westfield Drive in the area that appears to flood is 762.39 (221 South Westfield Drive), which is about 0.11 feet higher than the first floor elevation of the eastern Landmark Plaza building. For comparison, the first floor elevation of the Tippler Junior High Administration Building (761.31) is 2.61 feet above the lowest overflow elevation (758.70) that would allow water from the Tippler Basin to discharge to the City road network east of the Tippler property. During the June 10/11, 2004 storm event, our model shows that the overflow of the Tippler Basin had a 1.53-foot depth of stormwater flowing through it. With the 1.53-foot depth of flow through the spillway, the Tippler Junior High Administration Building still had approximately 1.07 feet of freeboard between the modeled high water elevation and the first floor of the building. As described in more detail in Section 4.01, we would recommend a minimum of 1.5 feet of freeboard (with 2 feet being desirable) from the first floor elevation of a building to the computed 100-year water surface elevation adjacent to the building. This is consistent with NR 116-Wisconsin’s Floodplain Management Program. 3. According to the XP-SWMMTM model, Sawyer Creek did not directly back up into the Landmark Plaza during the June 10/11, 2004, rainfall event. However, it may have contributed to a reduced capacity in the upstream stormwater conveyance system. The elevations surveyed by the City on June 11, 2004, as high water marks and the relevant invert elevations of the storm sewer system at diversion locations are shown in Figure 2.07-1. 4. There are four diversion/cross connection points along Washburn Street that allow flows to move into and out of adjacent basins as shown in Figure 3.02-3. These four diversion/cross connection points appear to have been naturally occurring drainage routes prior to development occurring in these locations. This analysis indicates that the capacity of the culvert beneath USH 41 south of Dickinson Avenue is less than the peak discharge coming to that point (Diversion Point 1). This causes flows exceeding the capacity of the culvert to divert to the north along Washburn Street until that flow reaches Diversion Point 4. Diversion Point 4 allows very little flow (15.5 cfs during the existing conditions June 10/11, 2004 storm event) to cross easterly across USH 41 thus causing flows exceeding its capacity to flow north toward Diversion Point 2. The culvert that creates Diversion Point 4 is sloped from east to west. However, before the flows get to the north side of 9th Avenue, they are attenuated by surface ponding between Diversion Point 1 and Diversion Point 4 (south of W. 9th Avenue); therefore the flows at Diversion Point 2 are not as high as at Diversion Point 1 or Diversion Point 4. Diverting additional flows toward Sawyer Creek and thus away from the Landmark Plaza at Diversion Point 2 appears feasible only if the storm sewer leading from just north of Witzel EXISTING CONDITIONS DIVERSION ANALYSIS NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 3 . 0 2 - 3 1- 382 . 0 3 0 Diversion PT 3 30" RCP IE = 760.27 Diversion PT 2 3' x 4.5' RCP Box IE = 762.54 Diversion PT 1 High PT = 776.35 42" RCP IE = 775.25 Diversion PT 4 36" RCP IE = 769.53 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 3 . 02 - 3 - Ex i st ing C o n d i tion s D i ve r si on A n a l ys i s . m xd 0 500 1,000250 Feet ³ Legend Drainage Basin Boundary Sub Drainage Basin Boundary Landmark Plaza Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer ^_Diversion Point ^_ ^_ ^_ ^_ Flow (CFS) Q1 = 9 Q2 = 20 Q5 = 33 Q10 = 42 Q25 = 59 Q50 = 90 Q100 = 108 Q6/11/04 =76 Flow (CFS) Q1 = 6 Q2 = 17 Q5 = 30 Q10 = 37 Q25 = 52 Q50 = 67 Q100 = 72 Q6/11/04 = 67 Flow (CFS) Q1 = 16 Q2 = 32 Q5 = 43 Q10 = 49 Q25 = 57 Q50 = 63 Q100 = 69 Q6/11/04 = 62 Flow (CFS) Q1 = 0 Q2 = 0 Q5 = 0 Q10 = 0 Q25 = 0 Q50 = 0 Q100 = 10 Q6/11/04 = 0 Flow (CFS) Q1 = 17 Q2 = 22 Q5 = 33 Q10 = 38 Q25 = 46 Q50 = 48 Q100 = 50 Q6/11/04 = 48 Flow (CFS) Q1 = 26 Q2 = 32 Q5 = 35 Q10 = 36 Q25 = 37 Q50 = 38 Q100 = 38 Q6/11/04 = 37 Flow (CFS) Q1 = 16 Q2 = 30 Q5 = 41 Q10 = 46 Q25 = 52 Q50 = 55 Q100 = 58 Q6/11/04 = 57 Flow (CFS) Q1 = -2 Q2 = 8 Q5 = 13 Q10 = 15 Q25 = 17 Q50 = 19 Q100 = 20 Q6/11/04 = 16 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® 3-7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S3.doc\022508 Avenue to the Sawyer Creek/Washburn Street outfall is upsized to maintain the existing 100-year capacity of that segment of storm sewer. Diversion of additional flow to the east to reduce flooding along Washburn Street at Diversion Point 1 appears to be feasible, provided it is routed to the proposed Armory detention pond. Diversion of additional flow to the east at Diversion Point 4 does not appear to be feasible with the proposed reconstruction of USH 41. 5. As discussed in the original report, the capacity of the existing ditch and connecting storm sewer culvert through Landmark Plaza are currently limited by backwater caused by the downstream drainage system. The western four ditch segments through Landmark Plaza currently have a 2-year, 2-hour duration capacity. The easternmost ditch segment has a 5-year, 2-hour duration capacity. The existing storm sewer culvert along the ditch currently has a 2-year, 2-hour duration capacity. In general, if the downstream “bottleneck” and associated backwater are reduced/relieved, modeling results indicate that these ditch segments and connecting storm sewer culvert appear to be able to pass the 100-year, 2-hour duration storm event flows around the west and south sides of the southern Landmark Plaza building and the movie theater building without inundating these buildings. 6. As described in the original report, the Landmark Plaza internal drainage in the areas west and southwest of the eastern Landmark Plaza building (modeled nodes 06-846, 06-847, and 06-1293.2) have adequate overland flow routes that would convey flows around the building rather than flood the building if the downstream drainage system capacity is increased. If each of these nodes were to be clogged with debris so that the inlets were not accepting flow, the 100-year, 2-hour duration storm event would be passed around the north and south sides of the building at a maximum elevation of 761.95 (761.55 north side, 761.60 middle, and 761.95 south side), which is 0.33 feet (4 inches) lower than the first floor elevation of the eastern Landmark Plaza building if downstream drainage system capacity is increased. However, node 06-846 would have to pond to 12.8 inches, node 06-847 would have to pond to 15.5 inches, and node 06-1293.2 would have to pond to 11.8 inches before overflowing along these routes. We would normally recommend no more than 6 to 9 inches of ponding to avoid damage to vehicles at low points. In summary, if the downstream backwater effects are alleviated, these three nodes appear to have adequate overland flow routes to the east and southeast sides of the eastern Landmark Plaza building. If the downstream backwater effects are not alleviated, then flooding similar to the June 10/11, 2004, storm event in larger storm events will continue. We recommend that the owner of the Landmark Plaza perform a study to determine how to reduce potential ponding at the three stormwater inlets (nodes 06-846, 06-847, and 06-1293.2) to an acceptable level considering that downstream backwater effects are alleviated. See Figure 3.02-1 (located in the pocket folder of the original report dated May 2006) for node locations. SECTION 4 ALTERNATIVE ANALYSIS City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-1 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 Location Available (acre-feet) Armory 2.7 Westhaven Golf Course 8.1 Wal-Mart 6.9 Upstream of Washburn Street 10.4 Total Existing Detention 28.1 Table 4.01-1 Existing Available Detention 4.01 GENERAL A. Alternatives Analysis Overview This section discusses alternatives analyzed to address existing flooding at Landmark Plaza, based on discussions between City and Strand Associates staff. Each alternative includes a description, the effects on flooding at Landmark Plaza, the effects on flooding watershed-wide, and the planning-level Opinion of Probable Cost. Costs presented were estimated using historical bid costs, where available, and supplemented by other reference sources. All estimated project costs include allowances for engineering and contingencies, soils investigation where necessary, and land acquisition costs. The goal of this report is to provide City personnel with the information required to initiate the budgeting and planning phase for facilities improvements. All costs are presented in 4th quarter 2007 dollars. Future construction costs should be adjusted for inflation when final project schedules are determined. Opinions of probable construction cost estimates will be updated during the design phase. B. Existing Detention in Watershed Each alternative model includes existing detention at the Armory, Westhaven Golf Course, and Wal- Mart. Upstream of Washburn Street, all detention with greater than 0.7 acre-feet of available storage (17 detention basins) was modeled for an aggregate available storage of 10.4 acre-feet. The available detention at each of these existing facilities is included in Table 4.01-1. Table 4.01-2 shows the potential amount of storage available for the alternatives being considered. C. Overview of Alternatives Evaluated The components of alternatives 12 through 16 are shown in Table 4.01-3. In early 2007, the City contacted Curwood Inc./Bemis to investigate the feasibility of locating a detention pond on their property at the following two sites. However, the investigation ruled out these locations as potential detention sites and they were not analyzed as part of this plan. 1. Vacant land at the 2151 Universal Street (west side) site 2. Vacant land at the 2200 Badger Avenue site located south of the Universal Street and West 20th Avenue intersection (south of the railroad tracks). In early 2007, the City contacted Continental Girbau to investigate the feasibility of locating a detention pond on a vacant portion of their property at 2500 STH 44 located at northwest corner of the STH 44 and Universal Street intersection. However, the investigation and cursory analysis ruled out this location as a potential detention site because of the following reasons and thus was not analyzed as part of this plan. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 3–Engineering Analysis Prepared by Strand Associates, Inc.® Page 1 of 1 JHL:PLL\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 4.01-2.doc\022608 TABLE 4.01-2 PROPOSED ALTERNATIVES DETENTION AVAILABILITY–FUTURE CONDITIONS Potential Detention Sites Potential Available Storage (acre-feet) Max 100-Year 12 hr Modeled Storage (acre-feet) Alternative 12 (formerly Alternative 7) 12a–Expanded Detention at Tippler Junior High Property 41.5 31.3 12b–Fully Expanded Armory Detention and USH 41 Pipe Upsizing (Wet Pond) 44.1 44.1 12c–Detention at Vacant Lot Southwest of 9th Avenue/Washburn Street Intersection 28.9 25.7 12d-Wet Detention Basin in Agricultural Land Southeast of STH 44/N. Gray Rd. Intersection meeting County ordinances 22.0 18.7 Total 136.5 119.8 Alternative 13 13a-Partially Expanded Westhaven Golf Course Ponds (Two Wet Ponds) 45.7 45.7 13b-Partially Expanded Armory Detention 30.9 30.0 13c-Expanded Detention at Tippler Junior High Property 41.5 38.2 13d-Wet Detention Basin in Agricultural Land Southeast of STH 44/N. Gray Rd. Intersection meeting County ordinances 22.0 18.7 Total 140.1 132.5 Alternative 13 B 13 B 1-Fully Expanded Westhaven Golf Course Ponds (Two Wet Ponds) 154.3 154.3 13 B 2-Partially Expanded Armory Detention 30.9 27.0 13 B 3-Expanded Detention at Tippler Junior High Property 41.5 33.8 16d- Wet Detention Basin in Agricultural Land Southeast of STH 44/N. Clay Rd. Intersection meeting County ordinances 22.0 18.6 Total 248.7 233.7 Alternative 14 14a-Detention at Southeast Corner of STH 44/West Waukau Avenue Intersection (Wet Pond) 17.7 17.1 14b-Fully Expanded Armory Detention 44.1 44.5 14c-Expanded Detention at Tippler Junior High Property 41.5 37.1 14d-Wet Detention Basin in Agricultural Land Southeast of STH 44/West Waukau Avenue Intersection meeting County ordinances 22.0 16.3 Total 125.3 114.8 Alternative 15 15a-Expanded Detention Basin In Agricultural Land Southeast of STH 44/ N. Clay Rd. Intersection(Wet Pond) meeting City stormwater ordinances 36.1 28.7 15b-Fully Expanded Armory Detention 44.3 44.3 15c-Expanded Detention at Tippler Junior High Property 41.5 37.2 Total 121.9 110.2 Alternative 16 16a-Fully Expanded Westhaven Golf Course Ponds (Two Wet Ponds) 154.6 154.6 16b-Fully Expanded Armory Detention 44.1 34.8 16c-Expanded Detention at Tippler Junior High Property 41.5 32.2 16d- Wet Detention Basin in Agricultural Land Southeast of STH 44/N. Clay Rd. Intersection meeting County ordinances 22.0 18.6 Total 262.2 240.1 Notes: 1. Potential Available Storage at elevation just prior to use of pond overflow. 2. Alternatives 12, 13, 13B, 14, and 16 include a detention basin (22.0 acre-feet) meeting County stormwater ordinances for the Agricultural Land Southeast of STH 44/N. Clay Rd. Intersection that would be built as part of future development. 3. Alternatives 13 through 16 are intended to find an alternative to the detention proposed at the vacant lot southwest of 9th Avenue//Washburn Street Intersection. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 1. Topographic constraints that drastically reduce the available storage at this site. 2. A navigable portion of Campbell Creek exists on the property. Detention at this location would thus have to be on-line which would generally not be permittable by DNR. D. Alternative Goals In assessing/ranking each Alternative, we have focused on not only alleviating flooding in the Landmark Plaza area but also have assessed each alternative in terms of the watershed-wide benefit. The goals of the alternatives are the following. In Sections 4.02 to 4.13, the benefits of each option are stated in terms of freeboard and flooding at Landmark Plaza (analyzed at the low point on the east side of the eastern Landmark Plaza building) and meeting of Landmark Plaza freeboard Alternative 12 13 13B 14 15 16 Detention at Tippler Junior High (previously considered in Alts. 1 and 5) No No No No No No Expanded Detention at Tippler Junior High Yes Yes Yes Yes Yes Yes Larger Pipe from Landmark Plaza to Tippler Yes Yes Yes Yes Yes Yes Detention South of Landmark Plaza (previously considered in Alts. 1 and 5) No No No No No No Existing Detention at Armory (previously considered in Alts. 2 and 4) No No No No No No Partially Expanded Detention at Armory No Yes Yes No No No Fully Expanded Detention at Armory Yes No No Yes Yes Yes Detention at 9th Avenue/Washburn Street Yes No No No No No Existing Westhaven Golf Course Detention Yes No No Yes Yes No Original Westhaven Expanded Golf Course Detention (previously considered in Alts. 3, 8, 9, 10, and 11) No No No No No No Partially Expanded Westhaven Golf Course Ponds (2 Wet Ponds) No Yes No No No No Fully Expanded Westhaven Golf Course Ponds (2 Wet Ponds) No No Yes No No Yes Pump Station at Campbell Creek Outfall (previously considered in Alt. 4) No No No No No No Diversion Pipe under Hwy 41 at Landmark Plaza Yes Yes Yes Yes Yes Yes 100-year storm sewer in WisDOT ROW from Landmark Plaza Diversion to Sawyer Creek along USH 41 (previously considered in Alt. 6, 8, and 10) No No No No No No Existing Wal-Mart Detention Yes Yes Yes Yes Yes Yes Increase Conveyance Capacity from Landmark Plaza to Campbell Creek Outfall (previously considered in Alt. 2) No No No No No No Increase Internal Conveyance Capacity at Landmark Plaza (previously considered in Alt. 2) No No No No No No Modified Diversion Pipe under Hwy 41 at Landmark Plaza (previously considered in Alt. 3) No No No No No No Detention at Southeast Corner of STH 44/W. Waukau Avenue Intersection (Wet Pond) No No No Yes No No Detention basin meeting County ordinances for the Agricultural Land Southeast of STH 44/North Clay Road Intersection. Yes Yes Yes Yes No Yes Expanded Detention Basin In Agricultural Land Southeast of STH 44/ North Clay Road Intersection(Wet Pond) meeting City stormwater ordinances No No No No Yes No 50-Year Design Storm Sewer/Ditch Capacity along USH 41 by WisDOT Yes Yes Yes Yes Yes Yes Table 4.01-3 Alternative Components City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-3 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 criteria for the 10-year, 2-hour duration, 100-year, 2-hour and 12-hour duration, and June 10/11, 2004, storm events. They are also ranked in terms of watershed-wide benefit. The ranking data and criteria used for these rankings are included in Tables 4.07-2 and 4.07-3. 1. Landmark Plaza a. Provide a minimum of 1.5 feet of freeboard from the computed high water elevation in the Landmark Plaza Basin to the elevation of the 1st floor elevation (762.28) of the eastern Landmark Plaza Building with 2 feet of freeboard being desirable for the 100-year storm of critical duration. b. Provide a minimum of 1.5 feet of freeboard from the computed high water elevation in the Tippler Junior High Basin to the elevation of the 1st floor elevation (761.31) of the Tippler Junior High northern building with 2 feet of freeboard being desirable for the 100-year storm of either 2-hour or 12-hour duration (whichever controls by causing a higher elevation at the Tippler Basin). c. Reduce the number of locations and occurrence frequency of pipe and ditch overflows in the Landmark Plaza Basin. d. Treat areas without defined floodplains in a similar manner as defined floodplains (per FEMA maps) so that certain provisions of NR 116- Wisconsin’s Floodplain Management Program would apply. NR 116 calls for new structures to be built at or above the flood protection elevation. The flood protection elevation means an elevation 2 feet above the regional flood elevation or calculated 100-year elevation adjacent to a structure. The 2 feet of freeboard is a safety factor that compensates for the effects of many factors that contribute to flood heights greater than those calculated (debris accumulation, effects of urbanization, and loss of flood storage because of development, among others defined in NR 116). NR 116 can be found on-line at: http://www.legis.state.wi.us/rsb/code/nr/nr116.pdf. Many times in retrofit situations, a lesser freeboard of 1.5 feet is considered acceptable in recognition of the fact that it may not be cost-effective to provide the full 2 feet of freeboard. However, each alternative analyzed in this report provides greater than 2 feet of freeboard to the Landmark Plaza eastern building and the Tippler buildings. 2. Watershedwide a. Reduce the amount of flooding in the watershed for the 1- through 100-year storm events under future conditions and for the June 10 and 11, 2004, storm event. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-4 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 b. Reduce the amount of flooding occurring in the 10-year storm event under future conditions by reducing flows through as many existing storm sewers as possible to less than a 10-year storm event with the Alternatives considered. c. Maximize the use of detention considered with these alternatives to provide opportunities for TSS reductions along with peak flow reductions. d. Reduce the peak discharge rates to the USH 41/Sawyer Creek, Westfield Drive/Sawyer Creek, and Campbell Creek outfalls to the maximum extent practicable with the Alternatives considered. e. Keep the total stormwater volume discharging at the Sawyer Creek/Washburn outfall to a minimum. f. Keep the increase in flows to the USH 41/Sawyer Creek outfall as small as possible. This is in recognition that for Alternatives 12 through 16 include increasing the size of the existing storm sewer/conveyance system to provide a 50-year design storm capacity along the west side of USH 41 from the USH 41/Sawyer Creek outfall to Allerton Drive. The new storm sewer/conveyance system providing a 50-year design storm capacity is WisDOT’s current plan along USH 41. The reason for this is that there are already downstream flooding problems in the area of the Westfield Drive/Sawyer Creek outfall. It is recommended that the Sawyer Creek watershed upstream of this point be provided with detention that will offset the difference between the future conditions 100-year flow rate (with upsized storm sewer contemplated under this study) and the existing conditions 100-year flow rate (approximately 134 cfs for 2-hour duration and 124 for 12-hour duration). 4.02 ALTERNATIVE 12 (FORMERLY ALTERNATIVE 7) We have analyzed the following mix of project components as shown in Figure 4.02-1: 1. Expanded Detention (31.3 acre-feet) at Tippler Junior High property (see Figure 4.02-2). To provide flooding relief directly to the Landmark Plaza as well as to downstream areas, we have analyzed the addition of detention at Tippler Junior High. Being on school district property, it appears feasible to construct a dry detention basin with a small wet pond in the center that would be used for detention during large rain events and as athletic fields when it is not raining. The basin is sized so that a soccer field and a football field could fit on the bottom of the basin. During final design, a dry detention pond without a wet pond in the center will be analyzed to achieve similar performance to the dry pond/wet pond combination. This parcel currently appears to be somewhat of a depressional area that overflows to the east once reaching approximately elevation 758.70 according to our field survey information. ALTERNATIVE 12 - COMPONENTS NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4 . 0 2 - 1 1- 3 82 . 0 3 0 Tippler Detention Channel Regrading and Twice Yearly Ditch Maintenance Twice Yearly Ditch Maintenance Additional 46 LF 27" RCP Parallel to Existing Storm Sewer 33" DIA Orifice Plate Upgrade Storm Sewer to 3' x 6' Upgrade Storm Sewer to 48" x 76" HERCP Total Length = 1021 LF Armory Detention Detention at 9th Ave and Washburn St !( FO R E B A Y FOR E B A Y Upgrade Storm Sewer to 3' x 5' W 9TH AVE WITZEL AVE S W A S H B U R N S T US H W Y 4 1 S O U T H B O U N D US H W Y 4 1 N O R T H B O U N D N K O E L L E R S T S K O E L L E R S T S E A G L E S T RE I C H O W S T W 5TH AVE US H W Y 4 1 R A M P S W E S T F I E L D S T OSBOR N A V E LI L A C S T AR M O R Y P L GR A C E L A N D D R MA R I C O P A D R MO R E L A N D S T ABBEY AVE W 6TH AVE W 7TH AVE WI N D S O R S T CU M B E R L A N D T R N E A G L E S T BISMARCK AVE CRYSTAL SPRINGS AVE WE S T B R O O K D R N W E S T F I E L D S T DICKINSON AVE MENARD DR S W E S T F I E L D S T US H W Y 4 1 R A M P W 7TH AVE 0 76 6 77 4 77 6 780 77 8 768 770 77 2 76 2 760 758 756 754 752 750 748 746 744 742 764 708 782 704 702 78 4 700698 78 6 696 790 78 8 792 79 4 694 782 764 77 4 772 77 2 78 0 784 77 0 77 8 0 0 77 6 77 6 78 2 778 782 770 782 78 2 772 78 0 774 772 78 2 0 700 77 4 78 0 774 778 76 2 77 4 766 77 4 782 76 2 762 77 8 77 4 780 766 776 77 8 78 0 78 0 772 768 77 6 78 0 77 0 784 0 778 0 76 6 0 782 780 77 4 776 78 6 764 764 780 766 77 4 774 772 782 760 766 77 4 772 764 0 78 6 77 8 778 780 77 0 78 8 788 770 78 4 76 4 0 77 8 77 8 780 0 0 776 0 772 772 78 4 782 0 77 2 77 8 764 778 778 764 780 77 6 77 2 76 8 77 4 77 4 782 75 8 79 4 0 0 77 8 78 2 778 77 6 782 78 6 786 77 2 786 0 762 78 0 782 780 770 762 76 8 782 774 0 764 776 77 4 77 2 778 784 770 780 784 776 0 78 2 772 76 2 772 770 776 780 780 778 782 77 4 78 0 778 0 77 4 772 778 76 2 772 78 0 77 8 764 77 6 77 6 77 4 778 764 768 77 0 778 776 696 78 0 77 8 784 77 4 770 77 6 77 8 78 2 77 8 76 4 774 76 8 76 4 77 2 76 2 77 6 770 77 8 0 76 4 77 8 766 78 0 782 77 8 0 0 0 79 0 77 8 77 4 0 76 2 77 0 780 78 0 0 77 8 0 778 774 764 772 0 0 78 0 77 6 778 780 0 784 772 0 770 784 77 8 76 2 77 2 780 0 780 76 8 772 77 2 77 2 768 758 768 78 0 778 782 770 764 77 4 76 6 76 4 0 77 0 704 780 77 6 772 782 78 0 778 77 6 77 8 772 786 78 4 772 778 77 8 77 2 77 6 77 2 77 6 784 78 2 782 778 762 0 0 766 778 77 6 780 778 762 42 48 15 5836 24 27 18 2516 12 6 8 21 36 54 60 30 5031 3658 19 3 0 51 3 1 0 1423 10 20 6540 18 12 8 12 30 12 21 27 121212 18 12 12 18 21 18 12 15 27 20 8 27 21 12 12 15 8 21 42 24 18 8 8 12 27 15 12 24 8 24 15 15 24 48 12 12 12 21 18 12 12 12 12 3658 12 12 15 12 8 18 12 15 18 24 18 18 12 12 12 27 12 18 10 1218 12 18 5836 24 12 24 12 24 18 10 18 21 21 8 15 15 24 24 12 48 24 15 24 27 12 42 12 12 15 10 12 12 12 24 15 12 12 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 4 . 