36C25020B0008-0001002.pdf

PDF Posted Jan 16, 2020

Attached to: Expand East Parking 610-312
Solicitation number: 36C25020B0008
Issued by: Department of Veterans Affairs Veterans Health Administration Veterans Integrated Service Network 10

About this file

Written by GovTribe AI · Dec 29, 2023

This document provides details on an upcoming federal construction contract opportunity and an asbestos inspection report for the related project site. The solicitation will be for demolition of an existing structure and construction of a new parking lot at the Fort Wayne VA Medical Center. Work must be performed in accordance with contract drawings and specifications. The requirement is set aside solely for Service-Disabled Veteran-Owned Small Businesses. The North American Industry Classification Code is 236220 for commercial and institutional building construction. The contract value is estimated between $500,000 and $1,000,000. The asbestos inspection report identifies various homogeneous areas at the project site location and whether sampled materials contained asbestos.

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36C25020B0008 0001 610-312_Specs Updated 1.16.2020_Part2.pdf

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Asbestos Homogeneous Area (HA) and Sampling Summary

Samples Collected By:

Location: 2333 Lake Avenue, Fort Wayne, Indiana Mike Ardis

No.

Description

Type of

ACBM ¹

Approx.

Quantity

(Entire HA) ² Friable?

(Yes/No)

Damage (N,L,M,H) ³

Sample No. Sample Location Asbestos Content

Pre-Demo Building Inspection

19-0047-AL-001

Date Collected

(via Method EPA 600/R-93/116 and/or EPA Method 600/M4-82-020)

Project:

Date Collected: 4/16/2019 4/16/2019 -

Alliance Project Number:

PD-02 Plaster over Drywall (Ceiling Plaster - Base

Coat)

SM N/A No L 021B Garage None Detected4/16/2019

FT-03 9" x 9" Light Brown with White Streaks Floor Tile

MISC Approx 500 Total SF

No L 022A Basement % Chrysotile24/16/2019

FT-03 Mastic Associated with 9" x 9" Light Brown with

White Streaks Floor Tile

MISC Approx 500 Total SF

No L 022B Basement % Chrysotile24/16/2019

FT-04 9" x 9" Brown with Splotches Floor Tile

MISC Approx 500 Total SF

No L 023A Basement % Chrysotile24/16/2019

FT-04 Mastic Associated with 9" x 9" Brown with Splotches

Floor Tile

MISC Approx 500 Total SF

No L 023B Basement % Chrysotile24/16/2019

FT-05 9" x 9" Dark Brown with Splotches

MISC Approx 500 Total SF

No L 024A Basement % Chrysotile24/16/2019

FT-05 Mastic Associated with 9" x 9" Dark Brown with

Splotches

MISC Approx 500 Total SF

No L 024B Basement % Chrysotile<14/16/2019

G-01 Interior Window Glazing MISC 36 LF (6 Windows)

Yes L 025 Basement % Chrysotile<0.254/16/2019

G-01 Interior Window Glazing MISC 36 LF (6 Windows)

Yes L 026 Basement % Chrysotile<0.254/16/2019

BM-01 Ceramic Tile MISC N/A No L 027A Hallway Bathroom None Detected4/16/2019

BM-01 Black Mastic Associated with Ceramic Tile

MISC N/A No L 027B Hallway Bathroom None Detected4/16/2019

SM = Surfacing Material; TSI = Thermal System Insulation; Misc. = Miscellaneous Material N = None; L = Low; M = Medium; H = HighSF = Square Feet; LF = Linear Feet; FTG = Fitting1 2 3

Location: 2333 Lake Avenue, Fort Wayne, Indiana Mike Ardis

No.

Description

Type of

ACBM ¹

Approx.

Quantity

(Entire HA) ² Friable?

(Yes/No)

Damage (N,L,M,H) ³

Sample No. Sample Location Asbestos Content

Pre-Demo Building Inspection

19-0047-AL-001

Date Collected

(via Method EPA 600/R-93/116 and/or EPA Method 600/M4-82-020)

Project:

Date Collected: 4/16/2019 4/16/2019 -

Alliance Project Number:

BM-01 Grout Associated with Ceramic Tile

MISC N/A No L 027C Hallway Bathroom None Detected4/16/2019

BM-01 Ceramic Tile MISC N/A No L 028A Hallway Bathroom None Detected4/16/2019

BM-01 Black Mastic Associated with Ceramic Tile

MISC N/A No L 028B Hallway Bathroom None Detected4/16/2019

BM-01 Grout Associated with Ceramic Tile

MISC N/A No L 028C Hallway Bathroom None Detected4/16/2019

AI-01 Brown Blown-In Insulation MISC N/A Yes L 029 Attic None Detected4/16/2019

AI-01 Brown Blown-In Insulation MISC N/A Yes L 030 Attic None Detected4/16/2019

DT-01 Old Duct Tape on HVAC - Tape

MISC N/A Yes L 031A Attic None Detected4/16/2019

DT-01 Old Duct Tape on HVAC - Mastic

MISC N/A Yes L 031B Attic None Detected4/16/2019

DT-01 Old Duct Tape on HVAC - Tape

MISC N/A Yes L 032A Attic None Detected4/16/2019

DT-01 Old Duct Tape on HVAC - Mastic

MISC N/A Yes L 032B Attic None Detected4/16/2019

C-01 White Exterior Caulking MISC N/A No L 033 South Exterior Door None Detected4/16/2019

C-01 White Exterior Caulking MISC N/A No L 034 Northeast Exterior Door None Detected4/16/2019

CP-01 Exterior Cementitious Panel

MISC Approx 1,200

No L 035 South Exterior Wall % Chrysotile204/16/2019

SM = Surfacing Material; TSI = Thermal System Insulation; Misc. = Miscellaneous Material N = None; L = Low; M = Medium; H = HighSF = Square Feet; LF = Linear Feet; FTG = Fitting1 2 3

Location: 2333 Lake Avenue, Fort Wayne, Indiana Mike Ardis

No.

Description

Type of

ACBM ¹

Approx.

Quantity

(Entire HA) ² Friable?

