ML13242A356

Shine Draft Responses to Environmental Site Audit Information Needs (1 of 2)

ML13242A356
Person / Time
Site:	SHINE Medical Technologies
Issue date:	08/30/2013
From:	Moser M R NRC/NRR/DLR/RERGUB
To:
Moser M R
References
Download: ML13242A356 (418)

Text

August 30, 2013 NOTE TO: File FROM: Michelle Rome Moser, Project Manager Environmental Review and Guidance Update Branch Division of License Renewal Office of Nuclear Reactor Regulation

SUBJECT:

DRAFT RESPONSES TO ENVIRONMENTAL SITE AUDIT NEEDS (PART 1 of 2) Enclosed contain SHINE Medical Inc.s draft responses to the staffs environmental site audit needs.

1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Thursday, August 15, 2013 5:08 PM To: Moser, Michelle; Lynch, Steven

Subject:

DRAFT SHINE Response to Transportation Request #6 Attachments:

DRAFT - Transportation Request 6 Response - Revision 2.pdfMichelle and Steve, Attached is the Draft SHINE Response to Transportation Request #6.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

1 Moser, Michelle From: Jim Costedio <Jim.Costedio@shinemed.com>

Sent: Thursday, August 08, 2013 1:11 PM To: Lynch, Steven Cc:Moser, Michelle; Jeff Bartelme; Bill Hennessy

Subject:

DRAFT SHINE Response to Proposed Action Request #5 Attachments:

SHINE Response to Proposed Action Request

1. 5.pdf; Attachment 18 - Figure 19.2.2-1, Revision 1.pdf Importance:High HiSteve,IamprovidingyouwiththeseattachmentstofacilitateyourdiscussionregardingproprietaryinformationwithALAdams.Attachedisadraftofwhatweplanonsubmitting.Note that Reference 2 in the attached response to Proposed Action Request #5 is the SHINE Medical Technologies, Inc. letter to NRC, dated March 26, 2013, Part One of the SHINE Medical Technologies, Inc. Application for Construction Permit (ML130880226).JimJim Costedio Licensing Manager SHINE Medical Technologies 608-210-1730 Proposed Action Request #5 Please provide a high-level non-proprietary schematic that visually describes the overall isotope production process. Please include target solution loading, tritium target loading, accelerator startup, chemical adjustment, off-gas removal, heat removal/dissipation, target solution removal, product separation, recycle of target solution, cleanup of target solution, removal of solid/liquid/gaseous discharges, and other relevant process steps that show input and output of resources and wastes.

SHINE Response

Upon further review, SHINE determined that the benefits of the greater transparency afforded by releasing Figure 19.2.2-1 to the public outweigh the potential harm caused to the company.

The proprietary marking has been removed from the figure. Attachment 18 provides Figure 19.2.2-1, Revision 1, a high-level non-proprietary schematic that visually describes the overall isotope production process. An I ssues Management Report (IMR) has been issued to address this change to Figure 19.2.2-1 of the ER.

SHINE requests the NRC replace Revision 0 of Figure 19.2.2-1 provided in Part One of the SHINE Medical Technologies, Inc. Application for Construction Permit (Reference 2) with Revision 1 of Figure 19.2.2-1, provided in Attachment 18.

1 page follows ENCLOSURE 1 ATTACHMENT 18 SHINE MEDICAL TECHNOLOGIES, INC. SHINE MEDICAL TECHNOLOGIES, INC. APPLICATION FOR CONSTRUCTION PERMIT RESPONSE TO ENVIRONMENTAL SITE AUDIT REQUEST FOR ADDITIONAL INFORMATION FIGURE 19.2.2 ISOTOPE PRODUCTION SYSTEM HIGH-LEVEL FLOW DIAGRAM REVISION 1 Chapter 19 - Environmental Review Radioisotope Facility Description SHINE Medical Technologies Rev. 0 Figure 19.2.2 Isotope Production System High-Level Flow Diagram Proprietary Information

- Withhold from public disclosure under 10 CFR 2.390(a)(4) 1 1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Monday, August 12, 2013 2:49 PM To: Moser, Michelle; Lynch, Steven

Subject:

SHINE Environmental Audit Response Update Attachments:

DRAFT - Transportation Request 3 Response - Revision 1.pdf; DRAFT - Proposed Action Request 3 Response - Revision 1.pdf; DRAF T - Proposed Action Request 14 Response -

Revision 1.pdf; DRAFT - Air Quality Request 10 Response - Revision 1.pdfMichelle and Steve, Attached are the Draft SHINE Response s to Transportation Request #3, Proposed Action Request #3, Proposed Action Request #14, Air Quality #10.

Bill Hennessy LicensingEngineer,SHINEMedicalTechnologies608210 1734 Part 1: Question NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Question No.: Transportation Request #3 Rev 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

SHINE suggested that traffic could be optimized using traffic signals at the entrance and exit. Please clarify whether SHINE intends to obtain a traffic light (optimization) at the entrance and exit to mitigate traffic issues. If so, please describe the current status of obtaining this traffic light (i.e., has it been negotiated, or otherwise agreed upon?). Part 2: Response Assigned to: **** Response:

SHINE will not be providing a traffic signal at the entrance and exit to the plant site. Access to the SHINE plant will comply with Federal and Wisconsin Department of Transportation requirements for entrance and exit to the US Highway. SHINE plans to use a staggered construction work shift schedule to reduce the hourly traffic flow onto Highway 51. In addition SHINE will post signs near the construction entrances and exits to make the public aware of potential high traffic areas. SHINE will consider buses, vans, and carpools combined with the staggered shifts to optimize the traffic flow to and from Highway 51. To the extent possible SHINE will plan for truck deliveries early in the day to help reduce traffic congestion.

Additional Action Taken (e.g., IMR)

Part 1 : Question NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Question No.: Proposed Action Request #3, Rev 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

Please provide an estimate of the amount of diesel fuel that the facility would use annually.

Please explain if there is any equipment, other than the standby generator, that would use diesel fuel. Part 2: Response Assigned to: **** Response:

Construction.

Preoperational.

and Decommissioning This estimate assumes a 12 month construction period and a 6 month preoperational period. Decommissioning is assumed to be 6 months. The amount of diesel fuel used per month is provided in the ER, Section 19.2 Proposed Action. Construction

-295,044 gal Preoperational-70,326 gal Decommissioning

-171,642 gal Operation There are two diesel engines at the SHINE facility, a standby diesel generator and a diesel-driven fire pump. SHINE estimates that the standby diesel generator will be run one hour per month for testing and maintenance and will use approximately 1500 gal/year.

SHINE estimates that the diesel-driven fire pump will be run weekly for testing and maintenance and use approximately 360 gal/year.

The total annual diesel fuel used is approximately 1860 gal/year.

These estimates are based on a suitable representative diesel generator and diesel-driven fire pump. The actual devices will be chosen during final design. Additional Action Taken (e.g., IMR) None Part 1 : Question NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Question No.: Proposed Action Request #14, Rev 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

Please clarify the extent to which SHINE will conduct activities in accordance with 10 CFR 50.1 O(a)(2) prior to receiving a construction permit. If known, please provide a description of the activities that SHINE will conduct, the timeline for performing these activities, and any regulatory, or other requirements that must be met prior to commencing these activities.

Part 2: Response Assigned to: Response:

SHINE has prepared a detailed permit, construction, and system startup schedule outlining key activities and milestones.

Prior to receiving the construction permit, over 15 different permit applications will be completed to support early site preparation and support receipt of the construction permit. These permit applications are identified in PSAR Chapter 19, Table 19.1 .2-1. The SHINE plan is to submit permit applications and perform these activities between the first quarter of 2014 through the first quarter of 2015. As allowed by 10 CFR 50.1 O(a)(2) SHINE may perform the following activities prior to receiving a construction permit:

• temporary fencing and other access control measures,

• access road entrance and exit,

• temporary power line and surveying for electrical substation,

• early site road grading with road gravel and construction signage,

• surveying markers and grading profiles,

• interface points for water, sewage, natural gas lines,

• temporary lighting and poles for communication,

• excavation borings to determine foundation conditions,

• installation of drainage and erosion control measures,

• erection of support buildings, and

• procurement or fabrication of components or portions of the facility at a location other than the final location.

Each of these early activities will be aligned with local and state permits to support the facility construction permit and the critical path activities.

The following list provides the construction activity and associated approximate time frame. The time frames are based on the current project schedule and are subject to change based on a number of variables.

1. Detailed site survey with markers to support grading -3/14 through 8/14 2. Temporary fencing for site perimeter-4/14 through 9/14 3. Early site grading with on-site road gravel and signage-5/14 through 10/14 4. Temporary power line and substation surveying

-5/14 through 9/14 5. Site road entrance and exit from Hwy 51 -5/14 through 10/14 6. Placement of temporary construction trailers/support

-5/14 through 9/14 7. Clearing and installation of erosion and drainage control measures-5114 through 9/14 8. Excavation borings to determine foundation conditions

-5/14 through 1 0/14

9. Temporary lighting and poles for communication-5/14 through 10/14 10. Construct interface points for water, sewage, natural gas lines -4/14 through 10/14 11. Installation of drainage and erosion control measures -5/14 through 10/14 Additional Action Taken (e.g., IMR) None NRC 2013 SITE ENVIRONMENTAL ESTIO Part 1: Question Question No.: Air Quality Request #1 0 Revision 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

Part 2: Response:

Vehicle emissions need to be quantified and documented.

Please provide estimated vehicle emissions for all operational activities such as workforce commuting and truck deliveries.

nse Vehicle air emissions for operational activities have been calculated in SHINE calculation CALC-2013-0007, including workforce commuting and truck deliveries.

The calculation results are provided in Tables 1 through 4. The fuel type for the standard passenger automobiles was assumed to be gasoline, and the fuel type for the monthly truck deliveries was assumed to be diesel fuel. The units for all of the calculated emissions are in tons/year.

PSAR Subsection 19.4.7 provided the total number of personnel automobiles that will be used during construction, operations, and decommissioning.

The units for the emission values in Tables 1 -4 are in tons/year.

T bl a e 1: f W k A E .. m1ss1ons or or er b'l d . c utomo 1 es unng onstruct1on Engine Peak Horse* Number Type of power of Hydro-Vehicle (hp) Vehicles co NOx carbons PM-10 PM-2.5 C02 Standard Passenger Automobile 150 391 50.643 3.734 5.802 0.024 0.022 1984.774 (50 Miles Daily Commute) Standard Passenger Automobile 150 29 7.512 0.554 0.861 0.004 0.003 294.417 (100 Miles Daily Commute) Total 420 58 4 7 0.03 0.03 2279 The duration of construction activities was assumed to be 24 months (PSAR Subsection 19.4.7.1 ). The actual construction schedule is 12 months. However, using 24 months is conservative because this duration over-predicts the expected amount of equipment needed for construction of the facility, thereby over-predicting the total amount of emissions as a result of the amount of equipment used.

T bl 2 E .. f W k At b"l d . 0 a e m1ss1ons or or er u omo 1 es unn g 1perat1ons Engine Horse-Type of power Monthly Hydro-Vehicle (hp) Average co NOx carbons PM-10 PM-2.5 C02 Standard Passenger Automobile 150 139 18.004 1.327 2.063 0.008 0.008 705.585 (50 Miles Daily Commute) Standard Passenger Automobile 150 11 2.849 0.210 0.326 0.001 0.001 111.675 (100 Miles Daily Commute) Total 150 21 2 2 0.01 0.01 817 f M thl T k Sh" t d . 0 r T bl 3 E .. a e m1ss1ons or on 1y rue 1pmen s unng )pera 1ons Engine Horse-Type of power Monthly Hydro-Vehicle (hp) Average co NOx PM carbons so2 C02 Semi Tracker & Trailer (20 cy) Mack 450 36 67.635 313.875 0.018 25.009 20.756 11643.750 MP8 (Shipments/

Deliveries)

Semi Tracker & Trailer (20 cy) Mack 450 1 1.879 8.719 0.000 0.695 0.577 323.438 MP8 (Rad Waste Shipment)

Total 37 70 323 0.02 26 21 11967 For operation, the monthly delivery trucks will be used as follows: approximately nine product shipments per week, one non-radioactive solid waste shipment per week, and the rest of the trucks will be used for delivery of consumables, parts, and other miscellaneous supplies needed to operate the plant. In addition to the monthly delivery trucks, there will be one radioactive waste shipment per month. PSAR Section 19.2 provided the monthly average truck deliveries and waste shipment.

T bl 4 E .. f W rk A a e m1ss1ons or 0 er utomo b'l d . D 1 es unnQ ecomm 1ss1onmg Engine Horse-Type of power Monthly Hydro-Vehicle (hp) Average co NOx carbons PM-10 PM-2.5 C02 Standard Passenger Automobile (50 Miles Daily Commute) 150 239 30.956 2.282 3.547 O.Q14 O.o14 1213.199 Standard Passenger Automobile (100 Miles Daily Commute) 150 22 5.699 0.420 0.653 0.003 0.002 223.351 Total 261 37 3 4 0.02 0.02 1437 The duration of decommissioning was assumed to be 12 months, which is half the duration of construction activities.

Fugitive dust was not calculated for the personnel automobiles because the automobiles will be parked at the site during construction, operations, and decommissioning activities.

Fugitive dust was not calculated for the monthly truck shipments that will occur during operations because the roads that will be in use will be paved. The references that were used to calculate the vehicle emissions for construction, operation, and decommissioning activities are the following:

1. Average Annual Emissions and Fuel Consumption for Gasoline-Fueled Passenger Cars and Light Trucks, United States Environmental Protection Agency, Website accessed:

http://www.epa.gov/otaq/consumer/420f08024.pdf, Date accessed:

July 23, 2013. 2. Gasoline and Industrial Engines, Chapter 3, Section 3.3, Table 3.3-1, United States Environmental Protection Agency Fifth Edition Compilation of Air Pollutant Emissions Factors, Volume 1: Stationary Point and Area Sources, Fifth Edition, USEPA, Website accessed:

http://www.epa.gov/ttn/chief/ap42/ch03/final/c03s03.pdf, Date accessed:

July 22, 2013. Additional Action Taken (e.g., IMR) 1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Monday, August 12, 2013 4:26 PM To: Moser, Michelle; Lynch, Steven

Subject:

SHINE Environmental Audit Response Update Attachments:

DRAFT - Alternatives Request 2 Resp onse - Revision 1 - Part 1.pdfMichelle and Steve, Attached is Part 1 of 2 of the Draft SHINE Response to Alternatives Request #2.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

Part 1 : Question NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Question No.: Alternatives Request #2, Rev 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

Please make available any site selection studies or summaries prepared to support the site evaluation and selection process. Part 2: Response Assigned to: Response:

SHINE's site selection process is described in PSAR Section 19.5.2.1.1.

No additional comparative site selection studies or summaries were prepared to support the site evaluation and selection process. However, a Phase I Environmental Site Assessment was performed and four groundwater monitoring wells were installed at the Stevens Point site. Reports from those activities are attached as follows: Attachment 1 : Phase I Environmental Site Assessment (Draft) for Stevens Point (February 10, 2012). SHINE currently does not have access to Revision 0 of the Phase I Environmental Site Assessment for the Stevens Point site. When Revision 0 becomes available, SHINE will provide the finalized Phase I Environmental Site Assessment for the Stevens Point site to the NRC. An Issues Management Report has been initiated to track submittal of the Revision 0 Phase I Environmental Site Assessment to the NRC. Attachment 2: Data Report of Well Installation-Stevens Point, Wisconsin (September 26, 2012). Samples were collected from the groundwater wells on the Stevens Point site during December 2011 and January-February 2012. Sampling data from this time period is not available at this time. When the data becomes available, SHINE will provide the water sampling data for the Stevens Point site to the NRC. An Issues Management Report has been initiated to track submittal of the data to the NRC. Additional Action Taken (e.g., IMR) IMR-2013-0034, IMR-2013-0035 Aworldcapabilitieslocally

REPORT PHASE I ENVIRONMENTAL SITE ASSESSMENTSHINE MEDICAL STEVENS POINT, WIT23N R8W, SECTION 1 STEVENS POINT, WI 54481Submitted To:SHINE Medical Technologies8123 Forsythia St. Suite 140 Middleton, WI 53562 Submitted By:

Golder Associates Inc.

4438 Haines Road

Duluth, MN 55811February 10, 2012Project No. 113-81093 Golder Associates 4438 Haines Road Duluth, MN 55811 Ph. 218-724-0088 Fax 218-724-0089 February 10, 2012 Dr. Gregory Piefer/CEO SHINE Medical Technologies

8123 Forsythia St. Suite 140

Middleton, WI 53562 Our Ref: 113-81093 RE: Phase I Environmental Site Assessment P113-81093 SHINE Medical - Stevens Point, WI

Lands End Way

Dear Dr. Piefer:

Golder Associates (Golder) is pleased to present to SHINE Medical Technolgies this Phase I Environmental Site Assessment Report for the Subject Property. Information presented in this Report is

subject to the general limitations presented in the Report and Golder's Proposal dated December 7, 2011.Golder appreciates this opportunity to assist you with your environmental needs. If you have any questions or comments regarding the information presented in this report, please call our office.

Sincerely, GOLDER ASSOCIATES INC.

Kathryn R Larson Kathryn R Larson Senior Project Geologist Golder Associates 2/10/2012 Table of Contents Project No. 113-81093

SUMMARY

1....................................................................................................................................................

1.0INTRODUCTION

2....................................................................................................................................1.1Purpose 2.......................................................................................................................................1.2Scope of Services 2........................................................................................................................1.3Limitations and Exceptions 3..........................................................................................................1.4Special Terms and Conditions 4.....................................................................................................1.5User Reliance 4..............................................................................................................................2.0PROPERTY DESCRIPTION 5..................................................................................................................2.1Location and Legal Description 5...................................................................................................2.2Site and Vicinity General Characteristics 5.....................................................................................2.3Current Use of the Subject Property 5............................................................................................2.4Description of Structures, Roads, and Other Improvements on the Subject Property5

.................2.5Current Use of Adjoining Properties 6............................................................................................3.0USER PROVIDED INFORMATION 7........................................................................................................3.1Environmental Cleanup Liens 7......................................................................................................3.2Activity and Use Limitations 7.........................................................................................................3.3Relationship of the Purchase Price to the Fair Market Value 7.......................................................3.4Commonly Known or Reasonably Ascertainable Information 7......................................................3.5The Degree of Obviousness or the Presence of Contamination 8.................................................3.6Reason for Conducting ESA 8........................................................................................................4.0RECORDS REVIEW 9..............................................................................................................................4.1Standard Environmental Records Sources, Federal and State 9...................................................4.1.1Subject Property Database Listing 9....................................................................................4.1.2Off-Site Properties Database Listings 10.............................................................................4.1.3Orphans Summary 10..........................................................................................................4.1.4Other Agency Records 10....................................................................................................4.2Additional Environmental Record Sources 10................................................................................4.3Physical Setting Sources 10...........................................................................................................4.3.1Sources Reviewed 10..........................................................................................................4.3.2General Topographic Setting of the Area 10........................................................................4.3.3Geologic and Hydrogeologic Setting 10...............................................................................4.3.4Surface Water and Hydrologic Setting 11............................................................................4.4Historical Use Information on the Subject Property 11...................................................................4.4.1Subject Property Historical Use Summary 11......................................................................4.4.2Standard Historical Records 11...........................................................................................4.5Historical Use Information on Adjoining Properties 13...................................................................5.0SITE RECONNAISSANCE 14...................................................................................................................5.1Methodology and Limiting Conditions 14........................................................................................5.2General Site Setting 14...................................................................................................................5.2.1Current Use of the Subject Property 14...............................................................................5.2.2Past Use of the Subject Property 14....................................................................................5.2.3General Description of Structures 14...................................................................................5.2.4Roads 14..............................................................................................................................5.2.5Potable Water Supply 14......................................................................................................5.2.6Sewage Disposal System 14...............................................................................................

2/10/2012 Table of Contents Project No. 113-810935.3Interior and Exterior Observations 15.............................................................................................5.3.1Storage Tanks 15.................................................................................................................5.3.2Odors 15..............................................................................................................................5.3.3Pools of Liquid 15.................................................................................................................5.3.4Drums 15.............................................................................................................................5.3.5Hazardous Substance and Petroleum Product Containers 15.............................................5.3.6Unidentied Substance Containers 15.................................................................................5.3.7Evidence of Polychlorinated Biphenyls 15...........................................................................5.3.8Heating/Conditioning 15.......................................................................................................5.3.9Stains or Corrosion 15.........................................................................................................5.3.10Drains and Sumps 15...........................................................................................................5.3.11Pits, Ponds, or Lagoons 16..................................................................................................5.3.12Stained Soil or Pavements 16..............................................................................................5.3.13Stressed Vegetation 16........................................................................................................5.3.14Solid Waste Disposal 16......................................................................................................5.3.15Waste Water 16....................................................................................................................5.3.16Wells 16...............................................................................................................................5.3.17Septic Systems 16...............................................................................................................5.3.18Other Interior and Exterior Observations 16........................................................................5.4Off-Site Conditions 16.....................................................................................................................5.4.1Adjoining Properties 16........................................................................................................5.4.2Other Surrounding Properties 16.........................................................................................6.0INTERVIEWS 17.......................................................................................................................................6.1Overview 17....................................................................................................................................6.2Interview with Owners, Past Owners, Past Operators and Past Occupants 17..............................6.3Interview with Site Manager 17.......................................................................................................6.4Interview with Occupants 17...........................................................................................................6.5Interview with Local Government Ofcials 18.................................................................................6.6Interviews with Others 18...............................................................................................................7.0DISCUSSION 19.......................................................................................................................................7.1Findings and Opinions 19...............................................................................................................7.1.1Recognized Environmental Conditions 19...........................................................................7.1.2Historical Recognized Environmental Conditions 19...........................................................7.1.3De Minimis Conditions 19....................................................................................................7.2Additional Investigation 19..............................................................................................................7.3Data Gaps 19..................................................................................................................................

8.0CONCLUSION

S 20...................................................................................................................................9.0QUALIFICATIONS AND SIGNATURES OF ENVIRONMENTAL PROFESSIONALS 21...........................

10.0REFERENCES

22.....................................................................................................................................

LIST OF FIGURESFIGURE 1 VICINITY MAP FIGURE 2 SITE MAP LIST OF APPENDICESAppendix A Legal Description of the Subject Property/Chain of Title Report Appendix B Federal and State Regulatory Database Search 2/10/2012 Table of Contents Project No. 113-81093Appendix C Historical DocumentationAppendix D Photographs Recorded During the Subject Property Inspection

Appendix E User Questionnaire Appendix F Resumes of Environmental Professionals 2/10/2012 1 Project No. 113-81093

SUMMARY

SHINE Medical retained Golder Associates Inc. (Golder) to perform a Phase I Environmental Site Assessment (ESA) of the property locatedat T23N, R8W, Section 1, Stevens Point, WI. The purpose of this Phase I ESA is to identify recognized environmental conditions (RECs) in connection with the

Subject Property, to the extent feasible, pursuant to the processes prescribed in the ASTM Practice E

1527-05 entitled "Standard Practice for Environmental Site Assessments: Phase I Environmental Site

Assessment Process" (ASTM Standard), and the EPA Rule entitled, "Standards and Practices for All

Appropriate Inquiries; Final Rule" (AAI Rule), 40 CFR Part 312, the Golder Proposal dated December

15th, 2011(the Proposal), and Golder's professional judgment.

This Summary is to be used only in conjunction with the attached Phase I ESAfor SHINE Medical, Stevens Point, Wisconsin dated February 2, 2012 (the Report). All definitions used in this Summary

have the same meanings as in the Report, and the use of this Summary is subject to the limitations and

conditions contained in the Report. The Report shall govern in the event of any inconsistency between

this Summary and the Report.

This assessment has revealed no evidence of RECs in connection with the Subject Property except for the following:

Golder identified the following de minimis conditions, at the Subject Property:

FINDING: Pesticides and herbicides have been used on the Subject Property for agricultural and forestry activities. There is no evidence that pesticides and herbicides are stored or have been stored on the Subject Property in the past.

OPINION: The use of pesticides and herbicides on the Subject Property generally does not present a threat to human health or the environmental and generally would not be the subject of enforcement

action if brought to the attention of appropriate governmental agencies. The use of pesticides and

herbicides is a de minimis condition.

De minimis conditions are not recognized environmental conditions. De minimis conditions generally do not present a threat to human health or the environment and generally would not be the subject of an enforcement action if brought to the attention of appropriate governmental agencies.

2/10/2012 2 Project No. 113-8109

31.0INTRODUCTION

1.1PurposeSHINE Medical(the User) retained Golder Associates Inc. (Golder) to perform a Phase I EnvironmentalSite Assessment (ESA) of the property locatedat T23N, R8W, Section 1, Stevens Point, WI. The

purpose of this Phase I ESA is to identify recognized environmental conditions (RECs) in connection

with the Subject Property, to the extent feasible, pursuant to the processes prescribed in the ASTM

Practice E 1527-05 entitled "Standard Practice for Environmental Site Assessments: Phase I

Environmental Site Assessment Process" (ASTM Standard), and the EPA Rule entitled, "Standards and

Practices for All Appropriate Inquiries; Final Rule" (AAI Rule), 40 CFR Part 312, the Golder Proposal dated December 7, 2011, and Golder's professional judgment. Golder representatives performed the Phase I ESA in conformance with these criteria.

The AAI Rule states that the ASTM Standard may be used to comply with the requirements of the AAI Rule, so whenever reference is made in this Report to the ASTM Standard, it shall include the AAI Rule.

The ASTM Standard defines RECs as "the presence or likely presence of any hazardous substances or petroleum products on a property under conditions that indicate an existing release, a past release, or a material threat of a release of any hazardous substances or petroleum products into structures on the

property or into the ground, groundwater, or surface water of the property. The term includes hazardous

substances or petroleum products even under conditions in compliance with laws."1.2Scope of Services The scope of services for this ESA consisted of the following tasks:

Records Review

• Reviewing property information to confirm the legal description and location of the Subject Property.

This information is included in Appendix A;*Reviewing environmental record sources including federal and state regulatory databases to identify facilities with past or current regulatory enforcement actions within applicable distances of the

Subject Property as defined in the ASTM Standard. The regulatory database search report is

presented in Appendix B;*Reviewing physical setting information sources to identify information about the geologic, hydrogeologic, hydrologic, and topographic conditions in the area of the Subject Property. The U.S.

Geological Survey (USGS) 7.5-minute topographic map of the area of the Subject Property is shown on Figure 1;*Reviewing historical record sources to identify past land use activities at the Subject Property and surrounding properties. Selected historical information obtained during performance of the Phase I

ESA investigation is included in Appendix C.

Site Reconnaissance

• Performing a visual inspection of the Subject Property and surrounding properties to identify potential sources of chemical and petroleum contamination such as aboveground storage tanks (ASTs),

underground storage tanks (USTs), potential sources of polychlorinated biphenyls (PCBs),

chemicals, and hazardous materials. Surficial evidence of potential RECs such as distressed

vegetation, stained soils, and/or stained paving was also evaluated. Photographs recorded during the site reconnaissance are included in Appendix D.

2/10/2012 3 Project No. 113-81093 Interviews*Interviewing available individuals with knowledge of current or historical use, storage, or disposal of potentially hazardous materials or other environmentally related activities on or adjacent to the Subject Property. User provided information is included in Appendix E.

Report Preparation

• Preparing a report that documents the findings, opinions, and conclusions of the Phase I ESA investigation conducted at the Subject Property, and provides the supporting documentation and

references for those findings, opinions, and conclusions (the Report). Resumes for the environmental professionals that performed the assessment and prepared this Phase I ESA Report are included in Appendix F. 1.3Limitations and Exceptions Golder performed our services in accordance with the following principles, which are an integral part of the ASTM Standard: (i) No environmental site assessment can wholly eliminate uncertainty regarding the potential for RECs in connection with a property. Performance of this ESA is intended to reduce, but

not eliminate, uncertainty regarding the potential for RECs in connection with the Subject Property, and

the ASTM Standard recognizes reasonable limits of time and cost; (ii) "all appropriate inquiry" does not

mean an exhaustive assessment of a property. Golder performed this ESA in conformance with the

ASTM Standard's principle of identifying a balance between the competing goals of limiting the costs

and time demands inherent in performing an ESA and the reduction of uncertainty about unknown conditions resulting from additional information; (iii) not every property warrants the same level of assessment - the type of property subject to the assessment, the expertise and risk tolerance of the

user, and the information developed in the course of the inquiry guided the appropriate level of

assessment for this ESA; and (iv) ESAs must be evaluated based on the reasonableness of judgments

made at the time and under the circumstances in which they were made. Subsequent ESAs should not

be considered valid standards to judge the appropriateness of any prior assessment based on hindsight, new information, use of developing technology or analytical techniques, or other factors.

Along with all of the limitations set forth in various sections of the ASTM E 1527-00 protocol, the accuracy and completeness of this report may be limited by the following:

Access Limitations - None

Physical Obstructions to Observations - Dormant winter vegetation, dense woodland

Outstanding Information Requests - None

Other - None The information and conclusions contained in this report are based upon work undertaken by trained

professional and technical staff in accordance with generally accepted engineering and scientific

practices current at the time the work was performed. The conclusions and recommendations

presented represent the best judgment of Golder based on the data obtained from the work. Due to the

nature of investigation and the limited data available, Golder cannot warrant against undiscovered

environmental liabilities. Conclusions and recommendations presented in this report should not be construed as legal advice.

Should additional information become available which differs significantly from our understanding of

conditions presented in this report, we request that this information be brought to our attention so that

we may reassess the conclusions provided herein.

2/10/2012 4 Project No. 113-810931.4Special Terms and Conditions No special terms and conditions are applicable to this ESA.1.5User Reliance Golder has prepared this Report at the request of the User for the purpose identified by the User in Section 3.6. Use of the information contained in this Report by anyone other than User is permissible

only with the prior written authorization to do so from Golder, and only under the conditions allowed by

the ASTM Standard. Golder is not responsible for independent conclusions, opinions, or recommendations made by others or otherwise based on the findings presented in this Report.

2/10/2012 5 Project No. 113-810932.0PROPERTY DESCRIPTION2.1Location and Legal DescriptionThe Subject Property is located at T23N, R8W, Section 1, Stevens Point, WI. The parcel is located one quarter-mile north of County Road HH and one half-mile west of Burbank Road and is accessed by a

private road that extends west from Burbank Road. The square-shaped parcel is comprised of

88.08acres of land.

The Subject Property is located in Section1, T23N, R8W on the United States Geological Survey(USGS) 7.5-minute, Polonia,WI topographic quadrangle map, as shown on Figure 1. The Assessor's Parcel Numbers for the Subject Property are 020-23-0801-01.04, 020-23-0801-02.02, 020-23-0801-02.06, 020-23-0801-03.01, 020-23-0801-03.02, 020-23-0801-04.01, 030-23-0801-13, and 030-23-0801-14. The Subject Property is located at approximately44 30' 27.45"N and 89 29' 41.70"W.

The site layout is shown on Figure 2.

According to The City of Stevens Point, the legal description for the Subject Property is a parcel of land located in the NE 1/4 of the NE 1/4 of the NE 1/4 of Section 1, T23N, R8W, Town of Hull and Town of Plover, Marathon and Portage Counties, Wisconsin bounded and described in Appendix A. A copy of the description isincluded in Appendix A.2.2Site and Vicinity General Characteristics The Subject Property is located on the easternedge of Stevens Point, WI . The adjacent properties to the north, south, and east ofthe Subject Property are rural, consisting of agricultural and forest land and, according to aerial photographs, has been agricultural and forest land since at least 1938. The adjacent

properties to the west of the Subject Property are developed as industrial and residential areas.

Development to the west of the Subject Property has occurred recently with the adjacent property being

developed after 1998. A rail line exists within one quarter-mile to the north of the Subject Property. The

rail line has been north of the Subject Property since at least 1938.

The topographic gradient is low and gently slopes toPortage River and McDill Pondlocated approximately 2 miles to the southwest. 2.3Current Use of the Subject Property The Subject Property is used for agriculture and forestry.No buildings exist on the property.

Pesticides and herbicides are applied to theagricultural areas of the Subject Propertybi-annually. No hazardous substances or petroleum products are stored, generated,or disposed of on site.

Selective tree harvesting has occurred on the wooded portions of the parcel. 2.4Description of Structures, Roads, and Other Improvements on the Subject Property Nostructures exist on the Subject Property.

A privateaccess road extends west from Burbank Road through the subject property.

A private trap shooting range located near the center of the Subject Property is used approximately twice a year.

Residences and businesses in the vicinity of the Subject Property are served by municipal water from

the city of Stevens Point Wisconsin. Wastewater in thevicinity of the Subject Property is handled by the

City of Stevens Point Wastewater Treatment system.

2/10/2012 6 Project No. 113-810932.5Current Use of Adjoining Properties The adjoining property uses are described below:

North - Agriculture and woodland.A rail line exists just north of these parcels.

East - Agriculture and woodland.

South - Agriculture and woodland.

West - Industrial Park. A Land's End Inlet occupies the adjoining parcel.

2/10/2012 7 Project No. 113-810933.0USER PROVIDED INFORMATION The ASTM Standard defines User as the party seeking to use Practice E 1527 to complete an ESA of the Subject Property. The ASTM Standard requires the User to provide certain information to theenvironmental professional. Golder has provided a User Questionnaire toSHINE Medial to facilitate the

transfer of this information to Golder.Dawn Sovinec ofSHINE Medical completed the User

Questionnaire and provided it to Golder onDecember 21st, 2011. A copy of the completed User

Questionnaire is included in Appendix E. 3.1Environmental Cleanup Liens Golder representatives asked the User about their knowledge of environmental cleanup liens against the Subject Property that are filed or recorded under federal, tribal, state or local law. The User replied:

User has no knowledge of environmental cleanup liens on the Subject Property.3.2Activity and Use Limitations Golder representatives asked the User about their knowledge of activity and use limitations (AULs), such as engineering controls, land use restrictions or institutional controls that are in place on the

Subject Property or have that been filed or recorded in a registry under federal, tribal, state or local law.

The User replied:

User has no information regarding activity or land use limitations at the Subject Property.3.3Relationship of the Purchase Price to the Fair Market Value Golder representatives asked the User if the purchase price being paid for this property reasonably reflects the fair market value of the property. The User replied:

User believes the purchase price being paid for the Subject Property reasonably reflects the fair market value of the property. 3.4Commonly Known or Reasonably Ascertainable Information Golder representatives asked the User if they were aware of commonly known or reasonably ascertainable information about the Subject Property that would assist the environmental professional in identifying conditions indicative of releases or threatened releases. Golder representatives asked the following questions:

a) Do you know the past uses of the Subject Property? The User replied:

The User knows that the Subject Property has been used as an agricultural field and that selective tree

harvesting/logging has occurred on the wooded portions of the parcel, and is being used for such purposes currently.

b) Do you know of specific chemicals that are present or once were present at the Subject Property?

The User replied:

The User has no information regarding specific chemicals that are, or once were, present at the Subject

Property.

c) Do you know of spills or other chemical releases that have taken place at the Subject Property? The User replied:

The User knows of no spills or other chemical releases that have taken place at the Subject Property.

2/10/2012 8 Project No. 113-81093 d) Do you know of any environmental cleanups that have taken place at the Subject Property? The User replied:

The User knows of no environmental cleanups that have taken place at the Subject Property. 3.5The Degree of Obviousness or the Presence of Contamination Golder representatives asked the User if, based on User's knowledge and experience related to the Subject Property, there are any obvious indicators that point to the presence or likely presence of contamination at the Subject Property. The User replied:

The User has no information regarding contamination on the Subject Property. 3.6Reason for Conducting ESA The User indicatedthe ESA is being conducted as part of a property transfer and financing, to satisfy one of the conditions required for landowner liability protection (LLP) under CERCLA.

2/10/2012 9 Project No. 113-810934.0RECORDS REVIEW4.1Standard Environmental Records Sources, Federal and State Golder retainedEnvironmental Data Resources (EDR)to perform an environmental regulatory database search of the general area of the Subject Property, which is presented in Appendix B. In accordance

with the search requirements of ASTM E-1527-05 Standard, Golder representatives reviewed the

federal and state regulatory agency records listed below to identify the use, generation, storage, treatment or disposal of hazardous substances or petroleum products, or release incidents of such

materials that might impact the Subject Property. A summary of significant listings (Subject Property and

adjacent properties with the potential to impact the Subject Property) presented in the environmental regulatory database report is presented below. The following is a listing of databases reviewed during the Phase I ESA.

Federal ASTM Standard Databases Database Approximate Minimum Search Distance Federal NPL (National Priorities List) 1.0 mile Federal delisted NPL site list 0.5 mile Federal Comprehensive Environmental Response, Compensation and Liability Information System (CERCLIS) site list 0.5 mile Federal CERCLIS-No Further Remedial Action

Planned (NFRAP) site list 0.5 mile Federal Resource Conservation and Recovery Act (RCRA) CORRACTS (Corrective Action Report) facilities list 1.0 mile Federal RCRA non-CORRACTS Treatment

0.5 mile Federal RCRA Generators list Subject Property and adjoining properties Federal Institutional Control/Engineering Control

Subject Property Federal Emergency Response Notification System (ERNS) list Subject Property State and Tribal ASTM Standard Databases Database Approximate Minimum Search Distance State and tribal hazardous waste sites identified

for investigation or remediation: NPL - equivalent sites 1.0 mile State and tribal hazardous waste sites identified for investigation or remediation: CERCLIS -

equivalent sites 0.5 mile State and tribal landfill and/or solid waste disposal

site list 0.5 mile State and tribal leaking storage tank lists 0.5 mile State and tribal registered storage tank lists Subject Property and adjoining properties State and tribal Institutional Control/Engineering

Control Registries Subject Property State and tribal voluntary cleanup sites 0.5 mile State and tribal Brownfield sites 0.5 mile4.1.1Subject Property Database Listing The Subject Property is not listed on any of the databases listed in the EDR database report.

2/10/2012 10 Project No. 113-810934.1.2Off-Site Properties Database Listings No off-site facilities were identified in the environmental database report that are considered potential environmental concerns to the Subject Property.4.1.3Orphans Summary Thirteenfacilities listed in the EDR Report were shown as "orphan sites." These are sites that are listed in environmental databases, but which EDR has been unable to locate with adequate precision to

determine whether they are pertinent to the investigation at the Subject Property. Golder was able to determine to a reasonable degree of certainty that these orphan sites were not listed on databases that indicated environmental impairment and/or were not within the specified database search distances. 4.1.4Other Agency Records No other agency records were reviewed for this Phase I ESA.4.2Additional Environmental Record Sources Golder representatives did not review additional environmental record sources as part of this Phase I ESA.4.3Physical Setting Sources4.3.1Sources Reviewed The USGS 7.5-minutePolonia, WItopographic map was reviewed in order to obtain information regarding the topographic, geologic, hydrogeologic, and hydrologic characteristics of the area of the

Subject Property. In the sections below (4.3.2 through 4.3.4), topographic conditions are noted to the

extent that they can be determined from review of topographic maps, or were visually and/or physically observed during the Site visit.4.3.2General Topographic Setting of the Area Based on the site reconnaissance, the EDR Radius Map with GeoCheck and information provided on the USGS Polonia, Wisconsin, 7.5 Minute Series Topographic Maps, the Subject Property is

characterized by low topographic relief, lying approximately 1090 feet above mean sea level.4.3.3Geologic and Hydrogeologic Setting Golder installed four groundwater monitoring wells at the Subject Property in December of 2011 (Figure 2). Based on Golder's 2012Geotechnical and Hydrological Investigation of the site the soil conditions

indicated by the boreholes is about one foot of topsoil and crop residue overlying a medium to coarse grained, siltySAND nding to depths of 9 to 14 feet. Below this is a relatively clean, medium to coarse grained, SAND with silt to the borehole termination depth of 31 feet. One borehole was advanced

without sampling to a depth of 140 feet adjacent to SM-GW3A. This borehole was intended for a well

installation into bedrock and bedrock was not encountered within 140 feet of the urface. Groundwater

was encountered in all of the wells at elevations ranging from about 1096 to 1106 (about 8 to 11 feet

below grade) as indicated in the table below. Groundwater levels should be expected to fluctuate

seasonally and annually with changes in precipitation patterns.

2/10/2012 11 Project No. 113-810934.3.4Surface Water and Hydrologic Setting Surface water runoff in the vicinity of the Subject Property is to the southwest toward thePortage River and McDill Pond. ThePortageRiver flows to the Mississippi River to the Southwest.4.4Historical Use Information on the Subject Property4.4.1Subject Property Historical Use Summary Land adjacent into the Subject Property has supported agriculture and forestry since at least 1938.

Sometime between 1998 and 2005, a business park has developed to the west of the Subject Property.4.4.2Standard Historical Records4.4.2.1Aerial Photographs Review Golder representatives obtained historical aerial photographs from Historical Information Gatherers, Inc.for the years 2010, 2005, 1998, 1992, 1986, 1978, 1968, 1960, 1953, and 1938. Selected historical aerial photographs are provided in Appendix C. The following table summarizes observations from the

review of these aerial photographs.

YearScaleDescription 19381" = 500'The Subject Property and surrounding area is a mix of woodlands and argicultural land. A railroad appears to run east west approximately 700 feet north of the Subject Property.

19531" = 500'The Subject Property and surround area appear relatively unchanged from the 1938 photograph.

19601" = 500'The Subject Property and surround area appear relatively unchanged from the 1938 and 1953 photographs.

19681" = 500'The Subject Property and surround area appear relatively unchanged from the 1938, 1953 and 1960 photographs.

19781" = 500'The Subject Property and surround area appear relatively unchanged from the 1938, 1953, 1960 and 1968

photographs.

19861" = 800'The Subject Property and surround area appear relatively unchanged from the 1938, 1953, 1960, 1968 and 1978

photographs.

19921" = 500'The Subject Property and surround area appear relatively unchanged from the 1938, 1953, 1960, 1968, 1978 and 1986

photographs.

19981" = 500'The Subject Property and surround area appear relatively unchanged from the 1938, 1953, 1960, 1968, 1978, 1986

and 1992 photographs.

20051' = 500'The Subjecr Property and surrounding area appear unchanged from the previous photographs except that the edge of a business park is visible just west of the Subject Property.

20101" = 500'The Subject Property and surrounding area appears relatively unchanged from the 2005 photograph. 4.4.2.2Sanborn Fire Insurance Map Review Golder representatives requested historical Sanborn© Fire Insurance Maps from Environmental Data Resources, Inc. Golder was informed that Sanborn© maps were not developed for the area surrounding

the Subject Property. A copy of the "No Coverage" document is included in Appendix C.

2/10/2012 12 Project No. 113-810934.4.2.3Property Tax Files Golder representatives obtained Subject Property Tax records for the County Parcel ID Nos:

Parcel ID Number 020-23-0801-02.06- Owner = Thomas Mocadlo and Margaret Jakusz

020-23-0801-03.01- Owner = Thomas Mocadlo and Margaret Jakusz

020-23-0801-02.02- Owner = Thomas J. and Sandra M. Mocadlo

020-23-0801-01.04- Owner = Bernard Mocadlo

020-23-0801-04.01- Owner = Bernard Mocadlo 020-23-0801-03.02- Owner = Blue Top Farms, Inc.

030-23-0801 Owner = Blue Top Farms, Inc.

030-23-0801 Owner = MS & S Enterprises Limited Partnership

Copies andparcel maps are provided in Appendix A.

The property tax records did not indicate records of past ownership, appraisals, maps, sketches, photos, or other information pertaining to the property. 4.4.2.4Recorded Land Title Records Title documents were not obtained for this Phase I ESA. 4.4.2.5Historical Topographic Map Review Golder representatives obtained historical USGS topographic quadrangle maps fromEnvironmentalData Resources, Inc.for the years 1955, 1957, 1969, 1970, 1976, 1978, 1980, 1986, and 1991. Copies

of the historical topographic maps are provided in Appendix C. The following paragraphs summarize our

observations from the review of these historical topographic maps.

YearScaleDescription 19551:48000A portion of the Subject Property is visible in the southwest corner of the topographic map. An elecric tranmission line

runs near the southern boundary of the Subject Property.

The Minneapolis, St. Paul and Sault Ste Marie Rail Line is

visible north of the Subject Property.

19691:24000The Subject Property is entirely visible on this map. The map appears similar ot the 1955 map.

19861:24000The Subject Property is entirely visible on this map. The map appears similar ot the 1955 map. 4.4.2.6Local Street Directories Local StreetDirectories fromEDRwere requested.The Subject Property address was not included in the city directory listing.4.4.2.7Building Department Records No building records pertaining to the Subject Property were available.4.4.2.8Zoning and Land Use Records Golder usedthe Portage County Geographic InformationSystems (GIS) Mapto review a property profile for the Subject Property. Information indicated that the Subject Property is zonedA1 for agriculturaluse.

2/10/2012 13 Project No. 113-810934.4.2.9Other Historical Records No additional historical records were reviewed during this assessment. 4.5Historical Use Information on Adjoining Properties The following is a summary of historical use information for adjacent properties based on information obtained from the Subject Property visit, a review of historical topographic maps and previous ESA

reports for the Subject Property:

The adjacent properties were all agricultural and woodland since at least 1938. The rail line present north of the Subject Property was operational since at least 1938 and has been operated by at least two

railroads. An electrical transmission linehas runnear the southernboundary of the Subject Property

since at least1938.A business park was built west of the Subject Property some time between 1998

and 2005.

2/10/2012 14 Project No. 113-810935.0SITE RECONNAISSANCE Golder representative Alexandra A.Praschperformed a visual assessment of the Subject PropertyonDecember 15th, 2011to identify potential sources of chemical and petroleum contamination. The Golder representative assessed surficial evidence of potential impacts such as waste or refuse dumping, distressed vegetation, stained soils, and/or stained paving. Photographs recorded during the site

assessment are presented in Appendix D.5.1Methodology and Limiting Conditions The site reconnaissance was conducted during the period of December 15th - December 17th, 2011 by Alexandra Prasch, Environmental Technician with Golder Associates. Weather conditions at the time of

the site reconnaissance were sunny, partly cloudy, and windy. The visual reconnaissance consisted of

observing the boundaries of the property and systematically traversing the site to provide an overlapping

field of view, wherever possible.Portions of theproperty and boundaries were inaccessible due to

heavily wooded land and brush. Photographs of pertinent site features identified during the site

reconnaissance are included in Appendix D. 5.2General Site Setting The Subject Property consists of approximately 88.08 acres of farmland and forestwith no buildings, utilities, or other developments. The ground surface at the site is level and slopes gently to the

southwest. The Subject Property is accessed from a private road extending west from Burbank Road.5.2.1Current Use of the Subject Property Information about the current use of the Subject Property is detailed in section 2.3 of this report. 5.2.2Past Use of the Subject Property The Subject Property has been used for agricultural and forestry purposes since 1938 or before. The use of the Subject Property prior to 1938 is unknown.5.2.3General Description of Structures No structureswere observed on the Subject Property.5.2.4Roads There are no public roads through or leading to the Subject Property. A private access road extends to and through the Subject Property from Burbank Road.5.2.5Potable Water Supply Currently the Subject Property has no potable water supply.5.2.6Sewage Disposal System There is no sewage disposal system within the Subject Property.

2/10/2012 15 Project No. 113-810935.3Interior and Exterior Observations Golder identified current or past uses likely to involve the use, treatment, storage, disposal or generation of hazardous substances or petroleum products, to the extent they were visually and/or physically observed during the Subject Property visit or identified from the interviews or the records review. The

substances and approximate quantities, types of containers (if any) and storage conditions are

discussed in the following subsections.5.3.1Storage Tanks Golder observed no evidence of underground or aboveground storage tanks at the Subject Property at the time of the site visit.5.3.2Odors Golder observed no unusual odors at the Subject Property at the time of the site visit. 5.3.3Pools of Liquid Golder observed nopools of liquidat the Subject Property at the time of the site visit.5.3.4Drums Golder observed no drums at the Subject Property at the time of the site visit. 5.3.5Hazardous Substance and Petroleum Product Containers Golder observed no hazardous substance or petroleum product containersat the Subject Property at the time of the site visit. 5.3.6Unidentified Substance Containers Golder observed no unidentified substance containers at the Subject Property at the time of the site visit. 5.3.7Evidence of Polychlorinated Biphenyls Golder observed no evidence of polychlorinated biphenyls.5.3.8Heating/Conditioning The Subject Property is undeveloped. No heating or air conditioning systems were present. 5.3.9Stains or Corrosion Golder observed noevidence of stains or corrosionat the Subject Property at the time of the site visit.5.3.10Drains and Sumps Golder observed no drains or sumps on the Subject Property at the time of the site visit.

2/10/2012 16 Project No. 113-810935.3.11Pits, Ponds, or Lagoons Golder observed no pits, ponds, or lagoons on the Subject Property at the time of the site visit.5.3.12Stained Soil or Pavements Golder observed nostained soil or pavementsat the Subject Property at the time of the site visit.5.3.13Stressed Vegetation Golder observed nostressed vegetationat the Subject Property at the time of the site visit.5.3.14Solid Waste Disposal No readily apparent evidence of solid waste dumping, suspect fill material, or landfills was identified on the Subject Property during the site reconnaissance.5.3.15Waste Water Golder observed no evidence that industrial waste water is generated or dischargedfrom the Subject Property at the time of the site visit. 5.3.16Wells Golder observed noevidence of wellsat the Subject Property at the time of the site visit.5.3.17Septic Systems Golder observed noevidence of septic systemsat the Subject Property at the time of the site visit.5.3.18Other Interior and Exterior Observations Golder made no other interior or exterior observations of the Subject Property during the site visit.5.4Off-Site Conditions The following two sections discuss the off-site observations, to the extent that the current uses of the adjoining properties were observable during the Subject Property reconnaissance, and were likely to

indicate an REC in connection with the adjoining properties or the Subject Property.5.4.1Adjoining Properties Golder did not observe any evidence of RECs on adjoining properties from the Subject Property during the site visit.5.4.2Other Surrounding Properties The adjacent properties were observed to be a business park, forested land and agricultural land during the site visit.There were noindications of RECs noted on other surrounding properties during the site visit.

2/10/2012 17 Project No. 113-810936.0INTERVIEWS6.1Overview During the completion of this Phase I ESA, available individuals were interviewed with knowledge of current or historical use, storage, or disposal of potentially hazardous materials or other environmentally

related activities on or adjacent to the Subject Property. Information provided is summarized throughout

the text of the report and in the following sections.6.2Interview with Owners, Past Owners, Past Operators and Past Occupants Golder interviewed the owners identified in section 4.4.2.3 of the report. Interviews were conducted via telephone call. Phase I ESA Interview forms summarizing the interviews are available for review in the

Golder file.

Thomas Mocadlo, owner of parcels 020-23-081-02.02, 020-23-081-02.06 and 020-23-801-03.01, indicated that he purchased the property around 1985 for the purpose of hunting and gathering firewood. His brother Bernardowns other parcels that are part of the Subject Property. He was not aware of any solid or liquid wastes that have been handled or disposed of on the Subject Property. He

indicated that small amounts of pesticides or herbicides have been used in the past on the Subject

Property, but they have not been stored on the Subject Property.

Bernard Mocadlo, owner of parcels 020-23-0801-04.01 and 020-23-1.04, indicated that he has owned

the property for 54 years and farmed the property for 30 years. The land has been used for potato, sweet corn, pea and vegetable crops. He was not aware of any solid or liquid wastes that have been handled or disposed of on the Subject Property. He indicated that small amounts of pesticides or

herbicides have been used in the past on the Subject Property, but they have not been stored on the

Subject Property.

Curt Soik, owner of parcel 030-230-0801-1.13, indicated that he purchased his parcel in 1962 from a

farmer.His parcel has been used for growing of corn and other vegetable crops. He was not aware of

any solid or liquid wastes that have been handled or disposed of on the Subject Property. He indicated that small amounts of pesticides have been used in the past on the Subject Property, but they have not been stored on the Subject Property.

Peter Zakrzewski, President of Blue Top Farms and owner of parcels 030-230-801.14 and

020-230-801-03.02,indicated that he is the son of the original owner (J. James Zakrzewski). His father

purchased the property 30 years ago. Peter has been the Vice President of Blue Top Farms for the last

10 years. The property has been used for corn, green bean, soy bean and potato crops. He rented a portion ofthe parcels he owns to apotato farmer in the past. He believed liquid manure was handled in the southwest corner of the parcels he owns in the past, but has not been used in the last two years. He

indicated thatpesticides and herbicides have been used in the past on the Subject Property, but they

have not been stored on the Subject Property. He does maintain a private shooting range on the

parcels that he owns. He uses the shooting range no more than a few times a year.6.3Interview with Site Manager Golder did not interview a Site Manager for the Phase I ESA.6.4Interview with Occupants Golder did not interview Occupants for the Phase I ESA.

2/10/2012 18 Project No. 113-810936.5Interview with Local Government Officials Golder did not interview Local Government Officials for the Phase I ESA.6.6Interviews with Others Golder did not interview Others for the Phase I ESA.

2/10/2012 19 Project No. 113-810937.0DISCUSSION This section identifies the known or suspect RECs, historical RECs, and de minimis conditions identified during the assessment.7.1Findings and Opinions7.1.1Recognized Environmental Conditions No Recognized Environmental Conditions were identified during this assessment.7.1.2Historical Recognized Environmental Conditions An HREC is an environmental condition which, in the past, would have been considered a REC, but which may or may not be considered a REC currently. Golder's rationale for considering these

environmental conditions as HRECs is based solely on the information stated herein. Designation as an

HREC however, does not preclude the potential for the condition to affect the Subject Property.

No Historical Recognized Environmental Conditions were identified during this assessment. 7.1.3De Minimis Conditions De minimis conditions are not recognized environmental conditions. De minimis conditions generally do not present a threat to human health or the environment and generally would not be the subject of an enforcement action if brought to the attention of appropriate governmental agencies.

FINDING: Pesticides and herbicides have been used on the Subject Property for agricultural and

forestry activities. There is no evidence that pesticides and herbicides are stored or have been stored

on the Subject Property in the past.

OPINION: The use of pesticides and herbicides on the Subject Property generally does not present a threat to human health or the environmental and generally would not be the subject of enforcement action if brought to the attention of appropriate governmental agencies. The use of pesticides and

herbicides is a de minimis condition. 7.2Additional Investigation No additional investigation is indicated based on the information gathered during this assessment.7.3Data Gaps A Data Failure occurs when all of the standard historical sources that are reasonably ascertainable and likely to be useful have been reviewed and yet the objectives have not been met. Some Data Failures

may comprise Data Gaps. A Data Gap is defined as the lack of or inability to obtain information required by the ASTM Standard despite good faith efforts by the EP to gather such information. A significant data gap occurs when a data gap impacts the ability of the EP to identify RECs.

Golder representatives did not identify significant data gaps during this assessment.

