Asbestos and Hazardous/Regulated Material Survey Report For the Vacant Residential Property Located at:

5391 Crane Detroit, Michigan P.O. #: 1.27.2016D Project # ABF-16-1799 Date: March 7, 2016 Prepared by:

Prepared for:

ABF Environmental 28200 Orchard Lake Road, Suite 101 Farmington Hills, Michigan, 48334 Phone: 586-405-5416

James Wright Detroit Building Authority 1301 Third Street, Suite 328 Detroit, MI 48226

___________________________ Michael Piddington State Certified Inspector #A32756

Table of Contents 1.0

INTRODUCTION ................................................................................................................................. 1

2.0

SUMMARY OF FINDINGS ................................................................................................................... 1

3.0

RECOMMENDATIONS........................................................................................................................ 3

4.0

LIMITATIONS ..................................................................................................................................... 4

TABLE 1 (ASBESTOS-CONTAINING MATERIALS) ............................................................................................ 1 TABLE 2 (HAZARDOUS/ REGULATED MATERIALS) ........................................................................................ 2

APPENDICES APPENDIX A - INSPECTOR ACCREDITATION APPENDIX B - LABORATORY ANALYTICAL RESULTS AND CHAIN OF CUSTODY FORMS APPENDIX C - EXHIBITS D, E, H, I, AND SITE DIAGRAM(S)

APPENDIX D - SITE PHOTOGRAPHS

1.0

INTRODUCTION

On February 17, 2016, State of Michigan Asbestos Inspector, Michael Piddington (A32756), conducted a pre-demolition asbestos and hazardous/regulated material survey of the unoccupied residential property located at 5391 Crane in Detroit, Michigan. The dwelling is a two-story home with a basement. Debris was present throughout the dwelling. A copy of the inspector’s proof of accreditation with the State of Michigan is provided in Appendix A. The purpose of this survey was to task an accredited asbestos inspector to complete a predemolition asbestos and hazardous/regulated material survey of the site and provide recommendation options for removal and disposal prior to demolition of the building. All areas were accessible. 2.0

SUMMARY OF FINDINGS

The following Tables listed below provide a summary of findings for the pre-demolition asbestos and other regulated materials survey. Table 1 identifies the asbestos-containing materials (>1% asbestos) identified during the survey, their locations, approximate quantity, type and percentage of asbestos. TABLE 1 (ASBESTOS-CONTAINING MATERIALS) ID#

Material

Location

Approximate Quantity

Result

6 A-C

Caulk

Exterior

Not Estimated

2% Chrysotile

SF-Square Feet, LF-Linear Feet

The suspect ACM that was sampled and found to not contain more than one percent asbestos is presented on Exhibit D in Appendix B. A copy of required forms Exhibit D, E, H, and I, including a site diagram is provided in Appendix C. Samples were analyzed by a NVLAP certified laboratory (certificate attached) by polarized light microscopy (PLM) using first positive stop. Sampling methodology and QA/QC are indicated on the attached laboratory results. No other suspect ACM was observed on the Site. Although not anticipated based on surface observations, underground structures that could contain ACM may be present and should be managed accordingly if encountered prior to our during demolition. Abatement of ACMs, including non-friable ACMs, must be performed by a State of Michigan licensed, certified and registered asbestos abatement contractor in accordance with state and federal Occupational Safety and Health Administration (OSHA) and local air quality management regulations. Sampling procedures were performed in accordance with Asbestos Hazard Emergency Response Act, 40 CFR Part 763 (AHERA) protocols by State of Michigan licensed asbestos inspectors. Elements of the asbestos building inspections were based on practices specified in the National