(Yes/No)

Damage (N,L,M,H) ³

Sample No. Sample Location Asbestos Content

Pre-Demo Building Inspection

19-0047-AL-001

Date Collected

(via Method EPA 600/R-93/116 and/or EPA Method 600/M4-82-020)

Project:

Date Collected: 4/16/2019 4/16/2019 -

Alliance Project Number:

CP-01 Exterior Cementitious Panel

MISC Approx 1,200

No L 036 South Exterior Wall Stop Positive4/16/2019

R-01 Roofing Material MISC Approx 2700

No L N/A Roof Assumed Positive4/16/2019

SM = Surfacing Material; TSI = Thermal System Insulation; Misc. = Miscellaneous Material N = None; L = Low; M = Medium; H = HighSF = Square Feet; LF = Linear Feet; FTG = Fitting1 2 3

Sample ID

Client:

Project Location:

Alliance Project Number:

Collected By:

Collection Date: Description Analytical Results

% by weight

Veridian Architectural Design 2333 Lake Avenue, Fort Wayne, Indiana

Lead in Paint Chips

19‐0047‐AL‐001

Benjamin Hood

Lead in Paint Chips via Method SW‐846‐3050B*/7000B

Comments

001 Garage 2.0% wt White Paint04/16/2019

002 Garage <0.0089% wt Brown‐Over‐Green Paint04/16/2019

OSHA ‐ If lead is present, work must be performed in accordance with OSHA Lead Standards

EMSL Analytical, Inc.

6340 CastlePlace Dr. Indianapolis, IN 46250

Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / indianapolislab@emsl.com

161907079EMSL Order:

Customer ID: ALLI65

Customer PO:

Project ID:

Attention: Phone:Michael Ardis (317) 865-3400

Fax:Alliance Environmental Group, Inc. (317) 865-3401

Received Date:5153 Commerce Square Drive 04/17/2019 2:59 PM

Analysis Date:Suite E 04/23/2019 - 04/24/2019

Collected Date:Indianapolis, IN 46237 04/16/2019

Project: 19-0047-AL-001

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

001-Floor Tile

161907079-0001

None DetectedNon-fibrous (Other)100%Brown/Tan

Non-Fibrous

Homogeneous

Kitchen - 12x12 Tan w/ Brown Streaks

Floor Tile & Mastic

HA: FT-01

001-Mastic

161907079-0001A

None DetectedNon-fibrous (Other)100%Black

Non-Fibrous

Homogeneous

Kitchen - 12x12 Tan w/ Brown Streaks

Floor Tile & Mastic

HA: FT-01

002-Floor Tile

161907079-0002

None DetectedNon-fibrous (Other)100%Brown/Tan

Non-Fibrous

Homogeneous

Laundry Area - 12x12

Tan w/ Brown Streaks

Floor Tile & Mastic

HA: FT-01

002-Mastic

161907079-0002A

None DetectedNon-fibrous (Other)100%Black

Non-Fibrous

Homogeneous

Laundry Area - 12x12

Tan w/ Brown Streaks

Floor Tile & Mastic

HA: FT-01

003-Cove Base

161907079-0003

None DetectedNon-fibrous (Other)100%Brown

Non-Fibrous

Homogeneous

Kitchen - Brown Cove

Base & Mastic

HA: CB-01

003-Mastic

161907079-0003A

None DetectedNon-fibrous (Other)100%Tan/Yellow

Non-Fibrous

Homogeneous

Kitchen - Brown Cove

Base & Mastic

HA: CB-01

004-Cove Base

161907079-0004

None DetectedNon-fibrous (Other)100%Brown

Non-Fibrous

Homogeneous

Laundry Area - Brown

Cove Base & Mastic

HA: CB-01

004-Mastic

161907079-0004A

None DetectedNon-fibrous (Other)100%Tan

Non-Fibrous

Homogeneous

Laundry Area - Brown

Cove Base & Mastic

HA: CB-01

161907079-0005

3% ChrysotileNon-fibrous (Other)97%Black

Non-Fibrous

Homogeneous

Kitchen - Black Sink

Undercoat

HA: SI-01

161907079-0006

Positive Stop (Not Analyzed)Kitchen - Black Sink

Undercoat

HA: SI-01

007-Plaster

161907079-0007

None DetectedQuartz

Perlite

Non-fibrous (Other)

10%

88%

Gray

Fibrous

Heterogeneous

Kitchen - Plaster over

Drywall (Wall)

HA: PD-01

007-Drywall

161907079-0007A

None DetectedGypsum

Non-fibrous (Other)

70%

10%

Cellulose20%Brown/White

Fibrous

Heterogeneous

Kitchen - Plaster over

Drywall (Wall)

HA: PD-01

Initial report from: 04/24/2019 09:36:15

Page 1 of 5ASB_PLM_0008_0001 - 1.78 Printed: 4/24/2019 9:36 AM

Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / indianapolislab@emsl.com

161907079EMSL Order:

Customer ID: ALLI65

Customer PO:

Project ID:

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

008-Plaster

161907079-0008

None DetectedQuartz

Non-fibrous (Other)

10%

85%

Cellulose5%Gray

Fibrous

Heterogeneous

Living Room - Plaster over Drywall (Wall)

HA: PD-01

008-Drywall

161907079-0008A

None DetectedGypsum

Non-fibrous (Other)

70%

10%

Cellulose20%Brown/White

Fibrous

Heterogeneous

Living Room - Plaster over Drywall (Wall)

HA: PD-01

009-Finish Coat

161907079-0009

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Laundry Area -

Plaster over Drywall

(Ceiling)

HA: PD-02

009-Base Coat

161907079-0009A

None DetectedPerlite

Non-fibrous (Other)

10%

90%

Gray

Non-Fibrous

Homogeneous

Laundry Area -

Plaster over Drywall

(Ceiling)

HA: PD-02

010-Finish Coat

161907079-0010

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Northwest Bedroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

010-Base Coat

161907079-0010A

None DetectedPerlite

Non-fibrous (Other)

10%

88%

Cellulose2%Gray

Non-Fibrous

Homogeneous

Northwest Bedroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

011-Floor Tile

161907079-0011

None DetectedNon-fibrous (Other)100%Gray

Non-Fibrous

Homogeneous

Hall Bathroom -

12x12 Off-White w/

Gray Streaks Floor

Tile & Mastic

HA: FT-02

011-Mastic

161907079-0011A

None DetectedNon-fibrous (Other)100%Black

Non-Fibrous

Homogeneous

Hall Bathroom -

12x12 Off-White w/

Gray Streaks Floor

Tile & Mastic

HA: FT-02

012-Floor Tile

161907079-0012

None DetectedNon-fibrous (Other)100%Gray

Non-Fibrous

Homogeneous

Hall Bathroom -

12x12 Off-White w/

Gray Streaks Floor

Tile & Mastic

HA: FT-02

012-Mastic

161907079-0012A

None DetectedNon-fibrous (Other)100%Black

Non-Fibrous

Homogeneous

Hall Bathroom -

12x12 Off-White w/

Gray Streaks Floor

Tile & Mastic

HA: FT-02

161907079-0013

None DetectedQuartz

Non-fibrous (Other)

