Atch_4_Asbestos_Report_0003.pdf

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Attached to
WICA REHABILITATE ELEVATORS Federal contract opportunity
Solicitation number
140P6323B0013
Issued by
Department of the Interior National Park Service Midwest Region

About this file

This document contains an asbestos inspection report for the Elevator Building at Wind Cave National Park. Analytical testing found window glazing on the first floor south side containing 4% chrysotile asbestos. No other sampled materials were found to contain asbestos. The report recommends procedures for handling the non-friable asbestos-containing glazing and notes no other materials require special handling. The related federal contract opportunity is to rehabilitate elevators at Wind Cave National Park with solicitation number 140P6323B0013 issued by the Department of the Interior National Park Service Midwest Region.

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Text version

EMSL Analytical, Inc.

3410 Winnetka Avenue North New Hope, MN 55427

Tel/Fax: (763) 449-4922 / (763) 449-4924 http://www.EMSL.com / minneapolislab@emsl.com

352103314EMSL Order:

Customer ID: PRAE42

Customer PO:

Project ID:

Attention: Phone:Jason Biggins (605) 496-1366

Fax:Prairie Environmental Consulting, LLC

Received Date:309 N. Duluth Ave 04/22/2021 9:25 AM

Analysis Date:Apt. 2 04/22/2021

Collected Date:Sioux Falls, SD 57104

Project: Wind Cave National Park- Elevator Building (additional samples)

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

Light Microscopy

Sample Description Appearance % Fibrous % Non-Fibrous

Non-Asbestos Asbestos

% Type

WC-01-Floor Tile

352103314-0001

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Heterogeneous

Men's Restroom -

12x12 FT & adhesive

WC-01-Adhesive

352103314-0001A

None DetectedNon-fibrous (Other)100%Tan

Non-Fibrous

Heterogeneous

Men's Restroom -

12x12 FT & adhesive

WC-02-Wall Tile

352103314-0002

None DetectedNon-fibrous (Other)100%Pink

Non-Fibrous

Heterogeneous

Men's Restroom -

Wall tile & adhesive

(pink)

WC-02-Adhesive

352103314-0002A

None DetectedNon-fibrous (Other)100%Tan

Non-Fibrous

Heterogeneous

Men's Restroom -

Wall tile & adhesive

(pink)

WC-03-Wall Tile

352103314-0003

None DetectedNon-fibrous (Other)100%Black

Non-Fibrous

Heterogeneous

Men's Restroom -

Wall tile & adhesive

(black)

WC-03-Adhesive

352103314-0003A

None DetectedNon-fibrous (Other)100%Tan

Non-Fibrous

Heterogeneous

Men's Restroom -

Wall tile & adhesive

(black)

Analyst(s)

Rachel Travis (6) Rachel Travis, Laboratory Manager or Other Approved Signatory

EMSL maintains liability limited to cost of analysis . Interpretation and use of test results are the responsibility of the client. This report relates only to the samples reported above, 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 . The report reflects the samples as received.

Results are generated from the field sampling data (sampling volumes and areas, locations, etc.) provided by the client on the Chain of Custody. Samples are within quality control criteria and met method specifications unless otherwise noted. The above analyses were performed in general compliance with Appendix E to Subpart E of 40 CFR (previously EPA 600/M4-82-020 “Interim Method”) but augmented with procedures outlined in the 1993 (”final”) version of the method. 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 . Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Estimation of uncertainty is available on request.

Samples analyzed by EMSL Analytical, Inc. New Hope, MN NVLAP Lab Code 200019-0; Colorado AL-24478

Initial report from: 04/22/2021 18:10:59

Page 1 of 1ASB_PLM_0008_0001 - 1.78 Printed: 4/22/2021 5:11 PM

Asbestos Inspection Report Wind Cave National Park

Elevator Building

ASBESTOS BUILDING

INSPECTION

Prepared for:

Joshua Kreilaus

Prepared by:

Prairie Environmental Consulting, LLC

PO Box 1266 Sioux Falls, SD 57101

Inspection Date: April 6, 2021

Report Date: April 12, 2021

PROJECT SUMMARY

PROPERTY ADDRESS: Elevator Building – Wind Cave National Park

CLIENT: National Park Service – Wind Cave National Park

CONSULTANT: Prairie Environmental Consulting, LLC PO Box 1266 Sioux Falls, SD 57101

AHERA BUILDING INSPECTOR: Jason Biggins, SD Cert #8347

INSPECTION AND SAMPLING DATE: April 6, 2021

REPORT DATE: April 12, 2021

Executive Summary

Jason Biggins of Prairie Environmental Consulting, LLC was contacted by Joshua Kreilaus with NPS – Wind Cave regarding an asbestos inspection at the Elevator Buidling, located near the Visitor’s Center in Wind Cave National Park.

An asbestos inspection will help the determine if any materials require special consideration or should be removed prior to renovation of this property.

On April 6, 2021, Jason arrived on-site at 3:00pm to conduct the inspection.

Jason collected five asbestos bulk samples of materials within the building.

The analytical results indicate that the following building materials DO contain asbestos:

o Window Glaze – 1st fl E Window (S side) – 4% Chrysotile

The analytical results indicate that the following building materials do NOT contain asbestos:

o Window Glazing – Other 1st floor windows o Concrete o Sheet Flooring o 12x12 Floor Tile + Adhesive o Wall Tile + Adhesive

The following building materials were NOT sampled and are presumed to be asbestos-containing.

o None

Asbestos Bulk Sampling Methodology

Asbestos bulk samples were collected and placed in sample bags for laboratory analysis. This sampling was performed to identify asbestos in specific suspect asbestos-containing materials (ACM). The samples were submitted for standard turnaround time analysis via polarized light microscopy (PLM).

The PLM method is the most commonly used method to analyze the building materials for the presence of asbestos. The PLM method is in accordance with the EPA Interim Method of the Determination of Asbestos in Bulk Samples (EPA, July 1993). This method utilizes the optical properties of minerals to identify the selected constituent. The use of this method enables identification of the type and the percentage of asbestos in a sample.

The detection limit of the PLM method for asbestos identification is approximately one percent (1%) asbestos. PEC recommends Transmission Electron Microscopy (TEM) or Point Counting analysis for asbestos samples with trace, or less than one percent (<1%) when analyzed via PLM.

In some cases, samples collected from an apparently homogeneous material and yielding mixed results may, in face, have been taken from different homogeneous materials displaying similar visual characteristics buy composed of different constituents. Although materials may appear to be homogeneous, different manufacturers may have produced them in different batches. Materials, which appear to be homogeneous buy yield mixed results, are typically assumed, in accordance with AHERA procedures, to be asbestos containing in all areas where the materials are located.

PLM Asbestos Bulk Analysis Laboratory

Collected asbestos bulk samples were submitted under chain of custody for standard turnaround PLM analysis to EMSL Analytical in Minneapolis, MN. EMSL is NVLAP (#101234-0) accredited for bulk (PLM) asbestos analysis.

PLM Asbestos Bulk Sample Results

Positive samples identify building components as ACM. Asbestos-containing materials are regulated materials. ACM scheduled for disturbance or in poor condition are subject to handling and disposal according to all local, state, and federal regulations.

On April 6, 2021, a total of 5 bulk samples of what appeared to be 3 homogeneous area were collected at the subject property for PLM analysis.

Table 1: Laboratory Analytical Results

Sample No. Location Description Condition Asbestos Content

WC-01 1st Fl – Mens RR Concrete Friable – Undamaged NAD

WC-02 Mech Rm Linoleum Non-Friable – Damaged

NAD

WC-03 1st Fl – E Window (N) Window Glaze Non-Friable – Damaged

NAD

WC-04 1st Fl – E Window Central Window Glaze Non-Friable –

Damaged

NAD

WC-05 1st Fl – E Window (S) Window Glaze Non-Friable – Damaged

4% Chrysotile

Table 1: Laboratory Analytical Results

Sample No. Location Description Condition Asbestos Content

WC-01a Mens RR 12x12 FT Non-Friable - Undamaged NAD

WC-01b Mens RR 12x12 FT mastic Non-Friable – Undamaged

NAD

WC-02a Mens RR Wall Tile Non-Friable – Damaged

NAD

WC-02b Mens RR Wall Tile Adhesive (pink)

