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- AG-02NV-S-15-0024
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640 EAST WILMINGTON AVE SALT LAKE CITY UT 84106 TELEPHONE: 801-466-2223 FAX: 801-466-9616 E-MAIL: IHI@IHI-ENV.COM
SALT LAKE CITY SAN FRANCISCO PHOENIX DENVER SEATTLE
PRE-DEMOLITION INSPECTION FOR ASBESTOS AND
UNIVERSAL, HAZARDOUS, AND TOXIC WASTES
USDA Forest Service
Bridger-Teton National Forest Compound Jackson, Wyoming
Building TN822009
Visitor Information Center
September 5, 2014
Prepared for:
Mr. Kevin Lewis, Project Manager Case, Lowe & Hart, Inc.
2484 Washington Boulevard Ogden, Utah 84401
Prepared by: Reviewed by:
John C. Larson, Utah State Certification No. ASB-0894
AHERA Certification No. 130712
Jon H. Self Asbestos Program Manager
State of Utah Company Certification No. 22
IHI Project No. AL147459G
USDA FS/Visitor Information Center Table of Contents IHI Environmental Asbestos Inspection Project No. AL147459G
TABLE OF CONTENTS
EXECUTIVE SUMMARY
1.0 INTRODUCTION
1.1 Facility Description
1.2 Scope of Work
2.0 METHODOLOGY
2.1 Bulk Sample Collection
2.2 Bulk Sample Analysis
2.3 Bulk Sample Results
3.0 CONCLUSIONS AND DISCUSSION
3.1 Inaccessible Areas/Materials
4.0 PROJECT LIMITATIONS
TABLES
Table 1: Material Inspection Summary
APPENDICES
Appendix A: Laboratory Analytical Reports Appendix B: Photographic Log of Materials Sampled Appendix C: Asbestos Sampling Locations (Drawing) Appendix D: Universal, Hazardous, and Toxic Wastes Inspection Appendix E: Inspector Certifications
USDA FS/Visitors’ Information Center Executive Summary IHI Environmental
EXECUTIVE SUMMARY
On August 6, 2014, IHI Environmental conducted a pre-demolition inspection of the Visitor
Information Center building located at the USDA Forest Service, Bridger Teton National
Forest Compound, Jackson, Wyoming. Mr. Kevin Lewis, Project Manager for Case, Lowe and Hart, Inc., requested this inspection to identify asbestos-containing material (ACM) and
Universal, Hazardous, and Toxic Wastes materials that need to be addressed before the building is demolished or renovated. The following ACM and Universal, Hazardous, and
Toxic Wastes materials were identified during this inspection and assessment.
ACM
None
Universal, Hazardous, and Toxic Wastes
Mercury-vapor fluorescent light tubes (50 – 4-foot)
Ballasts containing PCBs (25)
Containers of liquid waste (TBD)
Table 1 in this Asbestos Inspection and Assessment Report contains detailed information about the suspect material sampled, and Section 2 (Findings) in the Universal, Hazardous, and Toxic Waste Inspection Report contains detailed information about the Universal, Hazardous, and Toxic Wastes.
CONCLUSIONS
ACM – No ACM was identified in this building. No further action is required.
Universal, Hazardous, and Toxic Wastes – Protocols for identification and disposal of hazardous materials have been developed by the Salt Lake County Health Department
(SLCHD). These protocols require building owners to identify and remove all Universal, Hazardous, and/or Toxic Wastes from buildings before they are demolished. Disposition of these materials must follow EPA Guidance outlined in 40 CFR 273 (Standards for Universal
Waste Management) and 40 CFR 261 and 262 (Resource Conservation and Recovery Act), and Department of Transportation regulations outlined at 49 CFR 173 (Shippers - General
Requirements for Shipments and Packaging). Using the same guidelines as the SLCHD sets
USDA FS/Visitors’ Information Center Executive Summary IHI Environmental forth in Utah, IHI recommends that the materials identified during this inspection be removed and disposed of by properly trained and licensed contractors.