95%

White

Non-Fibrous

Homogeneous

Hallway - 1st Floor -

Off-White Floor

Leveler

HA: FL-01

161907079-0014

None DetectedQuartz

Non-fibrous (Other)

95%

White

Non-Fibrous

Homogeneous

Hallway - 1st Floor -

Off-White Floor

Leveler

HA: FL-01

161907079-0015

None DetectedQuartz

Perlite

Non-fibrous (Other)

10%

88%

Gray

Non-Fibrous

Heterogeneous

Living Room - Plaster over Drywall (Wall)

HA: PD-01

161907079-0016

None DetectedQuartz

Perlite

Non-fibrous (Other)

10%

88%

Cellulose<1%Gray

Non-Fibrous

Heterogeneous

Garage - Plaster over

Drywall (Wall)

Page 2 of 5ASB_PLM_0008_0001 - 1.78 Printed: 4/24/2019 9:36 AM

Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / indianapolislab@emsl.com

161907079EMSL Order:

Customer ID: ALLI65

Customer PO:

Project ID:

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

HA: PD-01

161907079-0017

None DetectedQuartz

Perlite

Non-fibrous (Other)

10%

88%

Gray

Non-Fibrous

Heterogeneous

Hallway - 1st Floor -

Plaster over Drywall

(Wall)

HA: PD-01

018-Finish Coat

161907079-0018

None DetectedQuartz

Non-fibrous (Other)

10%

90%

White

Non-Fibrous

Homogeneous

North Bedroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

018-Base Coat

161907079-0018A

None DetectedPerlite

Non-fibrous (Other)

10%

90%

Gray

Non-Fibrous

Homogeneous

North Bedroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

019-Finish Coat

161907079-0019

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Hallway Bathroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

019-Base Coat

161907079-0019A

None DetectedPerlite

Non-fibrous (Other)

10%

90%

Gray

Non-Fibrous

Homogeneous

Hallway Bathroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

020-Finish Coat

161907079-0020

None DetectedQuartz

Non-fibrous (Other)

10%

90%

White

Non-Fibrous

Homogeneous

Southwest Bedroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

020-Base Coat

161907079-0020A

None DetectedPerlite

Non-fibrous (Other)

10%

90%

Gray

Non-Fibrous

Homogeneous

Southwest Bedroom -

Plaster over Drywall

(Ceiling)

HA: PD-02

021-Finish Coat

161907079-0021

None DetectedQuartz

Non-fibrous (Other)

10%

90%

White

Non-Fibrous

Homogeneous

Garage - Plaster over

Drywall (Ceiling)

HA: PD-02

021-Base Coat

161907079-0021A

None DetectedPerlite

Non-fibrous (Other)

10%

90%

Gray

Non-Fibrous

Homogeneous

Garage - Plaster over

Drywall (Ceiling)

HA: PD-02

022-Floor Tile

161907079-0022

2% ChrysotileNon-fibrous (Other)98%Brown

Non-Fibrous

Homogeneous

Basement - 9x9 Light

Brown w/ White

Streaks Floor Tile &

Mastic

HA: FT-03

022-Mastic

161907079-0022A

2% ChrysotileNon-fibrous (Other)98%Tan/Black

Non-Fibrous

Homogeneous

Basement - 9x9 Light

Brown w/ White

Streaks Floor Tile &

Mastic

HA: FT-03

023-Floor Tile

161907079-0023

2% ChrysotileNon-fibrous (Other)98%Brown

Non-Fibrous

Homogeneous

Basement - 9x9

Brown w/ Splotches

Floor Tile & Mastic

HA: FT-04

023-Mastic

161907079-0023A

2% ChrysotileNon-fibrous (Other)98%Black

Non-Fibrous

Homogeneous

Basement - 9x9

Brown w/ Splotches

Floor Tile & Mastic

HA: FT-04

024-Floor Tile

161907079-0024

2% ChrysotileNon-fibrous (Other)98%Brown

Non-Fibrous

Homogeneous

Basement - 9x9 Dark

Brown w/ Splotches

Floor Tile & Mastic

Page 3 of 5ASB_PLM_0008_0001 - 1.78 Printed: 4/24/2019 9:36 AM

Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / indianapolislab@emsl.com

161907079EMSL Order:

Customer ID: ALLI65

Customer PO:

Project ID:

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

HA: FT-05

024-Mastic

161907079-0024A

<1% ChrysotileNon-fibrous (Other)100%Black/Yellow

Non-Fibrous

Homogeneous

Basement - 9x9 Dark

Brown w/ Splotches

Floor Tile & Mastic

HA: FT-05

161907079-0025

<1% ChrysotileNon-fibrous (Other)100%Gray

Non-Fibrous

Homogeneous

Basement - Interior

Window Glazing

HA: G-01

161907079-0026

<1% ChrysotileNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Basement - Interior

Window Glazing

HA: G-01

027-Ceramic Tile

161907079-0027

None DetectedNon-fibrous (Other)100%White/Pink

Non-Fibrous

Homogeneous

Hallway Bathroom -

Black Mastic under

Ceramic Tile

HA: BM-01

027-Mastic

161907079-0027A

None DetectedNon-fibrous (Other)100%Tan/Black

Non-Fibrous

Homogeneous

Hallway Bathroom -

Black Mastic under

Ceramic Tile

HA: BM-01

027-Grout

161907079-0027B

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Hallway Bathroom -

Black Mastic under

Ceramic Tile

HA: BM-01

028-Ceramic Tile

161907079-0028

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Hallway Bathroom -

Black Mastic under

Ceramic Tile

HA: BM-01

028-Mastic

161907079-0028A

None DetectedNon-fibrous (Other)100%Tan/Black

Non-Fibrous

Homogeneous

Hallway Bathroom -

Black Mastic under

Ceramic Tile

HA: BM-01

028-Grout

161907079-0028B

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Hallway Bathroom -

Black Mastic under

Ceramic Tile

HA: BM-01

161907079-0029

None DetectedNon-fibrous (Other)2%Cellulose98%Brown

Fibrous

Homogeneous

Attic - Brown Blown-in

Insulation

HA: AI-01

161907079-0030

None DetectedNon-fibrous (Other)5%Cellulose95%Brown

Fibrous

Homogeneous

Attic - Brown Blown-in

Insulation

HA: AI-01

031-Tape

161907079-0031

None DetectedNon-fibrous (Other)40%Cellulose60%Gray/Tan

Fibrous

Homogeneous

Attic - Old Duct Tape on HVAC

HA: DT-01

031-Mastic

161907079-0031A

None DetectedNon-fibrous (Other)100%Tan

Non-Fibrous

Homogeneous

Attic - Old Duct Tape on HVAC

HA: DT-01

032-Tape

161907079-0032

None DetectedNon-fibrous (Other)30%Cellulose70%Gray/Tan

Fibrous

Homogeneous

Attic - Old Duct Tape on HVAC

HA: DT-01

Page 4 of 5ASB_PLM_0008_0001 - 1.78 Printed: 4/24/2019 9:36 AM

Tel/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / indianapolislab@emsl.com