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Emission Standards for Hazardous Air Pollutants (NESHAPS), Michigan Public Act 440 of 1988, U.S. Environmental Protection Agency (EPA) and Occupational Safety and Health Administration (OSHA) standards and included the identification of homogeneous areas within the subject facilities, bulk sample collection of suspect materials, and laboratory analysis. Field activities were performed by Accredited Asbestos Building Inspectors as recognized by the State of Michigan Department Labor and Economic Growth (MDLEG) who have met the requirements of Section 206 of the Toxic Substances Control Act and the Asbestos School Hazard Abatement Reauthorization Act (ASHARA). Sample locations were selected to be representative of homogeneous materials identified within the buildings. Samples were obtained in a manner to minimize damage and, where possible, were collected from previously exposed/damaged locations. Factors used in the selection of sample locations included accessibility, potential for occupant exposure, and/or general safety. Photographs of each side of the building followed by photographs of sample location areas are provided in Appendix D. Lead-based paint may be present on the site and is a hazardous substance. Its condition, handling and disposal are regulated by federal, state, and local agencies. LBP generally does not pose a health threat unless particles are disturbed, become airborne and are inhaled or ingested. Contractors and their employers that will be disturbing the building during demolition should follow all applicable requirements in the OSHA Lead in Construction Standard. Further testing may be required of debris generated from demolition activities to determine whether the debris should be disposed as hazardous waste under the Resource Conservation and Recovery Act (RCRA) in accordance with 40-CFR Part 261 Subpart C. We also performed an Hazardous/ Regulated Materials (ORM) assessment of the site structure to identify potential areas/ items of environmental concern in/on the structures that require decontamination or disposal prior to demolition. The Other Regulated Materials identified within the structure are identified in the following table, including locations and quantities. TABLE 2 (HAZARDOUS/ REGULATED MATERIALS) Floor

IOI Description

Location

Quantity

Units

Comments

Disposal Concern

1

CRTs, TVs, Screens, Electronics

Room 2, 8

2

Each

TVs

Mercury

1-2

Misc. Items (Glues, Solvents, Cleaners)

Room 1, 11

10

Each

1 gallon or less

Disposal

1

Paint Cans

Room 1, 2

50

Each

Size

Page 2

VOCs

3.0

RECOMMENDATIONS

Except for the following items listed below, Section 61.145(c) of the Asbestos NESHAP requires that each owner or operator of a demolition or renovation activity involving RACM remove all such material from a facility being demolished or renovated before any activity begins that would break up, dislodge, or similarly disturb the material or preclude access to the material for subsequent removal. Contractors performing asbestos abatement should notify the State of Michigan in accordance with NESHAP, 40 CFR Part 61, Subpart M and State requirements. ACM need not be removed before demolition if it: (i) Is a Category I non-friable ACM that is not friable. (ii) Is on a facility component that is encased in concrete or other similarly hard material and is adequately wet whenever exposed during demolition. (iii) Was not accessible for testing and therefore was not discovered until after demolition began and, as a result of the demolition, cannot be safely removed. If not removed for safety reasons, the exposed RACM and any asbestos-contaminated debris must be treated as asbestoscontaining waste material and kept adequately wet at all times until disposed of. (iv) Is a Category II non-friable ACM and the probability is low that the material will become crumbled, pulverized, or reduced to powder during demolition. Demolition with Roofing Materials in Place is covered under the NESHAP regulations (40 CFR Part 61 Subpart M). Roofing materials (if found to be asbestos containing) is considered a Category I asbestoscontaining material. Since demolition activities do not include sanding, grinding, cutting, or abrading, Category I asbestos-containing roofing materials not in poor condition and not friable are not considered RACM and are allowed to remain in place during demolition. If the asbestos-containing roofing material is not in poor condition and is not friable, it may be disposed of in a landfill which accepts ordinary demolition waste. The asbestos-containing roofing material may not be ground up for recycling into other products. In addition, contractors should ensure they follow all OSHA regulations pertaining to demolition of Category I Asbestos-containing materials. Category I or II non-friable ACM that is not subject to 61.150(a)(3) would still have to be disposed of in a landfill that accepts building debris, in a landfill that operates in accordance with 61.154, or at a facility that operates in accordance with 61.155. Prior to demolition, the following is recommended:

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A licensed asbestos abatement company in the State of Michigan should remove the materials identified in Table 1 in accordance with all applicable Local, State, and Federal Requirements prior to demolition. Removal, transportation, disposal and / or recycling activities for the ORMs should be performed by a licensed contractor with training and experience in handling the items identified, in accordance with all applicable regulations. 4.0

LIMITATIONS

The results, findings, conclusions, and recommendations expressed in the report are based only on conditions that were noted during the assessment of the vacant above-referenced residential property. Any conditions or materials that could not be visually identified through limited destructive sampling were not inspected and may differ from those conditions or materials noted. The user of this report should keep in mind that conditions at the time of the site reconnaissance may not be consistent with future observations made by others. If during demolition, asbestos containing materials are identified or if suspect asbestoscontaining materials that were not previously identified and/or samples are encountered, work should stop, access to the suspect material should be restricted, and sampling should be performed by a State of Michigan licensed asbestos inspector. Any positive ACMs must be abated by a licensed asbestos abatement contractor. The report is designed to aid the building owner, architect, construction manager, general contractors, and potential asbestos abatement contractors in locating asbestos building materials to be removed prior to demolition activities. This report is not intended to be utilized as a bidding document or as a project specification document. Contractors bidding the demolition of this site should field verify project information.