COST ESTIMATES
IHI’s cost estimates to remove the ACM and remaining hazardous materials outlined above are:
ACM: None
Hazardous Materials: $430
These estimates do not include the costs for asbestos abatement design and management consulting services
The report that follows this Executive Summary should be read in its entirety because it includes important information, such as material descriptions and locations, regulatory requirements, and building specific recommended response actions.
USDA FS/Visitor’s Information Center 1 IHI Environmental
1.0 INTRODUCTION
On August 6, 2014, IHI Environmental conducted a pre-demolition inspection of the Visitor
Information Center building located at the USDA Forest Service, Bridger Teton National
Forest Compound, Jackson, Wyoming. Bulk samples of suspect asbestos-containing material were collected by Mr. John Larson (State of Utah, Asbestos Inspector Certification Number
ASB-0894) (AHERA Certification Number 130712). The State of Wyoming has a reciprocal agreement with the State of Utah and honors the same requirements for certification.
1.1 Facility Description
The building is a single-level structure with a 4’ crawlspace. Building size is approximately
1,472 square feet. Construction date is 1966. The construction is wood frame with a log exterior. Interior finishes are wood walls and ceilings, with coarse wood fiber panel ceilings in the north portion. The floors have carpeting and vinyl floor sheeting on a wood substrate.
The roof area has tar and felt build-up on a wood substrate. The building’s heating system consists of electrical radiant heaters. No cooling system was identified.
1.2 Scope of Work
The objective of this inspection was to locate, identify, quantify, and document the accessible suspect ACM, universal, hazardous and toxic wastes, and to provide a cost estimate for proper removal. The inspection was limited to accessible surfaces, structures, and mechanical systems with minor destructive sampling of wall cavities.
ACM is any material containing more than one percent asbestos, as determined by polarized light microscopy (PLM).
2.0 METHODOLOGY
Suspected ACM was identified and characterized in terms of homogeneous areas. A homogeneous area is defined as a single material, uniform in texture and appearance, installed at one time, and unlikely to consist of more than one type or formulation of material.
All suspect ACM was touched to determine its friability. Friable ACM, when dry, can be crumbled, pulverized, or reduced to powder by hand pressure.
USDA FS/Visitor’s Information Center 2 IHI Environmental
The inspector photographed each homogeneous area sampled. Photographs are included in
Appendix B of this report.
2.1 Bulk Sample Collection
Bulk samples were collected from accessible homogeneous areas of suspected ACM for subsequent laboratory analysis to determine actual asbestos content. Sampling was generally conducted in a manner that minimized damage and unsightly marks in the building and did not create a health hazard for building occupants or inspectors.
The number of samples collected from each homogeneous area generally followed the
Environmental Protection Agency (EPA) Asbestos Hazard Emergency Response Act
(AHERA) regulations (see 40 CFR part 763, subpart E), and the Wyoming Department of
Environmental Quality regulations, which generally follow the AHERA guidelines.
Although AHERA regulations do not apply to this property, the AHERA regulations provide the most comprehensive and acceptable guidance for conducting field inspections for ACM.
The AHERA regulations require the inspector to collect between three and seven samples of surfacing materials, depending on the size of the homogeneous area. Likewise, inspectors collect enough samples of thermal system insulation and miscellaneous materials to confidently characterize the material’s composition.
2.2 Bulk Sample Analysis
All bulk samples were analyzed by EMLab P&K, in Phoenix, AZ, using PLM in accordance with the EPA Method for the Determination of Asbestos in Bulk Building Materials (EPA-
600/R-93-116). EMLab P&K is accredited by the National Institute of Standards and
Technology (NIST) under the National Voluntary Laboratory Accreditation Program
(NVLAP).
2.3 Bulk Sample Results
Table 1 identifies all material sample numbers and locations, the homogeneous area number and description, and the quantity of the material. Appendix A includes the analytical reports provided by the laboratory. Appendix B contains photographs of each homogeneous area of suspect ACM identified during this inspection.
USDA FS/Visitor’s Information Center 3 IHI Environmental
3.0 CONCLUSIONS AND DISCUSSION
No ACM was identified in this building. No further action is required.
3.1 Inaccessible Areas/Materials
The storage room east of the west restroom was locked, with no accessible key. Suspect materials that were hidden or inaccessible may not have been characterized by this inspection. Therefore, any material not identified in this report as having been tested should be treated as suspect ACM until it has been sampled by a Wyoming-certified inspector and analyzed by an accredited laboratory applying EPA methods.
