14_Asbestos - Lead Paint Survey 20160125.pdf

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Design Build - Edinburg Pump Station
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191BWC21R0004
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This document contains information regarding a federal solicitation and related federal contract opportunity. The solicitation is for a design-build contract to rehabilitate approximately 800 linear feet of levee at the Edinburg Pump Station in Hidalgo County, Texas. Work will include earthen embankment, concrete floodwalls, ramps, geotechnical analysis and testing, assessing structures, levee widening, floodwall construction, gatewell replacement, backfilling, road surfacing, fencing replacement and revegetation. The solicitation is issued by the United States Section of the International Boundary and Water Commission for work to be performed by Hidalgo County Irrigation District No. 1 to provide flood control and meet FEMA and Corps of Engineers standards.

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Limited Asbestos Survey and Lead-Containing Paint Survey

PUMP STATION

EAST OLD MILITARY ROAD

PENITAS, TEXAS

January 25, 2016 Terracon Project No. 88157214

Prepared for:

Hidalgo County Irrigation District No. 1

1904 North Expressway 281 Edinburg, Texas 78542

Prepared by:

Terracon Consultants, Inc.

Pharr, Texas

Terracon Consultants, Inc. 1506 Mid Cities Drive, Pharr, Texas 78572 P [956] 283-8254 F [956] 283-8279 t er racon.com

January 25, 2016

Hidalgo County Irrigation District No. 1 1904 North Expressway 281 Edinburg, Texas 78542

Attn: Mr. Rusty McDaniel, General Manager T: (956) 383-3886 E: rusty@hidalgocountyirrigation.com

Re: Limited Asbestos & Lead-Containing Paint Survey Pump Station East Old Military Road Penitas, Texas 78576 Terracon Project No. 88157214

Dear Mr. McDaniel:

On December 22, 2015, Terracon Consultants, Inc. (Terracon) conducted a limited asbestos-containing materials (ACM) survey and lead-containing paint (LCP) survey to establish asbestos content and lead levels present in the building materials associated with the Pump Station located at East Old Military Road in Penitas, Texas.

Asbestos was not identified in the materials sampled from the Pump Station. Please refer to the attached report for details.

Various paint coatings sampled were found to have detectable levels of lead in the paint combinations sampled. A single paint coating sampled was found to exhibit a lead content above 5,000 ppm which would be considered “Lead-Based Paint”. Please refer to the attached report for details.

mailto:rusty@hidalgocountyirrigation.com

Responsive ■ Resourceful ■ Reliable

TABLE OF CONTENTS

Page

1.0 INTRODUCTION

1.1 Project Objective

2.0 BUILDING DESCRIPTION

3.0 FIELD ACTIVITIES

3.1 Visual Assessment

3.2 Physical Assessment

3.3 Sample Collection

3.4 Sample Analysis

4.0 REGULATORY OVERVIEW

5.0 FINDINGS AND RECOMMENDATIONS

6.0 GENERAL COMMENTS

APPENDIX A ASBESTOS SURVEY SAMPLE SUMMARY

APPENDIX B ASBESTOS ANALYTICAL LABORATORY DATA

APPENDIX C LEAD SAMPLE SUMMARY

APPENDIX D LEAD ANALYTICAL LABORATORY DATA

APPENDIX E LICENSES AND CERTIFICATIONS

APPENDIX F SAMPLE LOCATION DRAWINGS

Responsive ■ Resourceful ■ Reliable 1

LIMITED ASBESTOS SURVEY AND LEAD-CONTAINING PAINT

SURVEY

PUMP STATION

EAST OLD MILITARY ROAD

PENITAS, TEXAS

Terracon Project No. 88157214

1.0 INTRODUCTION

Terracon conducted a limited asbestos-containing materials (ACM) survey and lead-containing paint (LCP) survey of the Pump Station building located at East Old Military Road in Penitas, Texas. The survey was conducted on December 22, 2015, by Mr. Guadalupe Torres, a Texas Department of State Health Services (TDSHS) licensed and Environmental Protection Agency (EPA) accredited Asbestos Inspector in general accordance with our proposal dated October 22, 2015.

