DRAFT - Subject to Change. Cathedral Building 212 North Ash Street Crookston, Minnesota. Prepared For. Project FA June 29, 2011

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Transcription:

DRAFT Phase I Environmental Site Assessment Cathedral Building 212 North Ash Street Crookston, Minnesota Prepared For Braun Intertec Corporation

Ms. Kay Hegge Prairie Skyline Foundation 27048 310th Street SW Crookston, MN 56716 Re: DRAFT Phase I Environmental Site Assessment Cathedral Building 212 North Ash Street Crookston, Minnesota Dear Ms. Hegge: In accordance with your written authorization, Braun Intertec conducted a Phase I Environmental Site Assessment (ESA) of the above-referenced site (Site). The objective of the Phase I ESA was to evaluate the Site for indications of recognized environmental conditions and to assist in satisfying All Appropriate Inquiries (AAI) standards and practices. The Phase I ESA was conducted in general conformance with the scope and limitations of ASTM Practice E 1527-05 and 40 CFR Part 312. The Phase I ESA was prepared on behalf of, and for use by the No other party has a right to rely on the contents of the Phase I ESA without written authorization by Braun Intertec. The Phase I ESA was prepared in association with the proposed restoration of the Site building. Please refer to the attached report for the scope, methods and conclusions of our assessment. We appreciate the opportunity to provide our professional services for you for this project. If you have any questions regarding this letter or the attached report, please contact Brad Schneider at 701.232.8701 or Ted Hubbes at 218.263.8869. Sincerely, BRAUN INTERTEC CORPORATION Bradly A. Schneider, PG Project Scientist Ted R. Hubbes, PG, CHMM Associate Principal Attachment: Phase I Environmental Site Assessment Report PH 1 ESA Cathedral Building, Crookston, MN

Table of Contents A. Introduction...1 A.1. Purpose...1 A.2. Scope of Services...1 A.3. User-Provided Information...3 A.3.a. Title Records...4 A.3.b. Environmental Liens...4 A.3.c. Activity and Use Limitations...4 A.3.d. Specialized Environmental Knowledge...4 A.3.e. Valuation Reduction for Environmental Issues...4 A.3.f. Commonly Known or Reasonably Ascertainable Information...5 B. Site Description...5 B.1. Site Location...5 B.2. Site Characteristics...5 B.3. Adjoining Property Use and Characteristics...5 C. Records Review...6 C.1. Physical Setting Information...6 C.1.a. Topography...6 C.1.b. Soil...6 C.1.c. Geology...6 C.1.d. Hydrogeology...6 C.2. Regulatory Information...7 C.2.a. Site...7 C.2.b. Adjoining Properties...7 C.2.c. Surrounding Area...8 C.3. Additional Government Records...8 C.3.a. City of Crookston...8 C.3.b. Polk County...8 C.3.c. Minnesota County Well Index...8 C.3.d. State Regulatory Web Pages...8 C.4. Historical-Use Information...9 C.4.a. Fire Insurance Maps...9 C.4.b. Historical Topographic Maps...9 C.4.c. Aerial Photographs...10 C.4.d. City Directory Information...10 C.5. Previous Environmental Documents...10 D. Interviews...10 E. Site Reconnaissance...11 E.1. Site Layout...11 E.2. Site Improvements...12 E.3. Site Land Use...12 E.4. Land-Surface Observations...12 E.5. Surface-Water Observations...12 E.6. Hazardous Substances...12 E.7. Petroleum Products...12 E.8. Storage Tanks...13

Table of Contents (Continued) E.9. Electrical and Hydraulic Equipment...13 E.10. Waste Disposal...13 E.11. Wastewater Discharges...13 E.12. Wells...13 E.13. Adjoining Property Observations...13 F. Limitations and Data Gaps...14 G. Findings...15 H. Opinions...15 H.1. Recognized Environmental Conditions...15 H.2. Historical Recognized Environmental Conditions...16 H.3. De Minimis Conditions...16 H.4. Additional Considerations...16 I. Conclusions...17 J. References...17 K. Environmental Professional Statement and Qualifications...18 Appendices A: Site Location Map B: Site Sketch C: Environmental Data Resources, Inc. Report D: Sanborn Maps E: Aerial Photographs F: Site Photographs G: References