02 - 1 - Al terna t i v e 12 . m x d 0 450 900225 Feet ³ Legend Storm Manhole Storm Sewer Culvert Sanitary Manhole Sanitary Sewer Water Valve Water Main Parcel Contour (2 FT.) Proposed Detention Proposed Pipe STH 44/Clay Rd Pond CL A Y R D STATE R D 4 4 BELLFIE L D D R 84 6 844 842 838 834 836 840 84 8 850 832 852 854 856 858 848 84 8 84 8 854 846 840 848 856 848 852 838 836 832 85 6 832 850 83 4 84 0850 85 2 83 6 846838 84 6 844 844 836 83 6 832 842 840 850 838 840 848 84 4 854 12 15 18 6 8 12 0 600300 Feet ALT ER NA T I V E 12 - C O M P O N E N T S 12 A & 12 D TIP P LE R DET E N TI O N & LA N D MAR K PL A Z A TO T I P P L E R I M P ROV E M E N T S EX PA N D E D TIP P LE R DET E N TI O N NORT H B R AN C H CA MP B EL L CRE EK S T O R MW A TE R S T U DY AD D E ND U M N O . 1 CI T Y OF O S H K O SH WI N N E B AG O C O U NT Y , W I S C O NS I N FIGURE 4.02-21-382.030 ¬ Maintain Overland Flow Routes IE = 753.61 Proposed Manhole IE = 753.52 405 LF - 12" PVC @ 0.20% Proposed Manhole IE = 752.70 70 LF - 12" PVC @ 0.20% IE = 752.84 435 LF - 12" PVC @ 0.20% 52 LF - 12" PVC @ 0.20% Proposed Manhole IE = 751.83 67 LF - 36" x 60" HERCP @ 0.25%IE = 752.00 480 LF - 12" PVC @ 0.165% Proposed Manhole IE = 752.79 IE = 752.91 110 LF - 12" PVC @ 0.10% IE = 753.52 Proposed Manhole IE = 753.45 35 LF - 12" PVC @ 0.20% 400 LF - 12" PVC @ 0.165% IE = 752.00 Normal WSEL = 752.00 754 754 754 754 754 754 753 753 752 755 3 175' Lot Depth 3 120' Additional Parking ¬ ¬ Maintain Overland Flow Routes Provide Fill to Raise Property Above Over Land Flow Route Elevations High Capacity Inlets at Low Points ¬ ¬ Football Field ¬ ¬ ALT-7 Channel Regrading and Twice Yearly Ditch Maintenance ALT-7 Twice Yearly Ditch Maintenance ALT-7 Additional 46 LF 27" RCP Parallel to Existing Storm Sewer !( Soccer Field WITZEL AVE S E A G L E S T N K O E L L E R S T BISMARCK AVE US H W Y 4 1 S O U T H B O U N D US H W Y 4 1 N O R T H B O U N D S W E S T F I E L D S T S W A S H B U R N S T W 4TH AVE W 2ND AVE N E A G L E S T N M E A D O W S T LI L A C S T N W E S T F I E L D S T MO N T I C E L L O D R p v t 0 766 76 2 764 76 0 76 8 770 758 774776 77 8 780782 784 78 6 762 764 76 4 0 0 76 2 0 76 8 76 2 764 76 4 764 0 764 76 8 75 8 76 4 76 0 0 76 2 760 766 762 0 76 2 76 4 77 0 766 00 768 76 2 76 4 770 766 76 2 76 6 77 0 762 0 0 76 4 766 0 764 762 76 8 766 762 764 764 76 0 766 764 762 762 764 766 76 4 77 0 5836 18 27 8 21 24 42 15 30 12 3658 51 3 1 36 3654 10 20 2945 2820 24 12 18 12 24 15 12 21 12 18 15 12 12 12 15 18 24 15 21 27 12 18 21 12 24 24 12 12 S:\@SAI\351--400\382\030\Data\GIS\Report Figures\Figure 4.02-2 - Alternative Expanded Tippler Detention.mxd 0 200 400100 Feet ³ Legend Storm Manhole Storm Sewer Sanitary Manhole Sanitary Sewer Water Valve Water Main Parcel Contour (2 FT.) Proposed Detention Proposed Pipe Landmark Diversion ALT-12 = Steel Plate w/Orifice 33" Inch Dia Proposed Box Culvert (320 LF) ALT-12 = 3 x 5 Proposed Box Culvert (107 LF) ALT-12 = 3 x 6 Proposed Box Culvert (420 LF) ALT-12 = 3 x 6 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-5 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 Parcel Number Area 91311840100 1.772 acres 91311870100 (existing home at north end) 1.997 acres 91311860000 4.621 acres 91311860100 3.830 acres Total 12.22 acres Table 4.02-1 Vacant Parcel Information–Component 1c 2. Expanded Detention (44.1 acre-feet) at the Armory site and upstream pipe upsizing to feed the basin (Figure 4.02-3). This component was originally proposed in the December 1994 Stormwater Management study. The 1994 study recommended this basin be sized to store 40 acre-feet for the 10- year storm and 85 acre-feet for the 100-year storm. The wet detention basin shown in Figure 4.02-1e of the original report can hold about 53 acre-feet during the 100-year storm prior to berm overtopping. To fully utilize this detention, upgrading of the upstream storm sewer system extending to the west side of USH 41 is necessary and is referred to as a diversion modification. Because of the existing ditch (navigable portion of Campbell Creek) located on the north side of this basin, we have modeled the basin at the influent to the pond with a diversion structure that would allow flow to split either into a 24-inch orifice and continue through the ditch or through a 53-inch by 83-inch HERCP pipe to the pond. This is recommended to keep base flow in the ditch and provide for aquatic and terrestrial habitat in and along the ditch. This pond is situated in an area that has been officially mapped by the City of Oshkosh as a regional stormwater detention facility. By agreement with the State of Wisconsin, there would be no associated land acquisition costs associated with the eastern portion of the pond that is located on the Armory property. However, the western portion of the property is located on private lands and would require acquisition of approximately 5 acres of land. Since the DNR has determined (per verbal c onversations with the City) that the ditch located on the north side of the proposed Armory Pond is navigable, this pond cannot be expanded to become an on-line pond extending all the way to the north property line as was previously discussed. 3. Detention (25.7 acre-feet) at West 9th Avenue and Washburn Street (Figure 4.02-4). We have analyzed the addition of detention at the vacant parcel southwest of the West 9th Avenue/ Washburn Street intersection. This area is actually four parcels. A house is currently located on one of these parcels. As shown in Table 4.02-1, the total area of these four parcels is 12.22 acres. Of this total, about 10.76 acres (504 feet x 930 feet) appears to be feasible for the footprint of a detention basin. This 10.76-acre area could conceivably provide about 35.5 acre- feet of storage assuming a wet pond configuration as shown in Figure 4.02-4. The layout shown provides for an aesthetically pleasing edge as well as an island to benefit wildlife habitat. This parcel currently appears to drain easterly toward Washburn Street. The cost shown for this component in Figure 4.02-2 is the cost for a basin approximately 15-percent larger than that shown in Figure 4.02-4 to allow for maximizing the use of the parcel for stormwater storage. ALT ER NA T I V E 12 - C O M P O N E N T 12 B ARMO R Y DET E N T IO N NORT H B R AN C H CA MP B EL L CRE EK S T O R MW A TE R S T U DY AD D E ND U M N O . 1 CI T Y OF O S H K O SH WI N N E B AG O C O U NT Y , W I S C O NS I N FIGURE 4.02-31-382.030 IE = 765.0 IE = 765.0 IE = 764.88 Normal WSEL = 765.0 100-YR WSEL = VARIES PER ALT. 60 LF - 21" RCP @ 0.2% Existing Ditch Top of Berm Elev. = 771.0 Place Steel Plate W/ 2' DIA. Orifice on Downstream Pipe (IE = 768.69) 110 LF - 53" x 83" HERCP @ 4.3%Future Road ROWFuture Road ROW Existing Armory Drainage000Existing Armory DrainageExisting Armory Drainage Upgrade Storm Sewer to 48" x 76" HERCP Total Length = 1251 LF IE = 769.69 42" Camb e l l C r e e k S K O E L L E R S T S W A S H B U R N S T US H W Y 4 1 S O U T H B O U N D US H W Y 4 1 N O R T H B O U N D MO R E L A N D S T CRYSTAL SPRINGS AVE OSBOR N A V E US H W Y 4 1 R A M P MENARD DR AR M O R Y P L DICKINSON AVE WI N D S O R S T RE I C H O W S T S W E S T F I E L D S T 77 6 77 8 774 77 2 770 780 768 762 760 758 756 754 752 750 742 782 702 700 698 766 696784786 77 4 778 77 4 77 8 77 4 77 6 778 776 778 77 4 776 778 77 4 778 77 8 78 0 772 780 77 6 778 780 778 77 6 776 78 0 77 8 77 8 780 77 6 766 778 776 776 77 4 77 4 77 6 77 6 77 6 77 4 77 8 77 4 776 77 8 784 78 2 780 774 786 774 78 0 77 6 77 6 77 8 77 2 78 0 77 8 77 6 780 768 77 8 77 4 778 77 6 77 6 77 8 778 77 8 780 77 6 77 6 778 77 4 78 0 77 8 778 77 4 778 778776 76 8 24 4815 4212 27 18 0 2438 2516 8 12 42 12 12 42 24 24 12 24 24 12 12 24 12 12 42 12 12 24 12 12 15 15 48 12 24 24 12 12 15 15 24 12 27 42 12 12 12 12 12 S:\@SAI\351--400\382\030\Data\GIS\Report Figures\Figure 4.02-3 - South Branch Detention 1A.mxd 0 200 400100 Feet ³ Legend Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer Parcel Contour (2 FT.) Proposed Detention Proposed Pipe ALTERNATIVE 12 - COMPONENT 12CDETENTION AT VACANT LOT SOUTHEAST OF 9TH/WASHBURN STREET INTERSECTION NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4 . 0 2 - 4 1- 3 82 . 0 3 0 Normal WSEL = 771.0 100-YR WSEL = 775.49 Top of Water Feature Elevation = 777.0 120' - 15" RCP @ 0.09% 238' - 18" RCP @ 0.86% 315' - 42" RCP @ 0.16% Construct New Manhole IE = 771.0 IE = 771.0 IE = 771.0 Construct New Manhole Over Existing Pipe IE = 771.49 Bulkhead Existing 42" Storm sewer to East Extra Inlets to Accept 100-YR Flow Extra Inlets to Accept 100-YR Flow FO R E B A Y FOR E B A Y 132' - 15" RCP @ 0.09% 175' - 15" RCP @ 0.09% Construct New Manhole IE = 770.62 CU M B E R L A N D T R MARICOPA DR 77 8 780 776 78 2 774 782 78 0 782 780 78 0 78 0 77 8 78 0 77 6 778 77 8 778 78 0 78 0 780 78 0 778 776 77 8 778 780 78 0 780 77 8 78 0 42 24 15 12 18 0 27 30 12 42 0 12 12 42 42 15 18 18 42 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 4 . 02 - 4 - Al terna t i v e 12 c . m x d 0 100 20050 Feet ³ Legend Storm Manhole Storm Sewer Sanitary Manhole Sanitary Sewer Water Valve Water Main Parcel Contour (2 FT.) Proposed Detention Proposed Pipe City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-6 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 4. Storm Sewer Upsizing from Landmark Plaza to Tippler (see Figure 4.02-2). a. Provision for twice-yearly maintenance (mowing and debris removal) on the first ditch segment (modeled ditch number D-AEW-11) downstream from the Diversion Point 2 outfall into Landmark Plaza to allow for a more efficient cross section (change from Manning’s “n” of 0.10 to 0.075). b. Construction of a 27-inch-diameter storm sewer culvert parallel to the existing 31-inch by 51-inch RCP (modeled node P-LP-1) just downstream from ditch D-AEW-11. c. Reconstruction and regrading of the two downstream-most ditch segments (D-LP-4 and D-LP-5) in Landmark Plaza with a cross section consisting of a 2-foot width bottom and maximum 2 H : 1 V side slopes to eliminate the current high point at node LP-5. This would also include provision for twice- yearly maintenance (mowing and debris removal) to allow for a more efficient cross section (change from Manning’s “n” of 0.10 to 0.075). d. Construction of a 33-inch-diameter orifice plate on the upstream end of the existing 3-foot by 4.5-foot RCP box that crosses USH 41 at Diversion Point 2 to reduce flows able to enter Landmark Plaza. 5. Detention basin (18.7 acre-feet) meeting County ordinances for the Agricultural Land Southeast of STH 44/N. Clay Road Intersection. Under proposed land use conditions, the land that would develop in subbasin SBB-190 would need to meet County stormwater ordinances. For this alternative and for Alternatives 13, 13 B, 14 and 16, subbasin SBB-190 is modeled under proposed landuse conditions with a pond meeting the County stormwater ordinance. The ponds are sized and modeled such that the proposed peak discharge for the 2, 10, 25, and 100-year design storms are less than or equal to the predeveloped peak discharge for the 2, 10, 25, and 100-year design storms which meets the County stormwater ordinance. This component was not previously part of the Alternative 7 analysis in the original report. Alternative 15 contemplates further restricting the peak discharge from this pond to meet City ordinances. The cost of this detention basin is not included in the costs for Alternatives 12, 13, 13B, 14, and 16 because the detention basin is simply simulating the effect of this developed land. It is likely that the land in subbasin SBB-190 will develop in two or more developments such that each of these developments would construct their own detention basins with a cumulative effect similar to the single basin that we have modeled for this subbasin. 6. Wisconsin Department of Transportation storm sewer with 50-year design storm sewer/ditch capacity along USH 41 from south of Dickinson Avenue north to Sawyer Creek along the west side of USH 41 as shown in Figure 4.02-5. However, the originally analyzed Alternative 7 in the May 2006 Stormwater Plan did not include this component. The Opinion of Probable Costs for the alternative outlined above is shown in Table 4.02-2. WISDOT 50 YEAR DESIGNSTORMWATER CONVEYANCE FACILITIES NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4 . 0 2 - 5 1- 382 . 0 3 0 Taft Ave. Witzel Ave. 9th Ave. Dickinson Ave. Alltero n D r . We s t b r o o k D r . US H 4 1 Sawyer C r e e k S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 4 . 02 - 5 - WD O T 5 0 Y e a r Des i g n. mx d 0 500 1,000250 Feet ³ Legend Drainage Basin Boundary Sub Drainage Basin Boundary Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer Modeled Pipe Sizes 36-Inch RCP 38 x 60 Inch HERCP 43 x 68 Inch HERCP 48 x 76 Inch HERCP 48-Inch RCP 53 x 83 Inch HERCP 66-Inch RCP Ditch Section City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-7 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 Item Capital Cost Component 12a–Expanded Detention at Tippler Junior High property Mobilization $5,000 Excavation 1,034,500 Riprap 3,600 Piping and Structures 112,900 Erosion Control 10,400 Landscaping/Restoration 461,500 Subtotal 1,627,900 Engineering and Contingencies (25%) 407,000 Subtotal 2,034,800 Soils Investigation $6,000 Land Acquisition (10.31 acres @ $20,000/ac) 206,200 Easements (2 @ $2,300 each) 4,600 Total $2,251,600 Component 12b–Detention at the Armory site and upstream pipe upsizing to feed the basin. Mobilization 5,000 Excavation (Includes excavation and off-site disposal of 17,000 CY of existing earthen hill) $2,313,200 Riprap 3,200 Piping and Structures 45,400 Erosion Control 11,800 Landscaping/Restoration 206,300 Upstream Pipe Upsizing and Manholes 353,700 Subtotal $2,938,600 Engineering and Contingencies (25%) 734,600 Subtotal $3,673,200 Soils Investigation 6,000 Land Acquisition (5 acres @ $653,400/acre) $3,267,000 Total $6,946,200 Component 12c–Additional Detention in Vacant Land Southwest of 9th Street/Washburn Street Intersection Excavation $1,002,900 Riprap $ 2,600 Piping and Structures 112,300 Erosion Control 14,100 Landscaping/Restoration 144,000 Subtotal $1,275,800 Engineering and Contingencies (25%) 319,000 Subtotal $1,594,800 Soils Investigation 4,000 Land Acquisition (10.76 acres @ $653,400/acre) $7,030,600 Easements (2 @ $2,300 each) $4,600 Total $8,634,000 Additional Stormwater Quality Cost For Excavation of Permanent Pool Incl/ 25% Contingency $628,500 Component 12d-Storm Sewer System Improvements from Landmark Plaza to Tippler Mobilization $5,000 3-foot by 5-foot RCP Box (325 lf) and 3-foot by 6-foot RCP Box (525 LF) 293,800 One 3-foot by 5-foot RCP Box AEW and one 3-foot by 6-foot RCP Box AEW $10,000 27-inch RCP and 27-inch AEW 6,300 100-Year Inlet Capacity on Westfield Street 7,700 Storm Sewer Junction Chamber and High Capacity Inlet at Landmark Plaza $29,100 Ditch Regrading and Restoration $29,100 34-inch orifice plate $1,100 Curb and Gutter and Asphalt Restoration $ 2,000 Subtotal $384,100 Engineering and Contingency (25%) $ 96,000 Total $479,900 Grand Total (Not including Stormwater Quality Cost for Component 12c) $18,311,700 Notes: 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 12c. All other component costs include excavation below the normal WSEL. Table 4.02-2 Alternative 12 (Formerly Alternative 7) Opinion of Probable Cost City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-8 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 The benefit of this alternative is shown in Table 4.02-3. Modeling indicates this alternative would meet the desirable 2 feet of freeboard at the eastern Landmark Plaza building for both the 100-year, 2-hour and 12-hour duration storm events. Had this infrastructure been in place during the June 10/11, 2004, storm event, the flooding volume would have been eliminated according to the model (internal flooding of Landmark Plaza inlets notwithstanding). Under a 100-year storm event, there is still some surface ponding at the parking lot inlets at Landmark Plaza and at the low point east of the eastern Landmark Plaza building. This alternative is ranked fourth for watershed-wide benefit. At the expanded Tippler Pond, our model shows that the overland flow route would not be operating under the 100-year, 2-hour and 100-year, 12-hour duration storms. Under these storms, modeling shows that there is 4.61 and 3.00 feet of freeboard, respectively, to the Tippler Administration building. Along the Landmark Plaza ditch, Alternative 12 provides an approximate 100-year capacity in the five ditch segments as well as for the culvert P-LP-1. The model shows that these five ditch segments and culvert would not reach elevations that would enter the first floor elevation of the southern Landmark Plaza building or the movie theater building after implementation of this alternative. For this alternative, the City would be able to claim TSS reductions to help meet the Phase 2 DNR requirements of 20 percent TSS reduction by March 10, 2008, and 40 percent TSS reduction by March 10, 2013, for the expanded Tippler (if the wet pond design is retained) and W. 9th Avenue/Washburn Street ponds. 4.03 ALTERNATIVE 13 Alternative 13 consists of all of the components of Alternative 12 except for the 9th and Washburn detention basin. In the place of the 9th and Washburn detention basin, this alternative includes detention at the Westhaven Golf Course and upstream diversion of stormwater to the golf course as shown in Figure 4.03-1. In addition, it includes partially expanded detention at the Armory Pond as shown in Figure 4.03-2. The partially expanded Westhaven Golf Course detention and upstream diversion as shown in Figure 4.03-1 consist of: 1. Diversion of Campbell Creek at the bend in the creek southeast of Universal Street–This diversion will divert the full capacity of a 21 inch RCP which will divert approximately 20.2 percent (17 cfs) of the peak flow coming to the diversion location for the 100-year, 12-hour storm event under proposed conditions landuse. This would leave Location Freeboard at Landmark Plaza (feet) Meets Freeboard Criteria at Landmark Plaza (out of 6) Alternative Ranking for Watershed-Wide Benefit 10-year, 2-hour w/alternative 3.24 N/A 100-year, 2-hour w/alternative 2.77 Yes 100-year, 12-hour w/alternative 3.51 Yes June 11, 2004 w/ alternative (Existing Conditions) 3.55 N/A 3 Table 4.02-3 Future Conditions Effects–Alternative 12 (Formerly Alternative 7) ALTERNTATIVE 13 - WESTHAVEN GOLF COURSEDETENTION AND UPSTREAM DIVERSION COMPONENTNORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4. 0 3 - 1 1- 3 8 2 . 0 3 0 Dickenson Ave 940' - 21" RCP @ 0.82% Existing Ditch Railroad Tracks IE = 790.51 (W) IE = 791.51 (E) IE = 775.90 570 LF - 18" RCP @ 0.016% 15" AEW EL = 775.50 For Local Drainage IE = 774.95 555 LF - 15" RCP @ 0.10% 75' Buffer IE = 776.0 IE = 776.32 IE = 778.22 (E) IE = 779.22 (N) 436.5 LF - 12" RCP @ 0.55% NWSEL = 776.00 IE = 811.23 (In Ditch) 262 LF - 24" RCP @ 2.2% 374 LF - 30" RCP @ 2.2% IE = 786.00 NWSEL = 786.00 1433.5' - 18" RCP @ 0.7% IE = 776.0 156 LF - 24" RCP @ 0.05% 10' Wide Bike Path 399 LF - 12" RCP @ 0.20% IE = 776.78 (N) IE = 777.78 (E) IE = 776.00 Unive r s a l S t S W e s t h a v e n D r Mar i c o p a D r Ma r i c o p a D r Allert o n D r Co v i n g t o n D r Cu m b e r l a n d T r a i l S W a s h b u r n S t W 20th Ave IE = 803.47 164 LF - 30" RCP @ 2.2% IE = 797.75 IE = 794.17 366 LF - 12" RCP @ 1.2% 100 YR WSEL = 791.26Top of Berm ELEV = 793.25 IE = 786.00 IE = 776.00 IE = 776.24 (S, W) IE = 777.24 (E) 553 LF - 12" RCP @ 0.045%IE = 776.13 IE = 775.65 29.4 LF - 24" RCP @ 5.4% IE = 776.00 NWSEL = 776 100 YR WSEL = 780.45 Top of Berm ELEV = 762.09 75' Buffer Provide Drainage Swale Around Berm 553 LF - 12" RCP @ 0.045% 1350' - Ditch @ 1.0% IE = 786.00 Bulkhead Existing Storm Sewer to East Power Poles (TYP.) Overhead Power Lines (TYP.) Spillway IE = 791.00 Camb e l l C r e e k Di v e r s i o n Return 42 6 24 10 12 27 1930 21 50 3 1 8 0 18 15 2516 30 15 8 30 12 18 30 42 12 18 12 8 24 8 15 12 21 15 18 12 15 12 18 8 15 30 6 30 42 15 18 2516 24 8 15 27 12 27 5031 12 12 15 15 8 8 27 21 12 8 30 15 12 12 8 12 12 10 12 12 8 12 12 24 42 8 15 15 12 12 12 12 21 15 30 27 18 15 50 3 1 12 12 15 108 8 30 12 12 10 18 12 12 128 8 8 18 8 18 12 15 18 12 15 8 8 8 15 27 18 12 812 12 30 12 0 12 12 42 18 18 18 15 12 18 18 12 24 8 8 8 12 12 18 24 12 15 8 15 15 15 8 30 8 21 15 24 12 21 12 21 12 15 8 12 15 12 30 15 21 30 18 15 12 8 15 12 15 12 15 15 18 12 18 12 27 15 12 8 8 12 12 12 21 18 12 18 15 S: \ @ S AI \ 3 5 1 - - 4 0 0 \ 3 8 2 \ 0 3 0 \ D at a \ G I S \R e p o r t F i g u r e s \ F i g u r e 4 . 0 3 - 1 - A lt e r n a t i v e 1 3 E xp a n d e d G ol f C o u r s e . m x d 0 400 800200 Feet ³ Legend Drainage Basin Boundary Parcel Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer Proposed Detention Proposed Pipe ALT ER NA T I V E 13 - C O M P O N E N T 13 B PAR TIAL L Y E X P A N D ED A R M O R Y DET E N T IO N B A S I N NORT H B R AN C H CA MP B EL L CRE EK S T O R MW A TE R S T U DY CI T Y OF O S H K O SH WI N N E B AG O C O U NT Y , W I S C O NS I N FIGURE 4.03-21-382.030 IE = 765.0 IE = 764.88 Normal WSEL = 765.0 100-YR WSEL = VARIES PER ALT. 60 LF - 21" RCP @ 0.2% Existing Ditch Top of Berm Elev. = 771.0 Place Steel Plate W/ 2' DIA. Orifice on Downstream Pipe (IE = 769.22) Future Road ROWFuture Road ROW Existing Armory Drainage000Existing Armory DrainageExisting Armory Drainage Upgrade Storm Sewer to 38" x 60" HERCP Total Length = 1370 LF IE = 768.22 42" IE = 765.0400.5' - 38"X60" HERPC @ 1.05% Camb e l l C r e e k S K O E L L E R S T S W A S H B U R N S T US H W Y 4 1 S O U T H B O U N D US H W Y 4 1 N O R T H B O U N D MO R E L A N D S T CRYSTAL SPRINGS AVE OSBOR N A V E US H W Y 4 1 R A M P MENARD DR AR M O R Y P L DICKINSON AVE WI N D S O R S T RE I C H O W S T S W E S T F I E L D S T 77 6 77 8 774 77 2 770 780 768 762 760 758 756 754 752 750 742 782 702 700 698 766 696784786 77 4 778 77 4 77 8 77 4 77 6 778 776 778 77 4 776 778 77 4 778 77 8 78 0 772 780 77 6 778 780 778 77 6 776 78 0 77 8 77 8 780 77 6 766 778 776 77 4 77 4 77 6 77 6 77 6 77 4 77 8 77 4 776 77 8 784 78 2 780 774 786 774 78 0 77 6 77 6 77 8 77 2 78 0 77 8 77 6 780 768 77 8 77 4 778 77 6 77 6 77 8 778 77 8 780 77 6 77 6 778 77 4 78 0 77 8 778 77 4 778 778776 76 8 24 4815 4212 27 18 2438 2516 8 12 42 12 12 48 42 24 24 48 12 24 24 12 12 24 12 12 42 12 12 24 12 12 15 15 48 12 24 24 12 12 15 15 24 12 27 42 12 12 48 12 12 12 S:\@SAI\351--400\382\030\Data\GIS\Report Figures\Figure 4.03-2 - Alt 13 Reduced Armory.mxd 0 200 400100 Feet ³ Legend Storm Manhole Storm Sewer Sanitary Manhole Sanitary Sewer Water Valve Water Main Parcel Contour (2 FT.) Proposed Detention City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-9 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 approximately 67 cfs continuing down Campbell Creek at the diversion location. A 1.25-foot-high berm downstream of the diversion location would be needed to assist in diverting this flow. Because the DNR has determined that this portion of Campbell Creek is navigable (through verbal conversations with the City), this diversion would invoke the need for a Chapter 30 permit for stream rerouting. It is our understanding that the City has received positive feedback from the DNR on the permitability of the stream rerouting. 