Interior and exterior building components were surveyed and homogeneous areas of suspect asbestos-containing materials (ACM) were visually identified and documented. Although reasonable effort was made to survey accessible suspect materials, additional suspect but un-sampled materials could be located in walls, in voids or in other concealed areas. Suspect ACM samples were collected in accordance with Texas Asbestos Health Protection Rules (TAHPR) and in general accordance with EPA guidance document number EPA 560 5/84-024, and were intended to identify, and assess suspect materials prior to demolition activities.

Samples were delivered to a National Voluntary Laboratory Accreditation Program (NVLAP) accredited and TDSHS licensed laboratory for analysis by Polarized Light Microscopy (PLM) protocol.

The lead-containing paint sampling was intended to identify and assess the lead content of the paint/coating materials which might be disturbed in the planned renovation/demolition activities. Samples of suspect LCP were delivered to an American Industrial Hygiene Association (AIHA) accredited laboratory for analysis utilizing Atomic Absorption Spectrometry (AAS Flame) methodology.

1.1 Project Objective

We understand that this survey was requested to facilitate the potential renovation of the building currently on the site. The Texas Department of State Health Services (TDSHS) regulates asbestos-related activities in the State of Texas. The TDSHS Texas Asbestos

Limited Asbestos Survey and Lead-Containing Paint Survey Pump Station ■ Penitas, Texas January 25, 2016 ■ Terracon Project No. 88157214

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Health Protection Rules (TAHPR) require that a licensed Asbestos Inspector conduct an asbestos survey which conforms to generally accepted industry standards such as the protocol specified in 40 CFR Part 763.85, commonly referred to as the Asbestos Hazard Emergency Response Act (AHERA) that applies to schools. Other factors are taken into consideration when determining the best method to determine the location, extent and condition of Asbestos- Containing Materials (ACMs) in a non-school building.

EPA regulation 40 CFR 61, Subpart M, National Emission Standards for Hazardous Air Pollutants (NESHAP), prohibits the release of asbestos fibers to the atmosphere during renovation or demolition activities. The asbestos NESHAP, which is enforced by the TDSHS, requires that prior to the commencement of demolition or renovation, that the facility or part of the facility affected be thoroughly inspected for the presence of both Friable (Regulated Asbestos-Containing Building Materials), and Non-Friable (Category I & II Asbestos-Containing Materials). The Occupational Health and Safety Administration (OSHA) has promulgated a worker protection standard for the disturbance of asbestos during renovation and demolition projects.

The Department of Housing and Urban Development (HUD) guidelines consider a lead content equal to or greater than 5,000 parts per million (PPM) to be the level at which paint is considered to be “lead-based” and at which point a potential hazard exists. The Occupational Safety and Health Administration (OSHA) considers paint containing any level of lead above the analytical method detection limit a potential hazard which should be communicated to any employees or contractors who may disturb the materials in the course of their assigned work.

2.0 BUILDING DESCRIPTION

The building is a one-story, approximately 5,500 square foot concrete structure atop a concrete slab-on-grade foundation. The roof is a steep-sloped metal panel system. Interior walls consisted of either concrete or brick with a painted and plastered finish. The ceiling was unfinished. The floors in the building consisted of either exposed concrete or expanded metal catwalks.

3.0 FIELD ACTIVITIES

The survey was conducted and bulk material samples were obtained by Mr. Guadalupe Torres, a Texas Department of State Health Services (TDSHS) licensed and Environmental Protection Agency (EPA) accredited Asbestos Inspector employed by Terracon. A copy of the individual licenses and certificates are attached in Appendix F. The survey was conducted in general accordance with the sample collection protocols established in the TAHPR and/or EPA regulation 40 CFR 763, the Asbestos Hazard Emergency Response Act (AHERA). The lead sampling was conducted by Mr. Guadalupe Torres, an appropriately trained Lead Inspector. A summary of survey activities is provided below.