2/10/2012 20 Project No. 113-8109

38.0CONCLUSION

SGolder performed a Phase I ESA of the property located at T23N, R8W, Section 1, Stevens Point, WI in conformance with the scope and limitations of the ASTM Standard. Any exceptions to, or deletions from, the ASTM Standard are described in the appropriate sections of this Report. This assessment has

revealed no evidence of RECs in connection with the Subject Property except:

Golder identified the following de minimis conditions, at the Subject Property:

FINDING: Pesticides and herbicides have been used on the Subject Property for agricultural and forestry activities. There is no evidence that pesticides and herbicides are stored or have been stored on the Subject Property in the past.

OPINION: The use of pesticides and herbicides on the Subject Property generally does not present a threat to human health or the environmental and generally would not be the subject of enforcement

action if brought to the attention of appropriate governmental agencies. The use of pesticides and

herbicides is a de minimis condition.

De minimis conditions are not recognized environmental conditions. De minimis conditions generally do

not present a threat to human health or the environment and generally would not be the subject of an

enforcement action if brought to the attention of appropriate governmental agencies.

2/10/2012 21 Project No. 113-810939.0QUALIFICATIONS AND SIGNATURES OF ENVIRONMENTAL PROFESSIONALS Alexandra Prasch, Geologist in Training, Level 1Environmental Technician with2 years of professional experience, conducted the site visit. Kathryn Larson, Senior ProjectGeologist with 15 years of experience,prepared this Report, and Amy Thorson, Senior Engineer with 20 years of professional

experience, served as thesenior reviewer of the Report. Resumes for members of the project team are

included in Appendix F.

"We declare that, to the best of our professional knowledge and belief, we meet the definition of Environmental Professional as defined in Section 312.10 of 40 CFR Part 312.

We have the specific qualifications based on education, training, and experience to assess a property of

the nature, history, and setting of the Subject Property. We have developed and performed the all

appropriate inquiries in conformance with the standards and practices set forth in 40 CFR Part 312."

GOLDER ASSOCIATES INC.

2/10/2012 22 Project No. 113-81093

10.0REFERENCES

The Report's author annotated the reference sources relied upon in preparing the Phase I ESA in the relevant sections of this Report.

List of Figures SCALE 0 1 1 MILES CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.J:\2011 Jobs\113-81093 SHINE Steven's Point WI\CAD\VICINITY_MAP_WI.dwg l 1/11/2012 10:58 AM l AGarrigus l STEVENS POINT 1--------APG1/11/12MTK1/11/12AT1/11/12 0----FIG.113-81051 VICINITY_MAP_WI.dwg SMT / STEVENS POINT / AK VICINITY MAP SHINE MEDICAL TECHNOLOGIES STEVENS POINT, WISCONSIN REFERENCE TOPOGRAPHIC MAP PROVIDED BY WISCONSIN DNR.

PROJECT LOCATION PROJECT LOCATION 100'162'66'100'60'66'66'66'2308-01-2101-01 2308-01-2201-01 4.26 AC.13 AC.80 AC.2.4 AC.18.61 AC.

1,868' 1,868'TRANSMISSION LINE 1,000'R 1,000'R 80' FUTURE STREET 100' FUTURE STREET TRANSIT FACILITY 21 AC.3 AC.21 AC.2.2 AC.5 AC.2.4 AC.5.1 AC.17.52 AC.19.93 AC.3.7 AC.25.23 AC.10.33 AC.23.34 AC.1.5 AC.34.23 AC.35.69 AC.700'700'700'0.4 AC.10.43 AC.5.1 AC.1.5 AC.316'-3" 316'-3" SM-GW1A SM-GW2A SM-GW3A SM-GW4A 1.) LOCATION OF POTENTIAL LOCATION FOR SHINE MEDICAL FACILITY PROVIDED BY CITY OF STEVENS POINT ON 12/20/11.

2.) AERIAL IMAGERY PROVIDED BY PROVIDED BY CITY OF STEVENS POINT ON 12/20/11.

REFERENCES\\anc1-s-fs2-vm\Jobs_In_Progress\2011 Jobs\113-81093 SHINE Steven's Point WI\CAD\Proposed_building_layout_SP.dwg l 1/11/2012 11:01 AM l AGarrigus l STEVENS POINT SCALE 0 FEET 100O 100O 2--------APG1/11/12MTK1/11/12AT1/11/121----FIG.113-81051 Proposed_building_layout_SP.dwg SMT / STEVENS POINT / AK SITE MAP SHINE MEDICAL TECHNOLOGIES STEVENS POINT, WISCONSIN CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.PROPOSED BUILDING OUTLINE PROPOSED BUILDING AREA INTERSTATE HIGHWAY 39 PROPOSED PROPERTY BOUNDARY 1.) NORTHINGS AND EASTINGS PROVIDED IN NAD_1983_HARN_WISCRS_PORTAGE_COUNTY_FEET NOTES Appendix ALegal Description of the Subject Property/

Chain of Title Report RFI RESPONSE FORM PM-001, Revision 2 RFI NO.: GOLDER-2011-RFI Revision:

0 0051 Due Date: 12/16/2011 Sheet 1 of 3 RFI RESPONSE:

The following table is the leaal parcels description for the Stevens Point property:

• Parcel Township Owner(s) Approximate Identification Acreage Number 020-23-0801-02.06 Town of Hull Thomas Mocad1o and 7.2 Margaret Jakusz 020-23-0801-03.01 TownofHull Thomas Mocadlo and 19.92 Margaret Jakusz . 020-23-0801-02.02 Town ofHu]J Thomas J. and Sandra 6.6 M. Mocadlo 020-23-0801-01

.04 Town of Hull Bernard J. Mocad1o 25.23 020-23-0801-04.01 020-23-0801-03.02 Town of Hull Blue Top Farms, Inc. 19.93 030-23-0801-1 4 Town of Plover Blue Top Farms, Inc. 5.5 030-23-0801-13 Town of Plover MS & S Enterprises

3.7 Limited

Total Combined 88.08 Parcel Acreqe Please also find Phase 1 ESA User Questionnaire responses on pages 2 and 3 of the RFI response.

Responder:

Dawn Sovinec Company: SHINE Medical Independent Reviewer (for Design Input)-----'------------

Responder's Management:

SHINE Licensing:

X Gregory R Piefer Greg Plefer CEO Signed by: greg.p@shlnemed.com 12/28/2011 Originator Acceptance: Date: 12.21.11 Phone No.: 608-831-0814 Date:

Date:

My Map020230801-01.04This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:26:25 PM.

My Map020230801-02.02This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:40:03 PM.

My Map020230801-02.06This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:42:58 PM.

My Map020230801-03.01This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:15:59 PM.

My Map020-23-0801-03.02This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:30:47 PM.

My Map020230801-04.01This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:28:50 PM.

My Map030-23-0801-13This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:34:11 PM.

My Map030-23-0801-14This map does not constitute a legal survey. Contact Planning and Zoning Office (715) 346-1334 Tue Jan 3 2012 02:32:31 PM.

Appendix BFederal and State Regulatory Database Searc h FORM-BPK-SPMkcehCoeG htiw tropeR ŽpaM suidaR RDE ehT 440 Wheelers Farms Road Milford, CT 06461

Toll Free: 800.352.0050

www.edrnet.com SHINE Medical Stevens Point, WI Lands End Way, Stevens Point, WI 54482 Inquiry Number: 3220399.2s December 07, 2011 SECTION PAGE Executive Summary ES1 Overview Map 2 Detail Map 3 Map Findings Summary 4 Map Findings 7 Orphan Summary 8 Government Records Searched/Data Currency Tracking GR-1 GEOCHECK ADDENDUM Physical Setting Source Addendum A-1 Physical Setting Source Summary A-2 Physical Setting SSURGO Soil Map A-5 Physical Setting Source Map A-9 Physical Setting Source Map Findings A-11 Physical Setting Source Records Searched A-30 TC3220399.2s Page 1 Thank you for your business.

Please contact EDR at 1-800-352-0050 with any questions or comments.

Disclaimer - Copyright and Trademark Notice This Report contains certain information obtained from a variety of public and other sources reasonably available to Environmen tal Data Resources, Inc. It cannot be concluded from this Report that coverage information for the target and surrounding properties doe s not exist from other sources.

NO WARRANTY EXPRESSED OR IMPLIED, IS MADE WHATSOEVER IN CONNECTION WITH THIS REPORT. ENVIRONMENTAL DATA RESOURCES, INC. SPECIFICALLY DISCLAIMS THE MAKING OF ANY SUCH WARRANTIES, INCLUDING WITHOUT LIMITATION, MERCHANTABILITY OR FITNESS FOR A PARTICULAR USE OR PURPOSE. ALL RISK IS ASSUMED BY THE USER. IN NO EVENT SHALL

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Purchaser accepts this Report "AS IS". Any analyses, estimates, ratings, environmental risk levels or risk codes provided in this Report are provided for illustrative purposes only, and are not intend ed to provide, nor should they be interpreted as providing any facts regarding, or prediction or forecast of, any environmental risk for any prope rty. Only a Phase I

Environmental Site Assessment performed by an environmental professional can provide information regarding the environmental ri sk for any

property. Additionally, the information provided in this Report is not to be construed as legal advice.

Copyright 2011 by Environmental Data Resources, Inc. All rights reserved. Reproduction in any media or format, in whole or in part, of any report or map of Environmental Data Resources, Inc., or its affiliates, is prohibited without prior written permission.

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TABLE OF CONTENTS EXECUTIVE

SUMMARY

TC3220399.2s EXECUTIVE

SUMMARY

1 A search of available environmental records was conducted by Environmental Data Resources, Inc (EDR).

The report was designed to assist parties seeking to meet the search requirements of EPA's Standards

and Practices for All Appropriate Inquiries (40 CFR Part 312), the ASTM Standard Practice for

Environmental Site Assessments (E 1527-05) or custom requirements developed for the evaluation of

environmental risk associated with a parcel of real estate.

TARGET PROPERTY INFORMATION ADDRESS LANDS END WAY, STEVENS POINT, WI 54482 COORDINATES 44.507000 - 44 30' 25.2

Latitude (North):

89.495900 - 89 29' 45.2

Longitude (West):

Zone 16 Universal Tranverse Mercator:

301598.3 UTM X (Meters):

4931000.0 UTM Y (Meters):

1113 ft. above sea level Elevation:

USGS TOPOGRAPHIC MAP ASSOCIATED WITH TARGET PROPERTY 44089-E4 POLONIA, WI Target Property Map:

1986 Most Recent Revision:

44089-D4 ARNOTT, WI South Map:

1969 Most Recent Revision:

44089-D5 WHITING, WI Southwest Map:

1976 Most Recent Revision:

44089-E5 STEVENS POINT, WI West Map: 1991 Most Recent Revision:

AERIAL PHOTOGRAPHY IN THIS REPORT 2010 Photo Year:

USDA Source: TARGET PROPERTY SEARCH RESULTS The target property was not listed in any of the databases searched by EDR.

EXECUTIVE

SUMMARY

TC3220399.2s EXECUTIVE

SUMMARY

2 DATABASES WITH NO MAPPED SITES No mapped sites were found in EDR's search of available ("reasonably ascertainable ") government records either on the target property or within the search radius around the target property for the

following databases:

STANDARD ENVIRONMENTAL RECORDS Federal NPL site listNPLNational Priority List Proposed NPL Proposed National Priority List Sites NPL LIENS Federal Superfund Liens Federal Delisted NPL site list Delisted NPLNational Priority List Deletions Federal CERCLIS list CERCLISComprehensive Environmental Response, Compensation, and Liability Information SystemFEDERAL FACILITYFederal Facility Site Information listing Federal CERCLIS NFRAP site List CERC-NFRAPCERCLIS No Further Remedial Action Planned Federal RCRA CORRACTS facilities list CORRACTSCorrective Action Report Federal RCRA non-CORRACTS TSD facilities list RCRA-TSDFRCRA - Treatment, Storage and Disposal Federal RCRA generators list RCRA-LQGRCRA - Large Quantity Generators RCRA-SQG RCRA - Small Quantity Generators RCRA-CESQG RCRA - Conditionally Exempt Small Quantity Generator Federal institutional controls / engineering controls registries US ENG CONTROLSEngineering Controls Sites ListUS INST CONTROLSites with Institutional Controls Federal ERNS list ERNSEmergency Response Notification System State- and tribal - equivalent CERCLIS SHWSHazard Ranking List EXECUTIVE

SUMMARY

TC3220399.2s EXECUTIVE

SUMMARY

3 State and tribal landfill and/or solid waste disposal site listsSWF/LFList of Licensed Landfills WDS Registry of Waste Disposal Sites SHWIMS Solid & Hazardous Waste Information Management System State and tribal leaking storage tank lists LUSTLeaking Underground Storage Tank Database LAST Leaking Aboveground Storage Tank Listing INDIAN LUST Leaking Underground Storage Tanks on Indian Land State and tribal registered storage tank lists USTRegistered Underground Storage Tanks AST Tanks Database INDIAN UST Underground Storage Tanks on Indian Land FEMA UST Underground Storage Tank Listing State and tribal institutional control / engineering control registries CRSClosed Remediation Sites AUL Deed Restriction at Closeout Sites State and tribal voluntary cleanup sites VCPVoluntary Party Liability Exemption Sites INDIAN VCP Voluntary Cleanup Priority Listing State and tribal Brownfields sites BEAPBrownfields Environmental Assessment Program BROWNFIELDS Brownfields Site Locations Listing ADDITIONAL ENVIRONMENTAL RECORDS Local Brownfield lists US BROWNFIELDSA Listing of Brownfields Sites Local Lists of Landfill / Solid Waste Disposal Sites DEBRIS REGION 9Torres Martinez Reservation Illegal Dump Site Locations ODI Open Dump Inventory SWRCY Recycling Center Listing INDIAN ODI Report on the Status of Open Dumps on Indian Lands Local Lists of Hazardous waste / Contaminated Sites US CDLClandestine Drug Labs WI ERP Environmental Repair Program Database CDL Clandestine Drug Lab Listing US HIST CDL National Clandestine Laboratory Register EXECUTIVE

SUMMARY

TC3220399.2s EXECUTIVE

SUMMARY

4 Local Land RecordsLIENS 2CERCLA Lien Information LUCIS Land Use Control Information System Records of Emergency Release Reports HMIRSHazardous Materials Information Reporting System SPILLS Spills Database AGSPILLS Agricultural Spill Cases Other Ascertainable Records RCRA-NonGenRCRA - Non Generators DOT OPS Incident and Accident Data DOD Department of Defense Sites FUDS Formerly Used Defense Sites CONSENT Superfund (CERCLA) Consent Decrees ROD Records Of Decision UMTRA Uranium Mill Tailings Sites MINES Mines Master Index File TRIS Toxic Chemical Release Inventory System TSCA Toxic Substances Control Act FTTS FIFRA/ TSCA Tracking System - FIFRA (Federal Insecticide, Fungicide, & Rodenticide Act)/TSCA (Toxic Substances Control Act)

HIST FTTS FIFRA/TSCA Tracking System Administrative Case Listing SSTS Section 7 Tracking Systems ICIS Integrated Compliance Information System PADS PCB Activity Database System MLTS Material Licensing Tracking System RADINFO Radiation Information Database FINDS Facility Index System/Facility Registry System RAATS RCRA Administrative Action Tracking System BRRTS Bureau of Remediation & Redevelopment Tracking System NPDES NPDES Permit Listing MANIFEST Hazardous Waste Manifest Data DRYCLEANERS Five Star Recognition Program Sites WI WRRSER Wisconsin Remedial Response Site Evaluation Report AIRS Air Permit Program Listing TIER 2 Tier 2 Facility Listing LEAD Lead Inspection Data INDIAN RESERV Indian ReservationsSCRD DRYCLEANERSState Coalition for Remediation of Drycleaners Listing COAL ASH EPA Coal Combustion Residues Surface Impoundments ListFINANCIAL ASSURANCEFinancial Assurance Information Listing COAL ASH Coal Ash Disposal Site ListingPCB TRANSFORMERPCB Transformer Registration Database COAL ASH DOE Sleam-Electric Plan Operation Data EDR PROPRIETARY RECORDS EDR Proprietary Records Manufactured Gas PlantsEDR Proprietary Manufactured Gas Plants EXECUTIVE

SUMMARY

TC3220399.2s EXECUTIVE

SUMMARY

5 SURROUNDING SITES: SEARCH RESULTS Surrounding sites were not identified.

Unmappable (orphan) sites are not considered in the foregoing analysis.

EXECUTIVE

SUMMARY

TC3220399.2s EXECUTIVE

SUMMARY

6 Due to poor or inadequate address information, the following sites were not mapped. Count: 13 records.

Site Name Database(s)____________ ____________STEVENS POINT MUNICIPAL AIRPORT NPDESSTEVENS POINT MUNI FINDS FROM STEVENS POINT CTY LIMITS TO C SPILLS JUNCTION CITY TO STEVENS POINT SPILLS WI RIVER & WISCONSIN ST SPILLS UW STEVENS POINT BALDWIN HALL SPILLS WISCONSIN RIVER BELOW POINT PAPER SPILLS STEVENS POINT AIRPORT #2 WI WRRSER KWIK TRIP - STEVENS POINT WI WRRSER STEVENS POINT BRRTS WI RIVER BOAT LANDING BRRTS STEVENS POINT BRRTS STEVENS POINT WATER DEPARTMENT - W TIER 2 EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.

1120 EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.

N Target Property .... Sites at elevations higher than or equal to the target property

• Slt8s at elevations lower than the target property .&. Manufactured Gas Plants li Sensitive ReceptDrs EJ National Priority Ust SiiH ITJJ Dept. Defense Silas SITE NAME: SHINE Medical Stevens Point, WI ADDRESS: Lands End Way, Stevens Point WI 54482 LA T/LONG: 44.5070 /89.4959 DETAIL MAP -3220399.2s 0 Indian Reservations BIA N Oil & Gas pipelines from USGS 100-year flood zone 600-yaar flood zone This report includes Interactive Map Layers to display and/or hide map information.

The legend includes only those icons for the default map view. CLIENT: Golder Associates CONTACT: Kattvyn Larson INQUIRY#:

3220399.2s DATE: Decermer07,2011 11:47am !lDpyrlgllt02D11 EDR, lnc.C2D1DUIIJIIIMIIII.

07120011.

MAP FINDINGS

SUMMARY

SearchTargetDistanceTotalDatabaseProperty(Miles)< 1/81/8 - 1/41/4 - 1/21/2 - 1> 1Plotted STANDARD ENVIRONMENTAL RECORDS Federal NPL site list 0 NR 0 0 0 0 1.000 NPL 0 NR 0 0 0 0 1.000 Proposed NPL 0 NR NR NR NR NR TP NPL LIENS Federal Delisted NPL site list 0 NR 0 0 0 0 1.000 Delisted NPL

Federal CERCLIS list 0 NR NR 0 0 0 0.500 CERCLIS 0 NR 0 0 0 0 1.000 FEDERAL FACILITY

Federal CERCLIS NFRAP site List 0 NR NR 0 0 0 0.500 CERC-NFRAP

Federal RCRA CORRACTS facilities list 0 NR 0 0 0 0 1.000 CORRACTS Federal RCRA non-CORRACTS TSD facilities list 0 NR NR 0 0 0 0.500 RCRA-TSDF Federal RCRA generators list 0 NR NR NR 0 0 0.250 RCRA-LQG 0 NR NR NR 0 0 0.250 RCRA-SQG 0 NR NR NR 0 0 0.250 RCRA-CESQG

Federal institutional controls /

engineering controls registries 0 NR NR 0 0 0 0.500 US ENG CONTROLS 0 NR NR 0 0 0 0.500 US INST CONTROL Federal ERNS list 0 NR NR NR NR NR TP ERNS State- and tribal - equivalent CERCLIS 0 NR 0 0 0 0 1.000 SHWS State and tribal landfill and/or solid waste disposal site lists 0 NR NR 0 0 0 0.500 SWF/LF 0 NR NR 0 0 0 0.500 WDS 0 NR NR NR NR NR TP SHWIMS State and tribal leaking storage tank lists 0 NR NR 0 0 0 0.500 LUST 0 NR NR 0 0 0 0.500 LAST 0 NR NR 0 0 0 0.500 INDIAN LUST TC3220399.2s Page 4 MAP FINDINGS

SUMMARY

SearchTargetDistanceTotalDatabaseProperty(Miles)< 1/81/8 - 1/41/4 - 1/21/2 - 1> 1Plotted State and tribal registered storage tank lists 0 NR NR NR 0 0 0.250 UST 0 NR NR NR 0 0 0.250 AST 0 NR NR NR 0 0 0.250 INDIAN UST 0 NR NR NR 0 0 0.250 FEMA UST State and tribal institutional control / engineering control registries 0 NR NR NR NR NR TP CRS 0 NR NR 0 0 0 0.500 AUL State and tribal voluntary cleanup sites 0 NR NR 0 0 0 0.500 VCP 0 NR NR 0 0 0 0.500 INDIAN VCP

State and tribal Brownfields sites 0 NR NR 0 0 0 0.500 BEAP 0 NR NR 0 0 0 0.500 BROWNFIELDS ADDITIONAL ENVIRONMENTAL RECORDS Local Brownfield lists 0 NR NR 0 0 0 0.500 US BROWNFIELDS

Local Lists of Landfill / Solid Waste Disposal Sites 0 NR NR 0 0 0 0.500 DEBRIS REGION 9 0 NR NR 0 0 0 0.500 ODI 0 NR NR 0 0 0 0.500 SWRCY 0 NR NR 0 0 0 0.500 INDIAN ODI Local Lists of Hazardous waste /

Contaminated Sites 0 NR NR NR NR NR TP US CDL 0 NR NR 0 0 0 0.500 WI ERP 0 NR NR NR NR NR TP CDL 0 NR NR NR NR NR TP US HIST CDL Local Land Records 0 NR NR NR NR NR TP LIENS 2 0 NR NR 0 0 0 0.500 LUCIS Records of Emergency Release Reports 0 NR NR NR NR NR TP HMIRS 0 NR NR NR NR NR TP SPILLS 0 NR NR NR NR NR TP AGSPILLS Other Ascertainable Records 0 NR NR NR 0 0 0.250 RCRA-NonGen TC3220399.2s Page 5 MAP FINDINGS

SUMMARY

SearchTargetDistanceTotalDatabaseProperty(Miles)< 1/81/8 - 1/41/4 - 1/21/2 - 1> 1Plotted 0 NR NR NR NR NR TP DOT OPS 0 NR 0 0 0 0 1.000 DOD 0 NR 0 0 0 0 1.000 FUDS 0 NR 0 0 0 0 1.000 CONSENT 0 NR 0 0 0 0 1.000 ROD 0 NR NR 0 0 0 0.500 UMTRA 0 NR NR NR 0 0 0.250 MINES 0 NR NR NR NR NR TP TRIS 0 NR NR NR NR NR TP TSCA 0 NR NR NR NR NR TP FTTS 0 NR NR NR NR NR TP HIST FTTS 0 NR NR NR NR NR TP SSTS 0 NR NR NR NR NR TP ICIS 0 NR NR NR NR NR TP PADS 0 NR NR NR NR NR TP MLTS 0 NR NR NR NR NR TP RADINFO 0 NR NR NR NR NR TP FINDS 0 NR NR NR NR NR TP RAATS 0 NR NR NR NR NR TP BRRTS 0 NR NR NR NR NR TP NPDES 0 NR NR NR 0 0 0.250 MANIFEST 0 NR NR NR 0 0 0.250 DRYCLEANERS 0 NR NR NR NR NR TP WI WRRSER 0 NR NR NR NR NR TP AIRS 0 NR NR NR NR NR TP TIER 2 0 NR NR NR NR NR TP LEAD 0 NR 0 0 0 0 1.000 INDIAN RESERV 0 NR NR 0 0 0 0.500 SCRD DRYCLEANERS 0 NR NR 0 0 0 0.500 COAL ASH EPA 0 NR NR NR NR NR TP FINANCIAL ASSURANCE 0 NR NR 0 0 0 0.500 COAL ASH 0 NR NR NR NR NR TP PCB TRANSFORMER 0 NR NR NR NR NR TP COAL ASH DOE EDR PROPRIETARY RECORDS EDR Proprietary Records 0 NR 0 0 0 0 1.000 Manufactured Gas Plants NOTES: TP = Target Property

NR = Not Requested at this Search Distance

Sites may be listed in more than one database TC3220399.2s Page 6 MAP FINDINGS Map ID Direction EDR ID Number Distance EPA ID Number Database(s)

Site Elevation NO SITES FOUND TC3220399.2s Page 7 ORPHAN

SUMMARY

City EDR ID Site Name Site Address Zip Database(s)

Count: 13 records.

STEVENS POINT S109260948 STEVENS POINT AIRPORT #2 HWY 66 WI WRRSER STEVENS POINT S110356483 STEVENS POINT MUNICIPAL AIRPORT HWY 66 OF POINT E NPDES STEVENS POINT S106975782 STEVENS POINT ADDRESS UNKNOWN BRRTS STEVENS POINT S107426958 FROM STEVENS POINT CTY LIMITS TO C FROM STEVENS PT SPILLS STEVENS POINT S100670543 KWIK TRIP - STEVENS POINT 3533 E HWY 66 WI WRRSER STEVENS POINT S107429234 JUNCTION CITY TO STEVENS POINT JUNCTION CITY TO STEVENS PT SPILLS STEVENS POINT S109326408 WI RIVER & WISCONSIN ST WI RIV S SPILLS STEVENS POINT S110674654 WI RIVER BOAT LANDING RIVER RD BRRTS STEVENS POINT S107432651 UW STEVENS POINT BALDWIN HALL UW STEVENS PT SPILLS S TEVENS POINT S 11035760 2 S TEVENS POINT S TEVENS PT B RRTS S TEVENS POINT 1 01198539 8 S TEVENS POINT MUNI U NKNOWN F INDS S TEVENS POINT S 10768514 9 S TEVENS POINT WATER DEPARTMENT - W 1 00 WELL FIELD RD T IER 2 S TEVENS POINT S 10743321 9 W ISCONSIN RIVER BELOW POINT PAPER W ISCONSIN RIVER BELOW PT S PILLS TC3220399.2s Page 8 To maintain currency of the following federal and state databases, EDR contacts the appropriate governmental agency on a monthly or quarterly basis, as required.

Number of Days to Update:

Provides confirmation that EDR is reporting records that have been updated within 90 days from the date the government agency made the information available to the public.

STANDARD ENVIRONMENTAL RECORDS Federal NPL site list

NPL: National Priority List National Priorities List (Superfund). The NPL is a subset of CERCLIS and identifies over 1,200 sites for priority cleanup under the Superfund Program. NPL sites may encompass relatively large areas. As such, EDR provides polygon

coverage for over 1,000 NPL site boundaries produced by EPA's Environmental Photographic Interpretation Center (EPIC) and regional EPA offices.

Date of Government Version: 06/30/2011 Date Data Arrived at EDR: 07/12/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 79 Source: EPA

Telephone: N/A

Last EDR Contact: 10/12/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly NPL Site Boundaries Sources:

EPA's Environmental Photographic Interpretation Center (EPIC)

Telephone: 202-564-7333EPA Region 1EPA Region 6Telephone 617-918-1143Telephone: 214-655-6659EPA Region 3EPA Region 7Telephone 215-814-5418Telephone: 913-551-7247EPA Region 4EPA Region 8Telephone 404-562-8033Telephone: 303-312-6774EPA Region 5EPA Region 9Telephone 312-886-6686Telephone: 415-947-4246 EPA Region 10 Telephone 206-553-8665 Proposed NPL: Proposed National Priority List SitesA site that has been proposed for listing on the NationalPriorities List through the issuance of a proposed rule in the Federal Register.EPA then accepts public comments on the site, responds to the comments,and places on the NPL those sites that continue to meet therequirements for listing.

Date of Government Version: 06/30/2011 Date Data Arrived at EDR: 07/12/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 79 Source: EPA

Telephone: N/A

Last EDR Contact: 10/12/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly NPL LIENS: Federal Superfund Liens Federal Superfund Liens. Under the authority granted the USEPA by CERCLA of 1980, the USEPA has the authority

to file liens against real property in order to recover remedial action expenditures or when the property owner

received notification of potential liability. USEPA compiles a listing of filed notices of Superfund Liens.

Date of Government Version: 10/15/1991 Date Data Arrived at EDR: 02/02/1994

Date Made Active in Reports: 03/30/1994

Number of Days to Update: 56 Source: EPA

Telephone: 202-564-4267

Last EDR Contact: 08/15/2011

Next Scheduled EDR Contact: 11/28/2011

Data Release Frequency: No Update Planned TC3220399.2s Page GR-1 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Federal Delisted NPL site list DELISTED NPL: National Priority List Deletions The National Oil and Hazardous Substances Pollution Contingency Plan (NCP) establishes the criteria that the EPA uses to delete sites from the NPL. In accordance with 40 CFR 300.425.(e), sites may be deleted from the

NPL where no further response is appropriate.

Date of Government Version: 06/30/2011 Date Data Arrived at EDR: 07/12/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 79 Source: EPA

Telephone: N/A

Last EDR Contact: 10/12/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly Federal CERCLIS list CERCLIS: Comprehensive Environmental Response, Compensation, and Liability Information System CERCLIS contains data on potentially hazardous waste sites that have been reported to the USEPA by states, municipalities, private companies and private persons, pursuant to Section 103 of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA). CERCLIS contains sites which are either proposed to or on the National Priorities

List (NPL) and sites which are in the screening and assessment phase for possible inclusion on the NPL.

Date of Government Version: 02/25/2011 Date Data Arrived at EDR: 03/01/2011

Date Made Active in Reports: 05/02/2011

Number of Days to Update: 62 Source: EPA

Telephone: 703-412-9810

Last EDR Contact: 11/29/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Quarterly FEDERAL FACILITY: Federal Facility Site Information listing A listing of National Priority List (NPL) and Base Realignment and Closure (BRAC) sites found in the Comprehensive

Environmental Response, Compensation and Liability Information System (CERCLIS) Database where EPA Federal Facilities

Restoration and Reuse Office is involved in cleanup activities.

Date of Government Version: 12/10/2010 Date Data Arrived at EDR: 01/11/2011

Date Made Active in Reports: 02/16/2011

Number of Days to Update: 36 Source: Environmental Protection Agency

Telephone: 703-603-8704

Last EDR Contact: 10/14/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Varies Federal CERCLIS NFRAP site List CERCLIS-NFRAP: CERCLIS No Further Remedial Action Planned Archived sites are sites that have been removed and archived from the inventory of CERCLIS sites. Archived status indicates that, to the best of EPA's knowledge, assessment at a site has been completed and that EPA has determined

no further steps will be taken to list this site on the National Priorities List (NPL), unless information indicates

this decision was not appropriate or other considerations require a recommendation for listing at a later time.

This decision does not necessarily mean that there is no hazard associated with a given site; it only means that, based upon available information, the location is not judged to be a potential NPL site.

Date of Government Version: 02/25/2011 Date Data Arrived at EDR: 03/01/2011

Date Made Active in Reports: 05/02/2011

Number of Days to Update: 62 Source: EPA

Telephone: 703-412-9810

Last EDR Contact: 11/29/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Quarterly Federal RCRA CORRACTS facilities list CORRACTS: Corrective Action Report CORRACTS identifies hazardous waste handlers with RCRA corrective action activity.

TC3220399.2s Page GR-2 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 03/09/2011 Date Data Arrived at EDR: 03/15/2011

Date Made Active in Reports: 06/14/2011

Number of Days to Update: 91 Source: EPA

Telephone: 800-424-9346

Last EDR Contact: 11/14/2011

Next Scheduled EDR Contact: 02/27/2012

Data Release Frequency: Quarterly Federal RCRA non-CORRACTS TSD facilities list RCRA-TSDF: RCRA - Treatment, Storage and Disposal RCRAInfo is EPA's comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database

includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste

as defined by the Resource Conservation and Recovery Act (RCRA). Transporters are individuals or entities that

move hazardous waste from the generator offsite to a facility that can recycle, treat, store, or dispose of the

waste. TSDFs treat, store, or dispose of the waste.

Date of Government Version: 06/15/2011 Date Data Arrived at EDR: 07/07/2011

Date Made Active in Reports: 08/08/2011

Number of Days to Update: 32 Source: Environmental Protection Agency

Telephone: 312-886-6186

Last EDR Contact: 10/05/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Quarterly Federal RCRA generators list RCRA-LQG: RCRA - Large Quantity Generators RCRAInfo is EPA's comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database

includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste

as defined by the Resource Conservation and Recovery Act (RCRA). Large quantity generators (LQGs) generate

over 1,000 kilograms (kg) of hazardous waste, or over 1 kg of acutely hazardous waste per month.

Date of Government Version: 06/15/2011 Date Data Arrived at EDR: 07/07/2011

Date Made Active in Reports: 08/08/2011

Number of Days to Update: 32 Source: Environmental Protection Agency

Telephone: 312-886-6186

Last EDR Contact: 10/05/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Quarterly RCRA-SQG: RCRA - Small Quantity Generators RCRAInfo is EPA's comprehensive information system, providing access to data supporting the Resource Conservation

and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database

includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste

as defined by the Resource Conservation and Recovery Act (RCRA). Small quantity generators (SQGs) generate

between 100 kg and 1,000 kg of hazardous waste per month.

Date of Government Version: 06/15/2011 Date Data Arrived at EDR: 07/07/2011

Date Made Active in Reports: 08/08/2011

Number of Days to Update: 32 Source: Environmental Protection Agency

Telephone: 312-886-6186

Last EDR Contact: 10/05/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Quarterly RCRA-CESQG: RCRA - Conditionally Exempt Small Quantity Generators RCRAInfo is EPA's comprehensive information system, providing access to data supporting the Resource Conservation

and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database

includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste

as defined by the Resource Conservation and Recovery Act (RCRA). Conditionally exempt small quantity generators (CESQGs) generate less than 100 kg of hazardous waste, or less than 1 kg of acutely hazardous waste per month.

Date of Government Version: 06/15/2011 Date Data Arrived at EDR: 07/07/2011

Date Made Active in Reports: 08/08/2011

Number of Days to Update: 32 Source: Environmental Protection Agency

Telephone: 312-886-6186

Last EDR Contact: 10/05/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Varies TC3220399.2s Page GR-3 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Federal institutional controls / engineering controls registries US ENG CONTROLS: Engineering Controls Sites List A listing of sites with engineering controls in place. Engineering controls include various forms of caps, building foundations, liners, and treatment methods to create pathway elimination for regulated substances to enter environmental

media or effect human health.

Date of Government Version: 03/16/2011 Date Data Arrived at EDR: 03/25/2011

Date Made Active in Reports: 06/14/2011

Number of Days to Update: 81 Source: Environmental Protection Agency

Telephone: 703-603-0695

Last EDR Contact: 09/12/2011

Next Scheduled EDR Contact: 12/26/2011

Data Release Frequency: Varies US INST CONTROL: Sites with Institutional Controls A listing of sites with institutional controls in place. Institutional controls include administrative measures, such as groundwater use restrictions, construction restrictions, property use restrictions, and post remediation

care requirements intended to prevent exposure to contaminants remaining on site. Deed restrictions are generally

required as part of the institutional controls.

Date of Government Version: 03/16/2011 Date Data Arrived at EDR: 03/25/2011

Date Made Active in Reports: 06/14/2011

Number of Days to Update: 81 Source: Environmental Protection Agency

Telephone: 703-603-0695

Last EDR Contact: 09/12/2011

Next Scheduled EDR Contact: 12/26/2011

Data Release Frequency: Varies Federal ERNS list ERNS: Emergency Response Notification System Emergency Response Notification System. ERNS records and stores information on reported releases of oil and hazardous substances.

Date of Government Version: 10/03/2011 Date Data Arrived at EDR: 10/04/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 38 Source: National Response Center, United States Coast Guard

Telephone: 202-267-2180

Last EDR Contact: 10/04/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Annually State- and tribal - equivalent CERCLIS SHWS: Hazard Ranking List State Hazardous Waste Sites. State hazardous waste site records are the states' equivalent to CERCLIS. These sites may or may not already be listed on the federal CERCLIS list. Priority sites planned for cleanup using state funds (state equivalent of Superfund) are identified along with sites where cleanup will be paid for by potentially

responsible parties. Available information varies by state.

Date of Government Version: 11/30/1994 Date Data Arrived at EDR: 02/10/1995

Date Made Active in Reports: 03/01/1995

Number of Days to Update: 19 Source: Department of Natural Resources

Telephone: 608-266-2632

Last EDR Contact: 10/03/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: No Update Planned State and tribal landfill and/or solid waste disposal site lists SWF/LF: List of Licensed Landfills Solid Waste Facilities/Landfill Sites. SWF/LF type records typically contain an inventory of solid waste disposal facilities or landfills in a particular state. Depending on the state, these may be active or inactive facilities

or open dumps that failed to meet RCRA Subtitle D Section 4004 criteria for solid waste landfills or disposal

sites.TC3220399.2s Page GR-4 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 10/12/2011 Date Data Arrived at EDR: 10/13/2011

Date Made Active in Reports: 11/22/2011

Number of Days to Update: 40 Source: Department of Natural Resources

Telephone: 608-267-7557

Last EDR Contact: 10/03/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Semi-Annually WDS: Registry of Waste Disposal Sites The registry was created by the DNR to serve as a comprehensive listing of all sites where solid or hazardous

wastes have been or may have been deposited.

Date of Government Version: 07/19/2011 Date Data Arrived at EDR: 10/06/2011

Date Made Active in Reports: 10/25/2011

Number of Days to Update: 19 Source: Department of Natural Resources

Telephone: 608-266-2632

Last EDR Contact: 10/06/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: No Update Planned SHWIMS: Solid & Hazardous Waste Information Management System Information on sites, and facilities operating at sites, that are regulated by the Waste Management program Date of Government Version: 10/04/2011 Date Data Arrived at EDR: 10/06/2011

Date Made Active in Reports: 10/25/2011

Number of Days to Update: 19 Source: Department of Natural Resources

Telephone: 608-266-2414

Last EDR Contact: 10/06/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Quarterly State and tribal leaking storage tank lists LUST: Leaking Underground Storage Tank Database Leaking Underground Storage Tank Incident Reports. LUST records contain an inventory of reported leaking underground storage tank incidents. Not all states maintain these records, and the information stored varies by state.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly LAST: Leaking Aboveground Storage Tank Listing A listing of leaking aboveground storage tank sites.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Varies INDIAN LUST R9: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Arizona, California, New Mexico and Nevada Date of Government Version: 01/31/2011 Date Data Arrived at EDR: 02/01/2011

Date Made Active in Reports: 03/21/2011

Number of Days to Update: 48 Source: Environmental Protection Agency

Telephone: 415-972-3372

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Quarterly INDIAN LUST R4: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Florida, Mississippi and North Carolina.

Date of Government Version: 08/11/2011 Date Data Arrived at EDR: 08/12/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 32 Source: EPA Region 4

Telephone: 404-562-8677

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Semi-Annually TC3220399.2s Page GR-5 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING INDIAN LUST R10: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Alaska, Idaho, Oregon and Washington.

Date of Government Version: 11/02/2011 Date Data Arrived at EDR: 11/04/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 7 Source: EPA Region 10

Telephone: 206-553-2857

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Quarterly INDIAN LUST R1: Leaking Underground Storage Tanks on Indian Land A listing of leaking underground storage tank locations on Indian Land.

Date of Government Version: 10/01/2011 Date Data Arrived at EDR: 11/01/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 10 Source: EPA Region 1

Telephone: 617-918-1313

Last EDR Contact: 11/01/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies INDIAN LUST R6: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in New Mexico and Oklahoma.

Date of Government Version: 09/12/2011 Date Data Arrived at EDR: 09/13/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 59 Source: EPA Region 6

Telephone: 214-665-6597

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies INDIAN LUST R7: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Iowa, Kansas, and Nebraska Date of Government Version: 02/16/2011 Date Data Arrived at EDR: 06/02/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 103 Source: EPA Region 7

Telephone: 913-551-7003

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies INDIAN LUST R8: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Colorado, Montana, North Dakota, South Dakota, Utah and Wyoming.

Date of Government Version: 08/18/2011 Date Data Arrived at EDR: 08/19/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 25 Source: EPA Region 8

Telephone: 303-312-6271

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Quarterly State and tribal registered storage tank lists UST: Registered Underground Storage Tanks Registered Underground Storage Tanks. UST's are regulated under Subtitle I of the Resource Conservation and Recovery Act (RCRA) and must be registered with the state department responsible for administering the UST program. Available

information varies by state program.

Date of Government Version: 09/16/2011 Date Data Arrived at EDR: 09/22/2011

Date Made Active in Reports: 10/13/2011

Number of Days to Update: 21 Source: Department of Commerce

Telephone: 608-266-7874

Last EDR Contact: 09/22/2011

Next Scheduled EDR Contact: 01/02/2012

Data Release Frequency: Quarterly AST: Tanks Database Aboveground storage tank site locations.

TC3220399.2s Page GR-6 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 09/16/2011 Date Data Arrived at EDR: 09/22/2011

Date Made Active in Reports: 10/13/2011

Number of Days to Update: 21 Source: Department of Commerce

Telephone: 608-266-7874

Last EDR Contact: 09/22/2011

Next Scheduled EDR Contact: 01/02/2012

Data Release Frequency: Quarterly INDIAN UST R9: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 9 (Arizona, California, Hawaii, Nevada, the Pacific Islands, and Tribal Nations).

Date of Government Version: 08/04/2011 Date Data Arrived at EDR: 08/05/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 39 Source: EPA Region 9

Telephone: 415-972-3368

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Quarterly INDIAN UST R8: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 8 (Colorado, Montana, North Dakota, South Dakota, Utah, Wyoming and 27 Tribal Nations).

Date of Government Version: 08/18/2011 Date Data Arrived at EDR: 08/19/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 25 Source: EPA Region 8

Telephone: 303-312-6137

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Quarterly INDIAN UST R7: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 7 (Iowa, Kansas, Missouri, Nebraska, and 9 Tribal Nations).

Date of Government Version: 04/01/2011 Date Data Arrived at EDR: 06/01/2011

Date Made Active in Reports: 06/14/2011

Number of Days to Update: 13 Source: EPA Region 7

Telephone: 913-551-7003

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies INDIAN UST R10: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 10 (Alaska, Idaho, Oregon, Washington, and Tribal Nations).

Date of Government Version: 11/02/2011 Date Data Arrived at EDR: 11/04/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 7 Source: EPA Region 10

Telephone: 206-553-2857

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Quarterly INDIAN UST R1: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 1 (Connecticut, Maine, Massachusetts, New Hampshire, Rhode Island, Vermont and ten Tribal

Nations).Date of Government Version: 10/01/2011 Date Data Arrived at EDR: 11/01/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 10 Source: EPA, Region 1

Telephone: 617-918-1313

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies INDIAN UST R4: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 4 (Alabama, Florida, Georgia, Kentucky, Mississippi, North Carolina, South Carolina, Tennessee

and Tribal Nations)

TC3220399.2s Page GR-7 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 08/11/2011 Date Data Arrived at EDR: 08/12/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 32 Source: EPA Region 4

Telephone: 404-562-9424

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Semi-Annually INDIAN UST R5: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 5 (Michigan, Minnesota and Wisconsin and Tribal Nations).

Date of Government Version: 07/01/2011 Date Data Arrived at EDR: 08/26/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 18 Source: EPA Region 5

Telephone: 312-886-6136

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies INDIAN UST R6: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian

land in EPA Region 6 (Louisiana, Arkansas, Oklahoma, New Mexico, Texas and 65 Tribes).

Date of Government Version: 05/10/2011 Date Data Arrived at EDR: 05/11/2011

Date Made Active in Reports: 06/14/2011

Number of Days to Update: 34 Source: EPA Region 6

Telephone: 214-665-7591

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Semi-Annually FEMA UST: Underground Storage Tank Listing A listing of all FEMA owned underground storage tanks.

Date of Government Version: 01/01/2010 Date Data Arrived at EDR: 02/16/2010

Date Made Active in Reports: 04/12/2010

Number of Days to Update: 55 Source: FEMA

Telephone: 202-646-5797

Last EDR Contact: 10/17/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: Varies State and tribal institutional control / engineering control registries CRS: Closed Remediation Sites A Closed Remediation Site is parcel of land at which the groundwater has become contaminated and which is affected by a particular type of legal restriction. Specifically, certain steps have been taken to stabilize/remediate

the contamination, and the state is satisfied that no further efforts are necessary provided that the property

is not used for certain purposes.

Date of Government Version: 08/23/2011 Date Data Arrived at EDR: 08/25/2011

Date Made Active in Reports: 09/14/2011

Number of Days to Update: 20 Source: Department of Natural Resources

Telephone: 608-267-0554

Last EDR Contact: 11/24/2011

Next Scheduled EDR Contact: 03/05/2012

Data Release Frequency: Semi-Annually AUL: Deed Restriction at Closeout Sites Date a deed restriction is recorded at the Register of Deeds office for a property. Extent of soil contamination

is known but impracticable to remove now or an engineering control is required to be maintained or NR720 industrial

stds are applied. Restricts property use or requires future actions.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly State and tribal voluntary cleanup sites TC3220399.2s Page GR-8 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING INDIAN VCP R1: Voluntary Cleanup Priority Listing A listing of voluntary cleanup priority sites located on Indian Land located in Region 1.

Date of Government Version: 08/04/2011 Date Data Arrived at EDR: 10/04/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 38 Source: EPA, Region 1

Telephone: 617-918-1102

Last EDR Contact: 10/04/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Varies VCP: Voluntary Party Liability Exemption Sites The Voluntary Party Liability Exemption is an elective environmental cleanup program. Interested persons who meet

the definition of "voluntary party" are eligible to apply. A "voluntary party" is any person who submits an application

and pays all the necessary fees.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Varies INDIAN VCP R7: Voluntary Cleanup Priority Lisitng A listing of voluntary cleanup priority sites located on Indian Land located in Region 7.

Date of Government Version: 03/20/2008 Date Data Arrived at EDR: 04/22/2008

Date Made Active in Reports: 05/19/2008

Number of Days to Update: 27 Source: EPA, Region 7

Telephone: 913-551-7365

Last EDR Contact: 04/20/2009

Next Scheduled EDR Contact: 07/20/2009

Data Release Frequency: Varies State and tribal Brownfields sites BEAP: Brownfields Environmental Assessment Program The Brownfields Environmental Assessment Program (BEAP) was a federal program that assisted municipalities with Environmental Site Assessments (ESA's) for tax delinquent or bankrupt properties, or properties a local government

acquired for redevelopment. Using federal dollars, site assessments were conducted by Department of Natural Resources (DNR) staff to determine if the properties were contaminated.

Date of Government Version: 12/31/2000 Date Data Arrived at EDR: 05/29/2001

Date Made Active in Reports: 06/29/2001

Number of Days to Update: 31 Source: Department of Natural Resources

Telephone: 608-266-1618

Last EDR Contact: 08/17/2009

Next Scheduled EDR Contact: 11/16/2009

Data Release Frequency: No Update Planned BROWNFIELDS: Brownfields Site Locations Listing A listing of brownfields sites included in the BRRTS database. Brownfields are abandoned, idle or underused commercial

or industrial properties, where the expansion or redevelopment is hindered by real or perceived contamination.

Brownfields vary in size, location, age, and past use -- they can be anything from a five-hundred acre automobile

assembly plant to a small, abandoned corner gas station.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-266-3084

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly ADDITIONAL ENVIRONMENTAL RECORDS Local Brownfield lists US BROWNFIELDS: A Listing of Brownfields Sites TC3220399.2s Page GR-9 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Included in the listing are brownfields properties addresses by Cooperative Agreement Recipients and brownfields properties addressed by Targeted Brownfields Assessments. Targeted Brownfields Assessments-EPA's Targeted Brownfields

Assessments (TBA) program is designed to help states, tribes, and municipalities--especially those without EPA

Brownfields Assessment Demonstration Pilots--minimize the uncertainties of contamination often associated with

brownfields. Under the TBA program, EPA provides funding and/or technical assistance for environmental assessments

at brownfields sites throughout the country. Targeted Brownfields Assessments supplement and work with other efforts

under EPA's Brownfields Initiative to promote cleanup and redevelopment of brownfields. Cooperative Agreement

Recipients-States, political subdivisions, territories, and Indian tribes become Brownfields Cleanup Revolving

Loan Fund (BCRLF) cooperative agreement recipients when they enter into BCRLF cooperative agreements with the

U.S. EPA. EPA selects BCRLF cooperative agreement recipients based on a proposal and application process. BCRLF

cooperative agreement recipients must use EPA funds provided through BCRLF cooperative agreement for specified

brownfields-related cleanup activities.

Date of Government Version: 06/27/2011 Date Data Arrived at EDR: 06/27/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 78 Source: Environmental Protection Agency

Telephone: 202-566-2777

Last EDR Contact: 09/28/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: Semi-Annually Local Lists of Landfill / Solid Waste Disposal Sites ODI: Open Dump Inventory An open dump is defined as a disposal facility that does not comply with one or more of the Part 257 or Part 258 Subtitle D Criteria.

Date of Government Version: 06/30/1985 Date Data Arrived at EDR: 08/09/2004

Date Made Active in Reports: 09/17/2004

Number of Days to Update: 39 Source: Environmental Protection Agency

Telephone: 800-424-9346

Last EDR Contact: 06/09/2004

Next Scheduled EDR Contact: N/A

Data Release Frequency: No Update Planned DEBRIS REGION 9: Torres Martinez Reservation Illegal Dump Site Locations A listing of illegal dump sites location on the Torres Martinez Indian Reservation located in eastern Riverside

County and northern Imperial County, California.

Date of Government Version: 01/12/2009 Date Data Arrived at EDR: 05/07/2009

Date Made Active in Reports: 09/21/2009

Number of Days to Update: 137 Source: EPA, Region 9

Telephone: 415-947-4219

Last EDR Contact: 09/26/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: No Update Planned SWRCY: Recycling Center Listing A listing of recycling center locations.

Date of Government Version: 09/14/2011 Date Data Arrived at EDR: 09/16/2011

Date Made Active in Reports: 10/14/2011

Number of Days to Update: 28 Source: Solid & Hazardous Waste Education center

Telephone: 608-262-0936

Last EDR Contact: 11/28/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: Varies INDIAN ODI: Report on the Status of Open Dumps on Indian Lands Location of open dumps on Indian land.

Date of Government Version: 12/31/1998 Date Data Arrived at EDR: 12/03/2007

Date Made Active in Reports: 01/24/2008

Number of Days to Update: 52 Source: Environmental Protection Agency

Telephone: 703-308-8245

Last EDR Contact: 11/07/2011

Next Scheduled EDR Contact: 02/20/2012

Data Release Frequency: Varies Local Lists of Hazardous waste / Contaminated Sites TC3220399.2s Page GR-10 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING US CDL: Clandestine Drug Labs A listing of clandestine drug lab locations. The U.S. Department of Justice ("the Department") provides this web site as a public service. It contains addresses of some locations where law enforcement agencies reported

they found chemicals or other items that indicated the presence of either clandestine drug laboratories or dumpsites.

In most cases, the source of the entries is not the Department, and the Department has not verified the entry

and does not guarantee its accuracy. Members of the public must verify the accuracy of all entries by, for example, contacting local law enforcement and local health departments.

Date of Government Version: 06/08/2011 Date Data Arrived at EDR: 09/16/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 13 Source: Drug Enforcement Administration

Telephone: 202-307-1000

Last EDR Contact: 12/05/2011

Next Scheduled EDR Contact: 03/19/2012

Data Release Frequency: Quarterly ERP: Environmental Repair Program Database Environmental Repair Program sites are sites other than LUST's that have contaminated soil and/or groundwater.

Often, these are old historic releases to the environment.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly CDL: Clandestine Drug Lab Listing A listing of clandestine drug lab locations in the state.

Date of Government Version: 10/11/2011 Date Data Arrived at EDR: 10/21/2011

Date Made Active in Reports: 11/22/2011

Number of Days to Update: 32 Source: Department of Justice

Telephone: 920-832-2751

Last EDR Contact: 11/15/2011

Next Scheduled EDR Contact: 02/27/2012

Data Release Frequency: Varies US HIST CDL: National Clandestine Laboratory Register A listing of clandestine drug lab locations. The U.S. Department of Justice ("the Department") provides this

web site as a public service. It contains addresses of some locations where law enforcement agencies reported

they found chemicals or other items that indicated the presence of either clandestine drug laboratories or dumpsites.

In most cases, the source of the entries is not the Department, and the Department has not verified the entry

and does not guarantee its accuracy. Members of the public must verify the accuracy of all entries by, for example, contacting local law enforcement and local health departments.

Date of Government Version: 09/01/2007 Date Data Arrived at EDR: 11/19/2008

Date Made Active in Reports: 03/30/2009

Number of Days to Update: 131 Source: Drug Enforcement Administration

Telephone: 202-307-1000

Last EDR Contact: 03/23/2009

Next Scheduled EDR Contact: 06/22/2009

Data Release Frequency: No Update Planned Local Land Records LIENS 2: CERCLA Lien Information A Federal CERCLA ('Superfund') lien can exist by operation of law at any site or property at which EPA has spent Superfund monies. These monies are spent to investigate and address releases and threatened releases of contamination.

CERCLIS provides information as to the identity of these sites and properties.

Date of Government Version: 09/09/2011 Date Data Arrived at EDR: 09/16/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 13 Source: Environmental Protection Agency

Telephone: 202-564-6023

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies TC3220399.2s Page GR-11 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING LUCIS: Land Use Control Information System LUCIS contains records of land use control information pertaining to the former Navy Base Realignment and Closure properties.

Date of Government Version: 12/09/2005 Date Data Arrived at EDR: 12/11/2006

Date Made Active in Reports: 01/11/2007

Number of Days to Update: 31 Source: Department of the Navy

Telephone: 843-820-7326

Last EDR Contact: 11/22/2011

Next Scheduled EDR Contact: 03/05/2012

Data Release Frequency: Varies Records of Emergency Release Reports HMIRS: Hazardous Materials Information Reporting System Hazardous Materials Incident Report System. HMIRS contains hazardous material spill incidents reported to DOT.

Date of Government Version: 10/04/2011 Date Data Arrived at EDR: 10/04/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 38 Source: U.S. Department of Transportation

Telephone: 202-366-4555

Last EDR Contact: 10/04/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Annually SPILLS: Spills Database A discharge of a hazardous substance that may adversely impact, or threaten to adversely impact public health, welfare or the environment. Spills are usually cleaned up quickly.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly AG SPILLS: Agricultural Spill Cases Spills reported to the Department of Agriculture, Trade & Consumer Protection. There are two types of spills.

Long-term: These are mainly pesticide and fertilizer cases. Some might include other contaminants at the same

site. Some might involve wood-treaters - which use pesticides. All of them involve spills of products, but these

spills generally result from day to day use (chronic spills) rather than accidental spills (acute). Accidental:

These are the acute spills of pesticides and fertilizers and only involve pesticides and fertilizers. Most of

these are cleaned up and closed within 3 to 6 months.