2. Pond System through Westhaven Golf Course (South Pond=15.5 ac-ft, North Pond=30.2 ac-ft, Total = 45.7 ac-ft)–Figure 4.03-1 shows two detention ponds linked by an 18-inch storm sewer. The storm sewer would pass routed flows up to the 100-year storm event (modeling shows that approximately 3 inches of flow would flow through the spillway during the 100-year 12-hour storm) and appears to be preferable to a swale between the ponds because of base flow and small storm erosion issues as well as topographic constraints. To save construction cost, this storm sewer could be PVC for most of its length since it wouldn’t be subject to vehicular traffic. The overflow of the upstream pond will be a grass-lined swale with a capacity of the full 100-year flow to the upstream pond. We have preliminarily designed the two pond system to exceed the pond surface area required to obtain an 80 percent TSS reduction (based upon contributing watershed area and characteristics) per the DNR Wet Detention Basin Technical Standard. The remaining portion of the basin has been preliminarily designed as a wetland treatment system to reduce the excavation quantity for this option (i.e., no wet pond excavation in the wetland area). The wetland portion of the basin would include restored wetland microtopography that consists of depressions and mounds similar to those found in hummocky or forested wetlands. The mounds would be planted with trees and bushes conducive to prolonged submergence and wetland plants/seed. The total peak inflow to this pond system for the 100-year, 12-hour storm is 55 cfs and the outgoing peak flow from the pond system is approximately 13 cfs. The three pipes leading to the north pond both discharge flow to the pond and also act as outlet pipes once the peak has passed. The eastern outlet pipe (sloping east) from the north pond initially experiences westerly flows into the pond until the pond stages up high enough to push water back east out of the pipe. Since the ponds are receiving diverted flows consisting of base flow and most of the water quality-type design storms from Universal Street, the City could claim TSS reduction for this pond. Areas draining directly from adjacent to the golf course would also receive TSS treatment from the ponds. For cost purposes, we have assumed that ten percent of the excavated material will be able to be reused on site through site regrading. This would be confirmed during design. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-10 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 3. Storm Sewer System Tie In At Northeast Corner of Golf Course–The pond and swale system will tie back into the existing system with an 18-inch-diameter storm sewer. The peak discharge from this pipe during the 100-year, 12-hour storm is 6 cfs. 4. Park and Recreational Facilities at Westhaven Golf Course– As Figure 4.03-1 shows, portions of the Westhaven Golf Course not dedicated to stormwater storage and conveyance could be developed into a passive community park that could be converted into native prairie or low maintenance vegetated fields/woodland. We have included costs for restoration/plant-community modification outside of the pond footprint. Purchase and locating of detention in the Westhaven Golf Course provides an excellent opportunity to provide stormwater quantity and quality control in the Campbell Creek watershed in mainly a fully built out portion of the City. Not only would purchase of the golf course benefit Campbell Creek in this way, it would also provide an excellent opportunity for mainly stormwater quantity (flooding) control in the adjacent Sawyer Creek watershed by providing a location for an off-line detention basin. There may also be opportunities for stormwater quality control in the Sawyer Creek basin as well. 5. The partially Expanded Detention (30.0 acre-feet) at the Armory site and upstream pipe upsizing to feed the basin (Figure 4.03-2). This component was originally proposed in the December 1994 Stormwater Management study. The 1994 study recommended this basin be sized to store 40 acre-feet for the 10-year storm and 85 ac re-feet for the 100-year storm. The wet detention basin shown in Figure 4.02-1e of the original report can hold about 43.6 acre-feet during the 100-year storm prior to the emergency spillway being used. To fully utilize this detention, upgrading of the upstream storm sewer system extending to the west side of USH 41 is necessary and is referred to as a diversion modification. Because of the existing ditch located on the north side of this basin, we have modeled the basin at the influent to the pond with a diversion structure that would allow flow to split either into a 24-inch orifice and continue through the ditch or through a 38-inch by 60-inch HERCP pipe (set 1-foot above the invert elevation of the orifice) to the pond. This is recommended to keep base flow in the ditch and provide for aquatic and terrestrial habitat in and along the ditch. This pond is situated in an area that has been officially mapped by the City of Oshkosh as a regional stormwater detention facility. By agreement with the State of Wisconsin, there would be no associated land acquisition costs associated with the eastern portion of the pond that is located on the Armory property. Alternative 16 includes the detention west of this location which is located on private lands which would require acquisition of approximately 5 acres of land. Since the DNR has determined (per verbal conversations with the City) that the ditch located on the north side of the proposed Armory Pond is navigable, this pond cannot be expanded to become an on-line pond extending all the way to the north property line as was previously discussed. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-11 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 The Opinion of Probable Costs for the alternative outlined above is shown in Table 4.03-1. The benefit of this alternative is shown in Table 4.03-2. Modeling indicates this alternative would meet the desirable 2 feet of freeboard at the eastern Landmark Plaza building for both the 100-year, 2-hour and 12-hour duration storm events. Had this infrastructure been in place during the June 10/11, 2004, storm event, the flooding volume would have been eliminated according to the model (internal flooding of Landmark Plaza inlets notwithstanding). Under a 100-year storm event, there is still some surface ponding at the parking lot inlets at Landmark Plaza and at the low point east of the eastern Landmark Plaza building. This alternative is ranked second for watershed-wide benefit. At the expanded Tippler Pond, our model shows that the overland flow route would not be operating under the 100-year, 2-hour duration storm or the 100-year, 12-hour duration storm. Under these storms, modeling shows that there is 4.59 and 2.57 feet of freeboard, respectively, to the Tippler Administration building. Along the Landmark Plaza ditch, Alternative 13 provides an approximate 100-year capacity in the five ditch segments as well as for the culvert P-LP-1. The model shows that these five ditch segments and culvert would not reach elevations that would enter the first floor elevation of the southern Landmark Plaza building or the movie theater building after implementation of this alternative. Item Capital Cost Component 13a–Expanded Detention at Tippler Junior High property (see component 12a) $2,251,600 Component 13b–Partially Expanded Detention at Armory Site (see component 12b) $2,495,400 Component 13c–Storm Sewer System Improvements from Landmark Plaza to Tippler (see component 12d) $479,900 Component 13d-Partially Expanded Westhaven Golf Course Detention and Upstream Diversion Mobilization $10,000 Excavation and Fill 1,697,100 Riprap $6,800 Piping and Structures $380,900 Erosion Control $15,800 Landscaping/Restoration $767,900 Asphalt Multi-Use Path $196,800 Subtotal $3,075,300 Engineering and Contingency (25%) $768,800 Subtotal $3,844,200 Soils Investigation $8,000 Land Acquisition (Verbal Selling Price = $3,000,000) $3,000,000 Easements (7@$2,300) $16,100 Total $6,868,300 Additional Stormwater Quality Cost For Excavation of Permanent Pool Incl/ 25% Contingency $830,900 Grand Total $12,095,200 Notes: 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 13d. All other component costs include excavation below the normal WSEL. Table 4.03-1 Alternative 13–Opinion of Probable Cost City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-12 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 Location Freeboard at Landmark Plaza (feet) Meets Freeboard Criteria at Landmark Plaza (out of 6) Alternative Ranking for Watershed-Wide Benefit 10-year, 2-hour w/alternative 3.24 N/A 100-year, 2-hour w/alternative 2.72 Yes 100-year, 12-hour w/alternative 3.48 Yes June 11, 2004 w/alternative (Existing Conditions) 3.55 N/A 3 Table 4.03-2 Future Conditions Effects–Alternative 13 For this alternative, the City would be able to claim TSS reductions for the expanded Tippler (if the wet pond design is retained) and the Westhaven Golf Course ponds. 4.04 ALTERNATIVE 13 B Alternative 13 B consists of all of the components of Alternative 12 except for the 9th and Washburn detention basin. In the place of the 9th and Washburn detention basin, this alternative includes detention at the Westhaven Golf Course and upstream diversion of stormwater to the golf course as shown in Figure 4.04-1. All of the components of Alternative 13 B are shown in Figure 4.04-2. 1. Diversion of Campbell Creek at the bend in the creek southeast of Universal Street–This diversion will divert the full capacity of a 3-foot x 6-foot RCP box which will divert approximately 82.4 percent (70 cfs) of the peak flow coming to the diversion location for the 100-year, 12-hour storm event under proposed conditions landuse. This would leave approximately 15 cfs continuing down Campbell Creek at the diversion location–A 1.25-foot-high berm downstream of the diversion location would be needed to assist in diverting this flow. Because the DNR has determined that this portion of Campbell Creek is navigable (through verbal conversations with the City), this diversion would invoke the need for a Chapter 30 permit for stream rerouting. It is our understanding that the City has received positive feedback from the DNR on the permitability of the stream rerouting. 2. Pond System through Westhaven Golf Course (South Pond=62.8 ac-ft, North Pond=91.5 ac-ft, Total = 154.3 ac-ft)–Figure 4.04-1 shows two detention ponds linked by a 21-inch storm sewer. The storm sewer would pass routed flows up to the 100-year storm event and appears to be preferable to a swale between the ponds because of base flow and small storm erosion issues as well as topographic constraints. To save construction cost, this storm sewer could be PVC for most of its length since it wouldn’t be subject to vehicular traffic. The overflow of the upstream pond will be a grass-lined swale with a capacity of the full 100-year flow to the upstream pond. ALTERNTATIVE 13B - WESTHAVEN GOLF COURSEDETENTION AND UPSTREAM DIVERSION COMPONENT 13B4NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4. 0 4 - 1 1- 3 8 2 . 0 3 0 Dickenson Ave 940' - 3'x6' Box @ 0.83% Existing Ditch Railroad TracksIE = 791.51 Provide Inlets Along Street to Collect 100 YR Flow IE = 775.90 Bulkhead Existing Storm Sewer to East 527 LF - 24" RCP @ 0.02% 15" AEW EL = 776 For Local Drainage IE = 774.95 424 LF - 15" RCP @ 0.25% 75' Buffer IE = 776.0 IE = 776.32 Provide Inlets at Intersection to Collect 100 YR Flow Bulkhead Existing Storm Sewer to North IE = 778.91 395 LF - 43"x68" RCP @ 0.74% Provide Inlets at Low Point to Collect 100 YR Flow NWSE L = 7 7 6 100 Y R W S E L = 7 8 0 . 8 2 IE = 811.23 (In Ditch) 262 LF - 3'x6' Box @ 2.2% 355 LF - 3'x6' Box @ 3.4% IE = 782 1086' - 21" RCP @ 0.55% IE = 776.0 Bulkhead Existing Storm Sewer to East156 LF - 24"x38" RCP @ 0.05% 10' Wide Multi-use Path 347 LF - 36" RCP @ 0.27% IE = 777 IE = 776 Unive r s a l S t S W e s t h a v e n D r Mar i c o p a D r Ma r i c o p a D r Allert o n D r Co v i n g t o n D r Cu m b e r l a n d T r a i l S W a s h b u r n S t W 20th Ave IE = 803.47 164 LF - 3'x6' Box @ 2.2% IE = 797.75 IE = 794.17 383 LF - 36" DIA RCP @ 2.5% NWSEL = 782 100 YR WSEL = 796.17Top of Berm ELEV = 798.18 IE = 782 IE = 776.0 IE = 776.24 494 LF - 24"x38" RCP @ 0.05%IE = 776.12 IE = 775.65 IE = 776 Top of Berm ELEV = 782.81 75' Buffer Provide Drainage Swale Around Berm IE = 782 Bulkhead Connection to North 75' Buffer Spillway ELEV = 796 966' - Ditch @ 1.24% 494 LF - 24"x38" RCP @ 0.05% Proposed Spillway ELEV = 781.82 Wetland Microtopography Wetland Microtopography 527 LF - 24" RCP @ 0.02% Overhead Power Lines (Typ.) Power Poles (Typ.) 42 6 24 10 12 27 1930 21 50 3 1 8 0 18 15 30 15 42 15 0 812 8 8 21 27 18 27 21 12 15 30 15 24 15 8 30 1930 12 15 12 15 10 12 21 8 8 15 15 12 12 15 27 8 30 18 12 15 21 18 12 12 6 12 12 8 8 15 8 12 12 15 12 15 12 12 18 15 12 8 30 15 18 18 12 24 8 12 8 21 18 30 15 12 12 12 18 12 12 8 8 8 12 8 18 18 18 21 18 12 15 15 8 8 24 24 24 12 12 12 30 15 18 12 15 15 15 18 12 8 27 18 18 15 8 8 8 18 15 8 15 21 12 12 24 12 15 12 24 12 12 18 6 12 8 12 15 812 12 15 21 30 18 15 12 8 12 42 15 12 15 12 12 8 42 21 12 15 10 12 12 8 8 18 12 12 8 12 12 18 15 S: \ @ S AI \ 3 5 1 - - 4 0 0 \ 3 8 2 \ 0 3 0 \ D at a \ G I S \R e p o r t F i g u r e s \ F i g u r e 4 . 0 4 - 1 - A lt e r n a t i v e 1 3 B E xp a n d e d G o l f C ou r s e . m x d 0 400 800200 Feet ³ Legend Drainage Basin Boundary Parcel Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer ALTERNATIVE 13B - COMPONENTS NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4 . 0 4 - 2 1- 3 82 . 0 3 0 Tippler Detention Channel Regrading and Twice Yearly Ditch Maintenance Twice Yearly Ditch Maintenance Additional 46 LF 27" RCP Parallel to Existing Storm Sewer 33" DIA Orifice Plate Upgrade Storm Sewer to 3' x 6' Upgrade Storm Sewer to 38" x 60" HERCP Total Length = 1370 LF Armory Detention !( Upgrade Storm Sewer to 3' x 5' W 9TH AVE WITZEL AVE S W A S H B U R N S T S K O E L L E R S T US H W Y 4 1 S O U T H B O U N D US H W Y 4 1 N O R T H B O U N D MA R I C O P A D R GR E E N F I E L D T R ABBEY AVE RE I C H O W S T OSBOR N A V E W 5TH AVE ALLER T O N D R GR A C E L A N D D R US H W Y 4 1 R A M P HE R I T A G E T R S W E S T F I E L D S T VILL A P A R K D R S W E S T H A V E N D R LI L A C S T AR M O R Y P L CO V I N G T O N D R CU M B E R L A N D T R TH O R N T O N D R DE E R F I E L D D R MO R E L A N D S T GOLDEN AVE CAPITAL DR W 6TH AVE W 7TH AVE AR D M O R E T R WI N D S O R S T WE S T B R O O K D R N W E S T F I E L D S T CA M D E N L N KATY CT S W E S T F I E L D S T W 7TH AVE 0 78 2 784 778 78 6 776 77 4 79 8 79 6 794 79 0 792 78 8 80 0 770 780 768 772 766 806 764 76 0 762 758 756 75 4 75 2 750 74 8 746 74 4 74 2 74 0 734 732 730 728 71 6 714 708 706 704 702 700 698 696 804 802 81 0 808 694 76 2 780 792 774 786 780 774 77 2 786 78 0 792 0 77 6 0 784 764 77 8 0 776 77 8 784 77 2 772 772 76 2 79 0 76 2 770 776 77 0 77 8 780 76 2 778 0 792 788 77 8 77 8 76 8 774 77 4 76 0 77 6 782 0 772 706 76 8 780 778 77 6 778 77 0 776 778 780 700 80 0 78 2 780 0 78 6 790 788 76 0 0 77 4 782 778780 0 784 776 786 76 2 0 78 8 782 788 782 0 78 0 77 6 782 79 6 78 2 772 760 784 77 4 76 8 77 8 780 782 78 0 784 794 770 0 78 6 77 2 776 774 77 6 78 8 79 2 0 782 79 0 78 0 78 2 80 0 780 0 786 770 0 0 77 0 0 794 782 778 79 2 77 8 0 764 77 0 76 4 786 778 77 4 780 778 780 772 77 4 770 784 782 77 8 0 798 782 78 478 0 782 79 6 0 782 78 2 780 784 77 4 784 782 77 8 782 77 8 770 782 0 78 6 780 796 790 784 0 77 8 784 78 2 782 0 772 0 0 0 78 6 790 77 8 778 782 784 762 0 0 78 2 782 770 80 0 782 782 762 0 776 790 768 80 0 776 0 76 4 77 4 788 772 790 0 790 0 704 77 8 77 4 788 784 782 778 77 4 79 2 790 76 4 796 786 766 77 6 78 0 78 8 780 0 780 76 6 0 772 76 2 77 8 79 2 79 0 78 0 78 8 80 0 77 8 786 784 77 2 762 77 8 764 76 4 0 796 0 0 0 78 6 79 0 776 77 6 770 810 77 4 776 77 4 78 8 778 764 0 0 786 778 700 0 78 2 782 0 0 0 0 0 784 792 778 762 0 78 0 0 0 760 786 0 77 6 0 766 780 788 786 76 2 764 782 0 782 78 4 78 6 78 6 764 772 77 6 78 2 76 2 79 2 778 77 4 780 702 77 6 790 78 2 780 780 77 4 77 0 788 77 2 772 790 772 80 0 78 0 796 768 77 6 78 0 782 77 4 788 798 772 78 2 784 78 2 78 2 780 79 2 78 0 786 79 8 77 4 768 0 77 2 77 0 806 780 78 6 778 77 4 772 782 792 77 6 76 8 774 764 774 774 77 6 780 79 2 760 796 78 0 77 4 79 0 788 774 786 762 790 784 784 77 2 778 0 794 0 77 8 0 780 0 778 0 782 0 79 4 0 0 790 786 0 778 764 0 764 786 77 0 778 788 77 4 778 798 788 798 78 0 772 78 2 790 77 0 780 774 0 786 778 778 788 77 2 78 6 78 2 76 4 78 8 77 6 774 784 792 764 772 78 4 786 788 0 0 770 786 776 0 78 6 778 78 6 30 42 48 5836 24 27 2516 12 6 8 60 15 18 21 54 5031 3658 193 0 2438 51 3 1 0 1423 10 6540 12 12 27 10 12 12 15 12 18 15 12 12 24 12 21 18 12 10 18 21 8 6 21 18 27 15 18 8 8 18 18 15 21 15 24 15 27 18 12 12 12 15 8 0 12 15 6 18 15 12 12 8 15 15 6 24 12 12 12 18 27 24 12 18 18 12 12 42 15 19 3 0 8 8 12 21 12 18 12 18 8 12 30 48278 12 15 30 8 24 10 30 8 8 27 10 8 21 30 30 12 42 15 30 18 18 15 12 8 18 10 12 12 8 27 21 24 12 30 12 12 8 24 6 24 15 18 24 12 24 27 12 15 12 8 24 15 24 8 12 12 12 24 12 12 12 18 21 18 21 12 21 12 12 15 30 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 4 . 04 - 2 - Al terna t i v e 13 B Com pon e n t s . mx d 0 450 900225 Feet ³ Legend Storm Manhole Storm Sewer Culvert Sanitary Manhole Sanitary Sewer Water Valve Water Main Parcel Contour (2 FT.) Proposed Detention Proposed Pipe STH 44/Clay Rd Pond CL A Y R D STATE R D 4 4 BELLFIE L D D R 846 84 4 842 838 834 836 840 84 8 850 832 852 854 856 858 848 848 854 840 848 856 848 852 836 832 85 6 840 850 83 4 84 0850 85 2 83 6 846 84 6 844 844 836 83 6 832 842 840 850 838 840 844 854 15 18 6 8 0 600300 Feet City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-13 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 We have preliminarily designed the two pond system to exceed the pond surface area required to obtain an 80 percent TSS reduction (based upon contributing watershed area and characteristics) per the DNR Wet Detention Basin Technical Standard. The remaining portion of the basin has been preliminarily designed as a wetland treatment system to reduce the excavation quantity for this option (i.e., no wet pond excavation in the wetland area). The wetland portion of the basin would include restored wetland microtopography that consists of depressions and mounds similar to those found in hummocky or forested wetlands. The mounds would be planted with trees and shrubs conducive to prolonged submergence and wetland plants/seed. The total peak inflow to this pond system for the 100-year, 12-hour storm is 203 cfs and the outgoing peak flow from the pond system is approximately 24 cfs. There are two outlets from the pond system. The north pond outlet is a 24 inch RCP exiting at the east side of the north detention pond. The outlet pipe initially accepts a peak flow of 16 cfs into the pond prior to the pond staging up and pushing water back out to the east at 12 cfs. The south pond inlet pipe is a 36 inch RCP entering at the east side of the south detention pond. The inlet pipe initially accepts a peak flow of 15 cfs into the pond prior to the pond staging up and pushing water back out at a rate of 12 to the east to become overland flow in Maricopa Drive. During design, we recommend that all home and lot elevations surrounding the Westhaven Golf Course be surveyed and particular attention be paid to establishing adequate overland flow routes for flows potentially exceeding the 100-year storm event and/or for potential blockages of outlet structures. Since the ponds are receiving diverted flows consisting of base flow and most of the water quality-type design storms from Universal Street, the City could claim TSS reduction for this pond. Areas draining directly from adjacent to the golf course would also receive TSS treatment from the ponds. For cost purposes, we have assumed that five percent of the excavated material will be able to be reused on site through site regrading. This would be confirmed during design 3. Storm Sewer System Tie In At Northeast Corner of Golf Course–The pond and swale system will tie back into the existing system with a 24-inch-diameter storm sewer. The peak discharge from this pipe during the 100-year, 12-hour storm is 12 cfs. 4. Park and Recreational Facilities at Westhaven Golf Course–As Figure 4.04-1 shows,, portions of the Westhaven Golf Course not dedicated to stormwater storage and conveyance could be developed into a passive community park that could be converted into native prairie or low maintenance vegetated fields/woodland. We have included costs for restoration/plant-community modification outside of the pond footprint. Purchase and locating of detention in the Westhaven Golf Course provides an excellent opportunity to provide stormwater quantity and quality control in the Campbell Creek watershed in mainly a fully built out portion of the City. Not only would purchase of the golf course benefit Campbell Creek in this way, it would also provide an excellent opportunity for mainly stormwater quantity (flooding) control in the adjacent Sawyer City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-14 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 Creek watershed by providing a location for an off-line detention basin. There may also be opportunities for stormwater quality control in the Sawyer Creek basin as well. The Opinion of Probable Costs for the alternative outlined above is shown in Table 4.04-1. The benefit of this alternative is shown in Table 4.04-2. Modeling indicates this alternative would meet the desirable 2 feet of freeboard at the eastern Landmark Plaza building for both the 100-year, 2-hour and 12-hour duration storm events. Had this infrastructure been in place during the June 10/11, 2004, storm event, the flooding volume would have been eliminated according to the model (internal flooding of Landmark Plaza inlets notwithstanding). Under a 100-year storm event, there is still some surface ponding at the parking lot inlets at Landmark Plaza and at the low point east of the eastern Landmark Plaza building. This alternative is ranked second for watershed-wide benefit. At the expanded Tippler Pond, our model shows that the overland flow route would not be operating under the 100-year, 2-hour duration storm or the 100-year, 12-hour duration storm. Under these storms, modeling shows that there is 4.64 and 3.49 feet of freeboard, respectively, to the Tippler Administration building. Along the Item Capital Cost Component 13 B 1–Expanded Detention at Tippler Junior High property (see component 12a) $2,251,600 Component13 B 2–Partially Expanded Detention at Armory Site (see component 13b) $2,495,400 Component 13 B 3–Storm Sewer System Improvements from Landmark Plaza to Tippler (see component 12d) $479,900 Component 13 B 4-Fully Expanded Westhaven Golf Course Detention and Upstream Diversion Mobilization $10,000 Excavation and Fill $4,072,600 Riprap $8,800 Piping and Structures $1,160,600 Erosion Control $20,000 Landscaping/Restoration $1,216,600 Asphalt Multi-Use Path $196,800 Subtotal $6,685,400 Engineering and Contingency (25%) $1,671,300 Subtotal $8,356,700 Soils Investigation $10,000 Land Acquisition (Verbal Selling Price = $3,000,000) $3,000,000 Easements (7 @ $2300) $16,100 Total $11,382,800 Additional Stormwater Quality Cost For Excavation of Permanent Pool Incl/ 25% Contingency $1,480,300 Grand Total $16,609,700 Notes: 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 13 B 4. All other component costs include excavation below the normal WSEL. Table 4.04-1 Alternative 13 B–Opinion of Probable Cost City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-15 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 Landmark Plaza ditch, Alternative 13 B provides an approximate 100-year capacity in the five ditch segments as well as for the culvert P-LP-1. The model shows that these five ditch segments and culvert would not reach elevations that would enter the first floor elevation of the southern Landmark Plaza building or the movie theater building after implementation of this alternative. For this alternative, the City would be able to claim TSS reductions for the expanded Tippler (if the wet pond design is retained) and the Westhaven Golf Course ponds. 