161907079EMSL Order:

Customer ID: ALLI65

Customer PO:

Project ID:

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

032-Mastic

161907079-0032A

None DetectedNon-fibrous (Other)100%Tan

Non-Fibrous

Homogeneous

Attic - Old Duct Tape on HVAC

HA: DT-01

161907079-0033

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

South Exterior Door -

White Exterior

Caulking

HA: C-01

161907079-0034

None DetectedNon-fibrous (Other)100%White

Non-Fibrous

Homogeneous

Northeast Exterior

Corner - White

Exterior Caulking

HA: C-01

161907079-0035

20% ChrysotileNon-fibrous (Other)80%Gray

Fibrous

Homogeneous

South Exterior Wall -

Exterior Cement

Panel

HA: CP-01

161907079-0036

Positive Stop (Not Analyzed)South Exterior Wall -

Exterior Cement

Panel

HA: CP-01

Analyst(s)

Amanda Straw (22)

Paul Rihm (35)

Richard Harding, Laboratory Manager or Other Approved Signatory

EMSL maintains liability limited to cost of analysis . 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 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 . Interpretation and use of test results are the responsibility of the client. All samples received in acceptable condition unless otherwise noted. 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. EMSL recommends gravimetric reduction for all non -friable organically bound materials prior to analysis. Estimation of uncertainty is available on request.

Samples analyzed by EMSL Analytical, Inc. Indianapolis, IN NVLAP Lab Code 200188-0, AZ0939, CA 2575, CO AL-15132, TX 300262, LA 04135

Page 5 of 5ASB_PLM_0008_0001 - 1.78 Printed: 4/24/2019 9:36 AM

Phone/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com / indianapolislab@emsl.com

EMSL Order: 161907079

Customer ID: ALLI65

Customer PO:

Project ID:

Attention: Michael Ardis Phone: (317) 865-3400

Alliance Environmental Group, Inc. Fax: (317) 865-3401

5153 Commerce Square Drive Received: 04/17/2019 2:59 PM

Suite E Analysis Date: 04/29/2019

Indianapolis, IN 46237 Collected: 04/16/2019

Project: 19-0047-AL-001

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

Polarized Light Microscopy. Quantitation using 400 Point Count Procedure

Sample Description Appearance % Fibrous % Non-Fibrous % Type

Non-Asbestos Asbestos

Gray

Non-Fibrous

Homogeneous

Basement - Interior

Window Glazing

161907079-0025

Non-fibrous (Other)100.0% <0.25%Chrysotile

HA: G-01

White

Non-Fibrous

Homogeneous

Basement - Interior

Window Glazing

161907079-0026

Non-fibrous (Other)100.0% <0.25%Chrysotile

HA: G-01

Analyst(s)

Ross Matlock (2) Richard Harding, Laboratory Manager or other approved signatory

Disclaimer:Some samples may contain asbestos fibers present in dimensions below PLM resolution limits. The limit of detection as stated in the method is 0.25%. EMSL Analytical Inc suggests that samples reported as <0.25% or none detected undergo additional analysis via TEM . The above test report relates only to the items tested. This report may not be reproduced, except in full, without written approval of EMSL Analytical Inc. This test report must not be used by the client to claim product endorsement by NVLAP or any agency of the United States Government . EMSL

Analytical Inc., bears no responsibility for sample collection activities, analytical method limitations, or the accuracy of results when requested to separate layered samples. EMSL Analytical Inc., liability is limited to the cost of sample analysis.The test results contained within this report meet the requirements of NELAC unless otherwise noted. Samples received in good condition unless otherwise noted. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample.

Samples analyzed by EMSL Analytical, Inc. Indianapolis, IN

Initial report from: 04/29/2019 10:35:36

ASB_PLMPC_0006_0003 Printed 4/29/2019 10:35:40AM Page 1 of 1

ConcentrationAnalyzed Weight RDL LeadClient SampleDescription Collected

Test Report: Lead in Paint Chips by Flame AAS (SW 846 3050B/7000B)*

EMSL Analytical, Inc.

6340 CastlePlace Dr., Indianapolis, IN 46250 Phone/Fax: (317) 803-2997 / (317) 803-3047 http://www.EMSL.com indianapolislab@emsl.com

Attn: Michael Ardis Alliance Environmental Group, Inc.

5153 Commerce Square Drive Suite E Indianapolis, IN 46237

Received: 04/17/19 2:58 PM

Pre-Demo Inspection - 2333 Lake Ave, Fort Wayne, IN

Fax: (317) 865-3401 Phone: (317) 865-3400

Project:

4/16/2019Collected:

161907214 CustomerID: ALLI65 CustomerPO:

ProjectID:

EMSL Order:

Site: GARAGE - OFF-WHITE PAINT CHIPS

2.0 % wt4/19/2019 0.2245 g

161907214-0001 0.224/16/2019001 % wt

Site: GARAGE - BROWN OVER GREEN PAINT CHIPS <0.0089 % wt4/19/2019 0.2251 g

161907214-0002 0.00894/16/2019002 % wt

Page 1 of 1Test Report PB w/RDL-2.0.0.0 Printed: 4/23/2019 4:27:51 PM

Doug Wiegand, Laboratory Manager or other approved signatory

*Analysis following Lead in Paint by EMSL SOP/Determination of Environmental Lead by FLAA. Reporting limit is 0.010 % wt based on the minimum sample weight per our SOP. Unless noted, results in this report are not blank corrected. 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. Samples received in good condition unless otherwise noted. "<" (less than) result signifies that the analyte was not detected at or above the reporting limit. Measurement of uncertainty is available upon request. The QC data associated with the sample results included in this report meet the recovery and precision requirements unless specifically indicated otherwise.

Definitions of modifications are available upon request.

Samples analyzed by EMSL Analytical, Inc. Indianapolis, IN AIHA-LAP, LLC--ELLAP 157245, OH E10040

Initial report from 04/23/2019 16:27:51 http://www.EMSL.com mailto:indianapolislab@emsl.com

#=CL#

April 24, 2019

LIMS USE: FR - JEREMY MALCOM

LIMS OBJECT ID: 50222454

50222454 Project:

Pace Project No.:

RE:

JEREMY MALCOM

ALLIANCE ENVIRONMENTAL GROUP, INC.