Date of Government Version: 08/15/2011 Date Data Arrived at EDR: 08/19/2011

Date Made Active in Reports: 10/10/2011

Number of Days to Update: 52 Source: Department of Agriculture, Trade & Consumer Protection

Telephone: 608-224-5058

Last EDR Contact: 11/14/2011

Next Scheduled EDR Contact: 02/27/2012

Data Release Frequency: Varies Other Ascertainable Records RCRA-NonGen: RCRA - Non Generators RCRAInfo is EPA's comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database

includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste

as defined by the Resource Conservation and Recovery Act (RCRA). Non-Generators do not presently generate hazardous

waste.Date of Government Version: 06/15/2011 Date Data Arrived at EDR: 07/07/2011

Date Made Active in Reports: 08/08/2011

Number of Days to Update: 32 Source: Environmental Protection Agency

Telephone: 312-886-6186

Last EDR Contact: 10/05/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Varies TC3220399.2s Page GR-12 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING DOT OPS: Incident and Accident Data Department of Transporation, Office of Pipeline Safety Incident and Accident data.

Date of Government Version: 07/29/2011 Date Data Arrived at EDR: 08/09/2011

Date Made Active in Reports: 11/11/2011

Number of Days to Update: 94 Source: Department of Transporation, Office of Pipeline Safety

Telephone: 202-366-4595

Last EDR Contact: 11/08/2011

Next Scheduled EDR Contact: 02/20/2012

Data Release Frequency: Varies DOD: Department of Defense Sites This data set consists of federally owned or administered lands, administered by the Department of Defense, that

have any area equal to or greater than 640 acres of the United States, Puerto Rico, and the U.S. Virgin Islands.

Date of Government Version: 12/31/2005 Date Data Arrived at EDR: 11/10/2006

Date Made Active in Reports: 01/11/2007

Number of Days to Update: 62 Source: USGS

Telephone: 888-275-8747

Last EDR Contact: 10/20/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: Semi-Annually FUDS: Formerly Used Defense Sites The listing includes locations of Formerly Used Defense Sites properties where the US Army Corps of Engineers

is actively working or will take necessary cleanup actions.

Date of Government Version: 12/31/2009 Date Data Arrived at EDR: 08/12/2010

Date Made Active in Reports: 12/02/2010

Number of Days to Update: 112 Source: U.S. Army Corps of Engineers

Telephone: 202-528-4285

Last EDR Contact: 09/12/2011

Next Scheduled EDR Contact: 12/26/2011

Data Release Frequency: Varies CONSENT: Superfund (CERCLA) Consent Decrees Major legal settlements that establish responsibility and standards for cleanup at NPL (Superfund) sites. Released

periodically by United States District Courts after settlement by parties to litigation matters.

Date of Government Version: 06/01/2011 Date Data Arrived at EDR: 08/19/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 41 Source: Department of Justice, Consent Decree Library

Telephone: Varies

Last EDR Contact: 10/03/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Varies ROD: Records Of Decision Record of Decision. ROD documents mandate a permanent remedy at an NPL (Superfund) site containing technical

and health information to aid in the cleanup.

Date of Government Version: 07/31/2011 Date Data Arrived at EDR: 09/14/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 15 Source: EPA

Telephone: 703-416-0223

Last EDR Contact: 09/14/2011

Next Scheduled EDR Contact: 12/26/2011

Data Release Frequency: Annually UMTRA: Uranium Mill Tailings Sites Uranium ore was mined by private companies for federal government use in national defense programs. When the mills

shut down, large piles of the sand-like material (mill tailings) remain after uranium has been extracted from the ore. Levels of human exposure to radioactive materials from the piles are low; however, in some cases tailings

were used as construction materials before the potential health hazards of the tailings were recognized.

Date of Government Version: 09/14/2010 Date Data Arrived at EDR: 10/21/2010

Date Made Active in Reports: 01/28/2011

Number of Days to Update: 99 Source: Department of Energy

Telephone: 505-845-0011

Last EDR Contact: 11/29/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Varies TC3220399.2s Page GR-13 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING MINES: Mines Master Index File Contains all mine identification numbers issued for mines active or opened since 1971. The data also includes violation information.

Date of Government Version: 08/18/2011 Date Data Arrived at EDR: 09/08/2011

Date Made Active in Reports: 09/29/2011

Number of Days to Update: 21 Source: Department of Labor, Mine Safety and Health Administration

Telephone: 303-231-5959

Last EDR Contact: 12/07/2011

Next Scheduled EDR Contact: 03/19/2012

Data Release Frequency: Semi-Annually TRIS: Toxic Chemical Release Inventory System Toxic Release Inventory System. TRIS identifies facilities which release toxic chemicals to the air, water and

land in reportable quantities under SARA Title III Section 313.

Date of Government Version: 12/31/2009 Date Data Arrived at EDR: 12/17/2010

Date Made Active in Reports: 03/21/2011

Number of Days to Update: 94 Source: EPA

Telephone: 202-566-0250

Last EDR Contact: 12/02/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Annually TSCA: Toxic Substances Control Act Toxic Substances Control Act. TSCA identifies manufacturers and importers of chemical substances included on the

TSCA Chemical Substance Inventory list. It includes data on the production volume of these substances by plant

site.Date of Government Version: 12/31/2006 Date Data Arrived at EDR: 09/29/2010

Date Made Active in Reports: 12/02/2010

Number of Days to Update: 64 Source: EPA

Telephone: 202-260-5521

Last EDR Contact: 09/27/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: Every 4 Years FTTS: FIFRA/ TSCA Tracking System - FIFRA (Federal Insecticide, Fungicide, & Rodenticide Act)/TSCA (Toxic Substances Control A ct)FTTS tracks administrative cases and pesticide enforcement actions and compliance activities related to FIFRA, TSCA and EPCRA (Emergency Planning and Community Right-to-Know Act). To maintain currency, EDR contacts the

Agency on a quarterly basis.

Date of Government Version: 04/09/2009 Date Data Arrived at EDR: 04/16/2009

Date Made Active in Reports: 05/11/2009

Number of Days to Update: 25 Source: EPA/Office of Prevention, Pesticides and Toxic Substances

Telephone: 202-566-1667

Last EDR Contact: 11/28/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Quarterly FTTS INSP: FIFRA/ TSCA Tracking System - FIFRA (Federal Insecticide, Fungicide, & Rodenticide Act)/TSCA (Toxic Substances Cont rol Act)A listing of FIFRA/TSCA Tracking System (FTTS) inspections and enforcements.

Date of Government Version: 04/09/2009 Date Data Arrived at EDR: 04/16/2009

Date Made Active in Reports: 05/11/2009

Number of Days to Update: 25 Source: EPA

Telephone: 202-566-1667

Last EDR Contact: 11/28/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Quarterly HIST FTTS: FIFRA/TSCA Tracking System Administrative Case Listing A complete administrative case listing from the FIFRA/TSCA Tracking System (FTTS) for all ten EPA regions. The

information was obtained from the National Compliance Database (NCDB). NCDB supports the implementation of FIFRA (Federal Insecticide, Fungicide, and Rodenticide Act) and TSCA (Toxic Substances Control Act). Some EPA regions

are now closing out records. Because of that, and the fact that some EPA regions are not providing EPA Headquarters

with updated records, it was decided to create a HIST FTTS database. It included records that may not be included

in the newer FTTS database updates. This database is no longer updated.

TC3220399.2s Page GR-14 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 10/19/2006 Date Data Arrived at EDR: 03/01/2007

Date Made Active in Reports: 04/10/2007

Number of Days to Update: 40 Source: Environmental Protection Agency

Telephone: 202-564-2501

Last EDR Contact: 12/17/2007

Next Scheduled EDR Contact: 03/17/2008

Data Release Frequency: No Update Planned HIST FTTS INSP: FIFRA/TSCA Tracking System Inspection & Enforcement Case Listing A complete inspection and enforcement case listing from the FIFRA/TSCA Tracking System (FTTS) for all ten EPA

regions. The information was obtained from the National Compliance Database (NCDB). NCDB supports the implementation

of FIFRA (Federal Insecticide, Fungicide, and Rodenticide Act) and TSCA (Toxic Substances Control Act). Some

EPA regions are now closing out records. Because of that, and the fact that some EPA regions are not providing

EPA Headquarters with updated records, it was decided to create a HIST FTTS database. It included records that

may not be included in the newer FTTS database updates. This database is no longer updated.

Date of Government Version: 10/19/2006 Date Data Arrived at EDR: 03/01/2007

Date Made Active in Reports: 04/10/2007

Number of Days to Update: 40 Source: Environmental Protection Agency

Telephone: 202-564-2501

Last EDR Contact: 12/17/2008

Next Scheduled EDR Contact: 03/17/2008

Data Release Frequency: No Update Planned SSTS: Section 7 Tracking Systems Section 7 of the Federal Insecticide, Fungicide and Rodenticide Act, as amended (92 Stat. 829) requires all

registered pesticide-producing establishments to submit a report to the Environmental Protection Agency by March

1st each year. Each establishment must report the types and amounts of pesticides, active ingredients and devices

being produced, and those having been produced and sold or distributed in the past year.

Date of Government Version: 12/31/2009 Date Data Arrived at EDR: 12/10/2010

Date Made Active in Reports: 02/25/2011

Number of Days to Update: 77 Source: EPA

Telephone: 202-564-4203

Last EDR Contact: 10/31/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Annually ICIS: Integrated Compliance Information System The Integrated Compliance Information System (ICIS) supports the information needs of the national enforcement

and compliance program as well as the unique needs of the National Pollutant Discharge Elimination System (NPDES)

program.Date of Government Version: 01/07/2011 Date Data Arrived at EDR: 01/21/2011

Date Made Active in Reports: 03/21/2011

Number of Days to Update: 59 Source: Environmental Protection Agency

Telephone: 202-564-5088

Last EDR Contact: 09/26/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: Quarterly PADS: PCB Activity Database System PCB Activity Database. PADS Identifies generators, transporters, commercial storers and/or brokers and disposers

of PCB's who are required to notify the EPA of such activities.

Date of Government Version: 11/01/2010 Date Data Arrived at EDR: 11/10/2010

Date Made Active in Reports: 02/16/2011

Number of Days to Update: 98 Source: EPA

Telephone: 202-566-0500

Last EDR Contact: 10/19/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: Annually MLTS: Material Licensing Tracking System MLTS is maintained by the Nuclear Regulatory Commission and contains a list of approximately 8,100 sites which

possess or use radioactive materials and which are subject to NRC licensing requirements. To maintain currency, EDR contacts the Agency on a quarterly basis.

Date of Government Version: 06/21/2011 Date Data Arrived at EDR: 07/15/2011

Date Made Active in Reports: 09/13/2011

Number of Days to Update: 60 Source: Nuclear Regulatory Commission

Telephone: 301-415-7169

Last EDR Contact: 09/12/2011

Next Scheduled EDR Contact: 12/26/2011

Data Release Frequency: Quarterly TC3220399.2s Page GR-15 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING RADINFO: Radiation Information Database The Radiation Information Database (RADINFO) contains information about facilities that are regulated by U.S.

Environmental Protection Agency (EPA) regulations for radiation and radioactivity.

Date of Government Version: 01/11/2011 Date Data Arrived at EDR: 01/13/2011

Date Made Active in Reports: 02/16/2011

Number of Days to Update: 34 Source: Environmental Protection Agency

Telephone: 202-343-9775

Last EDR Contact: 10/13/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly FINDS: Facility Index System/Facility Registry System Facility Index System. FINDS contains both facility information and 'pointers' to other sources that contain more

detail. EDR includes the following FINDS databases in this report: PCS (Permit Compliance System), AIRS (Aerometric

Information Retrieval System), DOCKET (Enforcement Docket used to manage and track information on civil judicial

enforcement cases for all environmental statutes), FURS (Federal Underground Injection Control), C-DOCKET (Criminal

Docket System used to track criminal enforcement actions for all environmental statutes), FFIS (Federal Facilities

Information System), STATE (State Environmental Laws and Statutes), and PADS (PCB Activity Data System).

Date of Government Version: 04/14/2010 Date Data Arrived at EDR: 04/16/2010

Date Made Active in Reports: 05/27/2010

Number of Days to Update: 41 Source: EPA

Telephone: (312) 353-2000

Last EDR Contact: 09/13/2011

Next Scheduled EDR Contact: 12/26/2011

Data Release Frequency: Quarterly RAATS: RCRA Administrative Action Tracking System RCRA Administration Action Tracking System. RAATS contains records based on enforcement actions issued under RCRA

pertaining to major violators and includes administrative and civil actions brought by the EPA. For administration

actions after September 30, 1995, data entry in the RAATS database was discontinued. EPA will retain a copy of

the database for historical records. It was necessary to terminate RAATS because a decrease in agency resources

made it impossible to continue to update the information contained in the database.

Date of Government Version: 04/17/1995 Date Data Arrived at EDR: 07/03/1995

Date Made Active in Reports: 08/07/1995

Number of Days to Update: 35 Source: EPA

Telephone: 202-564-4104

Last EDR Contact: 06/02/2008

Next Scheduled EDR Contact: 09/01/2008

Data Release Frequency: No Update Planned BRS: Biennial Reporting System The Biennial Reporting System is a national system administered by the EPA that collects data on the generation

and management of hazardous waste. BRS captures detailed data from two groups: Large Quantity Generators (LQG)

and Treatment, Storage, and Disposal Facilities.

Date of Government Version: 12/31/2009 Date Data Arrived at EDR: 03/01/2011

Date Made Active in Reports: 05/02/2011

Number of Days to Update: 62 Source: EPA/NTIS

Telephone: 800-424-9346

Last EDR Contact: 11/30/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Biennially BRRTS: Bureau of Remediation & Redevelopment Tracking System TC3220399.2s Page GR-16 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING BRRTS is a tracking system of contaminated sites. It holds key information for finding out more about a site or an activity. Activity types included are: Abandoned Container - An abandoned container with potentially hazardous

contents recovered from a site. No discharge to the environment occurs. If the container did release a hazardous

substance, a spill would be associated with the site. Superfund - is a federal program created by Congress in

1980 to finance cleanup of the nation's worst hazardous waste sites. VPLE - Voluntary Property Liability Exemptions

apply to sites in which a property owner conducts an environmental investigation and cleanup of an entire property

and then receives limits on their future liability. General Property - Environmental actions which apply to the

property as a whole, rather than a specific source of contamination, such as the LUST or environmental repair

site. Examples would be off-site letters, municipal liability clarification letters, lease letters, voluntary

party liability exemption actions, and general liability clarification letters.

Date of Government Version: 07/18/2011 Date Data Arrived at EDR: 07/21/2011

Date Made Active in Reports: 08/01/2011

Number of Days to Update: 11 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 11/03/2011

Next Scheduled EDR Contact: 01/23/2012

Data Release Frequency: Quarterly NPDES: NPDES Permit Listing A listing of stormwater permit industrial facilities.

Date of Government Version: 09/01/2011 Date Data Arrived at EDR: 09/01/2011

Date Made Active in Reports: 10/14/2011

Number of Days to Update: 43 Source: Department of Natural Resources

Telephone: 608-264-8971

Last EDR Contact: 11/30/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Quarterly WI MANIFEST: Manifest Information Hazardous waste manifest information.

Date of Government Version: 12/31/2010 Date Data Arrived at EDR: 08/19/2011

Date Made Active in Reports: 09/15/2011

Number of Days to Update: 27 Source: Department of Natural Resources

Telephone: N/A

Last EDR Contact: 09/19/2011

Next Scheduled EDR Contact: 01/02/2012

Data Release Frequency: Annually DRYCLEANERS: Five Star Recognition Program Sites Drycleaning facilities enrolled in the Five Star Recognition Program. The primary focus of the Five Star program

is to encourage reductions in the use and emissions of perchloroethylene (perc), a common but potentially hazardous

drycleaning solvent. Participating cleaners pursue recycling opportunities, spill prevention strategies, more

efficient solvent use, and more wet cleaning to reduce their perc consumption.

Date of Government Version: 10/05/2011 Date Data Arrived at EDR: 10/06/2011

Date Made Active in Reports: 10/25/2011

Number of Days to Update: 19 Source: Department of Natural Resources

Telephone: 608-267-3125

Last EDR Contact: 09/23/2011

Next Scheduled EDR Contact: 01/02/2012

Data Release Frequency: Varies WRRSER: Wisconsin Remedial Response Site Evaluation Report The WRRSER provides information about location, status, and priority of sites or facilities in the state which

are known to cause or have a high potential to cause environmental pollution.

Date of Government Version: 10/01/1995 Date Data Arrived at EDR: 01/02/1996

Date Made Active in Reports: 02/01/1996

Number of Days to Update: 30 Source: Department of Natural Resources

Telephone: 608-261-6422

Last EDR Contact: 10/03/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: No Update Planned AIRS: Air Permit Program Listing A listing of permits issued by the Air Permit Program.

TC3220399.2s Page GR-17 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 12/31/2010 Date Data Arrived at EDR: 08/05/2011

Date Made Active in Reports: 09/15/2011

Number of Days to Update: 41 Source: Department of Natural Resources

Telephone: 608-266-2621

Last EDR Contact: 10/24/2011

Next Scheduled EDR Contact: 02/06/2012

Data Release Frequency: Annually TIER 2: Tier 2 Facility Listing A listing of facilities which store or manufacture hazardous materials that submit a chemical inventory report.

Date of Government Version: 12/31/2009 Date Data Arrived at EDR: 08/17/2010

Date Made Active in Reports: 09/29/2010

Number of Days to Update: 43 Source: Department of Natural Resources

Telephone: 608-242-3225

Last EDR Contact: 10/24/2011

Next Scheduled EDR Contact: 02/06/2012

Data Release Frequency: Varies LEAD: Lead Inspection Data Lead inspection information.

Date of Government Version: 04/29/2011 Date Data Arrived at EDR: 04/29/2011

Date Made Active in Reports: 06/06/2011

Number of Days to Update: 38 Source: Department of Health & Family Services

Telephone: 608-267-0473

Last EDR Contact: 10/25/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: Annually INDIAN RESERV: Indian Reservations This map layer portrays Indian administered lands of the United States that have any area equal to or greater

than 640 acres.

Date of Government Version: 12/31/2005 Date Data Arrived at EDR: 12/08/2006

Date Made Active in Reports: 01/11/2007

Number of Days to Update: 34 Source: USGS

Telephone: 202-208-3710

Last EDR Contact: 10/20/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: Semi-Annually SCRD DRYCLEANERS: State Coalition for Remediation of Drycleaners Listing The State Coalition for Remediation of Drycleaners was established in 1998, with support from the U.S. EPA Office

of Superfund Remediation and Technology Innovation. It is comprised of representatives of states with established

drycleaner remediation programs. Currently the member states are Alabama, Connecticut, Florida, Illinois, Kansas, Minnesota, Missouri, North Carolina, Oregon, South Carolina, Tennessee, Texas, and Wisconsin.

Date of Government Version: 03/07/2011 Date Data Arrived at EDR: 03/09/2011

Date Made Active in Reports: 05/02/2011

Number of Days to Update: 54 Source: Environmental Protection Agency

Telephone: 615-532-8599

Last EDR Contact: 10/24/2011

Next Scheduled EDR Contact: 02/06/2012

Data Release Frequency: Varies FEDLAND: Federal and Indian Lands Federally and Indian administrated lands of the United States. Lands included are administrated by: Army Corps

of Engineers, Bureau of Reclamation, National Wild and Scenic River, National Wildlife Refuge, Public Domain Land, Wilderness, Wilderness Study Area, Wildlife Management Area, Bureau of Indian Affairs, Bureau of Land Management, Department of Justice, Forest Service, Fish and Wildlife Service, National Park Service.

Date of Government Version: 12/31/2005 Date Data Arrived at EDR: 02/06/2006

Date Made Active in Reports: 01/11/2007

Number of Days to Update: 339 Source: U.S. Geological Survey

Telephone: 888-275-8747

Last EDR Contact: 10/20/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: N/A COAL ASH EPA: Coal Combustion Residues Surface Impoundments List A listing of coal combustion residues surface impoundments with high hazard potential ratings.

TC3220399.2s Page GR-18 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 08/17/2010 Date Data Arrived at EDR: 01/03/2011

Date Made Active in Reports: 03/21/2011

Number of Days to Update: 77 Source: Environmental Protection Agency

Telephone: N/A

Last EDR Contact: 09/16/2011

Next Scheduled EDR Contact: 12/26/2011

Data Release Frequency: Varies FINANCIAL ASSURANCE 1: Financial Assurance Information Listing Financial Assurance information.

Date of Government Version: 09/26/2011 Date Data Arrived at EDR: 09/27/2011

Date Made Active in Reports: 10/14/2011

Number of Days to Update: 17 Source: Department of Natural Resources

Telephone: 608-266-6965

Last EDR Contact: 09/26/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: Varies COAL ASH: Coal Ash Disposal Site Listing A listing of coal combusion monofills.

Date of Government Version: 03/16/2011 Date Data Arrived at EDR: 03/18/2011

Date Made Active in Reports: 04/12/2011

Number of Days to Update: 25 Source: Deaprtment of Natural Resources

Telephone: 608-267-3538

Last EDR Contact: 10/03/2011

Next Scheduled EDR Contact: 01/16/2012

Data Release Frequency: Varies PCB TRANSFORMER: PCB Transformer Registration Database The database of PCB transformer registrations that includes all PCB registration submittals.

Date of Government Version: 01/01/2008 Date Data Arrived at EDR: 02/18/2009

Date Made Active in Reports: 05/29/2009

Number of Days to Update: 100 Source: Environmental Protection Agency

Telephone: 202-566-0517

Last EDR Contact: 11/04/2011

Next Scheduled EDR Contact: 02/13/2012

Data Release Frequency: Varies COAL ASH DOE: Sleam-Electric Plan Operation Data A listing of power plants that store ash in surface ponds.

Date of Government Version: 12/31/2005 Date Data Arrived at EDR: 08/07/2009

Date Made Active in Reports: 10/22/2009

Number of Days to Update: 76 Source: Department of Energy

Telephone: 202-586-8719

Last EDR Contact: 10/18/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: Varies FINANCIAL ASSURANCE 2: Financial Assurance Information Listing Information for underground storage tanks. Financial assurance is intended to ensure that resources are available

to pay for the cost of closure, post-closure care, and corrective measures if the owner or operator of a regulated

facility is unable or unwilling to pay.

Date of Government Version: 09/26/2011 Date Data Arrived at EDR: 10/19/2011

Date Made Active in Reports: 11/22/2011

Number of Days to Update: 34 Source: Department of Commerce

Telephone: 608-266-0956

Last EDR Contact: 09/26/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: Varies EDR PROPRIETARY RECORDS EDR Proprietary Records Manufactured Gas Plants: EDR Proprietary Manufactured Gas Plants The EDR Proprietary Manufactured Gas Plant Database includes records of coal gas plants (manufactured gas plants) compiled by EDR's researchers. Manufactured gas sites were used in the United States from the 1800's to 1950's

to produce a gas that could be distributed and used as fuel. These plants used whale oil, rosin, coal, or a mixture

of coal, oil, and water that also produced a significant amount of waste. Many of the byproducts of the gas production, such as coal tar (oily waste containing volatile and non-volatile chemicals), sludges, oils and other compounds

are potentially hazardous to human health and the environment. The byproduct from this process was frequently

disposed of directly at the plant site and can remain or spread slowly, serving as a continuous source of soil

and groundwater contamination.

TC3220399.2s Page GR-19 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: N/A Date Data Arrived at EDR: N/A

Date Made Active in Reports: N/A

Number of Days to Update: N/A Source: EDR, Inc.

Telephone: N/A

Last EDR Contact: N/A

Next Scheduled EDR Contact: N/A

Data Release Frequency: No Update Planned OTHER DATABASE(S)

Depending on the geographic area covered by this report, the data provided in these specialty databases may or may not be

complete. For example, the existence of wetlands information data in a specific report does not mean that all wetlands in the

area covered by the report are included. Moreover, the absence of any reported wetlands information does not necessarily

mean that wetlands do not exist in the area covered by the report.

CT MANIFEST: Hazardous Waste Manifest Data Facility and manifest data. Manifest is a document that lists and tracks hazardous waste from the generator through transporters to a tsd facility.

Date of Government Version: 12/31/2007 Date Data Arrived at EDR: 08/26/2009

Date Made Active in Reports: 09/11/2009

Number of Days to Update: 16 Source: Department of Environmental Protection

Telephone: 860-424-3375

Last EDR Contact: 11/22/2011

Next Scheduled EDR Contact: 03/05/2012

Data Release Frequency: Annually NJ MANIFEST: Manifest Information Hazardous waste manifest information.

Date of Government Version: 12/31/2010 Date Data Arrived at EDR: 07/20/2011

Date Made Active in Reports: 08/11/2011

Number of Days to Update: 22 Source: Department of Environmental Protection

Telephone: N/A

Last EDR Contact: 10/18/2011

Next Scheduled EDR Contact: 01/30/2012

Data Release Frequency: Annually NY MANIFEST: Facility and Manifest Data Manifest is a document that lists and tracks hazardous waste from the generator through transporters to a TSD

facility.Date of Government Version: 08/01/2011 Date Data Arrived at EDR: 08/09/2011

Date Made Active in Reports: 09/16/2011

Number of Days to Update: 38 Source: Department of Environmental Conservation

Telephone: 518-402-8651

Last EDR Contact: 11/08/2011

Next Scheduled EDR Contact: 02/20/2012

Data Release Frequency: Annually PA MANIFEST: Manifest Information Hazardous waste manifest information.

Date of Government Version: 12/31/2008 Date Data Arrived at EDR: 12/01/2009

Date Made Active in Reports: 12/14/2009

Number of Days to Update: 13 Source: Department of Environmental Protection

Telephone: 717-783-8990

Last EDR Contact: 09/26/2011

Next Scheduled EDR Contact: 01/09/2012

Data Release Frequency: Annually RI MANIFEST: Manifest information Hazardous waste manifest information Date of Government Version: 12/31/2010 Date Data Arrived at EDR: 06/24/2011

Date Made Active in Reports: 06/30/2011

Number of Days to Update: 6 Source: Department of Environmental Management

Telephone: 401-222-2797

Last EDR Contact: 11/28/2011

Next Scheduled EDR Contact: 03/12/2012

Data Release Frequency: Annually TC3220399.2s Page GR-20 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING VT MANIFEST: Hazardous Waste Manifest Data Hazardous waste manifest information.

Date of Government Version: 08/11/2011 Date Data Arrived at EDR: 08/26/2011

Date Made Active in Reports: 09/14/2011

Number of Days to Update: 19 Source: Department of Environmental Conservation

Telephone: 802-241-3443

Last EDR Contact: 10/24/2011

Next Scheduled EDR Contact: 02/06/2012

Data Release Frequency: AnnuallyOil/Gas Pipelines:This data was obtained by EDR from the USGS in 1994. It is referred to by USGS as GeoData Digital Line Graphs

from 1:100,000-Scale Maps. It was extracted from the transportation category including some oil, but primarily

gas pipelines.

Electric Power Transmission Line Data Source: Rextag Strategies Corp.

Telephone: (281) 769-2247

U.S. Electric Transmission and Power Plants Systems Digital GIS DataSensitive Receptors:There are individuals deemed sensitive receptors due to their fragile immune systems and special sensitivity

to environmental discharges. These sensitive receptors typically include the elderly, the sick, and children. While the locat ion of all

sensitive receptors cannot be determined, EDR indicates those buildings and facilities - schools, daycares, hospitals, medical

centers, and nursing homes - where individuals who are sensitive receptors are likely to be located.

AHA Hospitals:

Source: American Hospital Association, Inc.

Telephone: 312-280-5991

The database includes a listing of hospitals based on the American Hospital Association's annual survey of hospitals.

Medical Centers: Provider of Services Listing Source: Centers for Medicare & Medicaid Services

Telephone: 410-786-3000

A listing of hospitals with Medicare provider number, produced by Centers of Medicare & Medicaid Services, a federal agency within the U.S. Department of Health and Human Services.

Nursing Homes Source: National Institutes of Health

Telephone: 301-594-6248

Information on Medicare and Medicaid certified nursing homes in the United States.

Public Schools Source: National Center for Education Statistics

Telephone: 202-502-7300

The National Center for Education Statistics' primary database on elementary

and secondary public education in the United States. It is a comprehensive, annual, national statistical

database of all public elementary and secondary schools and school districts, which contains data that are

comparable across all states.

Private Schools Source: National Center for Education Statistics

Telephone: 202-502-7300

The National Center for Education Statistics' primary database on private school locations in the United States.

Daycare Centers: Day Care Directory Source: Department of Health & Family Services

Telephone: 608-266-9314Flood Zone Data:This data, available in select counties across the country, was obtained by EDR in 2003 & 2011 from the Federal

Emergency Management Agency (FEMA). Data depicts 100-year and 500-year flood zones as defined by FEMA.NWI:National Wetlands Inventory. This data, available in select counties across the country, was obtained by EDR in 2002 and 2005 from the U.S. Fish and Wildlife Service.

Scanned Digital USGS 7.5' Topographic Map (DRG)

Source: United States Geologic Survey A digital raster graphic (DRG) is a scanned image of a U.S. Geological Survey topographic map. The map images

are made by scanning published paper maps on high-resolution scanners. The raster image

is georeferenced and fit to the Universal Transverse Mercator (UTM) projection.

TC3220399.2s Page GR-21 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING STREET AND ADDRESS INFORMATION

© 2010 Tele Atlas North America, Inc. All rights reserved. This material is proprietary and the subject of copyright protectio n and other intellectual property rights owned by or licensed to Tele Atlas North America, Inc. The use of this material is subj ect to the terms of a license agreement. You will be held liable for any unauthorized copying or disclosure of this material.

TC3220399.2s Page GR-22 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING TC3220399.2s Page A-1 geologic strata.

of the soil, and nearby wells. Groundwater flow velocity is generally impacted by the nature of the

Groundwater flow direction may be impacted by surface topography, hydrology, hydrogeology, characteristics

2. Groundwater flow velocity.

1. Groundwater flow direction, and Assessment of the impact of contaminant migration generally has two principle investigative components:

forming an opinion about the impact of potential contaminant migration.

EDR's GeoCheck Physical Setting Source Addendum is provided to assist the environmental professional in 1991 Most Recent Revision:

44089-E5 STEVENS POINT, WI West Map: 1976 Most Recent Revision:

44089-D5 WHITING, WI Southwest Map:

1969 Most Recent Revision:

44089-D4 ARNOTT, WI South Map:

1986 Most Recent Revision:

44089-E4 POLONIA, WI Target Property Map:

USGS TOPOGRAPHIC MAP 1113 ft. above sea level Elevation:

4931000.0 UTM Y (Meters):

301598.3 UTM X (Meters):

Zone 16 Universal Tranverse Mercator:

89.4959 - 89 29' 45.3

Longitude (West):

44.50700 - 44 30' 25.2

Latitude (North):

TARGET PROPERTY COORDINATES STEVENS POINT, WI 54482

LANDS END WAY, SHINE MEDICAL STEVENS POINT, WI TARGET PROPERTY ADDRESSGEOCHECK - PHYSICAL SETTING SOURCE ADDENDUM TC3220399.2s Page A-2 should be field verified.

on a relative (not an absolute) basis. Relative elevation information between sites of close proximity

Source: Topography has been determined from the USGS 7.5' Digital Elevation Model and should be evaluated SURROUNDING TOPOGRAPHY: ELEVATION PROFILES Elevation (ft)

Elevation (ft)

TP TP 0 1/2 1 MilesTarget Property Elevation: 1113 ft.

North SouthWestEast 1106 1107 1108 1110 1110 1111 1111 1111 1111 1113 1113 1114 1115 1114 1113 1113 1113 1112 1112 1105 1105 1107 1108 1109 1110 1111 1111 1111 1113 1113 1114 1115 1116 1118 1120 1121 1124 1125 General SW General Topographic Gradient:

TARGET PROPERTY TOPOGRAPHY should contamination exist on the target property, what downgradient sites might be impacted.

assist the environmental professional in forming an opinion about the impact of nearby contaminated properties or, Surface topography may be indicative of the direction of surficial groundwater flow. This information can be used to TOPOGRAPHIC INFORMATION collected on nearby properties, and regional groundwater flow information (from deep aquifers).

sources of information, such as surface topographic information, hydrologic information, hydrogeologic data

using site-specific well data. If such data is not reasonably ascertainable, it may be necessary to rely on other

Groundwater flow direction for a particular site is best determined by a qualified environmental professional GROUNDWATER FLOW DIRECTION INFORMATIONGEOCHECK - PHYSICAL SETTING SOURCE

SUMMARY

TC3220399.2s Page A-3 Not Reported GENERAL DIRECTION LOCATION GROUNDWATER FLOW FROM TP MAP ID hydrogeologically, and the depth to water table.

authorities at select sites and has extracted the date of the report, groundwater flow direction as determined

flow at specific points. EDR has reviewed reports submitted by environmental professionals to regulatory

EDR has developed the AQUIFLOW Information System to provide data on the general direction of groundwater AQUIFLOW Search Radius: 1.000 Mile.

Not found Status:

1.25 miles Search Radius:

Site-Specific Hydrogeological Data*:

of the information and opinions presented are those of the cited EPA report(s), which were completed under a Comprehensive Environmental Response Compensation and Liability Information System (CERCLIS) investigation.

contamination exist on the target property, what downgradient sites might be impacted.

environmental professional in forming an opinion about the impact of nearby contaminated properties or, should

of groundwater flow direction in the immediate area. Such hydrogeologic information can be used to assist the

Hydrogeologic information obtained by installation of wells on a specific site can often be an indicator HYDROGEOLOGIC INFORMATION YES - refer to the Overview Map and Detail Map NOT AVAILABLE NATIONAL WETLAND INVENTORY NWI Electronic Data Coverage NWI Quad at Target Property Not Reported Additional Panels in search area:

55097C - FEMA DFIRM Flood data Flood Plain Panel at Target Property:

YES - refer to the Overview Map and Detail Map PORTAGE, WI FEMA FLOOD ZONE FEMA Flood

Electronic Data Target Property County and bodies of water).

Refer to the Physical Setting Source Map following this summary for hydrologic information (major waterways contamination exist on the target property, what downgradient sites might be impacted.

the environmental professional in forming an opinion about the impact of nearby contaminated properties or, should

Surface water can act as a hydrologic barrier to groundwater flow. Such hydrologic information can be used to assist HYDROLOGIC INFORMATIONGEOCHECK - PHYSICAL SETTING SOURCE

SUMMARY

TC3220399.2s Page A-4 Map, USGS Digital Data Series DDS - 11 (1994).

of the Conterminous U.S. at 1:2,500,000 Scale - a digital representation of the 1974 P.B. King and H.M. Beikman

Geologic Age and Rock Stratigraphic Unit Source: P.G. Schruben, R.E. Arndt and W.J. Bawiec, Geology ROCK STRATIGRAPHIC UNIT GEOLOGIC AGE IDENTIFICATION Stratified Sequence Category: Paleozoic Era: Cambrian System: Cambrian Series: C Code: (decoded above as Era, System & Series) at which contaminant migration may be occurring.

Geologic information can be used by the environmental professional in forming an opinion about the relative speed GEOLOGIC INFORMATION IN GENERAL AREA OF TARGET PROPERTY move more quickly through sandy-gravelly types of soils than silty-clayey types of soils.

characteristics data collected on nearby properties and regional soil information. In general, contaminant plumes

to rely on other sources of information, including geologic age identification, rock stratigraphic unit and soil

using site specific geologic and soil strata data. If such data are not reasonably ascertainable, it may be necessary

Groundwater flow velocity information for a particular site is best determined by a qualified environmental professional GROUNDWATER FLOW VELOCITY INFORMATIONGEOCHECK - PHYSICAL SETTING SOURCE

SUMMARY

EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.

1 2 3 0 1/16 1/8 1/4 Miles TC3220399.2s Page A-6 Well drained Soil Drainage Class:

textures.moderately well and well drained soils with moderately coarse

Class B - Moderate infiltration rates. Deep and moderately deep, Hydrologic Group:

sandy loam Soil Surface Texture:

Billett Soil Component Name:

Soil Map ID: 2 Min: 6.1 Max: 7.3 Min: 42 Max: 141 Not reported Not reported sand 59 inches 40 inches 5 Min: 6.1 Max: 7.3 Min: 42 Max: 141 Not reported Not reported loamy sand 40 inches 33 inches 4 Min: 6.1 Max: 7.3 Min: 42 Max: 141 Not reported Not reported sandy loam 33 inches 27 inches 3 Min: 6.1 Max: 7.3 Min: 42 Max: 141 Not reported Not reported loamy sand 27 inches 7 inches 2 Min: 6.1 Max: 7.3 Min: 42 Max: 141 Not reported Not reported loamy sand 7 inches 0 inches 1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity

micro m/secLayerUpperLowerSoil Texture ClassAASHTO GroupUnified Soil Soil Reaction (pH) > 0 inches Depth to Watertable Min:

> 0 inches Depth to Bedrock Min:

Low Corrosion Potential - Uncoated Steel:

Hydric Status: Not hydric Somewhat excessively drained Soil Drainage Class:

excessively drained sands and gravels.

Class A - High infiltration rates. Soils are deep, well drained to Hydrologic Group:

loamy sand Soil Surface Texture:

Richford Soil Component Name:

Soil Map ID: 1 in a landscape. The following information is based on Soil Conservation Service SSURGO data.

for privately owned lands in the United States. A soil map in a soil survey is a representation of soil patterns

Survey (NCSS) and is responsible for collecting, storing, maintaining and distributing soil survey information

The U.S. Department of Agriculture's (USDA) Soil Conservation Service (SCS) leads the National Cooperative Soil DOMINANT SOIL COMPOSITION IN GENERAL AREA OF TARGET PROPERTYGEOCHECK - PHYSICAL SETTING SOURCE

SUMMARY

TC3220399.2s Page A-7 Min: 5.1 Max: 6.5 Min: 42 Max: 141 Not reported Not reported loam 7 inches 0 inches 1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity

micro m/secLayerUpperLowerSoil Texture ClassAASHTO GroupUnified Soil Soil Reaction (pH) > 0 inches Depth to Watertable Min:

> 0 inches Depth to Bedrock Min:

Low Corrosion Potential - Uncoated Steel:

Hydric Status: Not hydric Well drained Soil Drainage Class:

textures.moderately well and well drained soils with moderately coarse

Class B - Moderate infiltration rates. Deep and moderately deep, Hydrologic Group:

loam Soil Surface Texture:

Rosholt Soil Component Name:

Soil Map ID: 3 Min: 5.1 Max: 7.8 Min: 42 Max: 141 Not reported Not reported loamy sand 59 inches 33 inches 4 Min: 5.1 Max: 7.8 Min: 42 Max: 141 Not reported Not reported loamy sand 33 inches 27 inches 3 Min: 5.1 Max: 7.8 Min: 42 Max: 141 Not reported Not reported sandy loam 27 inches 9 inches 2 Min: 5.1 Max: 7.8 Min: 42 Max: 141 Not reported Not reported sandy loam 9 inches 0 inches 1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity

micro m/secLayerUpperLowerSoil Texture ClassAASHTO GroupUnified Soil Soil Reaction (pH) > 0 inches Depth to Watertable Min:

> 0 inches Depth to Bedrock Min:

Low Corrosion Potential - Uncoated Steel:

Hydric Status: Not hydricGEOCHECK - PHYSICAL SETTING SOURCE

SUMMARY

TC3220399.2s Page A-8 1/2 - 1 Mile SSW USGS2429210 16 1/2 - 1 Mile South USGS2429203 15 1/2 - 1 Mile WSW USGS2429044 14 1/2 - 1 Mile South USGS2429204 13 1/2 - 1 Mile NE USGS2429102 12 1/2 - 1 Mile WNW USGS2429076 11 1/2 - 1 Mile West USGS2429070 10 1/2 - 1 Mile West USGS2429067 9 1/2 - 1 Mile SSE USGS2429032 A7 1/2 - 1 Mile SSE USGS2429033 A6 1/2 - 1 Mile SE USGS2429047 5 1/2 - 1 Mile North USGS2429094 4 1/2 - 1 Mile ENE USGS2429073 3 1/2 - 1 Mile West USGS2429066 2 1/4 - 1/2 Mile SSW USGS2429048 1 FEDERAL USGS WELL INFORMATION LOCATION FROM TP WELL ID MAP ID 1.000 State Database Nearest PWS within 1 mile Federal FRDS PWS 1.000 Federal USGS WELL SEARCH DISTANCE INFORMATION SEARCH DISTANCE (miles)

DATABASE opinion about the impact of contaminant migration on nearby drinking water wells.

professional in assessing sources that may impact ground water flow direction, and in forming an

EDR Local/Regional Water Agency records provide water well information to assist the environmental LOCAL / REGIONAL WATER AGENCY RECORDS Min: 5.1 Max: 6.5 Min: 42 Max: 141 Not reported Not reported to gravel stratified sand 59 inches 33 inches 5 Min: 5.1 Max: 6.5 Min: 42 Max: 141 Not reported Not reported sand gravelly loamy 33 inches 27 inches 4 Min: 5.1 Max: 6.5 Min: 42 Max: 141 Not reported Not reported sandy loam

gravelly fine 27 inches 12 inches 3 Min: 5.1 Max: 6.5 Min: 42 Max: 141 Not reported Not reported fine sandy loam 12 inches 7 inches 2 Soil Layer Information Boundary Classification Saturated hydraulic conductivity

micro m/secLayerUpperLowerSoil Texture ClassAASHTO GroupUnified Soil Soil Reaction (pH)GEOCHECK - PHYSICAL SETTING SOURCE

SUMMARY

TC3220399.2s Page A-9 1/2 - 1 Mile WSW WI3000000008386 8 STATE DATABASE WELL INFORMATION LOCATION FROM TP WELL ID MAP ID Note: PWS System location is not always the same as well location.

No PWS System Found FEDERAL FRDS PUBLIC WATER SUPPLY SYSTEM INFORMATION LOCATION FROM TP WELL ID MAP ID 1/2 - 1 Mile SSW USGS2429138 20 1/2 - 1 Mile ENE USGS2429081 B19 1/2 - 1 Mile ENE USGS2429083 B18 1/2 - 1 Mile ENE USGS2429082 B17 FEDERAL USGS WELL INFORMATION LOCATION FROM TP WELL ID MAP IDGEOCHECK - PHYSICAL SETTING SOURCE

SUMMARY

EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.

WI PHYSICAL SETTING SOURCE MAP-3220399.2s N County Boundary N Major Roads N Contour Lines @ Earthquake epicenter, Richter 5 or greater WaterWells Public Water Supply Wells Cluster of Multiple Icons SITE NAME: SHINE Medical Stevens Point, WI ADDRESS: Lands End Way, Stevens Point WI 54482 LAT/LONG:

44.5070/89.4959 0 114 112 + Groundwater Flow Direction

@]) Indeterminate Groundwater Flow at Location @ Groundwater Flow Varies at Location (ij]) Closest Hydrogeological Da1B CLIENT: Golder Associates CONTACT: Kathryn Larson INQUIRY#:

3220399.2s DATE: December 07, 2011 11:47 am c 2011 EDR, Inc. o 2010 Tolo Allu Rei. 0712009.

TC3220399.2s Page A-11 2 West 1/2 - 1 Mile

Lower USGS2429066 FED USGS1964-06-0712.00 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1 1 Ground water data count:

1964-06-07 Ground water data end date:

Ground water data begin date: 1964-06-07 0 Water quality data count:

0000-00-00 Water quality data end date:

0000-00-00 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

80.0 Hole depth:

80.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1110.00 Altitude: 24000 Map scale:

POLONIA Location map:

NESWS01 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.49872787 Dec lon: 44.50135807 Dec lat: 0892955 Longitude:

USGS2429048 EDR Site id:

443005 Latitude: PT-23/08E/01-0511 Site name:

443005089295501 Site no: USGS Agency cd:

1 SSW 1/4 - 1/2 Mile

Lower USGS2429048 FED USGS Map ID Direction Distance Elevation EDR ID Number DatabaseGEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS 1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Monday, August 12, 2013 4:33 PM To: Moser, Michelle; Lynch, Steven

Subject:

SHINE Environmental Audit Response Update Attachments:

DRAFT - Alternatives Request 2 Resp onse - Revision 1 - Part 2.pdfMichelle and Steve, Attached is Part 2 of 2 of the Draft SHINE Response to Alternatives Request #2.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

TC3220399.2s Page A-12 CST Mean greenwich time offset:

19870429 Date inventoried:

19850618 Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Not Reported Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1120 Altitude: 24000 Map scale:

POLONIA Location map:

NWNWS06 T23N R09E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.48650552 Dec lon: 44.51052505 Dec lat: 0892911 Longitude:

USGS2429073 EDR Site id:

443038 Latitude: PT-23/09E/06-1157 Site name:

443038089291101 Site no: USGS Agency cd:

3 ENE 1/2 - 1 Mile

Higher USGS2429073 FED USGS Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

Not Reported Hole depth:

Not Reported Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

Not Reported Altitude datum:

Not Reported Altitude accuracy:

Not Reported Altitude method:

Not Reported Altitude: Not Reported Map scale:

Not Reported Location map:

Not Reported Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

M Coor accr:

M Coor meth:

-89.50622809 Dec lon: 44.50746908 Dec lat: 0893022 Longitude:

USGS2429066 EDR Site id:

443027 Latitude: PERM 24126 Site name:

443027089302201 Site no: WI001 Agency cd:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-13 Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

Not Reported Hole depth:

Not Reported Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

Not Reported Altitude datum:

Not Reported Altitude accuracy:

Not Reported Altitude method:

Not Reported Altitude: Not Reported Map scale:

Not Reported Location map:

Not Reported Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

M Coor accr:

M Coor meth:

-89.49733911 Dec lon: 44.51469148 Dec lat: 0892950 Longitude:

USGS2429094 EDR Site id:

443053 Latitude: PERM 24279 Site name:

443053089295001 Site no: WI001 Agency cd:

4 North 1/2 - 1 Mile

Higher USGS2429094 FED USGS1985-06-186.0 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1 1 Ground water data count:

1985-06-18 Ground water data end date:

Ground water data begin date: 1985-06-18 0 Water quality data count:

0000-00-00 Water quality data end date:

0000-00-00 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

other government (other than USGS)

Source of depth data:

71.0 Hole depth:

71.0 Well depth:

SAND AND GRAVEL AQUIFER Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-14 A6 SSE 1/2 - 1 Mile

Higher USGS2429033 FED USGS1963-04-0121.00 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1 1 Ground water data count:

1963-04-01 Ground water data end date:

Ground water data begin date: 1963-04-01 0 Water quality data count:

0000-00-00 Water quality data end date:

0000-00-00 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

116 Hole depth:

116 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1130.00 Altitude: 24000 Map scale:

POLONIA Location map:

S06 T023N R009E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

T Coor accr:

M Coor meth:

-89.48733876 Dec lon: 44.50108056 Dec lat: 0892914 Longitude:

USGS2429047 EDR Site id:

443004 Latitude: PT-23/09E/06-0486 Site name:

443004089291401 Site no: USGS Agency cd:

5 SE 1/2 - 1 Mile

Higher USGS2429047 FED USGS Map ID Direction Distance Elevation EDR ID Number DatabaseGEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-15 CST Mean greenwich time offset:

Not Reported Date inventoried:

19591113 Date construction:

Ground-water other than Spring Site type:

Flat surface Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

.1 Altitude accuracy:

Level or other surveying method Altitude method:

1115.32 Altitude: 24000 Map scale:

ARNOTT Location map:

NENENES12 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.48928325 Dec lon: 44.49830276 Dec lat: 0892921 Longitude:

USGS2429032 EDR Site id:

442954 Latitude: PT-23/08E/12-0361 Site name:

442954089292101 Site no: USGS Agency cd:

A7 SSE 1/2 - 1 Mile

Higher USGS2429032 FED USGS1959-10-1613.83 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1 1 Ground water data count:

1959-10-16 Ground water data end date:

Ground water data begin date: 1959-10-16 2 Water quality data count:

1974-07-12 Water quality data end date:

1965-06-10 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

driller Source of depth data:

92.0 Hole depth:

87.4 Well depth:

QUATERNARY Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

19591016 Date construction:

Ground-water other than Spring Site type:

Flat surface Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1113.00 Altitude: 24000 Map scale:

ARNOTT Location map:

NENENES12 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.48928325 Dec lon: 44.49830276 Dec lat: 0892921 Longitude:

USGS2429033 EDR Site id:

442954 Latitude: PT-23/08E/12-0360 Site name:

442954089292102 Site no: USGS Agency cd:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-16 Not Reported Block no: Not Reported Lot no: Not Reported Subdivisio:

Not Reported Well stree:

Not Reported Fire: STEVENS POINT Municipal1:

C Municipal:

0490 Construc 6:

54467 Construc 5:

WI Construc 4:

PLOVER Construc 3:

PO BOX 490 Construc 2:

3262 Construc 1:

ROBERTS IRRIGATION CO INC Constructo:

01/03/2008 Dnr rece 2:

01/03/2008 Dnr rece 1:

10/18/2007 Dnr receiv:

06/21/2007 Complete d:

Not Reported Owner ph 1:

Not Reported Owner phon:

Not Reported Owner are:

Not Reported Owner zip2:

54481 Owner zip1:

WI Owner stat:

STEVENS POINT Owner city:

3217 JOHN JOANIS DR Owner mail:

ADVENTURE 2120 Owner name:

Not Reported Tax parcel:

6 District c:

5.0E+001 County cod:

Not Reported County wel:

TY626 Wi unique:

8 WSW 1/2 - 1 Mile

Lower WI3000000008386 WI WELLS1959-11-139.00 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1 1 Ground water data count:

1959-11-13 Ground water data end date:

Ground water data begin date: 1959-11-13 1 Water quality data count:

1965-06-10 Water quality data end date:

1965-06-10 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

driller Source of depth data:

31.3 Hole depth:

31.3 Well depth:

QUATERNARY Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-17 Not Reported Animal yar:

0 Pav anim 1:

Not Reported Pav animal:

0 Wastewtr a:

Not Reported Wastewtr s:

0 Clewtr amt:

Not Reported Clewtr sum:

0 Coll sew 1:

Not Reported Coll sewer:

Not Reported Build se 3:

Not Reported Build se 2:

0 Build se 1:

Not Reported Build sewe:

Not Reported Build dr 2:

0 Build dr 1:

Not Reported Build drai:

0 Found dr 1:

Not Reported Found drai:

0 Found cl 1:

Not Reported Found clwt:

0 Privy amt:

Not Reported Privy code:

0 Dwnspot 1:

Not Reported Dwnspot hy:

0 Shorline p:

Not Reported Shoreline:

0 Buried p 1:

Not Reported Buried pet:

0 Buried o 1:

Not Reported Buried oil:

0 Nonconfo 1:

Not Reported Nonconform:

0 Sew abso 1:

Not Reported Sew absorb:

0 Septic t 1:

Not Reported Septic tan:

1.4E+001 Build oh a:

Not Reported Build over:

0 Landfill a:

Not Reported Landfill q:

N Flood plai:

Not Reported Highest po:

N Hicap prop:

N Hicap well:

IRRIGATION Facility t:

Not Reported Service co:

X Well categ:

Not Reported Other expl:

1 Well type:

Not Reported New well i:

Not Reported Prev well:

Not Reported Replace re:

Not Reported Orig year:

1 Well statu:

E E w: 8.0E+000 Range no: 2.3E+001 Township n:

2.0E+000 Section: NE Quar: SE Quar quar:

Not Reported Govt lot:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-18 B Static w 1:

2.7E+001 Static wtr:

Not Reported Depth: S Sacks ya 1:

Not Reported Seal num 1:

5.3E+001 Seal to 1:

3.1E+001 Seal from1:

1. 20 RED FLINT Seal kind1:

S Sacks yard:

Not Reported Seal numbe:

3.1E+001 Seal to am:

0 Seal from:

DRILL CUTTINGS Seal kind:

Not Reported Seal metho:

5.3E+001 Screen to:

4.3E+001 Screen fro:

JOHNSON #20 GALV Screen Type:

6.0E+000 Screen dia:

0 Cls to a 3:

0 Cls to a 2:

0 Cls to a 1:

4.3E+001 Cls to amt:

0 Cls from 3:

0 Cls from 2:

0 Cls from 1:

0 Cls from a:

Not Reported Cls desc 3:

Not Reported Cls desc 2:

Not Reported Cls desc 1:

A53 BLACK NORTHWEST PIPE .280 WELDED Cls desc t:

0 Cls dia 3:

0 Cls dia 2:

0 Cls dia 1:

6.0E+000 Cls dia am:

Not Reported Other ex 1:

Not Reported Other dril:

Not Reported Remove exp:

Not Reported Temp otr r:

0 Dia temp a:

Not Reported Tem otr ca:

0 Cable bit1:

Not Reported Cable bit:

Not Reported Rev rot co:

Not Reported Rot foam c:

Not Reported Rot air co:

X Rot mud co:

0 Dr4 to amt:

0 Dr4 from a:

0 Dr4 dia am:

0 Dr3 to amt:

0 Dr3 from a:

0 Dr3 dia am:

0 Dr2 to amt:

0 Dr2 from a:

0 Dr2 dia am:

5.3E+001 Dr1 to amt:

0 Dr1 from a:

9.0E+000 Dr1 dia am:

Not Reported Nr112 text:

0 Nr 112 a 1:

Not Reported Nr 112 amt:

Not Reported Manure s 2:

0 Manure s 1:

Not Reported Manure sto:

Not Reported Manure t 1:

Not Reported Manure typ:

0 Manure p 1:

Not Reported Manure pip:

0 Barn gut 1:

Not Reported Barn gutte:

Not Reported Silo type:

0 Silo amt: Not Reported Silo: 0 Animal y 1:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-19 9 West 1/2 - 1 Mile

Lower USGS2429067 FED USGS WI3000000008386 Site id: Not Reported Empty gy: 26915464 Notificati:

WELL CONSTRUCTION Record sou:

1117 Batch: 4 Spec capac:

09/07/2006 Approval d:

Not Reported Approval n:

Not Reported Fid 1: Not Reported Common wel:

Not Reported Hicap no: 0 Collet sew:

Not Reported Collect se:

Not Reported Varince is:

Not Reported Temp outer:

Not Reported Lower cabl:

Not Reported Lower ro 2:

Not Reported Lower ro 1:

Not Reported Lower rota:

Not Reported Drill casi:

GPS008 Lat long m:

30.555 Long minut:

89 Long degre:

30.192 Lat minute:

44 Lat degree:

PORTAGE County tex:

5.3E+001 Bottom: 05/22/2008 File creat:

Not Reported Shoreline1:

Not Reported Septic typ:

0 Ditch amt:

Y Label sent:

Not Reported Comment fl:

10/15/2007 Ro sign da:

PR Rig op ini:

10/15/2007 Wc sign da:

JP Well cont:

Not Reported Proper s 1:

Not Reported Proper sea:

Y Well cappe:

Y Well disin:

Y Well dev c:

A Well abvbe:

1.3E+001 Well depth:

1.0E+000 Pump hrs t:

M Pump by co:

3.0E+001 Pump gals:

3.4E+001 Pump wtr b:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-20 CST Mean greenwich time offset:

19870422 Date inventoried:

19830603 Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Not Reported Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1112 Altitude: 24000 Map scale:

STEVENS POINT Location map:

NENWS01 T23N R08E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.51122822 Dec lon: 44.50913568 Dec lat: 0893040 Longitude:

USGS2429070 EDR Site id:

443033 Latitude: PT-23/08E/01-1125 Site name:

443033089304001 Site no: USGS Agency cd:

10 West 1/2 - 1 Mile

Lower USGS2429070 FED USGS Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

78.0 Hole depth:

78.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

10 Altitude accuracy:

Interpolated from topographic map Altitude method:

1105.00 Altitude: 24000 Map scale:

STEVENS POINT Location map:

NWSENES02 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.51095042 Dec lon: 44.50746901 Dec lat: 0893039 Longitude:

USGS2429067 EDR Site id:

443027 Latitude: PT-23/08E/02-0895 Site name:

443027089303901 Site no: USGS Agency cd:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-21 1 Ground water data count:

1975-05-05 Ground water data end date:

Ground water data begin date: 1975-05-05 0 Water quality data count:

0000-00-00 Water quality data end date:

0000-00-00 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

45.0 Hole depth:

45.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1106.00 Altitude: 24000 Map scale:

STEVENS POINT Location map:

NENES02 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.51095046 Dec lon: 44.51108014 Dec lat: 0893039 Longitude:

USGS2429076 EDR Site id:

443040 Latitude: PT-23/08E/02-0875 Site name:

443040089303901 Site no: USGS Agency cd:

11 WNW 1/2 - 1 Mile

Lower USGS2429076 FED USGS1983-06-037.0 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1 1 Ground water data count:

1983-06-03 Ground water data end date:

Ground water data begin date: 1983-06-03 0 Water quality data count:

0000-00-00 Water quality data end date:

0000-00-00 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

other government (other than USGS)

Source of depth data:

54.0 Hole depth:

54.0 Well depth:

SAND AND GRAVEL AQUIFER Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-22 13 South 1/2 - 1 Mile

Lower USGS2429204 FED USGS Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

other government (other than USGS)

Source of depth data:

76 Hole depth:

76 Well depth:

SAND AND GRAVEL AQUIFER Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

19870203 Date inventoried:

19820512 Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Not Reported Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1117 Altitude: 24000 Map scale:

POLONIA Location map:

NWSWS31 T024N R009E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

T Coor accr:

M Coor meth:

-89.48678338 Dec lon: 44.51663617 Dec lat: 0892912 Longitude:

USGS2429102 EDR Site id:

443100 Latitude: PT-24/09E/31-1076 Site name:

443100089291201 Site no: USGS Agency cd:

12 NE 1/2 - 1 Mile

Higher USGS2429102 FED USGS1975-05-0523.00 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-23 CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

2.5 Altitude

accuracy:

Interpolated from topographic map Altitude method:

1100.00 Altitude: 24000 Map scale:

WHITING Location map:

SESES02 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.51122811 Dec lon: 44.49996898 Dec lat: 0893040 Longitude:

USGS2429044 EDR Site id:

443000 Latitude: PT-23/08E/02-0593 Site name:

443000089304001 Site no: USGS Agency cd:

14 WSW 1/2 - 1 Mile

Lower USGS2429044 FED USGS Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

78.0 Hole depth:

78.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1110.00 Altitude: 24000 Map scale:

ARNOTT Location map:

NES12 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.49345004 Dec lon: 44.49413604 Dec lat: 0892936 Longitude:

USGS2429204 EDR Site id:

442939 Latitude: PT-23/08E/12-1054 Site name:

442939089293601 Site no: USGS Agency cd:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-24 4 Ground water data count:

1953-10-14 Ground water data end date:

Ground water data begin date: 1950-07-20 0 Water quality data count:

0000-00-00 Water quality data end date:

0000-00-00 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

30.0 Hole depth:

29.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1100.00 Altitude: 24000 Map scale:

ARNOTT Location map:

SWNES12 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

S Coor accr:

M Coor meth:

-89.49706122 Dec lon: 44.49385818 Dec lat: 0892949 Longitude:

USGS2429203 EDR Site id:

442938 Latitude: PT-23/08E/12-0002 Site name:

442938089294901 Site no: USGS Agency cd:

15 South 1/2 - 1 Mile

Lower USGS2429203 FED USGS1967-05-0421.00 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 1 1 Ground water data count:

1967-05-04 Ground water data end date:

Ground water data begin date: 1967-05-04 0 Water quality data count:

0000-00-00 Water quality data end date:

0000-00-00 Water quality data begin date:

0 Peak flow data count:

0000-00-00 Peak flow data end date:

0000-00-00 Peak flow data begin date:

0 Daily flow data count:

0000-00-00 Daily flow data end date:

0000-00-00 Daily flow data begin date:

0 Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

86.0 Hole depth:

86.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-25 B17 ENE 1/2 - 1 Mile

Higher USGS2429082 FED USGS Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

90.0 Hole depth:

90.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1105.00 Altitude: 24000 Map scale:

WHITING Location map:

NWNWS12 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

S Coor accr:

M Coor meth:

-89.50567249 Dec lon: 44.49580245 Dec lat: 0893020 Longitude:

USGS2429210 EDR Site id:

442945 Latitude: PT-23/08E/12-0894 Site name:

442945089302001 Site no: USGS Agency cd:

16 SSW 1/2 - 1 Mile

Lower USGS2429210 FED USGS1950-10-1710.421950-07-2010.031953-10-149.201950-11-2510.91 Date Feet below Surface Feet to Sealevel-------------------------------------------------

Date Feet below

Surface Feet to Sealevel-------------------------------------------------

Ground-water levels, Number of Measurements: 4GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-26 CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

Not Reported Altitude datum:

Not Reported Altitude accuracy:

Not Reported Altitude method:

Not Reported Altitude: Not Reported Map scale:

Not Reported Location map:

Not Reported Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

M Coor accr:

M Coor meth:

-89.47817205 Dec lon: 44.51191414 Dec lat: 0892841 Longitude:

USGS2429083 EDR Site id:

443043 Latitude: PERM 24110 Site name:

443043089284103 Site no: WI001 Agency cd:

B18 ENE 1/2 - 1 Mile

Higher USGS2429083 FED USGS Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

Not Reported Hole depth:

Not Reported Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

Not Reported Altitude datum:

Not Reported Altitude accuracy:

Not Reported Altitude method:

Not Reported Altitude: Not Reported Map scale:

Not Reported Location map:

Not Reported Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

M Coor accr:

M Coor meth:

-89.47817205 Dec lon: 44.51191414 Dec lat: 0892841 Longitude:

USGS2429082 EDR Site id:

443043 Latitude: PERM 23908 Site name:

443043089284102 Site no: WI001 Agency cd:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-27 Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

96.0 Hole depth:

96.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1132.00 Altitude: 24000 Map scale:

POLONIA Location map:

SESWS31 T024N R009E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

F Coor accr:

M Coor meth:

-89.47817205 Dec lon: 44.51191414 Dec lat: 0892841 Longitude:

USGS2429081 EDR Site id:

443043 Latitude: PT-24/09E/31-0828 Site name:

443043089284101 Site no: USGS Agency cd:

B19 ENE 1/2 - 1 Mile

Higher USGS2429081 FED USGS Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

Not Reported Source of depth data:

Not Reported Hole depth:

Not Reported Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-28 Ground-water levels, Number of Measurements: 0 Not Reported Ground water data count:

Not Reported Ground water data end date:

Ground water data begin date: Not Reported Not Reported Water quality data count:

Not Reported Water quality data end date:

Not Reported Water quality data begin date:

Not Reported Peak flow data count:

Not Reported Peak flow data end date:

Not Reported Peak flow data begin date:

Not Reported Daily flow data count:

Not Reported Daily flow data end date:

Not Reported Daily flow data begin date:

Not Reported Real time data flag:

Not Reported Project number:

driller Source of depth data:

80.0 Hole depth:

80.0 Well depth:

Not Reported Aquifer: Not Reported Aquifer Type:

Single well, other than collector or Ranney type Type of ground water site:

Y Local standard time flag:

CST Mean greenwich time offset:

Not Reported Date inventoried:

Not Reported Date construction:

Ground-water other than Spring Site type:

Not Reported Topographic:

Castle Rock. Wisconsin. Area = 3250 sq.mi.