4.0 PROJECT LIMITATIONS
This project was performed using, as a minimum, practices consistent with standards acceptable within the industry at this time, and a level of diligence typically exercised by industrial hygiene consultants performing similar services.
The procedures used in this investigation attempt to establish a balance between the competing goals of limiting investigative and reporting costs and time, and reducing the uncertainty about unknown conditions. Therefore, because the findings of this report were derived from the scope, costs, time, and other limitations, the conclusions should not be construed as a guarantee that all hazardous materials have been identified and fully evaluated. IHI’s professional opinions are based in part on the interpretation of data from discrete sampling locations that may not represent conditions at non-sampled locations. IHI assumes no responsibility for omissions or errors resulting from inaccurate information, or data, provided by sources outside of IHI or from omissions or errors in public records.
Furthermore, it is emphasized that the final decision on how much risk to accept always remains with the client since IHI is not in a position to fully understand all of the client’s needs. Clients with a greater aversion to risk may want to take additional actions while others, with less aversion to risk, may want to take no further action.
Table 1
Material Inspection Summary
Material Sample #
Homogeneous Area Number, Material Description, & Location Lab Result Quantity Sample Location (See Appendix C)
47459G-1 M001: Wall panel – brown, plant fiber, tack-board – the south, main entry room, and the conference/meeting room.
None detected ~260 square feet South entry room, northeast corner
47459G-2 M002: Ceiling panel – coarse wood fiber with white binder – north area of the building None detected ~670 square feet West restroom, northeast corner
47459G-3 M003: Vinyl floor sheeting – cream, tan, and mauve small mosaic pattern – south, main entry room
None detected ~95 square feet South, main entry room, west doorway
47459G-4 M004: Wall system – gypsum board, tape and joint compound – north wall of the conference room
None detected ~195 square feet Conference room, north wall, west end light switch
47459G-5 M005: Sink undercoating – off-white– north wall of the conference room None detected 1 unit Conference room, north wall
47459G-6 M006: Carpet adhesive – tan – conference room, offices and hallway None detected ~1,210 square feet Conference room, south doorway
47459G-7 M007: Vinyl floor sheeting – cream, tile pattern – both restrooms None detected ~100 square feet West restroom, doorway
47459G-8 M008: Vinyl floor sheeting – off-white with brown splotches and gold flecks – north entry hallway/storage
None detected ~65 square feet North entry, northeast corner
47459G-9 M009: Exterior caulking – brown – south entry room exterior, and random other locations
None detected
~490 linear feet
South entry, north of the door
47459G-10 None detected South side of the south entry room
47459G-11 None detected East side of the south entry room
Table 1 Material Inspection Summary
Material Sample #
Homogeneous Area Number, Material Description, & Location Lab Result Quantity Sample Location (See Appendix C)
47459G-12 M010: Roofing material – tar and felt build-up with pea gravel – entire roof
None detected
~1,500 square feet
South edge of the south entry room
47459G-13 None detected East edge, south of the east entry
47459G-14 None detected North pitch, southwest area, approximately over the west restroom
Appendix A
Laboratory Analytical Reports
Approved by:
Approved Signatory Renee Luna
Report for:
Mr. John Larson IHI Environmental, Salt Lake City 640 E. Wilmington Avenue Salt Lake City, UT 84106
Regarding: Project: AL147459; Visitor Information Center
EML ID: 1246144
All samples were received in acceptable condition unless noted in the Report Comments portion in the body of the report. The results relate only to the items tested. The results include an inherent uncertainty of measurement associated with estimating percentages by polarized light microscopy. Measurement uncertainty data for sample results with >1% asbestos concentration can be provided when requested.
EMLab P&K ("the Company") shall have no liability to the client or the client's customer with respect to decisions or recommendations made, actions taken or courses of conduct implemented by either the client or the client's customer as a result of or based upon the Test Results. In no event shall the Company be liable to the client with respect to the Test Results except for the Company's own willful misconduct or gross negligence nor shall the Company be liable for incidental or consequential damages or lost profits or revenues to the fullest extent such liability may be disclaimed by law, even if the Company has been advised of the possibility of such damages, lost profits or lost revenues. In no event shall the Company's liability with respect to the Test Results exceed the amount paid to the Company by the client therefor.