4.05 ALTERNATIVE 14 Alternative 14 consists of all of the components of Alternative 12 except for the 9th and Washburn detention basin. In the place of the 9th and Washburn detention basin, this alternative includes detention at the east side of the intersection of STH 44 and Waukau Avenue as shown in Figure 4.05-1. The STH 44/Waukau Ave detention basin consists of: 1. Diversion of Upstream Stormwater–A new manhole will be installed on the existing 3.5-foot-diameter storm sewer that runs adjacent to the pond. A 3.5 foot diameter storm sewer will then run to the pond. In the manhole, a 1-foot-diameter orifice will be placed on the downstream end of the manhole to restrict flows traveling along STH 44. The 1-foot-diameter orifice invert elevation will be set 2.5 feet above the invert elevation of the outgoing pipe. 2. Pond–This pond is modeled to store approximately 17.1 acre-feet of stormwater during the 100-year, 12-hour duration storm event. The peak flow during this storm event upstream of the diversion manhole is approximately 61.4 cfs while the diversion into the pond takes 59.3 cfs and 2.1 cfs continues down the mainline. Of the 59.3 cfs diverted flow into the pond, the peak flow downstream of the pond after discharge back into the mainline is approximately 7.7 cfs for an approximate 87 percent reduction in peak flow at this location for this storm event. The pond is located on two existing commercial lots, one of which has an existing business and buildings on it. Costs are included for demolition of the buildings. It is recommended that the City perform a Phase I environmental assessment on the properties to determine if there are any environmental issues on the properties. Location Freeboard at Landmark Plaza (feet) Meets Freeboard Criteria at Landmark Plaza (out of 6) Alternative Ranking for Watershed-Wide Benefit 10-year, 2-hour w/alternative 3.24 N/A 100-year, 2-hour w/alternative 2.75 Yes 100-year, 12-hour w/alternative 3.49 Yes June 11, 2004 w/ alternative (Existing Conditions) 3.55 N/A 2 Table 4.04-2 Future Conditions Effects–Alternative 13 B ALTERNTATIVE 14 - STH 44/W WAUKAU AVEDETENTION COMPONENTNORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO.1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4. 0 5 - 1 1- 3 8 2 . 0 3 0 70 LF - 12" RCP @ 0.33% New Manhole (IE = 830.37) w/12" Orfice @ IE = 832.86 90 LF - 42" RCP @ 0.41% Top of Berm EL = 837.0 50 LF - 24" RCP Normal WSEL = 830.0 100-YR WSEL = 835.84 IE = 830.0IE = 830.0 IE = 830.0 Connect to Existing Storm Sewer IE = 829.77 Pond Spillway Remove Existing 10" Sanitary Sewer Buildings to be Demolished Buildings to be Demolished Reroute 10" Sanitary Sewer 940 LF @ 0.28% Remove Existing 10" Sanitary Sewer Ca m b e l l C r e e k STATE R D 4 4 W WAUKAU AVE BE L L F I E L D D R 848 850 834 852 832 840 842 838 844 836 846 84 0 844 840 84 0 834 836 838 844 844 84 6 84 2 836 84 0 836 838 844 836 848 838 840 842 844 84 2 842 838 840 834 838 840 84 0 832 832 838 836 838 842 838 844 844 SBB-140 SBB-180 SBB-175 SBB-170 SBB-165 SBB-150 SBB-185 SBB-135 SBB-160 SBB-176 15 42 18 12 24 8 12 24 24 12 12 12 12 15 12 24 24 12 42 24 12 24 42 42 42 42 S: \ @ S AI \ 3 5 1 - - 4 0 0 \ 3 8 2 \ 0 3 0 \ D at a \ G I S \R e p o r t F i g u r e s \ F i g u r e 4 . 0 5 - 1 - A lt e r n a t i v e 1 4 S TH 4 4 & W W au k a u A ve . m x d 0 100 20050 Feet ³ Legend Drainage Basin Boundary Sub Drainage Basin Boundary Parcel Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer Contour (2 FT.) Proposed Detention Proposed Pipe City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-16 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 3. Sanitary Sewer Diversion–There is currently a 10-inch-diameter sanitary sewer running between the two lots that this pond is located on. Thus, this pond will require rerouting of this sanitary sewer around the pond as shown in Figure 4.04-1 at the minimum slope allowed by the DNR of 0.28 percent for a 10-inch diameter pipe. It appears that this is possible when looking at invert elevations from the City’s GIS layer. The Opinion of Probable Costs for the alternative outlined above is shown in Table 4.05-1. The benefit of this alternative is shown in Table 4.05-2. Modeling indicates this alternative would meet the desirable 2 feet of freeboard at the eastern Landmark Plaza building for both the 100-year, 2-hour and 12-hour duration storm events. Had this infrastructure been in place during the June 10/11, 2004, storm event, the flooding volume would have been eliminated according to the model (internal flooding of Landmark Plaza inlets notwithstanding). Under a 100-year storm event, there is still some surface ponding at the parking lot inlets at Landmark Plaza and at the low point east of the eastern Landmark Plaza building. This alternative is ranked fifth for watershed-wide benefit. At the expanded Tippler Pond, our model shows that the overland flow route would not be operating under the 100-year, 2-hour Item Capital Cost Component 14a–Expanded Detention at Tippler Junior High property (see component 12a) $2,251,600 Component 14b–Fully Expanded Detention at Armory Site (see component 12b) $6,946,200 Component 14c–Storm Sewer System Improvements from Landmark Plaza to Tippler (see component 12d) $479,900 Component 14d-STH 44/Waukau Ave. Detention Basin Mobilization $5,000 Excavation and Fill $590,700 Riprap $13,200 Piping and Structures $37,700 Erosion Control $6,000 Landscaping/Restoration $102,100 Sanitary Sewer Rerouting $42,700 Building Demolition $20,000 Subtotal $817,300 Engineering and Contingency (25%) $204,300 Subtotal $1,021,600 Soils Investigation $4,500 Land Acquisition (5.05 acres @ $653,400/acre) $3,299,700 Total $4,325,800 Additional Stormwater Quality Cost For Excavation of Permanent Pool Incl/ 25% Contingency $269,600 Grand Total $14,003,500 Notes: 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 14d. All other component costs include excavation below the normal WSEL. Table 4.05-1 Alternative 14–Opinion of Probable Cost City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-17 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 or the 100-year, 12-hour duration storm. Under these storms, modeling shows that there is 4.66 and 3.11 feet of freeboard, respectively, to the Tippler Administration building. Along the Landmark Plaza ditch, Alternative 14 provides an approximate 100-year capacity in the five ditch segments as well as for the culvert P-LP-1. The model shows that these five ditch segments and culvert would not reach elevations that would enter the first floor elevation of the southern Landmark Plaza building or the movie theater building after implementation of this alternative. For this alternative, the City would be able to claim TSS reductions for the expanded Tippler (if the wet pond design is retained) and the STH 44/Waukau detention ponds 4.06 ALTERNATIVE 15 Alternative 15 consists of all of the components of Alternative 12 except for the 9th and Washburn detention basin and Component 5. In the place of the 9th and Washburn detention basin, this alternative includes detention southeast of the STH 44/N. Clay Road intersection as shown in Figure 4.06-1. As discussed above, Alternatives 12, 13, 13B, 14, and 16 include Component 5 which is a detention basin in this location sized to meet the Winnebago County stormwater ordinance. In Alternative 15, we are looking at further reducing the peak discharge from the pond in the 2-, 10-, 25-, and 100-year design storm events to meet the City stormwater ordinance. This will pond water to a higher elevation in this pond as well as to a greater footprint. The STH 44/North Clay Road detention basin consists of collection of upstream water in a crescent shaped pond prior to discharge into the downstream wetland. For modeling purposes, we have designed the outlet as a single pipe at the north end of the pond. However, during design of this pond we recommend that the crescent shaped pond include three separate cells with three separate outlets to help maintain baseflow along the wetland into which the pond discharges. This pond has a modeled total storage capacity of 37.2 acre-feet for the 100-year, 12-hour duration storm event. If the City were to construct this pond, the City could charge the cost of this pond back to the upstream developer’s to assist them in meeting the City stormwater ordinance requirements in a regional detention basin arrangement. Since approximately 156.5 acres drain to this pond and the pond cost is $1,858,500 the City could conceivably charge the cost of the detention basin to the upstream developers at a rate of about $11,875 per acre of developed land. Should this basin be built and treat Location Freeboard at Landmark Plaza (feet) Meets Freeboard Criteria at Landmark Plaza (out of 6) Alternative Ranking for Watershed-Wide Benefit 10-year, 2-hour w/alternative 3.24 N/A 100-year, 2-hour w/alternative 2.73 Yes 100-year, 12-hour w/alternative 3.48 Yes June 11, 2004 w/ alternative (Existing Conditions) 3.55 N/A 5 Table 4.05-2 Future Conditions Effects–Alternative 14 ALTERNTATIVE 15 - EXPANDED DETENTION BASINSE OF STH 44/N CLAY RD INTERSECTION COMPONENTNORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO.1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4. 0 6 - 1 1- 3 8 2 . 0 3 0 85' - 21" RCP @ 0.25% Extents of 100-YR WSEL in Alternatives 100-YR WSEL = 838.9 Top of Berm EL = 840.0 Provide Spillway @ EL = 839.0 Cl a y R d Proposed Property Aquisition STATE R D 4 4 BELLFIE L D D R 844 85 0 852 84 8 846 842 854 856 834 83 6 858 860 832 838 862 840 844 832 85 4 838 840 836 844 83 2 838 844 836 834 842 840 85 0 848 850 848 85 0 83 6 852 83 4 848 846 854 85 0 838 846 836 860 85 2 832 840 SBB-190 SBB-175 SBB-176 SBB-185 SBB-180 15 8 12 12 1212 12 S: \ @ S AI \ 3 5 1 - - 4 0 0 \ 3 8 2 \ 0 3 0 \ D at a \ G I S \R e p o r t F i g u r e s \ F i g u r e 4 . 0 6 - 1 - A lt e r n a t i v e 1 5 S TH 4 4 & N C la y R d. m x d 0 200 400100 Feet ³ Legend Drainage Basin Boundary Sub Drainage Basin Boundary Parcel Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer Contour (2 FT.) Proposed Detention Proposed Pipe City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-18 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 agricultural land for many years prior to upstream development actually occurring, the City should pay close attention to maintenance and possible swale or buffer pretreatment of the flows from upstream lands so that this basin doesn’t fill up with sediment prematurely. The Opinion of Probable Costs for the alternative outlined above is shown in Table 4.06-1. The benefit of this alternative is shown in Table 4.06-2. Modeling indicates this alternative would meet the desirable 2 feet of freeboard at the eastern Landmark Plaza building for both the 100-year, 2-hour and 12-hour duration storm events. Had this infrastructure been in place during the June 10/11, 2004, storm event, the flooding volume would have been eliminated according to the model (internal flooding of Landmark Plaza inlets notwithstanding). Under a 100-year storm event, there is still some surface ponding at the parking lot inlets at Landmark Plaza and at the low point east of the eastern Landmark Plaza building. This alternative is ranked fourth for watershed-wide benefit. At the expanded Tippler Pond, our model shows that the overland flow route would not be operating under the 100-year, 2-hour, and 100-year, 12-hour duration storm events. Under these storms, modeling shows that there is 4.63 and 2.66 feet of freeboard, respectively, to the Tippler Administration building. Along the Landmark Plaza ditch, Alternative 15 provides an approximate 100-year capacity in the five ditch segments as well as for the culvert P-LP-1. The model shows that these five ditch segments and culvert would not Item Capital Cost Component 15a–Expanded Detention at Tippler Junior High property (see component 12a) $2,251,600 Component 15b–Fully Expanded Detention at Armory Site (see component 12b) $6,946,200 Component 15c–Storm Sewer System Improvements from Landmark Plaza to Tippler (see component 12d) $479,900 Component 15d-Expanded Detention Southeast of STH 44/N. Clay Road Mobilization $5,000 Excavation and Fill 393,300 Riprap $38,800 Piping and Structures $17,600 Erosion Control $15,000 Landscaping and Restoration $270,200 Subtotal $739,900 Engineering and Contingency (25%) $185,000 Subtotal $924,900 Soils Investigation $5,000 Land Acquisition (22.9 acres @ $20,000/acre) $458,000 Easements (1 @ $2,300) $2,300 Total $1,390,200 Additional Stormwater Quality Cost For Excavation of Permanent Pool Incl/ 25% Contingency $468,300 Grand Total $11,067,900 Notes: 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 15d. All other component costs include excavation below the normal WSEL. Table 4.06-1 Alternative 15–Opinion of Probable Cost City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-19 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 reach elevations that would enter the first floor elevation of the southern Landmark Plaza building or the movie theater building after implementation of this alternative. For this alternative, the City would be able to claim TSS reductions for the expanded Tippler (if the wet pond design is retained). The STH 44/Clay Road pond would not gain the City any TSS reduction credit since the land upstream of the pond is currently undeveloped. 4.07 ALTERNATIVE 16 Alternative 16 consists of all of the components of Alternative 12 except for the 9th and Washburn detention basin. In the place of the 9th and Washburn detention basin, this alternative includes detention at the Westhaven Golf Course and upstream diversion of stormwater to the golf course as shown in Figure 4.07-1. The Westhaven Golf Course detention and upstream diversion consist of: 1. Diversion of Campbell Creek at the bend in the creek southeast of Universal Street–This diversion will divert the full capacity of a 3-foot x 6-foot RCP box which will divert approximately 82.5 percent (70 cfs) of the peak flow coming to the diversion location for the 100-year, 12-hour storm event under proposed conditions landuse. This would leave approximately 15 cfs continuing down Campbell Creek at the diversion location. A 1.25-foot-high berm downstream of the diversion location would be needed to assist in diverting this flow. Because the DNR has determined that this portion of Campbell Creek is navigable (through verbal conversations with the City), this diversion would invoke the need for a Chapter 30 permit for stream rerouting. It is our understanding that the City has received positive feedback from the DNR on the permitability of the stream rerouting. 2. Pond System through Westhaven Golf Course (South Pond=62.8 ac-ft, North Pond=91.8 ac-ft, Total = 154.6 ac-ft)–Figure 4.07-1 shows two detention ponds linked by a 21-inch storm sewer. The storm sewer would pass routed flows up to the 100-year storm event and appears to be preferable to a swale between the ponds because of base flow and small storm erosion issues as well as topographic constraints. To save construction cost, this storm sewer could be PVC for most of its length since it wouldn’t be subject to Location Freeboard at Landmark Plaza (feet) Meets Freeboard Criteria at Landmark Plaza (out of 6) Alternative Ranking for Watershed-Wide Benefit 10-year, 2-hour w/alternative 3.24 N/A 100-year, 2-hour w/alternative 2.74 Yes 100-year, 12-hour w/alternative 3.49 Yes June 11, 2004 w/ alternative (Existing Conditions) 3.55 N/A 6 Table 4.06-2 Future Conditions Effects–Alternative 15 ALTERNTATIVE 16 - WESTHAVEN GOLF COURSEDETENTION AND UPSTREAM DIVERSION COMPONENTNORTH BRANCH CAMPBELL CREEK STORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4. 0 7 - 1 1- 3 8 2 . 0 3 0 Dickenson Ave 940' - 3'x6' Box @ 0.83% Existing Ditch Railroad TracksIE = 791.51 Provide Inlets Along Street to Collect 100 YR Flow IE = 775.90 Bulkhead Existing Storm Sewer to East 527 LF - 24" RCP @ 0.02% 15" AEW EL = 776 For Local Drainage IE = 774.95 424 LF - 15" RCP @ 0.25% 75' Buffer IE = 776.0 IE = 776.32 Provide Inlets at Intersection to Collect 100 YR Flow Bulkhead Existing Storm Sewer to North IE = 778.91 395 LF - 43"x68" RCP @ 0.74% Provide Inlets at Low Point to Collect 100 YR Flow NWSE L = 7 7 6 100 Y R W S E L = 7 8 0 . 8 5 IE = 811.23 (In Ditch) 262 LF - 3'x6' Box @ 2.2% 355 LF - 3'x6' Box @ 3.4% IE = 782 1086' - 21" RCP @ 0.55% IE = 776.0 Bulkhead Existing Storm Sewer to East156 LF - 24"x38" RCP @ 0.05% 10' Wide Bike Path 347 LF - 36" RCP @ 0.27% IE = 777 IE = 776 Unive r s a l S t S W e s t h a v e n D r Ma r i c o p a D r Ma r i c o p a D r Allert o n D r Co v i n g t o n D r Cu m b e r l a n d T r a i l S W a s h b u r n S t W 20th Ave IE = 803.47 164 LF - 3'x6' Box @ 2.2% IE = 797.75 IE = 794.17 383 LF - 36" DIA RCP @ 2.5% NWSEL = 782 100 YR WSEL = 796.18Top of Berm ELEV = 798.18 IE = 782 IE = 776.0 IE = 776.24 494 LF - 24"x38" RCP @ 0.05%IE = 776.12 IE = 775.65 IE = 776 Top of Berm ELEV = 782.81 75' Buffer Provide Drainage Swale Around Berm IE = 782 Bulkhead Connection to North 75' Buffer Spillway ELEV = 796 966' - Ditch @ 1.24% 494 LF - 24"x38" RCP @ 0.05% Proposed Spillway ELEV = 781.85 Wetland Microtopography Wetland Microtopography 527 LF - 24" RCP @ 0.02% Power Poles (TYP.) Overhead Power Lines (TYP.) 42 6 24 10 12 27 1930 21 50 3 1 8 0 18 15 30 15 42 15 0 812 8 8 27 18 27 21 12 15 30 15 24 15 18 8 30 1930 12 15 12 15 10 12 21 8 8 15 15 12 12 15 27 8 30 18 12 15 21 18 12 12 6 12 12 8 8 15 8 12 12 15 12 15 12 12 18 15 12 8 30 15 18 18 12 24 8 12 8 21 18 30 15 12 12 12 18 12 12 8 8 8 12 8 18 18 18 21 18 12 15 15 8 8 24 24 24 12 12 12 30 15 18 12 15 15 15 18 12 8 27 18 18 15 8 8 8 18 15 8 15 12 12 24 12 15 12 24 12 12 18 6 12 8 12 15 812 12 15 21 30 18 15 12 8 12 42 15 12 15 12 12 8 42 12 15 12 12 8 8 18 12 12 8 12 12 18 15 S: \ @ S AI \ 3 5 1 - - 4 0 0 \ 3 8 2 \ 0 3 0 \ D at a \ G I S \R e p o r t F i g u r e s \ F i g u r e 4 . 0 7 - 1 - A lt e r n a t i v e 1 6 E xp a n d e d G ol f C o u r s e . m x d 0 400 800200 Feet ³ Legend Drainage Basin Boundary Parcel Storm Manhole Storm Sewer Culvert Water Valve Water Main Sanitary Manhole Sanitary Sewer Proposed Detention City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-20 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 vehicular traffic. The overflow of the upstream pond will be a grass-lined swale with a capacity of the full 100-year flow to the upstream pond. We have preliminarily designed the two pond system to exceed the pond surface area required to obtain an 80 percent TSS reduction (based upon contributing watershed area and characteristics) per the DNR Wet Detention Basin Technical Standard. The remaining portion of the basin has been preliminarily designed as a wetland treatment system to reduce the excavation quantity for this option (i.e., no wet pond excavation in the wetland area). The wetland portion of the basin would include restored wetland microtopography that consists of depressions and mounds similar to those found in hummocky or forested wetlands. The mounds would be planted with trees and shrubs conducive to prolonged submergence and wetland plants/seed. The total peak inflow to this pond system for the 100-year, 12-hour storm is 203 cfs and the outgoing peak flow from the pond system is approximately 24 cfs. There are two outlets from the pond system. The north pond outlet is a 24-inch RCP exiting at the east side of the north detention pond. The outlet pipe initially accepts a peak flow of 16 cfs into the pond prior to the pond staging up and pushing water back out to the east at 12 cfs. The south pond inlet pipe is a 36 inch RCP entering at the east side of the south detention pond. The inlet pipe initially accepts a peak flow of 15 cfs into the pond prior to the pond staging up and pushing water back out at a rate of 12 to the east to become overland flow in Maricopa Drive. During design, we recommend that all home and lot elevations surrounding the Westhaven Golf Course be surveyed and particular attention be paid to establishing adequate overland flow routes for flows potentially exceeding the 100-year storm event and/or for potential blockages of outlet structures. Since the ponds are receiving diverted flows consisting of base flow and most of the water quality-type design storms from Universal Street, the City could claim TSS reduction for this pond. Areas draining directly from adjacent to the golf course would also receive TSS treatment from the ponds. For cost purposes, we have assumed that five percent of the excavated material will be able to be reused on site through site regrading. This would be confirmed during design 3. Storm Sewer System Tie In At Northeast Corner of Golf Course–The pond and swale system will tie back into the existing system with a 24-inch-diameter storm sewer. The peak discharge from this pipe during the 100-year, 12-hour storm is 12 cfs. 4. Park and Recreational Facilities at Westhaven Golf Course–As Figure 4.07-1 shows, portions of the Westhaven Golf Course not dedicated to stormwater storage and conveyance could be developed into a passive community park that could be converted into native prairie or low maintenance vegetated fields/woodland. We have included costs for restoration/plant-community modification outside of the pond footprint. Purchase and locating of detention in the Westhaven Golf Course provides an excellent opportunity to provide stormwater quantity and quality control in the Campbell Creek City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-21 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022508 watershed in mainly a fully built out portion of the City. Not only would purchase of the golf course benefit Campbell Creek in this way, it would also provide an excellent opportunity for mainly stormwater quantity (flooding) control in the adjacent Sawyer Creek watershed by providing a location for an off-line detention basin. There may also be opportunities for stormwater quality control in the Sawyer Creek basin as well. The Opinion of Probable Costs for the alternative outlined above is shown in Table 4.07-1. The benefit of this alternative is shown in Table 4.07-2. Modeling indicates this alternative would meet the desirable 2 feet of freeboard at the eastern Landmark Plaza building for both the 100-year, 2-hour and 12-hour duration storm events. Had this infrastructure been in place during the June 10/11, 2004, storm event, the flooding volume would have been eliminated according to the model (internal flooding of Landmark Plaza inlets notwithstanding). Under a 100-year storm event, there is still some surface ponding at the parking lot inlets at Landmark Plaza and at the low point east of the eastern Landmark Plaza building. This alternative is ranked first for watershed-wide benefit. At the expanded Tippler Pond, our model shows that the overland flow route would not be operating under the 100-year, 2-hour duration storm or the 100-year, 12-hour duration storm. Under these storms, modeling shows that there Item Capital Cost Component 16a–Expanded Detention at Tippler Junior High property (see component 12a) $2,251,600 Component 16b–Fully Expanded Detention at Armory Site (see component 12b) $6,946,200 Component 16c–Storm Sewer System Improvements from Landmark Plaza to Tippler (see component 12d) $479,900 Component 16d-Fully Expanded Westhaven Golf Course Detention and Upstream Diversion Mobilization $10,000 Excavation and Fill $4,072,600 Riprap $8,800 Piping and Structures $1,160,600 Erosion Control $20,000 Landscaping/Restoration $1,216,600 Asphalt Multi-Use Path 196,800 Subtotal $6,685,400 Engineering and Contingency (25%) $1,671,300 Subtotal $8,356,700 Soils Investigation $10,000 Land Acquisition (Verbal Selling Price = $3,000,000) $3,000,000 Easements (7 @ $2300) $16,100 Total $11,382,800 Additional Stormwater Quality Cost For Excavation of Permanent Pool Incl/ 25% Contingency $1,480,300 Grand Total $21,060,500 Notes: 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 16d. All other component costs include excavation below the normal WSEL. Table 4.07-1 Alternative 16–Opinion of Probable Cost City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-22 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 is 4.68 and 3.69 feet of freeboard, respectively, to the Tippler Administration building. Along the Landmark Plaza ditch, Alternative 13 provides an approximate 100-year capacity in the five ditch segments as well as for the culvert P-LP-1. The model shows that these five ditch segments and culvert would not reach elevations that would enter the first floor elevation of the southern Landmark Plaza building or the movie theater building after implementation of this alternative. For this alternative, the City would be able to claim TSS reductions for the expanded Tippler (if the wet pond design is retained) and the Westhaven Golf Course ponds. 