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APPENDIX A INSPECTOR ACCREDITATION

APPENDIX B LABORATORY ANALYTICAL RESULTS AND CHAIN OF CUSTODY FORMS

EMSL Analytical, Inc.

EMSL Order: 161602526

2001 East 52nd St. Indianapolis, IN 46205 Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / [email protected]

Customer ID: ABFE34 Customer PO: ABF-16-1799 Project ID: ABF-DLB

Attention: Fredrick Abdou ABF Environmental

Phone: (586) 405-5416 Fax: Received Date: 02/18/2016 10:05 AM Analysis Date: 02/22/2016 Collected Date: 02/17/2016

28200 Orchard Lake Rd. Suite 101 Farmington Hills, MI 48334 Project: 5391 CRANE / ABF-16-1799 - ABF-DLB (ABF-DLB)

Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Sample

Description

Appearance

1A

W. Plaster

Gray/White Non-Fibrous Heterogeneous

161602526-0001

% Fibrous

<1% Hair

Asbestos % Non-Fibrous

% Type

15% Quartz 85% Non-fibrous (Other)

None Detected

100% Non-fibrous (Other)

None Detected

20% Quartz 80% Non-fibrous (Other)

None Detected

100% Non-fibrous (Other)

None Detected

20% Quartz 80% Non-fibrous (Other)

None Detected

100% Non-fibrous (Other)

None Detected

20% Quartz 80% Non-fibrous (Other)

None Detected

100% Non-fibrous (Other)

None Detected

20% Quartz 80% Non-fibrous (Other)

None Detected

100% Non-fibrous (Other)

None Detected

Inseparable paint / coating layer included in analysis

1B-Finish Coat

W. Plaster

161602526-0002

White Non-Fibrous Homogeneous

Inseparable paint / coating layer included in analysis

1B-Base Coat

W. Plaster

Gray Non-Fibrous Homogeneous

W. Plaster

White Non-Fibrous Homogeneous

161602526-0002A

1C-Finish Coat 161602526-0003

<1% Hair

Inseparable paint / coating layer included in analysis

1C-Base Coat

W. Plaster

Gray Non-Fibrous Homogeneous

C. Plaster

White Non-Fibrous Homogeneous

C. Plaster

Gray Non-Fibrous Homogeneous

C. Plaster

White Non-Fibrous Homogeneous

161602526-0003A

2A-Finish Coat 161602526-0004

2A-Base Coat 161602526-0004A

2B-Finish Coat 161602526-0005

<1% Hair

<1% Hair

Inseparable paint / coating layer included in analysis

2B-Base Coat

C. Plaster

Gray Non-Fibrous Homogeneous

C. Plaster

White Non-Fibrous Homogeneous

161602526-0005A

2C-Finish Coat 161602526-0006

<1% Hair

Inseparable paint / coating layer included in analysis

2C-Base Coat

C. Plaster

Gray Non-Fibrous Homogeneous

<1% Hair

20% Quartz 80% Non-fibrous (Other)

None Detected

Ext. Siding

Various Fibrous Heterogeneous

60% Cellulose

40% Non-fibrous (Other)

None Detected

Ext. Siding

Various Fibrous Heterogeneous

60% Cellulose

40% Non-fibrous (Other)

None Detected

Ext. Siding

Various Fibrous Heterogeneous

50% Cellulose

50% Non-fibrous (Other)

None Detected

Carp. Mast.

Brown Non-Fibrous Homogeneous

100% Non-fibrous (Other)

None Detected

161602526-0006A

3A 161602526-0007

3B 161602526-0008

3C 161602526-0009

4A 161602526-0010

Initial Report From: 02/22/2016 12:12:23

PLM - 1.67 Printed: 2/22/2016 12:12 PM

Page 1 of 3

EMSL Analytical, Inc.