Non-Friable – Damaged

NAD

WC-03a Mens RR Wall Tile Non-Friable – Damaged

NAD

WC-03b Mens RR Wall Tile Adhesive (black)

Non-Friable – Damaged

NAD

The analytical results indicate that the following building materials DO contain asbestos:

o Window Glaze – 1st fl E Window (S side) – 4% Chrysotile

The analytical results indicate that the following building materials do NOT contain asbestos:

o Window Glazing – Other 1st floor windows o Concrete o Sheet Flooring o 12x12 Floor Tile + Adhesive o Wall Tile + Adhesive

The following building materials were NOT sampled and are presumed to be asbestos-containing.

o None

Conclusions

1. The window glazing on the 1st floor East Window (south end) contains 4% Chrysotile asbestos.

Recommendations

1. Because one window glazing sample came back as asbestos-containing, we must assume that other windows that were not tested contain glazing that is >1% asbestos, and must be considered asbestos-containing. The window glazing is considered a non-friable asbestos-containing material, even though sections of it are maginally damaged in some areas.

Limitations

The field observations, measurements, and research reported herein are considered sufficient in detail and scope to determine the asbestos content of the tested materials at the subject property. The assessment, conclusions, and recommendations presented herein are based upon specifically limited data.

They do no represent all conditions at the subject property as they reflect the information gathered for specific building systems. PEC warrants the findings and conclusions contain herein have been promulgated in accordance with generally accepted industrial hygiene methodology and only for the site described in this report.

Use by Third Parties

This report was prepared pursuant to the contract PEC has with the client. That contractual relationship included an exchance of information about the subject property that was unique and between PEC and its client and serves as the basis upon which this report was prepared. Because of the importance fo the communication between PEC and its client, reliance or any use of this report by anyone other than the client, for whom it was prepared, is prohibited and therefore not foreseeable to PEC.

Reliance or use by any such third party without explicit authorization in the report does not make said third party a third party beneficiary to PEC’s contract with the client. Any such unauthorized reliance on or use of this report, including any of its information or conclusions, will be at third party’s risk. For the same reasons, no warranties or representations, expressed or implied in this report, are made to any such third party.

Unidentifiable Conditions

This asbestos-related environmental consulting report has been developed to provide the client with information regarding apparent conditions related to limited accessible building materials in the subject property. Although PEC believes that the findings and conclusions provided in this report are reasonable, the assessment is necessarily limited to the conditions observed and to the information available at the time of the work. Due to the nature of the work, this is a possibility conditions exist that could not be identified within the scope of the assessment or which were not apparent at the time of our site work. The assessment is also limited to information available from the client at the time it was conducted. It is possible that the testing methods employed at the time of the report may later be superseded by other methods. PEC does not accept responsibility for changes in testing methods.

Prairie Environmental Consulting, LLC does not guarantee that all contaminated areas in the subject property were recognized during our evaluation. This report is limited only to the samples taken and locations sampled. Additional sampling may be needed to further identify other pollutants, or other affected areas inside the property.

We have employed state-of-the-art practices to perform this analysis of risk and identification, but this evaluation is limited in scope to the areas listed above. Our services consist of professional opinions and recommendations made in accordance with generally accepted engineering principles and practices, and are designed to provide an analytical tool to assist the client.

Prarie Environmental Consulting, LLC, or those representing Prairie Environmental Consulting, LLC bear no responsibility for the actual condition of the structure or safety of a site pertaining to IAQ contamination regardless of actions taken by the client.

Thank you for choosing Prairie Environmental Consulting, LLC to provide professional consulting services. If you have any questions regarding this report, please do not hesitate to contact us.

Certification:

I hereby attest that I am a certified asbestos inspector in the state of South Dakota and personally collected all samples and conducted the herein described inspection of the property.

Jason Biggins, South Dakota State Certified Asbestos Inspector SD Cert #8709

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