Hydrologic:

National Geodetic Vertical Datum of 1929 Altitude datum:

5 Altitude accuracy:

Interpolated from topographic map Altitude method:

1110.00 Altitude: 24000 Map scale:

WHITING Location map:

NWSENWS12 T023N R008E 4 Land net: US Country: 097 County: 55 State: 55 District: NAD83 Dec latlong datum:

NAD27 Latlong datum:

S Coor accr:

M Coor meth:

-89.50372802 Dec lon: 44.49385806 Dec lat: 0893013 Longitude:

USGS2429138 EDR Site id:

442938 Latitude: PT-23/08E/12-0512 Site name:

442838089301301 Site no: USGS Agency cd:

20 SSW 1/2 - 1 Mile

Lower USGS2429138 FED USGS Map ID Direction Distance Elevation EDR ID Number DatabaseGEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS TC3220399.2s Page A-29 0%33%67%4.258 pCi/L Basement Not Reported Not Reported Not Reported Not Reported Living Area - 2nd Floor 0%0%100%1.150 pCi/L Living Area - 1st Floor

% >20 pCi/L

% 4-20 pCi/L

% <4 pCi/L Average Activity Area Number of sites tested: 24

Federal Area Radon Information for PORTAGE COUNTY, WI

Zone 3 indoor average level < 2 pCi/L.

Zone 2 indoor average level >= 2 pCi/L and <= 4 pCi/L.

Note: Zone 1 indoor average level > 4 pCi/L.

Federal EPA Radon Zone for PORTAGE County: 1 AREA RADON INFORMATIONGEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS RADON TOPOGRAPHIC INFORMATION USGS 7.5' Digital Elevation Model (DEM)

Source: United States Geologic Survey EDR acquired the USGS 7.5' Digital Elevation Model in 2002 and updated it in 2006. The 7.5 minute DEM corresponds

to the USGS 1:24,000- and 1:25,000-scale topographic quadrangle maps. The DEM provides elevation data

with consistent elevation units and projection.

Scanned Digital USGS 7.5' Topographic Map (DRG)

Source: United States Geologic Survey

A digital raster graphic (DRG) is a scanned image of a U.S. Geological Survey topographic map. The map images

are made by scanning published paper maps on high-resolution scanners. The raster image

is georeferenced and fit to the Universal Transverse Mercator (UTM) projection.

HYDROLOGIC INFORMATIONFlood Zone Data:This data, available in select counties across the country, was obtained by EDR in 2003 & 2011 from the Federal

Emergency Management Agency (FEMA). Data depicts 100-year and 500-year flood zones as defined by FEMA.NWI:National Wetlands Inventory. This data, available in select counties across the country, was obtained by EDR in 2002 and 2005 from the U.S. Fish and Wildlife Service.

HYDROGEOLOGIC INFORMATION AQUIFLOW Information System R Source: EDR proprietary database of groundwater flow information EDR has developed the AQUIFLOW Information System (AIS) to provide data on the general direction of groundwater flow at specific points. EDR has reviewed reports submitted to regulatory authorities at select sites and has

extracted the date of the report, hydrogeologically determined groundwater flow direction and depth to water table

information.

GEOLOGIC INFORMATION Geologic Age and Rock Stratigraphic Unit Source: P.G. Schruben, R.E. Arndt and W.J. Bawiec, Geology of the Conterminous U.S. at 1:2,500,000 Scale - A digital

representation of the 1974 P.B. King and H.M. Beikman Map, USGS Digital Data Series DDS - 11 (1994).STATSGO:State Soil Geographic Database Source: Department of Agriculture, Natural Resources Conservation Services

The U.S. Department of Agriculture's (USDA) Natural Resources Conservation Service (NRCS) leads the national

Conservation Soil Survey (NCSS) and is responsible for collecting, storing, maintaining and distributing soil

survey information for privately owned lands in the United States. A soil map in a soil survey is a representation

of soil patterns in a landscape. Soil maps for STATSGO are compiled by generalizing more detailed (SSURGO)

soil survey maps.

SSURGO: Soil Survey Geographic Database Source: Department of Agriculture, Natural Resources Conservation Services (NRCS)

Telephone: 800-672-5559

SSURGO is the most detailed level of mapping done by the Natural Resources Conservation Services, mapping

scales generally range from 1:12,000 to 1:63,360. Field mapping methods using national standards are used to

construct the soil maps in the Soil Survey Geographic (SSURGO) database. SSURGO digitizing duplicates the

original soil survey maps. This level of mapping is designed for use by landowners, townships and county

natural resource planning and management.

TC3220399.2s Page A-30 PHYSICAL SETTING SOURCE RECORDS SEARCHED LOCAL / REGIONAL WATER AGENCY RECORDS FEDERAL WATER WELLSPWS:Public Water Systems Source: EPA/Office of Drinking Water Telephone: 202-564-3750

Public Water System data from the Federal Reporting Data System. A PWS is any water system which provides water to at least 25 people for at least 60 days annually. PWSs provide water from wells, rivers and other sources.PWS ENF:Public Water Systems Violation and Enforcement Data Source: EPA/Office of Drinking Water

Telephone: 202-564-3750

Violation and Enforcement data for Public Water Systems from the Safe Drinking Water Information System (SDWIS) after August 1995. Prior to August 1995, the data came from the Federal Reporting Data System (FRDS).USGS Water Wells: USGS National Water Inventory System (NWIS)

This database contains descriptive information on sites where the USGS collects or has collected data on surface

water and/or groundwater. The groundwater data includes information on wells, springs, and other sources of groundwater.

STATE RECORDS

Wisconsin Well Construction Report File Source: Department of Natural Resources Telephone: 608-266-0153

In the past, not all latitude/longitudes were accurate. Many were protracted from centroid (center of the quarter sections given in PLSS). The ones that were not accurate were removed from the well database.

OTHER STATE DATABASE INFORMATION RADON State Database: WI Radon Source: Department of Health & Family Services Telephone: 608-266-1865

Wisconsin Measurement Summary Area Radon Information Source: USGS

Telephone: 703-356-4020

The National Radon Database has been developed by the U.S. Environmental Protection Agency (USEPA) and is a compilation of the EPA/State Residential Radon Survey and the National Residential Radon Survey.

The study covers the years 1986 - 1992. Where necessary data has been supplemented by information collected at

private sources such as universities and research institutions.

EPA Radon Zones Source: EPA

Telephone: 703-356-4020

Sections 307 & 309 of IRAA directed EPA to list and identify areas of U.S. with the potential for elevated indoor

radon levels.

OTHERAirport Landing Facilities:Private and public use landing facilities Source: Federal Aviation Administration, 800-457-6656Epicenters:World earthquake epicenters, Richter 5 or greater Source: Department of Commerce, National Oceanic and Atmospheric Administration TC3220399.2s Page A-31 PHYSICAL SETTING SOURCE RECORDS SEARCHED STREET AND ADDRESS INFORMATION

© 2010 Tele Atlas North America, Inc. All rights reserved. This material is proprietary and the subject of copyright protectio n and other intellectual property rights owned by or licensed to Tele Atlas North America, Inc. The use of this material is subj ect to the terms of a license agreement. You will be held liable for any unauthorized copying or disclosure of this material.

TC3220399.2s Page A-32 PHYSICAL SETTING SOURCE RECORDS SEARCHED Appendix C Historical Documentation

SHINE Medical Stevens Point, WI Lands End Way, Stevens Point, WI 54482 Inquiry Number: 3220399.3 December 07, 2011 Certified Sanborn Map Report 12/07/11 Site Name:

SHINE Medical Stevens Point, Lands End Way, Stevens Point, WI 54482 Client Name:

Golder Associates 1751 West County Rd B

Roseville, MN 55113EDR Inquiry #3220399.3Contact:Kathryn LarsonThe complete Sanborn Library collection has been searched by EDR, and fire insurance maps covering the targetproperty location provided by Golder Associates were identified for the years listed below. The certified Sanborn Library search results in this report can be authenticated by visiting www.edrnet.com/sanborn and entering the certification number. Only Environmental Data Resources Inc. (EDR) is authorized to grant rights for commercial reproduction of

maps by Sanborn Library LLC, the copyright holder for the collection.

Certified Sanborn Results:

Site Name:

SHINE Medical Stevens Point, WI Address: Lands End Way, City, State, Zip:

Stevens Point, WI 54482 Cross Street:

P.O. #113-81093 Project: 113-81093 Certification #

CC0B-4397-AE8B Library of Congress University Publications of America EDR Private Collection The Sanborn Library LLC Since 1866ŽThe Sanborn Library includes more than 1.2 millionSanborn fire insurance maps, which track historical property usage in approximately 12,000 American

cities and towns. Collections searched:

Sanborn Library search results Certification # CC0B-4397-AE8B UNMAPPED PROPERTYThis report certifies that the complete holdings of the SanbornLibrary, LLC collection have been searched based on client supplied target property information, and fire insurance maps

covering the target property were not found.

Limited Permission To Make CopiesGolder Associates (the client) is permitted to make up to THREE photocopies of this Sanborn Map transmittal and each fire insurance mapaccompanying this report solely for the limited use of its customer. No one other than the client is authorized to make copies. Upon request made directly to an EDR Account Executive, the client may be permitted to make a limited number of additional photocopies. This permission is

conditioned upon compliance by the client, its customer and their agents with EDR's copyright policy; a copy of which is available upon request.

Disclaimer - Copyright and Trademark noticeThis Report contains certain information obtained from a variety of public and other sources reasonably available to Environmental Data Resources, Inc. It cannot beconcluded from this Report that coverage information for the target and surrounding properties does not exist from other sources. NO WARRANTY EXPRESSED OR IMPLIED, IS MADE WHATSOEVER IN CONNECTION WITH THIS REPORT. ENVIRONMENTAL DATA RESOURCES, INC. SPECIFICALLY DISCLAIMS THE MAKING OF ANY SUCH WARRANTIES, INCLUDING WITHOUT LIMITATION, MERCHANTABILITY OR FITNESS FOR A PARTICULAR USE OR PURPOSE. ALL RISK IS ASSUMED BY THE USER. IN NO EVENT SHALL ENVIRONMENTAL DATA RESOURCES, INC. BE LIABLE TO ANYONE, WHETHER ARISING OUT OF ERRORS OR OMISSIONS, NEGLIGENCE, ACCIDENT OR ANY OTHER CAUSE, FOR ANY LOSS OF DAMAGE, INCLUDING, WITHOUT LIMITATION, SPECIAL, INCIDENTAL CONSEQUENTIAL, OR EXEMPLARY DAMAGES. ANY LIABILITY ON THE PART OF ENVIRONMENTAL DATA RESOURCES, INC. IS STRICTLY LIMITED TO A REFUND OF THE AMOUNT PAID FOR THIS REPORT. Purchaser accepts this Report "AS IS". Any analyses, estimates, ratings, environmental risk levels or risk codes provided in this Report are provided for illustrative purposes only, and are not intended to provide, nor should they be interpreted as providing any facts regarding, or prediction or forecast of, any environmental risk for any property. Only a Phase I Environmental Site Assessment performed by an environmental professional can provide information regarding the environmental risk for any property. Additionally, the information provided in this Report is not to be

construed as legal advice.Copyright 2011 by Environmental Data Resources, Inc. All rights reserved. Reproduction in any media or format, in whole or in part, of any report or map of Environmental Data Resources, Inc., or its affiliates, is prohibited without prior written permission.EDR and its logos (including Sanborn and Sanborn Map) are trademarks of Environmental Data Resources, Inc. or its affiliates. All other trademarks used herein are the property of their respective owners.

3220399 - 3 page 2

SHINE Medical Stevens Point, WI Lands End Way, Stevens Point, WI 54482 Inquiry Number: 3220399.4 December 07, 2011 EDR Historical Topographic Map Report Environmental Data Resources, Inc.s (EDR) Historical Topographic Map Report is designed to assist professionals in evaluating potential liability on a target property resulting from past activities. EDRs Historical Topographic Map Report

includes a search of a collection of public and private color historical topographic maps, dating back to the early 1900s.

Thank you for your business.

Please contact EDR at 1-800-352-0050 with any questions or comments.

Disclaimer - Copyright and Trademark Notice This Report contains certain information obtained from a variety of public and other sources reasonably available to Environmental Data Resources, Inc.

It cannot be concluded from this Report that coverage information for the target and surrounding properties does not exist from other sources.

NO WARRANTY EXPRESSED OR IMPLIED, IS MADE WHATSOEVER IN CONNECTION WITH THIS REPORT. ENVIRONMENTAL DATA

RESOURCES, INC. SPECIFICALLY DISCLAIMS THE MAKING OF ANY SUCH WARRANTIES, INCLUDING WITHOUT LIMITATION, MERCHANTABILITY OR FITNESS FOR A PARTICULAR USE OR PURPOSE. ALL RISK IS ASSUMED BY THE USER. IN NO EVENT SHALL

ENVIRONMENTAL DATA RESOURCES, INC. BE LIABLE TO ANYONE, WHETHER ARISING OUT OF ERRORS OR OMISSIONS, NEGLIGENCE, ACCIDENT OR ANY OTHER CAUSE, FOR ANY LOSS OF DAMAGE, INCLUDING, WITHOUT LIMITATION, SPECIAL, INCIDENTAL, CONSEQUENTIAL, OR EXEMPLARY DAMAGES. ANY LIABILITY ON THE PART OF ENVIRONMENTAL DATA RESOURCES, INC. IS STRICTLY

LIMITED TO A REFUND OF THE AMOUNT PAID FOR THIS REPORT.

Purchaser accepts this Report AS IS. Any analyses, estimates, ratings, environmental risk levels or risk codes provided in this Report are provided for illustrative purposes only, and are not intended to provide, nor should they

be interpreted as providing any facts regarding, or prediction or forecast of, any environmental risk for any property. Only a Phase I Environmental Site

Assessment performed by an environmental professional can provide information regarding the environmental risk for any property. Additionally, the

information provided in this Report is not to be construed as legal advice.

Copyright 2011 by Environmental Data Resources, Inc. All rights reserved. Reproduction in any media or format, in whole or in part, of any report or map of Environmental Data Resources, Inc., or its affiliates, is prohibited without prior written permission.

EDR and its logos (including Sanborn and Sanborn Map) are trademarks of Environmental Data Resources, Inc. or its affiliates. All other trademarks used herein are the property of their respective owners.

Historical Topographic Map N TARGET QUAD

TARGET QUADNAME:ROSHOLT MAP YEAR:1955SERIES:15SCALE:1:48000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 I I II* II' II II I

-. -1m*-. Stockto n Sc h & (A b andonod) II. IF e--ll II I 31 Stockton 1 -*--0 ---=---I ---*--*----*-6 0 17 20 ,:.;! Heffron ..

• Sch 29 * -* ----*-0 5 AR N OT 2.9 M I.

Historical Topographic Map N TARGET QUAD

TARGET QUADNAME:POLONIA MAP YEAR:1969SERIES:7.5SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 I ('" ['.,.....,*..-..., . .........., I \

• 0 I 115.f. .,./) ( I !I \. ./ -;.._,_ <";,\'Gravel Pit Historical Topographic Map N TARGET QUAD

TARGET QUADNAME:POLONIA MAP YEAR:1986 PHOTOINSPECTED:1969 SERIES:7.5 SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 4 I I " 0 " 1/ --!..-I I I I I 1 \,_J_---.-.-1 -.

• 1 ,1110 1 I p (G 0 V E R I I I

• II II ,, I ll II II II II II II =( II?{) -\ . -) J a .. 0 t ' ( I Pit I ......... { \ ( 31; sao r I II " II 111/JO ..., Stockton -'"' 0 ' Grave l Pot / We I ,, ,,o1 R. 8 [ R 9 E Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:AMHERST MAP YEAR:1957SERIES:15SCALE:1:48000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 ,

• 30' R. B E 3Q2000m.[. 1 Cem 18 s Arnott Sc h ELLIS 5.Z M l '*" "* r o us 10 0 5 T 0 .Cern 1 6 c K T 0 . 15 N Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:WHITING MAP YEAR:1957SERIES:15SCALE:1:48000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 p L 0 1 E R 1 32 I I " d II I I II I I -6 II II II II II II II +s:: II II " II

• 4 3 Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:ARNOTT MAP YEAR:1969SERIES:7.5SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 N. I o I jt l I I I I I l{ __ .c_ + I r I I RaE R9E 1 1112 -..... I I I , I I I I -1105 3Q300<lm E. 3 Q6 .. c._ Cern

• I

c. ..,_ -/117 0 ..

Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:STEVENS POINT MAP YEAR:1970SERIES:7.5SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:WHITING MAP YEAR:1970SERIES:7.5SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 n Q:) "' ,ocP 1 1 j 1 5 2 F 4 9 I -"::). l f.:* C"\. I \1 Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:WHITING MAP YEAR:1976 PHOTOINSPECTED:1970 SERIES:7.5 SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011I l J Well ( DRIV E 1 0931 W el l 1 24 Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:STEVENS POINT MAP YEAR:1978 PHOTOREVISED:1970 SERIES:7.5 SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:STEVENS POINT MAP YEAR:1980 PHOTOINSPECTED:1970 SERIES:7.5 SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011

.... ,* I 1105 1103 r Historical Topographic Map N ADJOINING QUAD

ADJOINING QUADNAME:STEVENS POINT MAP YEAR:1991 REVISED:1970 SERIES:7.5 SCALE:1:24000SITE NAME:SHINE Medical Stevens Point, WI ADDRESS:Lands End Way, Stevens Point, WI 54482LAT/LONG:44.507 / -89.4959CLIENT:Golder Associates CONTACT:Kathryn Larson INQUIRY#:3220399.4 RESEARCH DATE:12/07/2011 Summary of Historical Research Site Location Conducted For HIG Project Number:

Completion Date:

Well Information:

Well Records and/or Location Maps are provided for wells that may be located on or near the site. This well information was obtained from the following source(s):

City Directories:

HIG researched City Directory coverage for the site, with the following results:

Aerial Photography:

Aerial Photographs from the years listed below are provided for the site location. The year and scale of each photograph is provided on the photograph title block.

Property Records Review:

HIG researched information pertaining to the site at local government offices. A summary of this research and the corresponding documents are included in the attached Summary of Local Government Records.

USGS Topographic Maps:

Additional Maps:

Historical Information Gatherers, Inc. (HIG) researches and obtains data from numerous sources and publishers. This Summary of Historical Research presents a summary of the services requested and a list of the data provided by HIG for the above referenced site. When a particular product or service was requested but not available, the research conducted by HIG is summarized below.

Please see page 2 for HIG's Disclaimer & Waiver of Liability and Copyright Notices.

Services Requested:

ph. 952-253-2004 l fax 952-253-2005 l email: orders@historicalinfo.com www.historicalinfo.com FIM+ : HIG researched available Fire Insurance and similar maps. See attached report for complete details.

Regulatory Database Report:

GeoSearch has prepared a Radius Report for the site. The report includes all databases and search radii required to comply with the AAI rule and ASTM Standard for Phase I Environmental Assessments. Please see full report for details on database and radii included for the site.SHINE Medical Technologies Stevens Point, WI Golder and Associates 4438 Haines Road, Suite 3

Duluth, MN MBB-5623 12/8/11The following City Directory(s) were located and provided for the streets and years listed:

1938, 1953, 1960, 1968, 1978, 1986, 1992, 1998, 2005, 2010 Copyright Notices Copyright 2009 by Historical Information Gatherers, Inc. All rights reserved. The person or entity that ordered and paid for this HIG Report ("the User") is granted a limited license to reproduce the contents of this HIG Report solely for purposes of providing supporting documentation for reports produced for the site which is the subject of this HIG Report. Any other reproduction in any media or format, in whole or in part, is prohibited without prior written permission.

The licensing agreement between HIG and infoUSA, Inc. provides that HIG may include photocopies or reproductions of portions of Polk City Directories, Hill-Donnelley Criss-Cross Directories and other Directories under infoUSA copyright, as supporting documentation for reports produced for the site which is the subject of this HIG Report. HIG is also permitted to provide photocopies or reproductions to the User for the User to include as supporting documents for reports produced for the site which is the subject of this HIG Report.

Disclaimer & Waiver of Liability This Summary of Historical Research and the included documents (hereafter referred to as the "HIG Report") contain information obtained from a variety of public and other sources. Additional relevant information for the site and surrounding properties may exist. Accordingly, there can be no guaranty that the information provided is complete. No warranty expressed or implied, is made whatsoever in connection with this HIG Report. Historical Information Gatherers, Inc. (HIG) specifically disclaims the making of any such warranties, including without limitation, merchantability or fitness for a particular

purpose. HIG, its officers, employees and independent contractors cannot be held liable to anyone for any loss or damage, whether arising out of errors or omissions, negligence, accident or any other cause, resulting directly or indirectly from any information provided by HIG. Any liability on the part of HIG is strictly limited to a refund equal to the amount paid for this HIG Report.

ph. 952-253-2004 l fax 952-253-2005 l email: orders@historicalinfo.com www.historicalinfo.com

!"#$!#!&'(%)+,,-./....0!%)+%/123/4445 #!654445 #!654445 #!654445 #!65

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!"#$!#!&'(%)+,,-./3723723723720!%)+%/123/4445 #!654445 #!654445 #!654445 #!65

!"#$!#!&'(%)+,,-./323232320!%)+%/123/4445 #!654445 #!654445 #!654445 #!65

!"#$!#!&'(%)+,,-./33330!%)+%/123/4445 #!654445 #!654445 #!654445 #!65

!"#$!#!&'(%)+,,-./3/3/3/3/0!%)+%/123/4445 #!654445 #!654445 #!654445 #!65

!"#$!#!&'(%)+,,-./3/23/23/23/20!%)+%/123/4445 #!654445 #!654445 #!654445 #!65 Appendix DPhotographs Recorded During the Subject Proper ty Inspection 2/10/2012 1 Project No. 113-81093 Lands End Parking Lot looking South West Property Line looking South 2/10/2012 2 Project No. 113-81093 West Property Line West Property Line looking South 2/10/2012 3 Project No. 113-81093 West Property Line looking East West Property Line looking East 2/10/2012 4 Project No. 113-81093 Southwest Property Corner looking East South Property Line looking North 2/10/2012 5 Project No. 113-81093 South Property Line looking South South Property Line looking North 2/10/2012 6 Project No. 113-81093 Southeast Property Corner looking North East Property Line looking West 2/10/2012 7 Project No. 113-81093 East Property Line looking North Woodland 2/10/2012 8 Project No. 113-81093 Shooting Practice Area Shooting Practice Area 2/10/2012 9 Project No. 113-81093 Shooting Area Practice Shooting Practice Area 2/10/2012 10 Project No. 113-81093 Shooting Practice Area Irrigation on the Property Appendix E User Questionnaire ASTMInternationalStandardE1527-05UserQuestionnaireforStevensPoint,WIGAI DUL F44 RL0 12/2011 Golder Associates Page 1 of 3 TheASTMStandardrequiresthepersoncommissioningaPhaseIEnvironmentalSiteAssessment(theuser)toprovidethefollowinginformation(ifavailable)totheenvironmentalprofessional.Failuretoprovidethisinformationcouldresultinadeterminationthat"allappropriateinquiry"isnotcomplete.1.Environmentalcleanupliensthatarefiledorrecordedagainstthesite(40CFR312.25).Areyouawareofanyenvironmentalcleanupliensagainstthesubjectpropertythatarefiledorrecordedunderfederal,tribal,stateorlocallaw?

UserhasnoknowledgeofenvironmentalcleanupliensontheSubjectProperty.

2.Activityandlan duselimitations(AULs)thatareinplaceonthesiteorhavethatbeenfiledorrecordedinaregistry(40CFR312.26).

AreyouawareofanyAULs,suchasengineeringcontrols,landuserestrictionsorinstitutionalcontrolsthatareinplaceatthesiteand/orhavebeenfiledorrecordedinaregistryun derfederal,tribal,stateorlocallaw?UserhasnoinformationregardingactivityorlanduselimitationsattheSubjectProperty.

3.Specializedknowledgeorexperienceoftheuser(40CFR312.28).

AstheuserofthisESAdoyouhaveanyspecializedkn owledgeorexperiencerelatedtothesubjectpropertyornearbyproperties?Forexample,areyouinvolvedinthesamelineofbusinessasthecurrentorformeroccupantsofthepropertyoranadjoiningpropertysothatyouwouldhavespecializedknowledgeofthechemicalsandprocessesusedbythistypeofbusiness?

SiteName:StevensPoint,WIGAI DUL F44 RL0 12/2011 Golder Associates Page 2 of 3 UserhasnospecializedknowledgeorexperiencerelatedtotheSubjectPropertyornearbyproperties.4.Relationshipofthepurchasepricetothefairmarketvalueofthepropertyifitwerenotcontaminated(40CFR312.29).

Doesthepurchasepricebeingpaidforthispropertyreasonablyreflectthefairmarketvalueoftheproperty?Ifyouconcludethatthereisadifferencehaveyouconsideredwhetherthelowerpurchasepriceisbecausecontaminationisknoworbelievedtobepresentattheproperty?Userbelievesthepurchasepricebeingpaidforthepropertyreasonablyreflectsthefairmarketvalueoftheproperty.

5.Commonlyknownorreasonablyascertainableinformationabouttheproperty(40CFR312.30).

Areyouawareofcommonlyknownorreasonablyascertainableinformationaboutthepropertythatwouldhelptheenvironmentalprofessionaltoidentifyconditionsindicativeofreleasesorthreatenedreleases?Forexample,asuser,a) Doyouknowthepastusesoftheproperty?TheUserknowsthattheSubjectPropertyhasbeenusedasanagriculturalfieldandthatselectivetreeharvesting/logginghasoccurredonthewoodedportionsoftheparcel,andisbeingusedforsuchpurposescurrently.b) Doyouknowofspecificchemicalsthatarepresentoroncewerepresentattheproperty?TheUserhasnoinformationregardingspecificchemicalsthatare,oroncewere,presentattheSubjectProperty.c) Doyouknowofspillsorotherchemicalreleasesthathavetakenplaceattheproperty?TheUserknowsofnospillsorotherchemicalreleasesthathavetakenplaceattheSubjectProperty.

SiteName:StevensPoint,WIGAI DUL F44 RL0 12/2011 Golder Associates Page 3 of 3 d) Doyouknowofanyenvironmentalcleanupsthathavetakenplaceattheproperty?TheUserknowsofnoenvironmentalcleanupsthathavetakenplaceattheSubjectProperty.6. Thedegreeofobviousnessorthepresenceorlikelypresenceofcontaminationattheproperty ,andtheabilitytodetectth econtaminationbyappr opriateinvestigation(40CFR312.31).AstheuserofthisESA ,basedonyourknowledgeandexperiencerelatedtothepropertyarethereanyobviousindicatorsthatpointtothepresenceorlikelypresenceofcontaminationattheproperty?TheUserhasnoinformationregardingcontaminatio nontheSubj ectProperty.UserQuestionnaireCompletedBy:DawnSovinecDate:12/21/11 Appendix FResumes of Environmental Professionals

No documents have been associated with this appendix.

DATA REPORT OF

WELL INSTALLATION STEVENS POINT, WISCONSIN

Submitted To: Richard Vann Bynum, COO SHINE Medical Technologies 8123 Forsythia St., Suite 140 Middleton, WI 53562 Submitted By: Golder Associates Inc. 4438 Haines Road Duluth, MN 55811 USA Distribution: Katrina Pitas, SHINE Medical Technologies Golder Associates Inc.

Project No. 113-81093 Report No. Golder Report 1, Project No 113-81093, Rev 2, Sept. 26, 2012

DATA REPORT OF WELL INSTALLATION

September 26, 2012 i Project No. 113-81093 Table of Contents

1.0INTRODUCTION

..................................................................................................................

............. 11.1Project Location and Site Description .........................................................................................

.. 11.2Proposed Deve lopment ..........................................................................................................

....... 12.0SITE RECO NNAISANCE ...........................................................................................................

...... 23.0FIELD INVEST IGATION ...........................................................................................................

........ 33.1Monitoring Well Installation ..................................................................................................

......... 33.2Sample Collection .............................................................................................................

............ 33.3SPT Corrections ...............................................................................................................

............. 43.4Geotechnical Building Borings .................................................................................................

..... 43.5Field and Laboratory Testing ..................................................................................................

...... 43.6Survey ........................................................................................................................

................... 43.7Monitoring Well Abandonment ...................................................................................................

... 54.0SUBSURFACE CONDITIONS .......................................................................................................... 65.0REFERE NCES ....................................................................................................................

.............. 76.0USE OF REPORT .................................................................................................................

............ 97.0CLOSING .......................................................................................................................

................. 10 September 26, 2012 ii Project No. 113-81093 List of Tables (in text) Table 3.6-1 Monitoring Well Locations and Elevations Table 4.0-1 Water Level Readings List of Figures Figure 1 Vicinity Map Figure 2 Project Site Location Map Figure 3 Well Location Map Figure 4 Soil Classification/Legend Appendix A - Monitoring Wells Figure A1 Record of Borehole SM-GW1A Figure A2 Record of Borehole SM-GW2A Figure A3 Record of Borehole SM-GW3A Figure A4 Record of Borehole SM-GW4A

September 26, 2012 1 Project No. 113-81093

1.0 INTRODUCTION

This data report presents the results of subsurface investigation and monitoring well installation for the proposed SHINE Medical Technologies (SHINE) isotope production facility at the contingency site near Stevens Point, Wisconsin. Golder Associates Inc. (Golder) was contracted by SHINE (December 5, 2011) to provide geotechnical and hydrogeological investigation services. These services are to assess the suitability of the site for the proposed development and provide sp ecific sections in the Safety Analysis Report (SAR) for the Nuclear Regulatory Commission (NRC) facility license permit application (NUREG-1537).

Field efforts were performed in strict conformance with Golder's Duluth Office Field and Laboratory Quality Manual (Golder, 2011a). Golder was approved as a vendor for these services following a supplier assessment performed by SHINE in October/November, 2011. The supplier assessment of Golder was performed in accordance with SHINE's Quality Assurance Program Description (SHINE 2011), based on guidance in Regulatory Guide 2.5 and ANSI/ANS 15.8-1995. 1.1 Project Location and Site Description The proposed SHINE Medical Technologies facility project contingency site is located near Stevens Point, Wisconsin. Specifically, the building site is located east of Stevens Point, about 0.5 miles north of McDill Avenue between Eisenhower Road and Burbank Road. 1.2 Proposed Development The proposed SHINE production facility will produce molybdenum-99 (Mo-99) for use in medical diagnostic testing. The production facility will be comprised of a single building having an irregular footprint of approximately 167 feet in the east-west direction by 415 feet in the north-south direction and an estimated floor to roof deck height of 86 feet for a portion of the facility with a 33 feet roof deck height for approximately two-thirds of the facility (Merrick and Company 2012). The majority of the building will be constructed with an at-grade finished floor elevation near the existing ground surface. The entire facility will be classified as a radiological facility.

September 26, 2012 2 Project No. 113-81093 2.0 SITE RECONNAISANCE The location and topography of the site are depicted in Figures 1 and 2. On December 15, 2011, a site reconnaissance was performed to observe visible and potential geohazards at the site and surrounding area. A Phase I Environmental Site Assessment was performed in accordance with ASTM procedure 1527, the results of which are included in Golder, 2012b. The project site is presently about 60% wooded and 40% agricultural fields. Based on our field observations, corn was the crop raised during the 2011 growing season. The crops had been harvested at the time of our investigation. No surficially dumped or uncontrolled fill, existing structures, or remnants of prior development (such as foundations) were observed. Surface topography of the area generally slopes gently down to the west and south. Ground surface across the proposed building area also generally slopes gently down to the west and south with grades dropping up to six feet across the site.

The site was visually reviewed for geohazards as part of the site reconnaissance. We looked for faulting, landslides, erosion, sediment deposits from rivers or lakes, karst features or mining activity, ground subsidence, and soil shrinking or swelling. There was no evidence of geohazards as noted above in our field review.

September 26, 2012 3 Project No. 113-81093

3.0 FIELD

INVESTIGATION 3.1 Monitoring Well Installation The hydrogeological investigation consisted of installing four groundwater monitoring wells at the site between the dates of December 14 and 18, 2011. The well locations, shown in Figure 3, were submitted to Shine for review on December 8, revised on December 13 (reduced from 5 to 4 wells), and approved on December 13, 2011. The monitoring wells were installed by Twin Ports Testing, under the direction of a Golder geologist.

The wells consisted of 2 inch diameter PVC with 10 ft long slotted screens. Screen elevations were determined based on the elevation of groundwater encountered while drilling. The monitoring wells extend approximately three feet above grade within protective casing having locking covers. Three protective pipe bumpers were installed around each well. The wells were developed by Golder following installation, on December 17 and 18, 2011. We understand that SHINE contracted AMEC to measure monthly groundwater elevations and provide the data to Golder. 3.2 Sample Collection In all monitoring well boreholes, representative samples of the soils encountered in the borehole were obtained by driving a split-spoon sampler ahead of the 4.24" Hollow-Stem Auger in accordance with ASTM Designation D1586, generally known as the Standard Penetration Test (SPT). Drive samples were collected at 5-foot intervals in monitoring wells SM-GW1A and SM-GW2A, and continuous sampling to 16 feet then 5-foot intervals thereafter in monitoring wells SM-GW3A and SM-GW4A. Drive samples were collected using a 2-inch (2-in.) outside diameter (O.D.) split-spoon sampler. The sampler was driven a depth of 18 or 24 inches for each test within the boreholes. Length of sample recovery was measured and recorded along with driving length on boring logs located in Appendix A. The sampler was driven vertically in measured intervals for each test using a 140-pound automatic drop hammer free-falling for 30 inches. The number of blows required to drive the sampler each 6-inch interval of the sampling attempt is recorded on the borehole logs. In addition, the total number of blows required to advance the sampler through the 18- to 24-inch sampling interval is presented as "N" on the borehole logs; this total is commonly referred to as a blow count. The blow counts shown on the borehole logs are field values that have not been corrected for overburden, sampler size, or other factors.

The monitoring well logs were generated by a Golder Engineer who observed the well installations and recovered samples. Recovered soil samples were visually classified accordi ng to the Unified Soils Classification System (USCS) that is summarized in Figure 4. The monitoring well logs are presented in Appendix A, as Figures A1 thru A4.

September 26, 2012 4 Project No. 113-81093 3.3 SPT Corrections Prior to driving the split-spoon, the exposed segment of the drill rod was measured to verify sampler depth and/or check for sand heave in the auger. Although no soil heaving was detected in borehole checks during drilling, loose sandy soils were observed close to the groundwater levels in all of the boreholes. It is likely that water-bearing soils may have experienced disturbance prior to a SPT due to the HSA method. If geotechnical analysis is performed for this contingency site, the field blow counts should be adjusted for various factors that might differ from standard SPT sampling procedures, including the following: hammer weight and drop height, split spoon sampler size, borehole diameter, rod length, sample set-up and liner, and energy ratio (ER) efficiency relative to 60 percent theoretical energy efficiency. To account for the increased efficiency of the automatic hammer, Golder recommends an ER factor of 72% (i.e., 20% more energy efficient). Twin Ports Testing performed hammer energy measurements on a separate project in March 2009 with energy transfer ratios ranging between 81% and 91%; thus our recommended 72% ER is considered conservative. Blow counts should be normalized to a common reference effective overburden stress (100 kiloPascals, or approximately 1 ton/sq. ft). The product of these factors determines corrected SPT (N 1)60 values. 3.4 Geotechnical Building Borings Ten borings and one seismic test hole within the potential building footprint were proposed to SHINE as part of Stage 2 services and field seismic testing was proposed as Stage 3 services, which may be authorized by SHINE at a later date if it is desired to further evaluate this contingency site. These future stages have not been performed to date, and thus are not included in this report. 3.5 Field and Laboratory Testing Golder proposed stage 2 services to include laboratory testing of geotechnical samples and field hydrogeological testing to include slug tests and falling head permeability tests. Golder proposed stage 3 services to include vertical seismic profiling. Stage 2 and 3 services have not been performed to date, and thus are not included in this report.

3.6 Survey

Upon receiving approval from SHINE representatives, Golder personnel located the four groundwater monitoring wells relative to the originally mapped property area using a Garmin GPS unit. Ayres Associates (Ayres), a professional surveyor licensed in the state of Wisconsin, surveyed the completed monitoring wells on December 23, 2011. The horizontal survey datum used was NAD/1983/91 Harn, US Survey Feet. The vertical datum was NAVD88 (2007) Geoid 09. Table 2.3-1 below lists the location (northing and easting) and ground surface elevation of the monitoring wells.

September 26, 2012 5 Project No. 113-81093 Table 3.6-1 Monitoring Well Locations and Elevations Boring Number Depth (ft) Surface Elevation (ft) Northing (ft) Easting (ft) SM-GW1A 16.0 1108.7 N 246,550.68 E 2,099,316.48 SM-GW2A 16.0 1107.3 N 244,939.33E 2,099,393.36 SM-GW3A 18.0 1113.0 N 245,281.57E 2,100,542.56 SM-GW4A 18.0 1113.9 N 246,217.67E 2,100,916.83

3.7 Monitoring

Well Abandonment At the request of SHINE, the four monitoring wells were abandoned on March 15, 2012. Borehole abandonment was performed in strict accordance with Chapter NR 141 of the Wisconsin Administrative Code (WIS DNR, 2011).

September 26, 2012 6 Project No. 113-81093

4.0 SUBSURFACE

CONDITIONS The subsurface conditions encountered at the site are depicted in detail on the Record of Well Logs displayed in Appendix A. The soil conditions indicated by the boreholes is about one foot of topsoil and crop residue overlying a medium to coarse grained, silty SAND extending to depths of 9 to 14 feet. Below this is a relatively clean, medium to coarse grained, SAND with silt to the borehole termination depth of 31 feet. In general the density of the sand was loose throughout the boreholes to a depth of 31. Cobbles or boulders were not noted during drilling. If geotechnical analysis is performed for this contingency site, the above Section 3.3 on SPT corrections should be considered. One borehole was advanced without sampling to a depth of 140 feet adjacent to SM-GW3A. This borehole was intended for a well installation into bedrock, but bedrock was not encountered within 140 feet of the surface. Groundwater was encountered in all of the wells at elevations ranging from about 1096 to 1106 (about 8 to 11 feet below grade) as indicated in the table below. Groundwater levels should be expected to fluctuate seasonally and annually with changes in precipitation patterns.

Table 4.0-1 Water Level Readings Borehole Number Surface Elevation (ft) Depth to Top of Well Screen (ft) Length of Well Screen (ft) Water Elevation (ft) SM-GW 1A 1108.7 6.0 10.0 1100.4 SM-GW 2A 1107.3 6.0 10.0 1096.9 SM-GW 3A 1113.0 8.2 10.0 1102.2 SM-GW 4A 1113.9 8.0 10.0 1106.1 Notes: 1) Surface elevation determined from survey. 2) Depth to top of well screen and length of well screen recorded during well installation. 3) Water elevation measured during well development.

September 26, 2012 7 Project No. 113-81093

5.0 REFERENCES

1. ANSI/ANS, 1995. American National Standards Institute Inc., American Nation Standard ANSI/ANS 15.8-1995, Quality Assurance Program Requirements for Research Reactors, Reaffirmed September 14, 2005.

2. ASTM D1586 - 11. Standard Test Method for Standard Penetration Test (SPT) and Split-Barrel Sampling of Soils.

3. ASTM D2487-11. Standard Practice for Classification of Soils for Engineering Purposes (Unified Soil Classification System), by ASTM International.

4. ASTM D2488-09a. Standard Practice for Description and Identification of Soils (Visual-Manual Procedure), by ASTM International.

5. Golder, 2011a. Duluth Office Field and Laboratory Quality Manual (FLQM), RL 0, October 17, 2011. 6. Golder, 2012b. Phase I Environmental Site Assessment, Golder Report 2, Project 113-81093, Revision 1, May 11, 2012.

7. Golder, 2012c. Quality Assurance Program Description (QAPD), GAI DUL D02 01/2012 RL1, Project No. 113-81051, Golder Associates Inc., January 12, 2012.

8. Merrick & Company, 2012. Preliminary Design Report Molybdenum-99 Production Facility, Prepared for SHINE Medical Technologies. Layout 3, 2012.

9. SHINE, 2011. Quality Assurance Program Description (QAPD), Revision - 0 (RL 0), based on guidance in Regulatory Guide 2.5 and ANSI/ANS 15.8-1995, July 14, 2011. 10. U.S. Nuclear Regulatory Commission, Washington, DC, 1996a. NUREG-1537, Part 1, Guidelines for Preparing and Reviewing Applications for the Licensing of Non-Power Reactors.¹ 11. U.S. Nuclear Regulatory Commission, Washington, DC, 1996b. NUREG-1537, Part 2, Guidelines for Preparing and Reviewing Applications for the Licensing of Non-Power Reactors.¹ 12. U.S. Nuclear Regulatory Commission, Washington, DC, 2010. Regulatory Guide2.5, Revision 1, Quality Assurance Program Requirements for Research and Test Reactors, June 2010. ¹ 13. WISDNR, 2011, Wisconsin Department of Natural Resources, Administrative Code, Chapter NR141, March 2011.

September 26, 2012 8 Project No. 113-81093 Note 1: Documents are available at: http://www.nrc.gov/reading-rm/doc-collections/

September 26, 2012 9 Project No. 113-81093 6.0 USE OF REPORT This data report was prepared for the exclusive use of SHINE Medical Technologies for design of the proposed Mo-99 production facility. We understand that SHINE will provide Golder with additional information about the proposed facility to assist us in preparing geotechnical recommendations for the project. We may be contacted if additional information is required for this contingency site to obtain additional information, perform engineering analysis, and make conclusions and recommendations.

The subsurface conditions at this site appear relatively consistent between the boreholes. However, there is always the possibility of variations in subsurface conditions between the boreholes and also with time. We highly recommend inspection and testing be performed by a qualified geotechnical engineer during construction to verify that conditions encountered are similar to those upon which our recommendations are based, and to provide corrective recommendations if conditions are different than expected or have changed. Unanticipated soil conditions are commonly encountered that cannot fully be determined by a limited number of explorations or soil samples. Such unexpected conditions frequently result in additional project costs in order to build the project as designed. Therefore, a contingency for unanticipated conditions should be included in the construction budget and schedule. The work program for this project followed the standard of care expected of professionals undertaking similar work in the State of Wisconsin under similar conditions, and adhering to the requirements in Golder's Quality Assurance Program Description (Golder, 2012c). No warranty expressed or implied is made.

September 26, 2012 10 Project No. 113-81093

7.0 CLOSING

This report is respectfully submitted to SHINE Medical Technologies. If you have questions or require additional information, please contact Golder at (218) 724-0088. Sincerely, GOLDER ASSOCIATES INC.

Joel D. Ulring, P.E. Amy Thorson, P.E. Senior Geotechnical Engineer Associate, Duluth Operations Manager Wisconsin Registration No. 27236-006 Wisconsin Registration No. 35963-006

Thomas G. Krzewinski, P.E. D.GE, F. ASCE Principal Geotechnical Engineer Wisconsin Registration No. 24946-006

FIGURES SCALE 0 1 1 MILES CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.J:\2011 Jobs\113-81093 SHINE Steven's Point WI\CAD\VICINITY_MAP_WI.dwg l 9/26/2012 11:48 AM l AGarrigus l STEVENS POINT 1--------APG9/11/12MTK9/11/12AT9/11/12 0----FIG.113-81093 VICINITY_MAP_WI.dwg SHN / STEVENS POINT / WI VICINITY MAP SHINE MEDICAL TECHNOLOGIES STEVENS POINT, WISCONSIN REFERENCE 1.) 1:24,000 SCALE TOPOGRAPHIC MAPS PRODUCED BY USGS AND DISTRIBUTED BY WISCONSIN DNR (2012).

QUADRANGLES SHOWN INCLUDE STEVENS POINT (1970), POLONIA (1969), ARNOTT (1969), AND WHITING (1970).

PROJECT LOCATION PROJECT LOCATION

CLEM'S WAY DRIVE JOHN JOANIS BUSINESS PARK DRIVE BRILOWSKI ROAD S.T.H. 51/I 39 E.M. COPPS DRIVE BUSINESS PARK DRIVE BRILOWSKI ROAD WISCONSIN CENTRAL LTD.

WOODLAND RD.

WISCONSIN CENTRAL LTD.

100'162'66'100'60'66'66'66'CITY OF STEVENS POINT TOWN OF HULL COYE DRIVE JOERNS DRIVE JADE COURT VIOLET PASS AVENUE COURT HEFFRON COURT 70+00 75+00 60+00 55+00 45+00 40+00 35+00 30+00 25+00 110+00 90+00 85+00 (END TAPER) 17+00 1516.65'TOWN OF PLOVER 02-4002-01 02-4002-04 02-1000-04 (3317)(3325)02-4005-01 02-4005-04 11+54.84(JEY) 10+65.67(JEY) 12+69.33(JEY) 70+00 02-1001-05 02-1001-03 02-1001-02 02-1001-01 02-1000-07 02-4005-03 (5416)(5500)(3017)(3101)(5400)+299.900 85.30'+324.284 85.30' 80' 70.23'

+300.328 82.02'+324.712 82.02'40 FT. SEWER & WATER MAIN EASEMENT SEWER & WATER MAIN EASEMENT 20'40'2308-01-2101-01 2308-01-2201-01 E.M. COPPS DRIVE WPS EASEMENT V675/813 WPS EASEMENT V676/760 WPS EASEMENT V679/788 WPS EASEMENT V687/176 WPS EASEMENT V687/176 WPS EASEMENT V679/341 WPS EASEMENT V676/748 WPS EASEMENT V687/176 WPS EASEMENT V679/341 80+00 85+00 LANDS' END WAY 15 FT. UTILITY EASEMENT (3301)(3241)(3001)(2917)02-1002-01 02-1003-01 02-4005-12 02-4005-11 02-4002-05 02-1000-10 02-1000-10 02-1000-10 02-1000-10 02-4000-15 02-4000-07 02-4000-07 01-2300-02 01-2300-01 01-2200-03 (5700)01-2200-02 01-2200-01 S.T.H. 51/I 39 02-1000-10 01-2300-03 (3300)(5501)02-1100-01 02-1002-02 UTILITY EASEMENT (2901)THIS IS A NON-TANGENT CURVE 02-1100-03 02-1000-08 02-4000-16 02-4000-06 (5533)02-1001-06 02-4000-10 02-4001-01 CARRIE FROST DRIVE 02-4004-06 02-4004-05 02-4001-03 02-4004-99 ROW 02-4000-18 (3316)02-4000-99 02-4005-99 02-4005-99 02-4005-99 02-4005-99 01-3000-03 01-3000-02 02-1002-03 02-1002-03 02-4005-07 02-4005-10 02-4005-09 02-4005-08 02-4005-11 02-4005-11 02-4004-04 02-4001-02 K.B. WILLETT DRIVE 02-1000-11 (5525)02-1000-16 (5525)02-4005-13 02-1000-09 02-4000-07 02-1000-14 02-4002-08 02-1000-15 CARRIE FROST DRIVE VENTURE DRIVE TOWN OF STOCKTON TOWN OF PLOVER TOWN OF HULL TOWN OF HULL TOWN OF STOCKTON 4.26 AC.13 AC.80 AC.2.4 AC.18.61 AC.