January 25, 2016 ■ Terracon Project No. 88157214

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3.1 Visual Assessment

Our survey activities began with visual observation of the interior and exterior areas of the building on the site to identify homogeneous areas of suspect ACM. A homogeneous area consists of building materials that appear similar throughout in terms of color, texture and date of application. Interior assessment was conducted throughout visually accessible areas of the building where renovations are reportedly planned. Building materials identified as concrete, glass, wood, masonry, metal or rubber were not considered suspect ACM.

Suspect materials located behind mirrors were not sampled in order to prevent excessive damage to the material. Suspect materials, such as mastic should be sampled prior to renovation activities if the activities will disturb the materials.

Terracon visually assessed interior and exterior areas of the building to identify painted/coated surfaces with suspect Lead Containing Paint (LCP). Painted/coated surfaces which appear similar throughout in terms of color, texture, substrate and date of application are treated as a homogeneous material for paint chip collection purposes. Painted/coated surfaces were visually assessed for evidence of distress, flaking, chipping and/or peeling.

3.2 Physical Assessment

A physical assessment of each homogeneous area of suspect ACM was conducted to assess the friability and condition of the materials. A friable material is defined by the EPA as a material which can be crumbled, pulverized or reduced to powder by hand pressure when dry.

Friability was assessed by physically touching suspect materials.

A physical assessment for the LCP sampling of each painted/coated surface was conducted to assess its condition. The painted/coated surfaces were assessed to be in good, fair or poor condition depending on degree of cracking, flaking, chipping and/or peeling.

3.3 Sample Collection

Based on results of the visual observation, bulk samples of suspect ACM were collected in general accordance with AHERA and TAHPA sampling protocols. Random samples of suspect materials were collected in each homogeneous area. The sample team member collected bulk samples using wet methods as applicable to reduce the potential for fiber release. Samples were placed in sealable containers and labeled with unique sample numbers using an indelible marker.

Nineteen (19) bulk samples were collected from five (5) homogeneous areas of suspect ACM.

A summary of suspect ACM samples collected during the survey is included as Appendix A.

January 25, 2016 ■ Terracon Project No. 88157214

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Six (6) bulk samples of suspect paint/coating materials were collected for lead analysis. The sample team member collected a bulk sample; the sample was placed in a sealable container and labeled with a unique sample number using an indelible marker. A summary of the suspect lead-containing samples collected during the survey is included as Appendix C.

3.4 Sample Analysis

Bulk samples of suspect ACM materials were submitted under chain-of-custody to Moody Labs of Farmers Branch, Texas for analysis by Polarized Light Microscopy with dispersion staining (PLM/DS) techniques per EPA’s Method for the Determination of Asbestos in Bulk Building Materials (600/R-93-116). The percentage of asbestos, where applicable, was determined by microscopical visual estimation. Moody Labs is accredited under the National Voluntary Laboratory Accreditation Program (NVLAP), Accreditation No. 102056-0) and licensed by the TDSHS (License No. 300084). Analytical results and sample chain-of-custody documentation are included in Appendix B of this report.

Bulk samples of the suspect lead-containing paint materials collected during the limited survey were analyzed by Environmental Hazards Services (EHS), L.L.C., an American Industrial Hygiene Association (AIHA) accredited laboratory utilizing Atomic Absorption Spectrometry (AAS Flame) methodology. Reports of laboratory analysis of the suspect lead-containing paint samples collected and sample chain-of-custody documentation are included in Appendix D.

4.0 REGULATORY OVERVIEW

The State of Texas has established the Texas Asbestos Health Protection Rules (TAHPR) which requires any asbestos-related activity to be performed by an individual licensed by the State of Texas, through the TDSHS. An asbestos related activity consists of the disturbance (whether intentional or unintentional), removal, encapsulation, or enclosure of asbestos, including preparations or final clearance, the performance of asbestos surveys, the development of management plans and response actions, asbestos project design, the collection or analysis of asbestos samples, monitoring for airborne asbestos, bidding for a contract for any of these activities, or any other activity required to be licensed under TAHPR.

Abatement must be performed by a State of Texas licensed asbestos abatement contractor in accordance with a project design prepared by a State of Texas licensed asbestos consultant.