Executive Summary Braun Intertec Corporation conducted a Phase I Environmental Site Assessment (ESA) of the cathedral building located at 212 North Ash Street in Crookston, Minnesota (Site) in general conformance with the scope and limitations of ASTM Practice E 1527-05 and 40 CFR Part 312. The Site was originally developed some time between 1896 and 1900 with a residential home along with the property adjacent to the north and south of the Site. Some time between 1906 and 1912, the residential home on the Site was demolished or removed from the Site. In 1912, the current Site building, which consists of an approximately 7,545-squared foot brick, three-tower neo-gothic style cathedral, was constructed on the Site. The cathedral was used by the Catholic church until approximately 1990 when the Catholic Diocese transferred ownership of the cathedral and associated rectory, located north of the Site, to a nearby homeless shelter. The cathedral has been left generally vacant and un-used since approximately 1990 and was in a general state of disrepair at the time of the reconnaissance. This assessment identified no recognized environmental conditions in connection with the Site.

A. Introduction A.1. Purpose Braun Intertec Corporation received authorization from Ms. Kay Hegge of Prairie Skyline Foundation, Inc. (Client) to conduct a Phase I Environmental Site Assessment (ESA) of the existing cathedral building located at 212 North Ash Street in Crookston, MN (Site). The objective of the Phase I ESA was to evaluate the Site for indications of recognized environmental conditions and to assist in satisfying All Appropriate Inquiries (AAI) standards and practices. The Phase I ESA was conducted in general conformance with the scope and limitations of ASTM Practice E 1527-05 and 40 CFR Part 312. The Phase I ESA was prepared on behalf of, and for the use by the (User) in accordance with the contract between and Braun Intertec, including the Braun Intertec General Conditions. No other party has a right to rely on the contents of the Phase I ESA without written authorization by Braun Intertec. All authorized parties are entitled to rely on the attached report according to our contract with Client, and under the same terms, conditions and circumstances. Please note that our contract with Client may contain a limitation of our total liability. If so, such limitation also applies to all those receiving this permission. According to the User, the Phase I ESA was conducted in association with the proposed restoration of the Site building. The purpose of this Phase I ESA was to evaluate the Site for indications of recognized environmental conditions. Recognized environmental conditions are defined by ASTM Practice E 1527-05 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. The term is not intended to include de minimis conditions that generally do not present a threat to human health or the environment and that generally would not be the subject of an enforcement action if brought to the attention of appropriate governmental agencies. A.2. Scope of Services Services provided for this project included:

Page 2 Preparing a description of the Site location, current use and improvements and surrounding area. Preparing a general description of the topography, soils, geology and groundwater flow direction at the Site. Reviewing reasonably ascertainable and practically reviewable regulatory information published by state and federal agencies, health, and/or environmental agencies. Reviewing the history of the Site, including aerial photographs, fire insurance maps, directories, and other readily available Site development data. Conducting a reconnaissance and environmental review of the Site, including observations of the Site for indications of hazardous materials, petroleum products, polychlorinated biphenyls (PCBs), wells, storage tanks, solid waste disposal, pits and sumps, and utilities. Conducting an area reconnaissance, including a brief review of adjoining property uses and pertinent environmental information noted in the Site vicinity. Interviewing current owners and/or occupants of the Site, and accessible past Site owners, operators and/or occupants. Interviewing local government officials or agencies having jurisdiction over hazardous waste disposal or other environmental matters in the area of the Site. Reviewing previous environmental reports prepared for the Site, if provided. Preparing a written report of our methods, results, and conclusions. The Standard Scope of the ASTM Practice E 1527-05 is not intended to provide a universal analysis of potential environmental risks and hazards. This assessment included no analysis of non-standard scope environmental risks and hazards unless otherwise listed above. Analysis of other non-standard scope issues by Braun Intertec would require additional contractual arrangements. This assessment does not include vapor encroachment screening as defined in ASTM Practice E2600-10, Standard Guide for Vapor Encroachment Screening on Property Involved in Real Estate Transactions. ASTM Practice E2600-10 is not a requirement or component of all appropriate inquiry, and its results