1,868' 1,868'TRANSMISSION LINE 1,000'R 1,000'R 80' FUTURE STREET 100' FUTURE STREET TRANSIT FACILITY 21 AC.3 AC.21 AC.2.2 AC.5 AC.2.4 AC.5.1 AC.17.52 AC.19.93 AC.3.7 AC.25.23 AC.10.33 AC.23.34 AC.1.5 AC.34.23 AC.35.69 AC.700'700'700'0.4 AC.10.43 AC.5.1 AC.1.5 AC.SM-GW1A SM-GW2A SM-GW3A SM-GW4A 316'316'1.) LOCATION OF POTENTIAL LOCATION FOR SHINE MEDICAL FACILITY PROVIDED BY CITY OF STEVENS POINT ON 12/20/11.

2.) AERIAL IMAGERY PROVIDED BY USDA FARM SERVICE AGENCY AND DATED 6/7/2010.

REFERENCESJ:\2011 Jobs\113-81093 SHINE Steven's Point WI\CAD\Proposed_building_layout_SP.dwg l 9/26/2012 11:58 AM l AGarrigus l STEVENS POINT SCALE 0 FEET 100O 100O 2--------APG9/12/12AT9/12/12AT9/12/121----FIG.113-81093 Proposed_building_layout_SP.dwg SHN / STEVENS POINT / WI PROJECT SITE LOCATION MAP SHINE MEDICAL TECHNOLOGIES STEVENS POINT, WISCONSIN CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.POSSIBLE BUILDING AREA INTERSTATE HIGHWAY 39 PROPOSED PROPERTY BOUNDARY 1.) NORTHINGS AND EASTINGS PROVIDED IN WISCONSIN STATE PLANE, CENTRAL ZONE, NAD83(HARN), US FT.

2.) ELEVATIONS REFERENCED TO VERTICAL DATUM NAVD88(2007) GEOID09.

NOTES

CITY OF STEVENS POINT TOWN OF HULL TOWN OF PLOVER WPS EASEMENT V679/341 WPS EASEMENT V676/748 WPS EASEMENT V679/341 TOWN OF STOCKTON TOWN OF PLOVER TOWN OF HULL TOWN OF HULL TOWN OF STOCKTON 80 AC.

1,868' 1,868'TRANSMISSION LINE 80' FUTURE STREET 100' FUTURE STREET 2.2 AC.5 AC.2.4 AC.5.1 AC.17.52 AC.19.93 AC.3.7 AC.25.23 AC.23.34 AC.1.5 AC.34.23 AC.35.69 AC.0.4 AC.5.1 AC.1.5 AC.SM-GW1A SM-GW2A SM-GW3A SM-GW4A 316'316'Point Table DESCRIPTION SM-GW1A SM-GW2A SM-GW3A SM-GW4A NORTHING (FT)246550.68 244939.33 245281.57 246217.67 EASTING (FT)2099316.48 2099393.36

2100542.56 2100916.83 GROUND ELEVATION (FT)1108.7 1107.3 1113.0 1113.9 1.) LOCATION OF POTENTIAL LOCATION FOR SHINE MEDICAL FACILITY PROVIDED BY CITY OF STEVENS POINT ON 12/20/11.

2.) AERIAL IMAGERY PROVIDED BY USDA FARM SERVICE AGENCY AND DATED 6/7/2010.

REFERENCESJ:\2011 Jobs\113-81093 SHINE Steven's Point WI\CAD\Proposed_building_layout_SP.dwg l 9/26/2012 12:01 PM l AGarrigus l STEVENS POINT SCALE 0 FEET 500 500 3--------APG9/12/12AT9/12/12AT9/12/121----FIG.113-81093 Proposed_building_layout_SP.dwg SHN / STEVENS POINT / WI WELL LOCATION MAP SHINE MEDICAL TECHNOLOGIES STEVENS POINT, WISCONSIN CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.POSSIBLE BUILDING AREA PROPOSED PROPERTY BOUNDARY 1.) BOREHOLE COORDINATES AS SURVEYED BY AYERS ASSOCIATES ON 11/11/2011.

2.) PROPOSED BUILDING FOOTPRINT IS A SQUARE, MEASURING 316 FEET ON EACH SIDE.

3.) CENTER OF BUILDING OUTLINE PLACED WITHIN PROPOSED SITE POLYGON AS DIRECTED BY CLIENT.

4.) NORTHINGS AND EASTINGS PROVIDED IN WISCONSIN STATE PLANE, CENTRAL ZONE, NAD83(HARN), US FT.

5.) ELEVATIONS REFERENCED TO VERTICAL DATUM NAVD88(2007) GEOID09.

NOTES BOREHOLE LOCATION AND DESIGNATOR LEGEND SM-GW1A OVERHEAD ELECTRIC POWERLINE

APPENDIX A MONITORING WELLS

1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Tuesday, August 13, 2013 11:05 AM To: Moser, Michelle; Lynch, Steven

Subject:

DRAFT SHINE Response to Air Quality Request #1 Attachments:

DRAFT - Air Quality Request 1 Response - Revision 2.pdfMichelle and Steve, Attached is the Draft SHINE Response to Air Quality Request #1.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

Part 1: Question NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Question No. Air Qyality Request #1 Revision 2 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

Air emissions during construction need to be quantified to evaluate potential impacts. Please provide air emission estimated quantities and durations for construction activities, including emissions from construction equipment (onsite equipment use, onsite vehicle emissions, site disturbing activities, etc.) as well as construction-related traffic (commuting workforce).

Please identify all emission sources, estimate emissions from each source, and describe all assumptions and calculations used to estimate emissions.

Part 2: Response Assigned to: -Response:

Construction air emissions have been estimated in SHINE calculation CALC-2013-0007.

Table 1 provides the calculated construction air emissions from CALC-2013-0007:

Table 1: Total Calculated Air Emissions for Construction Activities Annual Emissions (Tons/yr}

co 96 NOx 180 PM 13 Hydrocarbons 21 so2 12 C02 8802 PSAR Table 19.2.0-2 provided a list of equipment that would be needed for construction activities.

RFI-AMEC-2011-0033 provided the amount of each type of equipment that would be needed over the duration of construction activities, which was assumed to be 24 months. The total annual emissions listed above include emissions from both the construction equipment and personnel vehicles.

RFI-AMEC-2011-0033 was used only for an estimate of the amount of construction equipment that will be used. The start and end dates for construction provided in this RFI are no longer accurate start and end dates. Tables 2 and 3 provide the calculated construction air emissions for each type of equipment used during construction and the personnel automobiles used during construction.

The fuel for the construction equipment was assumed to be diesel fuel. The units for the calculated emissions are in tons/year.

Table 2: Emissions for Equipment Used During Construction Activities Total Engine Amount of Horse* Equipment Average Type of power (24 month per Hydro* Vehicle (hp) period) Month co NO. PM carbons so2 C02 Asphalt Compactor Cat 107 5 0.208 0.093 0.432 0.031 0.034 0.029 16.022 CB434C Asphalt Paver, Barber Greene 174 5 0.208 0.151 0.702 0.050 0.056 0.046 26.055 AP-1000 Backhoe/Loader 105 67 2.792 1.224 5.679 0.403 0.453 0.376 210.684 Cat 430 Boom Lift JLG 65 76 3.167 0.859 3.988 0.283 0.318 0.264 147.943 800AJ Concrete Pump Putzmeister 300 29 1.208 1.513 7.023 0.498 0.560 0.464 260.547 47Z-Meter Crane (Lattice Boom, 205 13 0.542 0.464 2.151 0.153 0.171 0.142 79.811 Manitowoc 8000 -BOt) Crane (Picker, Grove RT530E-160 55 2.292 1.531 7.104 0.504 0.566 0.470 263.542 2 30t) Crane (Picker, Grove RT600E-173 11 0.458 0.331 1.536 0.109 0.122 0.102 56.991 50t) Dump, Dual axel (15 cy) 350 47 1.958 2.862 13.280 0.942 1.058 0.878 492.643 Mack Excavator (Large, Cat 380 5 0.208 0.331 1.534 0.109 0.122 0.101 56.901 345D L) Excavator (Medium, Cat 148 13 0.542 0.335 1.553 0.110 0.124 0.103 57.620 321D LCR) Extended Forklift Lull 115 97 4.042 1.941 9.005 0.639 0.718 0.596 334.069 1044C-54 Fuel Truck, 150 14 0.583 0.365 1.695 0.120 0.135 0.112 62.891 Mack MP6 Material Truck 270 31 1.292 1.456 6.757 0.480 0.538 0.447 250.664 2-1/2t F-650 Mechanic's Truck 2-1/2t F-270 27 1.125 1.268 5.885 0.418 0.469 0.389 218.320 650 Motor Grader 183 15 0.625 0.478 2.216 0.157 0.177 0.147 82.207 Cat 140M Pickup Truck F-300 183 7.625 9.550 44.320 3.145 3.531 2.931 1644.141 250 Total Engine Amount of Horse-Equipment Average Type of power (24 month per Hydro-Vehicle (hp) . period) Month co NOx PM carbons so2 C02 Semi Tracker & Trailer (20 cy) 450 69 2.875 5.401 25.066 1.779 1.997 1.658 929.883 Mack MP8 Skidsteer Loader Case 75 79 3.292 1.031 4.783 0.339 0.381 0.316 177.441 SR200 Tracked Dozer 150 21 0.875 0.548 2.543 0.180 0.203 0.168 94.336 CatD6 Tracked Dozer 235 26 1.083 1.063 4.933 0.350 0.393 0.326 182.982 CatD7 Tracked Dozer 310 19 0.792 1.025 4.755 0.337 0.379 0.314 176.393 Cat D8 Tracked Loader 242 43 1.792 1.810 8.401 0.596 0.669 0.556 311.638 CAT973C Vibratory Soil Compactor Cat 156 14 0.583 0.380 1.763 0.125 0.140 0.117 65.406 C874 Water Truck 150 11 0.458 0.287 1.332 0.095 0.106 0.088 49.414 Mack MP6 Portable Air 50 54 2.250 0.470 2.180 0.155 0.174 0.144 80.859 Compressors Portable 50 61 2.542 0.531 2.462 0.175 0.196 0.163 91.341 Generators Portable 50 45 1.875 0.391 1.816 0.129 0.145 0.120 67.383 Welders Walk Behind 50 23 0.958 0.200 0.928 0.066 0.074 0.061 34.440 Compactor Total 1158 48 38 176 12 14 12 6523 Table 3: Emissions from Personnel Automobiles Used During Construction Activities Engine Horse-Type of Fuel power Peak Number Hydro-Vehicle Type (hp) of Vehicles co NOx carbons PM-10 PM-2.5 C02 Standard Passenger Automobile Gasoline 150 391 50.643 3.734 5.802 0.024 0.022 1984.774 (50 Miles Daily Commute) Standard Passenger Automobile Gasoline 150 29 7.512 0.554 0.861 0.004 0.003 294.417 (1 00 Miles Daily Commute) Total 420 58 4 7 0.03 0.03 2279 The equation from US EPA AP-42, Section 13.2.3 (Heavy Construction Operations) was used to calculate the fugitive dust emissions from construction activities (Reference 3 below). The amount of fugitive dust generated during construction activities that affect 51.0 acres of land is 734 tons/year.

For the fugitive dust calculations, we assumed that no mitigative measures were taken to reduce the amount of fugitive dust generated during construction activities.

The equation provided in Reference 3 assumes that the construction activities will be performed in a semiarid climate. The location of the construction activities for the SHINE site (Janesville, WI) is not located in a semiarid climate zone. Therefore, the amount of dust at the Janesville site would be less than the amount of dust in a semiarid climate and the results of the fugitive dust calculations are conservative.

The following assumptions were made to calculate the emissions from construction activities:

• The daily shift duration was assumed to be 10 hours0.417 days <br />0.0595 weeks <br />0.0137 months <br /> per day. Construction activities were assumed to occur 5 days per week for 50 weeks per year. For the construction equipment, it was assumed that the equipment was running for 5 hours0.208 days <br />0.0298 weeks <br />0.00685 months <br /> each day. From these assumptions, it was calculated that the construction equipment would be in use for 1250 hours52.083 days <br />7.44 weeks <br />1.712 months <br /> annually.

• The equipment used during construction was found in PSAR Table 19.2.0-2.

The quantity of the construction equipment was found in RFI-AMEC-2011-0033.

• The fuel for the construction equipment is assumed to be diesel fuel. This is a bounding assumption as diesel fuel has higher emission rates than gasoline.

• The number of passenger automobiles for construction was assumed to be 420 automobiles per month (the peak number of automobiles) (PSAR Subsection 19.4.7.1.1

). The number of workers commuting 50 miles daily was assumed to be 391 , and the number of workers commuting 1 00 miles daily was assumed to be 29.

• The fuel for the passenger automobiles was assumed to be gasoline.

A standard passenger automobile was assumed as the type of personnel vehicle.

• The duration of construction activities was assumed to be 24 months (PSAR Subsection 19.4.7.1 ). The actual construction schedule is 12 months. However, using 24 months is conservative because this duration over-predicts the expected amount of equipment needed for construction of the facility, thereby over-predicting the total amount of emissions as a result of the amount of equipment used.

• For fugitive dust calculations, the total number of acres affected due to construction activities was assumed to be 51.0 acres (PSAR Section 19.2). The amount of land permanently converted to industrial facilities will be 25.67 acres (PSAR Subsection 19.4.1.1.1) and the remaining 25.1 acres will only be temporarily disturbed during construction activities (PSAR Subsection 19.2). Fugitive dust was not calculated for the personnel automobiles because the automobiles will be parked at the site during construction activities.

The references that were used to calculate the emissions from construction are the following:

1. Average Annual Emissions and Fuel Consumption for Gasoline-Fueled Passenger Cars and Light Trucks, United States Environmental Protection Agency, Website accessed:

http://www.epa.gov/otaq/consumer/420f08024.pdf, Date accessed:

July 23, 2013. 2. Gasoline and Industrial Engines, Chapter 3, Section 3.3, Table 3.3-1, United States Environmental Protection Agency Fifth Edition Compilation of Air Pollutant Emissions Factors, Volume 1: Stationary Point and Area Sources, Fifth Edition, USEPA, Website accessed:

http://www.epa.gov/ttnlchief/ap42/ch03/final/c03s03.pdf, Date accessed:

July 22, 2013. 3. Heavy Construction Operations, Chapter 13, Section 13.2.3, United States Environmental Protection Agency Fifth Edition Compilation of Air Pollutant Emissions Factors, Volume 1: Stationary Point and Area Sources, Fifth Edition, USEPA, Website accessed:

http://www .epa. qov/ttnchie 1/ap42/ch 13/final/c 13s02-3. pdf, Date accessed:

August 6, 2013. Attachment 1 is RFI-AMEC-2011-0033.

Additional Action Taken (e.g., IMR)

Sl Medic al Technologies RFI Number:RFI-AMEC-2011-0033 Sargent & Lundy Construction Inputs REQUEST FOR INFORMATION (RFI) SHINE Procedure PM-001, Rev 2 RFI Revision:

1 Information needed to support the assessment of impacts associated with construction of the facility.

Requested information to include the following: 1 . Proposed grading plan including site runoff calculations, infiltration analyses, detention basins and design flows, erosion and sediment control measures and BMPs) 2. List of Construction Equipment Expected (AMEC will use to identify potential noise emission rates during construction)

3. Site Excavation and Soil Management Plan (depth of excavation, soil stockpile/disposal locations, etc.) 4. Construction Dewatering Plan (Need for dewatering, method/location of water disposal SHINE DAlE SHINE Licensin : Jim Freels Date: 06-13-12 Date Re uest Forwarded to Res onder RFI RESPONSE 1. Proposed Grading Plan A Site Utilization Plot Plan (SUPP), Rev 0, and Construction Grading Plan, Rev 0, have been developed.

As advised by City of Janesville Economic Development Department personnel, under the Rock County Airport Development Plan detention/retention basins are not allowed at the SHINE site because of concerns about glare and water fowl interfering with aircraft using the Southern Wisconsin Regional Airport. Therefore, basins are not shown on the SUPP or Construction Grading Plan. Instead, storm water is controlled using ditches, culverts, swales, diversion berms, etc., as described below. During operation, all storm water runoff from the developed parts of the site flows through a vegetated swale where the peak flow is controlled (detention) and a portion of the water is allowed to infiltrate.

Any water that does not infiltrate is discharged through an outfall control structure to the existing drainage ditch along Highway 51. Runoff from the undeveloped parts of the site follows natural draina e atterns and is dischar ed throu h a culvert to the draina e ditch along Highway 51. During construction, storm water run-on is diverted around the site via perimeter berms and ditches and then discharged back on the existing agricultural field through a flow spreader.

Storm water falling on disturbed construction areas is routed to the sedimentation and flow controls discussed above prior to being discharged to the existing ditch along Highway 51. Construction erosion and sedimentation controls will be in place throughout construction activities.

Operational controls will be installed during the later part of construction.

Final site design will include preparation of detailed grading plans and construction details, site storm water runoff calculations, infiltration analyses, peak discharge requirements, sediment reduction modeling, and water quality improvements.

A storm water management plan for erosion and sediment control during and after construction will be developed in accordance with Wisconsin Administrative Code NRs 151 and 216, and City of Janesville Ordinances 2004-228 and 2004-229.

Designs for storm water control will include Best Management Practices (BMPs) as presented in the Wisconsin Best Management Practices Manual, as adapted to specific physical conditions of the SHINE site. All controls will be designed to minimize potential adverse effects such as erosion, increased runoff, sediment transport off-site, and water quality management issues. Both construction and operation erosion, sedimentation, and other storm water controls will be designed, at a minimum, to meet City of Janesville ordinances and State code requirements.

Such controls must comply with the standards for multiple storm events up to and including the 1 00-year, 24-hour rainfall.

Culverts and ditches will be designed to convey the 1 00-year, 24-hour storm event. Storm water controls shown on the Rev 0 SUPP and Construction Grading Plan reflect preliminary sizing approximated in compliance with applicable regulations and guidance manuals. During final design, detailed runoff calculations and infiltration analyses will be submitted along with required documentation, in permit application form, to the City of Janesville for their review. Once acceptance of the permit application is achieved, the storm water control features will be incorporated into the design and construction documents, specifications, drawings, and details. 2. List of Construction Equipment Attachment 1 includes bounding estimate of the construction equipment necessary to construct, start up, and commission the Shine facility.

This estimate is based on input information provided by responses to RFis AMEC-2011-0041, AMEC-2011-0031, S&L-2012-0030 and information included in this RFI. The table provides the estimated average monthly construction equipment by type and quantity deemed necessary to construct the facility.

3. Site Excavation and Soil Management Plan Excavation quantities were estimated based on Layout Option 3 for the main building (provided in a June 28, 2012, e-mail from Clay Taylor to Maury Pressburger) and decisions reached in July 2012. The anticipated maximum depth of excavation is 39 feet below final grade, based on the following:

• The top of the lowest subfloor is considered at a depth of 32 feet, based on the Facility Review Team Final Report, dated June 22, 2012. Below this depth there is a six foot thick concrete mat, and a one foot over-excavation for mudmat placement, as decided during a July 13, 2012, telephone conversation with Bob Richardella (documented in meeting notes prepared by Massimo Bianchini).

• The in situ soil at the bottom of the excavation is assumed to be suitable for supporting the loads from the building.

This assumption will be confirmed when the loads have been established and an evaluation of bearing capacity has been performed.

In order to provide a bounding estimate of excavation quantities, the entire Radiological Control Area (RCA) shown in Layout Option 3 was assumed to be excavated to the maximum depth of 39 feet. Ancillary buildings and underground utilities, as shown on the Site Utilization Plot Plan (SUPP), Rev 0, were assumed to be excavated to a depth of 5 feet. Based on the RCA dimensions shown in Layout Option 3 and the dimensions of ancillary buildings and underground utilities shown in the SUPP, the estimated excavation for these structures is 210,000 cubic yards. There is an additional 68,000 cy of excavation and topsoil removal for the remainder of the site development area. Thus, the total excavation and topsoil removal for site development is 278,000 cy. This quantity includes a 25% margin for bounding considerations.

The fill material needed for the site grading is estimated to be 10,000 cy. This includes a 15% increase for shrinkage of material during compaction.

This is needed to grade the site to a Rough Grade Elevation of 824 feet NAVD 88 in the building area. This quantity would reduce the 71,000 cy of excess excavated material not used as backfill as noted below. In addition to adding 25% margin, the following assumptions were made in order to provide bounding estimates for this RFI response:

• The maximum frost depth is no more than 4 feet. A minimum depth of 5 feet was considered for the ancillary building foundations.

Thus, all foundations will be at least at this depth.

• The bearing material at the final depth of excavation is suitable for supporting the design load; therefore, over-excavation will not be needed.

• There is no separation between the upper 1 foot of topsoil and the underlying sand (SP) material.

All material beneath the topsoil is considered to be the same material.

• An allowance for a 12" thick mudmat was considered at the bottom of all excavations.

• No dewatering of excavations will be needed except after periods of heavy rain, as discussed in Item 4 below.

• Excavated slopes are stable on a slope of 1.5 Horizontal to 1 Vertical (1.5H:1V).

• An 8-foot wide bench is included in the RCA excavation for slope stability concerns since the overall excavation is 39 feet deep.

• The excavation is 1 0 feet wider around the sides of the RCA block at a depth of 39 feet to allow for erection of forms and providing a working area. Disposal of all excavated material can be on the site. There is an estimated 61,000 cy of excavated material that will not be reused as backfill in the excavations after site grading. This material can be spread out over the site as general fill. It would be equivalent to approximately 1 foot over 38 acres, or 2 feet over 19 acres. This 61,000 cy could alternatively be used to construct berms around the site for drainage control or for site control. The topsoil could be stockpiled for final grading and seeding. The Construction Grading Plan, Rev 0, shows tentative locations for topsoil and cut/fill stockpiles.

4. Construction Dewatering Plan Soil borings at the site encountered groundwater at a depth of approximately 59 feet to 65 feet, which corresponds to an approximate elevation of 764 feet NAVD 88. Considering a final site grade at elevation 827 feet NAVD 88 per the SUPP, a groundwater level at approximately elevation 766 feet NAVD 88 (used for conservatism), and a maximum depth of excavation of 39 feet (as discussed in Item 3), the groundwater level will be approximately 22 feet below the bottom of the mat excavation.

Even with a possible variation of several feet in the site grade elevation and a slight rise in the groundwater level, there should be no need for a construction dewatering program. In addition, the granular nature of the in situ soil should allow infiltration of any precipitation during construction.

However, the use of sumps and pumps may be required after periods of heavy rain during the excavation and backfilling of the buildings.

Responder:

Item 1

• Doug Dahlberg Responder Phone: 312-269-2402 Item 2

• Earl Wendorf 312-269-3401 Items 3 & 4

• Dan Kocunik 312-269-6572 Date Response Provided:

07/30/2012 Independent Reviewer:

-'=-""' -'-" ':-==:,

-Date: '"F'§.:: -=,--:_ __ -;::::E,-SHINE Licensing:

Jim Freels Date: 7-31-12 ) A Forwarded to Originator 7-31-12 Originator Acceptance:

Date: y; 7-1 "Z. vo (.)

RFI-AMEC-2011-003 Attachment 1 Months of Construction<-7/1/2013<-1/1/2014<-1/1/20156/30/14->123456789101112131415161718192021222324 Notice to ProceedIa. Site Developmen t Mobilize to site Site Preparation Ib. Substructure Excavation, Foundations, Substructure Backfill & Compact

Support U/G Utilities - Installation IIa. Above grade civil/structural/architectura l Facility above grade structure Roof Architectural details

External Building Foundations III. Mechanical Installation

Piping & Equipment HVAC Examination, Construction Testing & Turnover IV. Electrical Installation Electrical Raceway (Conduit, tray and supports)

CablePull&Termination V. Construction & Site Suppor t V I. Final Site work/Gradin g V II. Turnover, Start-up, & Commissionin g Equipment Asphalt Compactor, Cat CB434C, 107 Hp 002100000000000000001100 Asphalt Paver, Barber GreeneAP-1000, 174 Hp 001100000000000000001110Backhoe/Loader - Cat 430 - 105 Hp2 46622222222222222266421 Boom Lift, JLG 800AJ, 65 Hp 122211122233335788355421 Concrete Pump, Putzmeister 47Z-Meter, 300 Hp 112222222222211111000000 Crane - Lattice Boom, Manitowoc 8000 - 80t, 205 Hp 000000111111111111100000 Crane - Picker, Grove RT530E-2 30t, 160 Hp 112222333333344444220000 Crane - Picker, Grove RT600E - 50t, 173 Hp 000000111111111110000000 Dump, Dual axel (15 cy) Mack 350 Hp 222444444442210000002200 Excavator - Large, Cat 345D L, 380 Hp 011111000000000000000000 Excavator - Medium, Cat 321D LCR, 148 Hp 111111111111100000000000 Extended Forklift, Lull 1044C-54, 115 Hp 133355555555888883211000 Fuel Truck, Mack MP6, 150 Hp 111111111111110000000000 Material truck 2-1/2 ton, F-650, 270 Hp 111111111122222222111110 Mechanic's Truck 2-1/2 ton, F-650, 270 Hp 112221111111111110002221 Motor Grader, Cat 140M, 183 Hp 111100011111111000001110 Pickup Truck, F-250, 300 Hp446668888888881010101010108854Semi Tractor & Trailer (20 cy), Mack MP8, 450 Hp3212116 80000000000000000000 Skidsteer Loader- Case SR200 - 75 Hp 2 44444444444422222244441Tracked Dozer, Cat D6, 150 Hp1 11111111122210000001111 Tracked Dozer, Cat D7, 235 Hp 112222222222200000000110 Tracked Dozer, Cat D8, 310 Hp 112222222210000000000000 Tracked Loader, CAT 973C, 242 Hp 223333333333311100011100 Vibratory Soil Compactor, Cat CS74, 156 Hp 011111111111100000000110 Water Truck, Mack MP6, 150 Hp 001100000111111000011100 Portable Air Compressors <50Hp 233333322222333333100221 Portable generators <50 Hp 444222233333333333210221 Portable Welders <50Hp 222222222223333330000221 Walk behind compactor <50 Hp 044000000000440000002221 1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Tuesday, August 13, 2013 11:09 AM To: Moser, Michelle; Lynch, Steven

Subject:

DRAFT SHINE Response to Air Quality Request #7 and Proposed Action #11 Attachments:

DRAFT - Air Quality Request 7 Response -

Revision 1.pdf; DRAFT - Proposed Action Request 11 Response - Revision 1.pdf Follow Up Flag:Follow up Flag Status:

CompletedMichelle and Steve, Attached are the Draft SHINE Response s to Air Quality Request #7 and Proposed Action Request #11.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

Part 1: Question NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Question No.: Air Quality Request #7 Rev 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

Emission rates for hazardous air pollutants and toxic chemicals regulated under Wisconsin regulations need to be quantified.

Please provide emission estimates during construction, operation, and decommissioning for hazardous air pollutants and other toxic pollutants regulated under Wisconsin air regulations.

Please identify all emission sources, estimate emissions from each source, and describe all assumptions and calculations used to estimate emissions.

Part 2: Response Assigned to: ***** Response:

Wisconsin Administrative Code (NA 460.02) defines hazardous air pollutants as any air pollutant included in the list in section 112 (b) (1) of the act (42 USC 7412 (b) (1)) as revised by 40 CFR part 63 subpart C. Except for radionuclides, the SHINE plant will not emit any of the air pollutants in the list. This is because except for incidental amounts (e.g., gasoline in lawnmowers and snowblowers, cleaning fluids) SHINE will not have any of these hazardous air pollutants on site. The emission of radionuclides is discussed in EA Subsection 19.4.8.2.4.1.

Toxic chemicals emissions are discussed in the answer to Human Health I Waste Management

1. 5. During construction or decommissioning SHINE does not plan use any products or processes that would emit hazardous air pollutants.

Shine also does not plan to have on site or use any toxic chemicals in excess of the threshold amounts listed in the Wisconsin Administrative Code WEM 3.04 during construction or decommissioning.

Additional Action Taken (e.g., IMR)

Part 1: Question NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Question No.: Proposed Action Request #11, Rev 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

SHINE intends to acquire water from the Janesville municipality to use for isotope production, product processing, potable water, blowdown and facility heating water, fire protection system makeup, and chilled water makeup, as described in the EA. Please provide an estimate of the volume of water expected to be required for various construction activities and supply source. Please estimate the annual water use by the chilled water cooling system that must be discharged to the sanitary sewer after treatment.

Describe the nature of wastewater proposed for discharge to the Janesville Waste Treatment Facility, including source volume(s), expected constituents and concentrations (ER Section 19.2.3.1 ). Clarify whether any specific permits or limitations would apply to the discharge (e.g., industrial user provisions).

Part 2: Response Assigned to: *** Response:

The water usage of the SHINE facility has been broken down into two phases; construction and operation.

During the construction phase, the majority of water consumption will be dedicated to construction (personnel}

support, concrete mixing, and dust mitigation.

With respect to personnel support, section 19.4.7.1.3 of the SHINE PSAR states that a conservatively assumed 30 gal/day will be consumed for each worker on-site for 8-12 hours0.5 days <br />0.0714 weeks <br />0.0164 months <br />. With an estimated on-site workforce of 420, an estimated 12,600 gal/day will be required for construction support. This water will be supplied by the Janesville Water Utility. Water needs for concrete mixing will be met using the Janesville Water Utility. It is estimated that 700,000 gal/year will be required to meet this need. Dust mitigation/suppression will be accomplished by the use of water trucks during construction.

The use of dust mitigation will be limited to initial site preparation and early construction setup. It is estimated that these activities will require a total of 10,000 gallons. During the operation phase of the SHINE facility, cooling will be provided to the facility by way of chilled water. A final decision on the type of cooling unit to be used has not been made. This response assumes a closed-loop system is selected.

It is estimated that the volume of water used by a closed-loop chilled water system will be on the order of 10,000 gallons. It is assumed that the system will be flushed an average of once per year, discharging 10,000 gal/year to the Janesville sanitary sewer system. The temperature of this water will not exceed 149 degrees Fat discharge and will not exceed 40 degrees C (1 04 degrees F) at its introduction to the Janesville wastewater treatment facili , in accordance with Janesville Ci Ordinance 13.16.

Section 19.2.3.2.2 of the SHINE PSAR states that the chilled water system may use biocides, corrosion inhibitors, and scale inhibitors in the closed-loop chilled water system. Although the particular chemicals to be used in the SHINE closed loop cooling system have not yet been determined, any water discharged to the Janesville sewer from the SHINE facility will have concentrations of these pollutants below the Maximum Day Limit listed (from Janesville City Ordinance 13.16.060):

Maximum Day Limit Pollutant (mg/L) Cadmium (Total) 0.30 Chromium (Total) 3.00 Copper (Total) 2.60 Cyanide (Total) 0.50 Lead (Total) 0.30 Nickel {Total) 0.90 Zinc (Total) 3.65 Arsenic (Total) 1.00 Silver (Total) 3.90 Mercury No detectable discharge Total Toxic Organics (ITO) 2.13 Phosphorus 18.0 Cooling water chemical additions and likely maximum concentrations under consideration for the closed loop cooling system include the following: Cooling Loop Chemical Concentration Sodium sulfite Sodium lauroyl sarcosinate

<100 ppm Non-phosphate buffer* pH 9 to 9.5

• The buffer chosen will not include phosphorus to help the Janesville wastewater treatment plant comply with its phosphorus discharge limits. System water (and make-up water) may be softened to inhibit scale formation.

A schematic of the expected wastewater to be discharged to the Janesville sanitary sewer system is attached in 1-HR-SK-001.

With respect to waste water permitting, please refer to the response provided in Human Health/Waste Management Request #4. Additional Action Taken (e.a .. IMR) None ...

R e v A J u l y 1 5 , 2 0 1 3 S H I N E W a t e r B a l a n c e D i a g r a m 1-H R-S K-0 0 1 N o n-P r o p r i e t a r y M u n i c i p a l W a t e r S u p p l y W a t e r D e m i n e r a l i z e r S h o w e r s , L a v a t o r i e s , L a b o r a t o r i e s , e t c.F a c i l i t y S t e a m B o i l e r 1 1 3 g a l/d a y 3 2 7 0 g a l/d a y 2 5 8 0 g a l/d a y W a s t e w a t e r 3 2 7 0 g a l/d a y 2 5 8 0 g a l/d a y T o A t m o s p h e r e 3 g a l/d a y T o S e w e r 5 8 5 0 g a l/d a y S H I N E P R O P R I E T A R Y I S O T O P E P R O D U C T I O N P R O C E S S 1 1 0 g a l/d a y 6 0 7 0 g a l/d a y T o D i s p o s a l S i t e 2 2 0 g a l/d a y C o m b i n e d W a s t e 2 2 0 g a l/d a y 1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Tuesday, August 13, 2013 11:12 AM To: Moser, Michelle; Lynch, Steven

Subject:

DRAFT SHINE Response to Geology and Soil/Wa ter Resources Request #1 - Part 1 of 8 Attachments:

DRAFT - Geology and Soil-Water Resources R equest 1 Response - Revision 1 - Part 1 of 8.pdfMichelle and Steve, Attached is Part 1 of 8 of the Draft SHINE Response to Geology and Soil/Water Resources Request #1.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

NRC 2013 SITE ENVIRONMENTAL VISIT QUESTION Part 1: Question Question No.: Geology and Soil/Water Resources Request #1, Rev 1 Inspector:

NRC Audit Team Date: July 3, 2013 Question:

Please provide a reference for Figure 19.3.3-5, "Site Cross Section" and Figure 19.3.3-4, "Regional Structural Geology." Part 2: Response Assigned to: ***** Response:

Figure 19.3.3-5, "Site Cross Section," was developed from Figure 3.2-5, "Schematic E-W Cross Section," of the Preliminary Hydrological Analyses; Janesville, Wisconsin; August 3, 2012 (Attachment 1). Figure 19.3.3-4, "Regional Structural Geology," was developed from Figure 2.1-2 of the Seismic Hazard Assessment Report; Janesville, Wisconsin; August 3, 2012 (Attachment 2}. The National Water Quality Monitoring Council provides a large amount of water quality data available for download at this site: http://www.waterqualitvdata.us/portal.jsp None of the wells in the database are located directly on the Janesville or alternate sites, however, there are data for many nearby wells. SHINE used the USGS Wisconsin Water Science Center website to collect historical groundwater depth data during the site selection process found here: http://wi.water.usqs

.gov/data/qroundwater

.html A search of the Wisconsin Department of Agriculture, Trade and Consumer Protection's Well Constructor's Reports Database (http://datcpqis.wi.gov/slv/index

.htmi?Viewer=WeiiConstructorReports) yielded one Well Constructor's Report for the general area south of the site, completed on May 2, 1974 (Attachment 3). Discussions with the property lessee indicate that the private well just south of the site, near the old helicopter hangar, is currently being used to wash equipment and for one indoor sink. SHINE does not know of any water quality data available for this well. Attachment 1: Attachment 2: Attachment 3: Preliminary Hydrological Analyses; Janesville, Wisconsin; August 3, 2012 (192 pages) Seismic Hazard Assessment Report; Janesville, Wisconsin; August 3, 2012 (62 pages) Well Constructor's Report (Form 3300-15);

State of Wisconsin Department of Natural Resources; May 14, 1974 (1 page). Additional Action Taken (e.g., IMR) None

PRELIMINARY

HYDROLOGICAL ANALYSES

JANESVILLE, WISCONSIN

Submitted To: Dr. Gregory Piefer/CEO SHINE Medical Technologies 8123 Forsythia St., Suite 140 Middleton, WI 53562

Submitted By: Golder Associates Inc.

4438 Haines Road Duluth, MN 55811 USA

Distribution: Katrina Pitas, SHINE Medical Technologies Golder Associates Inc.

Project No. 113-81051 Report No. Golder Report 7, Rev 3, August 3, 2012 PRELIMINARY HYDROLOGICAL ANALYSIS

August 2012 i 113-81051

113-81051 shine final hydrology report august 2012.docx Table of Contents

1.0INTRODUCTION

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............ 11.1Location ......................................................................................................................

.................. 11.2Work Scope ....................................................................................................................

.............. 11.3Limitati ons ...................................................................................................................

................. 22.0HYDROLOGIC ASSESSMENT ....................................................................................................... 32.1Surface Water Features ........................................................................................................

....... 32.1.1General Setting and Site Description ....................................................................................... 32.1.2Rivers and Streams ............................................................................................................

..... 32.1.3Dams ..........................................................................................................................

.............. 42.2Stormwater In formation ........................................................................................................

........ 42.3FEMA Flood Insurance Studies ................................................................................................... 52.3.1Flood Issu es ..................................................................................................................

........... 52.3.2Recurrent Rock River Flows ....................................................................................................

52.3.3Flood Magnitudes...............................................................................................................

...... 52.4Probable Maximum Precipitation and Probable Maximum Flood ................................................ 62.4.1Probable Maximum Precipitation Estimates ............................................................................ 72.4.2Probable Maximum Fl ood Estimates ....................................................................................... 82.5Flood Related Consequence

........................................................................................................ 83.0HYDROGEOLOGICAL ASSESSMENT - GROUNDWATER

.......................................................... 93.1Hydrogeological Setting .......................................................................................................

........ 93.2Evaluation of Hydrogeologi cal (Slug)

Tests ................................................................................. 93.3Preliminary Hydrogeological and Solute Transp ort Analysis for Surface Leak Events ............. 143.3.1Boundary Co nditions ...........................................................................................................

... 153.3.2Subsurface Seepage Analysis - SEEP/W ............................................................................. 173.3.3Contaminant Transport Si mulation - CTRAN/W ................................................................... 194.0OTHER HYDROLOGIC RISKS ..................................................................................................... 204.1Tsunamis ......................................................................................................................

.............. 205.0USE OF REPORT .................................................................................................................

......... 216.0CLOSING .......................................................................................................................

................ 2

27.0REFERENCES

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113-81051 shine final hydrology report august 2012.docx List of Tables Table 2.2-1 Design Precipitati on 24-hour Storm Accumulations ........................................................... 4 Table 2.3.3-1 Summary of FEMA Fl ood Information for t he Rock Ri ver................................................... 6 Table 2.3.3-2 Summary of FEMA Flood Information for the Un-Named Tributary to the Rock River

...... 6 Table 2.4.1-1 Summary of NOAA and USACE (1978) Regional Greatest Average Precipitation .................................................................................................................

....... 7 Table 2.4.1-2 NOAA and USACE (1978) Calculated PMP Values for Similar Basin Size

........................ 7 Table 3.2-1 Slug Test Results for Monitoring Wells SM-GW1A, SM-GW2A, and SM-GW3A ............ 10 Table 3.2-2 Permeabilities Evaluated from Bouwer and Rice (1 976) Method, AQTESOLV, and the Average, Standard Deviation of the Results for All of the Tests and Slug-in, Slug-out Tests. ........................................................................................................................

........ 12 Table 3.2-3 Hydrobench Analysis Parameters

..................................................................................... 13 Table 3.2-4 Permeability Values Retrieved from Numerical Inversion of Slug Test Time Histories using Hydrobench Ž......................................................................................................... 14 Table 3.3.1-1 Water Table Implem entation ....................................................................................

......... 16 Table 3.3.2-1 Hydrogeological Parameters used in SEEP/W Groundwater Modeling .......................... 18 Table 3.3.2-2 SEEP/W Verification Simulation Results ........................................................................

.. 18 List of Figures Figure 1-1 Vicinity Map Figure 1-2 Project Site Location Map Figure 2.3.2-1 USGS Flows for the Rock River at Afton near the Site Figure 3.1-1 Hydrologic Features Figure 3.1-2 Generalized Geologic Cross Section of Rock County, West - East Figure 3.2-1 Combined Slug Tests for GW1A-MW1 Figure 3.2-2 Combined Slug Tests for GW2A-MW2 Figure 3.2-3 Combined Slug Tests for GW3A-MW3 Figure 3.2-4 Effective Radius Coefficients A, B, and C (Bouwer and Rice, 1976) Figure 3.2-5 Schematic E-W Cross Section. Figure 3.2-6 AQTESOLV Solution to the Slug-in Test in the Monitoring Well GW1A, First Trial. Figure 3.3.1-1 Surface Topography Contours from the Measurements at the Groundwater Monitoring Wells and Geotechnical Borings. Figure 3.3.1-2 E-W Geologic Cross-Section Figure 3.3.1-3 N-S Geologic Cross-Section August 2012 iii 113-81051

113-81051 shine final hydrology report august 2012.docx Figure 3.3.1-4 Smoothed Water Table Elevation Contours and the Water Table Sections used for the 2D SEEP/W Seepage Analysis. Figure 3.3.1-5 Surface Topography Level and Water Table Profile of the E-W Section (A-A) and N-S Section (B-B) Figure 3.3.1-6 Water Tables in the Monitoring Wells Figure 3.3.2-1 Model Geometry and Boundary Condition Figure 3.3.2-2 Volumetric Water Content Function for Dense Sand (center), Suction Function (right), and Conductivity of Unsaturated Zone Figure 3.3.2-3 Evaluated Total Head (top) and Pore Pressure (bottom) Contours after SEEP/W Analysis Figure 3.3.3-1 Contaminant Particle Tracking from SHINE Site, Janesville, to Rock River in the Critical E-W Pathway

Appendices Appendix A FEMA Flood Insurance Studies Appendix B Map of Dams along the Rock River in Rock County Appendix C Abbreviated Version of the City of Janesville Report on the 2008 Flood Appendix D FEMA Flood Area Map from Rock County, FEMA FIRMs through Janesville and near Site Appendix E Figures from the National Oceanic and Atmospheric Administration and US Army Corps of Engineers (1978) Report No. 51 PMP Study East of the 105th Meridian Appendix F Hydrobench Slug Test Visualization Appendix G AQTESOLV Slug Test Analysis

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1.0 INTRODUCTION

This analysis report presents preliminary hydrology assessments and review in support of the proposed SHINE Medical Technologies (SHINE) isotope production facility at Janesville, Wisconsin. SHINE proposes to construct a manufacturing plant for production of Molybdenum-99 (Mo-99) at a site located south of the community of Janesville in Rock County, Wisconsin (Figures 1-1 and 1-2). SHINE has contracted Golder Associates Inc. (Golder) to provide a range of technical services in support of the environmental impact assessment, site application process for the U.S. Nuclear Regulatory Commission (NRC), and geotechnical engineering analysis. To date, Golder has completed a range of subsurface boreholes, soil testing, hydraulic testing, and geotechnical analys es at the Janesville site. This current report is a draft document for development of the Safety Analysis Report chapter. Hydrogeologic analyses for the Safety Analysis Report chapter will be carried out using the full year of hydrogeologic data monitoring. Therefore, the flow and transport simulations reported here will be superseded and replaced by base case simulations and sensitivity simulations to be carried out and included in the Safety Analysis Report chapter. However, it is not anticipated that conclusions provided from the Safety Analysis Report chapter will be materially different from the results from this report.

1.1 Location

The proposed SHINE Medical Technologies facility project site (Site) is located at 4021 U.S. Highway 51 South, in Janesville, Wisconsin. Specifically, the building site is located in south Janesville about 0.75 miles south of East Avalon Road between North Riverside Drive and Prairie Street. This is directly east of the Southern Wisconsin Regional Airport (see Figure 1-1). 1.2 Work Scope The full extent of professional services and associated tasks contracted by SHINE from Golder are set out in Golder's proposal to Shine Medical Technologies on October 6, 2011 (Golder proposal P113-81051). An important aspect of both the site safety assessment process and engineering design is the assessment of hydrologic conditions at the Janesville site. Three types of hydrology conditions are considered in this report: Flood risk from Rock River and its tributaries Stormwater and runoff management and related risks Groundwater flow and transport NUREG (NUREG 1537, 1996) requires an assessment of all applicable hydrologic, hydrogeologic, and solute transport risks to nuclear facilities, both during operation and post-closure. The Hydrologic August 2012 2 113-81051

113-81051 shine final hydrology report august 2012.docx Scoping Assessment was carried out as a preliminary site hydrologic and hydrogeologic risk evaluation. The analysis included identification of hydrological processes that could contribute to radioactive releases, and characterization of those processes and the resulting hydrogeologic pathways. The analysis was built upon information provided by the SHINE project, together with data collected during the geotechnical assessment tasks. Specific tasks considered in the Hydrologic Assessment include the following: Qualitative assessment of surface and groundwater features, such as rivers, streams, reservoirs or impoundments (i.e., ponds) that have potential hydrologic and/or hydrogeologic effects on the facility. Flood frequency, magnitude, and consequence estimation. Probable maximum flood assessment. Preliminary hydrogeologic and solute transport analysis for surface leak events. Assessment of other hydrologic risks such as floods or tsunamis, as well as other events that could indirectly lead to hydrologic and hydrogeologic risks. For the present report, Golder has undertaken the following specific office-based tasks: Acquisition and review of available regional and site data, including information pertaining to precipitation (i.e., NOAA), stormwater, flow controls in the Rock River, floods (i.e., FEMA), hydrogeologic, and meteoric within approximately 40 kilometers of the project site. Evaluation of the peak flood levels (100-year and 500-year events) for the Rock River, based on Federal Emergency Management Act (FEMA) studies (Appendix A), in order to review flood frequency and magnitude and thereby understand potential consequence impacts at the site. Search of online databases of historical flood accounts in the area to assess the potential impacts to the site. Review of the Probable Maximum Precipitation (PMP) event at the site, with discussion regarding how the Probable Maximum Flood (PMF) would be determined. Preliminary surface and groundwater solute transport analysis for surface leak events. Preparation of this report, including discussion of the results, figures, maps, tables, and databases.

1.3 Limitations

This report was prepared using available information and provides preliminary analyses only. As of the date of this report, there is not 12 months of groundwater elevation data, which is required by NUREG standards for licensing purposes. This report relies on geological information and site description provided in Golder 2012a, Preliminary Geotechnical Report. Golder 2012b, Golder Quality Assurance Program Description (QAPD), provides a description of the quality assurance program under which this work was performed.

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113-81051 shine final hydrology report august 2012.docx 2.0 HYDROLOGIC ASSESSMENT This preliminary Hydrologic Scoping Assessment uses available information to identify and review potential surface water and flood related hazards that may impact the site. 2.1 Surface Water Features The following provides a summary and discussion of the surface water conditions and potential corresponding hazards at or near the site. 2.1.1 General Setting and Site Description The area around the site in Rock County experiences long cold winters and warm humid summers. Temperatures range from -27 degrees Fahrenheit (F) to over 100 degrees F. The County records show an average annual precipitation of approximately 33 inches, which includes winter snowfall accumulations. Annual snow accumulations range from less than 65 inches to as much as 109 inches. Approximately 60 percent of the accumulated precipitation occurs within the 5-month period from May to September, and can include an average of up to 40 thunderstorms per year (FEMA, 2008; see Appendix A). The Site is presently an agricultural field with a center-pivot irrigation system. The fields are cultivated with corn and soybeans. Generalized surface topography of the area slopes gently to the southwest. The ground surface across the development area slopes gently to the northwest with grades dropping about 7 feet from the southeast to the northwest (i.e., from corner-to-corner). The Site's ground elevation ranges from approximately 811 to 827 feet above sea level (Figure 1-2). 2.1.2 Rivers and Streams The central and southeastern portions of Rock County are characterized as flat glacial outwash plains. The majority of the County's rivers and stream valleys are filled with thick deposits of alluvial sand and gravel. The alluvial sediments and upland plains are the result of glacial activity. Surface soils include silt loam and are underlain by glacial till or stratified sand and gravel outwash units, which then serve as the source sediments to rivers and streams (FEMA, 2008). The County is drained entirely by the Rock River and its tributaries. Major tributaries include the Yahara River, the Sugar River, Raccoon Creek, and Turtle Creek. Turtle Creek drains the southeastern portion of the County, to its confluence with the Rock River near South Beloit, located approximately 8 miles south of the site. The site is located in a bend of t he Rock River, The Rock River flows through Jane sville, north of the site, then flows generally southward through land west and south of the site (Figure 1-1); it is approximately 2 miles from the site at its closest point. Elevations along the Rock River channel during normal flow August 2012 4 113-81051

113-81051 shine final hydrology report august 2012.docx conditions range from approximately 760 feet at Janesville, directly north of the site, to approximately 750 feet to the west and south of the site. The Rock River has a tributary area of approximately 3,340 square miles, as measured from the Afton U.S. Geological Survey (USGS) Gauge located just west of the site (FEMA, 2008). An un-named creek is located approximately 1 mile southeast of the site, and is referred to as the Un-Named Tributary in this analysis report. This tributary stream flows east-to-west to where it meets the Rock River approximately 2 miles south of the site. The stream has a tributary area of approximately 18.4 square miles (FEMA, 2008).

2.1.3 Dams The Rock River has two dams in the vicinity of Janesville, the Monterey Da m and Centerwa y Dam, both located upstream of the site (Appendix B). These dams are not designed or operated as flood control structures, and therefore have limited impoundments (FEMA, 2008). As such, the dams do not represent a potential hazard to downstream reaches of the river channel from increased releases or modification to flood flows. There are several upstream dams on the Rock River and its tributaries. However, these dams do not produce impoundments that pose any significant risk of cascading dam failures. 2.2 Stormwater Information The Rock County Storm Water Management Ordinance (Rock County 2004) provides guidance on the planning and design of surface water control structures. Section 28.07, (2), (B) of the ordinance addresses stormwater peak discharge rates and volumes, and provides the de sign rainfall runoff depths for characteristic 24-hour duration storms, as shown in Table 2.2-1 (Rock County).

Table 2.2-1 Design Precipitation 24-hour Storm Accumulations ReturnIntervalPrecipitationAccumulation(inches)2 Year2.9 10 Year4.1100 Year6.0 These design storm precipitation depths should be used to support any continued analysis of surface run-off, as well as to support design of stormwater mitigation structures at the site. The Rock County ordinance provides detailed guidance to establish long-term post-construction run-off management measures that require the use of Best Management Practices (BMPs) to reduce the amount of post-construction stormwater and associated pollutants that may reach waters of the State or other adjacent properties (Rock County). This guidance is consistent with Wisconsin NR 216 and NR 151.

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113-81051 shine final hydrology report august 2012.docx 2.3 FEMA Flood Insurance Studies The Federal Emergency Management Agency (FEMA) completed a flood hazard assessment for Rock County in August 2008 that looked at existence and severity of flood-related hazards, including the areas around the site. The study included the Rock River where it passes by the site, and the Un-Named Tributary stream located just to the south of the site. 2.3.1 Flood Issues The Rock River and the Un-Named Tributary stream are subject to flooding throughout the year; however, the majority of potential fl ooding occurs during the spring run-off. These floods are the result of combined precipitation and rain-on-snow events. Peak flows occurring during the winter months when temperatures are low can also often result in ice jam events. Based on available USGS flow data, March is the most common month for floods in the Rock River (USGS 2012a; FEMA, 2008). 2.3.2 Recurrent Rock River Flows Golder reviewed the USGS web-based flow data for the gauge site near Afton, located just across the river from the airport and just southwest of the site (see note on Figure 1-1). As shown in Figure 2.3.2-1, the peak stream flows range from approximately 10,000 to 17,000 cubic feet per second (cfs) over the approximate 100-year period of record for the gauge. Based on this record, flows of 10,000 to 13,000 cfs correspond approximately to the 10-year to 50-year events. The notable peak flow of 16,700 cfs in June 2008 is generally consistent with the 100-year flood levels along the Rock River (Janesville, 2008; see Appendix C, p 3-4). The flood level at the USGS gauge at Afton during the 2008 flood was approximately 755 feet. The 2008 flood is discussed in more detail in a summary report prepared by the City of Janesville (Janesville 2008) (Appendix C), which provides a comprehensive summary of the events leading up to the flood as well as emergency response and clean-up efforts. 2.3.3 Flood Magnitudes FEMA completed hydrologic and hydraulic analyses for the Rock River and the Un-Named Tributary stream to estimate flow magnitudes for various recurrence interval flood events, and to estimate the water surface elevations for corresponding flood events (Appendices A and D). Table 2.3.3-1 provides a summary of flows for the Rock River for the reach from Janesville to Afton near the USGS gauge, located just across the river from the site and the airport. Elevations are reported as an approximate range, based on the FEMA (2008) flood profiles, with the higher elevation corresponding to the upstream end of the reach at Janesville and the lo wer elevation at the downstream end near the USGS gauge at Afton. Table 2.3.3-2 provides a similar summary for the Un-Named Tributary to the Rock River for the reach between Highway 51 and the Prairie Road just to the south of the site. The range of reported elevations August 2012 6 113-81051

113-81051 shine final hydrology report august 2012.docx is similarly derived from the FEMA (2008) flood profiles. Channel bottom elevations are based on surveys that supported the FEMA (2008) studies. Table 2.3.3-1 Summary of FEMA Flood Information for the Rock River Table 2.3.3-2 Summary of FEMA Flood Information for the Un-Named Tributary to the Rock River The FEMA (2008) estimated flood level of approximately 755 feet, estimated for the 100-year event near the location of the USGS gauge at Afton (refer to Table 2.3.3-1), correlates well with the gauge flows and corresponding observed flood levels during the 2008 flood at the same location. The results show that the approximate 500-year floodwater surface elevations for the Rock River are well below the site ground elevation of approximately 830 fee t, for the full reach of the Rock River extending fr om Janesville downstream and around the site through Afton. Similarly, the approximate 500-year floodwater surface elevations for the Un-Named Tributary to the Rock River, for the reach just south of the site, are well below the site's approximate ground elevations. 2.4 Probable Maximum Precipitati on and Probable Maximum Flood Estimates of the Probable Maximum Precipitation (PMP) event for the site have been developed for areas east of the 105 th Meridian (NOAA and USACE, 1978; see Appendix E). These estimates are not specific to the site, but provide typical precipitation values for the regional area. The PMP is defined as the theoretically greatest depth of precipitation for a given duration that is physically possible over a particular drainage area at a certain time of year (AMS, 1959). Because of the limited data available for this extreme definition event, PMP results are typically considered to be estimates. PMP results are commonly used to support corresponding estimates of the Probable Maximum Flood (PMF), which is R P PeakDischarge(cfs)BottomofChannel(ft)WaterSurfaceElevation(ft)100.10 10,900 Approx.758.5to752 500.02 14,500 Approx.760to754 100 0.01 16,000 Approx.761to755 500 0.00219,000 Approx.762to756 Note:Elevationsareapproximate.ChannelbottomelevationsarebasedonFEMA(2008).ResultsreportedforthereachfromJanesvilletoAftonneartheUSGSgauge.Approx.738to748 R P PeakDischarge(cfs)BottomofChannel(ft)WaterSurfaceElevation(ft)100.10 2,255 Approx.758.5to774.5 500.02 3,473 Approx.759.5to775.5 100 0.01 4,205 Approx.760to776 500 0.0025,813 Approx.761to777 Note:Elevationsareapproximate.ChannelbottomelevationsarebasedonFEMA(2008).ResultsreportedforthereachbetweenHighway51andPrairieRoad.Approx.753to770 August 2012 7 113-81051

113-81051 shine final hydrology report august 2012.docx defined similarly as the theoretically greatest possible flood event at a given site location. The following provides a discussion and summary of the available PMP and PMF information pertaining to the site. 2.4.1 Probable Maximum Precipitation Estimates Estimates of the PMP were developed based on available meteorological data (NOAA and USACE, 1978). These PMP results are only estimates that allow for determination of average accumulated results for defined durations or storm events on a regional scale, and not specific to the site. Table 2.4.1-1 summarizes regional estimates for greatest precipitation values for monthly, weekly and 24-hour duration scenarios. Note the various databases used by the National Oceanic and Atmospheric Administration (NOAA) and the US Army Corps of Engineers (USACE). Table 2.4.1-1 Summary of NO AA and USACE (1978) Regional Greatest Average Precipitation

Further NOAA and USACE (1978) analysis of the available data developed estimates of PMP values (see Table 2.4.1-2) for various durations and for contributing basin areas of approximately 5,000 square miles, which is similar to the Rock River basin area (i.e., approximately 3,340 square miles). Since the PMP values of Table 2-4.1-2 are higher than those specified in the Rock County Storm Water Ordinance (Chapter 28), it is recommended that this PMP should conservatively be used for future PMF estimation.