Dates of Analysis:
Asbestos-EPA Method 600/R-93/116: 08-15-2014
Service SOPs: Asbestos-EPA Method 600/R-93/116 (EPA-600/M4-82-020 (SOP 01267))
EMLab ID: 1246144, Page 1 of 5Aerotech Laboratories, Inc
EMLab P&K 1501 West Knudsen Drive, Phoenix, AZ 85027
(800) 651-4802 Fax (623) 780-7695 www.emlab.com Client: IHI Environmental, Salt Lake City C/O: Mr. John Larson Re: AL147459; Visitor Information Center
Date of Sampling: 08-06-2014 Date of Receipt: 08-12-2014 Date of Report: 08-15-2014
ASBESTOS PLM REPORT: EPA-600/M4-82-020 & EPA METHOD 600/R-93-116
Total Samples Submitted: 14 Total Samples Analysed: 14
Total Samples with Layer Asbestos Content > 1%: 0
Location: 1, 47459G-1 Wall Panel Lab ID-Version‡: 5670750-1
Sample Layers Asbestos Content Brown Fibrous Material ND
Composite Non-Asbestos Content: 99% Cellulose Sample Composite Homogeneity: Good
Location: 2, 47459G-2 Ceiling Panel Lab ID-Version‡: 5670751-1
Sample Layers Asbestos Content Light Brown Wood ND
White Ceiling Texture with White Paint ND Composite Non-Asbestos Content: 90% Cellulose Sample Composite Homogeneity: Moderate
Location: 3, 47459G-3 Sheet Vinyl Lab ID-Version‡: 5670752-1
Sample Layers Asbestos Content Gray Sheet Flooring with Fibrous Backing ND
Composite Non-Asbestos Content: 15% Cellulose < 1% Glass Fibers < 1% Synthetic Fibers
Sample Composite Homogeneity: Good
Location: 4, 47459G-4 Wall System Lab ID-Version‡: 5670753-1
Sample Layers Asbestos Content White Drywall with Brown Paper ND
White Texture with Off-White Paint ND Composite Non-Asbestos Content: 10% Cellulose Sample Composite Homogeneity: Moderate
EMLab ID: 1246144, Page 2 of 5Aerotech Laboratories, Inc
The test report shall not be reproduced except in full, without written approval of the laboratory. The 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. EMLab P&K reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified.
Inhomogeneous samples are separated into homogeneous subsamples and analyzed individually. ND means no fibers were detected. When detected, the minimum detection and reporting limit is less than 1% unless point counting is performed. Floor tile samples may contain large amounts of interference material and it is recommended that the sample be analyzed by gravimetric point count analysis to lower the detection limit and to aid in asbestos identification.
‡ A "Version" indicated by -"x" after the Lab ID# with a value greater than 1 indicates a sample with amended data. The revision number is reflected by the value of "x".
(800) 651-4802 Fax (623) 780-7695 www.emlab.com Client: IHI Environmental, Salt Lake City C/O: Mr. John Larson Re: AL147459; Visitor Information Center
Date of Sampling: 08-06-2014 Date of Receipt: 08-12-2014 Date of Report: 08-15-2014
ASBESTOS PLM REPORT: EPA-600/M4-82-020 & EPA METHOD 600/R-93-116
Location: 5, 47459G-5 Sink Coating Lab ID-Version‡: 5670754-1
Sample Layers Asbestos Content Off-White Sink Undercoating ND
Sample Composite Homogeneity: Good
Location: 6, 47459G-6 Adhesive Lab ID-Version‡: 5670755-1
Sample Layers Asbestos Content Tan Mastic ND Composite Non-Asbestos Content: < 1% Cellulose Sample Composite Homogeneity: Good
Location: 7, 47459G-7 Sheet Vinyl Lab ID-Version‡: 5670756-1
Sample Layers Asbestos Content Brown Wood ND Cream Mastic ND
White Sheet Flooring ND Composite Non-Asbestos Content: 10% Cellulose Sample Composite Homogeneity: Good
Location: 8, 47459G-8 Sheet Vinyl Lab ID-Version‡: 5670757-1
Sample Layers Asbestos Content Tan Mastic ND
Gray Sheet Flooring with Fibrous Backing ND Composite Non-Asbestos Content: 15% Cellulose
< 1% Synthetic Fibers Sample Composite Homogeneity: Moderate
EMLab ID: 1246144, Page 3 of 5Aerotech Laboratories, Inc
The test report shall not be reproduced except in full, without written approval of the laboratory. The 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. EMLab P&K reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified.