4.08 SUMMARY OF ALTERNATIVES AND ALTERNATIVES ANALYSIS Table 4.08-1 summarizes the alternatives discussed in Sections 4.02 through 4.07. Table 4.08-2 provides the ranking data and Table 4.08-3 provides the ranking criteria. For comparison purposes, during the 100-year, 12-hour duration storm event under existing conditions, modeling shows that the volume of ponding in the system is approximately 240.5 acre-feet (basically street and other property flooding). For the alternatives considered, modeling shows that this volume of ponding in the system (other than that at detention basins) ranges from 101.1 acre-feet (Alternative 12) to 221.5 acre-feet (Alternative 16). As can be seen, there is a substantial decrease in street flooding in each of the alternatives considered basically through the addition of detention and the new WisDOT storm sewer along USH 41. To arrive at a recommendation after assessment of these five alternatives, we have used the following criteria. Select the most cost-effective alternative that meets the following criteria. 1. Meets Landmark Plaza Flooding Criteria (2 feet or greater freeboard) for the 2-hour and 12-hour duration, 100-year storm events. All options meet this criteria. 2. Meets Tippler Flooding Criteria (2 feet or greater freeboard) for the 2-hour and 12-hour duration, 100-year storm events. All options meet this criteria. 3. Is in the top three for watershed-wide benefit ranking. Alternatives 16, 13 B, and 13 are in the top three for watershed-wide ranking. Location Freeboard at Landmark Plaza (feet) Meets Freeboard Criteria at Landmark Plaza (out of 6) Alternative Ranking for Watershed-Wide Benefit 10-year, 2-hour w/alternative 3.24 N/A 100-year, 2-hour w/alternative 2.76 Yes 100-year, 12-hour w/alternative 3.50 Yes June 11, 2004 w/ alternative (Existing Conditions) 3.55 N/A 1 Table 4.07-2 Future Conditions Effects–Alternative 16 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan- Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® Page 1 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 4.08-1.doc\022608 TABLE 4.08-1 SUMMARY OF ALTERNATIVES (INCLUDING LAND ACQUISITION COSTS AND 25 PERCENT ENGINEERING AND CONTINGENCY) Alt Alternative Description Watershed wide Benefit Rank Meets Landmark Plaza and Tippler Criteria City Storage Provided (acre-feet) Opinion of Probable Cost* Cost per Acre- Foot of Storage Provided 12 Alt. 12 (Formerly Alt. 7) 4 Yes 101.1 $18,311,700 $181,100 13 Alt. 13–Incl/Partially Expanded Westhaven Golf Course Detention and Partially Expanded Armory Pond 3 Yes 113.9 $12,095,200 $106,200 13 B Alt. 13 B–Incl/Fully Expanded Westhaven Golf Course and Partially Expanded Armory Pond 2 Yes 215.1 $16,609,700 $77,200 14 Alt. 14–Incl/STH 44/Waukau Detention 5 Yes 98.5 $14,003,500 $142,200 15 Alt. 15–Incl/STH 44/Clay Road Detention 6 Yes 110.2 $11,067,900 $100,400 16 Alt. 16–Incl/Fully Expanded Westhaven Golf Course and Fully Expanded Armory Pond 1 Yes 221.5 $21,060,500 $95,100 * Costs do not include stormwater quality component costs. See individual Alternative paragraphs in Section 4 for stormwater quality component cost breakdowns. * Alternative 7 originally didn’t account for the proposed 50-year Design WisDOT Storm Sewer/Ditch along USH 41. * All Alternatives are considered equal (within 0.05 feet) for freeboard at Landmark Plaza with all Alternatives having between 2.72 feet and 2.77 feet of freeboard as modeled under the 2-hour duration, 100-year storm event. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan- Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® Page 2 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 4.08-1.doc\022608 Alternative 12 13 13 B 14 15 16 Detention at Tippler Junior High (previously considered in Alts. 1 and 5) No No No No No No Expanded Detention at Tippler Junior High Yes Yes Yes Yes Yes Yes Larger Pipe from Landmark Plaza to Tippler Yes Yes Yes Yes Yes Yes Detention South of Landmark Plaza (previously considered in Alts. 1 and 5) No No No No No No Existing Detention at Armory (previously considered in Alts. 2 and 4) No No No No No No Partially Expanded Detention at Armory No Yes Yes No No No Fully Expanded Detention at Armory Yes No No Yes Yes Yes Detention at 9th Avenue/Washburn Street Yes No No No No No Existing Westhaven Golf Course Detention Yes No No Yes Yes No Original Westhaven Expanded Golf Course Detention (previously considered in Alts. 3, 8, 9, 10, and 11) No No No No No No Partially Expanded Westhaven Golf Course Ponds (2 Wet Ponds) No Yes No No No No Fully Expanded Westhaven Golf Course Ponds (2 Wet Ponds) No No Yes No No Yes Pump Station at Campbell Creek Outfall (previously considered in Alt. 4) No No No No No No Diversion Pipe under Hwy 41 at Landmark Plaza Yes Yes Yes Yes Yes Yes 100-year storm sewer in WisDOT ROW from Landmark Plaza Diversion to Sawyer Creek along USH 41 (previously considered in Alt. 6, 8, and 10) No No No No No No Existing Wal-Mart Detention Yes Yes Yes Yes Yes Yes Increase Conveyance Capacity from Landmark Plaza to Campbell Creek Outfall (previously considered in Alt. 2) No No No No No No Increase Internal Conveyance Capacity at Landmark Plaza (previously considered in Alt. 2) No No No No No No Modified Diversion Pipe under Hwy 41 at Landmark Plaza (previously considered in Alt. 3) No No No No No No Detention at Southeast Corner of STH 44/W. Waukau Avenue Intersection (Wet Pond) No No No Yes No No Detention basin meeting County ordinances for the Agricultural Land Southeast of STH 44/North Clay Road Intersection. Yes Yes Yes Yes No Yes Expanded Detention Basin In Agricultural Land Southeast of STH 44/North Clay Road Intersection(Wet Pond) meeting City stormwater ordinances No No No No Yes No 50-Year Design Storm Sewer/Ditch Capacity along USH 41 by WisDOT Yes Yes Yes Yes Yes Yes City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Engineering Analysis Prepared by Strand Associates, Inc.® Page 1 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 4.08-2.doc\022608 TABLE 4.08-2 SUMMARY OF EFFECTS–RANKING DATA AP-1 - exist for Alts 2 and 4 and Existing Golf Course Pond in Alts Want 2 feet freeboard (759.31)for baseline 1, 2, 4, and 5 and baseline North Branch Campbell Creek Stormwater Management Plan Want 1.5 feet freeboard min.(759.81)also in 6 and 7 780 City of Oshkosh Want 1.5 feet freeboard min (760.78) Pond Overflow Elev. = 758.7 WM P-1 SBD A-1C WNWPOND WSWPOND Waukau MAW 2-25-2008 Want 2 feet freeboard (760.28) Tippler (S.) 1st Floor = 762.35 @13-550 MOON LMP Building 1st Floor = 762.28 Tippler (N.) 1st Floor = 761.31 Top of Berm Elevation = 770 Top of Berm Elevation = 771 Top of Berm Elevation = 777 Top of Berm Elevation = 782 Top of Berm Elevation = 797 Top of Berm = 837 Top of Berm = 840.00 (all future conditions except June 11, 2004 which is 20% higher RCNs with Existing RCNs)100-Year 100-Year 100-Year 100-Year 100-Year 100-Year 100-Year 100-Year 100-Year High Flooding Acceptable High Flooding Acceptable High Flooding Acceptable High Flooding Acceptable High Flooding Acceptable High Flooding Acceptable High Flooding Acceptable High Flooding Acceptable High Flooding Acceptable Water El. Volume Flooding Water El. Volume Flooding Water El. Volume Flooding Water El. Volume Flooding Water El. Volume Flooding Water El. Volume Flooding Water El. Volume Flooding Water El. Volume Flooding Water El. Volume Flooding Location (feet) (ac-ft) Elevation (feet) (ac-ft) Elevation (feet) (ac-ft)Elevation (feet) (ac-ft) Elevation (feet) (ac-ft) Elevation (feet) (ac-ft) Elevation (feet) (ac-ft) Elevation (feet) (ac-ft) Elevation (feet) (ac-ft) Elevation Alternative 12 (Formerly Alt 7)) 10-year, 2 hour w/Alternative 759.04 0.00 760.78 754.32 7.01 759.81 766.18 2.20 770.00 767.03 16.79 771.00 772.13 6.02 777.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A 834.34 7.56 840.00 100-year, 2 hour w/Alternative 759.51 0.01 760.78 756.45 22.62 759.81 769.09 5.94 770.00 768.45 29.29 771.00 773.74 15.12 777.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A 835.64 14.21 840.00 100-year 12 Hour w/ Alternative 758.77 0.00 760.78 757.52 31.32 759.81 768.73 5.48 770.00 770.05 44.06 771.00 775.49 25.73 777.00 N/A 0.00 N/A N/A 0.00 N/A N/A 0.00 N/A 836.42 18.68 840.00 June 11, 2004 w/ Alternative 758.73 0.00 760.78 756.55 23.43 759.81 767.83 4.33 770.00 769.58 39.66 771.00 775.10 23.35 777.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A 836.16 17.07 840.00 Alternative 13 B (Westhaven Golf Course Partially Expanded) 10-year, 2 hour w/Alternative 759.04 0.00 760.78 754.55 8.46 759.81 766.30 2.34 770.00 766.88 11.07 771.00 N/A N/A N/A 778.02 12.64 782.00 788.20 6.04 797.00 N/A N/A N/A 834.34 7.56 840.00 100-year, 2 hour w/Alternative 759.56 0.01 760.78 756.70 24.65 759.81 769.17 6.01 770.00 768.29 19.81 771.00 N/A N/A N/A 779.11 20.20 782.00 790.00 11.44 797.00 N/A N/A N/A 835.64 14.21 840.00 100-year, 12 hour w/Alternative 758.80 0.00 760.78 758.32 38.15 759.81 769.88 6.36 770.00 769.86 29.98 771.00 N/A 0.00 N/A 780.45 30.23 782.00 791.26 15.50 797.00 N/A 0.00 N/A 836.42 18.68 840.00 June 11, 2004 w/Alternative 758.73 0.00 760.78 757.27 29.25 759.81 768.43 5.09 770.00 769.28 26.17 771.00 N/A N/A N/A 780.31 29.14 782.00 791.25 15.46 797.00 N/A N/A N/A 835.91 15.65 840.00 Alternative 13B 10-year, 2 hour w/Alternative 759.04 0.00 760.78 754.43 7.71 759.81 766.19 2.21 770.00 766.44 8.44 771.00 N/A N/A N/A 777.73 31.52 782.00 786.80 17.66 797.00 N/A N/A N/A 834.34 7.56 840.00 100-year, 2 hour w/Alternative 759.53 0.01 760.78 756.67 24.38 759.81 769.17 6.01 770.00 767.85 17.03 771.00 N/A N/A N/A 779.29 61.24 782.00 792.06 41.16 797.00 N/A N/A N/A 835.64 14.21 840.00 100-year, 12 hour w/Alternative 758.79 0.00 760.78 757.82 33.80 759.81 769.48 6.16 770.00 769.40 26.96 771.00 N/A 0.00 N/A 780.82 91.49 782.00 796.18 62.82 797.00 N/A 0.00 N/A 836.42 18.59 840.00 June 11, 2004 w/Alternative 758.73 0.00 760.78 756.68 24.46 759.81 767.90 4.42 770.00 768.71 22.48 771.00 N/A N/A N/A 780.23 79.75 782.00 795.51 59.11 797.00 N/A N/A N/A 835.91 15.65 840.00 Alternative 14 - STH 44/Waukau Detention 10-year, 2 hour w/Alternative 759.04 0.00 760.75 754.50 8.15 759.81 766.23 2.21 770.00 766.84 15.18 771.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A 832.82 7.78 837.00 834.34 7.56 840.00 100-year, 2 hour w/Alternative 759.55 0.01 760.75 756.65 24.22 759.81 769.17 6.01 770.00 768.28 27.76 771.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A 834.55 12.96 837.00 835.63 14.15 840.00 100-year, 12 hour w/Alternative 758.80 0.00 760.75 758.20 37.08 759.81 769.58 6.21 770.00 770.09 44.45 771.00 N/A 0.00 N/A N/A 0.00 N/A N/A 0.00 N/A 835.84 17.13 837.00 836.03 16.31 840.00 June 11, 2004 w/Alternative 758.73 0.00 760.75 757.15 28.26 759.81 768.07 4.48 770.00 769.45 38.45 771.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A 835.67 16.58 837.00 835.86 15.38 840.00 Alternative 15-STH 44/Gray Road Detention 10-year, 2 hour w/Alternative 759.04 0.00 760.78 754.51 8.21 759.81 766.24 2.21 770.00 766.97 16.28 771.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 834.60 8.83 840.00 100-year, 2 hour w/Alternative 759.54 0.01 760.78 756.65 24.22 759.81 769.17 6.01 770.00 768.46 29.38 771.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 837.14 22.89 840.00 100-year, 12 hour w/Alternative 758.79 0.00 760.78 758.21 37.17 759.81 769.60 6.22 770.00 770.07 44.26 771.00 N/A 0.00 N/A N/A 0.00 N/A N/A 0.00 N/A N/A 0.00 N/A 838.03 28.73 840.00 June 11, 2004 w/Alternative 758.73 0.00 760.78 757.19 28.59 759.81 768.09 4.49 770.00 769.64 40.22 771.00 N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 838.09 29.15 840.00 Alternative 16 (Westhaven Golf Course Fully Expanded) 10-year, 2 hour w/Alternative 759.04 0.00 760.78 754.38 7.39 759.81 766.19 2.21 770.00 766.32 10.81 771.00 N/A N/A N/A 777.75 31.87 782.00 786.79 17.62 797.00 N/A N/A N/A 834.34 7.56 840.00 100-year, 2 hour w/Alternative 759.52 0.01 760.78 756.63 24.06 759.81 769.16 6.01 770.00 767.67 22.37 771.00 N/A N/A N/A 779.29 61.04 782.00 792.06 41.16 797.00 N/A N/A N/A 835.64 14.21 840.00 100-year 12 Hour w/Alternatives 758.78 0.00 760.78 757.62 32.15 759.81 769.06 5.90 770.00 769.06 34.81 771.00 N/A 0.00 N/A 780.85 91.74 782.00 796.18 62.82 797.00 N/A 0.00 N/A 836.42 18.59 840.00 June 11, 2004 w/Alternatives 758.73 0.00 760.78 756.57 23.58 759.81 767.84 4.34 770.00 768.29 27.85 771.00 N/A N/A N/A 780.23 79.40 782.00 795.51 59.11 797.00 N/A N/A N/A 835.91 15.65 840.00 Landmark Plaza, Node: Landmark Tippler Jr. High, Node: A-1D Armory Pond 9th/Washburn PondExisting Walmart Pond STH 44/Gray Road PondNew Westhaven Golf Course Pond SouthNew Westhaven Golf Course Pond North STH/Waukau Pond City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Engineering Analysis Prepared by Strand Associates, Inc.® Page 2 of 2 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 4.08-2.doc\022608 TABLE 4.08-2 (Continued) SUMMARY OF EFFECTS–RANKING DATA includes pipe and street flow, if any Univ/Badger Univ/ STH 44 Node: 226 Node: PR Outfall 2 Outfalls 4 Outfalls check all 3 Crossing to LMP Crossing to Armory New Cross Connection Node: Outfall 1 Node:D-OF-4 Node: Outfall 2A Node: Outfall 2B Node: Outfall 3 To Sawyer Creek Node: 06-494 Node: 06-468 Node: PR-27 P-06-1282 P-STR-5 D-AEW-37 D-AEW-25 P-AEW-26 (cfs) 4-Day 4-Day 4-Day 4-Day Total Flow US High US Peak High US Peak Outflow High Peak Outflow High Peak Outflow High Peak Outflow To Sawyer Cumulative Cumulative High US Peak High US Peak High Peak High US Peak High US Peak High DS Peak High DS Peak High DS Peak Water El. Flow Rate Water El. Flow Rate Volume Water El. Flow Rate Volume Water El. Flow Rate Volume Water El. Flow Rate Volume Creek/USH 41 4 Day 4 Day Water El. Flow Rate Water El. Flow Rate Water El. Flow Rate Water El. Flow Rate Water El. Flow Rate Water El. Flow Rate Water El. Flow Rate Water El. Flow Rate (Feet) (cfs) (Feet) (cfs) (ac-ft) (Feet) (cfs) (ac-ft) (Feet) (cfs) (ac-ft) (Feet) (cfs) (ac-ft) Outfall Volume (ac-ft) Volume (ac-ft) (Feet) (cfs) (Feet) (cfs) (Feet) (cfs) (Feet) (cfs) (Feet) (cfs) (Feet) (cfs) (Feet) (cfs) (Feet) (cfs) 748.63 136.45 747.55 235.89 752.55 62.59 752.55 95.56 749.57 50.19 158.15 751.70 24.48 753.09 155.78 776.83 117.47 763.02 16.31 775.79 62.91 771.90 8.00 818.26 74.49 832.78 42.05 750.37 187.34 748.38 410.04 755.37 96.07 755.37 144.76 751.04 94.37 240.83 752.23 42.73 753.62 249.56 779.31 227.08 764.55 50.70 778.96 93.08 773.46 20.34 818.55 88.44 834.60 44.25 749.33 162.25 747.76 283.22 349.79 755.37 62.64 24.05 755.37 132.11 183.50 751.04 70.92 31.77 194.75 207.55 589.11 752.13 32.26 753.49 200.06 777.80 140.77 763.96 40.83 777.54 69.82 772.59 6.21 818.46 73.93 834.24 44.37 748.73 154.75 747.66 241.25 754.33 39.16 754.33 105.33 750.49 51.28 144.49 752.06 29.65 753.36 175.31 776.85 116.28 763.38 23.97 775.92 62.42 771.94 3.97 818.35 71.60 834.06 43.76 748.63 138.00 747.55 236.28 752.55 62.59 752.55 110.12 749.57 50.18 172.71 751.71 24.46 753.11 158.48 777.15 116.30 763.69 32.30 776.85 54.16 772.58 8.00 818.26 77.28 832.78 40.54 750.37 187.37 748.38 410.07 755.37 96.05 755.37 145.62 751.04 94.37 241.67 752.23 42.73 753.62 250.02 779.80 228.16 764.62 51.90 779.47 75.37 773.80 20.34 818.55 83.96 834.60 44.31 749.34 165.16 747.76 283.50 351.69 755.37 62.64 24.05 755.37 140.98 177.97 751.04 70.92 30.35 203.62 202.02 584.06 752.14 32.71 753.50 202.73 779.07 153.47 764.50 50.00 778.74 55.70 773.26 6.27 818.46 74.11 834.24 44.26 748.75 157.68 747.66 243.14 754.33 39.79 754.33 126.95 750.49 51.33 166.74 752.09 31.00 753.40 179.55 777.58 116.52 763.95 40.54 777.29 54.75 772.75 3.98 818.36 75.05 834.04 43.64 748.63 138.59 747.55 236.43 752.55 62.59 752.55 104.73 749.57 50.12 167.32 751.70 24.50 753.12 163.17 776.83 101.14 763.49 26.90 776.61 47.41 772.31 8.00 818.26 67.32 832.78 42.28 750.38 187.60 748.38 410.65 755.37 96.05 755.37 145.45 751.04 94.37 241.50 752.23 42.71 753.63 245.15 779.83 227.66 764.62 51.78 779.52 74.04 773.78 20.34 818.54 89.51 834.60 44.30 749.33 163.16 747.76 283.36 314.40 755.37 62.64 24.05 755.37 139.23 116.82 751.04 70.92 29.97 201.87 140.87 485.24 752.13 32.32 753.50 202.72 778.76 143.15 764.35 47.99 778.45 50.78 773.08 6.24 818.45 84.53 834.24 44.37 748.74 155.95 747.66 242.10 754.33 39.80 754.33 115.39 750.49 51.32 155.19 752.07 29.95 753.39 178.54 776.86 96.41 763.75 34.13 776.74 45.46 772.36 3.94 818.34 79.37 834.04 44.12 748.63 136.62 747.55 236.15 752.55 62.59 752.55 107.11 749.57 50.19 169.70 751.70 24.45 753.09 159.58 776.84 117.50 763.58 29.15 775.80 63.40 772.42 8.00 818.26 74.66 831.61 39.11 750.37 187.16 748.38 410.04 755.37 96.07 755.37 145.49 751.04 94.37 241.56 752.23 42.74 753.62 249.56 779.35 225.43 764.61 51.74 778.99 96.27 773.75 20.34 818.54 88.38 834.40 42.92 749.33 163.73 747.76 283.32 357.33 755.37 62.64 24.05 755.37 140.28 182.27 751.04 70.92 29.63 202.92 206.32 593.28 752.14 32.72 753.49 200.07 778.00 142.51 764.43 49.27 777.69 72.02 773.16 6.25 818.44 82.96 833.56 41.85 748.74 156.28 747.66 241.63 754.33 39.15 754.33 118.86 750.49 51.28 158.01 752.09 30.81 753.36 174.22 776.86 115.45 763.82 36.25 775.93 62.78 772.48 3.98 818.31 76.49 832.44 41.26 748.63 136.56 747.55 235.93 752.55 62.59 752.55 107.16 749.57 50.26 169.75 751.70 24.48 753.09 155.79 776.84 117.54 763.58 29.20 775.81 63.42 772.42 8.00 818.26 74.49 832.79 42.06 750.37 187.21 748.38 410.20 755.37 96.04 755.37 145.48 751.04 94.37 241.52 752.23 42.75 753.63 249.57 779.35 225.45 764.61 51.72 778.99 96.27 773.75 20.34 818.55 88.45 834.61 44.14 749.33 163.57 747.76 283.35 358.71 755.37 62.63 24.43 755.37 140.38 184.54 751.04 70.92 29.79 203.01 208.97 597.47 752.14 32.75 753.49 200.09 778.01 142.77 764.44 49.12 777.70 72.16 773.16 6.26 818.46 83.93 834.23 44.00 748.74 156.54 747.66 241.81 754.33 39.16 754.33 118.98 750.49 51.28 158.14 752.09 30.93 753.37 174.84 776.87 116.23 763.82 36.33 775.95 63.00 772.49 3.98 818.35 78.59 833.94 43.75 748.63 136.46 747.55 235.94 752.55 62.59 752.55 101.23 749.57 50.19 163.82 751.70 24.48 753.09 156.21 776.66 100.87 763.36 23.51 775.56 54.75 772.17 8.00 818.26 75.06 832.78 42.06 750.38 187.60 748.38 411.27 755.37 96.06 755.37 145.33 751.04 94.37 241.39 752.23 43.35 753.63 248.22 779.32 224.69 764.61 51.60 778.97 95.55 773.72 20.34 818.54 89.48 834.60 44.30 749.33 162.29 747.76 283.12 318.76 755.37 62.64 24.05 755.37 136.34 110.73 751.04 70.92 34.88 198.98 134.78 488.42 752.13 32.19 753.49 200.81 777.44 129.94 764.15 45.08 777.24 67.50 772.91 6.20 818.45 84.53 834.24 44.47 748.73 154.79 747.66 241.14 754.33 39.80 754.33 111.14 750.49 51.32 150.94 752.07 29.70 753.36 175.35 776.64 96.27 763.60 29.60 775.57 52.78 772.17 3.94 818.34 79.37 834.04 44.09 STR 10 AEW-11.1Storm Sewer ConfluenceCampbell Creek Cunette Outfall AEW-25 AEW-26AEW-37AEW-14Campbell Creek Pipe Outfall Storm Sewer ConfluenceHWY 41 Outfall Westfield OutfallHWY 41 Outfall City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Engineering Analysis Prepared by Strand Associates, Inc.® Page 1 of 1 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Table 4.08-3.doc\022608 TABLE 4.08-3 SUMMARY OF EFFECTS–RANKINGS +Clay Road City Projects most = 1 least = 1 least = 1 least = 1 least = 1 (ac-ft) Cumulative 4 Day Run (all future conditions except June 11, 2004 (ac-ft) Total Watershed- 4-Day Total (lowest score is best) which is 20% higher RCNs with Existing RCNs)Total 4 Day Run (out of 6) (out of 16) @LMP 100-year 100-year controlling controlling Watershed- Ponding # of Wide Volume Minutes of USE Ponding No. of Total LMP LMP 100-year freeboard freebaord 100-year 100-year Wide Allowed Streets Used 4 Outfalls Flooding WATERSHED- WATERSHED- Allowed Streets Minutes of Ditch Pipe controlling @ @ 2' Freeboard 2' Freeboard Used (ac-ft) Flooding Storage WIDE WIDE Location (ac-ft)Flooding Flooding Overflows Overflows storm LMP Tippler @LMP @ Tippler Storage RANK RANK RANK RANK RANK RANK RANK Alternative 12 (Formerly Alt 7)) 10-year, 2 hour w/Alternative 14.42 46 0 4 -3.24 -6.99 100-year, 2 hour w/Alternative 110.13 79 0 4 -2.77 -4.86 100-year 12 Hour w/ Alternative 114.79 53 24,790 0 3 2 -3.51 -3.79 YES YES 119.8 5 3 4 4 5 4.20 4 June 11, 20004 w/ Alternative 75.03 39 0 0 -3.55 -4.76 Alternative 13 -Westhaven Park Detention 10-year, 2 hour w/Alternative 11.88 44 0 4 -3.24 -6.76 100-year, 2 hour w/Alternative 107.22 86 0 4 -2.72 -4.61 100-year, 12 hour w/Alternative 93.27 65 21,595 0 4 2 -3.48 -3.00 YES YES 132.5 3 4 3 3 3 3.20 3 June 11, 2004 w/Alternative 54.66 43 0 0 -3.55 -4.04 Alternative 13 -Westhaven Park Detention 10-year, 2 hour w/Alternative 7.14 36 0 4 -3.24 -6.88 100-year, 2 hour w/Alternative 79.3 73 0 4 -2.75 -4.64 100-year, 12 hour w/Alternative 54.92 51 13,882 0 4 2 -3.49 -3.49 YES YES 233.7 2 2 2 1 2 1.80 2 June 11, 2004 w/Alternative 27.67 30 0 0 -3.55 -4.63 Alternative 14 - STH 44/Waukau Detention 10-year, 2 hour w/Alternative 14.36 49 0 4 -3.24 -6.81 100-year, 2 hour w/Alternative 109.21 82 0 4 -2.73 -4.66 100-year, 12 hour w/Alternative 107.38 67 22,957 0 4 2 -3.48 -3.11 YES YES 115.0 4 6 5 5 4 4.80 5 June 11, 2004 w/Alternative 67.55 44 0 0 -3.55 -4.16 Alternative 15-STH 44/Gray Road Detention 10-year, 2 hour w/Alternative 14.64 48 0 4 -3.24 -6.80 100-year, 2 hour w/Alternative 115.4 81 0 4 -2.74 -4.66 100-year, 12 hour w/Alternative 117.28 65 25,850 0 4 2 -3.49 -3.10 YES YES 110.2 6 5 6 6 6 5.80 6 June 11, 2004 w/Alternative 75 41 0 0 -3.55 -4.12 Alternative 16 (Single Mix of Alt.) 10-year, 2 hour w/Alternative 5.94 38 0 4 -3.24 -6.93 100-year, 2 hour w/Alternative 71.9 71 0 4 -2.76 -4.68 100-year 12 Hour w/Alternatives 51.62 47 12,960 0 3 2 -3.50 -3.69 YES YES 240.1 1 1 1 2 1 1.20 1 June 11, 2004 w/Alternatives 25.3 30 0 0 -3.55 -4.74 Alt 15 was dropped to the 5th spot in streets flooding due to less storage *** City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-23 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 4. Is in the top three for storage considered under these alternatives. See Table 4.08-4. Alternatives 13, 13 B, and 16 are in the top three for watershed-wide ranking. 5. Is in the top three for least amount of volume discharging to the Sawyer Creek/USH 41 outfall over a 4 day period under 100-year, 12 hour storm with proposed conditions. See Table 4.08-5. Alternatives 13, 13 B, and 16 are in the top three. Additionally, Alternatives 13 B and 16 appear to closely mimic the volume of stormwater discharging to the Sawyer Creek/USH 41 outfall when compared to existing conditions. 6. Is in the top three for least amount of total minutes of flooding in the modeled system under the 100-year, 12 hour storm event under proposed conditions. See Table 4.08-5 (6). All alternatives significantly improve the storm sewer system compared to existing conditions. However, the top three are Alternatives 13, 13B, and 16. Alt. Existing Conditions 100-year, 12-hr 4-day volume to Sawyer Creek at USH 41 outfall (acre-feet) Future Conditions 100-year, 12-hr 4-day volume to Sawyer Creek at USH 41 outfall (acre-feet) Future Conditions 100-yr, 12-hr 4-day Increase Volume (acre-feet) Rank Existing Conditions 100-year, 12-hr 4-day minutes of flooding watershed- wide Future Conditions 100-year, 12- hr 2day and 4 day minutes of flooding watershed- wide Future Conditions 100-yr, 12-hr 2-day/4 day Minutes of flooding decrease Rank Existing 122 69,278 12 122 207.6 85.6 5 69,278 24,790 44,488 5 13 122 202.0 80.0 3 69,278 21,595 47,683 3 13 B 122 140.9 18.9 2 69,278 13,882 55,396 2 14 122 206.3 84.3 4 69,278 22,957 46,321 4 15 122 209.0 87.0 6 69,278 25,850 43,428 6 16 122 134.8 12.8 1 69,278 12,960 56,318 1 Table 4.08-5 Least Amount of Increase in 100-Year, 12-Hour Duration Volume at Sawyer Creek/USH 41 Outfall Ranking in Acre-Feet Alternative Future Conditions 100-yr, 12-hr Watershed-Wide Storage Usage (acre-feet) Rank 12 101.1 5 13 113.9 3 13 B 215.1 2 14 98.5 6 15 110.2 4 16 221.5 1 Table 4.08-4 Watershed-Wide Storage Provided (City-Provided Detention) City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-24 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 7. Keeps the increased peak discharge at USH 41 to a minimum. See Table 4.08-6 and Figure 4.08-2. All options are relatively equivalent for this criteria. 