5153 Commerce Square Dr.

Indianapolis, IN 46237

19-0047-AL-001

Dear JEREMY MALCOM:

Enclosed are the analytical results for sample(s) received by the laboratory on April 17, 2019. The results relate only to the samples included in this report. Results reported herein conform to the most current, applicable TNI/NELAC standards and the laboratory's Quality Assurance Manual, where applicable, unless otherwise noted in the body of the report.

If you have any questions concerning this report, please feel free to contact me.

Sincerely, Mick Mayse mick.mayse@pacelabs.com

Project Manager (317)228-3100

Enclosures cc: Alliance Environmental Group, Inc., Alliance Environmental Group, Inc.

Mr. Paul Krick, Alliance Environmental Group, Inc.

Mr. Sean Stults, Alliance Environmental Group

REPORT OF LABORATORY ANALYSIS

This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.

Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268 (317)228-3100

#=CP#

CERTIFICATIONS

Pace Project No.:

Project:

50222454

19-0047-AL-001

Indiana Certification IDs 7726 Moller Road, Indianapolis, IN 46268 Illinois Certification #: 200074 Indiana Certification #: C-49-06 Kansas/NELAP Certification #: E-10177 Kentucky UST Certification #: 80226 Kentucky WW Certification #: 98019 Michigan Department of Environmental Quality, Laboratory #9050

Ohio VAP Certification #: CL0065 Oklahoma Certification #: 2018-101 Texas Certification #: T104704355 West Virginia Certification #: 330 Wisconsin Certification #: 999788130 USDA Soil Permit #: P330-16-00257

REPORT OF LABORATORY ANALYSIS

This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.

Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

#=SS#

SAMPLE SUMMARY

Pace Project No.:

Project:

50222454

19-0047-AL-001

Lab ID Sample ID Matrix Date Collected Date Received

50222454001 001 Solid 04/16/19 12:30 04/17/19 15:44

REPORT OF LABORATORY ANALYSIS

This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.

Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

#=SA#

SAMPLE ANALYTE COUNT

Pace Project No.:

Project:

50222454

19-0047-AL-001

Lab ID Sample ID Method Analytes ReportedAnalysts

50222454001 001 EPA 8082 8RID

SM 2540G 1MMS

REPORT OF LABORATORY ANALYSIS

This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.

Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

#=AR#

ANALYTICAL RESULTS

Pace Project No.:

Project:

50222454

19-0047-AL-001

Sample: 001 Lab ID: 50222454001 Collected: 04/16/19 12:30 Received: 04/17/19 15:44 Matrix: Solid Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions.

Parameters Results Units DF Prepared Analyzed CAS No. QualReport Limit

Analytical Method: EPA 8082 Preparation Method: EPA 35468082 GCS PCB Solids

PCB-1016 (Aroclor 1016) ND ug/kg 04/22/19 11:44 12674-11-204/19/19 09:40100 1 PCB-1221 (Aroclor 1221) ND ug/kg 04/22/19 11:44 11104-28-204/19/19 09:40100 1 PCB-1232 (Aroclor 1232) ND ug/kg 04/22/19 11:44 11141-16-504/19/19 09:40100 1 PCB-1242 (Aroclor 1242) ND ug/kg 04/22/19 11:44 53469-21-904/19/19 09:40100 1 PCB-1248 (Aroclor 1248) ND ug/kg 04/22/19 11:44 12672-29-604/19/19 09:40100 1 PCB-1254 (Aroclor 1254) ND ug/kg 04/22/19 11:44 11097-69-104/19/19 09:40100 1 PCB-1260 (Aroclor 1260) ND ug/kg 04/22/19 11:44 11096-82-504/19/19 09:40100 1 Surrogates Tetrachloro-m-xylene (S) 39 %. 04/22/19 11:44 877-09-804/19/19 09:4026-140 1

Analytical Method: SM 2540GPercent Moisture

Percent Moisture 1.1 % 04/19/19 15:560.10 1

REPORT OF LABORATORY ANALYSIS

This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 04/24/2019 08:23 AM

Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

#=QC#

QUALITY CONTROL DATA

Pace Project No.:

Project:

50222454

19-0047-AL-001

Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.

QC Batch:

QC Batch Method:

Analysis Method:

Analysis Description:

495730

EPA 3546

EPA 8082

8082 GCS PCB

Associated Lab Samples: 50222454001

Parameter Units Blank Result

Reporting Limit Qualifiers

METHOD BLANK: 2287269

Associated Lab Samples: 50222454001

Matrix: Solid

Analyzed

PCB-1016 (Aroclor 1016) ug/kg ND 99.7 04/19/19 17:24 PCB-1221 (Aroclor 1221) ug/kg ND 99.7 04/19/19 17:24 PCB-1232 (Aroclor 1232) ug/kg ND 99.7 04/19/19 17:24 PCB-1242 (Aroclor 1242) ug/kg ND 99.7 04/19/19 17:24 PCB-1248 (Aroclor 1248) ug/kg ND 99.7 04/19/19 17:24 PCB-1254 (Aroclor 1254) ug/kg ND 99.7 04/19/19 17:24 PCB-1260 (Aroclor 1260) ug/kg ND 99.7 04/19/19 17:24 Tetrachloro-m-xylene (S) %. 71 26-140 04/19/19 17:24

Parameter Units

LCS

Result % Rec Limits Qualifiers% RecConc.

2287270LABORATORY CONTROL SAMPLE:

LCSSpike

PCB-1016 (Aroclor 1016) ug/kg 139166 84 59-119 PCB-1260 (Aroclor 1260) ug/kg 134166 81 57-119 Tetrachloro-m-xylene (S) %. 79 26-140

Parameter Units

Result % Rec Limits Qual% RecConc.

2287271MATRIX SPIKE & MATRIX SPIKE DUPLICATE:

MSSpike Result

50222572003

2287272

MSD

Result

MSD

% Rec RPD RPD

Max

MSDMS

Spike Conc.

PCB-1016 (Aroclor 1016) ug/kg 967 123 10-159142 11 20930ND 1190 1320 PCB-1260 (Aroclor 1260) ug/kg 967 56 11-13162 20930ND 540J 580 Tetrachloro-m-xylene (S) %. 62 26-14078

REPORT OF LABORATORY ANALYSIS

This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 04/24/2019 08:23 AM

Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

#=QC#

QUALITY CONTROL DATA

Pace Project No.:

Project:

50222454

19-0047-AL-001

Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.