Page 3 are not determinative of whether hazardous substances from a release are or may be present at the property for the sake of all appropriate inquiry or ASTM E1527-05. The vapor encroachment screen is not within the scope of this Phase I ESA and will not be conducted unless specifically requested by the User. A.3. User-Provided Information The User as defined by ASTM Practice E 1527-05, is the party seeking to use ASTM Practice E 1527-05 to complete an environmental site assessment and may include, without limitation, a potential purchaser, tenant, or owner of a property, a lender, or a property manager. As stated in 40 CFR 312 (the rule), the Brownfields Amendments provide important liability protections for Users who qualify as contiguous property owners, bona fide prospective purchasers, or innocent landowners. To meet the statutory requirements for any of these Landowner Liability Protections (LLPs), a User must meet certain threshold requirements and satisfy certain continuing obligations. To qualify as one of the three LLPs, the User must perform all appropriate inquiries (AAI) on or before the date on which the User acquired the Site. The rule defines AAI, which includes inquiries and activities performed by the User and an environmental professional (EP). The rule allows (but does not mandate) the User performing AAI to conduct inquiries or activities that may include searches for environmental liens, assessments of any specialized knowledge on the part of the User, an assessment of commonly known or reasonably ascertainable information about the Site, and an assessment of the relationship of the purchase price to fair market value. These inquiries and assessments are separate and independent of the assessment conducted by the EP. However, if the User performing AAI conducts one or more of these inquiries and/or activities, the rule allows (but does not mandate) that the User may communicate information gathered from these inquiries and/or activities to their EP to identify a possible recognized environmental condition. Braun Intertec provided a User Questionnaire to the Client as a means to communicate information gathered from these inquiries and/or activities to the EP. The User may elect whether to communicate this information to the EP and/or to communicate this information to the EP by other means (e.g., through conversation or submission of documents). As indicated in our contract, if multiple Users are requesting reliance on the Phase I ESA, the Client was responsible for forwarding a copy of the questionnaire to all appropriate entities (collectively the User).

Page 4 User-supplied information is discussed in applicable sections of this report. Sections A.3.a through A.3.f present any information communicated to us by the User that the EP has determined to indicate the possible presence or likely presence of a recognized environmental condition. A.3.a. Title Records A chain of title includes a sequence of historical transfers of title to the Site. A chain-of-title search was not conducted as part of the scope of services for this assessment. The information provided to us by the User identified no record or awareness of information regarding chain-of-title ownership history of the Site. A.3.b. Environmental Liens An environmental lien is a charge, security, or encumbrance, upon title to the Site to secure the payment of a cost, damage, debt, obligation, or duty arising out of response actions, cleanup, or other remediation of environmental issues at the Site. The information provided to us by the User identified no record or awareness of information regarding any environmental liens recorded against the Site. A.3.c. Activity and Use Limitations AULs include, but are not limited to, engineering controls, land-use restrictions or institutional controls that are in place at the Site and/or have been filed or recorded in a registry under federal, tribal, state or local law. The information provided to us by the User identified no record or awareness of information regarding any AULs associated with the Site that could indicate the possibility of a recognized environmental condition. The user did note however that the property has deed restrictions based on its state designation on the national register of historic places. A.3.d. Specialized Environmental Knowledge Specialized environmental knowledge includes any information and/or experience related to the Site or adjoining properties including, but not limited to, any obvious indicators that point to the presence or likely presence of environmental issues at the Site. The information provided to us by the User identified no record or awareness of information regarding specialized environmental knowledge pertaining to the Site. A.3.e. Valuation Reduction for Environmental Issues Valuation reduction for environmental issues includes the relationship of the purchase price to the fair market value of the property. The information provided to us by the User identified no record or awareness of information that would indicate any reduction in purchase price or fair market value of the Site due to environmental issues with the possible exception of the following:

Page 5 The user noted that the building has not been saleable due to the existence of pigeon droppings in the building and the negative perception of the droppings as well as pigeon carcasses in the Site building. The user also noted the possible existence of mold and asbestos containing materials in the building. A.3.f. Commonly Known or Reasonably Ascertainable Information Commonly known or reasonable ascertainable information includes information about the Site that generally is known to the public within the community where the Site is located and can be easily sought and found from individuals familiar with the Site or from easily attainable public sources of information. The information provided to us by the User identified no record or awareness of information regarding commonly known or reasonably ascertainable information pertaining to the Site. B. Site Description B.1. Site Location The address for the Site is 212 North Ash Street, Crookston, MN. The approximate center of the Site is located at Latitude 47.774200 North and Longitude -96.604400 West. The Site is located within the NE quarter of the NW quarter of Section 31, Township 150 North, Range 46 West, in the city of Crookston, Polk County, Minnesota. A Site location map and Site sketch are attached in Appendices A and B, respectively. B.2. Site Characteristics At the time of the reconnaissance, the Site consisted of a parcel totaling approximately 0.26 acres. The Site was developed with an approximately 7,545-square-foot brick structure constructed in 1912. Landscaped areas including grass and trees surrounded the Site building. B.3. Adjoining Property Use and Characteristics The Site was bordered on the north by the Hope Center homeless shelter with 3rd Street west and the former Centeral Junior High School campus located beyond; on the east by a brick structure housing the boiler used to heat the Site building and an undeveloped flood plain followed by the Red Lake River located beyond; on the south by vacant undeveloped property with Central Park Drive and the

Page 6 Crookston Public Library located beyond; and on the west by North Ash Street with commercial development located beyond. The Site was located in a commercial and public property development within the City of Crookston. C. Records Review C.1. Physical Setting Information C.1.a. Topography According to the United States Geological Survey (U.S.G.S) 7.5-minute topographic map series, Crookston, Minnesota quadrangle, the Site is located at an elevation of approximately 890 feet above mean sea level. C.1.b. Soil We reviewed the United States Department of Agriculture (USDA) National Resources Conservation Service (NRCS) website to obtain soil information regarding the Site. According to the NRCS, the soil at the Site consists of silty clay loam of the Bearden-Colvin complex. The soils are described as having lacustrine parent material with high available water capacity. C.1.c. Geology According to the Geologic Map of Minnesota, Quaternary Geology by Howard C. Hobbs and Joseph E. Goebel, 1982, the near surface soils at the Site are Pleistocene to Late Wisconsinan age glacial lake sedments consisting of clay and clayey silt. C.1.d. Hydrogeology Based on the topographic map, the regional groundwater flow direction within the unconsolidated deposits in the vicinity of the Site is generally to the east southeast toward the Red Lake River. However, the local direction of groundwater flow may be affected by nearby streams, lakes, wells, and/or wetlands. The Site-specific groundwater flow direction was not determined through direct measurement during this Phase I ESA. Additional field investigation, beyond the Scope of Services of this Phase I ESA, would be required to determine this information.