8. Has the least effect on the Sawyer Creek 100-year, 12-hour peak discharge rate under existing conditions at the USH 41/Sawyer Creek outfall. We have inserted the Campbell Creek watershed proposed conditions USH 41/Sawyer Creek outfall hydrographs the Sawyer Creek existing conditions HEC-HMS model to see the impact in peak discharge at the Sawyer Creek/USH 41 outfall as shown in Table 4.08-7. As the table shows, there are negligible effects on the Sawyer Creek peak discharge under existing conditions. This means that while all alternatives increase the peak discharge outfalling to Sawyer Creek from the 1,841 acre Campbell Creek watershed, the timing and routing of flows through the 10,026 acre Sawyer Creek watershed seem to mitigate the effects of the peak discharge increase coming from the Campbell Creek watershed. Figure 4.08-1 shows the Sawyer Creek watershed hydrograph in comparison to the USH 41/Sawyer Creek hydrograph entering from the Campbell Creek watershed with Alternative 13 B in place. As can be seen, the Campbell Creek hydrograph peaks much sooner than the Sawyer Creek watershed hydrograph. Alternative Existing Conditions 100-yr, 12-hr Peak Discharge at USH 41/Sawyer Creek Outfall (cfs) Reduction from Existing (cfs) Rank Existing Conditions 3,345.80 12 3,362.05 16.25 3 13 3,377.77 31.97 4 13 B 3,358.90 13.10 2 14 3,378.35 32.55 5 15 3,378.39 32.59 6 16 3,356.60 10.8 1 Table 4.08-7 Sawyer Creek Watershed Peak Discharge Effects Alternative Existing Conditions 100-year (2hr/12hr) Future Conditions 100-year (2hr/12hr) Future Conditions 100-year 12-hour peak flow increase Rank 7 124 127 3 12 124 195 71 1 13 124 204 80 6 13 B 124 202 78 3 14 124 203 79 4 15 124 203 79 5 16 124 199 75 2 Table 4.08-6 Least Amount of Increase in 100-Year, 12-Hour Duration Flow Rates in Cubic Feet/Second at Sawyer Creek/USH 41 Outfall Ranking *Alternative 7 doesn’t account for the proposed 50-year design storm WisDOT storm sewer along USH 41 SA W Y E R C R E E K / U S H 4 1 O U T F A L L H Y D R O G R A P H NO R T H B R A N C H C A M P B E L L C R E E K S T O R M W A T E R M A N A G E M E N T P L A N T CI T Y O F O S H K O S H OS H K O S H , W I S C O N S I N FIGURE 4.08-2 Campbell Creek Outfall to Sawyer Creek 0 50 100 150 200 250 6 / 1 0 / 0 4 1 2 : 0 0 P M 6 / 1 0 / 0 4 6 : 0 0 P M 6 / 1 1 / 0 4 1 2 : 0 0 A M 6 / 1 1 / 0 4 6 : 0 0 A M 6 / 1 1 / 0 4 1 2 : 0 0 P M 6 / 1 1 / 0 4 6 : 0 0 P M 6 / 1 2 / 0 4 1 2 : 0 0 A M 6 / 1 2 / 0 4 6 : 0 0 A M 6 / 1 2 / 0 4 1 2 : 0 0 P M 6 / 1 2 / 0 4 6 : 0 0 P M 6 / 1 3 / 0 4 1 2 : 0 0 A M 6 / 1 3 / 0 4 6 : 0 0 A M 6 / 1 3 / 0 4 1 2 : 0 0 P M 6 / 1 3 / 0 4 6 : 0 0 P M 6 / 1 4 / 0 4 1 2 : 0 0 A M 6 / 1 4 / 0 4 6 : 0 0 A M 6 / 1 4 / 0 4 1 2 : 0 0 P M 6 / 1 4 / 0 4 6 : 0 0 P M 6 / 1 5 / 0 4 1 2 : 0 0 A M Time Q ( c f s ) Alt 12 Alt 13 Alt 13 B Alt 14 Alt 15 Alt 16 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-25 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 The above discussion supports the recommendation of Alternative 13 B as the most cost- effective alternative for providing flooding relief in the Campbell Creek watershed. 4.09 STORM SEWER CAPACITY ANALYSIS UNDER FUTURE LAND USE CONDITIONS FOR MODELED STORM SEWERS WITH RECOMMENDED ALTERNATIVE IN PLACE (ALTERNATIVE 13 B) Figure 4.09-1 attached at the back of this report shows the capacities per storm conveyance reach under future land use conditions with Alternative 13B in place for the 2-hour duration storm event. This figure shows that there is substantial improvement in storm conveyance reach as compared to the existing condition shown in Figure 3.02-1 of the May 2006 Stormwater Plan. While some of the storm sewers show greater than 10-year capacity it is likely that inlet capacity is not sufficient to fill the pipes and allow full utilization of the storm capacity shown in Figure 4.09-1. We recommend that the city assess inlet capacity in conjunction with future street improvement projects to evaluate the benefits of adding inlets to fully realize the capacities shown in Figure 4.09-1. 13 cfs Increase Sawyer Creek Existing Conditions Sawyer Creek Existing Conditions + Campbell Creek Proposed Conditions With Alt. 13 B In Place Campbell Creek Proposed Conditions W/ Alt 13 B In Place 13 cfs Increase Sawyer Creek Existing Conditions Sawyer Creek Existing Conditions + Campbell Creek Proposed Conditions With Alt. 13 B In Place Campbell Creek Proposed Conditions W/ Alt 13 B In Place Figure 4.08-1 Alternative 13 B-Sawyer Creek Hydrograph at USH 41 Outfall City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-26 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 4.10 STORM SEWER CAPACITY ANALYSIS UNDER FUTURE LAND USE CONDITIONS FOR MODELED STORM SEWERS WITH ALTERNATIVE 16 IN PLACE Figure 4.10-1 attached at the back of this report shows the capacities per storm conveyance reach under future land use conditions with Alternative 16 in place for the 2-hour duration storm event. This figure shows that there is substantial improvement in storm conveyance reach as compared to the existing condition shown in Figure 3.02-1 of the May 2006 Stormwater Plan. While some of the storm sewers show greater than 10-year capacity it is likely that inlet capacity is not sufficient to fill the pipes and allow full utilization of the storm capacity shown in Figure 4.10-1. We recommend that the city assess inlet capacity in conjunction with future street improvement projects to evaluate the benefits of adding inlets to fully realize the capacities shown in Figure 4.10-1. While Alternative 16 provides the most detention of the alternatives considered, when comparing the improvement in storm conveyance reach capacity with Alternative 13B (Figure 4.09-1), it is apparent that the substantially increased cost for Alternative 16 over Alternative 13B makes Alternative 13B more cost-effective in providing similar watershed-wide benefits. 4.11 STORM SEWER SIZING FOR MAIN BRANCH TO CONVEY 10-YEAR FLOW WITH RECOMMENDED ALTERNATIVE IN PLACE Figure 4.11-1 shows the storm sewer upsizing necessary to convey the 10-year, 2-hour duration design storm from the Tippler Detention Basin to the Main Stem and through the Main Stem system to the Campbell Creek outfall with Alternative 13B in place under future land use conditions. Storm sewer reaches labeled as “Same” have at least a 10-year, 2-hour duration design storm capacity with Alternative 13B in place. The existing open channel from the Campbell Creek outfall to the Fox River backwater ranges in size from approximately 4-foot by 12-foot to 5-foot by 14 foot. The existing storm sewer upstream of the Campbell Creek storm sewer outfall is currently corrugated metal pipe. The City should consider upsizing these storm conveyance facilities as funds become available, as reconstruction becomes necessary and as feasible after implementation of Alternative 13B. 4.12 CHANGES IN DIVERSION AT DIVERSION POINTS 1, 2, AND 3 WITH RECOMMENDED ALTERNATIVE IN PLACE Figure 4.12-1 shows the changes in diversion with Alternative 13B in place under future land use conditions. This can be compared with the existing land use conditions diversion analysis shown in Figure 3.02-3. 4.13 OFF-LINE STORMWATER PONDS (NR 116) The City of Oshkosh is contemplating an off-line stormwater pond at the Armory property in the South Branch of Campbell Creek. In addition, the City will be contemplating off-line stormwater ponds in the Sawyer Creek Regional Detention Basin Study. It is our understanding that on-line stormwater ponds are not permittable by the DNR on navigable streams. The following discussion is intended to address the issues related to planning and construction of off-line stormwater detention ponds. DO W N S T RE AM P I P E U P S IZ I N G TO CON V E Y THE 1 0 - Y E A R F LO W WI T H AL T ER N A T E 1 3 B IN - PL AC E NORT H B R AN C H CA MP B EL L CRE EK S T O R MW A TE R S T U DY CI T Y OF O S H K O SH WI N N E B AG O C O U NT Y , W I S C O NS I N FIGURE 4.11-11-382.021 Same Same Same Same Same Same Same Same 4' x 19' Channel @ 0.15% 5' x 16' Channel @ 0.15%5' x 16' Channel @ 0.15% WITZEL AVE N K O E L L E R S T SOUTHLAND AVE KN A P P S T BISMARCK AVE JO S S L Y N S T N S A W Y E R S T US H W Y 4 1 S O U T H B O U N D US H W Y 4 1 N O R T H B O U N D N W E S T F I E L D S T S L A R K S T N W A S H B U R N S T S E A G L E S T N E A G L E S T FO S T E R S T DO V E S T HA W K S T PORTER AVE GU E N T H E R S T N M E A D O W S T N L A R K S T W 4TH AVE LOMBARD AVE W 2ND AVE S W A S H B U R N S T FAUST AVE SU L L I V A N S T SKYVIEW AVE NATIONAL AVE CLAYTON CT N E A G L E S T N L A R K S T W 4TH AVE SU L L I V A N S T 756 760 75 8 0 75 4 75 2 76 2 76 6 764 75 0 748 746 768 77 0 77 4 778 78 0 782 77 2 754 756 0 756 0 75 8 760 756 770 750 762 76 4 75 2 764 762 760 760 76 0 762 762 0 758 0 75 8 748 75 8 0 764 0 754 754 76 2 76 4 76 2 764 760 76 0 75 4 762 0 748 754 76 0 762 75 8 758 76 2 756 756 766 756 76 0 750 0 75 6 752 760 766 75 4 750 0 756 756 756 766 0 764 75 8 75 6 76 0 762 75 6 76 4 76 0 75 6 0 75 2 756 762 0 750 76 8 76 2 756 762 75 8 75 2 76 2 770 752 758 75 6 75 4 77 0 752 766 76 4 75 6 758 75 6 0 766 752 76 2 750 762 754 75 8 75 4 766 76 2 75 4 76 0 76 0 76 8 750 76 2 76 2 75 0 76 4 75 4 76 0 756 0 75 6 75 8 75 8 0 0 760 754 76 4 758 766 752 764 756 75 6 764 76 0 75 2 76 4 0 0 76 0 0 764 0 75 2 758 752 762 75 4 754 76 4 75 8 76 2 76 2 758 764 760 75 6 76 2 764 756 75 6 758 0 752 754 752 30 36 60 42 12 6 18 8 27 15 21 24 6540 36 5 8 50 3 1 3622 0 31 5 0 3654 10 12 24 12 15 15 18 24 21 15 12 15 12 15 12 30 12 8 27 18 6 12 21 21 18 12 27 12 12 15 12 30 12 24 15 12 21 10 15 15 18 24 15 21 12 15 8 10 15 15 15 8 18 15 15 24 12 24 18 18 15 18 15 30 18 18 12 12 15 42 15 18 12 12 18 12 18 S:\@SAI\351--400\382\021\GIS\Report Figures\Figure 4.11-1 - Alt 13B Downstream Pipe Sizing.mxd 0 400 800200 Feet ³ Legend Storm Manhole Storm Sewer Water Valve Water Main Sanitary Manhole Sanitary Sewer Parcel Contour (2 FT.) Same Same SAME SAME 2 - 3' x 5' RCP Box 2 - 3' x 6' RCP Box 2 - 3' x 6' RCP Box 2 - 3' x 6' RCP Box 2 - 4' x 6' RCP Box W 4TH AVE WITZEL AVE S S A W Y E R S T GU E N T H E R S T FO S T E R S T DURFEE A V E 75 2 754 756 750 758 748 752 752 752 75 4 752 75 6 750 75 2 752 75 6 752 75 2 752 752 756 750 3658 6540 18 42 12 20 15 724 4 50 3 1 15 12 12 0 200 400100 Feet DIVERSION ANALYSIS - WITH ALTERNATIVE 13B IN PLACE NORTH BRANCH CAMPBELL CREEK STORMWATER STUDYCITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FI G U RE 4 . 1 2 - 1 1- 382 . 0 3 0 ^_ ^_ ^_ ^_ Diversion Removed In Proposed Conditions Diversion PT 2 3' x 4.5' RCP Box With 33" Orfice in Steel Plate IE = 762.54 Diversion PT 1 High PT = 776.35 38"x60" HERCP IE = 775.25 36" RCP IE = 769.73 S:\@ S AI \ 35 1 --4 0 0 \ 3 8 2 \ 0 3 0 \ D a t a \ GI S \ Rep o r t F i gu r e s \ Fig u r e 4 . 12 - 1 - AL T 13 B Div e r s i on . mx d 0 500 1,000250 Feet ³ Legend Drainage Basin Boundary Sub Drainage Basin Boundary Landmark Plaza Storm Manhole Storm Sewer Alt 13-b Storm Sewer Water Valve Water Main Sanitary Manhole Sanitary Sewer ^_Diversion Point ^_ ^_ ^_ ^_ Flow (CFS) Q1 = 37.4 Q2 = 53.9 Q5 = 82.1 Q10 = 103.3 Q25 = 127.1 Q50 = 137.6 Q100 = 141.2 Q6/11/04 = 112.1 Flow (CFS) Q1 = 33.5 Q2 = 49 Q5 = 75.1 Q10 = 95.3 Q25 = 115.4 Q50 = 124.2 Q100 = 127.2 Q6/11/04 = 102 Flow (CFS) Q1 = 12.7 Q2 = 21.1 Q5 = 34.5 Q10 = 52.5 Q25 = 73.0 Q50 = 77.4 Q100 = 79.4 Q6/11/04 = 53.5 Flow (CFS) Q1 = 0.9 Q2 = 6.2 Q5 = 10.6 Q10 = 26.9 Q25 = 41.7 Q50 = 49.0 Q100 = 51.8 Q6/11/04 = 34.1 Flow (CFS) Q1 = 17.8 Q2 = 27.9 Q5 = 40.7 Q10 = 47.3 Q25 = 59.4 Q50 = 70.0 Q100 = 74.0 Q6/11/04 = 45.4 Flow (CFS) Q1 = 28.0 Q2 = 45.6 Q5 = 72.3 Q10 = 105.1 Q25 = 139.2 Q50 = 153.1 Q100 = 156.0 Q6/11/04 = 105.6 Flow (CFS) Q1 = 2.8 Q2 = 4.1 Q5 = 6.0 Q10 = 8.0 Q25 = 11.6 Q50 = 15.3 Q100 = 20.3 Q6/11/04 = 3.9 Flow (CFS) Q1 = 0 Q2 = 0 Q5 = 0 Q10 = 0 Q25 = 0 Q50 = 0 Q100 = 0 Q6/11/04 = 0 City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-27 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 The DNR maintains an excellent Web site to help navigate through this process at: http://www.dnr.state.wi.us/org/water/fhp/waterway/ponds.shtml . As a summary of this Web site and DNR regulations, the following is presented. 1. A general permit or individual permit is required to construct, dredge, or enlarge any part of a pond or artificial waterbody that is either: a. Connected to a waterway. b. Located within 500 feet of a navigable waterway STEP 1: Determine if your waterway has a special designation (Area of Special Natural Resource Interest–ASNRI, Public Rights Features–PRF, Priority Navigable Water–PNW) that might affect the exemption or permit requirements. A search of the Designated Waters Database (http://www.dnr.state.wi.us/org/water/fhp/waterway/waterslist.shtml) indicates that neither Campbell Creek nor Sawyer Creek have any special designations. Lake Butte Des Morts–Fox River is designated a PNW, ASNRI, and a Natural Heritage Inventory (NHI) water. However, ponds contemplated are currently not in or adjacent to this waterbody. STEP 2: Determine if your project qualifies for a general permit. A copy of the general permit application and Fee Sheet can be found at: http://dnr.wi.gov/org/water/fhp/waterway/ponds.shtml#step2. Most off-line ponds will require an individual permit because of the following. ƒ The crest of the berm of the pond or artificial water body is closer than 35 feet from the ordinary high water mark. ƒ The pond is subject to inflow from the navigable waterway up to the 10-year, 24-hour event. STEP 3: Apply for a General Permit. The fee for a general permit for a pond is $300. STEP 4: Apply for an Individual Permit. The fee for an individual permit for a pond is $500. Relevant Definitions “Navigable waterway” means any body of water with a defined bed and bank, which is navigable under the laws of the state. In Wisconsin, a navigable body of water is capable of floating the lightest boat or skiff used for recreation or any other purpose on a regularly recurring basis. “Ordinary high water mark” means the point on the bank or shore up to which the presence and action of water is so continuous as to leave a distinct mark either by erosion, destruction of terrestrial vegetation, or other easily recognizable characteristic. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 4–Alternative Analysis Prepared by Strand Associates, Inc.® 4-28 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S4.doc\022608 In summary, off-line stormwater ponds are permittable by the DNR but they should be built with the following recommendations. 1. The pond berms adjacent to the waterway should be located outside of the floodway in areas with regulatory floodway delineations. 2. The pond berms adjacent to the waterway should be located a minimum of 10 feet away from the top of bank of the waterway in areas without regulatory floodway delineations. In this case, the 2-year flow should be able to be conveyed in the waterway without the 2-year water surface elevation in the waterway intersecting the start of berm location. 3. Fish passage must be maintained in the main channel or creek. 4. The City should further explore the regulatory requirements with the DNR regarding permitting of off-line ponds. SECTION 5 CONCLUSIONS AND RECOMMENDATIONS City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 5–Conclusions and Recommendations Prepared by Strand Associates, Inc.® 5-1 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S5.doc\022508 5.01 GENERAL In this section, specific recommendations are presented for achieving the goals of the stormwater management plan. These recommendations are based on the discussion in Section 4 and on hydrologic analyses performed as part of this project. 5.02 RECOMMENDATIONS FOR ACHIEVING STORMWATER MANAGEMENT GOALS Section 5.03 includes Table 5.03-1 that lists the recommended stormwater plan for achieving the stormwater management goals. In addition, Section 4 lists the modeling impacts and benefits of the recommended improvements. In Section 5.05 of the original report, a uniform policy for addressing and documenting future stormwater issues is proposed. While working toward the implementation of this plan, we have the following recommendations: 1. The City should complete soils investigation to determine soil characteristics in locations where detention ponds are proposed. 2. The City should adopt the Policies and Practices identified in Section 5.05 of the original report and the Drainage Evaluation Form in Appendix B of the original report. 3. The City should coordinate detention basins recommended in this study with detention basins recommended in the water quality study being performed by another consultant. 4. The City should investigate funding opportunities for the detention basins through the DNR Municipal Flood Control Grant Program. The DNR Lake Protection Grant program, River Protection Grant program, and Stewardship Grant program should also be explored. 5. The City should update City stormwater facility maps using the field survey forms and survey information provided by Strand Associates. 6. The City should further explore the regulatory requirements with the DNR regarding permitting of off-line ponds. 7. The City should further explore the regulatory requirements regarding the diversion of the navigable Campbell Creek to the Westhaven Golf Course ponds. 8. The City should investigate possible utility conflicts and space availability for each component of the recommended Alternative. 9. The owner of Landmark Plaza should perform a study to determine how to reduce potential ponding at nodes 06-846, 06,847, and 06-1293.2 to an acceptable level considering that downstream backwater effects are alleviated as discussed in Section 3.02 C. 7 of the original report. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 5–Conclusions and Recommendations Prepared by Strand Associates, Inc.® 5-2 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S5.doc\022508 10. We recommend that the City assess inlet capacity in conjunction with future street improvement projects to evaluate the benefits of adding inlets to fully realize the capacities shown in Figure 4.09-1 11. The City should consider upsizing the storm conveyance facilities shown in Figure 4.11-1 as funds become available, as reconstruction becomes necessary and as feasible after implementation of the recommended Alternative. 12. The topographic surveys completed for each of the recommended projects should include survey of the properties (including the structure 1st floor elevation) surrounding each pond location. It is recommended that an acceptable pond overflow route be incorporated into the final design of each pond for flows potentially exceeding the 100- year storm event and/or for potential blockages of outlet structures. In addition, during design, it is recommended the berms at the ponds have 2 feet of freeboard between the modeled 100-year WSEL in the pond and the top of the berm to provide an added measure of protection to structures surrounding the recommended ponds (or to a height that would not invoke NR 333 as described below in item 14). The figures, herein, contemplate an approximate 1 foot of freeboard. 13. During design, we recommend running the XP-SWMM model to maximize the use of the Tippler, Armory, and Westhaven ponds after detailed topographic surveys are completed of the project sites, of the surrounding topography and 1st floor building elevations, and of the existing utility elevation information. After design is complete for all components of Alternative 13 B, we recommend that the XP-SWMM model be re-run with all changes to revise Figure 4.09-1 Storm Sewer Capacity Analysis Under Future Land Use Conditions For Modeled Storm Sewers With Alternative 13 B In-Place. 14. For the Westhaven ponds, we recommend that the City consult Chapter NR 333 Dam Design and Construction and the local DNR dam engineer to determine if these pond berms would fall under the applicability of this code section. The main requirement that would make these berms apply to this code section is if the berm has a structural height of more than 6 feet and a maximum storage capacity of 50-acre-feet or more of water. If they do, during design a dam breach analysis may be required as well as a Small Dam Safety Permit. City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 5–Conclusions and Recommendations Prepared by Strand Associates, Inc.® 5-3 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S5.doc\022508 5.03 IMPLEMENTATION PLAN Table 5.03-1 provides a listing of the recommended stormwater management plan components, the cost of each component, and the implementation schedule and possible funding source, if applicable. As discussed in Section 4.08, Alternative 13 B best meets the evaluation criteria for a recommended alternative. 5.04 FUNDING OPPORTUNITIES Appendix C includes a brochure produced by Strand Associates that describes some of the more popular DNR grant programs. The City of Oshkosh may want to investigate the programs for possible funding of the recommended stormwater plan components. The following programs are available: ƒ Municipal Flood Control Grant ƒ Urban Nonpoint Source and Stormwater Grant ƒ Targeted Runoff Management Grant ƒ Lake Planning and Management Grant ƒ River Protection Planning and Management Grant ƒ Stewardship Grant The Municipal Flood Control grant would be ideal for dry detention basins and wet detention basins in this watershed because of the documented flooding problems and property damage in the watershed. The Urban Nonpoint Source and Stormwater grant would be ideal for wet detention Component Description Opinion of Probable Cost Implementation Schedule and Funding Source 13 B 1 Expanded Detention at Tippler Junior High property $2,251,600 Priority 1-Municipal Flood Control Grant and Stormwater Utility 13 B 2 Partially Expanded Detention at Armory Site $2,495,400 Priority 4-Municipal Flood Control Grant and Stormwater Utility 13 B 3 Storm Sewer System Improvements from Landmark Plaza to Tippler $479,900 Priority 2-Municipal Flood Control Grant and Stormwater Utility 13 B 4 Fully Expanded Westhaven Golf Course Detention and Upstream Diversion $11,382,800 Priority 3-Municipal Flood Control Grant, UNPS Grant, Stormwater Utility, Stewardship Grant Total $16,609,700 1. Costs do not include utility conflict resolution, if any. 2. WisDOT is responsible for the cost of construction of the 50-year design storm sewer/ditch along USH 41. 3. Grand Total cost doesn’t include stormwater quality portion of the detention pond (i.e. excavation below normal WSEL) for Component 13 B 4. All other component costs include excavation below the normal WSEL. Table 5.03-1 Stormwater Plan Components and Implementation Plan (Costs include 25 Percent Engineering and Contingencies) City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Addendum No. 1 Section 5–Conclusions and Recommendations Prepared by Strand Associates, Inc.® 5-4 JHL:lr\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\S5.doc\022508 basins that are able to accept the 2-year flow and thus treat the smaller storms for total suspended solids. The DNR Lake Protection Grant program, River Protection Grant program, and the Stewardship Grant program should also be explored to see if these projects would be a fit for these grant programs. The Stewardship Grant program may assist in land acquisition to protect water resources and green space for facilities that might be able to incorporate some level of outdoor recreation facilities. 