Inhomogeneous samples are separated into homogeneous subsamples and analyzed individually. ND means no fibers were detected. When detected, the minimum detection and reporting limit is less than 1% unless point counting is performed. Floor tile samples may contain large amounts of interference material and it is recommended that the sample be analyzed by gravimetric point count analysis to lower the detection limit and to aid in asbestos identification.
‡ A "Version" indicated by -"x" after the Lab ID# with a value greater than 1 indicates a sample with amended data. The revision number is
(800) 651-4802 Fax (623) 780-7695 www.emlab.com Client: IHI Environmental, Salt Lake City C/O: Mr. John Larson Re: AL147459; Visitor Information Center
Date of Sampling: 08-06-2014 Date of Receipt: 08-12-2014 Date of Report: 08-15-2014
ASBESTOS PLM REPORT: EPA-600/M4-82-020 & EPA METHOD 600/R-93-116
Location: 9, 47459G-9 Exterior Caulk Lab ID-Version‡: 5670758-1
Sample Layers Asbestos Content Brown Caulk ND
Composite Non-Asbestos Content: < 1% Cellulose Sample Composite Homogeneity: Good
Location: 10, 47459G-10 Exterior Caulk Lab ID-Version‡: 5670759-1
Sample Layers Asbestos Content Brown Caulk ND
Composite Non-Asbestos Content: < 1% Cellulose Sample Composite Homogeneity: Good
Location: 11, 47459G-11 Exterior Caulk Lab ID-Version‡: 5670760-1
Sample Layers Asbestos Content Brown Caulk ND
Composite Non-Asbestos Content: < 1% Cellulose Sample Composite Homogeneity: Good
Location: 12, 47459G-12 Roof Core Lab ID-Version‡: 5670761-1
Sample Layers Asbestos Content Black Roofing Tar ND
Black Roofing Tar and Felt ND Black Roofing Tar and Felt ND
Composite Non-Asbestos Content: 10% Cellulose 5% Glass Fibers
Sample Composite Homogeneity: Poor
EMLab ID: 1246144, Page 4 of 5Aerotech Laboratories, Inc
The test report shall not be reproduced except in full, without written approval of the laboratory. The 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. EMLab P&K reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified.
Inhomogeneous samples are separated into homogeneous subsamples and analyzed individually. ND means no fibers were detected. When detected, the minimum detection and reporting limit is less than 1% unless point counting is performed. Floor tile samples may contain large amounts of interference material and it is recommended that the sample be analyzed by gravimetric point count analysis to lower the detection limit and to aid in asbestos identification.
‡ A "Version" indicated by -"x" after the Lab ID# with a value greater than 1 indicates a sample with amended data. The revision number is
(800) 651-4802 Fax (623) 780-7695 www.emlab.com Client: IHI Environmental, Salt Lake City C/O: Mr. John Larson Re: AL147459; Visitor Information Center
Date of Sampling: 08-06-2014 Date of Receipt: 08-12-2014 Date of Report: 08-15-2014
ASBESTOS PLM REPORT: EPA-600/M4-82-020 & EPA METHOD 600/R-93-116
Location: 13, 47459G-13 Roof Core Lab ID-Version‡: 5670762-1
Sample Layers Asbestos Content Brown Wood ND
Black Roofing Tar and Felt ND Black Roofing Tar and Felt ND Black Roofing Tar and Felt ND Black Roofing Tar and Felt ND
Composite Non-Asbestos Content: 15% Cellulose 2% Glass Fibers
Sample Composite Homogeneity: Poor
Location: 14, 47459G-14 Roof Core Lab ID-Version‡: 5670763-1
Sample Layers Asbestos Content Brown Wood ND
White Non-Fibrous Material ND Black Roofing Tar and Felt ND Black Roofing Tar and Felt ND
Composite Non-Asbestos Content: 20% Cellulose 3% Glass Fibers
Sample Composite Homogeneity: Poor
EMLab ID: 1246144, Page 5 of 5Aerotech Laboratories, Inc
The test report shall not be reproduced except in full, without written approval of the laboratory. The 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. EMLab P&K reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified.