Page 7 C.2. Regulatory Information We obtained regulatory information pertaining to the Site and surrounding area from Environmental Data Resources, Inc. (EDR). The EDR report is a compilation of records of facilities that are included on current federal and state environmental regulatory databases. The databases were searched based on the specified minimum search distances from the Site as established by ASTM Practice E 1527-05. The EDR report also includes a description, source reference, date of acquisition, and the specified approximate minimum search distance criteria for each database and list. A copy of the EDR report is attached in Appendix C. We reviewed the EDR report to identify records that indicate known or potential environmental hazards on the Site and/or surrounding area and to evaluate the likelihood for those hazards to impact the Site based on the information obtained in this Phase I ESA. C.2.a. Site The Site is not listed on the federal or state databases in the EDR report. C.2.b. Adjoining Properties The following facility, located west of North Ash Street, west of the Site, was identified in the EDR report: Qwest Communications, 119 E 2nd Street; located west of North Ash Street, west of the Site Site. The EDR report indicated that the facility is listed on the Leaking Underground Storage Tank (LUST) database. According to the EDR report, soil contamination was discovered at the facility in 1990 during an underground storage tank (UST) removal at the facility. Petroleum impacted soil was removed from the facility and no groundwater contamination was noted as a result of the leak. The facility was granted closure by the Minnesota Pollution Control Agency (MPCA) in September 1992 indicating that the impacts at the facility were addressed to the satisfaction of the MPCA. Based on the location of the closed status of the Quest Communications facility, the relative location of the facility to the Site and the noted lack of groundwater contamination at the facility, it appears unlikely that soil and/or groundwater contamination associated with the facility (if groundwater contamination exists) would have an adverse impact on the groundwater quality beneath the Site.

Page 8 C.2.c. Surrounding Area We reviewed the EDR report for facilities located beyond adjoining properties that may indicate a release or likely release of hazardous substances and/or petroleum products that may impact the Site. Based on factors that include regulatory status, distance from the Site, and/or location relative to the regional groundwater flow direction, as referenced in Section C.1, no facilities are identified in the EDR report that warrant further consideration as potential recognized environmental conditions. C.3. Additional Government Records C.3.a. City of Crookston We made inquiry to the following local government office and official with the City of Crookston to obtain knowledge or records of historical and current land-use information regarding the Site and surrounding area: Brian Halos, Captain for the City of Crookston Fire Department Section D of this report provides the discussion of the results of our inquiry and presents any applicable information obtained. C.3.b. Polk County No documents from Polk County were reviewed as part of this assessment. C.3.c. Minnesota County Well Index The Minnesota Geological Survey (MGS) maintains the Minnesota County Well Index (MCWI), which is a limited database of water well records. The MCWI was accessed through the Minnesota Department of Health (MDH) website. Not all private water wells are listed in that database. Our review of the MCWI database revealed no documentation of water wells located on the Site. C.3.d. State Regulatory Web Pages We accessed MPCA's Aboveground/Underground Storage Tank Site Search web page and MPCA's "What s In My Neighborhood" web pages for information regarding the potential for the Site, adjoining properties, or surrounding properties to be of environmental concern that were not identified in the FirstSearch report. No additional facilities not already identified in the EDR report were noted on the state regulatory web pages we accessed.

Page 9 C.4. Historical-Use Information The objective of the historical-use information review was to develop a history of the previous uses of the Site and surrounding area, to help evaluate the likelihood of past uses having led to recognized environmental conditions in connection with the property. We consulted only those historical sources that were readily available, practically reviewable, and likely to be useful to develop a history of previous uses of the Site and surrounding area within the time and cost constraints of this Phase I ESA. C.4.a. Fire Insurance Maps We retained EDR to obtain fire insurance maps of the Site and surrounding area. EDR provided fire insurance maps for the years 1884, 1890, 1896, 1900, 1906, 1913, 1922 and 1950. Copies of the Sanborn fire insurance maps are attached in Appendix D. 1884 1896 On the Sanborn maps from 1884 through 1896, the Site was vacant. The property in the vicinity of the Site was developed with churches and residential housing. The property north of the Site was vacant. 1900 1906 A residential home wais located on the Site on the 1900 and 1906 Sanborn maps. Residential homes were located on the property surrounding the Site with the exception of the property east of the Site, which was vacant, and the property west of North Ash street, where the Northwestern Telephone company building existed. 1913 1950 The cathedral was located on the Site in the Sanborn maps from 1913 through the 1950. The property immediately surrounding the Site was generally unchanged. North Ash street was located west of the Site in all of the Sanborn maps reviewed from 1884 through 1950. C.4.b. Historical Topographic Maps The USGS topographic map used for the figure in Appendix A is dated 1982. The cathedral was visible on the Site. No indications of issues of environmental concern were apparent at the Site on the map.