Table 2.4.1-2 NOAA and USACE (1978) Calculated PMP Values for Similar Basin Size DurationPrecipitation(inches)6 Approx. 8-9 12 Approx. 10-11 24 Approx. 12-13 48 Approx. 15-16 72 Approx. 17-18 These PMP results would be used to support continued hydrologic and hydraulic assessments of the PMF. PeriodPeriodofRecordPrecipitation(inches)Greatest Monthly Average 1931-1960 Approx. 10-12 Greatest Weekly Average 1906-1935 Approx. 5-7 Greatest 24-hour "through 1970" Approx 14-16 August 2012 8 113-81051

113-81051 shine final hydrology report august 2012.docx 2.4.2 Probable Maximum Flood Estimates The hydrologic and hydraulic studies to support development of PMF estimates specific to the site were not included in this study. The technical work required to develop PMF flows and corresponding water surface elevations relative to the site would incorporate the PMP results discussed above into a hydrologic model to generate recurrence interval flood magnitudes and hydrographs, and then route those flows along the Rock River in a hydrodynamics simulation model to estimate water surface elevations (USACOE, 1984). Additional analysis and detailed topographic and bathymetric information for the Rock River and the Un-named Tributary to the Rock River would be needed to complete the assessment. These PMF calculations will be provided in the SAR Chapter. 2.5 Flood Related Consequence Based on review of the available information discussed herein, it appears there is little or no likelihood for flood-related hazards from the Rock River or the Un-Named Tributary to the Rock River to impact the site for events up to the 500-year recurrence interval flood. Stormwater run-off impacts need to be assessed once preliminary facility design documents are available, using the local planning and design criteria (Rock County). Additional studies are needed to confirm conditions for the PMF. That said, the separation of more than approximately 50 feet in vertical elevation from either the Rock River or the Un-Named Tributary to the Rock River suggests the likelihood will be similarly low.

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113-81051 shine final hydrology report august 2012.docx 3.0 HYDROGEOLOGICAL ASSESSMENT - GROUNDWATER The United States Nuclear Regulatory Commission guidelines for preparing and reviewing applications for the licensing of non-power reactors (NUREG-1537, Part 2) states that the facility design must consider leakage or loss of primary coolant to groundwater. The project is a series of linear accelerators that do not use primary coolant, as a reactor would. Therefore, coolant spill is not a credible scenario for this project. Therefore, the spill scenario considers the effects of accidental releases of unspecified liquid effluents in groundwaters.

Release scenarios will be described in other sections of the SAR. We also discuss the plausible pathways of the contaminant that may result in the most severe impact to the groundwater resources and to the closest potable water source, the Rock River. The river flows more than 2 miles away from the proposed site both in west and south directions as the river changes its direction from North-South to East-West (Figure 1-1). 3.1 Hydrogeological Setting The SHINE Janesville site is located in a glacial deposition subjected to post-glacial erosional and depositional processes (Figure 3.1-1). The top soil is under-drained by a relatively clean, fine to coarse grained sand extending to depths of 180 to 185 feet. Below this is a 10- to 18-foot layer of sandy silt, which is underlain by silty sand to the borehole termination depth of 221 feet. Bedrock was not encountered during drilling, although sampler refusal was experien ced in all three of the deep boreholes at depths between 170 and 180 feet. The density increases with depth as the soils became dense to very dense below depths of about 60 to 100 feet. Depth to bedroc k at the Janesville site may be as deep as 300 feet and it consists of Cambrian and Ordovician sedimentary bedrock (conglomerate, dolomite, limestone, sandstone, shale) (Figure 3.1-2). The carbonate bedrock is susceptible to dissolution (WGNHS, 2009). The Rock County Hazard Mitigation Plan (Vierbicher, 2010) indicates that the County has karst potential, particularly in the eastern third of the County. The monitoring well and remaining geotechnical boreholes terminated at depths between 60 and 71 feet.

Groundwater was encountered in all of the bor eholes during drilling at elevations ranging from about 754 to 766 (about 60 to 65 feet below grade) (see Table 3.3.1-1). Groundwater levels should be expected to fluctuate seasonally and annually with changes in precipitation patterns. 3.2 Evaluation of Hydrog eological (Slug) Tests Golder performed slug tests at monitoring wells SM-GW1A, SM-GW2A and SM-GW3A. At each well, static water levels were measured, and then a LevelTROLL 500 data logger was placed in the well. After ensuring that the water level had recovered to the static water table, Golder performed in-situ hydraulic conductivity (slug) tests, which involved near-instantaneous introduction (or removal) of a solid object of known volume into the water column. Both falling- and rising- head tests were conducted. For the August 2012 10 113-81051

113-81051 shine final hydrology report august 2012.docx falling-head (slug-in) test, the slug was inserted into the well displacing a volume of water equal to the volume of the slug causing the water level in the well to rise. Once the well returned to static conditions, a rising-head (slug-out) test was performed by rapidly removing the slug. A visualization of each of the four slug tests carried out in the three wells is provided in Figures 3.2-1, 3.2-2, and 3.2-3. Tests are summarized in Table 3.2-1. Test data are provided in Golder 2012a. Note that these test results reflect simple, short duration testing procedures. More accurate results could be obtained using single and multi-well pumping tests. However, since these tests primarily confirm generic, published ranges of hydraulic properties for site geologic materials, more advanced testing procedures are not justified.

Table 3.2-1 Slug Test Results for Monitoring Wells SM-GW1A, SM-GW2A, and SM-GW3A WellTestTestHead 1Ho(ft)InitialHead 2H(ft)WellCoordinates 3Easting(ft)WellCoordinates 3Northing(ft)Aquiferthickness 3,4b(ft)Depthtotopofwellscreen 3d(ft)Lengthofwellscreen 5L(ft)TransducerDepth(ft)GW1ASlugIn#17.5407.110W492655.35 N248568.86100+5020(6.94)69GW1ASlugOut#16.8667.110W492655.35 N248568.86100+5020(6.94)69GW1ASlugIn#27.6107.110W492655.35 N248568.86100+5020(6.94)69GW1ASlugOut#26.8577.110W492655.35 N248568.86100+5020(6.94)69GW2ASlugIn#16.5395.695W492635.32 N246973.23100+5015(8.51)66GW2ASlugOut#15.2845.695W492635.32 N246973.23100+5015(8.51)66GW2ASlugIn#26.4675.695W492635.32 N246973.23100+5015(8.51)66GW2ASlugOut#25.1515.695W492635.32 N246973.23100+5015(8.51)66GW2ASlugIn#36.6625.695W492635.32 N246973.23100+5015(8.51)66GW2ASlugOut#35.3355.695W492635.32 N246973.23100+5015(8.51)66GW3ASlugIn#15.8435.346W493372.93 N247753.86100+5515(5.50)70GW3ASlugOut#15.1085.346W493372.93 N247753.86100+5515(5.50)70GW3ASlugIn#26.1885.346W493372.93 N247753.86100+5515(5.50)70GW3ASlugOut#25.0925.346W493372.93 N247753.86100+5515(5.50)70 1HeadmeasuredinTrolldataloggerduringtestconductedon12/22/11."TestheadHo"isthedisturbedheadduetosluginsertionorremoval.2HeadmeasuredinTrolldataloggerduringslugtestconductedon12/22/11."InitialHeadH"istheheadbeforetesting,andalsodepthfromthephreaticsurfacetopiezometer.3Wellcoordinates,aquiferthickness,depthtotopofwellscreenandlengthofwellscreenweredeterminedfromwellcompletionrecords.4Totalthicknessofaquiferisexpectedtobeover100feet,includingaquiferbelowbottomofwell.5Lengthofwellscreen:TotalLength(SaturatedLength).6 HydraulicconductivityestimatedusingAQTESOLVdiscussedinSection3.2andsummarizedonTable3.2 2.TestHeadHo,InitialHeadH,andTransducerDepth(inbold)aretestresultsmeasuredorcalculatedbasedon12/22/11slugtests.

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113-81051 shine final hydrology report august 2012.docx Golder used the empirical/analytical method of Bouwer and Rice (1976) for analysis using AQTESOLV (Hydrosolve, 2011):

Where R e is the effective radius, r w and r c are the radii of the well and the casing, respectively, H is level of the static water table (at equilibrium), D is the aquifer thickness, A and B are empirical functions of L/r w (Figure 3.2-4), L is the perforation length of the well and y is the rise (or fall) of water table in the well. The method is based on the Theim equation of steady state flow and is an approximate solution for a transient slug test. The term () is obtained from the best fitting straight line in a plot of ln y t versus t. In test cases, Bouwer and Rice (1976) found the equation is accurate to within 10-25 percent depending on how the well below the water table is perforated (or open). AQTESOLV aquifer test analysis software (Hydrosolve, 2011) was used to analyze slug test results. The depth of the aquifer was assumed to be 120 feet considering only the body of sand above the sandy silt and below the groundwater table (Figure 3.2-5). AQTESOLV plots the head data against time in semi-log plots and estimates the hydraulic conductivity (K) based on a best fit line. AQTESOLV analyses are presented in Appendix G. Figure 3.2-6 provides an example analysis. AQTESOLV results are summarized in Table 3.2-2. Appendix G reports the analyses for the other tests, and the corresponding permeabilities are summarized in Table 3.2-2. The slug-in tests result in a slightly higher average permeability estimate (0.0051 ft/sec) than the average permeability of slug-out tests (0.0039 ft/sec).

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113-81051 shine final hydrology report august 2012.docx Table 3.2-2 Permeabilities Evaluated from Bouwer and Rice (1976) Method, AQTESOLV, and the Average, Sta ndard Deviation of the Results for All of the Tests and Slug-in, Slug-out Tests. Borehole Test Number Test Type K (ft/sec) GW-1A 1 In 0.0029 GW-1A 1 Out 0.0037 GW-1A 2 In 0.0037 GW-1A 2 Out 0.0027 GW-2A 1 In 0.0078 GW-2A 1 Out 0.0034 GW-2A 2 In 0.0041 GW-2A 2 Out 0.0030 GW-2A 3 In 0.0038 GW-2A 3 Out 0.0020 GW-3A 1 In 0.0053 GW-3A 1 Out 0.0081 GW-3A 2 In 0.0083 GW-3A 2 Out 0.0043 Average In 0.0051 Stdev In 0.0021 Average Out 0.0039 Stdev Out 0.0020 Average 0.0045 Stdev 0.0021 Median 0.0037 Golder verified AQTESOLV results using Hydrobench (Golder, 2011). Hydrobench is an inversion tool which optimizes the free parameters of the transient flow equations to match the well tests results of different kinds of tests with multiple boundary conditions. Although designed for confined aquifers, Hydrobench provides a valuable verification for AQTESOLV solutions. Rather than using an analytical solution, Hydrobench uses optimization of aquifer properties to match the time histories of slug-in and slug-out tests. The input values used for the inversion are: Well diameter (5 cm) Aquifer thickness (120 ft) Density (1000 kg/m 3), compressibility (2E-09 1/Pa), and viscosity (1E-03 Pa.s) of water Lithology (Coarse sand, porosity 20 percent, see Golder, 2012a) Hydrobench analysis parameters are summarized in Table 3.2-3.

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113-81051 shine final hydrology report august 2012.docx Table 3.2-3 Hydrobench Analysis Parameters Test Top of Perf (ft) Bottom of Perf (ft) Interval Length (ft) Ref Point Elevation (ft) Transducer Depth (ft) GW-1 50 72 22 825.8 71.5 GW-2 50 71 21 819.3 69.0 GW-3, Shell 1 55 70 15 827.3 71.5 GW-3, Shell 2 55 70 15 827.3 71.5 The numerical inversions were performed for all the tests within each well in two different cases. For the first case, all slug test pressure responses were simulated together for each well and for the second case, each slug test within each well was simulated individually. The inversions optimize well skin, storativity, transmissivity, and the shell radius (distance away from well that head is being affected) to match the slug test time histories. Well test type-curve matches are provided in Appendix H. Figures 3.2-1, 3.2-2, and 3.2-3 present the full time histories of the tests performed on GW1A, GW2A, and GW3A wells, respectively. Magenta lines illustrate the fit from the inversions. The resulting permeability values from the full time histories and also the individual slug test pressure spikes are summarized in Table 3.2-4. We confirm that the AQTESOLV empirical-analytical solution of Bouwer and Rice is less than 20 percent different from the Hydrobench result. Golder's Hydrobench simulations result in a mean permeability of 0.0038 with a lower standard deviation than the empirical method.

The permeabilities from the two meth ods are compatible and the results confirm high conductivity of the poorly-graded sand (SP) as the average permeability from the 14 slug tests is 0.0045 ft/sec from the Bouwer-Rice method and 0.0038 ft/sec from numerical inversions. Considering the observation that the sand deposits get denser (and less conductive) by depth and the observation wells do not extend more than 10 feet below the water table (Table 3.2-4), the permeabilities inferred from the slug tests are upper bounds for the sand deposits. Based on the calculated data and engineering judgement, a permeability of 0.004 ft/sec (1.2 mm/sec) is considered to be an appropriate estimate for th e sand deposit over the sandy silt and silty sand (Figure 3.2-5).

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113-81051 shine final hydrology report august 2012.docx Table 3.2-4 Permeability Values Retrieved from Numerical Inversion of Slug Test Time Histories using Hydrobench Ž Combined Slug Tests Inversions Well K (ft/s)GW 1A0.0037 GW 2A0.0054 GW 3A,Shell10.0024 GW 3A,Shell20.0024 Average0.0035 Individual Slug Test Inversions Well Test Trial K (ft/s)

GW 1ASlug in10.0037 GW 1ASlug out 10.0057 GW 1ASlug in20.0039 GW 1ASlug out 20.0041 GW 2ASlug in10.0055 GW 2ASlug out 10.0053 GW 2ASlug in20.0055 GW 2ASlug out 20.0054 GW 2ASlug in30.0061 GW 2ASlug out 30.0058 GW 3A,Shell1Slug in10.0023 GW 3A,Shell1Slug out 10.0022 GW 3A,Shell2Slug in10.0007 GW 3A,Shell2Slug out 10.0014 GW 3A,Shell1Slug in20.0027 GW 3A,Shell1Slug out 20.0028 GW 3A,Shell2Slug in20.0019 GW 3A,Shell2Slug out 20.0028 Average0.0038 Standarddeviation0.0017 Median0.0038 3.3 Preliminary Hydrogeological and Solute Transport Analysis for Surface Leak Events Golder carried out a preliminary evaluation of groundwater transport pathways from the SHINE medical facility to the closest potable water body, the Rock River. Geoslope SEEP/WŽ 2D finite element August 2012 15 113-81051

113-81051 shine final hydrology report august 2012.docx groundwater flow software (Geoslope, 2011) was used to verify these calculations. The Rock River was selected as the closest potential surface water receptor. If additional potential receptors are identified by SHINE, these will be included in the update to this analysis to be reported in the SAR. 3.3.1 Boundary Conditions Boundary conditions for flow simulations were estimated from data available at the 4 monitoring wells and 10 geotechnical exploration boreholes (Table 3.3.1-1). The highest measured elevation is at the groundwater monitoring well at the far east (827 feet) and the lowest point is the monitoring well at the far west (811 feet) delineating a 1 percent east-west drainage slope for the site (Figure 3.3.1-1). The ground surface was derived from these 16 measurements for a 1500-ft. x 1500-ft. area encompassing the measurement points by Kriging to a 50-ft. x 50-ft. grid space (Figure 3.3.1-1). East-West (A-A) and North-South (B-B) cross sections used for SEEP/W simulations are pr ovided in Figures 3.3.1-2 and 3.3.1-3. East-West and North-South 15,000-foot cross sections from the construction site to the Rock River are shown in Figures 3.

3.1-2 and 3.3.1-3. Water table levels have been measured at 10 geotechnical testing boreholes and 4 monitoring wells. Water table elevations in three boreholes could not be well identified (G11-05, G11-06, and G11-09). Fitting a smooth water table surface to the monitoring wells and boreholes, we identify the local water table elevation as shown in Figure 3.3.1-4. Due to variability in the water table elevations in the geotechnical boreholes, the residual errors to the best fit are noted in Table 3.3.1-1. Table 3.3.1-1 indicates that the water table elevation at the construction site is at 763 to 764 feet with a 0.21 percent East-West and 0.1 percent North-South gradient. Cross sections in the East-West direction and the North-South direction (A-A and B-B, respectively in Figures 3.3.1-2 and 3.3.1-3) are depicted in Figure 3.3.1-5.

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113-81051 shine final hydrology report august 2012.docx Table 3.3.1-1 Water Table Implementation Borehole Number Surface Elevation Water Elevation Smoothed Water Table Elevation Residual Error (ft) (ft) (ft) (ft) G11-01 819.1 754.1 763.5 9.4 G11-02 822.32 763.8 763.8 0 G11-03 824.92 765.9 764.0 -1.9 G11-04 821.87 763.4 763.4 0 G11-05 824.55 (759.6)

• 763.5 3.9 G11-06 825.87 (725.9)

• 767.3 41.4 G11-07 826.35 761.4 763.8 2.4 G11-08 824.74 765.7 763.2 -2.5 G11-09 824.99 (765)

• 763.5 -1.5 G11-10 826.18 761.2 763.7 2.5 SM-GW 1A 825.78 763.8 763.8 0 SM-GW 2A 819.23 762.2 762.2 0 SM-GW 3A 827.31 764.8 764.8 0 SM-GW 4A 811.72 761.7 761.8 0.1

• Measurements are obscured by drilling fluids. Values cited are estimates only. Residual error of the estimates made for these boreholes is not significant to the development of a smoothed phreatic surface..

The subsurface flow rate and direction can be estimated using the average perm eability and head drop between the monitoring wells (Figure 3.3.1-5). Where E-W and N-S refer to flow in the East-West and North-South directions respectively, K refers to hydraulic conductivity, i_ refers to the hydraulic gradient, and h and l refer to difference in height and coordinate respectively. The Rock River is located at about the same distance from the site in North-South and East-West directions. The seepage hydraulic gradient can be calculated from the difference between the groundwater table at the SHINE site and the Rock River. Rock River heads estimates are shown in Figure 3.3.1-5. Gradients i E-W and iN-S are estimated using the following formulae:

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113-81051 shine final hydrology report august 2012.docx Based on these gradients, the advective groundwater can be estimated as: Where tE-W and t N-S refer to travel time in the East-West and North-South directions, respectively. Uncertainty in travel time results from both seasonal head variations and uncertainty in hydrologic properties. Winter time water table elevations in the four monitoring wells (Figure 3.3.1-6) indicate up to approximately 3 feet of variation in head. The average water table elevation based on Figure 3.3.1-5 and Table 3.3.1-1 is 763.4 feet while the October 26, 2011 measurements indicate a 765.1-foot elevation, which dropped to 764.7 on January 9, 2012 (Golder, 2012a). This results in seasonal variation in hydraulic gradient, assuming that the Rock River surface elevation is approximately constant, the hydraulic gradient in the East-West direction will increase to 0.14 percent, and t he travel time decreases to 63 years (14 percent decrease). This seasonal variation can be compared to the uncertainty in estimates of permeability from the slug tests. The highest hydraulic conductivity estimates in Tables 3.2-2 and 3.2-4 are twice the mean value, and correspond to a groundwater travel time of 36 years. Based on the permeability evaluations shown in Table 3.2-4, and considering the maximum observed water table level (October 2011), the average seepage travel time to the Rock River will be 77 years with a standard deviation of 39 years. These analyses will be updated for the SAR report chapter when a full year of groundwater monitoring data is available. 3.3.2 Subsurface Seepage Analysis - SEEP/W The scoping calculation of seepage velocity presented in Section 3.3.1 was verified using a SEEP/W groundwater flow simulation (GeoSlope, 2011). The simulation mesh is illustrated in Figure 3.3.2-1. The model implements a 15,000-foot-long East-West cross section from the site to the Rock River. Model stratigraphy is based on Figure 3.2-5. The water table is based on information in Figure 3.3.1-5. The water table is extended from the site to the Rock River. Material properties assumed in the model are provided in Table 3.3.2-1. The hydraulic conductivity for the upper (sand) layer is based on slug test results, and are at the upper end of the reference range. Values for silty sand and sandy silt were also selected near the upper end of the reference range.

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113-81051 shine final hydrology report august 2012.docx Table 3.3.2-1 Hydrogeological Parameters used in SEEP/W Groundwater Modeling Material Reference Range of Hydraulic Conductivity (m/year) Hydraulic ConductivityPorosity (m 3/m 3) Density (gr/cm 3) Compressibility(1/MPa) Sand1x10 21x10 5 (1)38,500m/yr(.004ft/s)0.32 (1)1.6 (2)1/140 (2)SandySilt1x10 11x10 4 (1)5,000m/yr(5.2x10 4ft/s)0.35 (1)1.6 (2)1/140 (2)Silt1x10 21x10 2 (1)100m/yr(1.04x10 5ft/s)0.35 (1)1.6 (2)1/140 (2) 1 USDOE, 1993 2 Domenico and Mifflin, 1965.

GeoSlopeŽ SEEP/W includes a capability to model a moving phreatic surface using a Volumetric Water Content function (VWC). VWC describes the volume of water that a material can store as a function of the pore-water pressure. As the pore-water pressure moves from a positive to a negative state, the soil begins to desaturate, and water content decreases. The water content must be specified as the volumetric water content, which is defined as the porosity multiplied by the degree of saturation. The reference VWC used for SHINE flow verification modeling is provided in Figure 3.3.2-2, which illustrates the variation of pore pressure (psf) and Total Head (ft) together with the total flux (ft 3/Day) at the specified cross sections after the steady state seepage analysis. SEEP/W simulation results are provided in Table 3.3.2-2 and Figure 3.3.2-3. Results verify the calculations presented in Section 3.3.1. The maximum velocity of 0.38 ft/sec corresponds to an approximate travel time of 79 years for contaminants to reach the Rock River by advective groundwater transport, consistent with the values obtained in Section 3.3.1.

Table 3.3.2-2 SEEP/W Verifi cation Simulation Results SoilLayerThickness(ft)Flux(ft 3/day)AdvectiveVelocity(ft/day)Sand11845.30.38SandySilt15<0.01<0.01SiltySand1265.20.04Total25950.50.19 August 2012 19 113-81051

113-81051 shine final hydrology report august 2012.docx 3.3.3 Contaminant Transport Simulation - CTRAN/W Preliminary groundwater travel time estimates provided in Sections 3.3.1 and 3.3.2 are for advective transport only. The finite element program CTRAN/W (Geoslope, 2011) was used to add dispersion to the groundwater travel time estimates. Anderson (1984) suggests a dispersivity of 10% of the model dimension in the direction of the flow. We specify dispersivities of 1,100 feet and 30 feet for the longitudinal and transverse directions for all of the materials. Preliminary advection/dispersion transport simulations were carried out with CTRAN/W. An example simulation result is shown in Figure 3.3.3-1. In this simulation, the first solute at breakthrough was 37.6 years at the Rock River. CTRAN/W and SEEP/W simulations verify the scoping groundwater transport travel times presented in Section 3.3.1. These values are for design support scoping purposes only. Detailed simulations in support of the SAR will be carr ied out as a future task.

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113-81051 shine final hydrology report august 2012.docx 4.0 OTHER HYDROLOGIC RISKS

4.1 Tsunamis

Other hydrologic hazards that may impact the site include tsunamis. Tsunami hazards would originate from Lake Michigan, located approximately 63 miles to the east of the site (GoogleEarth). The elevation of the lake in the Kenosha area is approximately 580 feet (USGS 2012b), which is approximately 230 to 250 feet below the elevation of the Shine site of approximately 811 to 827 feet. While the possibility of a large wave being generated in Lake Michigan is possible, there is a low probability of it being greater than 230 feet and then maintaining any appreciable height over the more than 60 miles to the Shine site. This very low probability suggests the risk of tsunami is correspondingly very low. Additional study and investigations would be required to further quantify the tsunami hazard and evaluate the risks to the site.

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113-81051 shine final hydrology report august 2012.docx 5.0 USE OF REPORT This analysis report was prepared for the exclusive use of SHINE Medical Technologies to support design of the proposed Mo-99 production facility. Analyses will be refined for use in preparation of NUREG licensing documents. This report is not to be used directly for NUREG purposes. This analysis report was based on available information. Golder is not responsible for the accuracy of documents sited, and the analyses presented here may not represent a comprehensive survey of available literature. The work program for this project followed the standard of care expected of professionals undertaking similar work in the State of Wisconsin under similar conditions and adhered to the quality requirements in Golder 2012b, Golder Quality Assurance Program Description (QAPD). No warranty expressed or implied is made.

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113-81051 shine final hydrology report august 2012.docx

6.0 CLOSING

This report is respectfully submitted to SHINE Medical Technologies. If you have questions or require additional information, please contact Golder at (218) 724-0088. Sincerely, GOLDER ASSOCIATES INC.

Bill Dershowitz, Ph.D., P.G., R. Hg. Amy Thorson, P.E.

Principal Associate, Duluth Operations Manager Washington Registration No. 1577 Wisconsin Registration No. 35963-006 Thomas G. Krzewinski, P.E. D.GE, F. ASCE Principal Geotechnical Engineer Wisconsin Registration No. 24946-006

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7.0 REFERENCES

1. AMS, 1959. American Meteorlogical Society. Boston, Massachusets. 638 p.

2. Anderson P.A., 1984. "Movement of Contaminants in Groundwater: Groundwater Transport -- Advection and Dispersion" in Groundwater Contamination, Geophysics Study Committee, Geophysics Research Forum, National Research Council, Chapter 2. (37-45), National Academy Press. 3. Bouwer, H. and R.C. Rice, 1976. A slug test method for determining hydraulic conductivity of unconfined aquifers with completely or partially penetrating wells, Water Resources Research, vol. 12, no. 3, pp. 423-428.

4. Domenico, P. A.; Mifflin, M. D., 1965. Water from low permeability sediments and land subsidence. Water Resources Research 1 (4): 563-576.

5. FEMA, 2008. Flood Insurance Study: Rock County, Wisconsin and Incorporated Areas. Federal Emergency Management Agency, Flood Insurance Study Number 55105CV001A. August 19, 2008. Two volumes.

6. Geoslope, 2011. SEEP/W and CTRAN/W Software Docume ntation and Theo ry. Website: [www.geoslope.com]

7. Golder, 2011. Hydrobench User Documentation. Golder, Celle Germany.

8. Golder, 2012a. Golder Report 6, Revision 3, August 3, 2012, Preliminary Geotechnical Engineering Report. Prepared for SHINE Medical Technologies by Golder Associates, Inc.

9. Golder, 2012b. Golder Quality Assurance Program Description (QAPD), January 12, 2012 (RL1).

10. Hydrosolve Inc., 2011. AQTESOLV User Documentation. Website: [1]

11. Janesville, 2008. Report on the 2008 Rock River Flood.

City of Janesville, Wisconsin, Engineering Division.

12. LeRoux, 1963. Geology and Ground-water Resources of Rock County, Wisconsin: US. Geological Survey Water-Supply Paper 1619-X. 50 p.

13. NOAA and USACE, 1978. Probable Maximum Precipitation Estimates, United States East of the 105 th Meridian; Hydrometeorological Report No. 51. US Department of Commerce, National August 2012 24 113-81051

113-81051 shine final hydrology report august 2012.docx Oceanic and Atmospheric Administration; US Army Corps of Engineers. Washington D C. June 1978. 14. NUREG 1537, 1996. Guidelines for Preparing and Reviewing Applications for the Licensing of Non-Power Reactors. U.S. Nuclear Regulatory Commission, Washington, DC.

15. Rock County, 2004. Rock County Storm Water Management Ordinance. Chapter 28 of the Rock County Code of Ordinances, Rock County, Wisconsin. Adopted March 2004.

16. USACOE, 1984. Probable Maximum Flood Estimation - Eastern United States, TP-100. U.S. Army Corps of Engineers, Hydrologic Engineering Center. September 1984.

17. US DOE, 1993. Data Collection Handbook to Support Modeling Impacts of Radioactive Material in Soil", Environmental Assessment and Information Sciences, Division Argonne National Laboratory, Argonne, Illinois, Sponsored by U.

S. Department of Energy.

http://web.ead.anl.gov/res rad/documents/data_collection.pdfNUREG 1537, Part 2, "Guidelines for Preparing and Reviewing Applications for the Licensing of Non-Power Reactors: Standard Review Plan and Acceptance Criteria".

18. USGS, 2012a. Stormwater Data. Obtained from webs ite:[2]

19. USGS, 2012b. Elevation Data. Obtained from website: [3]

20. WGNS, 1983. Thickness of Unconsolidated Material in Wisconsin. University of Wisconsin-Extension Geological and Natural History Survey. Website: [4], accessed 12/16/2011.

21. WGNHS, 2009. Map data. University of Wisconsin-Extension Geological and Natural History Survey. Website: [5]

22. Vierbicher, 2010. Rock County Hazard Mitigation Plan Update. Prepared by Vierbicher in cooperation with the Rock County Emergency Management and Rock County Planning Economic and Community Development Agency, 145 p. [6], ac cessed 1/20/2012.

FIGURES CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.J:\2011 jobs\113-81051 shine medical technologies, wisconsin\CAD\VICINITY_MAP_WI_hYDRO.dwg l 4/3/2012 12:57 PM l AGarrigus l JANESVILLE--------AG4/3/12BD4/3/12TK4/3/120----FIG.113-81051 VICINITY_MAP_WI_hYDRO.dwg JANESVILLE / SHN / WI SHINE MEDICAL TECHNOLOGIES JANESVILLE, WISCONSIN1.) 1:250,000 SCALE TOPOGRAPHIC MAP PRODUCED BY USGS AND DISTRIBUTED BY TERRASERVER (5 KM NE OF ROSCOE, ILLINOIS, UNITED STATES).

PROJECT LOCATION PROJECT LOCATION SCALE 0 1 1 MILES UN-NAMED TRIBUTARY 1 TO THE ROCK RIVER ROCK RIVER PROJECT LOCATION G11-08 G11-09 G11-10 G11-07 G11-06 G11-05 G11-04 G11-01 G11-02 G11-03 SM-GW2A SM-GW3A SM-GW1A SM-GW4A VSP-01 G11-01 G11-02 G11-03 G11-04 G11-05 G11-06 G11-07 G11-08 G11-09 G11-10 SM-GW1A SM-GW2A SM-GW3A SM-GW4A VSP-01 229143.33 229146.03 229145.94 229017.94 229017.01 229019.68 229018.48 228887.34 228890.59 228890.37 229871.84 228276.10 229064.89 229051.61 229016.11 2230824.06

2230954.95

2231085.65 2230826.22 2230913.86

2230996.02 2231083.35 2230829.93

2230958.33 2231084.76 2230854.43

2230852.17 2231581.03 2230112.60

2230956.34819.1 822.3 824.9 821.9 824.6 825.9 826.4 824.7 825.0 826.2 825.8 819.2 827.3 811.7 825.1J:\2011 jobs\113-81051 shine medical technologies, wisconsin\CAD\Janseville_Site_map_HARN-W-WI-SF.dwg l 6/18/2012 9:13 AM l AGarrigus l JANESVILLE--------APG6/18/12BD6/18/12TK6/18/1216/18/12 FIG.113-81051 SITE_MAP_HARN-W-WI-SG.DWG JANESVILLE / SHN / WI SHINE MEDICAL TECHNOLOGIES JANESVILLE, WISCONSIN 1.) AERIAL IMAGERY DISTRIBUTED BY CITY OF JANESVILLE AND PROVIDED BY CLIENT.

2.) ADDITIONAL AERIAL IMAGERY PROVIDED BY NAIP AND DISTRIBUTED BY U.S.G.S.

3.) FAA ZONE C BOUNDARY OF THE SOUTHERN WISCONSIN REGIONAL REPORT LAND USE PLAN AND AIRPORT OVERLAY ZONING DISTRICT ORDINANCE WAS PROVIDED BY CITY OF JANESVILLE ON 10/4/11.1.) BOREHOLE AND WELL LOCATION COORDINATES AS SURVEYED BY AYERS ASSOCIATES ON NOVEMBER 11, 2011.

2.) PROPOSED DEVELOPMENT AREA IS A SQUARE, MEASURING 316 FEET ON EACH SIDE.

3.) CENTER OF BUILDING OUTLINE PLACED WITHIN PROPOSED SITE POLYGON AS DIRECTED BY CLIENT.

4.) NORTHING AND EASTINGS PROVIDED IN WISCONSIN STATE PLANE, SOUTH ZONE, NAD1983/91 HARN, US SURVEY FEET. THE VERTICAL DATUM IS NAVD88 (2007) GEOID09.

PROPOSED DEVELOPMENT AREA SM-GW2A G11-08 WELL LOCATION AND DESIGNATOR FAA ZONE C BOUNDARY PROPOSED PROPERTY BOUNDARY BOREHOLE LOCATION AND DESIGNATOR CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.VSP-01 BOREHOLE LOCATION WITH 2 INCH PVC INSTALLED FOR SEISMIC TESTING AND DESIGNATOR SCALE 0 400 400 FEET March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 2.3.2-1USGS Flows for the Rock River at Afton near the Site Lake Winnebago Tichigan Lake Lake Koshkonong Muskego Lake Lake Kegonsa Rome Pond Lake Waubesa Lake Monona Rock Lake Pewaukee Lake Pine Lake Sheboygan Lake Pike Lake Cedar Lake Mud Lake Sinissippi Lake Fox Lake Lake Emily Little Green Lake Green Lake Rush Lake Lake Butte des Morts Goose Lake Eagle Lake Lake Marie Fox Lake Long Lake Elizabeth Lake Wonder Lake Crystal Lake Lake Zurich Lake Como Lake Geneva Whitewater Lake Lake Holiday Spring Lake Sawmill Lake Orland Lake Lake Calumet Cedar Lake Rynearson Flowage Wisconsin River Castle Rock Lake Wisconsin River Wisconsin River Mason Lake Lake Redstone Mirror Lake Lake Wisconsin Crystal Lake Lake Mendota Yellowstone Lake Spring Lake Mississippi River Lake Odessa Lake Michigan Neshonoc Lake LAKES (REGIONAL)

WATER (REGIONAL) 100 MILE RADIUS STATE BOUNDARYJ:\2011 jobs\113-81051 shine medical technologies, wisconsin\CAD\JanesvilleHYDRO_WITM.dwg l 6/15/2012 2:34 PM l AGarrigus l JANESVILLE--------APG6/18/12BD6/18/12TK6/18/1216/18/12 CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.FIG.113-81051 JanesvilleHYDRO_WITM.dwg JANESVILLE / SHN / WI SHINE MEDICAL TECHNOLOGIES JANESVILLE, WISCONSIN SCALE 0 MILES 20 20 PROJECT LOCATION1.) LAKE (REGIONAL) DATA DEVELOPED AND DISTRIBUTED BY ESRI BASED ON THE U.S. NATIONAL ATLAS WATER FEATURE AREAS AS DEVELOPED BY NATIONAL ATLAS OF THE UNITED STATES AND THE UNITED STATES GEOLOGICAL SURVEY AS PUBLISHED ON 11/09/1999.

2) WATER (REGIONAL) DATA DEVELOPED AND DISTRIBUTED BY ESRI BASED ON THE U.S. NATIONAL ATLAS WATER FEATURE LINES AS DEVELOPED BY NATIONAL ATLAS OF THE UNITED STATES AND THE

UNITED STATES GEOLOGICAL SURVEY AS PUBLISHED ON 11/09/1999.

Figure3.1-2 acMW1""~ ! "#$$%&%& Figure3.2-1CombinedSlugTestsforGW1A-MW1 MW2:"%~ #' Figure3.2-2CombinedSlugTestsforGW2A-MW2

~ ! "#$$%&%& Figure3.2-3CombinedSlugTestsforGW3A-MW3 March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.2-4 Effective Radius Coefficients A, B, and C (Bouwer and Rice, 1976)

March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.2-5Schematic E-W Cross Section Note: Water table is assumed to vary linearly from GW-4A monitoring well to the Rock River. The vertical scale is 10times the horizontal.

March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.2-6 AQTESOLV Solution to the Slug-in Test in the Monitoring Well GW1A, First TrialShine Medical Technologies 0.1.42.84.25.6 7.0.0010.010.1 1.H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002908ft/secy0 = 0.4066ft March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.3.1-1Surface Topography Contours from the Measurements at the GroundwaterMonitoring Wells and Geotechnical Borings

ELEVATION (FT)

A'HORIZONTAL DISTANCE (FT)

A 600 650 700 750 800 850 900 950 100005001000150020002500300035004000450050005500600065007000750080008500900095001000010500110001150012000125001300013500140001450015000 bh Name= G11-07 bh Name= G11-06 bh Name= G11-05 bh Name= G11-04 bh Name= SM-GW3A bh Name= SM-GW4A ROCK RIVER GROUND SURFACE 3.3.1-2J:\2011 jobs\113-81051 shine medical technologies, wisconsin\CAD\Janesville Site Map_ELEV_ROCK CO.dwg l 7/9/2012 10:16 AM l AGarrigus l JANESVILLE--------APG6/18/12BD6/18/12TK6/18120----CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.FIG.113-81051 Proposed_building_layout.DWG JANESVILLE / SHN / WI E-W GEOLOGIC CROSS-SECTION SHINE MEDICAL TECHNOLOGIES JANESVILLE, WISCONSIN 0 HORIZONTAL SCALE FEET 1000 1000 0 VERTICAL SCALE FEET 100 100 LEGEND ELEVATION (FT)

B'HORIZONTAL DISTANCE (FT)

B 600 650 700 750 800 850 900 950 100005001000150020002500300035004000450050005500600065007000750080008500900095001000010500110001150012000125001300013500140001450015000 ROCK RIVER GROUND SURFACE bh Name= G11-08 bh Name= G11-04 bh Name= G11-01 bh Name= SM-GW2A bh Name= SM-GW1A 3.3.1-3J:\2011 jobs\113-81051 shine medical technologies, wisconsin\CAD\Janesville Site Map_ELEV_ROCK CO.dwg l 7/9/2012 10:36 AM l AGarrigus l JANESVILLE--------APG6/18/12BD6/18/12TK6/18/120----CHECK REVIEW DESIGN CADD SCALE FILE No.PROJECT No.

TITLE AS SHOWN REV.FIG.113-81051 Proposed_building_layout.DWG JANESVILLE / SHN / WI N-S GEOLOGIC CROSS-SECTION SHINE MEDICAL TECHNOLOGIES JANESVILLE, WISCONSIN 0 HORIZONTAL SCALE FEET 1000 1000 0 VERTICAL SCALE FEET 100 100 LEGEND March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.3.1-4Smoothed Water Table Elevation Contours and the Water Table Sections used for the 2D SEEP/WSeepage Analysis March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.3.1-5Surface Topography Level and Water Table Profile of the E-W Section (A-A)and N-S Section (B-B)

June2012ProjectNo.113 81051763.00763.50 764.00 764.50 765.00 765.50 766.00 766.50October 11November 11December 11January 12February 12March 12April 12May 12 June 12WaterTableElevation(ft.)Figure3.3.1 6WaterTablesintheMonitoringWells SM GW 1A SM GW 2A SM GW 3A SM GW 4A 113 81051SHINEHydrologyReport_Figures March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.3.2-1Model Geometry and Boundary ConditionThe red lines are the predefined head boundary conditions.

March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures Figure 3.3.2-2Volumetric Water Content Function for Dense Sand (center), Suction Function (right) and Conductivity of Unsaturated ZoneVol. Water Content (ft³/ft³)Pore-Water Pressure (psf)0.10.150.20.250.30.35-20-40-60-80-1000Vol. Water Content (ft³/ft³)Matric Suction (psf)0.10.150.20.250.30.350.1 100 11 0X-Conductivity (ft/days)Matric Suction (psf) 1 1000 10 1000.01 1000.1110 March 2012 Project No. 113-81051 113-81051 shine hydrology report _figures

\ Figure 3.3.2-3Evaluated Total Head (top) and Pore Pressure (bottom)Contours after SEEP/W Analysis The total flux values for the control sections are also reported.

roject No. 113-81051 113-81051 shine hydrology report _figures Figure 3.3.3-1Contaminant Particle Tracking from SHINE Site, Ja sville, to Rock Riverin the Critical E-WPathway APPENDIX A FEMA FIS (ABBREVIATED SECTIONS FOCUSED ON ROCK RIVER AND TRIBUTARY NO. 1 TO THE ROCK RIVER FROM REPORT AND SUPPORTING FLOOD PROFILES)

ROCK COUNTY, WISCONSIN AND INCORPORATED AREAS

VOLUME 1 OF 2 Community Name Community Number BELOIT, CITY OF 555544 BRODHEAD, CITY OF 550160 CLINTON, VILLAGE OF 550067 EDGERTON, CITY OF 550365 EVANSVILLE, CITY OF 550366 FOOTVILLE, VILLAGE OF 550575 JANESVILLE, CITY OF 555560 MILTON, CITY OF 550026 ORFORDVILLE, VILLAGE OF 550369 ROCK COUNTY (UNINCORPORATED AREAS) 550363 August 19, 2008 Federal Emergency Management Agency FLOOD INSURANCE STUDY NUMBER 55105CV001A

NOTICE TO FLOOD INSURANCE STUDY USERS Communities participating in the National Flood Insurance Program have established repositories of flood hazard data for floodplain management and flood insurance purposes. This Flood Insurance Study (FIS) report may not contain all data available within the Community Map Repository. Please contact the Community Map Repository for any additional data.

The Federal Emergency Management Agency (FEMA) may re vise and republish part or all of this FIS report at any time. In addition, FEMA may revise part of this FIS report by the Letter of Map Re vision process, which does not involve republication or redistribution of the FIS report. Theref ore, users should consult with community officials and check the Community Map Repository to obtain the most current FIS report components.

Effective Date: August 19 , 2008

Revised Dates:

i TABLE OF CONTENTS VOLUME 1

1.0 INTRODUCTION

...............................................................................................................1 1.1 Purpose of Study............................................................................................................1 1.2 Authority and Acknowledgments..................................................................................

1 1.3 Coordination..................................................................................................................2 2.0 AREA STUDIED

.................................................................................................................

4 2.1 Scope of Study...............................................................................................................4

2.2 Community

Description.................................................................................................

6 2.3 Principal Flood Problems...............................................................................................7

2.4 Flood

Protection Measures............................................................................................8

3.0 ENGINEERING

METHODS.............................................................................................8 3.1 Hydrologic Analyses......................................................................................................

8 3.2 Hydraulic Analyses........................................................................................................1 6 3.3 Vertical Datum...............................................................................................................21 4.0 FLOODPLAIN MANAGEMENT APPLICATIONS......................................................22 4.1 Floodplain Boundaries...................................................................................................22 4.2 Floodways......................................................................................................................23 5.0 INSURANCE APPLICATIONS

........................................................................................

80 6.0 FLOOD INSURANCE RATE MAP..................................................................................81

7.0 OTHER

STUDIES...............................................................................................................81

8.0 LOCATION

OF DATA

.......................................................................................................

81 9.0 BIBLIOGRAPHY AND REFERE NCES..........................................................................84

TABLE OF CONTENTS (Continued) ii FIGURES Figure 1 - Floodway Schematic........................................................................................................80 TABLES Table 1 - Summary of Discharges...............................................................................................1 1-15 Table 2 - Summary of Stillwater Elevations.....................................................................................15 Table 3 - Floodway Data..............................................................................................................24-79 Table 4 - Community Map History...................................................................................................83 VOLUME 2 EXHIBITS Exhibit 1 - Flood Profiles Allen Creek 01P-05P Bass Creek 06P-12P Blackhawk Creek 13P-14P East Fork Raccoon Creek 15P-16P Fisher Creek 17P-21P Greenbelt Tributary 1 22P-23P Greenbelt Tributary 2 24P Greenbelt Tributary 3 25P Greenbelt Tributary 4 26P-27P Greenbelt Tributary 5 28P-29P Markham Creek 30P-33P Marsh Creek 34P-36P Morningside Tributary 37P-38P Otter Creek 39P-42P Raccoon Creek 43P-46P Rock River 47P-70P Saunders Creek 71P-74P Spring Brook (Beloit) 75P-79P Spring Brook (Janesville) 80P-81P Sugar River 82P-86P Turtle Creek 87P-97P Unnamed Tributary 1 to Raccoon Creek 98P-99P Unnamed Tributary 2 to Raccoon Creek 100P-102P Unnamed Tributary 1 to Rock River 103P Unnamed Tributary 1 to Turtle Creek 104P Unnamed Tributary 2 to Turtle Creek 105P-106P Unnamed Tributary to Blackhawk Creek 107P-108P Unnamed Tributary to East Fork Raccoon Creek 109P-112P Unnamed Tributary in Turtle Township 113P-115P Yahara River 116P-119P

Exhibit 2 - Flood Insurance Rate Ma p Index & Flood Insurance Rate Map FLOOD INSURANCE STUDY ROCK COUNTY [AND INCORPORATED AREAS]

1.0 INTRODUCTION

1.1 Purpose

of Study This Flood Insurance Study (FIS) revises and updates information on the existence and severity of flood hazards in the geographic area of Rock County, including the Cities of Beloit, Brodhead, Edgerton, Evansville, Janesville and Milton; the Villages of Clinton, Footville and Orfordville; and the unincorporated areas of Rock County (referred to collectively herein as Rock County), and aids in the administration of the National Flood Insurance Act of 1968 and the Flood

Disaster Protection Act of 1973. This study has developed flood-risk data for various areas of the commun ity that will be used to establish actuarial flood insurance rates and to assist the community in its efforts to promote sound floodplain management. Minimum floodplain management requirements for participation in the National Flood Insurance Program (NFIP) are set forth in the Code of Federal Regulations at 44 CFR, 60.3.

Please note that the City of Edgerton is geographically located in Rock and Dane Counties. Also, the City of Brodhead is geographically located in Rock and Green Counties. The City of Edgerton's special flood areas are included in its entirety in this FIS report. The flood-hazard information for the City of Brodhead is for information purposes only. See separa tely published FIS report and Flood Insurance Rate Map.

In some states or communities, floodplain management criteria or regulations may exist that are more restrictive or comprehensive than the minimum Federal requirements. In such cases, the more restrictive criteria take precedence and the State (or other jurisdictional agency) will be able to explain them.

1.2 Authority

and Acknowledgments

The sources of authority fo r this FIS are the National Flood Insurance Act of 1968 and the Flood Disaster Protection Act of 1973.

The hydrologic analyses for Saunders Creek, Fisher Creek, Markham Creek, Greenbelt Tributaries 1-5, Morningsid e Tributary, Blackhawk Creek, Unnamed Tributary to Blackhawk Creek, Unnamed Tributary 1 to Rock River, Spring Brook (Beloit), Unnamed Tributary in Turtle Township, Bass Creek above Footville Road, Lenigan Creek, Lenigan Creek Tributaries 1 & 2, Unnamed Clinton Tributary, Unnamed Tributary in Union Township, Philhower Road Tributary, Unnamed Tributary 2 to Rock River, and Milton Ditch was performed 1

2 by Wisconsin DNR. The hydraulic analyses for these same streams in addition to Rock River, Raccoon Creek, Unnamed Tri butaries 1 & 2 to Raccoon Creek, East Fork Raccoon Creek, Unnamed Tributary to East Fork Raccoon Creek was performed by Gannett Fleming, for the Federal Emergency Management Agency (FEMA), under Contract No. NMF00000316.

Mapping done countywide was performed by Gannett Fleming.

This work was completed in May 2006.

The hydrologic and hydraulic analyses for the following streams were done by Owen Ayres and Associates, Inc., for FE MA under Contract H-3805 completed in May 1979: Yahara River, Otter Creek, Ma rsh Creek, Sugar River, Turtle Creek, Unnamed Tributary 1 and 2 to Turtle Creek, Spring Brook (Janesville) and Bass Creek from Footville Road to its mouth. The hydrologic analyses for the Rock River, Raccoon Creek, Unnamed Tributar y 1 & 2 to Raccoon Creek, East Fork Raccoon Creek, Unnamed Tributary to Ea st Fork Raccoon Creek done under this same contract was incorporated into the new 2006 hydraulic study.

The hydrologic and hydraulic analyses for Allen Creek above the Lake Leota Dam were performed by the U.S. Department of Agriculture, Soil Conservation Service (SCS), as reported in a "Flood Hazard Study, City of Evansville, Rock County, Wisconsin" in January 1984. The hydr ologic analysis done in that study

was used in the 2006 hydraulic study.

The projection used in the preparation of this map was Universal Transverse Mercator (UTM) zone 16. The horizontal datum was NAD83, GRS1980 spheroid. Differences in datum, spheroid, projection or UTM zones used in the production of FIRMs for adjacent jurisdictions may result in slight positional differences in map features across ju risdiction boundaries. These differences do not affect the accuracy of this FIRM.

1.3 Coordination

Information on the coordination for each jurisdiction included in this countywide FIS, as compiled from their previously printed FIS reports, is shown below.

Beloit, City of: Streams requiring detailed and approximate study were identified at an initial coordination and time and cost meeting attende d by representatives of FEMA, the Study Contractor, and the City of Beloit on February 2, 1977. Base maps were obtained from the U.S. Army Corps of Engineers (COE), Rock

Island District; and the City of Beloit. Flood

elevations, flood bounda ries, and floodway delineations were determined by the Wisconsin Department of Natural Resources, the Rock Island District COE, and the U.S. Geological Survey (USGS).

3 On October 16, 1980, the results of the work by the Study Contractor were revi ewed and accepted at a final coordination meeting attended by

representatives of FEMA, the Study Contractor, and the City of Beloit.

Edgerton, City of: Streams requiring de tailed study were identified at a meeting attended by representatives of the Study Contractor, FEMA, the Wisconsin Department of

Natural Resources and representatives of the City of Edgerton on June 6, 1979. Results of the hydrologic analyses were coordinated with the Wisconsin Department of Natural Resources, Flood Plain Management Section, and the Engineering Department of the City of Edgerton.

On March 31, 1981, the results of the study were reviewed and accepted at a final meeting attended by representatives of the Study Contractor, FEMA and

community officials.

Evansville, City of: On February 21, 1983, the results of this study were reviewed and accepted at a final coordination meeting attended by representatives of the

community and FEMA.

Janesville, City of: At a time and cost meeting on August 6, 1980 with representatives of the Wisconsin Department of Natural Resources (WDNR), FEMA, the Study

Contractor, and the City Engineer, the limits of detailed and approximate study were determined.

The hydrology and hydraulics for the Rock River and

Spring Brook and the floodway were coordinated with the WDNR.

On January 18, 1984, the results of the work by the Study Contractor were revi ewed and accepted at a final coordination meeting attended by representatives of the Study Contractor, FEMA, and the community.

Rock County (Unincorporated Areas): A search for basic data was made at all levels of government. County officials, local residents, the U.S. Army Corps of Engineers (COE), the U.S.

4 Geological Survey (USGS) and the State of Wisconsin were contacted to obtain data on land use

and other available da ta within the county.

Discharges were coordinated with the COE, the USGS, and the States of Illinois and Wisconsin. An initial coordination meeting was held on February

21, 1975, to define study procedures and establish detailed study areas. This meeting was attended by

representatives of FEMA, the State of Wisconsin, Rock County, and the Study Contractor.

During the course of the work by the Study

Contractor, flood elevat ions, flood boundaries, and floodway delineations were reviewed with community officials and with officials from the Wisconsin Department of Natural Resources.

On October 14, 1980, the results of the work by the

Study Contractor were revi ewed and accepted at a final coordination meeting attended by personnel of FEMA, the State of Wisc onsin, the county, and the Study Contractor.

2.0 AREA STUDIED

2.1 Scope

of Study

This FIS covers the geographic area of Rock County, Wisconsin, including the incorporated communities listed in Section 1.1. The areas studied by detailed methods were selected with priority given to all known flood hazards and areas of projected development or proposed construction through September 2006.