5.05 CONCLUSION The goal of this report has been to provide the City of Oshkosh with a framework of how stormwater management facilities should be developed to address existing flooding and future development issues. It is not expected that all the recommended measures will be constructed immediately. Implementation of measures recommended in this report will help to relieve the flooding in the Campbell Creek watershed, will reduce the flooding at Landmark Plaza, and will provide a water quality benefit in complying with the City’s WPDES stormwater permit. APPENDIX A FLOODING PHOTOGRAPHS City of Oshkosh, Wisconsin North Branch Campbell Creek Stormwater Management Plan Appendix A–June 10 and 11, 2004 Addendum No. 1 Flooding Photographs Prepared by Strand Associates, Inc.® Page 1 of 1 JHL:pll\S:\@SAI\351--400\382\030\Wrd\Report-Addendum 1\Appendix A.doc\082207 Looking north at the Universal and Badger intersection. Looking south along Washburn Street/ USH 41 from south of West 9th Avenue Looking south along Washburn Street/ USH 41 from south of W. 9th Avenue APPENDIX B STORMWATER FUNDING BROCHURE Stormwater Management Funding The Wisconsin Department of Natural Resources (WDNR) and the Federal Emergency Management Association (FEMA) have a long history of providing funding for stormwater management planning, design, and construction. Some of the WDNR and FEMA programs include Urban Nonpoint Source and Stormwater Grants (UNPS & SW), Municipal Flood Con- trol Grants, Lake and River Planning and Management Grants, Targeted Runoff Management Grants, Clean Water Fund – Urban Runoff Loans, and FEMA – Hazard Mitigation Grants. In the last six years, we have been successful in helping many of our clients procure stormwater and lake grants as shown in the table below. Strand Associates, Inc.® Madison, WI 608-251-4843 Joliet, IL 815-744-4200 Louisville, KY 502-583-7020 Lexington, KY 859-225-8500 Mobile, AL 251-343-7775 Columbus, IN 812-372-9911 Columbus, OH 614-835-0460 Indianapolis, IN 317-423-0935 Milwaukee, WI 414-271-0771 Cincinnati, OH 513-861-5600 www.strand.com To learn how Strand can secure funding for your project or for additional information regarding stormwater or water re- sources funding, please contact Jon Lindert at our Madison office, 608-251-4843 or e-mail at jon.lindert@strand.com Please also visit us at www.strand.com Print Date: February 2008 * Project Description Inside Community Project Grant Type GrantAmount Algoma, WI SW Quality Management Plan U $17,990 Algoma, WI Regional Detention Basin Plan U $10,976 Bonduel, WI Stormwater Management Plan U $16,450 Bristol, WI North Lake George Flood Reduction Project M $333,603 Bristol, WI Detention Pond A Restoration and Enhancement * U $121,000 Bristol, WI Stormwater Quality Management Plan – Phase II U $19,950 Dodgeville, WI Stormwater Utility U $28,840 Dodgeville, WI Stormwater Plan U $21,600 Evansville, WI Lake Leota Management Plan - Phase I and II * L $20,000 Hartland, WI Stormwater Management Plan * U $35,700 Hartland, WI Stormwater Utility U $42,000 Hartland, WI Detention Basin Construction U $150,000 Janesville, WI Ordinances and Regional Detention Basin Plan U $84,000 Lake Mills, WI Owen Street Regional Detention Basin U $45,750 Lake Mills, WI Stormwater Plan and Utility U $55,860 Lancaster, WI Stormwater Utility U $28,000 Lancaster, WI Kolar Property Regional Detention Facility U $55,920 Madison, WI Wingra Creek Streambank Restoration * U $101,050 Maple Bluff, WI Stormwater Quality Management Plan U $12,600 Marsh! eld, WI Stormwater Utility and Ordinances U $73,010 Marsh! eld, WI Stormwater Management Plan U $36,800 Monona, WI Stormwater Utility Feasibility Study U $28,000 Monona, WI Stormwater Management Plan and Mapping U $24,220 New Glarus, WI Little Sugar River Streambank Restoration TRM $150,000 New Glarus, WI Stormwater Management Plan U $23,100 New Glarus, WI Stormwater Utility U $18,900 Omro, WI Wet Detention Basin Design, Construction, and Acquisition U $83,300 Omro, WI Stormwater Quality Management Plan U $12,250 Omro, WI Northeast Stormwater Management Plan U $4,270 Onalaska, WI Stormwater Quality Management Plan and Utility Feasibility Study U $46,750 Oshkosh, WI Murdock Detention Basin Property Acquisition M $330,000 Oshkosh, WI Anchorage Basin Relief Channel Construction * M $698,500 Oshkosh, WI Sawyer Creek Floodway Land Acquisition M $101,500 Prairie du Sac, WI Stormwater Utility U $30,000 Whitewater, WI Stormwater Utility Implementation U $27,000 Whitewater, WI Cravath & Tripp Lakes Stormwater & Erosion Ordinances* L $7,500 Whitewater, WI Stormwater Plan and Utility U $57,500 Total: $2,953,889 M = Municipal Flood Control Grants U = Urban Nonpoint Source and Stormwater Grants L = Lake Planning and Management Grants TRM = Targeted Runoff Management Grants April 15, 2008 § Streambank/ Shoreline Restoration § Wet Detention Ponds § Stormwater Utilities § Stormwater Mapping § Stormwater Management Plans § Stormwater/ Erosion Control Ordinances § Public Information/Education § Street Sweepers* § Best Management Practice (BMP) construction for new development § Projects that are not water quality based, such as projects to solely solve drainage ! ooding prob- lems § Dredging Projects § Urban Area De! ni- tion: Population Density of 1,000/sq miles or Commer- cial Land Use or for Planning Projects, projected to be urban in 20 years. § Check NPS Ranking on Watersheds and Lakes List for basin priorities. Funding Type Application Date State/Local % Cost Share Eligible Projects Non-Eligible Projects Restrictions/ Details Municipal Flood Control Grant – WDNR Priority: See eligible projects column . . . Planning, Design, Construction, and Administrative Activities. 70/30 Maximum allowed per applicant: 20% of funding avail- able in that grant cycle. § Eligible projects are in order of DNR priority. (Projects near bottom have less chance of being funded.). § Must have appraisal done prior to grant application forac- quisitions (must include copy with application). January 15, 2008 Every two years, if funding available § Acquisition & Removal of Struc- tures § Floodproo" ng and elevation of Structures § Streambank Restoration § Dam Removal § Fish & Native Plant Habitat § Restoration § Acquisition of Vacant Land for Flood Storage and Conveyance § Flood collection, retention, deten- tion, storage facilities. § Flood Insurance Studies and Flood Mapping Projects Lake Planning Grant - WDNR (Large Scale) February 1 and August 1, an- nually 75/25 Maximum of $10,000 per grant. Maximum of two grants per grant cycle. § Physical, chemical, biological and sociological data collection § Water Quality Assessment § Watershed Evaluation § Wetland Restoration § Ordinance Development § Management/Implementation plans for lake protection rehabilitation § Each lake eligible for more than one plan- ning grant with a lifetime maximum of $100,000Note: wetland restoration grants also available. Targeted Runoff Management Grant (TRM) - WDNR Priority: Control Polluted Runoff from both Urban and Rural Sites . . . Design and Construction of BMPs. April 15, 2008 70/30 up to a maximum of $150,000 50/50 for property acqui- sition (included in the $150,000 maximum) § Streambank Restoration § Wetland Construction § Detention Ponds § Cropland Protection § Livestock Waste Management Practices § Property Acquisition § Design and construc- tion of BMPs (previously construction only). § No Phase I or Phase II NR 216 Permit- ted Communities § Plan: River organization develop- ment, information and education, water quality/" sh/aquatic life assess- ment, non-point source assessments. § Management: In-stream/shoreland habitat restoration, land/easement purchase, local ordinance develop- ment. River Protection Grant - WDNR § Planning § Management May 1, annually 75/25 § Plan: Maximum of $10,000 per grant. § Management: Maximum $50,000 per grant. § Dam repair/operation § Dredging *DNR will fund the incremental cost to go from a conventional brush streetsweeper to a high-ef" ciency sweeper when buying a new sweeper. Lake Protection and Classi! cation Grant - WDNR May 1, annually Pre-application with WDNR highly recom- mended. § Purchase Property or Conserva- tion Easement § Restoration of wetlands and shorelands § Development of local regulations or ordinances § Lake management plan imple- mentation projects § Dam repair operation or removal § Purchase of property on which a dam is located § Water safety patrols § Dredging § Sanitary sewer septic systems § Chemical treatment § Aquatic plant harvesting § Operation and maintenance 75/25 § Maximum of $200,000 § Maximum of $100,000 for wetland and shore- land restoration § Maximum of $50,000 for regulations ordinances Urban Nonpoint Source & Stormwater Grant (UNPS&SW)–WDNR Priority: Urban Area Water Quality-Based Projects. Planning, Design, and Construction. Wisconsin administers the USEPA Section 319 monies through this program. Planning: 70/30 Design: 50/50 Construction: 50/50 Acquisition: 50/50 § Max of $85,000 for Plan- ning Project § Max of $150,000 for Construction Project § Projects Involving Land Acquisition and/or Per- manent Easements can request an additional $50,000. § BMP construction for new development § Projects that are not water quality based, projects to solely solve drainage/! ood- ing problems § Dredging projects § Rural projects in priority watershed areas. § Projects to control pollution regulated under WI law as a point source (i.e., NR 216 permitted communities). § Planning projects. Summarized below are a number of the more popular W DNR grant programs. Strand Associates, Inc.® Excellence in Engineering Since 1946 Oshkosh - Anchorage Basin Flood Relief Channel The Anchorage Basin is a 428-acre residential/commercial area in east Oshkosh currently experiencing fre- quent " ooding. This project will convert an abandoned railroad line into a " ood relief channel to alleviate this " ooding. The proposed " ood relief channel will provide a positive outlet to Lake Winnebago to augment the currently undersized storm sewer system serving the area. Construction and replacement of culverts are an integral component of the proposed project. An associated project in this basin, as shown in the table on the front of this brochure, is the Murdock Detention Basin. This detention basin is a component of the overall " ooding relief plan for the Anchorage Basin and received funding for property acquisition. Estimated Construction Cost: $2 million Whitewater - Cravath and Tripp Lakes Stormwater and Erosion Control Ordinances This project was prompted by a study showing that Year 2000 pollutant loadings were expected to result in total phosphorus concentrations in Cravath and Tripp Lakes that exceed the recommended levels for recreational use and for the maintenance of a warm-water ! shery. To begin to ad- dress these ! ndings, the City of Whitewater sought to establish administrative authority to control stormwater discharge from construction and post-construction sites. The stormwater and erosion control ordinances will minimize impacts of future de- velopment and prevent lake degradation. In addition, water- shed divide and land use mapping was completed to facilitate future analysis of pollution sources and resultant water quality problems in the lake. Technical Assistance Cost: $10,000 Bristol - Pond A Restoration and Enhancement Pond A was originally built as a " ood control pond but provided minimal water quality bene! ts. This project rehabilitated the existing pond that had ! lled in with sediment and was becom- ing a nuisance and potential hazard because of stagnant water and steep slopes. The project design included 4:1 side slopes, a 10’ safety shelf, sediment forebay, outlet control structure, 100-year emergency over" ow, and shoreline/wet edge seed mix around the perimeter of the pond. The restoration brought the pond into compliance with WDNR Wet Detention Basin Standard and will remove 80% of the total suspended solids reaching the pond from the 73-acre commercial land use watershed. In addition, the pond will control peak discharge up to a 100-year storm. Pond Construction Cost: $148,000 Evansville - Lake Leota Watershed Study As the ! rst step in implementing recommendations in our 2004 Lake Dredging Study, we prepared and submitted two successful Lake Planning grants for the City of Evansville. The study’s ultimate goal is to identify and address upstream sedimentation and nutrient solutions in an effort to protect the City’s upcoming dredging investment. Lake Leota is an impoundment of Allen Creek which originated as a mill pond in 1847. Over time, Lake Grant-Funded Stormwater Projects Leota has ! lled in resulting in a current, average lake depth of 18-inches or less. This study focused on identi! cation of source areas of nonpoint source (NPS) pollutants, estimation of pollutant loading (TSS and TP) in the lake from upstream agricultural lands and streambank erosion, exploration and recommendation of BMPs to improve watershed conditions, research of funding sources, and development of an informational and educational framework. Technical Assistance Cost: $26,666 Hartland - Phase II Stormwater Quality Management Plan The Village of Hartland was designated by the USEPA and the DNR as a permitted municipality under Phase 2 Stormwater Rules. In response to this designation and in an effort to protect the Bark River and other local resources, the Village budgeted funds to develop a Stormwater Management Plan. The primary objective of the plan was to reduce the adverse impacts of nonpoint source stormwater runoff discharging from the Village to adjacent water resources including the Bark River, nearby wetlands, and groundwater resources. The project mapped the urban discharge points and drainage basins within the Village, evaluated current Village practices and programs, developed SLAMM computer models to estimate pollutant loadings to each identi! ed outfall, identi! ed and evaluated potential types and locations of Best Management Practices (BMPs) to address impacts on stormwater runoff, developed a Capital Improvements Plan on prioritization of stormwater management practices, including stormwater management report, and assistance with grant administration. Technical Assistance Cost: $53,000 Madison - Wingra Creek Streambank Restoration - Phase I Wingra Creek is a major watercourse in the Lake Monona watershed, draining approximately 10 square miles of area in the City and Town of Madison, including UW-Madison Arboretum lands. The Wingra Creek watershed has experienced rapid urbanization, including signi! cant ! lling of adjacent wetlands over the past century. This has contributed to signi! cant erosion of the streambanks. The goals of this project were to restore streambanks, improve aesthetics of the watercourse, and reduce sediment loss to downstream areas. Since the creek, long ago, was a manmade channel, the City requested that we re-meander the creek to provide greater interest to the route. Streambank restoration techniques implemented on this project are: vegetated geogrid, vegetated boulder revetment, littoral shelf, sack gabions, toe stone protection, and paddling access. Two in-line stormwater treatment devices were also part of this project to help reduce sediment loads to the creek. Technical Assistance Cost: $44,300 Bristol - Pond A (Before) Whitewater - Cravath Lake Waterfront Wingra Creek - (Before) Bristol - Pond A (After) Wingra Creek - (After Rendering) Taft Ave Kn a p p S t W. S o u t h P a r k A v e US H W Y 4 1 ST H W Y 4 4 W 20th Ave S O a k w o o d R d W 9th Ave Witzel Ave US H W Y 4 1 S W e s t h a v e n D r S W a s h b u r n S t S W a s h b u r n S t Badger Ave Un i v e r s a l S t W Waukau Ave Cl a y R d Allert o n D r Badg e r A v e ST RD 91 S W e s t h a v e n D r S K o e l l e r S t Maricopa Dr N W e s t f i e l d S t S W e s t f i e l d S t Dickison Ave Cu m b e r l a n d Tr a i l Ma r i c o p a D r Co v i n g t o n D r Ci t y o f O s h k o s h To w n o f A l g o m a City of Oshkosh Town of Algoma Town of Nekimi To w n o f N e k i m i Ci t y o f O s h k o s h Town of Algoma City of Oshkosh FO X R I V E R CAMP B E L L C R E E K Town of Nekimi Town of Algoma SAW Y E R C R E E K 0 60 30 36 48 54 12 6 21 24 10 3658 27 2516 15 8 42 39 2945 3843 18 40 6 5 20 3150 50 3 1 2918 40 5 6 3453 26 3 3 1930 58 3 6 44 7 2 1219 2236 2438 3622 43 2 7 3958 51 3 1 6540 7244 1625 1423 3654 9 33 6 0 48 7 6 24 1 9 293 5 24 21 8 18 10 15 10 10 12 12 12 12 24 18 15 8 36 2 2 15 8 12 12 8 18 8 0 12 8 8 15 12 12 8 12 48 12 8 12 21 8 15 8 24 12 12 12 12 15 12 18 8 8 12 12 12 8 12 12 12 18 8 8 15 15 21 8 21 10 18 30 158 10 24 12 18 18 36 8 24 8 8 8 15 12 27 15 15 24 10 15 18 15 8 24 48 6 18 12 12 12 15 18 15 0 12 8 8 5836 10 6 0 15 8 27 30 3453 12 10 12 15 12 18 24 8 8 8 18 12 18 15 0 12 12 12 15 36 15 8 18 12 10 21 21 15 12 8 12 8 12 18 8 12 8 12 12 6 8 18 24 10 15 42 8 12 18 24 18 8 12 8 8 8 58 3 6 818 24 12 12 8 6 12 8 12 0 18 12 12 12 8 12 15 12 12 12 8 12 8 8 12 12 12 8 12 21 15 30 42 12 15 12 24 21 12 6 15 0 24 12 12 12 15 12 15 0 5836 8 12 108 8 18 12 8 21 18 18 18 8 10 12 15 21 15 12 12 24 8 8 10 18 0 10 12 15 21 21 27 8 12 12 21 15 12 50 3 1 24 24 8 12 21 0 30 10 8 12 21 8 8 8 18 8 12 8 12 24 24 12 8 8 0 12 12 8 8 12 8 24 12 30 21 12 12 30 30 12 8 15 36 12 12 12 12 18 24 18 8 12 8 18 2438 8 24 12 8 8 0 12 12 0 10 21 18 15 12 8 12 12 15 21 12 8 12 18 15 12 12 36 8 8 36 42 12 18 24 8 12 12 12 18 8 18 24 12 12 8 0 12 0 15 15 8 0 10 8 8 12 8 0 12 12 18 12 8 12 8 12 12 12 12 12 24 15 24 12 8 15 24 12 8 8 12 12 24 12 12 12 8 18 12 12 8 36 4327 24 12 2516 12 12 12 10 0 1930 8 18 24 12 8 18 12 2438 12 8 8 8 8 12 18 12 0 8 12 12 8 15 48 15 15 15 12 15 0 8 19 3 0 3658 15 12 18 8 2945 8 8 8 15 50 3 1 12 18 12 8 8 8 0 24 21 12 15 18 21 21 0 8 12 10 15 12 12 18 15 12 12 12 10 12 10 12 12 12 48 15 10 10 21 21 36 5 8 8 10 12 12 12 8 15 36 15 12 18 0 18 8 0 8 8 8 42 15 8 12 12 42 36 12 24 8 21 15 30 12 8 4815 0 27 18 8 10 12 42 30 12 12 18 24 24 18 24 12 12 15 12 18 0 8 8 21 6 15 8 36 8 21 27 15 18 15 8 24 10 12 30 18 15 12 8 0 24 8 30 8 12 8 10 15 12 8 6 2412 12 6 0 27 15 12 12 8 12 15 12 36 12 18 12 8 15 18 30 8 12 0 12 18 8 10 18 15 15 12 0 0 12 5836 8 8 12 15 12 15 30 8 6 8 12 10 12 36 0 8 8 15 18 20 18 8 18 12 18 15 0 8 29 1 8 24 15 15 12 12 12 42 30 8 18 10 15 8 12 24 8 27 8 12 15 15 8 8 15 12 15 10 8 8 10 12 18 10 12 8 21 12 15 15 15 15 6 12 8 8 12 36 8 27 15 10 24 12 12 12 12 21 15 10 18 20 10 12 8 8 15 15 18 8 8 8 0 8 0 15 8 12 15 15 8 30 18 12 15 8 8 21 21 24 15 60 12 12 24 8 6540 24 15 15 30 12 10 12 8 15 8 15 8 12 10 15 12 15 30 12 18 27 10 12 0 8 12 12 8 24 12 8 12 0 18 18 18 24 15 24 18 18 12 8 15 12 30 12 8 8 18 18 12 12 8 15 8 12 8 21 12 21 8 15 21 24 2945 30 18 8 8 12 15 18 8 10 18 27 12 6 12 15 12 8 18 15 15 12 36 1219 15 12 6 12 12 12 30 18 12 12 8 8 12 27 12 65 4 0 24 12 10 15 15 15 8 12 15 24 30 12 2516 24 8 6 15 12 12 48 15 12 12 15 8 8 12 12 8 21 0 18 12 12 18 8 36 42 12 15 24 15 18 10 42 27 36 0 8 8 24 12 10 12 24 8 30 8 24 12 18 218 15 2438 15 4327 12 8 12 0 10 18 12 8 27 0 18 20 18 8 12 15 8 12 12 18 12 8 8 18 12 15 12 12 8 12 18 18 6540 6 10 12 10 15 18 15 15 12 10 42 18 24 18 8 12 12 8 36 15 27 12 18 1423 0 30 3658 12 12 15 24 12 8 18 8 18 18 12 12 18 18 10 12 8 24 8 24 12 8 15 27 30 42 36 12 8 12 24 18 18 8 15 12 21 24 18 12 12 8 21 24 21 12 15 12 21 12 8 0 10 12 8 12 8 12 21 8 8 12 12 5031 12 12 8 12 21 12 15 30 8 8 29 4 5 8 12 12 12 27 8 12 12 12 31 5 0 12 15 12 8 21 12 18 12 15 12 24 6 12 8 12 18 12 15 30 12 2516 8 24 12 8 8 10 15 15 12 12 15 12 18 6 8 12 12 6 3622 12 12 12 10 19 3 0 12 12 15 24 12 12 12 12 15 10 10 27 6 8 42 8 12 10 12 12 15 18 15 10 12 12 20 18 18 30 24 18 8 8 12 15 15 12 8 30 15 12 15 15 8 10 12 12 12 36 5 8 8 0 0 24 8 30 8 18 24 43 2 7 24 8 12 12 12 12 12 15 12 12 24 12 8 21 15 54 18 18 15 6 24 15 12 15 15 8 12 12 18 12 12 12 15 36 30 21 8 12 0 30 12 10 8 12 15 12 24 12 8 18 SBB-190 CCB-10 SBB-15 SCB-100 SCB-35 CCB-05 SCB-85 SBB-75 SBB-65 SBB-175 SCB-75 SBB-76 SCB-70 SBB-95 SBB-85 SBB-70 SCB-50 SCB-10 NBB-30 SBB-60 CCB-20 SBB-55 SBB-141 NBB-20 SBB-140 SBB-45 SCB-15 SBB-50 SBB-25.A SBB-115 SBB-30 SBB-176 SBB-90 NBB-15 SBB-10 SCB-30 SCB-55 SBB-20 SCB-20 NBB-55 SBB-05 SBB-41 SCB-90 SBB-61 CCB-15 SBB-25.D SCB-95 NBB-10 SCB-25 SBB-71 SCB-80 SBB-40 SCB-40 SBB-135 SCB-60 SBB-80 SCB-65 SBB-25.F SBB-25.B SBB-185 SBB-180 NBB-45 NBB-25 SBB-42 NBB-05 SCB-05 NBB-40 SBB-25.E SBB-170 SBB-35 NBB-35 SBB-145 SBB-25.C SBB-155 NBB-50 SBB-105 SBB-120 SCB-45 SBB-165 SBB-130 SBB-150 SBB-110 SBB-100 SBB-160 DRAINAGE AREA MAP NORTH BRANCH CAMPBELL CREEK ST ORMWATER STUDYADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, W ISCONSIN FI GUR E 2 . 01 - 1 1-3 8 2 - 0 3 0 0 1,500 3,000750 Feet ³ S: \@ SA I \ 351 - -4 0 0 \38 2\ 030 \ D a t a\GI S \ Re p or t F i gur es\ Fi gu r e 2 . 0 1 - 1 - D r ai n a g e Sy st e m 22 x3 4 . m x d Witzel Ave US H W Y 4 1 60 12 24 18 30 15 27 21 19 3 0 3654 8 20 10 1423 6540 2820 12 12 15 18 12 12 30 8 12 15 30 10 12 10 15 12 1512 18 24 20 24 18 12 8 12 18 15 12 12 12 12 12 18 15 12 12 24 12 18 15 12 12 18 12 24 30 12 15 15 SCB-35 SCB-10 SCB-30 SCB-25 SCB-40 SCB-20 SCB-15 CCB-10 NBB-40 SCB-50 SCB-E NBB-45 NBB-55 SCB-B SCB-C NBB-35 SCB-D NBB-50 SCB-A SCB-45 NBB-25 Hwy 41 Updated Basins 0 600 1,200300 Feet Legend Municipal Boundary Drainage Basin Boundary Sub Drainage Basin Boundary Updated Basins Landmark Plaza Storm Manhole Storm Sewer Culvert Basin ID DesignationSCB-50 ROCKW E L L AVE. HIG H AVE . ALG O M A B L V D . PEA R L A V E . W. 5TH AVE. W. 3RD AVE. BISMARCK AVE. DA K O T A S T . WITZEL AVE. N. C A M P B E L L R D . W. W. W. W. W. AVE. AVE. AVE. AVE. AVE. 6TH 8TH 9TH 10TH 11TH DA K O T A S T . DA K O T A S T . ST . GE O R G I A W. SOUTH PARK PL U M M E R S T . FLORIDA AVE. W. 17TH AVE. DE L A W A R E ST . W. 20TH AVE.W. 20TH AVE. PR I V A T E R D . PL. DR. W. 9TH AVE. AVE. W.SOUTH PARK AVE.SA N D E R S S T . W.17TH AVE. FLORIDA ERIE AVE. AVE. RU G B Y SA N D E R S FA I R L A W N ST . ST . ST . BE R G E R ST . CONCORDIA AVE. KN A P P ST . OSBORN W.12TH W. W. W. 6TH 8TH 9TH W.10TH 11TH AVE. AVE. AVE. AVE. AVE. AVE. AVE. AVE. ID A H O ST . W.7TH WY O M I N G ST . SA W Y E R ST . W. 12TH AVE. W. 11TH AVE. W. 10TH AVE. SA W Y E R MA S O N KA N S A S WE I S B R O D ST . ST . ST . ST . KENSINGTON AVE. DE V O N S H I R E D R . DE V O N S H I R E D R . CAMBRIDGE AVE. CA N T E R B U R Y DR . HU N T I N G T O N P L . W.9TH AVE. S. E A G L E ST . W.7TH AVE. W.AVE. AR M O R Y WI N D S O R RE I C H O W S. W E S T F I E L D MO R E L A N D ST . ST . ST . PL . S. WE S T F I E L D LI L A C ST . ST . W. 7TH AVE. 6TH HA W T H O R N E S T . CRYSTAL SPRINGS AVE. RU G B Y ST . ST. RE I C H O W S T . W.5TH W.5TH AVE.AVE. BISMARCK AVE. W. 4TH AVE. DEMPSE Y T R . BISMARCK W. 2ND AVE. W. 3RD AVE. W. 4TH AVE, W. 4TH AVE, GLEN AVE. WITZEL WITZEL AVE.AVE. FAUST AVE. NATIONAL AVE. CLAYTON CT.SKYVIEW AVE. LOMBARD AVE. SOUTHLAND AVE. TAFTAVE.AVE. N. CA M P B E L L R D . RUSH AVE. AVE. AVE. AVE. AVE. AVE. PIERCE ADAMS COOLIDGE TYLER VANBUREN PORTER LI L A C S T . S. W E S T F I E L D ST . RE I C H O W S T . S. M E A D O W S T . S. E A G L E S T . S. L A R K S T . SA W Y E R ST . MA S O N ST . GU E N T H E R ST . FO S T E R S T . DURFEE A V E . KN A P P ST . ID A H O ST . N. N. N. N. N. EA G L E LA R K SA W Y E R SA W Y E R SA W Y E R ST . HA W K DO V E ST .ST . ST . ST . ST . ST . N. N. N. EA G L E ME A D O W LA R K ST . ST . ST . JO S S L Y N ST . BA U M A N ST . BR O O K W O O D C T . N. W E S T F I E L D ST . 4TH AVE. TR . SU L L I V A N S T . N. W E S T H A V E N DR. DR. WA Y W. 4TH AVE. DR. CT . OV E R L A N D DR. OSBORN AVE. OSBORN AVE. AVE.SOUTHLANDSOUTHLAND AVE. LN. ROSEWOOD KN A P P ST . DA K O T A ST . CAM P B E L L S. N. ST . WE S T F I E L D S. S. S. SY C A M O R E S T MARICOPA D R . TAFT AVE. JO S S L Y N N S T . STATE RD. 91 STATE R D . 4 4 CL A Y R D . CL A Y R D . STATE R D . 4 4 DR. BE L L F I E L D DR . W. WAUKAU AVE. STATE R D . 9 1 W. WAUKAU AVE. S. W A S H B U R N S T . U. S . H W Y . 4 1 S O U T H B O U N D U. S . H W Y . 