Page 10 C.4.c. Aerial Photographs We retained HIG to obtain aerial photographs of the Site and surrounding area. HIG provided aerial photographs for the years 1939, 1948, 1954, 1958, 1966, 1974, 1977, 1982, 1991, 2003 and 2010. Copies of the aerial photographs are attached in Appendix E. 1939 1982 The cathedral was visible on all of the aerial photographs from 1939 through 1982. The surrounding property appeared to be developed, in general, as it was at the time of the reconnaissance with the exception of Central Park Drive, south of the Site, which was not visible in the aerial photographs. 1991 2010 No significant changes were noted at the Site or surrounding area with the exception of the addition of Central Park Drive, which was visible on aerial photographs beginning in 1991. C.4.d. City Directory Information We retained HIG to obtain city directory information pertaining to the Site and surrounding area. HIG provided city directories for North Ash Street for various years from 1899 to 2009. Due to the number of documents the city directories are not included as an appendix. From 1899 through the 1904, the Site address of 212 North Ash Street was listed as residential housing. There were no addresses listed for the Site in the 1911 city directory. Starting with the city directory in 1915 through 1984, the cathedral is listed at the Site. In the 1987 directory, the Site address is listed as vacant, and in the directories from 1988 through 2009, the Site address is the location of a women s shelter. C.5. Previous Environmental Documents No previous environmental documents were reviewed as part of this assessment. D. Interviews We contacted the following individuals to obtain knowledge or historical and current land-use information regarding the Site: Ms. Kay Hegge, Board Chair (Site representative)

Page 11 Ms. Hegge was not aware of the use of any petroleum products used or stored at the Site. She also stated that she was not aware of any aboveground or underground storage tanks located on the Site and that to the best of her knowledge, there was no PCB containing equipment located on the Site. Ms. Hegge noted that the brick structure locted adjacent to the Site to the northeast of the Site building was the location of the boiler used to provide steam heat to the Site building in the past. To the best of her knowledge, any fuel associated with the boiler plant used to heat the Site building, was located off-site in the adjacent building and steam was supplied via a crawl space connecting the buildings. Ms. Hegge stated that she was not aware of environmental concerns at the Site with the exception of possible asbestos containing building materials and/or lead paint. In addition, she mentioned the need to address any pigeon droppings and pigeon carcasses which are known to be inside the Site building. Braun Intertec made inquiry to the the City of Crookston Fire Department in order to obtain knowledge or records of historical and current land-use information regarding the Site and surrounding area: Brian Halos, Captain for the City of Crookston Fire Department Mr. Halos indicated that besides the potential for hazardous building materials, pigeon droppings and carcasses and possibly mold inside the Site building, he was not aware of any environmental concerns associated with the Site. E. Site Reconnaissance A Braun Intertec environmental scientist, Brad Schneider, conducted a Site reconnaissance on June 20, 2011. We were unaccompanied during the Site reconnaissance. At the time of the Site reconnaissance, the weather was overcast with a temperature of about 75 degrees Fahrenheit. E.1. Site Layout At the time of the reconnaissance, the Site topography was relatively flat with a slope downward, away from the Site, toward the south and east. The drainage on the Site appeared to be toward south and east away from the Site toward the Red Lake River basin, in addition, drainage from the west portion of the Site was likely toward storm water catch basins located along North Ash Street. The cathedral