The flooding sources studied by detailed methods are listed below:

1. Allen Creek, from 450 ft below Stat e Highway 213 to about 6500 ft above City of Evansville Corporate Limits;

2. Bass Creek, from its mouth at the Rock River to W. Dorner Road;

3. Blackhawk Creek, from its confluence w ith Spring Brook (Jan esville) to about 500 ft. above S. Milton Shopiere Road;

4. East Fork Raccoon Creek, from the state boundary to Spring Creek Road;

5. Fisher Creek, from its mouth at the Rock River to about 2100 ft. above N.

Little Road;

6. Greenbelt Tributary 1, from its mouth at Blackhawk Creek to Sandhill Drive;

7. Greenbelt Tributary 2, from its mouth at Greenbelt Tributary 4 to about 600 feet above E. Milwaukee Street; 5 8. Greenbelt Tributary 3, from its mouth at Greenbelt Tributary 1 to about 1400 ft. above City of Janesville Corporate limits;

9. Greenbelt Tributary 4, from its mouth at Greenbelt Tributary 1 to about 350 ft.

above E. County Highway A;

10. Greenbelt Tributary 5, from its mouth at Greenbelt Tributary 4 to about 650 ft.

above N. State Highway 14;

11. Markham Creek, from its mouth at the Rock River to about 2200 ft. above W.

Hanover Road;

12. Marsh Creek, from its mouth at the Rock River to County Highway H;

13. Morningside Tributary, from its mouth at Spring Brook (Janesville) to State Highway 14 (Humes Road);

14. Otter Creek, from the county boundary to Bowers Road;

15. Raccoon Creek, from the downstream county boundary to State Highway 81;

16. Rock River, within the county boundaries;

17. Saunders Creek, within the county boundaries;

18. Spring Brook (Beloit), from its mouth at Turtle Creek to 100 ft. above S. Clinton Corners Road;

19. Spring Brook (Janesville), from its mouth at the Rock River to the confluence with Blackhawk Creek;

20. Sugar River, within the county boundaries;

21. Turtle Creek, from its confluence with the Rock River to about 2 miles upstream of Johnson Road;

22. Unnamed Tributary 1 to Raccoon Creek, from its mouth at Raccoon Creek to Beloit-Newark Road;

23. Unnamed Tributary 2 to Raccoon Creek, from its mouth at Unnamed Tributary 1 to Raccoon Cree k to Beloit-Newark Road;

24. Unnamed Tributary 1 to Rock River, from its mouth at the Rock River to County Highway G;

25. Unnamed Tributary 1 to Turtle Creek, from its mouth at Turtle Creek to Elm Drive; 26. Unnamed Tributary 2 to Turtle Creek, from its mouth at Turtle Creek to County Highway J;

27. Unnamed Tributary to Blackhawk Creek, from its mouth at Blackhawk Creek to N. Tarrant Road;

28. Unnamed Tributary to East Fork Raccoon Creek, from its mouth at East Fork Raccoon Creek to Beloit-Newark Road;

29. Unnamed Tributary in Turtle Township, from the state boundary to about 400 ft below S. Clinton Cor ners Road;

30. Yahara River, within the county boundaries.

The flooding sources studied by limited detailed methods are listed below:

1. Lenigan Creek, from its mouth at the Rock River to about 0.9 mile above City of Beloit Corporate limits;

2. Lenigan Creek Tributary 1, from its mouth at Lenigan Creek to about 250 ft. below the City of Beloit Corporate limits; 6 3. Lenigan Creek Tributary 2, from its mouth at Lenigan Creek to about 0.6 mile above McKinley Avenue;

4. Milton Ditch, from W. High St reet to State Highway 26;

5. Philhower Road Tributary, from its confluence with the Rock River to its confluence with Turtle Creek;

6. Unnamed Clinton Tributary, from about 700 ft. above Village of Clinton Corporate limits to confluence with S outhern Branch at railroad tracks;

7. Unnamed Clinton Tributary Southern Branch, from about 150 ft. above Village of Clinton Corporate limits to confluence with Clinton Tributary at railroad tracks;

8. Unnamed Tributary 2 to Rock River, from its mouth at the Rock River to W.

High Street;

9. Unnamed Tributary in Union Townshi p, from Union Township southern limits to just south of County Highway C Approximate analyses were used to study those areas having low development potential or minimal flood hazards. This was done by overlaying effective zone A floodplains over 10-foot contours to approximate flood elevations. These approximated elevations were then laid over year 2000 terrain data for a revised flood boundary. The scope and methods of study were proposed to, and agreed upon, by FEMA and the various affected communities.

2.2 Community

Description

Rock County, located in south-central Wisconsin, is bordered on the west by Green County, on the north by Dane and Jefferson Counties, on the east by Walworth County, and on the south by Winnebago and Boone Counties in Illinois. Rock

County includes the incorporated areas of F ootville, Evansville, Beloit, Janesville, Edgerton, Clinton, and Milton. Rock County's present boundaries were established in 1838. Prior to 1836 the county was a portion of Milwaukee County. Rock County derived its name from the Rock River which the French named "Riviere de la Roche".

Rock County has experienced a general increase in population since 1850 when there were 20,750 residents. By 1880 there were 43,220 residents, 113,913 by

1960, 131,970 by 1970, 140,103 in 1990 and 152,307 re sidents in 2000. Interstate Highway 90 is the major north-south highway.

Joseph Thiebeau, a French-Canadian fur trader, was the first white man to come to the county in 1824. The Rock River valley wa s under control of a number of Indian tribes until the end of the Black Hawk War in 1832. Following the end of Indian control, permanent settlement began to appear with all the present towns being organized by 1849. Wheat was the first stab le crop to be grown in the county; however, due to disease and soil depletion th e wheat production decreased, with increased acreage being devoted to oats, hay, and corn. The main farm enterprise in Rock County is dairying with the rais ing of beef cattle becoming increasingly 7 important. Important crops in the count y are field and swee t corn, hay, oats, soybeans, and peas. In addition to farming, Janesville and Beloit have become manufacturing centers for machinery and automobiles.

The climate of Rock County is classified as continental, with long cold winters and warm humid summers. The county has record ed an average annua l precipitation of 33 inches, which includes a moderate wi nter snowfall. Approximately 60 percent of this precipitation occurs within the five month period from May to September. Thunderstorms occur on the average of 40 times a year. The total annual snowfall has ranged from less than 10 inches to more than 65 inches. Prevailing winds are from the south in the summer and from the west during the winter months. The average wind speed during the windiest months (March, April, and November) is 12 miles per hour. The extreme temperatures recorded are -27 degrees Fahrenheit (F.) and 100 degrees F., exhibiting extreme seasonal variations.

Rock County is underlain entirely by sedimentary sandstones and limestone. The

county is divided into three physiographic regions. The northern region is composed of hills and kettles, the resu lt of glacial deposition. The central and southeastern portions of the county are typi fied by a flat glacial outwash plain. The southwestern corner of the county experienced less glacial activity, which is evidenced by deep valleys cut in sandstone ridges. A majority of the county's river and stream valleys are filled with thick deposits of alluvial sand and gravel. A majority of the soils in Rock County are a result of glacial activity. The county is generally typified by a surface layer of silt loam or loam underlain by glacial till or stratified sand and gravel outwash materials. The exception is the southwest region where shallow surface layers of loam or sandy loam overlay the bedrock

Rock County is drained entirely by the Rock River and its tributaries. The Rock River's major tributaries are the Yahara River, the Sugar River, Raccoon Creek and Turtle Creek. The Yahara River and its major tributary, Badf ish Creek, drain the northwestern corner of the county along Allen and Marsh Creeks. The Sugar River, Raccoon Creek, and their tri butaries drain the southwes tern region of the county.

Raccoon Creek confluences with the Sugar River in Illinois which in turn empties into the Rock River. The southeastern portion of the county is drained by Turtle Creek, which confluences with th e Rock River in South Beloit.

The floodplains include residential, commercial, industrial, recreational, and agricultural developments. The river floodplains, in general, follow the natural valley limits.

2.3 Principal

Flood Problems

The streams and rivers in Rock County ar e subject to flooding throughout the year; however, most flooding has occurred in the spring. These spring floods, the result of a combined snowmelt with moderate amounts of precipitation, can cause 8 flooding which is aggravated due to ice jams throughout the stream reaches. March is the most common month for peak annual discharges based on USGS stream flow records. Even though early spring is the most common time for flooding, the most

severe flood on record occu rred on Turtle Creek in la te April 1973. This flood was due to an intense period of rainfall over the Turtle Creek basin. It had an estimated return period of 150 years.

2.4 Flood

Protection Measures

There are a number of dams on the rive rs and creeks in Rock County; however, none of these dams were designed as fl ood control structures. The Rock Island COE has published a Phase I General Design Memorandum for a flood damage reduction project on Turtle Creek. That project was terminated due to a lack of economic justification. Rock County origin ally adopted a state approved floodplain zoning ordinance in November 1974. This Flood Insurance Study is expected to provide data that will be used to upda te the existing zoning ordinance. A levee system is located on the southwest flood plain of the Sugar River from the State Boundary to about one mile upstream of Nelson Road and on the northeast side from about two miles downstream of Nelson Road to about one mile upstream of Nelson Road. These levees will not provide any protection from the 100-year flood. 3.0 ENGINEERING METHODS For the flooding sources studied by detailed methods in the community, standard hydrologic and hydraulic study methods were used to determine the flood hazard data required for this study. Flood events of a magnitude that are expected to be equaled or exceeded once on the average during any 10-, 50-, 100-, or 500-year period (recurrence interval) have been selected as having special significance for floodplain management and for flood insurance rates. These events, commonly termed th e 10-, 50-, 100-, and 500-year floods, have a 10-, 2-, 1-, and 0.2-percent chance, re spectively, of being equaled or exceeded during any year. Although the recurrence interval represents the long-term, average period between floods of a specific ma gnitude, rare floods could occur at short intervals or even within the same year. The risk of experiencing a rare flood increases when periods greater than 1 year are considered. For example, the risk of having a flood

that equals or exceeds the 1-percent-annual-chance (100-year) flood in any 50-year period is approximately 40 per cent (4 in 10); for any 90-year period, the risk increases to approximately 60 percent (6 in 10). The an alyses reported herein reflect flooding potentials based on conditions existing in the community at the time of completion of this study. Maps and flood elevations will be amended periodically to reflect future changes.

3.1 Hydrologic

Analyses

9 Hydrologic analyses were carried out to establish peak discharge-frequency relationships for each flooding source studied by detailed methods affecting the community.

Precountywide Analyses Discharge values for the Yahara River at the Rock-Dane county line were taken from the discharge-frequency curve for the Stebbinsville Dam supplied by the USGS. Discharges downstream of the dam to the Badfish Creek confluence were based on a drainage area-discharge relati onship for the Stebbinsville Dam. An analysis of Badfish Creek was made to determine its impact on Yahara River flood flows. The discharge-frequency curve for Badfish Creek was based on a statistical analysis of 11 years of record for the nonrecordi ng USGS gage (No. 5-4301) located four miles southwest of Stoughton using a log-Pearson Type III distribution, and on Conger's method. Final values indicated that Badfish Creek controls the flood discharges on the Yahara River downstream of its confluence. Discharges used in this study are a comb ination of peak discharges on Badfish Creek plus a portion of the Yahara River flow.

The Rock River was previously studied in Rock County by various governmental

agencies. The discharges used in these reports were not a dopted due to updated methods of determining discharges. Fre quency-discharge relationships for the USGS gage at Afton (No. 543001) with a record from 1914 to present, located on the right bank in Afton and 1.1 miles upstream of Bass Creek, were computed by the log-Pearson Type III distribution. Discharges used were the result of

coordination between the States of Wisconsin and Il linois and FEMA. Frequency-discharge curves for other locations on the Rock River were determined by a drainage area comparison to the Afton gage.

Discharge values for Otter, Marsh, and Bass Creek downstream of S. Footville Road were determined by procedures set forth in Project Formulation Hydrology, Technical Release No. 20 (TR-20). Supporting computations were made using Conger's method and a peak discharge-drainage area comparison to Turtle Creek.

Discharges for Allen Creek were computed using the TR-20 method as reported in a Flood Hazard Study for the City of Evansville, Wisconsin.

Flood discharges for Turtle Creek are based on a statistical analysis of the USGS

recording station (No. 5-4315) with a period of record from 1939 to the present, located on the left bank of Turtle Creek immediately downstream of the State Highway 140 bridge, 2.7 miles north of Clinton. This analysis, using the log-Pearson Type III distribution, was the result of coordination between the States of Wisconsin and Illinois and was accepted by FEMA. The resulting discharge does not agree with previously accepted values due to the different methodology used and the inclusion of the April 1973 flood.

Discharge-frequency curves at other locations were based on a drainage area comparison to the Clinton gage.

10 Unnamed Tributary No. 1 to Turtle Creek and Unnamed Tributary No. 2 to Turtle Creek were studied by Conger's method, TR-20, and discharge-drainage area comparisons. The final discharge-frequency curves are a composite of these three methods. Discharges for the Sugar River are based on a statistical analysis of the USGS recording station (No. 5-4365) with a period of record from 1914 to the present, located on the left bank of the Sugar River, 1.2 miles southwest of Brodhead. The

adopted discharge-frequency relationship wa s the result of coordination between Wisconsin and Illinois and was accepted by FEMA. Discharges for the study were based on a drainage area-discharge comparison to the Brodhead gage.

Discharges for Raccoon Creek and its two unnamed tributaries were determined by

a TR-20 model. Supporting calculations were made by Conger's method and a discharge-drainage area comparison.

Discharges for the East Fork Raccoon Cr eek and its unnamed tributary were based on a TR-20 model. Supporting computations included a drainage area comparison to a USGS gage (No. 5-4372) with a period of record from 1958 to the present located on the unnamed tributary and Conger's method.

Flood discharges for Spring Brook Beloit and Spring Brook Janesville were based on the results of Conger's method, a drainage comparison, and the U.S. Department of Agriculture, Soil Conservation Service (SCS) method.

The hydrologic analyses for Allen Creek to establish the peak discharge relationships for floods of the 10-, 50-, 100-, and 500-year recurrence intervals were made utilizing the SCS hydrology computer program TR-20. The principal factors considered in this method are soil types, land use, slope of terrain, channel length and rainfall distributi on. Four rainfalls were used in the model. Rainfall data for the 10-, 500, 100-, and 500-ye ar return frequency stor ms were obtained from the U.S. Weather Bureau Technical Paper No. 40. The resulting flows computed in the TR-20 model were compared to U.

S. Geological Survey (USGS) gauged watersheds of similar characteristics and were determined to match reasonably well. Revised Analyses for this Countywide FIS The hydrologic analyses for Bass Creek upstream of S. Footville Road, Blackhawk Creek upstream of State Highway 14, Fish er Creek, Greenbelt Tributaries 1-5, Markham Creek, Morningside Tributary, Sa unders Creek, Spring Brook (Beloit), Unnamed Tributary 1 to Rock River, Unnamed Tributary to Blackhawk Creek and Unnamed Tributary in Turtle Township and all limited detail studies (outlined in section 2.1) were done using the Wiscons in DNR Hydrology Tool extension in

ArcView 3.2 and HEC-HMS 2.2.2.

11 The Loss rate method/abstraction used was SCS CN. CN data was based on WiscLand grid. The SCS Unit hydrograph/TR-55 flow path segment method was used. Channel properties were estimated from the 2000 digital terrain model (DTM). Manning's N values were deri ved from the 2000 orthophoto. Muskingum

Cunge was used for routing and channels were based off of the 2000 DTM.

Rainfall distribution curve was developed by SEWRPC for all southeast Wisconsin Counties. Rock County was on the fringe of this region, but it was determined that the curve still applied as the curve included gauge data from Rock County.

24-, 12-, 6- and 3-hour storm durations were run in HEC-HMS to determine the storm with the highest peak flow. The 24-, 12-, 6- and 3-hour rainfall for 10-, 50- and 100-year storms were obtained from th e U.S. Weather Bureau Technical Paper No. 40. The 500-year rainfall total was extr apolated based on th e previous totals.

There was a storm on August 5, 1998 that approximately measured as a 1 percent annual chance rainfall event.

This event was entered into the HEC-HMS models to compare the flow to the 1 percent annual chance peak flow. The values compared favorably.

The stream gauge on a tributary to Fish er Creek (#5430403) was used to verify Fisher Creek's peak value. This was the only stream gauge on any of the studies were new hydrology was performed.

Peak discharge-drainage area relationships for Rock County are shown in Table 1.

Table 1 - Summary of Discharges Peak Discharges (cubic feet per second) Flooding Source and Location Drainage Area (square miles) 10-Percent-Annual-Chance 2-Percent-Annual-Chance 1-Percent-Annual-Chance 0.2-Percent-Annual-Chance ALLEN CREEK Downstream of North State Highway 213 795 1,340 1,600 2,300 Approximately 1 mi. above North State Highway 213 765 1,290 1,545 2,230 Approximately 2.3 mi. above North State Highway 213 730 1,230 1,475 2,150 Halfway between E Church St. & Water St.

675 1,145 1,375 2,050 At Lake Leota Dam 590 1,010 1,215 1,770 BASS CREEK State Highway 11 14.0 2,225 3,537 4,362 6,283 Old State Highway 11 13.3 2,169 3,439 4,240 6,097 Dorner Road 9.3 1,705 2,649 3,234 4,553

12 Table 1 - Summary of Di scharges - continued Peak Discharges (cubic feet per second) Flooding Source and Location Drainage Area (square miles) 10-Percent-Annual-Chance 2-Percent-Annual-Chance 1-Percent-Annual-Chance 0.2-Percent-Annual-Chance BLACKHAWK CREEK State Highway 14 32.7 2,457 4,126 5,152 7,042 Confluence with Unnamed Trib to Blackhawk Creek 31.6 2,409 4,037 5,035 6,868 250' upstream of County Highway MM 14.2 1,132 1,899 2,364 3,205 1/2 mile upstream of Milton Shopeire Road at Tributary 12.5 995 1,675 2,081 2,819 E FORK RACCOON CREEK Wisconsin-Illinois State line 17.0 2,150 3,450 4,100 5,700 Above Unnamed Tributary to East Fork Raccoon Creek 10.8 1,450 2,300 2,750 3,900 Spring Creek Road 6.6 1,050 1,650 1,920 2,700 FISHER CREEK At mouth 5.9 861 1,491 1,817 2,831 Upstream of Unnamed Trib. 4.0 621 1,047 1,270 1,935 Rockport Road 3.5 540 914 1,099 1,646 State Highway 11 2.6 535 890 1,074 1,577 Downstream of Mineral Point Road 1.7 408 656 774 1,112 Upstream of Mineral Pt. Rd. 0.8 206 331 390 560 GREENBELT TRIBUTARY 1 Confluence with Greenbelt Tributary 4 4.5 804 1,212 1,453 1,983 Confluence with Unnamed 0.7 129 195 234 319 Tributary State Highway 14 0.4 61 93 112 154 GREENBELT TRIBUTARY 2 At mouth 0.8 140 214 258 356 GREENBELT TRIBUTARY 3 At mouth 0.4 76 113 135 181 GREENBELT TRIBUTARY 4 At mouth 2.9 516 778 934 1,278 Below confluence with Greenbelt Tributary 2 1.9 336 509 612 838 Above confluence with Greenbelt Tributary 2 1.0 213 320 383 522 GREENBELT TRIBUTARY 5 At mouth 1.1 183 277 333 456 MARKHAM CREEK At mouth 10.2 1,210 1,922 2,374 3,409 Confluence with Unnamed Tributary 8.8 1,158 1,811 2,230 3,187 Railroad Bridge 5.8 846 1,315 1,620 2,288 State Highway 11 3.8 583 898 1,087 1,496 N. Willowdale Road 2.7 387 604 734 1,015 Mineral Point Road 1.1 201 304 366 501 13 Table 1 - Summary of Di scharges - continued Peak Discharges (cubic feet per second) Flooding Source and Location Drainage Area (square miles) 10-Percent-Annual-Chance 2-Percent-Annual-Chance 1-Percent-Annual-Chance 0.2-Percent-Annual-Chance MARSH CREEK At mouth 30.8 1,800 2,900 3,470 4,900 State Highway 184 22.0 1,550 2,500 2,950 4,150 MORNINGSIDE TRIBUTARY At mouth 14.8 2,023 3,109 3,799 5,319 Confluence with Unnamed Tributary 6.2 891 1,412 1,738 2,444 Confluence with Unnamed Tributary 5.8 812 1,315 1,614 2,260 Mt. Zion Avenue 4.8 666 1,069 1,305 1,823 State Highway 14 2.8 388 608 738 1,025 OTTER CREEK At Rock County limits 50.3 2,150 3,550 4,250 6,000 RACCOON CREEK Wisconsin-Illinois State line 27.8 2,750 4,500 5,350 7,700 Approximately 1.3 miles above County Highway H 16.4 1,600 2,600 3,150 4,400 State Highway 81 12.1 1,400 2,300 2,700 3,900 ROCK RIVER Wisconsin-Illinois State line 3,450 11,500 15,300 16,900 20,100 At Afton Gage 3,340 10,900 14,500 16,000 19,000 At Monterey Dam 3,310 10,800 14,300 15,800 18,800 Above confluence with Markham Creek 3,280 10,600 14,100 15,600 18,500 At Centerway Dam 3,240 10,400 13,800 15,300 18,200 West State Highway 14 3,190 10,200 13,500 14,900 17,800 Approximately 3.7 miles above W State Highway 14 3,170 10,100 13,400 14,800 17,600 Below confluence with Yahara River 3,120 9,970 13,100 14,500 17,200 Above confluence with Yahara River 2,580 7,480 9,950 11,000 13,000 Outlet of Lake Koshkonong 2,500 7,140 9,500 10,500 12,400 SAUNDERS CREEK At mouth 42.0 918 1,580 2,016 2,930 Edgerton Southern Corporate Limits 41.7 919 1,582 2,018 2,934 Confluence near Stoughton Road 38.3 937 1,615 2,059 3,005 Dane - Rock County line 26.8 828 1,382 1,751 2,548 SPRING BROOK (BELOIT)

At mouth 15.0 1,280 1,933 2,332 3,227 550' above E. Lawn Rd. 14.2 1,235 1,864 2,227 3,145 Interstate Highway 90 9.1 752 1,309 1,644 2,388 Railroad at corporate limits 7.3 691 1,221 1,536 2,245 At trib 1/4 mile below Gustafson Road 5.3 586 1,072 1,320 1,911 At trib 0.65 mile below Gustafson Road 3.8 521 906 1,094 1,517 14 Table 1 - Summary of Di scharges - continued Peak Discharges (cubic feet per second) Flooding Source and Location Drainage Area (square miles) 10-Percent-Annual-Chance 2-Percent-Annual-Chance 1-Percent-Annual-Chance 0.2-Percent-Annual-Chance SPRING BROOK (JANESVILLE)

At mouth 48.74 3,165 5,250 6,075 7,300 Downstream of East Racine Street 46.26 3,080 4,960 5,920 7,125 Upstream of East Racine Street 44.06 2,950 4,760 5,675 6,840 At Ruger Avenue 42.83 2,900 4,700 5,590 6,740 SUGAR RIVER Wisconsin-Illinois State line 696 11,400 20,600 25,500 39,000 Below confluence with Taylor Creek 658 10,800 19,500 24,100 36,900 Above confluence with Taylor Creek 605 10,500 18,900 23,400 35,800 TURTLE CREEK At mouth 247 6,500 12,400 15,400 24,500 State Highway 15 217 5,980 11,400 14,200 22,500 Above Unnamed Tributary 1 to Turtle Creek 210 5,860 11,200 13,900 22,100 USGS gage at Clinton 202 5,730 10,900 13,600 21,600 Below Little Turtle Creek 184 5,220 9,900 12,400 19,700 Above Little Turtle Creek 116 3,290 6,300 7,800 12,400 UNNAMED TRIBUTARY 1 TO RACCOON CREEK At mouth 6.1 1,300 2,160 2,580 3,700 At State Highway 81 3.3 730 1,200 1,450 2,050 At Beloit-Newark Road 1.0 330 560 670 980 UNNAMED TRIBUTARY 2 TO RACCOON CREEK At mouth 2.4 580 960 1,150 1,650 UNNAMED TRIBUTARY 1 TO ROCK RIVER At mouth 18.4 2,255 3,473 4,205 5,813 Above State Highway 51 17.9 2,232 3,415 4,129 5,692 Field crossing 1/4 mile above State Highway 51 17.2 2,170 3,308 3,992 5,492 450' below County Highway G 16.7 2,113 3,214 3,876 5,331 County Highway G 15.8 2,000 3,038 3,662 5,036 UNNAMED TRIBUTARY 1 TO TURTLE CREEK At mouth 7.8 840 1,380 1,650 2,350 Town Road, S25 T2N R13E 4.7 620 1,100 1,330 2,000

15 Table 1 - Summary of Di scharges - continued Peak Discharges (cubic feet per second) Flooding Source and Location Drainage Area (square miles) 10-Percent-Annual-Chance 2-Percent-Annual-Chance 1-Percent-Annual-Chance 0.2-Percent-Annual-Chance UNNAMED TRIBUTARY 2 TO TURTLE CREEK At mouth 3.8 490 840 1,000 1,500 Above confluence with Unnamed Southern Trib.

2.4 360 575 680 950 At dam upstream of Buss Rd 1.2 230 420 520 810 UNNAMED TRIBUTARY TO BLACKHAWK CREEK Below Milton Shopiere Road 15.8 1,212 2,026 2,530 3,462 South of County Highway A 14.9 1,134 1,902 2,377 3,259 500' below Tarrant Rd 12.6 1,001 1,647 2,052 2,807 UNNAMED TRIBUTARY TO E FORK RACCOON CREEK At mouth 4.8 820 1,310 1,550 2,200 At Beloit-Newark Road 1.6 400 640 760 1,060 UNNAMED TRIBUTARY IN TURTLE TOWNSHIP Wisconsin-Illinois State line 6.5 643 1,051 1,307 1,908 East County Highway P 5.8 604 990 1,230 1,781 Confluence with Tributary 4.8 537 859 1,057 1,518 Confluence with Tributary 4.0 490 762 925 1,313 East County Highway P 3.3 424 643 795 1,126 East County Highway P 1.4 239 376 455 630 S. Clinton Corners Road 0.6 117 178 214 293 YAHARA RIVER At mouth 537 2,200 3,800 4,700 7,000 Dane-Rock County line 430 710 910 990 1,180 The City of Janesville Flood Insuran ce Study Hydrologic Summary produced by Owen Ayers & Associates in 1981 has flow values for portions of Fisher Creek, Markham Creek, Morningside Tributary and Greenbelt Tributaries 1-5 because they were previously approximate zones. These values compared favorably to the

HEC-HMS peak flow values attained in 2005.

Stillwater elevations for Lake Koshkonong are shown in Table 2.

Table 2 - Summary of Stillwater Elevations Water Surface Elevations (Feet NGVD29

1) Flooding Source 10-Percent-Annual-Chance 2-Percent-Annual-Chance 1-Percent-Annual-Chance 0.2-Percent-Annual-Chance Lake Koshkonong 781.8 783.6 784.6 785.8 1 National Geodetic Vertical Datum of 1929

3.2 Hydraulic

Analyses Analyses of the hydraulic characteristics of flooding from the sources studied were carried out to provide estimates of the elevations of floods of the selected recurrence intervals. Users should be aware that flood elevations shown on the Flood Insurance Rate Map (FIRM) repres ent rounded whole-foot elevations and may not exactly reflect the elevations shown on the Flood Profiles or in the Floodway Data Table in the FIS report. Flood elevations shown on the FIRM are primarily intended for flood insuran ce rating purposes. For construction and/or floodplain management purposes, users are cautioned to use the flood elevation data presented in this FIS report in conjunction with the data shown on

the FIRM.

Precountywide Analyses UNINCORPORATED AREAS There were 471 field measured cross sections for the Rock County study, of which 183 were supplied by the COE and the USGS.

The distances between cross sections were obtained from enlarged 1:24000 scale USGS quadrangle maps. Locations of selected cross sections us ed in the hydraulic analyses are shown on the Flood Profiles. For stream segments for which a floodway was computed (Section 4.2), selected cr oss section locations are also shown on the Flood Boundary and Floodway Map.

The channel and overbank roughness factors (Manning's "n") were assigned on the

basis of field inspection. These range from 0.028 to 0.05 in the channel and 0.04 to 0.15 in the overbanks.

The hydraulic model for Yahara Rive r reflects existing conditions. The powerhouse and dam on the Yahara River, near Fulton, are presently being modified or have future plans for m odification. The 18 wicket gates at the powerhouse are operable; howev er, they are blocked off from flow and were not considered in developing outflow rating curves from the lake. The powerhouse may be fully functional within a year's time, thus affecting the water-surface upstream of the dam. An area of divided flow exists at the Fulton Dam. A small portion of the 100-year flow separates from the main flow and is diverted east of the Fulton Dam through a divergence channel and then back into the Yahara River.

Flows through the divergen ce channel were taken into account in the hydraulic model. A levee located along the northern side of the channel prevents the diverging flow from overflowing into the flood plain. Hydraulic data upstream of the Stebbinsville Dam were obtained from the Dane County Flood Insurance Study. The river miles for the Yahara River do not agree with pr evious studies due to updated mapping.

16 Water-surface elevations were computed using the COE HEC-2 step-backwater computer program. Profiles were determ in ed for the 10-, 50-, 100-, and 500-year floods. Water-surface elevations for the other detailed study streams were started at bank full elevations at the main stem.

Starting water-surface elevations on Blackhawk Creek are the corresponding elevations of Spring Brook at the confluence point.

The starting water-surface elevations for Sugar River match the elevations at the upstream limit of the Winnebago Count y, Illinois, Flood Insurance Study.

Turtle Creek was studied in combination a nd coordinated with th e Beloit and South Beloit Flood Insurance Studies. Starting water surface elevations were taken from the Beloit Flood Insurance Study. Hydraulic data were also coordinated with the Rock Island COE. Due to the level of detail and lack of data, a possible overflow

bypass across Creek Road to the Rock River was not studied by detailed methods. All flow was assumed to continue dow nstream on Turtle Creek. Flood profiles were drawn showing computed water-surface elevations for floods of the selected

recurrence intervals.

Hydraulic characteristics of stream reaches studied by approximate methods were determined from flood prone area maps and by normal depth analysis.

The hydraulic analyses for Allen Creek were taken from the Flood Hazard Study for the City of Evansville. The flood profiles taken from the report were computed using the SCS WSP-2 computer program.

CITY OF JANESVILLE

Cross section data and structure data necessa ry for this analysis were developed by field survey and bridge data from the COE, Rock Island District, files, City of Janesville data, and use of topographic maps at a scale of 1:2400 with a contour interval of 2 feet for overbank areas.

The procedures used for calculating h ead losses through bridges and other structures causing constrictions to flow allowed the identification of significant backwater producing structures.

Locations of selected cross sections us ed in the hydraulic analyses are shown on the Flood Profiles. For stream segments for which a floodway was computed (Section 4.2), selected cr oss section locations are also shown on the Flood Boundary and Floodway Map.

Overbank roughness factors (Manning's "n") for the streams were estimated using engineering judgment and high water data from photographs taken at cross section locations and field observations. C hannel roughness factors were estimated by 17 comparison with table values and the step-by-step procedure for channel "n" values in Chow's text on open-channel hydraulics and historical high water data. These ranged from 0.028 to 0.033 for channel and 0.04 to 0.09 for overbanks on the Rock

River. For Spring Brook and Blackhawk Creek, which are hydraulically continuous, these values varied from 0.035 to 0.070 in the channel and 0.050 to 0.14 for overbanks.

Starting water-surface elevations on Spring Brook were determined using the corresponding 10-year fr equency water surf ace on the Rock Rive

r. Starting water-surface elevations on Blackhawk Creek are the elevation of Spring Creek at the confluence point. Water surface elevations were computed using the COE HEC-2 step-backwater computer program

CITY OF BELOIT Stream cross sections and structural data for all streams studied in detail were obtained from field survey and the Rock Island District COE.

Roughness coefficients (Manning's "n"), us ed in the hydraulic analyses, were based on field observations and engineering judgme nt, and were provided by the Rock Island District COE. The "n" values for the Rock River channel range from 0.03 to 0.045 and the overbanks range from 0.055 to 0.085. The "n" value for the Turtle Creek channel is 0.035 and the overbanks range from 0.05 to 0.075. The "n"'

values for the Spring Brook channel range from 0.03 to 0.07 and the overbanks range from 0.06 to 0.16.

Hydraulic information for Spring Brook was obtained from the Rock County, Wisconsin Flood Insurance Study.

Starting water-surface elevations for the Rock River and Turtle Creek were based on downstream flood profiles obtained from the South Beloit Flood Insurance Study. Starting water surface elevations for Spring Brook were obtained using the slope-area method. Water surface profiles for the various discharge-frequencies were determined using the COE HEC-2 computer program. Flood profiles were drawn showing computed water-surface el evations for floods of the selected recurrence intervals.

CITY OF EDGERTON The cross sections used for the study were obtained from 2-foot contour maps made available by the City.

All bridge elevation data and structural geometry for the backwater analyses of the

flooding source studied were obtained by fi eld surveys by the Study Contractor.

The channel soundings were also obtained by field measurement.

Channel roughness factors (Manning' s "n") used in the hydraulic computations were chosen by engineering judgment and based on field observations of the 18 streams and floodplain areas. Roughness values for the main channel of Saunders Creek range from 0.035 to 0.04 with fl oodplain roughness values ranging from 0.06 to 0.11 for all floods.

CITY OF EVANSVILLE Cross section data for Allen Creek were obtained from field survey measurem ents. All bridges and culverts were field surveyed to obtain elevation data and structural geometry.

Comparing the 100-year flood elevation with the contour maps, it was discovered that flow would occur over the Chicago a nd North Western railroad tracks toward the east in an area downstream of Main Street. The water that flows over the tracks does not re-enter Allen Creek until it joins the flow from a drainage basin from the east and enters Allen Creek south of the city. The divided flow was subtracted from the main flow in the channel.

Revised Analyses for this Countywide FIS All new hydraulic models were done by Gannett Fleming using HEC-RAS 3.1.3.

County-wide floodplain delinea tions were also created by Gannett Flem ing using year 2000 Rock County digital terrain data and ArcGIS 9.1.

The distances between all cross sect ions were obtained by calculating the distance along the stream centerline digitized from the 2000 Rock County orthophoto.

Locations of selected cross sections used in the hydraulic analyses are shown on the Flood Profiles. For stream segments for which a floodway was computed (Section 4.2), selected cross section locations are also shown on the Flood Insurance Rate Map.

The channel and overbank roughness factors (Manning's "n") for new studies

were assigned on the basis of inspection of the 2000 Rock County orthophoto.

All studies that were redelineated used the previous model's "n" values.

For all new detailed studies (Fisher Creek, Markham Creek, Morningside Trib, Greenbelt Tribs 1-5, Unnamed Trib to Blackhawk Creek, Unnamed Trib 1 to Rock River, Unnamed Trib in Turtle Township and portions of Saunders Creek, Spring

Brook-Beloit, Bass Creek and Blackhawk Cr eek) all bridges and culverts were field surveyed to obtain elevation data a nd structural geometr

y. For the following redelineated studies, all bri dges in the existing model were verified as the current existing bridges and the 2000 orthophoto was inspected to search for new bridges since the model was created: Rock Rive r, Raccoon Creek, Ea st Fork Raccoon Creek, Unnamed Tribs 1 & 2 to Raccoon Creek, Unnamed Trib to East Fork Raccoon Creek and the remaining portions of Saunders Creek, Spring Brook-Beloit 19 and Allen Creek. If the DOT had plans for a new bridge, it was entered into the HEC-RAS 3.1.3 model and re-run to get new water surface elevations.

There were no new hydraulic models create d for; Yahara River, Otter Creek, Marsh Creek, Turtle Creek, Unnamed Tribs 1 & 2 to Turtle Creek, Sugar River, Spring Brook-Janesville, the downstream-most 1.25 miles of Blackhawk Creek, upstream of the Lake Leota Dam on Allen Creek and below S. Footville Rd. on

Bass Creek. The old FIS profile was taken as is and those elevations were mapped on new terrain data. This was done largely for the fact that the original model could not be located on most of these. On the few that an original model could be found, complications including matching the cross sections to new terrain and time

constraints were used as the reason why the model was not updated. The only exception to this is that Fulton Dam was taken out of the profile of Yahara River since it has been removed since the last FIS.

The limited detail studies on Lenigan Cr eek, Lenigan Creek Tribs. 1 & 2, Philhower Road Trib., Unname d Clint on Trib., South Branch Unnamed Clinton Trib., Unnamed Trib. in Union Township, Milton Ditch and Unnamed Trib. 2 to Rock River were done in the same manne r in HEC-RAS 3.1.3 as the new detailed studies. The difference between these two types of studies was that the limited

detail studies' bridges were not surveyed into mean sea level (MSL). The bridges were measured in relative distances from the top of road.

The 10-year frequency water surface of the Rock River was used as the starting water surface for the following studies: Unnamed Trib. 1 to Rock River, Markham

Creek, Fisher Creek and Saunders Creek.

The 100-year frequency water surface elevation at the upstream end of the redelineate reach of Blackhawk Creek was used as the starting water surface elevation for the new detailed reach of Blackhawk Creek.

The 100-year frequency water surface elevation at the upstream end of the redelineate reach of Bass Creek was used as the starting water surface elevation for the new detailed reach of Bass Creek.

The 10-year frequency water surface of Blackhawk Creek was used as the starting water surface for Greenbelt Trib. 1 and Morningside Trib. Greenbelt Tribs. 1-5 were all entered in the same HEC-RAS model and Tribs. 2-5 starting water surface elevations are equal to the 100-year fr equency water surface of its receiving stream.

The Unnamed Trib. to Blackhawk Creek was included in the same HEC-RAS model as Blackhawk Creek, so its starting water surface elevation is equal to the 100-year frequency water surface of Bl ackhawk Creek at the confluence.

20 Spring Brook (Beloit) has a starting water surface elevation equal to the 10-year frequency water surface of Turtle Creek.

Starting water surface elevation for Unnamed Trib. in Turtle Township was done by norma l depth calculation.

Locations of selected cross sections used in the hydraulic analyses are shown on

the Flood Profiles (Exhibit 1). For stream segments for which a floodway was computed (Section 4.2), selected cross section locations are also shown on the FIRM (Exhibit 2).

The hydraulic analyses for this study were based on unobstructed flow. The flood elevations shown on the Flood Profiles (Exhibit 1) are thus considered

valid only if hydraulic structures rema in unobstructe d, operate properly, and do not fail.

3.3 Vertical

Datum All FIS reports and FIRMs are referenced to a specific vertical datum. The vertical datum provides a starting point against which flood, ground, and structure elevations can be referenced and compared. Until recently, the standard vertical datum in use for ne wly created or revised FIS reports and FIRMs was the National Geodetic Vertical Datum of 1929 (NGVD29). With the finalization of the North American Vertical Datum of 1988 (NAVD88), many FIS reports and FIRMs are being prepar ed using NAVD88 as the referenced vertical datum.

All flood elevations shown in this FIS report and on the FIRM are referenced to

NGVD29. Structure and ground elevations in the community must, therefore, be referenced to NGVD29. It is im portant to note that adjacent communities may be referenced to NAVD88. This may result in differences in Base Flood Elevations (BFEs) across the corporate limits between the communities.

For more information on NAVD88, s ee the FEMA publication entitled Converting the National Flood Insurance Program to the North American Vertical Datum of 1988 (FEMA, June 1992), or cont act the Vertical Network Branch, National Geodetic Survey, Coast and Geodetic Survey, National Oceanic and Atmospheric Administration, Silver Spring, Maryland 20910 (Internet address http://www.ngs.noaa.gov).

Temporary vertical monuments are often established during the preparation of a flood hazard analysis for the purpose of establishing local vertical control. Although these monuments are not shown on the FIRM, they may be found in the Technical Support Data Notebook associated with the FIS report and FIRM 21 for this community. Interested individuals may contact FEMA to access these data.

4.0 FLOODPLAIN

MANAGEMENT APPLICATIONS The NFIP encourages State and local governments to adopt sound floodplain management programs. Therefore, each FIS provides 1-percent-annual-chance (100-year) flood elevations and de lineations of the 1- and 0.2-percent-annual-chance (500-year) floodplain boundaries and 1-percen t-annual-chance floodway to assist communities in developing floodplain management measures. This information is presented on the FIRM and in many components of the FIS report, including Flood Profiles, Floodway Data Table, and Summary of Stillwater Elevations Table. Users should reference the data presented in the FIS report as well as additional information that may be available at the local map repository before making flood elevation and/or floodplain boundary determinations.

4.1 Floodplain

Boundaries To provide a national standard without regional discrimination, the 1-percent-

annual-chance flood has been adopted by FEMA as the base flood for floodplain management purposes. The 0.2-percent-annual-chance flood is employed to indicate additional areas of flood risk in the community. For each stream studied by detailed methods, the 1- and 0.2-pe rcent-annual-chance floodplain boundaries have been delineated using the flood elevations determined at each cross section.

Between cross sections, the boundaries we re delineated based on the 2000 Rock County digital terrain model.

The 1- and 0.2-percent-annual-chance floodplain boundaries are shown on the FIRM (Exhibit 2). On this map, the 1-percent-annual-chance floodplain

boundary corresponds to the boundary of the areas of special flood hazards (Zones A and AE), and the 0.2-percen t-annual-chance floodplain boundary corresponds to the boundary of areas of moderate flood hazards. Small areas within the floodplain boundaries may lie above the flood elevations but cannot be shown due to limitations of the map s cale and/or lack of detailed topographic data.

For the streams studied by approximate methods, only the 1-percent-annual-chance floodplain boundary is s how n on the FIRM (Exhibit 2).

22 23 4.2 Floodways Encroachment on floodplains, such as structures and fill, reduces flood-carrying capacity, increases flood he ights and velocitie s, and increases flood hazards in areas beyond the encroachment itself. One aspect of floodplain management involves balancing the economic gain from floodplain development against the resulting increase in flood hazard. For purposes of the NFIP, a floodway is used

as a tool to assist local communities in this aspect of floodplain management.

Under this concept, the area of the 1-pe rcent-annual-chance floodplain is divided into a floodway and a floodway fringe. The floodway is the channel of a stream, plus any adjacent floodplain areas, that must be kept free of encroachment so that the 1-percent-annual-chance flood can be carried without substantial increases in flood heights. Minimum Federal standards limit such increases to 1 foot, provided that hazardous velocities are not produced. The floodways in this study are presented to local agencies as minimum standards that can be adopted directly or that can be used as a basis for additional floodway studies.

The floodways presented in this FIS report and on the FIRM were computed for certain stream segments on the basis of equal-conveyance reduction from each side of the floodplain. Floodway widths were computed at cross sections.

Between cross sections, the floodway boundaries were interpolated. The results of the floodway computations have been tabulated for selected cross sections (Table3).

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River A 163.020 254 2,378 7.1 737.7 737.7 737.7 0.0 B 163.029 264 2,423 7.0 737.9 737.9 737.9 0.0 C 163.043 263 2,488 7.1 738.1 738.1 738.1 0.0 D 163.095 271 2,494 6.8 738.8 738.8 738.8 0.0 E 163.288 262 4,030 4.2 740.1 740.1 740.1 0.0 F 163.309 303 4,051 4.4 740.1 740.1 740.1 0.0 G 163.344 263 4,146 4.9 740.4 740.4 740.4 0.0 H 163.364 239 2,215 7.7 740.4 740.4 740.4 0.0 I 163.392 246 2,640 6.6 740.9 740.9 740.9 0.0 J 163.417 258 2,931 5.8 741.3 741.3 741.3 0.0 K 163.476 207 3,497 5.3 741.8 741.8 741.8 0.0 L 163.489 195 2,328 7.3 741.9 741.9 741.9 0.0 M 163.672 266 2,413 7.0 743.3 743.3 743.3 0.0 N 163.892 374 3,943 4.3 744.5 744.5 744.5 0.0 O 163.894 347 2,839 6.0 747.3 747.3 747.3 0.0 P 163.919 391 8,390 3.1 747.9 747.9 747.9 0.0 Q 163.945 630 4,200 4.0 747.9 747.9 747.9 0.0 R 163.955 682 2,696 6.3 747.9 747.9 747.9 0.0 S 163.971 716 2,797 6.0 747.9 747.9 747.9 0.0 T 164.011 593 4,641 3.7 748.3 748.3 748.3 0.0 U 164.045 535 8,343 2.4 748.5 748.5 748.5 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) V 164.080 505 8,368 2.4 748.5 748.5 748.5 0.0 W 164.541 851 8,107 2.1 748.7 748.7 748.7 0.0 X 164.937 690 11,569 2.1 748.9 748.9 748.9 0.0 Y 164.951 619 6,424 2.7 748.9 748.9 748.9 0.0 Z 164.975 896 6,444 2.7 748.9 748.9 748.9 0.0 AA 164.980 1,142 11,413 1.6 749.0 749.0 749.0 0.0 AB 165.327 1,084 9,510 1.8 749.1 749.1 749.1 0.0 AC 165.593 1,047 10,712 1.7 749.2 749.2 749.2 0.0 AD 166.327 803 8,023 2.2 749.4 749.4 749.4 0.0 AE 166.384 772 8,040 2.3 749.4 749.4 749.4 0.0 AF 166.401 737 8,854 2.1 749.5 749.5 749.5 0.0 AG 166.899 689 7,495 2.3 749.7 749.7 749.7 0.0 AH 167.352 841 8,323 2.1 749.9 749.9 749.9 0.0 AI 167.779 1,523 12,511 1.4 750.1 750.1 750.1 0.0 AJ 168.609 723 7,280 2.7 750.3 750.3 750.3 0.0 AK 169.034 470 6,805 3.6 750.8 750.8 750.8 0.0 AL 169.051 404 4,660 3.9 750.8 750.8 750.8 0.0 AM 169.082 391 4,714 3.6 750.9 750.9 750.9 0.0 AN 169.090 416 5,483 3.4 751.0 751.0 751.0 0.0 AO 169.536 577 5,192 4.3 751.7 751.7 751.7 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) AP 169.955 367 6,308 3.8 752.7 752.7 752.7 0.0 AQ 169.970 335 3,494 4.9 752.7 752.7 752.7 0.0 AR 170.002 395 3,534 4.8 752.8 752.8 752.8 0.0 AS 170.021 564 5,185 3.3 753.0 753.0 753.0 0.0 AT 170.692 1,018 8,297 2.1 753.8 753.8 753.8 0.0 AU 171.686 2,490 14,940 1.3 754.7 754.7 754.7 0.0 AV 172.252 1,989 11,416 1.6 755.1 755.1 755.1 0.0 AW 172.733 1,815 13,437 1.3 755.5 755.5 755.5 0.0 AX 173.675 364 4,539 3.5 756.4 756.4 756.4 0.0 AY 173.688 346 3,465 4.6 756.4 756.4 756.4 0.0 AZ 173.720 421 3,510 4.6 756.5 756.5 756.5 0.0 BA 173.737 449 11,761 2.8 756.7 756.7 756.7 0.0 BB 174.340 1,090 6,205 2.6 757.3 757.3 757.3 0.0 BC 175.232 509 4,677 3.4 758.5 758.5 758.5 0.0 BD 175.698 400 4,388 3.7 759.2 759.2 759.2 0.0 BE 175.748 406 4,358 4.0 759.2 759.2 759.2 0.0 BF 175.758 409 4,372 4.0 759.3 759.3 759.3 0.0 BG 175.904 512 5,563 3.0 759.6 759.6 759.6 0.0 BH 176.530 625 5,904 2.7 760.1 760.1 760.1 0.0 BI 177.058 468 8,165 2.7 760.5 760.5 760.5 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) BJ 177.634 491 5,352 3.1 761.1 761.1 761.1 0.0 BK 177.696 520 5,363 4.4 761.1 761.1 761.1 0.0 BL 177.728 549 5,663 4.4 761.2 761.2 761.2 0.0 BM 178.103 269 3,520 5.1 762.1 762.1 762.1 0.0 BN 178.377 659 6,371 2.5 762.7 762.7 762.7 0.0 BO 178.558 240 2,692 8.3 762.7 762.7 762.7 0.0 BP 178.580 216 2,525 7.0 763.1 763.1 763.1 0.0 BQ 178.599 192 2,532 7.6 763.1 763.1 763.1 0.0 BR 178.618 192 2,845 8.1 763.2 763.2 763.2 0.0 BS 178.635 198 2,705 8.3 763.3 763.3 763.3 0.0 BT 178.651 211 2,806 7.5 763.6 763.6 763.6 0.0 BU 178.665 228 2,643 7.2 763.8 763.8 763.8 0.0 BV 178.701 292 3,276 5.3 764.4 764.4 764.4 0.0 BW 178.705 301 2,509 7.0 766.2 766.2 766.2 0.0 BX 178.719 330 4,146 4.1 766.9 766.9 766.9 0.0 BY 178.732 368 4,164 3.8 766.9 766.9 766.9 0.0 BZ 178.779 521 5,825 2.7 767.1 767.1 767.1 0.0 CA 179.208 904 8,792 1.8 767.3 767.3 767.3 0.0 CB 179.439 491 3,686 4.2 767.3 767.3 767.3 0.0 CC 179.449 422 3,629 4.3 767.3 767.3 767.3 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) CD 179.459 397 3,651 4.3 767.3 767.3 767.3 0.0 CE 179.478 370 3,699 4.2 767.5 767.5 767.5 0.0 CF 179.484 364 3,426 4.6 767.5 767.5 767.5 0.0 CG 179.489 362 3,582 4.4 767.5 767.5 767.5 0.0 CH 179.517 371 3,649 4.3 767.6 767.6 767.6 0.0 CI 179.532 392 3,698 4.2 767.7 767.7 767.7 0.0 CJ 179.548 470 4,310 3.7 767.8 767.8 767.8 0.0 CK 179.993 291 3,695 4.3 768.3 768.3 768.3 0.0 CL 180.009 318 3,185 4.8 768.3 768.3 768.3 0.0 CM 180.044 268 3,208 5.1 768.4 768.4 768.4 0.0 CN 180.058 263 3,182 4.8 768.5 768.5 768.5 0.0 CO 180.400 228 3,495 4.4 769.0 769.0 769.0 0.0 CP 180.418 222 3,501 4.4 769.0 769.0 769.0 0.0 CQ 180.534 197 2,797 5.9 769.2 769.2 769.2 0.0 CR 180.545 198 2,807 5.8 769.2 769.2 769.2 0.0 CS 180.551 199 2,765 5.9 769.2 769.2 769.2 0.0 CT 180.565 212 2,783 5.6 769.3 769.3 769.3 0.0 CU 180.763 331 5,827 2.6 770.0 770.0 770.0 0.0 CV 180.772 345 3,107 5.4 774.9 774.9 774.9 0.0 CW 180.783 378 5,485 3.0 775.3 775.3 775.3 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) CX 180.795 368 6,035 2.5 775.3 775.3 775.3 0.0 CY 180.811 317 6,038 2.6 775.3 775.3 775.3 0.0 CZ 180.826 303 5,499 3.2 775.3 775.3 775.3 0.0 DA 180.864 332 4,857 3.2 775.3 775.3 775.3 0.0 DB 180.896 376 4,874 3.1 775.4 775.4 775.4 0.0 DC 180.991 476 4,721 3.2 775.4 775.4 775.4 0.0 DD 181.504 520 6,328 2.4 775.8 775.8 775.8 0.0 DE 181.526 510 6,334 2.4 775.8 775.8 775.8 0.0 DF 181.662 424 3,567 4.3 775.8 775.8 775.8 0.0 DG 182.012 647 8,103 2.0 776.2 776.2 776.2 0.0 DH 182.532 857 9,171 1.7 776.3 776.3 776.3 0.0 DI 183.194 463 5,236 2.9 776.5 776.5 776.5 0.0 DJ 183.561 408 4,600 3.4 776.7 776.7 776.7 0.0 DK 183.792 380 4,455 3.9 776.9 776.9 776.9 0.0 DL 184.565 446 6,205 2.6 777.6 777.6 777.6 0.0 DM 185.075 297 4,293 3.5 777.9 777.9 777.9 0.0 DN 185.091 287 4,306 3.6 777.9 777.9 777.9 0.0 DO 185.121 367 4,322 3.4 777.9 777.9 777.9 0.0 DP 185.140 471 6,334 2.4 778.1 778.1 778.1 0.0 DQ 185.709 464 5,947 2.5 778.4 778.4 778.4 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) DR 186.463 346 4,672 3.4 778.9 778.9 778.9 0.0 DS 187.021 541 7,494 2.0 779.3 779.3 779.3 0.0 DT 187.414 560 6,196 2.6 779.4 779.4 779.4 0.0 DU 187.716 445 6,858 2.2 779.6 779.6 779.6 0.0 DV 187.949 595 7,352 2.0 779.7 779.7 779.7 0.0 DW 188.425 435 7,990 2.0 779.9 779.9 779.9 0.0 DX 188.818 506 6,464 2.4 780.0 780.0 780.0 0.0 DY 189.076 560 8,312 1.8 780.1 780.1 780.1 0.0 DZ 189.532 554 8,177 1.9 780.3 780.3 780.3 0.0 EA 189.923 528 6,947 2.2 780.4 780.4 780.4 0.0 EB 190.303 383 4,902 3.1 780.5 780.5 780.5 0.0 EC 190.713 423 6,210 2.5 780.9 780.9 780.9 0.0 ED 191.139 886 6,013 2.5 781.2 781.2 781.2 0.0 EE 191.524 906 6,630 1.7 781.4 781.4 781.4 0.0 EF 191.940 625 9,264 1.2 781.6 781.6 781.6 0.0 EG 192.420 749 9,585 1.2 781.6 781.6 781.6 0.0 EH 192.850 644 7,621 1.4 781.7 781.7 781.7 0.0 EI 193.230 472 4,700 2.3 781.7 781.7 781.7 0.0 EJ 193.278 345 3,457 4.0 781.7 781.7 781.7 0.0 EK 193.284 334 2,167 6.5 781.7 781.7 781.7 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) EL 193.287 335 3,618 3.7 782.2 782.2 782.2 0.0 EM 193.301 339 4,755 2.9 782.3 782.3 782.3 0.0 EN 193.318 361 5,450 2.3 782.4 782.4 782.4 0.0 EO 193.401 385 6,126 2.0 782.4 782.4 782.4 0.0 EP 194.244 430 5,498 2.2 782.7 782.7 782.7 0.0 EQ 194.624 498 6,354 1.8 782.9 782.9 782.9 0.0 ER 194.646 528 6,360 1.8 782.9 782.9 782.9 0.0 ES 195.276 423 5,368 2.1 783.3 783.3 783.3 0.0 ET 195.446 575 4,339 2.4 783.3 783.3 783.3 0.0 EU 195.565 538 5,412 2.0 783.4 783.4 783.4 0.0 EV 195.582 499 5,424 2.2 783.5 783.5 783.5 0.0 EW 195.667 1,113 3,900 2.7 783.5 783.5 783.5 0.0 EX 196.062 683 7,326 1.5 783.8 783.8 783.8 0.0 EY 196.512 1,270 11,147 1.1 783.9 783.9 783.9 0.0 EZ 196.991 650 8,266 1.4 783.9 783.9 783.9 0.0 FA 197.493 543 6,311 1.7 784.0 784.0 784.0 0.0 FB 197.969 534 5,810 1.9 784.2 784.2 784.2 0.0 FC 198.294 481 5,115 2.1 784.3 784.3 784.3 0.0 FD 198.340 411 5,125 2.1 784.3 784.3 784.3 0.0 FE 198.347 407 5,191 2.1 784.3 784.3 784.3 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Rock River (continued) FF 198.361 697 5,195 2.1 784.3 784.3 784.3 0.0 FG 198.577 495 5,625 2.0 784.4 784.4 784.4 0.0 FH 198.589 460 6,417 1.7 784.4 784.4 784.4 0.0 FI 198.624 493 6,424 1.6 784.5 784.5 784.5 0.0 FJ 198.640 547 7,937 1.3 784.5 784.5 784.5 0.0 FK 198.987 1,390 12,358 0.9 784.5 784.5 784.5 0.0 FL 199.369 1,046 10,542 1.0 784.6 784.6 784.6 0.0 FM 199.522 1,468 15,256 0.7 784.6 784.6 784.6 0.0 FN 199.952 5,243 84,126 0.2 784.6 784.6 784.6 0.0 1 Miles above mouth FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS ROCK RIVER

FLOODING SOURCE FLOODWAY 1-PERCENT-ANNUAL-CHANCE-FLOOD WATER SURFACE ELEVATION CROSS SECTION DISTANCE 1 WIDTH (FEET) SECTION AREA (SQUARE FEET) MEAN VELOCITY (FEET PER SECOND) REGULATORY(FEET NGVD)

WITHOUT FLOODWAY (FEET NGVD)

WITH FLOODWAY (FEET NGVD)

INCREASE (FEET) Un. Trib. 1 to Rock River A 1,506 693 6,035 1.2 754.0 752.3 2 752.3 2 0.0 B 1,997 764 3,805 1.3 754.0 752.5 2 752.5 2 0.0 C 2,495 495 2,140 2.6 754.0 752.6 2 752.6 2 0.0 D 2,983 604 2,400 2.6 754.0 753.4 2 753.4 2 0.0 E 3,503 292 1,211 5.2 755.0 755.0 755.0 0.0 F 3,900 150 814 6.5 757.1 757.1 757.1 0.0 G 4,304 351 2,625 2.1 759.9 759.9 759.9 0.0 H 4,497 365 1,948 2.6 760.0 760.0 760.0 0.0 I 5,001 564 1,991 2.0 760.9 760.9 760.9 0.0 J 5,504 577 1,725 2.3 761.6 761.6 761.6 0.0 K 5,994 629 1,232 3.2 763.1 763.1 763.1 0.0 L 6,506 653 1,283 3.1 765.0 765.0 765.0 0.0 M 7,010 632 1,553 2.6 766.8 766.8 766.8 0.0 N 7,490 457 1,016 3.9 768.0 768.0 768.0 0.0 O 7,987 512 1,620 2.4 769.5 769.5 769.5 0.0 P 8,481 517 1,305 3.0 770.5 770.5 770.5 0.0 Q 8,996 407 1,440 3.3 772.0 772.0 772.0 0.0 R 9,526 484 1,820 2.1 772.9 772.9 772.9 0.0 S 10,015 378 853 4.6 773.4 773.4 773.4 0.0 T 10,461 363 1,030 3.8 775.4 775.4 775.4 0.0 U 10,980 69 1,763 16.4 779.7 779.7 779.7 0.0 1 Feet above confluence with Rock River 2 Elevation not considering backw ater effects from Rock River FLOODWAY DATA TABLE 3FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS UNNAMED TRIBUTARY 1 TO ROCK RIVER

The area between the floodway and 1-percent-annual-chance floodplain boundaries is termed the floodway fringe. The floodway fringe encompasses the portion of the floodplain that could be completely obstructed without increasing the water surface elevation of the 1-percent-annual-chance flood more than 1 foot at any point. Typical relationships between the floodway and the floodway fringe and their significance to floodplain development are shown in Figure 1.