4 1 N O R T H B O U N D PO B E R E Z N Y R D . PO B E R E Z N Y R D . TR. EN T E R P R I S E W. WAUKAU AVE.W. WAUKAU AVE. AVE. FO R E S T HO M E GOYK E A V E . NEUN T E U F E L L N . KN A P P S T . WAU P U N R D . VERN AVE. KILPS AVE. S. W A S H B U R N S T . U. S . H W Y . 4 1 S O U T H B O U N D U. S . H W Y . 4 1 N O R T H B O U N D UNIVERSAL ST. UN I V E R S A L ENT E R P R I S E W. 20TH AVE. S. O A K W O O D R D . S. O A K W O O D R D . STATE R D . 4 4 U. S . H W Y 4 1 - N O R T H B O U N D U. S . H W Y 4 1 - S O U T H B O U N D S. W A S H B U R N S T . UN I V E R S A L S T . BADGER AVE. BADGE R A V E . UNI V E R S A L S T . W. 9TH AVE. S. O A K W O O D A V E . S. O A K W O O D A V E . LI N D E N O A K S D R . MEADOWBROOK RD. HOMESTEAD DR. HUNTER S PL. PH E A S A N T C R E E K D R . FA I R F A X S T . REBECCA RUN WH E A T F I E L D RUSC H F I E L D DR. WE L L I N G T O N DR . MOCKINGBIRD WAY CREEK SAWYER DR . WHEATFIELD WA Y TI M O T H Y T R . RUS C H F I E L D DR. KILLARNEY CT. NEWPORT AVE. FOX TAIL LN. BE R N H E I M ST . HUNT E R S GL E N DR . WINDHURST DR. MONT C L A I R MERE W O R T H CT.MONTCLAIR PL. WO O D S T O C K ST . LE N N O X S T . S. W E S T H A V E N D R . BRE N T W O O D D R . CH A T H A M D R . CH A T H A M C R . BR E N T W O O D C R . NEWPORT AVE.NEWPORT CT. CHATH A M C T . MONTCLAIR PL. TEMPLETON PL. AR L I N G T O N D R . DR. CRE S T V I E W D R . MA R I C O P A D R . LAMPLIGHT CT. GASLIGHT CT. CT . CA N D L E L I G H T DO N E G A L C T . GA L W A Y C T . VILLAGE LN. VILL A G E L N . WESTHAVEN CR. S. W E S T H A V E N D R . ALLERTON DR. ALLER T O N D R . CO V I N G T O N D R . TH O R N T O N D R . WELDON CT. VILL A P A R K D R . DE E R F I E L D D R . MA R I C O P A D R . S. WA S H B U R N S T . W. 20TH AVE. S. WA S H B U R N S T . CU M B E R L A N D T R . CU M B E R L A N D T R . MARICOPA DR. DICKINSON AVE. MA R I C O P A D R . ARDM O R E T R . S. W A S H B U R N S T . HE R I T A G E T R . GREE N F I E L D T R . HERITAGE C T . ARCADIA AVE. VIKING C T . KINGSTON PL. CAM D E N L N . S. W E S T H A V E N D R . MA R I C O P A D R . W. 9TH AVE. MA R I C O P A D R . VIKING P L . W. 9TH AVE. U. S . H W Y 4 1 - N O R T H B O U N D U. S . H W Y 4 1 - S O U T H B O U N D S. K O E L L E R S T . U. S . H W Y 4 1 - N O R T H B O U N D U. S . H W Y 4 1 - S O U T H B O U N D MENARD DR. WITZEL AVE. S. O A K W O O D R D . N. O A K W O O D R D . QUA I L R U N DR . KI R K W O O D D R . RADDISON AVE. KI R K W O O D D R . E. PHE A S A N T C T . W. PHE A S A N T C T . QUAIL CT . FO X FI R E BROMFIELD DR. RO L L I N G G R E E N CIRCLE DR . FO X F I R E LU L L A B Y E R D . MANOR DR. SO U T H G A T E D R . OA K M A N O R D R . OA K P A R K D R . WYLDEWOOD RD. DANBE RD. EAST GATE DR. DR.OAK CREST OAK MANOR DR.COU N T R Y S I D E C T . WYLDE OAK CT. OAK WYLDE DR . FITCHBURG CT. WY L D E OA K OV E R L A N D TR . LN. OV E R L A N D T R . WOODRIDGE DR.WOODRIDGE DR. FO R E S T V I E W RD. RD . VIEW FO R E S T WY L D E B E R R Y WY L D E B E R R Y LN . WITZEL AVE.WITZEL AVE. S. K O E L L E R S T . S. W A S H B U R N S T . U. S . H W Y 4 1 S O U T H B O U N D U. S . H W Y 4 1 N O R T H B O U N D N. K O E L L E R S T . N. W A S H B U R N S T . U. S . H W Y 4 1 S O U T H B O U N D U. S . H W Y 4 1 N O R T H B O U N D SU L L I V A N S T . BA R T O N R D . MA R Y D E N R D . S. W E S T H A V E N D R . GR E E N F I E L D T R . HE R I T A G E T R . KINCAID AVE. GR A C E L A N D HE N N E S S Y S T . DR . ABBEY AVE.ABBEY AVE. GOLDEN AVE. GRACELAND CT. KATY CT. GR E E N F I E L D T R . GR A C E L A N D D R . GREE N F I E L D T R . GR A C E L A N D D R . NICOLE CT. WESTHAVEN CT. S. W E S T H A V E N D R . WE S T B R O O K D R . BROOKVIEW C T . MEADOWBROOK CT. WE S T B R O O K D R . NOEL CT. BLAKE CT. DR . SUNNYBROOK LAK E PO I N T E DR . SU N N Y B R O O K DR . SANDSTON ECT.FALL CREEK LN. WI N D I N G B R O O K DR . LAKES I D E C T . WI N D I N G B R O O K SECURITY D R . N. WES T H A V E N HAVENWOOD DR. STATE R D . 2 1 W E S T B O U N D YORKTON PL. WESTMOOR RD. WESTMOOR RD. BISO N PT . LINWAY CT. LI N W A Y C T . N. O A K W O O D R D . STATE RD. 21 WESTBOUND STATE RD. 21 EASTBOUND WESTMOOR RD. GULL I G C T . WE S T M O O R C T . CO L L E E N C T . AMAN D A C T . DAN I E L C T . SCENIC DR. WY L D E O A K D R . SC E N I C C T . SCENIC DR. HO N E Y C R E E K R D . FO R E S T V I E W D R . HONEY CREEK RD.TR I L L I U M TR. HO N E Y C R E E K R D . CI R . CREEK CREEK SID E D R . STATE R D . 2 1 E A S T B O U N D HU B B A R D S T . DE L A W A R E S T . MC C U R D Y S T . GE O R G I A S T . GE O R G I A S T . W. 18TH AVE. W. 19TH AVE. KN A P P S T . KN A P P S T . FA B R Y S T . HARMEL AVE. SA N D E R S S T . LAAGER LN. W. 19TH AVE. W. 18TH AVE. OR C H A R D L N . OR C H A R D C T . BLOSSOM CT. APPLE CT. PAR K ST . INDIGO DR. pvt VI R G I N I A AL E X A N D R A C T . SOU T H W. VEN T U R E DR. W. 20TH AVE. KOEL L E R S. ST . KN A P P S T . FO U N D A T I O N R D . WI T T M A N R D . KN A P P S T . HIGH OAK DR. BU R N W O O D D R . BU R N W O O D D R . KNAPP ST. PO B E R E Z N Y R D . KN A P P S T . RIPON L N . PARK AVE. SOUT H W. S. K O E L L E R S T . STATE R D . 4 4 FOUND A T I O N R D . VERN SCHAICKSCHAICK AVE.TO L L C T . MUSE U M R D . SCHAICK AVE. S. K O E L L E R S T . CAPITAL DR. CA P I T A L D R . DE L A W A R E S T . ECKARDT CT. pvtINDIGO DR. MAGNOLIA AVE. pvt W. 20TH AVE.W. 20TH AVE. WYLDEFLOWER CT. MOON C I R . HOLLY CT. ACORN CT. HAVENWOOD DR. WY L D E W O O D DR . REBECCA RUN WITTMAN RD. AUDREY LN. EI D E S T . CO R R I G A N L N . BRUGGER AVE. GALATIN AVE. EIDE RD. CELEBRATION WAY KILPS AV E . AVE. DR. VERN AVE. DO O L I T T L E R D . DO O L I T T L E R D . ST I T S R D . RI L E Y L N . NEUNTEUFEL LN. SCHAICK AVE. BI N D E R LN . WI T T M A N R D . WI T T M A N R D . CELEBRATION WAY WI T T M A N R D . CAP AVE.CAP AVE. KN A P P S T . WITTMAN RD. WITTMAN RD. ST I T S R D . ST I T S R D . LINDBERGH LINDBERGH HO M E FO R E S T KILPS AVE. GALATIN AVE. KNAPP ST. KILPS AVE.AVE. RD.RIDGE WEST DR. pvt POINTE S. W A S H B U R N S T . DR . PH E A S A N T CR E E K CT.BENNETT DR . CR E E K PH E A S A N T JU D Y LE E DR . FAIFAX ST. FA I R F A X ST . WE L L I N G T O N CT . HAYWARD AVE. NO R M A N C T . McCLONE DR. IN S U R A N C E WA Y WH I T E T A I L ATLAS A V E . ATLAS AVE. GLO B A L P A R K W A Y GL O B A L P A R K W A Y LN . QUAIL RUN DR. WOODL A N D AVE. ST. FO S T E R AVE.AVE.BISMARCK HE I D I DR. HAVEN HOLLOW CT.HALLIE HE I D I HA V E N C T . JO H N M O O R E D R . BAILEY CT . WILDERNESS PL. JU D Y L E E C T . RUFFED G R O U S E WAY SOUT HPOND C T . CUTT E R CT. MA R S H C R E E K R D . OLD A L E X C T . BELLFIE L D EL K R I D G E DR. TR. CAS E Y MOCKINGBIRD WAY ROBIN AVE. TAFT AVE. WITZEL AVE.N M O N T I C E L L O D R . p v t N. K O E L L E R S T . WESTOW N E A V E . N. W A S H B U R N S T . N. W E S T H A V E N D R . PATRIOT DR . SPRINGMILL DR. S- 1 3-1 033 P- 0 6-7 73 S- 1 3-8 74 P- 1 6-6 47 L385 P-AEW-1 P-2980-1.5 P-06-493 P-13-550 L381 P-06-602 P-13-764 P- 1 6-6 46 D-2449-1.2 P-06-678 P-13-1363 P-0 6-474 P- 1 6-4 27 P- 1 3-1 1 87 P- 1 6-4 29 P- 1 6-4 26 P- 1 3-8 49 P- 1 6-4 30 P- 1 3-4 59 P-06-679 P- 1 3-1 1 75 P-0 6-4 71 P- 1 3-4 60 P-13-4 P- 1 3-1 1 78 P-06-462 P-06-770 P-1 3-1035 P-W M P -1 P-06-486 P-06-490 P- 0 6-6 77 P- 1 3-8 46 P-13-559 P-13-456 P-13-561 P-13-547 P-13-455 P-A EW-28 P-06-685 P- 1 3-1 1 85 P-13-659 P- 0 6-6 88 P-06-552 P-06-1357 P- 1 3-7 91 D-A E W- 32 P-0 6-8 37 P- A EW -1 3 P-06-653 O- AE W -13 P-1 3-11 81 P-13-453 P-13-874 D-4 0D-1 P- 1 6-4 28 P- 0 6-8 47 D-WPS C-1 P- 1 3 -7 9 3 P-1 3-765 P-0 6-489 P-1 3-571 P-13-2 P-2751-4 P-13-1220 P-13-555 P- 1 6-4 25 P-1 3-1070 P-2125-75 P- 0 6-8 43 P-13-1365 P-13-2619 D-LP-3 P-06-553 P- 1 3-1 221 P- 0 6-6 80 P-13-1216 D-4 0D-1 .1 D-AEW-37 P-13-660 P-13-873 D-4 0D-2 6 L3 83 P-13-457 D-R R-20 P-13-853 P- 0 6-1 293 D-4 0D-2 4 P-13-983 P- 1 3-1 1 88 P-06-844 P-13-554 D-R R-19 D-D-OF-1 D-AD -3 D-4 0D-3 0 P-1 3-5 70 D-4 0D-2 7 D-4 0D-2 8 P-13-1362 D-R R-18 P-A EW-10 D-LP-4 D-4 0D-2 9 D-4 0D-2 5 D-A E W- 17 P-13-1041 D-RR-5 D-RR-9 D-A E W-7 D-RR-8 D-A E W- 5 P- 1 3-1 1 83 D-RR-13 P-13-2626 P-13-792 D-4 0D-9 D-R R-17 D-AD-1 D-D K- 5 P- 2 751- 2 D-RR-4 D-AE W-2 D-RR-14 D-RR-10 P-1 3-866 D-44D-9 D-4 0D-2 D-RR-6 D-40D-14 P-0 6-470 P-13-2629 D-AD-5 P-2 531-3 D-4 0D-1 1 P-2 531-2 D-RR-7 D-4 0D-1 5 P- 0 6-1 371 D-D K-3 P-AEW-22 D-4 0D-2 0 D-AEW-11 D-D -OF- 2 D-4 0D-8 P-06-841.1 D-4 0D-1 3 D-4 0D-4 P-13-562 D-4 0D-2 3 P-13-794 P-13-1364 P-1 3-1 1 79 D-44D-5 P- 1 3-8 64 D-4 0D-1 2 D-4 0D-3 D-44D-8 D-RR-3 P- 0 6-8 48 P-06-1293.2 P-13-6 D-DITC H D-RR-12 P- 1 3-2 371 D-44D-7 D-4 0D-7 D-4 0D-5 D-4 0D-1 8 D-44D-6 P-13-557 P-4 000-94 P-13-454 D-RR-16 P-06-468 D-4 0D-1 0 P-06-494 D-AD-4 P-13-2623 P-06-684 D-2 449 -1. 4 D-A E W-9 D-2980-1 P-A EW -8 P-06-686 P- A EW -3 P-4000-93 P-06-687.1 P-13-1033 P-13-1190 P-06-846 P- 1 3-5 69 D-4 0D-1 9 P-13-766 D-RR-2 P-13-1003 P-13-847 P- 4 000- 92 P-13-549 P-13-551.1.1 P- 1 3-1 280 P- 0 6-4 87 D-AD-2 P-1 3-420 P- 1 3-1 071 D-40D-17.1 P-06-469 P-13-1219 P- 1 6-4 69 P-13-1217 D-LP-2 D-44D-2 D-40D-16 D-RR-1 P-1 3-8 67 D-AEW-35 D-L P-5 P-13-1036 P-1 3-1 1 74 P-AEW-33 D-RR-11 D-WPSC-2 P-13-2622 D-D -OF-3 D-D K- 4S P-13-2613 P-13-551.2.1 P-2 980-4 D-DK-2 P-1 3-852 D-DK-1 P-AEW-40 P-2 301-1 P-06-473.1 P-06-473.2 P- 1 3-1 001 P-40D-22 P- 1 6-4 95 P-A EW -2 6 P06-1293.1 D-40D-6.1 P-13-871 P-2 751-3 D-AEW-21 P-2531-1 P-13-2614 P-2751-1 P-0 6-640 P- A P- 3 P-13-999 P-2449-1.6 P-13-1218 D-D K- 4N D-4 0D-2 1 P-AEW-34 P-13-548 D-RR-15 P-13-1703 p-WM MH-1 D-4 0D-6 P-WM P-2 P-13-1000 P-1 3-4 58 P-13-1189 P-13-2381 P-13-452 P-16-487 P-06-1353 P- 0 6-1 388 P-0 6-8 42 P-2301-3 D-AEW-25 P-STR-10.1 D-AEW-31 D-44D-4 D-40D-16.1 P- 1 3-4 71 P-AEW-16 D-AEW-23P-AEW-24 P-13-558 D-40D-31 P-13-1038 P-13-2625 P-13-546 P-STR-5.1 P- 2 449- 1.3 D-AEW-12 D-2980-3 P-4000-91 P-13-568 P-06-1370 P-13-2030 P-13-1292 D-13-1283 D-AEW-27 P-13-1281 P-AEW-30 P-06-1387 P-06-1391 P-06-467 P-2980-2 P-AEW-18 P-2301-1.1 P-06-836P-06-472 P-LP-1 P-06-1355 D-40D-17 P-2449-1.5 P-AEW-20 D-44D-1 P-AEW-15.1 P-13-2029 P-13-2304 P-06-841 P-06-1389 P-13-1279 P-2301-2.1 P-13-869 P-13-1282 P-2690-1 P-2301-2 P-13-1844 P-AEW-14.1 P-13-1704 P-13-2411.1 P-AEW-36 P-06-1392 P-13-2382 D-44D-3 P-06-1062 D-AEW-19 P-06-1282 P-13-552 P-06-845 P-13-1032 P-2449-1.1 P-06-492 P-06-687 D-LP-6 P-13-875 P-13-2624 P-06-1356 P-06-1354 S:\@SAI\351--400\382\030\Data\GIS\Report Figures\Figure 3.02-1 - Pipe Capacities 34x46.mxd EXISTING CONDITIONS PIPE NETWORK NORTH BRANCH CAMPBELL CREEK STORMW ATER ST UD YADDENDUM NO. 1CITY OF OSHKOSHWINNEBAGO COUNTY, WISCONSIN FIGURE 3.02-11-382.030 Legend Storm Sewer Landmark Plaza Basin Campbell Creek Basin North Branch Basin South Branch Basin Sawyer Creek Basin KN A P P S T WITZEL AVE TAFT AVE N K O E L L E R S T W 9TH AVE W 5TH AVE US H W Y 4 1 US H W Y 4 1 MA S O N S T JO S S L Y N S T DO V E S T S W A S H B U R N S T HA W K S T OSBOR N A V E N S A W Y E R S T N L A R K S T N W E S T F I E L D S T N W A S H B U R N S T SOUTHLAND AVE ADAMS AVE PIERCE AVE S K O E L L E R S T W. 9TH AVE BISMARCK AVE S E A G L E S T RE I C H O W S T S S A W Y E R S T RUSH AVE W 6TH AVE COOLIDGE AVE GR A C E L A N D D R BA U M A N S T S W E S T F I E L D S T W 7TH AVE S L A R K S T TYLER AVE GU E N T H E R S T LI L A C S T WE S T B R O O K D R AR M O R Y P L N E A G L E S T FO S T E R S T W 11TH AVE ROBIN AVE MA R I C O P A D R ABBEY AVE PORTER AVE N M E A D O W S T CU M B E R L A N D T R MO R E L A N D S T ARTHUR AVE KA N S A S S T W SOU T H P A R K A V E VAN BUREN AVE DURFEE A V E W 4TH AVE W 2ND AVE W 3RD AVE FAUST AVE WI N D S O R S T SU L L I V A N S T SKYVIEW AVE HE N N E S S Y S T NATIONAL AVE W 10TH AVE CRYSTAL SPRINGS AVE W 12TH AVE DE V O N S H I R E D R KENSINGTON AVE ARDM O R E T R LINWAY CT pvt MENARD DR COVI N G T O N D R GOLDEN AVE LUKE LN LO C U S T S T WE I S B R O D S T VIL L A P A R K D R CLAYTON CT THORNTON DR S M E A D O W S T HU N T I N G T O N P L HA W T H O R N E S T BR O O K W O O D C T N EAGL E S T N E A G L E S T S W E S T F I E L D S T S S A W Y E R S T SU L L I V A N S T VAN BUREN AVE W 7TH AVE W 7TH AVE N L A R K S T W 6TH AVE W 4TH AVE W 10TH AVE 0 792 79 6 804 78 8 80 8 79 8 790 78 6 766 794 770 776 768 784 782 780 764 806 83 0 816 762 81 8 82 6 800 82 2 81 2 772 802 81 4 83 6 778 82 8 760 774 758 81 0 83 2 82 0 756 75 2 824 846 748 83 8 842 844 754 84 0 83 4 75 0 738 734 73 0 744 728 746 736 72 0 718 732 72 2 716 712 742 714 710 84 8 702 724 740 706 708 850 704 852 726 700 854 87 8 698 696 692 694 856 858 86 0 86 4 86 2 870 69 0 788 770 0 840 814 756 752 80 0 816 846 71 0 766 838 82 8 0 83 2 752 84 0 784 80 6 804 760 79 6 820 854 79 0 78 4 764 758 754 796 754 79 4 82 4 762 79 0 75 2 788 76 0 79 6 742 764 832 750 780 778 860 77 8 842 82 8 83 4 838 78 6 810 760 79 4 832 788 72 8 81 6 784 77 2 776770 80 4 782 78 0 798 0 76 8 75 4 774 77 8 82 0 842 770 0 776 792 77 2 0 784 836 0 73 0 75 2 796 77 6 792 79 6 83 4 0 79 4 76 4 782 728 79 0 782 75 2 760 752 77 6 78 4 830 77 4 77 8 78 6 79 6 76 2 700 750 75 2 78 4 77 2 762 762 778 754 78 4 760 78 8 810 784 766 782 840 852 796 824 804 784 760 854 0 77 2 798 756 78 8 0 794 770 80 0 792 80 8 77 2 76 0 798 83 8 794 83 6 782 810 84 6 79 0 76 0 794 756 76 4 840 780 760 0 83 4 0 806 77 6 786 76 2 844 836 708 786 758 75 6 78 2 754 81 4 0 788 840 802 79 2 78 4 804 844 750 828 774 750 822 756 79 8 796 758 798 75 0 784 794 784 82 0 802 774 77 0 780 776 810 83 0 0 778 77 2 832 760 822 788 838 0 762 842 784 79 2 81 8 77 4 83 0 78 4 816 83 4 764 77 2 766 84 6 79 2 82 0 83 2 78 0 78 8 78 2 78 8 784 786 77 4 850 79 2 788 834 762 750 0 0 846 0 82 4 796 816 814 760 752 822 79 4 814 784 836 836 75 2 840 82 8 79 6 750 820 806 786 79 8 756 750 808 790 850 778 83 6 75 2 83 4 750 76 2 844 806 0 82 4 79 6 838 75 8 0 710 824 76 8 796 758 782 81 2 77 2 804 78 6 822 75 4 75 2 780 810 75 8 75 8 0 0 782 788 82 6 844 764 794 79 4 816 762 78 2 83 4 794 798 756 77 8 0 792 76 8 752 810 79 4 780 82 4 842 77 2 802 796 80 2 830 794 814 788 76 0 82 4 782 76 8 75 6 784 784 83 6 854 786 838 704 0 770 79 6 83 2 0 78 6 74 8 0 762 806 832 758 79 8 78 6 784 782 82 4 80 0 818 78 6 780 820 752 76 0 786 782 80 0 70 0 800 0 790 76 2 79 0 788 79 4 800 78 0 82 8 83 4 834 78 8 75 8 790 704 83 4 784 75 6 77 4 772 76 2 78 6 762 804 840 79 6 746 82 6 752 78 6 770 0 776 77 6 802 79 8 75 0 764 756 794 762 774 820 782 81 6 752 78 4 75 8 78 0 0 782 81 8 774 77 6 806 764 76 8 77 4 754 77 0 774 826 0 796 748 0 792 82 4 832 808 784 79 2 848 764 786 778 822 824 762 838 0 0 772 772 0 0 83 8 79 2 794 840 792 756 0 75 6 77 8 850 788 786 798 76 0 784 78 2 836848 782 756 77 2 75 6 77 4 790 0 79 2 778 788 748 786 79 4 78 2 83 4 794 822 778 778 75 2 78 6 86 0 788 754 818 752 796 796 828 0 76 8 77 2 774 79 0 798 772 0 812 836 82 0 764 820 782 854 76 4 76 0 818 832 838 0 84 4 70 6 750 80 4 770 752 780 806 834 786 79 2 784 832 764 762 0 788 790 798 782 75 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79 0 75 4 84 2 76 4 83 2 780 756 78 2 784 754 75 4 796 788 756 778 75 0 82 0 770 772 762 0 0 73 0 794 78 6 750 800 77 6 756 79 2 778 80 0 0 0 0 800 77 8 784 846 822 798 778 83 2 782 836 76 0 838 766 848 774 782 75 4 750 83 0 786 76 2 754 78 2 0 774 788 808 794 77 6 752 780 780 748 75 2 79 0 0 778 800 79 8 0 776 78 0 774 754 774 790 0 836 774 77 2 750 848 78 4 0 776 78 2 78 6 77 2 814 786 784 836 770 748 766 79 6 0 762 810 748 0 78 6 834 706 810 828 782 77 4 782 778 75 2 778 78 8 77 2 84 0 782 766 784 800 770 808 82 4 766 836 784 78 4 758 83 484 0 816 80 2 772 75 4 838 0 78 4 83 2 0 79 8 826 818 78 4 832 82 8 76 4 79 4 76 2 77 6 824 794 79 0 78 2 776 0 788 75 6 79 0 0796 780 76 4 794 79 6 82 0 766 796 75 2 0 82 2 79 0 808 78 6 786 790 776 0 846 834 76 2 824 83 4 782 84 8 786 0 0 758 82 4 780 75 4 820 808 750 75 6 0 82 6 76 4 796 768 0 77 4 848 77 6 76 2 780 840 782 76 8 76 0 772 778 812 778 83 8 798 756 77 2 758 752 786 79 8 816 776 76 0 0 83 6 832 814 754 79 6 840 788 83 2 78 8 788 850 75 6 0 75 4 780 762 78 2 780 77 0 774 790 75 0 76 0 848 77 4 774 0 83 2 0 83 0 782 77 6 752 81 4 762 766 800 792 76 0 852 772 78 2 696 754 78 8 83 8 0 79 6 77 4 850 778 0 77 2 79 0 75 6 792 772 752 77 8 78 0 780 786 0 846 776 756 82 4 840 82 8 828 844 770 0 772 844 778 79 6 774 778 78 2 834 848 758 838 782 860 818 79 2 75 4 844 822 78 4 754 78 6 798 83 8 80 0 78 8 75 2 770 74 2 782 82 6 774 83 8 84 4 78 6 830 77 8 77 4 792 752 812 79 6 77 0 76 6 77 8 75 2 784 76 0 0 790 75 8 0 79 4 83 0 77 6 0 780 78 0 782 82 0 798 798 0 786 756 786 762 790 82 6 75 4 752 780 76 4 762 0 78 8 76 4 836 840 772 754 77 6 760 0 78 6 770 82 0 794 81 2 758 78 6 842 838 0 756 824 756 78 2 79 6 764 796 816 838 778 83 4 786 848 788 782 0 77 8 82 0 784 78 8 784 75 8 788 694 77 6 808 778 756 800 782 756 786 78 0 0 0 842 76 2 79 6 792 752 812 792 78 6 76 4 786 798 756 756 79 0 75 4 76 0 766 75 0 762 81 8 796 836 794 76 4 820 76 4 80 4 784 83 0 854 794 754 75 2 0 75 8 83 6 778 77 8 818 75 4 76 8 0 768 80 6 79 8 750 80 2 776 84 4 76 8 780 78 2 760 836 804 79 0 78 6 796 778 75 6 756 820 79 4 822 786 752 0 796 810 0 79 2 0 0 768 0 80 2 85 6 846 78 4 784 836 768 800 842 82 2 82 2 786 826 772 762 846 76 0 780 78 8 76 0 780 79 4 752 75 6 83 2 824 76 6 0 764 788 840 828 758 796 784 816 760 750 782 782 780 77 4 850 762 800 0 706 82 2 83 8 772 0 0 832 852 0 770 81 6 76 8 760 818 80 8 846 760 0 0 754 834 788 76 4 77 2 832 77 2 840 75 8 77 4 0 780 754 756 77 0 790 0 79 2 786 794 80 0 80 8 79 4 818 820 78 4 800 0 77 6 83 2 792 80 2 840 75 8 786 790 850 80 2 772 82 4 802 758 77 8 776 79 0 76 4 792 754 0 790 83 4 0 796 83 0 802 0 75 8 750 78 4 76 0 796 75 6 78 0 784 780 75 6 776 778 80 0 0 83 0 0 78 8 822 78 4 842 77 8 760 752 812 794 76 0 0 798 82 8 76 0 786 80 0 83 8 852 756 822 77 4 77 0 800 796 752 760 78 6 79 4 764 79 6 752 83 8 844 846 76 6 79 6 76 4 784 810 76 2 802 77 8 782 790 0 776 79 8 75 6 0 0 77 4 784 79 0 0 790 76 4 842 838 79 8 778 754 78 6 774 796 756 84 0 778 82 8 764 74 8 77 2 808 74 8 802 81 8 79 0 82 0 78 2 77 4 778 77 8 788 75 0 782 77 8 0 826 75 8 81 0 710 0 82 8 782 78 2 75 0 840 796 79 0 83 8 80 2 750 78 4 77 2 762 85 0 80 6 774 76 0 846 0 830 83 4 81 6 784 76 2 80 8 778 78 8 782 76 8 82 0 77 4 768 78 6 818 760 788 84 4 772 792 78 8 792 0 784 78 4 79 8 838 77 4 832 820 774 766 776 838 800 78 2 78 6 77 2 766 77 4 77 8 848 780 788 786 800 76 8 834 81 0 778 794 780 818 77 8 764 80 0 802 0 75 2 0 766 786 79 6 0 824 786 82 8 856 0 782 76 4 842 812 782 778 786 792 796 70 8 784 80 0 0 840 79 4 80 2 78 0 824 78 6 752 782 824 790 754 750 0 754 76 0 776 83 6 796 0 75 4 750 81 6 830 83 6 76 2 798 766 790 848 0 760 0 75 0 832 77 8 78 2 79 6 76 8 0 78 2 78 2 808 790 780 0 758 0 792 0 846 844 854 780 83 6 780 792 83 4 760 752 792 788 81 4 0 792 78 2 780 76 2 752 816 75 2 0 758 79 2 788 83 4 780 794 802 794 790 0 78 2 78 4 780 80 0 752 796 846 794 784 756 752 854 756 83 4 790 836 804 75 4 764 770 82 6 75 4 780 820 77 0 0 782 754 78 8 770 838 752 846 77 0 78 2 0 79 4 836 76 2 800 69 2 780 766 82 0 748 838 78 8 78 0 754 780 838 774 764 79 2 82 0 0 81 4 778 0 84 2 786 800 818 792 786 83 6 766 782 790 800 784 78 0 83 6 0 786 782 83 4 796 83 8 82 8 80 0 830 84 0 784 76 2 79 0 0 786 778 774 754 840 74 8 788 83 4 750 794 794 75 8 77 4 0 782 784 780 75 8 0 0 0 0 790 78 6 75 4 80 4 0 82 4 0 78 2 754 79 4 790 77 2 774 0 784 75 6 764 774 77 6 78 2 776 750 818 784 766 0 792 780 76 0 832 792 0 76 2 82 8 846 78 8 0 78 4 0 852 784 770 79 0 784 85 0 77 6 846 792 778 83 6 80 8 83 6 754 77 4 78 8 766 0 762 78 6 822 770 83 8 0 79 0 818 0 0 840 794 78 6 782 776 786 810 826 750 0 0 75 2 780 0 752 0 816 842 794 78 2 786 77 2 786 816 830 804 76 8 788 84 6 78 8 78 6 764 0 78 6 84 2 788 0 76 2 778 780 792 0 768 77 2 0 816 826 76 8 77 4 75 4 75 4 79 4 750 81 4 830 818 786 79 0 704 75 0 750 76 2 83 4 794 824 774 844 756 790 764 788 0 83 6 77 2 764 810 81 6 786 768 838 0 80 0 752 756 84 4 752 82 4 840 76 4 838 780 770 786 78 6 778 77 0 838 794 788 752 77 8 0 778 782 780 778 754 802 836 752 790 804 834 796 844 770 778 0 0 78 4 758 782 0 0 76 2 75 2 790 786 772 780 788 756 PIPE CAPACITY ANALYSIS - WITH ALTERNATIVE 13B IN PLACE NORTH BRANCH CAMPBELL CREEK ST ORMWATER STUDYCITY OF OSHKOSHWINNEBAGO COUNTY, W ISCONSIN FIGUR E 4 . 09 -1 1-3 8 2 . 030 S:\@ SA I \ 351 - -4 0 0 \ 38 2\ 030 \ D a t a\ GI S \ Re p or t F i gur es\ Figu re 4 . 0 9 - 1 - A l t 1 3 B P i pe Ca pa c i t y An al ysi s 2 2 x 3 4. mx d 0 700 1,400350 Feet / Legend Storm Sewer Capacity <1 year 1 year 2 year 5 year 10 year 25 year 50 year 100 year Existing Drainage Basin Storm Manhole Storm Sewer Parcel KN A P P S T WITZEL AVE TAFT AVE N K O E L L E R S T W 9TH AVE W 5TH AVE US H W Y 4 1 US H W Y 4 1 MA S O N S T JO S S L Y N S T DO V E S T S W A S H B U R N S T HA W K S T OSBOR N A V E N S A W Y E R S T N L A R K S T N W E S T F I E L D S T N W A S H B U R N S T SOUTHLAND AVE ADAMS AVE PIERCE AVE S K O E L L E R S T W. 9TH AVE BISMARCK AVE S E A G L E S T RE I C H O W S T S S A W Y E R S T RUSH AVE W 6TH AVE COOLIDGE AVE GR A C E L A N D D R BA U M A N S T S W E S T F I E L D S T W 7TH AVE S L A R K S T TYLER AVE GU E N T H E R S T LI L A C S T WE S T B R O O K D R AR M O R Y P L N E A G L E S T FO S T E R S T W 11TH AVE ROBIN AVE MA R I C O P A D R ABBEY AVE PORTER AVE N M E A D O W S T CU M B E R L A N D T R MO R E L A N D S T ARTHUR AVE KA N S A S S T W SOU T H P A R K A V E VAN BUREN AVE DURFEE A V E W 4TH AVE W 2ND AVE W 3RD AVE FAUST AVE WI N D S O R S T SU L L I V A N S T SKYVIEW AVE HE N N E S S Y S T NATIONAL AVE W 10TH AVE CRYSTAL SPRINGS AVE W 12TH AVE DE V O N S H I R E D R KENSINGTON AVE ARDM O R E T R LINWAY CT pvt MENARD DR COVI N G T O N D R GOLDEN AVE LUKE LN LO C U S T S T WE I S B R O D S T VIL L A P A R K D R CLAYTON CT THORNTON DR S M E A D O W S T HU N T I N G T O N P L HA W T H O R N E S T BR O O K W O O D C T N EAGL E S T N E A G L E S T S W E S T F I E L D S T S S A W Y E R S T SU L L I V A N S T VAN BUREN AVE W 7TH AVE W 7TH AVE N L A R K S T W 6TH AVE W 4TH AVE W 10TH AVE 0 792 79 6 804 78 8 80 8 79 8 790 78 6 766 794 770 776 768 784 782 780 764 806 83 0 816 762 81 8 82 6 800 82 2 81 2 772 802 81 4 83 6 778 82 8 760 774 758 81 0 83 2 82 0 756 75 2 824 846 748 83 8 842 844 754 84 0 83 4 75 0 738 734 73 0 744 728 746 736 72 0 718 732 72 2 716 712 742 714 710 84 8 702 724 740 706 708 850 704 852 726 700 854 87 8 698 696 692 694 856 858 86 0 86 4 86 2 870 69 0 788 770 0 840 814 756 752 80 0 816 846 71 0 766 838 82 8 0 83 2 752 84 0 784 80 6 804 760 79 6 820 854 79 0 78 4 764 758 754 796 754 79 4 82 4 762 79 0 75 2 788 76 0 79 6 742 764 832 750 780 778 860 77 8 842 82 8 83 4 838 78 6 810 760 79 4 832 788 72 8 81 6 784 77 2 776770 80 4 782 78 0 798 0 76 8 75 4 774 77 8 82 0 842 770 0 776 792 77 2 0 784 836 0 73 0 75 2 796 77 6 792 79 6 83 4 0 79 4 76 4 782 728 79 0 782 75 2 760 752 77 6 78 4 830 77 4 77 8 78 6 79 6 76 2 700 750 75 2 78 4 77 2 762 762 778 754 78 4 760 78 8 810 784 766 782 840 852 796 824 804 784 760 854 0 77 2 798 756 78 8 0 794 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0 782 784 780 75 8 0 0 0 0 790 78 6 75 4 80 4 0 82 4 0 78 2 754 79 4 790 77 2 774 0 784 75 6 764 774 77 6 78 2 776 750 818 784 766 0 792 780 76 0 832 792 0 76 2 82 8 846 78 8 0 78 4 0 852 784 770 79 0 784 85 0 77 6 846 792 778 83 6 80 8 83 6 754 77 4 78 8 766 0 762 78 6 822 770 83 8 0 79 0 818 0 0 840 794 78 6 782 776 786 810 826 750 0 0 75 2 780 0 752 0 816 842 794 78 2 786 77 2 786 816 830 804 76 8 788 84 6 78 8 78 6 764 0 78 6 84 2 788 0 76 2 778 780 792 0 768 77 2 0 816 826 76 8 77 4 75 4 75 4 79 4 750 81 4 830 818 786 79 0 704 75 0 750 76 2 83 4 794 824 774 844 756 790 764 788 0 83 6 77 2 764 810 81 6 786 768 838 0 80 0 752 756 84 4 752 82 4 840 76 4 838 780 770 786 78 6 778 77 0 838 794 788 752 77 8 0 778 782 780 778 754 802 836 752 790 804 834 796 844 770 778 0 0 78 4 758 782 0 0 76 2 75 2 790 786 772 780 788 756 PIPE CAPACITY ANALYSIS - WITH ALTERNATIVE 16 IN PLACE NORTH BRANCH CAMPBELL CREEK ST ORMWATER STUDYCITY OF OSHKOSHWINNEBAGO COUNTY, W ISCONSIN FIGUR E 4 . 10 -1 1-3 8 2 . 030 S:\@ SA I \ 351 - -4 0 0 \ 38 2\ 030 \ D a t a\ GI S \ Re p or t F i gur es\ Figu re 4 . 1 0 . 1 - A l t 1 6 P i pe Ca pa c i t y An al y s i s 2 2 x 3 4. mx d 0 700 1,400350 Feet / Legend Storm Sewer Capacity <1 year 1 year 2 year 5 year 10 year 25 year 50 year 100 year Existing Drainage Basin Storm Manhole Storm Sewer Parcel