Page 12 building is located centrally on the Site with grasses, shrubs and a few trees located around the Site building. A Site Sketch and Site Photographs are attached in Appendices B and F, respectively. E.2. Site Improvements At the time of the reconnaissance, the Site was connected to municipal water and sanitary sewer services. The Site building had been heated using steamradiators. The steam was supplied by a boiler located in a brick structure located adjacent to the Site, northeast of the Site building. Steam entered the Site building via an underground crawl space connecting the buildings. The Site building was surrounded by grasses and shrubs. E.3. Site Land Use At the time of the reconnaissance, the Site was occupied with a brick, three-tower neo-gothic style cathedral building which was vacant and in a general state of disrepair. We did not access the interior of the Site building durig our reconnaisance. E.4. Land-Surface Observations No indications of any storage areas, waste disposal areas, observed fill or graded areas, burn pits or other land-surface observations were observed at the Site at the time of the reconnaissance. E.5. Surface-Water Observations No indications of surface-water features were observed at the Site at the time of our reconnaissance. E.6. Hazardous Substances No indications of current and/or historic use, storage or spills of hazardous substance were observed at the Site at the time of the reconnaissance. E.7. Petroleum Products No indications of current and/or historic use, storage or spills of petroleum product were observed at the Site at the time of the reconnaissance.

Page 13 E.8. Storage Tanks No indications of aboveground or underground storage tanks (AST/UST) were noted at the Site at the time of the reconnaissance. E.9. Electrical and Hydraulic Equipment No indications of potentially PCB-containing electrical or hydraulic equipment were noted at the Site at the time of the reconnaissance. E.10. Waste Disposal No indication of the uncontrolled disposal of solid waste or dumping was apparent on the Site at the time of the reconnaissance. E.11. Wastewater Discharges No indications of wastewater discharge was observed at the Site at the time of the reconnaissance. Municipal sewer services are available to the Site. E.12. Wells No indications of water wells were observed at the Site at the time of the reconnaissance. Municipal water services are available to the Site. E.13. Adjoining Property Observations No observations of environmental concern were noted on adjoining properties to the Site at the time of the reconnaissance.

Page 14 F. Limitations and Data Gaps The findings and conclusions presented in this report are based on procedures described in ASTM Practice E 1527-05, inquiries with public officials, available literature cited in this report, conditions noted at the time of our Phase I ESA, and our interpretation of the information obtained as part of this Phase I ESA. Our findings and conclusions are limited to the specific project and properties described in this report and by the accuracy and completeness of information provided by others. An environmental site assessment cannot wholly eliminate uncertainty regarding the potential for recognized environmental conditions in connection with a property. Performance of this practice is intended to reduce, but not eliminate, uncertainty regarding the potential for recognized environmental conditions in connection with a property within reasonable limits of time and cost. In performing its services, Braun Intertec used that degree of care and skill ordinarily exercised under similar circumstances by reputable members of its profession currently practicing in the same locality. No warranty, express or implied, is made. The following limitation was encountered: We did not have access to the inside of the Site building at the time of the reconnaissance. The identified limitation did not affect the environmental professional s ability to render opinions regarding conditions indicative of a release or threatened release. No data gaps were identified during the Phase I ESA process, with the exception of the following: Historical resources were not readily available for 5-year-or-less intervals from the time of the first developed use. The identified data gaps did not affect the environmental professional s ability to render opinions regarding conditions indicative of a release or threatened release. There have been no responses to our inquiries from local officials. An addendum will be provided if information is received after the issuance of this report that alters the findings of this report.

Page 15 G. Findings The findings include identified known or suspect recognized environmental conditions, historical recognized conditions, de minimis conditions and additional issues in connection with the Site. The following findings are based on the results of our assessment: Information regarding the Site was available back to 1884. The information indicates that the Site was originally developed from the late 1890s to some time between 1906 and 1912 with a residential home. The current Site building was constructed on the Site in 1912. The Site building has been vacant and generally unused since approximately 1990. According to the EDR Report, one closed LUST facility is locted west of North Ash Street, west of the Site. H. Opinions According to the User, the Phase I ESA was conducted in association with the proposed restoration of the Site building. Opinions expressed herein are influenced by the stated reason for conducting the Phase I ESA. Furthermore, the expressed opinions might not be applicable to alternate reasons for reliance on the content of the Phase I ESA. H.1. Recognized Environmental Conditions A recognized environmental condition, as defined by ASTM Practice E 1527-05 is 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 of storage and use in compliance with laws. This assessment identified no recognized environmental conditions in connection with the Site.