EMSL Order: 161602526

2001 East 52nd St. Indianapolis, IN 46205 Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / [email protected]

Customer ID: ABFE34 Customer PO: ABF-16-1799 Project ID: ABF-DLB

Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Description

Appearance

4B

Carp. Mast.

Brown Non-Fibrous Homogeneous

100% Non-fibrous (Other)

None Detected

Carp. Mast.

Brown Non-Fibrous Homogeneous

100% Non-fibrous (Other)

None Detected

Mortar

Gray Non-Fibrous Homogeneous

20% Quartz 80% Non-fibrous (Other)

None Detected

Mortar

Gray Non-Fibrous Homogeneous

20% Quartz 80% Non-fibrous (Other)

None Detected

Mortar

Gray Non-Fibrous Homogeneous

20% Quartz 80% Non-fibrous (Other)

None Detected

Caulk

Black Non-Fibrous Homogeneous

100% Non-fibrous (Other)

<1% Chrysotile

Black Non-Fibrous Homogeneous

100% Non-fibrous (Other)

None Detected

Black Non-Fibrous Homogeneous

98% Non-fibrous (Other)

2% Chrysotile

161602526-0011

4C 161602526-0012

5A 161602526-0013

5B 161602526-0014

5C 161602526-0015

6A 161602526-0016

% Fibrous

Asbestos

Sample

% Non-Fibrous

% Type

The sample group is not homogeneous

6B

Caulk

161602526-0017

The sample group is not homogeneous

6C

Caulk

161602526-0018

The sample group is not homogeneous

7A

Basement C.T.

Brown/White Fibrous Homogeneous

95% Cellulose

5% Non-fibrous (Other)

None Detected

Basement C.T.

Brown/White Fibrous Homogeneous

95% Cellulose

5% Non-fibrous (Other)

None Detected

Basement C.T.

Brown Fibrous Homogeneous

98% Cellulose

2% Non-fibrous (Other)

None Detected

Wire

Black Fibrous Heterogeneous

30% Cellulose

70% Non-fibrous (Other)

None Detected

Wire

Black Fibrous Heterogeneous

30% Cellulose

70% Non-fibrous (Other)

None Detected

Wire

Black Fibrous Heterogeneous

25% Cellulose

75% Non-fibrous (Other)

None Detected

Roof

Brown/Black Fibrous Heterogeneous

20% Glass

80% Non-fibrous (Other)

None Detected

Roof

Black Fibrous Heterogeneous

20% Glass

80% Non-fibrous (Other)

None Detected

Roof

Brown/Black Fibrous Heterogeneous

20% Glass

80% Non-fibrous (Other)

None Detected

Roof

White/Black/Green Fibrous Heterogeneous

30% Cellulose

70% Non-fibrous (Other)

None Detected

161602526-0019

7B 161602526-0020

7C 161602526-0021

8A 161602526-0022

8B 161602526-0023

8C 161602526-0024

9A-Shingle 161602526-0025

9A-Shingle 161602526-0025A

9B-Shingle 161602526-0026

9B-Shingle 161602526-0026A

Initial Report From: 02/22/2016 12:12:23

PLM - 1.67 Printed: 2/22/2016 12:12 PM

Page 2 of 3

EMSL Analytical, Inc.

EMSL Order: 161602526

2001 East 52nd St. Indianapolis, IN 46205 Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / [email protected]

Customer ID: ABFE34 Customer PO: ABF-16-1799 Project ID: ABF-DLB

Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Description

Appearance

9C-Shingle

Roof

Brown/Black Non-Fibrous Homogeneous

15% Glass

85% Non-fibrous (Other)

None Detected

Roof

White/Black Fibrous Heterogeneous

30% Cellulose

70% Non-fibrous (Other)

None Detected

161602526-0027

9C-Shingle 161602526-0027A

% Fibrous

Asbestos

Sample

% Non-Fibrous

% Type

Analyst(s)

Craig Nixon (23) Jadda Moffett (12)

Richard Harding, Laboratory Manager or Other Approved Signatory

EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Indianapolis, IN NVLAP Lab Code 200188-0, AZ0939, CA 2575, CO AL-15132, TX 300262

Initial Report From: 02/22/2016 12:12:23

PLM - 1.67 Printed: 2/22/2016 12:12 PM

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APPENDIX C EXHIBITS D, E, H, I, AND SITE DIAGRAM(S)

APPENDIX D SITE PHOTOGRAPHS