QC Batch:

QC Batch Method:

Analysis Method:

Analysis Description:

495819

SM 2540G

Dry Weight/Percent Moisture

Associated Lab Samples: 50222454001

Parameter Units Dup

Result Max RPD QualifiersRPDResult

50221815013

2287669SAMPLE DUPLICATE:

Percent Moisture % 17.5 5 518.4

Parameter Units Dup

Result Max RPD QualifiersRPDResult

50221880009

2288137SAMPLE DUPLICATE:

Percent Moisture % 11.9 5 511.4

REPORT OF LABORATORY ANALYSIS

This report shall not be reproduced, except in full, without the written consent of Pace Analytical Services, LLC.Date: 04/24/2019 08:23 AM

Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

#=QL#

QUALIFIERS

Pace Project No.:

Project:

50222454

19-0047-AL-001

DEFINITIONS

DF - Dilution Factor, if reported, represents the factor applied to the reported data due to dilution of the sample aliquot.

ND - Not Detected at or above adjusted reporting limit.

TNTC - Too Numerous To Count J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit.

MDL - Adjusted Method Detection Limit.

PQL - Practical Quantitation Limit.

RL - Reporting Limit - The lowest concentration value that meets project requirements for quantitative data with known precision and bias for a specific analyte in a specific matrix.

S - Surrogate 1,2-Diphenylhydrazine decomposes to and cannot be separated from Azobenzene using Method 8270. The result for each analyte is a combined concentration.

Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values.

LCS(D) - Laboratory Control Sample (Duplicate) MS(D) - Matrix Spike (Duplicate) DUP - Sample Duplicate RPD - Relative Percent Difference NC - Not Calculable.

SG - Silica Gel - Clean-Up U - Indicates the compound was analyzed for, but not detected.

N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for each analyte is a combined concentration.

Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes.

TNI - The NELAC Institute.

REPORT OF LABORATORY ANALYSIS

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Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

#=CR#

QUALITY CONTROL DATA CROSS REFERENCE TABLE

Pace Project No.:

Project:

50222454

19-0047-AL-001

Lab ID Sample ID QC Batch Method QC Batch Analytical Method Analytical Batch

50222454001 495730 495912001 EPA 3546 EPA 8082

50222454001 495819001 SM 2540G

REPORT OF LABORATORY ANALYSIS

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Pace Analytical Services, LLC 7726 Moller Road

Indianapolis, IN 46268

028213.41_Pre-Demo Building Inspection

Cover Letter

Certifications

Sample Summary

Sample Analyte Count

Analytical Results

Quality Control Data

Qualifiers

Quality Control Data Cross Reference Table

Chain of Custody

028333.13

PART 1 - GENERAL

1.1 SUMMARY

A. Section Includes:

1. Removing and disposal of peeling and delaminated lead-containing paints and paint debris as indicated in existing conditions report at 2333 Lake Avenue, Fort Wayne, Indiana.

1.2 RELATED REQUIREMENTS

A. Hazardous Material Abatement: Section 02 82 13.41, ASBESTOS ABATEMENT FOR TOTAL DEMOLITION PROJECTS.

B. Demolition Disturbing Lead-Based Paint: Section 02 41 00, DEMOLITION.

1.3 DEFINITIONS

A. Action Level: Employee exposure, without regard to use of respirator, to lead airborne concentration of 30 micrograms per cubic meter (0.03 parts per million) of air averaged over 8-hour period. As used in this section, ”30 micrograms per cubic met...

B. Area Monitoring: Sampling of lead concentrations within lead control area and inside physical boundaries which are representative of airborne lead concentrations which may reach breathing zone of personnel potentially exposed to lead.

C. Breathing Zone: Area within hemisphere, forward of shoulders, with 150 mm to 225 mm (6 to 9 inches) radius and center at nose or mouth of employee.

D. Certified Industrial Hygienist (CIH): As used in this section, refers to an Industrial Hygienist employed by Contractor.

E. Change Rooms and Shower Facilities: Rooms within designated physical boundary around lead control area equipped with separate storage facilities for clean protective work clothing and equipment and for street clothes which prevent cross- contaminat...

F. Competent Person: Person capable of identifying lead hazards in work area and authorized by contractor to take corrective action.

G. Decontamination Room: Room for removal of contaminated personal protective equipment (PPE).

H. Eight-Hour Time Weighted Average (TWA): Airborne concentration of lead averaged over 8-hour workday to which an employee is exposed.

I. High Efficiency Particulate Air (HEPA) Filter Equipment: HEPA filtered vacuuming equipment with UL 586 filter system capable of collecting and retaining lead-contaminated paint dust. HEPA filter means 99.97 percent efficient against 0.3 micron (0.0...

J. Lead: Metallic lead, inorganic lead compounds, and organic lead soaps. Excluded from this definition are other organic lead compounds.

K. Lead Control Area: Enclosed area or structure with full containment to prevent spreading lead dust, paint chips, and debris from lead-based paint removal operations. Lead control area is isolated by physical boundaries to prevent unauthorized entry...

L. Lead Permissible Exposure Limit (PEL): Fifty micrograms per cubic meter (0.05 parts per million) of air as 8-hour time weighted average as determined by 29 CFR Part 1910.1025. When employee is exposed for more than 8 hours per work day, determine P...

M. Personnel Monitoring: Sampling of lead concentrations within employee breathing zone to determine 8-hour time weighted average concentration according to 29 CFR Part 1910.1025. Take samples representative of employee's work tasks.

N. Physical Boundary: Area physically roped or partitioned off around enclosed lead control area to limit unauthorized entry of personnel. As used in this section, "inside boundary" shall mean same as "outside lead control area."

1.4 APPLICABLE PUBLICATIONS

A. Comply with references to extent specified in this section.

B. American National Standards Institute (ANSI):

1. Z9.2-12 - Fundamentals Governing the Design & Operation of Local Exhaust Ventilation Systems.

C. Code of Federal Regulations (CFR):

1. 29 CFR Part 1910 - Occupational Safety and Health Standards.

2. 29 CFR Part 1926 - Safety and Health Regulations for Construction.

3. 40 CFR Part 260 - Hazardous Waste Management System: General.

4. 40 CFR Part 261 - Identification and Listing of Hazardous Waste.

5. 40 CFR Part 262 - Standards Applicable to Generators of Hazardous Waste.

6. 40 CFR Part 263 - Standards Applicable to Transporters of Hazardous Waste.

7. 40 CFR Part 264 - Standards for Owners and Operations of Hazardous Waste Treatment, Storage, and Disposal Facilities.

8. 40 CFR Part 265 - Interim Status Standards for Owners and Operators of Hazardous Waste Treatment, Storage, and Disposal Facilities.

9. 40 CFR Part 268 - Land Disposal Restrictions.

10. 49 CFR Part 172 - Hazardous Material Table, Special Provisions, Hazardous Material Communications, Emergency Response Information, and Training Requirements, and Security Plans.

11. 49 CFR Part 178 - Specifications for Packagings.

D. Underwriters Laboratories (UL):

1. 586-09 - High-Efficiency, Particulate, Air Filter Units.