Page 16 H.2. Historical Recognized Environmental Conditions Historical recognized environmental conditions are conditions that were or would have been considered to be recognized environmental conditions in the past, but because of further information or a change of conditions may no longer be considered recognized environmental conditions. This assessment identified no historical recognized environmental conditions in connection with the Site. H.3. De Minimis Conditions A de minimis condition is a condition that generally does not present a threat to human health or the environment and that generally would not be the subject of an enforcement action if brought to the attention of regulatory governmental agencies. The following findings are considered de minimis conditions: The Site was vacant or developed for residential purposes since at least the late 1800s. It is our opinion that the use of the Site for agricultural and residential purposes is considered a de minimis condition for the Site. The Qwest Communications building located at 119 E. 2nd Street, located west of the Site is listed on the EDR report as a closed LUST facility. The information reviewed indicates that no groundwater impacts were noted at the facility and that the UST was removed during the investigation. The LUST facility was closed in 1992 and it is our opinion that the identified regulated facility is considered de minimis condition. H.4. Additional Considerations Historically, a residential building was located on the Site. It is unknown if the demolition debris associated with the building was buried on the Site or hauled away for disposal. The potential exists that buried materials are present at the Site that require management as solid or hazardous waste. If fill soils are encountered during future activities at the Site, which could include demolition debris and other wastes, additional evaluation of the fill soils might be required for management and disposal purposes. Because the Site building has been vacant for approximately 21 years and there has been damage to the structure due to weather and lack of maintenance, the Site representative indicated that pigeons

Page 17 have occupied a portion of the Site building. Also, it was noted that a large number of pigion droppings and carcasses are decaying inside the structue. In addition, due to the state of dis-repair, it has been noted that there may be mold and possibly damaged asbestos containing building materials inside the structure. I. Conclusions We have conducted this Phase I ESA of the Site in general conformance with the scope and limitations of ASTM Practice E 1527-05. Any exceptions to, or deletions from, this practice are described in Section G of this report. This assessment identified no recognized environmental conditions in connection with the Site. This assessment identified no historical recognized environmental conditions in connection with the Site. J. References References are listed in Appendix G.

Page 18 K. Environmental Professional Statement and Qualifications 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 allappropriate inquiries in conformance with the standards and practices set forth in 40 CFR Part 312. A Braun Intertec Statement of Qualifications for this Phase I ESA project will be provided to the User upon request. We declare that, to the best of our professional knowledge and belief, we meet the definition of Environmental Professional as defined in 312.10 of 40 CFR 312. BRAUN INTERTEC CORPORATION Bradly A. Schneider, PG Project Scientist Ted R. Hubbes, PG, CHMM Associate Principal

Appendix A Site Location Map

Appendix B Site Sketch

Appendix C Environmental Data Resources, Inc. Report

Appendix D Sanborn Maps

Appendix E Aerial Photographs

Appendix F Site Photographs

Appendix G References

Environmental Protection Agency 40 CFR Part 312 Standards and Practices for All Appropriate Inquiries; Final Rule; Vol. 70, No. 210; Tuesday, November 1, 2005; Rules and Regulations Hobbs, Howard C.; and Goebel, Joseph E.; 1982; Quaternary Geology; Geologic Map of Minnesota: University of Minnesota-Minnesota Geological Survey, State Map Series S-1, Scale 1:500,000. Minnesota County Well Index: http://www.health.state.mn.us/divs/eh/cwi/ Minnesota Pollution Control Agency Aboveground/Underground Storage Tank Site Search web page: http://www.pca.state.mn.us/programs/lust_psearch.cfm Minnesota Pollution Control Agency's What's In My Neighborhood web page: http://pcagis02.pca.state.mn.us/wimn2/index.html Standard Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process, 2005, Annual Book of ASTM Standards, Vol. 11.04, E 1527-05