Inhomogeneous samples are separated into homogeneous subsamples and analyzed individually. ND means no fibers were detected. When detected, the minimum detection and reporting limit is less than 1% unless point counting is performed. Floor tile samples may contain large amounts of interference material and it is recommended that the sample be analyzed by gravimetric point count analysis to lower the detection limit and to aid in asbestos identification.
‡ A "Version" indicated by -"x" after the Lab ID# with a value greater than 1 indicates a sample with amended data. The revision number is
Appendix B
Photographic Log of Materials Sampled
Photograph 1 Exterior view from the southwest.
Photograph 2 Non-ACM wall panel, homogeneous area M001.
Photograph 3 Non-ACM ceiling panel, homogeneous area M002.
Photograph 4 Non-ACM vinyl floor sheeting, homogeneous area M003.
Photograph 5 Non-ACM wall system, homogeneous area M004.
Photograph 6 Non-ACM sink undercoating, homogeneous area M005.
Photograph 7 Non-ACM carpet adhesive, homogeneous area M006.
Photograph 8
M007.
Photograph 9
M008.
Photograph 10 Non-ACM exterior caulking, homogeneous area M009.
Photograph 11 Non-ACM built-up roofing, homogeneous area M010.
Appendix C
Asbestos Sampling Locations (Drawing)
4 5
Mercury-Containing Fluorescent Light Tubes
Polychlorinated Biphenyl-Containing Light Ballast
Asbestos Sample Number & Location
Explanation
Note:
No Asbestos-Containing Materials Identified
Drawn By:
Checked By:
Approved By:
Project Mngr:
File No.
Date:
Scale:
Project No. FIG. No.
640 East Wilmington Avenue Salt Lake City, Utah
FAX. (801) 466-9616PH. (801) 466-2223
A
COMPANY
Visitor Information Center - Building # TN822009JHS
Keith
JCL
JRB
AL147459
1" = 10' - 0"
AL147459.dwg
August 2014
United States Forest Service Pre-Demolition Inspection Case Lowe & Hart, Inc.
340 North Cache Street Jackson, Wyoming
N
SCALE IN FEET
52.50 10
N P r o j e c t s A
L W o r k i n g
F i l e s D i a g r a m s D r a w i n g s F i g u r e s A
L d w g f i g b l d g g v i s t i n f o c n t r
A
M k f a r r e l l
A
N S
I f u l l b l e e d
A x
I n c h e s
Appendix D
Universal, Hazardous, and Toxic Wastes Inspection
640 EAST WILMINGTON AVE SALT LAKE CITY UT 84106 TELEPHONE: 801-466-2223 FAX: 801-466-9616 E-MAIL: IHI@IHI-ENV.COM
SALT LAKE CITY SAN FRANCISCO PHOENIX DENVER SEATTLE
UNIVERSAL, HAZARDOUS, AND TOXIC WASTE INSPECTION
USDA Forest Service Bridger-Teton National Forest Compound
Jackson, Wyoming
Building TN822009 Visitor Information Center
September 5, 2014
Prepared for:
Mr. Kevin Lewis, Project Manager Case, Lowe & Hart, Inc.
2484 Washington Boulevard Ogden, Utah 84401
Prepared by: Reviewed by:
John C. Larson, SL County Pre- Demo Building Inspector PBI-012
Jon H. Self Asbestos Program Manager
Project #AL147459G
USDA FS/Visitor Information Center IHI Environmental Hazmat Inspection Project No. AL147459G
TABLE OF CONTENTS
1.0 INTRODUCTION
2.0 METHODS
3.0 FINDINGS
4.0 CONCLUSIONS AND DISCUSSION
5.0 COST ESTIMATE
6.0 PROJECT LIMITATIONS
1.0 INTRODUCTION
On August 6, 2014, IHI Environmental conducted a pre-demolition inspection of the Visitor
Information Center building located at the USDA Forest Service, Bridger Teton National
Forest Compound, Jackson, Wyoming. Mr. Kevin Lewis, Project Manager for Case, Lowe and Hart, Inc., requested this inspection so that these materials could be identified and removed before demolition of this building.