1.5 PRE-REMOVAL MEETINGS

A. Conduct pre-removal meeting at project site minimum 30 days before beginning Work of this section.

1. Required Participants:

a. Contracting Officer's Representative.

b. Certified Industrial Hygienist.

c. Architect/Engineer.

d. Contractor.

e. Paint removal contractor.

2. Meeting Agenda: Distribute agenda to participants minimum 3 days before meeting.

a. Respiratory protection program.

b. Hazard communication program.

c. Hazardous waste management plan.

d. Safety and health regulation compliance.

e. Employee training.

f. Removal schedule.

g. Removal sequence.

h. Preparatory work.

i. Protection before, during, and after removal.

j. Removal.

k. Inspecting and testing.

l. Other items affecting successful completion.

3. Document and distribute meeting minutes to participants to record decisions affecting installation.

1.6 SUBMITTALS

A. Submittal Procedures: Section 01 33 23, SHOP DRAWINGS, PRODUCT DATA, AND SAMPLES.

B. Manufacturer's Literature and Data:

1. Description of each product.

a. Paint removal products.

b. Vacuum filters.

c. Respirators.

2. Safety data sheet for each paint removal product.

3. Installation instructions.

a. Paint removal products.

C. Test Reports: Submit testing laboratory reports.

1. Submit air monitoring results within three working days, signed by testing laboratory employee performing air monitoring, employee analyzing sample, and CIH.

D. Certificates: Certify completed training.

1. Submit certificate for each employee signed and dated by CIH and employee stating employee was trained.

E. Qualifications: Substantiate qualifications comply with specifications.

1. Paint removal contractor.

2. Testing laboratory.

a. Name, address, and telephone number.

b. Current evidence of participation in NIOSH PAT Program.

c. Copy of current AIHA accreditation certificate.

3. Industrial hygienist.

a. Name, address, and telephone number.

b. Resume showing previous experience.

c. Copy of current ABIH CIH certification.

4. Paint disposal facility.

a. Name, address, and telephone number.

b. Current license or authorization to receive and dispose lead contaminated waste.

F. Record Documents:

1. Completed and signed hazardous waste manifest from waste transporter.

2. Paint disposal facility receipts and disposition reports.

3. Certification of medical examinations.

4. Employee training certification.

1.7 QUALITY ASSURANCE

A. Safety and Health Regulation Compliance:

1. Comply with laws, ordinances, rules, and regulations of federal, state, and local authorities having jurisdiction regarding removing, handling, storing, transporting, and disposing lead waste materials.

a. Comply with applicable requirements of 29 CFR Part 1910.1025.

b. Notify Contracting Officer's Representative and request resolution of conflicts between regulations and specified requirements before starting work.

2. Comply with the following local laws, ordinances, criteria, rules and regulations regarding removing, handling, storing, transporting, and disposing lead-contaminated materials:

a. There are no local regulations that apply to this project.

B. Paint Removal Contractor: Experienced contractor, registered or licensed by applicable state agency regulating lead-based paint removal.

C. Testing Laboratory: State certified independent testing laboratory experienced in airborne lead monitoring, testing, and reporting.

1. Successful participant in NIOSH Proficiency Analytical Testing (PAT) Program within prior 12 months.

2. Accredited by American Industrial Hygiene Association (AIHA).

D. Certified Industrial Hygienist: Certified as CIH by American Board of Industrial Hygiene in comprehensive practice and responsible for:

1. Certify Training.

2. Review and approve lead-based paint removal plan for conformance to applicable referenced standards.

3. Inspect lead-based paint removal work for conformance with approved plan.

4. Direct monitoring.

5. Ensure work is performed according to specifications.

6. Ensure personnel and environment hazardous exposures are adequately controlled.

E. Paint Disposal Facility: State certified disposal facility qualified to receive and dispose lead-based paint.

F. Lead-based Paint Removal Plan:

1. Submit detailed, site-specific plan describing lead-based paint removal procedures.

2. Include sketch showing location, size, and details of lead control areas, decontamination rooms, change rooms, shower facilities, and mechanical ventilation system.

3. Include eating, drinking, and restroom procedures, interface of trades, work sequencing, collected wastewater and paint debris disposal plan, air sampling plan, respirators, protective equipment, and detailed description of containment methods ensu...

a. Eating, drinking, and smoking are not acceptable within lead control area.

4. Include air sampling, training and strategy, sampling methodology, frequency, duration, and qualifications of air monitoring personnel.

G. Respiratory Protection Program: Establish and implement program required by 29 CFR Part 1910.134, 29 CFR Part 1910.1025, and 29 CFR Part 1926.62.

1. Provide each employee negative pressure or other appropriate respirator.

a. Test fit each employee's respirator at initial fitting and maximum 6 month intervals, as required by 29 CFR Part 1926.62.

H. Hazard Communication Program: Establish and implement program required by 29 CFR Part 1910.1200.

I. Hazardous Waste Management Plan: Establish and implement plan according to applicable requirements of Federal, State, and local hazardous waste regulations including the following:

1. Identification of hazardous wastes associated with work.

2. Estimated quantities of generated and disposed waste.

3. Names and qualifications of each contractor transporting, storing, treating, and disposing wastes. Include facility location and 24-hour point of contact.

4. Names and qualifications (experience and training) of personnel working on-site with hazardous wastes.

5. List of required waste handling equipment including cleaning, volume reduction, and transport equipment.

6. Spill prevention, containment, and cleanup contingency implementation measures.

7. Work plan and schedule for waste containment, removal, and disposal with daily waste cleaned up and containerization.

8. Hazardous waste disposal cost.

1.8 WARRANTY

A. Construction Warranty: FAR clause 52.246-21, "Warranty of Construction."

PART 2 - PRODUCTS

2.1 PAINT REMOVAL PRODUCTS

A. Chemical Stripper: Biodegradable, non-toxic, capable of removing existing paint layers in one application, and acceptable to CIH.

2.2 ACCESSORIES

A. Waste Collection Drums: 49 CFR Part 178; Type 1A2, steel, removable head, 200 L (55 gal.) capacity, capable of containing waste without loss.

B. Vacuum Cleaner: HEPA filtered type.

C. Scrapers:

1. Metal type for use on metal, concrete, and masonry surfaces.

2. Plastic type for use on wood, plaster, gypsum board, and other surfaces.

D. Rinse Water: Potable.

E. Cleaning Cloths: Cotton.

PART 3 - EXECUTION

3.1 EXAMINATION

A. Before exposure to lead-contaminated dust, provide workers with comprehensive medical examination required by 29 CFR Part 1926.62 (I) (1) (i) and (ii).