Figure 1 - Floodway Schematic

5.0 INSURANCE

APPLICATIONS For flood insurance rating purposes, flood insura nce zone designations are assigned to a community based on the results of the engineering analyses. These zones are as follows:

Zone A

Zone A is the flood insurance risk zone that corresponds to the 1-percent-annual-chance floodplains that are determined in the FIS by approximate methods. Because detailed hydraulic analyses are not performed for such areas, no BFEs or ba se flood depths are shown within this zone.

Zone AE

Zone AE is the flood insurance risk zone th at corresponds to the 1-percent-annual-chance floodplains that are determined in the FIS by detailed methods. In most instances, whole-foot BFEs derived from the detailed hydraulic analyses are shown at selected intervals within this zone.

80 Zone X

Zone X is the flood insurance risk zone that corresponds to areas outside the 0.2-percent-

annual-chance floodplain, areas within the 0.2-percent-annual-chance floodplain, areas of 1-percent-annual-chance flooding where average depths are less than 1 foot, areas of 1-percent-annual-chance flooding where the contri buting drainage area is less than 1 square mile, and areas protected from the 1-percent-annual-chance flood by levees. No BFEs or base flood depths are shown within this zone.

6.0 FLOOD

INSURANCE RATE MAP The FIRM is designed for flood insurance and floodplain management applications.

For flood insurance applications, the map de signates flood insurance risk zones as described in Section 5.0 and, in the 1-perc ent-annual-chance floodplains that were studied by detailed methods, s hows selected whole-foot BFEs or average depths. Insurance agents use the zones and BFEs in conjunction with information on structures and their contents to assign premiu m rates for flood insurance policies.

For floodplain management applications, the map shows by tints, screens, and sym bols, the 1- and 0.2-percent-annual-chance floodpl ains, floodways, and the locations of selected cross sections used in the hydr aulic analyses and floodway computations.

The countywide FIRM presents flooding inform ation for the entire geographic area of Rock County. Previously, FIRMs were prep ared for each incorporated community and the unincorporated areas of the Count y identified as flood-prone.

7.0 OTHER

STUDIES Flood Insurance Studies have been prepared for the following neighboring Counties in Wisconsin: Green, Dane, Jefferson and Walwor th. Flood Insurance Studies have been prepared for the following neighboring C ounties in Illinois: Winnebago and Boone.

This report either supersedes or is compatible with all previous studies on streams studied in this report and should be considered authoritative for purposes of the NFIP.

8.0 LOCATION

OF DAT A Information concerning the pertinent data us ed in the preparation of this study can be obtained by contacting FEMA, Federal Insurance and Mitigation Division, Federal Regional Center, 800 North Loop 288, Denton, Texas 76209.

81 Information concerning the pertinent data us ed in the preparation of this study can be obtained by contacting FEMA, Federal Insurance and Mitigation Division, Federal Office Building, 2323 Grand Boulevard, Suite 900, Kansas City, Missouri 64108-2670.

Information concerning the pertinent data us ed in the preparation of this study can be obtained by contacting FEMA , Federal Insurance and Mi tigation Division, 536 South Clark Street, Sixth Floor , Chicago, Illinois 60605.

82 83 COMMUNITY NAME INITIAL IDENTIFICATION FLOOD HAZARD BOUNDARY MAP REVISION DATE(S)

FLOOD INSURANCE RATE MAP EFFECTIVE DATE FLOOD INSURANCE RATE MAP REVISION DATE(S)

Beloit, City of Brodhead, City of 1 Clinton, Village of Edgerton, City of

Evansville, City of

Footville, Village of

Janesville, City of

Milton, City of

Orfordville, Village of

Rock County (Unincorporated Areas)

July 10, 1971

February 8, 1974

N/A December 17, 1973

June 14, 1974

May 31, 1974 March 31, 1972

N/A N/A

August 1, 1983 April 23, 1976

April 16, 1976

None June 4, 1976

May 14, 1976 October 15, 1976

None

None None

None December 15, 1982

September 29, 1989

N/A April 15, 1982

January 18, 1 984 July 3, 1986

March 31, 1972

N/A N/A

August 1, 1983 None None

None None

May 4, 1992

None July 1, 1974 December 19, 1975 January 17, 1985 None None

None 1 No Special Flood Hazard Areas Identified TABLE 4 FEDERAL EMERGENCY MANAGEMENT AGENCY ROCK COUNTY, WI AND INCORPORATED AREAS COMMUNITY MAP HISTORY

84 9.0 BIBLIOGRAPHY AND REFERENCES

1. U.S. Department of Agriculture, Soil Survey of Rock County, Wisconsin , July 1974. 2. U.S. Department of Commerce, Bureau of the Census, 1970 Census of Population, Volume 1, Part 51, 1973.

3. Wisconsin Department of Natural Resources, Surface Water Resources of Rock County, Madison, Wisconsin, 1970.

4. U.S. Geological Survey, Water Resources Data for Wisconsin , 1968-1976.

5. U.S. Army Corps of Engineers, Rock Island District, Phase I General Design Memorandum for South Beloit, Illinois, September 1979.

6. Rock County, Shoreland Zoning Ordinance (with Flood Plain Amendment), Section 16, Rock County Ordinances, November 1974.

7. U.S. Water Resources Council, Bulletin No. 17, Guidelines for Determining Flood Flow Frequency , March 1976.

8. U.S. Geological Survey, Estimating Magnitude and Frequency of Floods in Wisconsin, D. H. Conger, Open-File Report, 1971.

9. U.S. Department of Housing and Urban Development, Federal Insurance Administration, Type 15 Flood Insurance Study, City of Beloit, Wisconsin, July 1971.

10. U.S. Department of Housing and Urban Development, Federal Insurance Administration, Type 15 Flood Insurance Study, Janesville, Wisconsin, March 1972.

11 U.S. Army Corps of Engineers, Rock Island District, Beloit, Wisconsin, Flood Plain Information , June 1968.

12. U.S. Geological Survey, Floods on Rock River in Northern Rock County, Wisconsin, HA-393, James 0. Shearman, 1970.

13. U.S. Department of Agriculture, Soil Conservation Service, Technical Release No. 20, Project Formulation Computer Program - Hydrology , 1965, with updates.

14. U.S. Department of Agriculture, Soil Conservation Service, Flood Hazard Study , City of Evansville, Rock County, Wisconsin, January 1982.

85 15. U.S. Department of Agriculture, Soil Conservation Service, National Engineering Handbook, Section 4, Chapter 7, "Hydrology," August 1972.

16. U.S. Army Corps of Engineers, Rock Island District, Janesville, Wisconsin, Flood Plain Information , June 1968.

17. U.S. Geological Survey, 7.5 Minute Topographic Maps , Scale 1:24000, Contour Interval 10 feet with intermediate five-foot contours: Avalon, Wisconsin, 1971; Beloit, Wisconsin, 1976; Brodhead East, Wisconsin-Illinois, 1971; Clinton, Wisconsin, 1971; Cooksville, Wisconsin, 1971; Durand, Illinois-Wisconsin, 1971; Edgerton, Wisconsin, 1971; Evansville, Wisconsin, 1971; Footville, Wisconsin, 1971; Janesville East, Wisconsin, 1971; Janesville West, Wisconsin, 1971; Lima Center, Wisconsin, 1971; Milton, Wisconsin, 1971; Newark, Wisconsin, 1971; Orfordville, Wisconsin, 1971; Shirland, Illinois-Wisconsin, 1971; Shopiere, Wisconsin, 1971; and South Beloit, Illinois-Wisconsin, 1971.

18. U.S. Department of Housing and Urban Development, Federal Insurance Administration, Type 15 Flood Insurance Study , County of Dane, Unincorporated Areas, Wisconsin, September 1978.

19. Federal Emergency Management Agency, Type 19 Flood Insurance Study , City of Beloit, Wisconsin, December 1982.

20. U.S. Army Corps of Engineers, HEC-2 Water-Surface Profiles, with Modification No. 58 , February 1976.

21. Federal Emergency Management Agency, Federal Insurance Administration, Type 15 Flood Insurance Study , County of Winnebago, Un incorporated Areas, Illinois, February 1981.

22. U.S. Department of Housing and Urban Development, Federal Insurance Administration, Type 15 Flood Insurance Study, City of South Beloit, Illinois, January 1980.

23. U.S. Geological Survey, Floodprone Area Maps , Scale 1:24000, C ontour Interval 10 feet: Avalon, 1975; Beloit, 1970; Brodhead East, 1970; Clinton, 1970; Cooksville, 1970; Edgerton 1970; Evansville, 1974; Footville, 1974; Janesville East, 1975; Janesville West, 1970; Lima Center, 1975; Milton, 1970; Newark, 1976; Orfordville, 1974; Shopiere, 1970.

24. U.S. Department of Agriculture, Soil Conservation Service, Technical Release No. 61, WSP-2 Computer Program , May 1976.

25. Wisconsin Department of Natural Resources, Wisconsin's Flood Plain Management Program , Chapter NR 116, Register No. 259, 1977.

86 26. Federal Emergency Management Agency, Flood Insurance Study, City of Edgerton, Wisconsin, October 1981.

27. Federal Emergency Management Agency, Federal Insurance Administration, Flood Insurance Study , County of Jefferson, Unincorporated Areas, Wisconsin, September 1978.

28. Federal Emergency Manageme nt Agency, Flood Insurance Study, County of Boone, Unincorporated Areas, Illinois, November 1982.

29. Federal Emergency Manageme nt Agency, Flood Insurance Study, City of Janesville, Wisconsin, July 1984.

30. Federal Emergency Manageme nt Agency, Flood Insurance Study, Village of Evansville, Wisconsin, May 1992.

31. Federal Emergency Management Agency, Flood Insurance Study, County of Rock, Unincorporated Areas, Wisconsin, February 1983.

32. Federal Emergency Manageme nt Agency, Flood Insurance Study, County of Green, Unincorporated Areas, Wisconsin, September 1986.

33. Federal Emergency Manageme nt Agency, Flood Insurance Study, County of Walworth, Unincorporated Areas, Wisconsin, February 1983.

34. U.S. Army Corps of Engineers, Rock Island District, Turtle Creek, Rock County, Wisconsin, Flood Plain Information, December 1967.

35. City of Janesville, Wisconsin Planning Division, Communication of September 1981.

36. City of Janesville, Wisconsin, Flood Plain Zoning Ordinance.

37. U.S. Army Corps of Engineers, Rock Island District, Corps of Engineers Files, 1981.

38. City of Janesville, Wisconsin, Engineering Files, 1981.

39. Chow, Ven Te, Open-Channel Hydraulics , New York: McGraw-Hill Book Company, Inc., 1959.

40. City of Janesville, Wiscons in, High Water Marks for 1973 Flood.

41. Wisconsin Department of Administration, Official Population Estimates for 1978 , Madison, Wisconsin.

87 42. Beloit Planning Office, unpublished land use survey.

43. Chicago Aerial Survey, Topographic Maps of the City of South Beloit, Illinois , Scale 1:2400, Contour Interval four feet: Franklin Park, Illinois, 1963.

44. The State of Wisconsin 1980 Blue Book compiled by the Wisconsin Legislative Reference Bureau, 1980.

45. The Underground and Surface Water Supplies of Wisconsin, Samuel Weidman and Alfred Schultz, State of Wisconsin, 1915.

46. U.S. Army Corps of Engineers, Hydrologic Engineering Center, Computer Program 723-X6-L2010 HEC-1 Hydrologic Package , Davis, California.

47. Hydraulic Review of Natural or Constricted Waterways (Bridge or Culvert), Wisconsin Department of Natural Res ources, Bureau of Water Regulation and Zoning, March 1978.

48. U.S. Department of Commerce, Bu reau of the Census, 1980 Census of Population, Number of Inhabitants, Wisconsin , Washington, D.C., February 1982.

49. U.S. Department of Commerce, Weather Bureau, Technical Paper No. 40, Rainfall Frequency Atlas of the United States, Washington, D.C., January 1963.

50. U.S. Army Corps of Engineers, Hydrologic Engineering Center. (May 2005).

HEC-RAS River Analysis System Computer Program , Version 3.1.3.

51. U.S. Army Corps of Engineers, Hydrologic Engineering Center. (May 2003). HEC-HMS Hydrologic Modeling System Computer Program , Version 2.2.

52. Southeastern Wisconsin Regional Planning Commission. (June 2005). SEWRPC Recommended Rainfall Distribution.

53. Aero-Metric, Inc. (March 2000 flight). Rock County DTM , Mass points, breaklines and contour interval 2 feet.

54. Aero-Metric, Inc. (March 2000 fl ight). Rock County Orthophotography 1' resolution.

55. Jenkins Survey & Design, Inc., Rock County Hydraulic Structure Survey (Blackhawk Creek & Trib., Ma rkham Creek, Fisher Creek), August 2005.

56. Jenkins Survey & Design, Inc., Rock County Hydraulic Structure Survey (Bass Cr., Saunders Cr., Un. Trib. 1 Rock River, Spring Bk, Un. Trib. Turtle Township), September 2005.

88 57. Rock County Planning, Economic and Community Development Agency, Rock County Bridge Metrics Field Surveys , March 2005.

58. Owen Ayers & Associates, Inc., City of Janesville, WI Flood Insurance Study Hydrologic Summary , August 1981.

59. Federal Emergency Management Agency. (March 2005). RASPLOT Computer Program, Version 2.5.

60. ESRI, ArcGIS Computer Program , Version 9.1

61. ESRI, ArcView Computer Program , Version 3.2

ROCK COUNTY, WISCONSIN AND INCORPORATED AREAS

VOLUME 2 OF 2 Community Name Community Number BELOIT, CITY OF 555544 BRODHEAD, CITY OF 550160 CLINTON, VILLAGE OF 550067 EDGERTON, CITY OF 550365 EVANSVILLE, CITY OF 550366 FOOTVILLE, VILLAGE OF 550575 JANESVILLE, CITY OF 555560 MILTON, CITY OF 550026 ORFORDVILLE, VILLAGE OF 550369 ROCK COUNTY (UNINCORPORATED AREAS) 550363 August 19, 2008 Federal Emergency Management Agency FLOOD INSURANCE STUDY NUMBER 55105CV002A

NOTICE TO FLOOD INSURANCE STUDY USERS Communities participating in the National Flood Insurance Program have established repositories of flood hazard data for floodplain management and flood insurance purposes. This Flood Insurance Study (FIS) report may not contain all data available within the Community Map Repository. Please contact the Community Map Repository for any additional data.

The Federal Emergency Management Agency (FEMA) may re vise and republish part or all of this FIS report at any time. In addition, FEMA may revise part of this FIS report by the Letter of Map Re vision process, which does not involve republication or redistribution of the FIS report. Theref ore, users should consult with community officials and check the Community Map Repository to obtain the most current FIS report components.

Effective Date: August 19 , 2008

Revised Dates:

1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Tuesday, August 13, 2013 11:13 AM To: Moser, Michelle; Lynch, Steven

Subject:

DRAFT SHINE Response to Geology and Soil/Wa ter Resources Request #1 - Part 2 of 8 Attachments:

DRAFT - Geology and Soil-Water Resources R equest 1 Response - Revision 1 - Part 2 of 8.pdfMichelle and Steve, Attached is Part 2 of 8 of the Draft SHINE Response to Geology and Soil/Water Resources Request #1.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

i TABLE OF CONTENTS VOLUME 1

1.0 INTRODUCTION

...............................................................................................................1 1.1 Purpose of Study............................................................................................................1 1.2 Authority and Acknowledgments..................................................................................

1 1.3 Coordination..................................................................................................................2 2.0 AREA ST UDIED.................................................................................................................4 2.1 Scope of Study...............................................................................................................4

2.2 Community

Description.................................................................................................

6 2.3 Principal Flood Problems...............................................................................................7

2.4 Flood

Protection Measures............................................................................................8

3.0 ENGINEERING

METHODS.............................................................................................8 3.1 Hydrologic Analyses......................................................................................................

8 3.2 Hydraulic Analyses........................................................................................................1 6 3.3 Vertical Datum...............................................................................................................21 4.0 FLOODPLAIN MANAGEMENT APPLICATIONS......................................................22 4.1 Floodplain Boundaries...................................................................................................22 4.2 Floodways......................................................................................................................23 5.0 INSURANCE APPLI CATIONS........................................................................................80

6.0 FLOOD

INSURANCE RATE MAP

..................................................................................

81 7.0 OTHER STUDIES

...............................................................................................................

81 8.0 LOCATION OF DAT A.......................................................................................................81

9.0 BIBLIOGRAPHY

AND REFERENCES..........................................................................84

TABLE OF CONTENTS (Continued) ii FIGURES Figure 1 - Floodway Schematic........................................................................................................80 TABLES Table 1 - Summary of Discharges...............................................................................................1 1-15 Table 2 - Summary of Stillwater Elevations.....................................................................................15 Table 3 - Floodway Data..............................................................................................................24-79 Table 4 - Community Map History...................................................................................................83 VOLUME 2 EXHIBITS Exhibit 1 - Flood Profiles Allen Creek 01P-05P Bass Creek 06P-12P Blackhawk Creek 13P-14P East Fork Raccoon Creek 15P-16P Fisher Creek 17P-21P Greenbelt Tributary 1 22P-23P Greenbelt Tributary 2 24P Greenbelt Tributary 3 25P Greenbelt Tributary 4 26P-27P Greenbelt Tributary 5 28P-29P Markham Creek 30P-33P Marsh Creek 34P-36P Morningside Tributary 37P-38P Otter Creek 39P-42P Raccoon Creek 43P-46P Rock River 47P-70P Saunders Creek 71P-74P Spring Brook (Beloit) 75P-79P Spring Brook (Janesville) 80P-81P Sugar River 82P-86P Turtle Creek 87P-97P Unnamed Tributary 1 to Raccoon Creek 98P-99P Unnamed Tributary 2 to Raccoon Creek 100P-102P Unnamed Tributary 1 to Rock River 103P Unnamed Tributary 1 to Turtle Creek 104P Unnamed Tributary 2 to Turtle Creek 105P-106P Unnamed Tributary to Blackhawk Creek 107P-108P Unnamed Tributary to East Fork Raccoon Creek 109P-112P Unnamed Tributary in Turtle Township 113P-115P Yahara River 116P-119P

Exhibit 2 - Flood Insurance Rate Ma p Index & Flood Insurance Rate Map 700 710 720 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790163.00163.125163.25163.375163.50163.625163.75163.875164.00164.125164.25164.375164.50164.625 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O FIL E S R O C K RIV E R 47P A B C D E F G H I J K L M N O P Q R S T U V W B L A C K H A W K D A M S HIR L A N D A V E N U E O L D R AIL R O A D B RID G E 4 T H S T R E E T P A R KIN G S T R U C T U R E W E S T G R A N D A V E N U E O L D R AIL R O A D B RID G E P O R T L A N D A V E N U E S T A T E B O U N D A R Y C O N F L U E N C E WIT H L E NIG A N C R E E K LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION DAM 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800164.625164.75164.875165.00165.125165.25165.375165.50165.625165.75165.875166.00166.125166.25 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O FIL E S R O C K RIV E R 48P X Y Z AA AB AC H E N R Y B RID G E CIT Y O F B E L O I T C O R P O R A T E LIMIT S LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800166.25166.375166.50166.625166.75166.875167.00167.125167.25167.375167.50167.625167.75167.875 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 49P AD AE AF AG AH AI C O U N T Y HIG H W A Y Q LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800167.875168.00168.125168.25168.375168.50168.625168.75168.875169.00169.125169.25169.375169.50 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 50P AJ AK AL AM ANIO W A A N D C HIC A G O R AIL R O A D C O N F L U E N C E WIT H U N N A M E D T RIB U T A R Y C O N F L U E N C E WIT H P HIL H O W E R R O A D T RIB U T A R Y LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800169.50169.625169.75169.875170.00170.125170.25170.375170.50170.625170.75170.875171.00171.125 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O FIL E S R O C K RIV E R 51P AO AP AQ AR AS AT T O W N LIN E R O A D C O N F L U E N C E WIT H U N N A M E D LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION T RIB U T A R Y 1 T O R O C K R I V E R 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800171.125171.25171.375171.50171.625171.75171.875172.00172.125172.25172.375172.50172.625172.75 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 52P AU AV AW C O N F L U E N C E WIT H B A S S C R E E K LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800172.75172.875173.00173.125173.25173.375173.50173.625173.75173.875174.00174.125174.25174.375 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 53P AX AY AZ BA BB E A U C L AIR E R O A D LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800174.375174.50174.625174.75174.875175.00175.125175.25175.375175.50175.625175.75175.875176.00 E L E V A T IO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O FIL E S R O C K R IV E R 54P BC BD BE BF BG U S H IG H W A Y 1 1 C IT Y O F J A N E S V IL L E C O R P O R A T E L IM IT S LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800176.00176.125176.25176.375176.50176.625176.75176.875177.00177.125177.25177.375177.50177.625 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 55P BH BI BJ C O N F L U E N C E WIT H M A R K H A M C R E E K C O N F L U E N C E WIT H FIS H E R C R E E K LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800177.625177.75177.875178.00178.125178.25178.375178.50178.625178.75178.875179.00179.125179.25 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K R IV E R 56P BK BL BM BN BO BP BQ BR BS BT BU BV BW BX BY BZ CA C HIC A G O MIL W A U K E E S T P A U L C H I C A G O A N D C E N T E R A V E N U E S O U T H C R O S B Y A V E N U E M O N T E R R E Y D A M LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION A N D P A CIFIC R AIL R O A D N O R T H W E S T E R N R R DAM 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800179.25179.375179.50179.625179.75179.875180.00180.125180.25180.375180.50180.625180.75180.875 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 57P CB CC CD CE CF CG CH CI CJ CK CL CM CN CO CP CQ CR CS CT CU CV CW CX CY CZ DA J A C K S O N S T R E E T BIK E P A T H B RID G E E A S T R A CIN E S T R E E T C O U R T S T R E E T MIL W A U K E E S T R E E T C E N T E R W A Y D A M C E N T E R W A Y S T R E E T C O N F L U E N C E WIT H S P RIN G B R O O K - J A N E S VIL L E LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION DAM 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820180.875181.00181.125181.25181.375181.50181.625181.75181.875182.00182.125182.25182.375182.50 E L E V A T IO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O FIL E S R O C K R IV E R 58P DB DC DD DE DF DG C H IC A G O A N D N O R T H W E S T E R N R A IL R O A D M E M O R IA L D R IV E LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820182.50182.625182.75182.875183.00183.125183.25183.375183.50183.625183.75183.875184.00184.125 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 59P DH DI DJ DK CIT Y O F J A N E S VIL L E C O R P O R A T E LIMIT S LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820184.125184.25184.375184.50184.625184.75184.875185.00185.125185.25185.375185.50185.625185.75 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 60P DL DM DN DO DP DQ U S HIG H W A Y 1 4 C O N F L U E N C E WIT H M A R S H C R E E K LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820185.75185.875186.00186.125186.25186.375186.50186.625186.75186.875187.00187.125187.25187.375 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 61P DR DS LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820187.375187.50187.625187.75187.875188.00188.125188.25188.375188.50188.625188.75188.875189.00 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K R IV E R 62P DT DU DV DW DX LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820189.00189.125189.25189.375189.50189.625189.75189.875190.00190.125190.25190.375190.50190.625 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 63P DY DZ EA EB LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820190.625190.75190.875191.00191.125191.25191.375191.50191.625191.75191.875192.00192.125192.25 E L E V A T IO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O FIL E S R O C K R IV E R 64P EC ED EE EF C O N F L U E N C E W IT H Y A H A R A R IV E R LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820192.25192.375192.50192.625192.75192.875193.00193.125193.25193.375193.50193.625193.75193.875 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 65P EG EH EI EJ EK EL EM EN EOIN DIA N F O R D D A M C O U N T Y HIG H W A Y M LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION DAM 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820193.875194.00194.125194.25194.375194.50194.625194.75194.875195.00195.125195.25195.375195.50 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K R IV E R 66P EP EQ ER ES ET U S HIG H W A Y 5 1 C O N F L U E N C E WIT H S A U N D E R S C R E E K LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820195.50195.625195.75195.875196.00196.125196.25196.375196.50196.625196.75196.875197.00197.125 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 67P EU EV EW EX EY EZ C HIC A G O MIL W A U K E S T P A U L C O N F L U E N C E WIT H U N N A M E D LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION A N D P A CIFIC R AIL R O A D T R I B U A T R Y 2 T O R O C K R I V E R 730 740 750 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820197.125197.25197.375197.50197.625197.75197.875198.00198.125198.25198.375198.50198.625198.75 E L E V A T IO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O FIL E S R O C K RIV E R 68P FA FB FC FD FE FF FG FH FI FJ IN T E R S T A T E 9 0 IN T E R S T A T E 9 0 S T A T E H IG H W A Y 5 9 LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION 740 750 760 760 770 770 780 780 790 790 800 800 810 810 820 820 830 830198.75198.875199.00199.125199.25199.375199.50199.625199.75199.875200.00200.125200.25200.375 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 69P FK FL FM FN LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION LAKE KOSHKONONG 750 760 770 770 780 780 790 790 800 800 810 810 820 820 830 830 840 840200.375200.50200.625200.75200.875201.00201.125201.25201.375201.50201.625201.75201.875202.00 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN MILES ABOVE MOUTH F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y, W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S R O C K RIV E R 70P C O U N T Y B O U N D A R Y LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION LAKE KOSHKONONG 710 720 730 730 740 740 750 750 760 760 770 770 780 780 790 790 800 800010002000300040005000600070008000900010000110001200013000 E L E V A TIO N IN F E E T (N G V D 2 9)STREAM DISTANCE IN FEET ABOVE THE CONFLUENCE OF ROCK RIVER F E D E R A L E M E R G E N C Y M A N A G E M E N T A G E N C Y R O C K C O U N T Y , W I A N D IN C O R P O R A T E D A R E A S F L O O D P R O F IL E S U N N A M E D T RIB U T A R Y 1 T O R O C K RIV E R 103P A B C D E F G H I J K L M N O P Q R S T U U S HIG H W A Y 5 1 LEGEND 0.2% ANNUAL CHANCE FLOOD 1% ANNUAL CHANCE FLOOD 2% ANNUAL CHANCE FLOOD 10% ANNUAL CHANCE FLOOD STREAM BED CROSS SECTION LOCATION BACKWATER FROM ROCK RIVER L I MIT O F D E T AIL E D S T U D Y C O N F L U E N C E WIT H R O C K RIV E R APPENDIX B MAP OF DAMS ALONG THE ROCK RIVER IN ROCK COUNTY

Dams of Rock County, WI 0 7.5 1522.5mi.Legend This map is a user generated static output from an Internet mapping site and is for general reference only. Data layers that appear on this map may or may not be accurate, current, or

otherwise reliable. THIS MAP IS NOT TO BE USED FOR NAVIGATION.

Scale: 1:409,194 APPENDIX C ABBREVIATED VERSION OF THE CITY OF JANESVILLE REPORT ON THE 2008 FLOOD 200 8 Janesville, Wisconsin Prepared by:

Engineering Division City of Janesville, WI

Introduction

USGS River Elevations

Indianford Station (Upstream Gauge)

Afton Station (Downstream Gauge)

Figure 1: Proximity of Indianford & Afton to Janesville

City of Janesville River Monitoring Operations Future Recommendations

S. River Road Bridge Monterey Dam Hedberg Library N. Traxler N. River Road Figure 2: River Monitoring Route

Figure 13: Rock River Elevations at Each Station for the 2008 Flood

APPENDIX D FEMA FLOOD AREA MAP FROM ROCK COUNTY, FEMA FIRM'S THROUGH JANESVILLE AND NEAR SITE

FEMA Floodplains Rock County Geographic Information System Page 1 of 1Map Output2/1/2012http://68.249.68.135/servlet/com.esri.esrimap.Esrimap?ServiceName=Rock&Form=True&E...

1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Tuesday, August 13, 2013 11:40 AM To: Moser, Michelle; Lynch, Steven

Subject:

DRAFT SHINE Response to Geology and Soil/Wa ter Resources Request #1 - Part 3a of 8 Attachments:

DRAFT - Geology and Soil-Water Resources Requ est 1 Response - Revision 1 - Part 3a of 8.pdfMichelle and Steve, Attached is Part 3a of 8 of the Draft SHINE Response to Geology and Soil/Water Resources Request #1.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

1 Moser, Michelle From:Bill Hennessy <Bill.Hennessy@shinemed.com>

Sent: Tuesday, August 13, 2013 11:44 AM To: Moser, Michelle; Lynch, Steven

Subject:

DRAFT SHINE Response to Geology and Soil/Wa ter Resources Request #1 - Part 3b of 8 Attachments:

DRAFT - Geology and Soil-Water Resources Requ est 1 Response - Revision 1 - Part 3b of 8.pdfMichelle and Steve, Attached is Part 3b of 8 of the Draft SHINE Response to Geology and Soil/Water Resources Request #1.

Bill Hennessy Licensing Engineer, SHINE Medical Technologies 608 210-1734

APPENDIX E FIGURES FROM THE NWS (1978) REPORT NO. 51 PMP STUDY EAST OF THE 105 TH MERIDIAN

HYDROMETEOROLOGICAL REPORT NO. 51 Probable Maximum Precipitation Estimates, United States East of the l05th Meridian U.S. DEPARTMENT OF COMMERCE NATIONAL OCEANIC AND ATMOSPHERIC ADMINISTRATION U.S. DEPARTMENT OF THE ARMY CORPS OF ENGINEERS Wwhmgton, DC June 1978 CONTENTS Page Abstract............................................................

1 1. 1.1. 1.2. 1.3. 1.4. 1. 4.1. 1.4.2. 1.5. 2. 2.1. 2.2. 2.2.1. 2.2.2. 2.2.3. 2.3. 2.3.1. 2.3.2. 2.3.3. 2.3.4. 2.3.5. 2.3.6. 2.4. 2.4.1. 2.4.2. 2.4.3. 2.4.4. 2.4.5. 2.4.6. 3. 3.1. 3.2. 3.2.1. 3.2.2.

3.2.3. 3.2.4. 3.2.5. 3.3. 3.3.1. 3.3.2. 3.3.3. Introduction

• • • • • • • • • .

Background

Assignment

Definition of PMP ** Scope **************

Generalized vs. individual drainage estimates.

Stippled regions on PMP maps ******* Application of drainage PMP values *** Approach to generalized PMP ** Introduction.

Basic data *** Sources **** Variation in rainfall data with duration and area size ** Point rainfall vs. 10-mi2 (26-km2) average rainfall ***** Moisture maximization

• • Definition

-concept. Atmospheric moisture.

Representative storm dew point. Maximum dew point .............. . Moisture adjustment

Elevation and barrier considerations.

Transposition

• • • • • .*****

Definition

• • • • • • • • • • • .

Transposition limits......

• ******** Transposition adjustment........ . ******

adjustment for tropical storm rainfall ........................................ . Large-area rainfall adjustment in the gentle upslope region .................... . Example of storm adjustments.

Details of analysis.

Minimum envelopes.

Special problems ** Introduction

• • • Adjustments greater than SO percent **** Colorado storm May 30-31, 1935 *****.***

1942 *** 1950. Smethport, Pa. storm July 17-18, Yankeetown, Fla. storm September 3-7, Consistency checks ****.*************

Introduction

..................... . Variation of incremental PMP with area size ***** Consistency in depth-area-duration relations

• • • • iii 1 1 1 2 2 2 3 3 3 3 4 4 6 7 7 7 8 8 9 9 9 10 10 10 11 11 11 14 16 16 26 26 28 28 28 29 30 30 31 32 3.3.4. 3.3.5. 3.3.6. 3.3.7. 4. 4.1. 4.2. 4.2.1. 4.2.2. 5. section checks *********

difference check **** Cross Rainfall Rainfall ratio check ***** PJ:.1P maps *****************

Evaluation of generalized PMP charts ******* Degree of envelopment

• • .*****************

Use of PMP for all durations in one PMP storm ** Introduction

Storm commonality test *** ...........

........ Use of charts .......................................... . Acknowledgments.

Page 32 32 32 38 38 38 40 40 40 42 43 References . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

44 Appendix --Maximum observed areal precipitation for important s torm.s *******************************************

TABLES 1. Number of analyzed storms, east of the 105th meridian, with areal rainfall depths for indicated area sizes and 78 durations. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

6 2. 3. 4. 5. 1. Example of computations of moisture maximization and trans-position adjustments

...................................... . Example of total storm adjustments

Storms that give moisture maximized rainfall within 10 percent of PMP for at least one area size and duration ***************

Exceptions to "storm commonality" ** FIGURES Location of storms ............................................. . 2. Distance-from-coast adjustment for transposing tropical storm rainfall ....................................... . 3. Gentle upslope region .......................................... . 4. Example of data used for storm adjustments

iv 17 18 39 42 5 12 13 15

5. 6. 7. 8. 9. Page Envelopment of 24-hr observed storm rainfall (in.) in place of occurrence for 10,000 mi2 (25,900 km2) ********************

20 Envelopment of 24-hr moisture maximized storm rainfall (in.)

• in place of occurrence for 10,000 mi2 (25,900 km2) ***********

21 Envelopment of greatest average monthly precipitation (in.) for State climatic divisions (1931-60)

22 Envelopment of greatest average weekly precipitation (in.) for State climatic divisions (1906-35)

• • • • • • • • • • • • • • • • • • .****

24 Envelopment of the greatest 24-hr station precipitation (in.) within each State climatic division (through 1970) ***********

25 10. Example of minimum smooth envelope of moisture maximized rainfall, in place and transposed

27 11. Adopted transposition adjustment along the Atlantic coast for the Yankeetown, Fla. storm, September 3-7, 1950 **************

31 12. Example of depth-duration smoothing

• • • • • • • • • • • • • .*****

• • * * * * * * *

• 33 13. Example of depth-area smoothing.

• * * * * * * * * * * * * * * * * * * * * * * * * * * * * * . 34 14. Example of cross-section smoothing--constant duration **********

35 15. Example of cross-section smoothing--constant area **************

36 16. Example of checks of durational differences in PMP *************

37 17. Regions for storm commonality tests ****************************

41 18. All-season PMP (in.) for 6 hr 10 mi 2 (26 km 2) ******************

48 19. 20. 21. 22. 23. 24. 25. All-season PMP (in.) for 12 hr 10 mi 2 (26 All-season PMP (in.) for 24 hr 10 mi 2 (26 All-season PMP (in.) for 48 hr 10 mi 2 (26 All-season PMP (in.) for 72 hr 10 mi 2 (26 2 km ) *****************

2 km ) *****************

2 km ) *****************

2 km ) *****************

All-season PMP (in.) for 6 hr 200 mi 2 2 (518 km ) ****************

All-season PMP (in.) for 12 hr 200 mi 2 (518 All-season PMP (in.) for 24 hr 200 mi 2 (518 v 2 km ) ***************

2 km ) ***************

49 50 51 52 53 54 55 Page 26. All-season PMP (in.) for 48 hr 200 mi 2 (518 2 km. ) ***************

56 27. All-season PMP (in.) for 72 hr 200 mi 2 (518 2 km. ) ***************

57 28. All-season PMP (in.) for 6 hr 1,000 mi 2 (2,590 km.2) ************

58 29. All-season PMP (in.) for 12 hr 1,000 mi 2 2 (2, 590 km. ) ***********

59 30. All-season PMP (in.) for 24 hr . 2 1,000 mi 2 (2, 590 km. ) ***********

60 31. All-season PMP (in.) for 48 hr 1,000 mi 2 2 (2, 590 km. ) ***********

61 32. All-season PMP (in.) for 72 hr 1,000 mi2 2 (2,590 km ) ***********

62 33. All-season PMP (in.) for 6 hr 5,000 mi 2 2 (12, 950 km ) ***********

63 34. All-season PMP (in.) for 12 hr 5,000 mi 2 2 (12' 950 km ) **********

64 35. All-season PMP (in.) for 24 hr 5,000 mi 2 2 (12,950 km ) **********

65 36. All-season PMP (in.) for 48 hr 5,000 mi 2 2 (12,950 km ) **********

66 37. All-season PMP (in.) for 72 hr 5,000 mi 2 2 (12,950 km. ) **********

67 38. All-season PMP (in.) for 6 hr 10,000 mi 2 2 (25,900 km. ) **********

68 39. All-season PMP (in.) for 12 hr 10,000 mi 2 2 (25,900 km ) *********

69 40. All-season PMP (in.) for 24 hr 10,000 mi 2 2 (25,900 km ) *********

70 41. All-season PMP (in.) for 48 hr 10,000 mi 2 2 (25,900 km ) *********

71 42. All-season PMP (in.) for 72 hr 10,000 mi 2 2 (25,900 km ) *********

72 43. All-season PMP (in.) for 6 hr 20,000 mi 2 2 (51,800 km ) **********

73 44. All-season PMP (in.) for 12 hr 20,000 mi 2 2 (51,800km)

74 45. All-season PMP (in.) for 24 hr 20,000 mi 2 2 (51,800 km ) *********

75 46. All-season PMP (in.) for 48 hr 20,000 mi 2 2 (51, 800 km ) *********

76 47. All-season PMP (in.) for 72 hr 20,000 mi 2 2 (51,800 km ) *********

77 vi Figure ?.--Envelopment of greatest average monthly preaipitation (in.) for State alimatia divisions (1931-60).

N N 2.7 AUG. 2.6 SEP. Figure B.--Envelopment of greatest average weekly preaipitation (in.) for State alimatia divisions (1906-35).

N

,........._

"'<.o / ... ...._, ... __ * s I _ l . ... 7.1 7 2 '

• v . . f * **:y-1 ,_ I ._

• I 3.< * ' --*-I . ( 1 3.st . J.o w .. Pr \ . 4 6. . * \ I

• I 8 \ 1--' --....1..__ . 7 'X I .-,if.;/7.5

26. 1 6.2 --t, . ... ,

'--LOCATION 10 AMOUNT 1 IN.= 25.4 MM BASED ON DATA FOR STATIONS WITH 10 OR MORE YEARS OF DATA Figure 9.--EnveZopment of the gPeatest 24-hP station pPeaipitation (in.) within eaah State aZimatia division (through 1970). \0 N V1

• ---I . -' i I I i 25'1; I I I 119' 103° 99' 95' 103' 99' 95' 91' 87' 83' Figure 33.--AZZ-season PMP (in.) for 6 hr mi 2 Jon 2 J. STATUTE MILES 100 0 100 200 300

• 100 6 100

• 260 3oo

• KILOMETERS 79' 75' .25' 0'\ w i 33'1 / 29' ' I i I 99' 95' 29' I \ _1 IN. = 25.4 MM I I I I '-_j____c_l I ) I 'lt I I 1-1-d--d-=:=:H , .... :::.::.:'" I \ I STAT UTE MILES ..J2 5' 100 200 300 25'1 1 I 119' 115' 111' 107' 103' 99' 95' 91' 87' 83' 79' 75' Figure 34.--AZZ-season PMP (in.) for 12 hr 5 3 000 mi 2 (12 3 950 km 2). 0\ -!:'-

99' 95' j _ _j__ I ' 29 I I 1" 25'1' I I I I i 119' 115° 103' 99' 95' 91' 87' 83' FiguPe J5.--AZZ-season PMP (in.) for 24 hr mi 2 km 2). 29' -STATUTE MILES ---1 25. 100 ? 190 200 390 100 o 100 260 3oo KILOMETERS 79' 75' 0\ IJl 99° 95" 91° 103° 99" 95° 91° 87" 83" Figure 56.--AZZ-season PMP (in.) for 48 hr mi 2 km 2 J. \-1\.-129' \II.=Z5.4i

---STATUTE MILES -1 25. 100 0 IQO 2QO 3QO u)o 6 ulo 200 J6o A6o KILOMmRS 79" 75° 0\ 0\

103' 99' 95' 91' 99' 95' 91' 87' 83' Figure 37.--AZZ-season PMP (in.) for 72 hr mi 2 km 2 J. . \ \-J -129' , ...

STATUTE MILES 1QO ? 190 2QO 3QO 100 0 160 260 300 A60 KILOMETERS 79' 75' (j\ .....

APPENDIX F AQTESOLV SLUG TEST ANALYSIS

AppendixF:AQTESSOLVERESULTSGW1A SlugIn#1Shine Medical Technologies 0.1.42.84.25.67.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002908 ft

/se cy0 = 0.4066 ft GW1A SlugOut#1Shine Medical Technologies 0.1.2.3.4.5.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003722 ft

/se cy0 = 0.2316 ft GW1A SlugIn#2Shine Medical Technologies0.1.2.3.4.5.1.0E-40.0010.010.1 Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003712 ft

/se cy0 = 0.03391 ft GW1A SlugOut#2Shine Medical Technologies 0.1.22.43.64.8 6.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002711 ft

/se cy0 = 0.1795 ft GW2A SlugIn#1Shine Medical Technologies 0.0.61.2 1.82.43.1.0E-40.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.007788 ft

/se cy0 = 0.09956 ft GW2A SlugOut#1Shine Medical Technologies 0.0.61.21.82.4 3.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003408 ft

/se cy0 = 0.2024 ft GW2A SlugIn#2Shine Medical Technologies 0.1.2.3.4.5.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.004141 ft

/se cy0 = 0.2165 ft GW2A SlugOut#2Shine Medical Technologies 0.1.2.3.4.5.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002999 ft

/se cy0 = 0.5741 ft GW2A SlugIn#3Shine Medical Technologies 0.1.22.43.64.86.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003751 ft

/se cy0 = 0.1545 ft GW2A SlugOut#3Shine Medical Technologies 0.2.4.6.8.10.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002038 ft

/se cy0 = 0.3552 ft GW3A SlugIn#1Shine Medical Technologies 0.0.81.62.43.24.0.0010.010.1 Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.005339 ft

/se cy0 = 0.08803 ft GW3A SlugOut#1Shine Medical Technologies 0.1.2.3.4.5.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.008109 ft

/se cy0 = 0.9739 ft GW3A SlugIn#2Shine Medical Technologies 0.0.40.81.21.6 2.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.008276 ft

/se cy0 = 0.4158 ft GW3A SlugOut#2Shine Medical Technologies 0.1.42.84.25.67.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.004267 ft

/se cy0 = 0.7386 ft APPENDIX G HYDROBENCH SLUG TEST VISUALIZATION

AppendixG:AQTESSOLVERESULTSGW1A SlugIn#1Shine Medical Technologies 0.1.42.84.25.67.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002908 ft

/se cy0 = 0.4066 ft GW1A SlugOut#1Shine Medical Technologies 0.1.2.3.4.5.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003722 ft

/se cy0 = 0.2316 ft GW1A SlugIn#2Shine Medical Technologies0.1.2.3.4.5.1.0E-40.0010.010.1 Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003712 ft

/se cy0 = 0.03391 ft GW1A SlugOut#2Shine Medical Technologies 0.1.22.43.64.8 6.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW1AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002711 ft

/se cy0 = 0.1795 ft GW2A SlugIn#1Shine Medical Technologies 0.0.61.2 1.82.43.1.0E-40.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.007788 ft

/se cy0 = 0.09956 ft GW2A SlugOut#1Shine Medical Technologies 0.0.61.21.82.4 3.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003408 ft

/se cy0 = 0.2024 ft GW2A SlugIn#2Shine Medical Technologies 0.1.2.3.4.5.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.004141 ft

/se cy0 = 0.2165 ft GW2A SlugOut#2Shine Medical Technologies 0.1.2.3.4.5.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002999 ft

/se cy0 = 0.5741 ft GW2A SlugIn#3Shine Medical Technologies 0.1.22.43.64.86.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.003751 ft

/se cy0 = 0.1545 ft GW2A SlugOut#3Shine Medical Technologies 0.2.4.6.8.10.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW2AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.002038 ft

/se cy0 = 0.3552 ft GW3A SlugIn#1Shine Medical Technologies 0.0.81.62.43.24.0.0010.010.1 Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.005339 ft

/se cy0 = 0.08803 ft GW3A SlugOut#1Shine Medical Technologies 0.1.2.3.4.5.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.008109 ft

/se cy0 = 0.9739 ft GW3A SlugIn#2Shine Medical Technologies 0.0.40.81.21.6 2.0.01 0.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.008276 ft

/se cy0 = 0.4158 ft GW3A SlugOut#2Shine Medical Technologies 0.1.42.84.25.67.0.0010.010.1 1.Ad justed Time (sec)H/H(0) in ftObs. WellsSM-GW3AAquifer ModelUnconfinedSolutionBouwer-RiceParametersK = 0.004267 ft

/se cy0 = 0.7386 ft

SEISMIC HAZARD ASSESMENT REPORT JANESVILLE, WISCONSIN

Submitted To: Dr. Gregory Piefer/CEO SHINE Medical Technologies 8123 Forsythia St., Suite 140 Middleton, WI 53562 Submitted By: Golder Associates Inc. 4438 Haines Road Duluth, MN 55811 USA

Distribution: Katrina Pitas, SHINE Medical Technologies Golder Associates Inc. Project No. 113-81051 Report No. Golder Report 5, Rev 4, August 3, 2012

SHINE Medical Technologies Seismic Hazard Report 1Report#5Executive Summary This report provides a summary of a seismic hazard assessment (SHA) completed by Golder Associates Inc. (Golder) for the site of the proposed SHINE medical isotope production facility in Rock County, Wisconsin. The SHA results include a summary of the geologic and tectonic history of a region within approximately 124 miles (200 km) of the SHINE site, a review of regional geologic structures to evaluate whether they are "capable" faults, a review of the historical record of felt and instrumentally-recorded earthquakes, estimation of the maximum earthquake potential, and the seismic parameters recommended for application of the 2009 International Building Code (2009 IBC) and American Society of Civil Engineers (ASCE) 7-05 standard. The geologic history of the basement rocks and the development and growth of major tectonic structures indicate that the SHINE site is located in a region of relative tectonic stability. Several post-500 million year old geologic structures have been mapped near the site, including the Sandwich and Plum River fault zones, the La Salle anticlinorium, and the Wisconsin and Kankakee Arches. These geologic structures appear to have formed and been seismogenic under a tectonic regime different from the present-day. No seismogenic "capable" faults are recognized within the SHINE site-the closest known "capable" faults are part of the Wabash Valley liquefaction features located about 170 miles (274 km) south of the site, and the New Madrid seismic zone located about 400 miles (644 km) south of the site. Within 124 miles (200 km) of the SHINE site, available earthquake catalogs contain only 35 epicenters for small to moderate earthquakes up to expected moment magnitude (E[

M]) 5.15 that have occurred since 1804. Interpretation of readily-available felt intensity records indicates that only moderate earthquake shaking (i.e., Modified Mercalli Intensity scale V) has probably been felt at the site four times in approximately the last 200 years. Estimates of seismic hazard for the region from the U.S. Geological Survey 2008 national seismic hazard maps indicate that the SHINE site is located within one of the lowest earthquake hazard areas in the conterminous United States. For example, a peak ground acceleration (PGA) value of 0.19 g (a moderate to strong level of earthquake ground shaking) has a return period estimated at more than 19,900 years. We evaluated the 2,475- to 19,900-year return period deaggregations of the national seismic hazard model for the SHINE site. Based on this model, a magnitude 5.8 earthquake is an acceptable estimate of the maximum earthquake magnitude expected for the SHINE site. Seismic parameters required for application of the 2009 IBC-ASCE 7-05 seismic design procedures are shown in Table ES-1 below.

2SHINE Medical Technologies Seismic Hazard Report Report#5Table ES-1 2009 IBC-ASCE 7-05 Seismic Parameters for the SHINE Site Parameter Value S S 0.129 g S 1 0.050 g Site Class D S MS 0.206 g S M1 0.119 g F a 1.6 F v 2.4 T L 12 seconds Notes: 1. Parameters based on SHINE site location of 42.624136°N, 89.024875°W. 2. Parameters include: short period spectral response acceleration (S S), 1-second spectral response acceleration (S 1), maximum considered earthquake spectral response for short period (S MS), maximum considered earthquake spectral response for 1-second period (S M1), site coefficient for short period (F a), site coefficient for 1-second pe-riod (F v) (IBC, 2009); long-period transition period (T L) (ASCE, 2005). 3. S S and S 1 are for Site Class B; S MS and S M1 for Site Class D.

Table of Contents

List of Tables List of Figures

5Report#5SHINE Medical Technologies Seismic Hazard Report 1.0) Introduction SHINE Medical Technologies (SHINE) proposes to construct a manufacturing plant for production of Molybdenum-99 (99Mo) at a site located south of the community of Janesville in Rock County, Wisconsin (Figure 1.1-1). SHINE has contracted Golder Associates Inc. (Golder) to provide a range of technical services in support of the environmental impact assessment, site application process for the U.S. Nuclear Regulatory Commission (USNRC), and groundwater hydrology and geotechnical engineering analysis for engineering design. To date, Golder has completed a range of subsurface boreholes, soil testing, groundwater assessment, and geotechnical analyses at the SHINE site (Golder, 2012a; 2012b; 2012c). The geotechnical analyses are to support initial engineering design of manufacturing and related facilities proposed at the SHINE site. One important aspect of both the site safety analysis process and engineering design is the assessment of seismic hazard at the site. While Wisconsin is not generally regarded as an area of high historical earthquake activity and seismic hazard, it remains necessary for engineering design to quantify the level of earthquake hazard at the site. Principal outputs of this seismic hazard assessment (SHA) are as follows:

• A description of the geologic, tectonic and seismic history of the region surrounding the SHINE site;

• An evaluation of the location and activity of any "capable" faults that could affect the SHINE site; and

• Seismic parameters recommended for structural analysis and design of both building and non-building structures as outlined in the 2009 IBC-ASCE 7-05 procedures. 1.1) Work Scope The full extent of professional services and associated tasks SHINE contracted from Golder are set out in Golder's proposal to Shine Medical Technologies on October 6, 2011 (Golder proposal P113-81051). For the SHA, Golder has undertaken the following office-based tasks:

• Acquire and review regional and site geology within the region of the SHINE site, including regional stratigraphy, regional geologic history and structural development, and location and seismic potential of any significant basement structures as indicated by the analysis of geophysical data such as magnetic and gravity anomalies, deep seismic reflection interpretations, and borehole measurements.

• Search online databases of historical seismicity to develop a project-specific historical epicenter catalog within the region of the SHINE site, including records of felt earthquake intensity (isoseismal maps) for the major historical earthquakes.

• Review available geologic information to evaluate the potential for seismically "capable" faults within the region of the SHINE site.

• Evaluate the seismic hazard at the site by obtaining estimates of peak ground acceleration (PGA) and spectral accelerations (S a) from the 2008 U.S. Geological 6Report#5SHINE Medical Technologies Seismic Hazard Report Survey (USGS) national seismic hazard maps and associated ground motion estimation tools.

• Recommend seismic parameters for application of the 2009 IBC-ASCE 7-05 standard procedures.

• Evaluate the Maximum Earthquake Potential for the site by completing a deaggregation of the 2008 USGS seismic hazard model to evaluate source(s) of the seismic hazard at a range of return periods from 475 to 19,900 years.

• Prepare this report, including figures, maps, tables, and databases. The principal purpose of this report is to summarize existing geologic and seismic information for the Shine site and surrounding region. The information is provided to contribute descriptions of the site geologic and seismic characteristics for the environmental impact assessment of the project. The seismic information contained in this report also forms part of the engineering analyses for the SHINE site. This report is not the Safety Analysis Report (SAR) for the site characteristics, which is at present in preparation. Golder has, however, reviewed the guidelines of NUREG 1537 Parts 1 and 2, Section 2.5 for non-power reactors so that information provided in this SHA is, wherever practical, compatible with the NUREG 1537 guidelines. The preparation of this report was undertaken following the Golder Quality Assurance Program Description (QAPD) (Golder, 2012d). Golder's Geotechnical Engineering Report for Janesville, Wisconsin (Golder, 2012a) provides a description of the QAPD. 1.2) Definitions For the purposes of this report we define the SHINE region as the area within a 124-mile (200 km) radius of the SHINE project site (SHINE site) near Janesville. For the assessment of the "capability" of the mapped faults, we use the definition of "capable" as set out in Appendix A of 10 CFR Part 100: a "capable" fault is a fault with at least one of the following: 1. Movement at or near the ground surface at least once within the past 35,000 years or movement of a recurring nature within the past 500,000 years. 2. Macro-seismicity instrumentally determined with records of sufficient precision to demonstrate a direct relationship with the fault. 3. A structural relationship to a capable fault according to characteristics above such that movement on one could be reasonably expected to be accompanied by movement on the other. The 10 CFR Part 100 definition of "capable" identifies faults that are considered capable of being the source of moderate to large earthquakes in the future. Evidence for the existence of capable faults is based on a geomorphic expression of surface fault rupture in surficial sediments that range in age from present day to 35,000 and/or 500,000 years old, instrumental evidence for the alignment of hypocenters that could indicate a subsurface fault; and in the case where these