The following materials were included in the scope of this inspection:
batteries pesticides mercury-containing thermostats and lamps
PCB light ballasts and oil-containing transformers identified and/or potential hazardous wastes
CFC-containing air conditioning units or refrigerators other containerized toxic or special wastes in the building
The building is a single-level structure with a 4’ crawlspace. Building size is approximately
1,472 square feet. Construction date is 1966.
2.0 METHODS
IHI conducted a visual inspection of all accessible areas throughout the building, but did not conduct any destructive inspection to characterize any material.
3.0 FINDINGS
The following materials were identified in the building:
Material Location Quantity Est. Removal
Cost
Mercury-vapor fluorescent light tubes Throughout 50 (4’) ~$130
Ballasts suspected of containing PCBs Throughout 25 Units ~$300
Material Location* Quantity Est. Removal
Cost
Containers of liquid waste Throughout TBD *Note
*Note: Liquid waste includes, but is not limited to, paints, thinners, pesticides, cleaners, and any other chemical compounds.
4.0 CONCLUSIONS AND DISCUSSION
Protocols for identification and disposal of hazardous materials have been developed by the
Salt Lake County Health Department (SLCHD). These protocols require building owners to identify and remove all Universal, Hazardous, and/or Toxic Wastes from buildings before they are demolished. Disposition of these materials must follow EPA Guidance outlined in
40 CFR 273 (Standards for Universal Waste Management) and 40 CFR 261 and 262
(Resource Conservation and Recovery Act), and Department of Transportation regulations outlined at 49 CFR 173 (Shippers - General Requirements for Shipments and Packaging).
Using the same guidelines as the SLCHD sets forth in Utah, IHI recommends that the materials identified during this inspection be removed and disposed of by properly trained and licensed contractors.
5.0 COST ESTIMATE
The estimated cost for the removal, packaging, transportation, and proper waste disposal of the remaining materials is approximately $430. This estimate does not include fees for design or management consulting services.
6.0 PROJECT LIMITATIONS
This Project was performed using, as a minimum, practices consistent with standards acceptable within the industry at this time, and a level of diligence typically exercised by
EH&S consultants performing similar services.
The procedures used attempt to establish a balance between the competing goals of limiting investigative and reporting costs and time, and reducing the uncertainty about unknown conditions. Therefore, because the findings of this report were derived from the scope, costs, time and other limitations, the conclusions should not be construed as a guarantee that all universal, toxic and/or hazardous wastes have been identified and fully evaluated.
Furthermore, IHI assumes no responsibility for omissions or errors resulting from inaccurate information, or data, provided by sources outside of IHI or from omissions or errors in public records.
It is emphasized that the final decision on how much risk to accept always remains with the client since IHI is not in a position to fully understand all of the client's needs. Clients with a greater aversion to risk may want to take additional actions while others, with less aversion to risk, may want to take no further action
Appendix E
Inspector Certifications
| Title Page |
| Table of Contents |
| Executive Summary |
| 1.0Introduction |
| 1.1 Facility Description |
| 1.2 Scope of Work |
| 2.0 Methodology |
| 2.1 Bulk Sample Collection |
| 2.2 Bulk Sample Analysis |
| 2.3 Bulk Sample Results |
| 3.0 Conclusions and Discussion |
| No ACM was identified in this building. No further action is required. |
| 3.1Inaccessible Areas/Materials |
| 4.0 Project Limitations |
| Appendix A - |
Laboratory Analytical Reports Appendix B - Photographic Log of Materials Sampled Appendix C - Asbestos Sampling Locations (Drawing) Appendix D - Universal, Hazardous, and Toxic Wastes Inspection Appendix E - Inspector Certifications
File details come from the government source that posted it. Updated .