1. Exemption: Examination is not required when employee medical records show last examination required by 29 CFR Part 1926.62(I) was completed within previous 12 months.

B. Maintain complete and accurate employee medical records according to 29 CFR Part 1910.20.

C. Train each employee performing paint removal, disposal, and air sampling operations according to 29 CFR Part 1926.62.

1. Certify training is completed before employee is permitted to work on project and enter lead control area.

3.2 PREPARATION

A. Notify Contracting Officer 20 days before starting paint removal work.

B. Boundary Requirements: Provide physical boundaries around lead control area by roping off area or providing curtains, portable partitions or other enclosures to ensure that airborne lead concentrations do not meet or exceed action level outside of ...

C. Change Room and Shower Facilities: Provide clean change rooms and shower facilities within physical boundary around lead control area according to 29 CFR Part 1926.62.

D. Mechanical Ventilation System:

1. Provide ventilation system to control personnel exposure to lead according to 29 CFR Part 1926.57.

2. Design, construct, install, and maintain HEPA filtered fixed local exhaust ventilation system according to ANSI Z9.2 and approved by CIH.

3. Exhaust ventilation air to exterior wherever possible.

4. When exhaust ventilation air must be recirculated into work area, provide HEPA filter with reliable back-up filter and controls to monitor lead concentration in return air and to bypass recirculation system automatically when system fails.

E. Personnel Protection: Provide and use required protective clothing and equipment within lead control area.

F. Warning Signs: Provide warning signs complying with 29 CFR Part 1926.62 at lead control area approaches. Locate signs so personnel read signs and take necessary precautions before entering lead control area.

3.3 WORK PROCEDURES

A. Remove lead-based paint according to approved lead-based paint removal plan.

1. Perform work only in presence of CIH or Industrial Hygienist (IH) Technician under direction of CIH ensuring continuous inspection of work in progress and direction of air monitoring activities.

2. Handle, store, transport, and dispose lead or and lead contaminated waste according to 40 CFR Part 260, 40 CFR Part 261, 40 CFR Part 262, 40 CFR Part 263, 40 CFR Part 264, and 40 CFR Part 265. Comply with land disposal restriction notification requ...

B. Use procedures and equipment required to limit occupational and environmental lead exposure when lead-based paint is removed according to 29 CFR Part 1926.62.

C. Dispose removed paint and waste according to Environmental Protection Agency (EPA), federal, state, and local requirements.

D. Personnel Exiting Procedures:

1. When personnel exit lead control area, comply with the following procedures:

a. Vacuum exposed clothing surfaces.

b. Remove protective clothing and equipment in decontamination room. Place clothing in approved impermeable disposal bag.

c. Shower.

d. Dress in clean clothes before leaving lead control area.

E. Monitoring - General:

1. Monitor airborne lead concentrations according to 29 CFR Part 1910.1025by testing laboratory as directed by CIH.

2. Take personal air monitoring samples on employees anticipated to have greatest exposure risk as determined by CIH. Additionally, take air monitoring samples on minimum 25 percent of work crew or minimum of two employees, whichever is greater, durin...

3. Submit results of air monitoring samples, signed by CIH, within 24 hours after taking air samples. Notify Contracting Officer's Representative immediately of lead exposure at or exceeding action level outside of lead control area.

F. Monitoring During Paint Removal:

1. Perform personal and area monitoring during entire paint removal operation.

2. Conduct area monitoring at physical boundary daily for each work shift to ensure unprotected personnel are not exposed above action level anytime.

3. For outdoor operations, take at least one sample on each shift leeward of lead control area. When adjacent areas are contaminated, clean area of contamination and have CIH visually inspect and certify lead contamination is cleaned.

4. Stop work when outside boundary lead levels meet or exceed action level. Notify Contracting Officer's Representative, immediately.

5. Correct conditions causing increased lead concentration as directed by CIH.

6. Review sampling data collected during work stoppage to determine if conditions require additional work method modifications as determined by CIH.

7. Resume paint removal when approved by CIH.

3.4 LEAD-BASED PAINT REMOVAL

A. Remove paint within areas indicated on drawings completely exposing substrate. Minimize damage to substrate.

B. Comply with paint removal processes described lead paint removal plan.

C. Lead-Based Paint Removal: Select processes for each application to minimize work area lead contamination and waste.

3.5 FIELD QUALITY CONTROL

A. Field Tests: Performed by testing laboratory specified in Section 01 45 29, TESTING LABORATORY SERVICES.

B. Perform sampling and testing for:

1. Air monitoring.

2. Lead based paint.

3.6 CLEANING AND DISPOSAL

A. Cleaning:

1. Maintain lead control area surfaces free of accumulating paint chips and dust. Confine dust, debris, and waste to work area.

2. Vacuum clean work area daily, at end of each shift, and when paint removal operation is complete.

B. CIH Certification: Certify in writing that inside and outside lead control area air monitoring samples are less than action level, employee respiratory protection was adequate, the work was performed according to 29 CFR Part 1926.62, and no visible...

1. Do not remove lead control area or roped-off boundary and warning signs before Contracting Officer's Representative's receipt of CIH's certification.

2. Reclean areas showing dust or residual paint chips.

C. Testing: Where indicated and when directed by Contracting Officer's Representative, test lead-based paint residue and used abrasive according to 40 CFR Part 261 for hazardous waste.

D. Waste Collection:

1. Collect lead-contaminated materials including waste, scrap, debris, bags, containers, equipment, and clothing, which may produce airborne lead contamination.

2. Place lead contaminated materials in waste disposal drums. Label each drum identifying waste type according to 49 CFR Part 172 and date waste materials were first put into drum. Obtain and complete the Uniform Hazardous Waste Manifest forms. Comply...

3. Coordinate temporary storage location on project site with Contracting Officer's Representative.

E. Waste Disposal:

1. Minimum 14 days before delivery, notify Contracting Officer's Representative who will arrange for job site inspection of drums and manifests by paint disposal facility personnel.

2. Contracting Officer's Representative will arrange hazardous wastes removal, transport and delivery to paint disposal facility to ensure drums do not remain on project site longer than 90 calendar days from drum label date.

F. Waste Disposal:

1. Do not store hazardous waste drums in temporary storage location longer than 90 calendar days from drum label date.

2. Remove, transport, and deliver drums to paint disposal facility.

a. Obtain signed receipt including date, time, quantity, and description of materials received according to 40 CFR Part 262.

b. Obtain final report of materials disposition after disposal completion.

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PART 1 - GENERAL
1.1 DESCRIPTION
1.2 RELATED WORK
1.3 qualITY ASSURANCE
1.4 SUBMITTALS

File details come from the government source that posted it. Updated Jan 16, 2020.