In addition, third party air monitoring must be conducted during the abatement activities.

The asbestos NESHAP (40 CFR Part 61 Subpart M) regulates asbestos fiber emission and asbestos waste disposal practices. It also requires the identification and classification of existing building materials prior to demolition or renovation activity. Under NESHAP, asbestos containing building materials are classified as either friable, Category I non-friable or Category II non-friable ACM. Friable materials are those that, when dry, may be crumbled, pulverized or

January 25, 2016 ■ Terracon Project No. 88157214

Responsive ■ Resourceful ■ Reliable 5 reduced to powder by hand pressure. Category I non-friable ACM includes packing, gaskets, resilient floor coverings and asphalt roofing products containing more than 1% asbestos.

Category II non-friable ACM are any materials other than Category I materials that contain more than 1% asbestos.

Friable ACM, Category I and II non-friable ACM in poor condition and has become friable or which will be subject to drilling, sanding, grinding, cutting, or abrading and which could be crushed or pulverized during anticipated renovation or demolition activities are considered regulated ACM (RACM). RACM must be removed prior to renovation or demolition activities.

The TAHPR and NESHAP require that written notification be submitted before beginning renovation projects which include the disturbance of any asbestos-containing material (ACM) in a building or facility, or before the demolition of a building or facility, even when no asbestos is present. This written notification must be provided to the TDSHS at least 10 working days prior to the commencement of asbestos abatement or demolition activities. Removal of RACM must be conducted by a State of Texas licensed asbestos contractor. In addition, third party air monitoring must be performed during the abatement.

The Occupational Safety and Health Administration (OSHA) Asbestos standard for the construction industry (29 CFR 1926.1101) regulates workplace exposure to asbestos. The OSHA standard requires employee exposure to airborne asbestos fibers be maintained below

0.1 asbestos fibers per cubic centimeter of air (0.1 f/cc). The OSHA standard classifies construction and maintenance activities which could disturb ACM and specifies work practices and precautions which employers must follow when engaging in each class of regulated work.

The State of Texas has established the Texas Environmental Lead Reduction Rules (TELRR) Texas Administrative Code (TAC), Title 25, Part 1, Chapter I, Subchapter 295 to establish the means to control and minimize public exposure to lead by regulating lead-based paint activities in target housing and child-occupied facilities. The TELRR contains procedures and requirements for the accreditation of lead training providers, procedures and requirements for the certification of individuals and firms engaged in lead-based paint activities and standards for performing such activities in target housing and child-occupied facilities. The TELRR requires that all lead-based paint activities in target housing and child-occupied facilities be performed by certified individuals.

Regulatory agencies (HUD, TDSHS) have defined LBP as a paint or other surface coating that contains equal to or greater than ≥5,000 parts per million (ppm) of lead or more than 0.5% of lead by weight for buildings that meet the definition of target housing. The Occupational Safety and Health Administration (OSHA) define LBP as a paint which contains lead, regardless of the concentration.

The OSHA Lead Standard for Construction (29 CFR 1926.62) applies to construction work where an employee may be occupationally exposed to lead. All work related to construction, January 25, 2016 ■ Terracon Project No. 88157214

Responsive ■ Resourceful ■ Reliable 6 alteration, or repair (including painting and decorating) is included. The lead-in-construction standard applies to any detectable concentration of lead in paint. OSHA considers paint containing any level of lead above the analytical method detection limit a potential hazard which should be communicated to any employees or contractors who may disturb the materials in the course of their assigned work.

As the building on the site is an industrial facility rather than Child Occupied or Target Housing, HUD and TDSHS lead regulations do not apply to removal operations within the facility. It is, however, recommended that they be consulted as a general guideline for occupant protection.

5.0 FINDINGS AND RECOMMENDATIONS

Laboratory analysis indicated no asbestos was detected in the materials sampled within the Pump Station located on the site.

It should be noted that suspect materials, other than those identified during the December 22, 2015, survey may exist within the building. Should suspect materials other than those which were identified during this survey be uncovered prior to or during the renovation process, those materials should be assumed asbestos-containing until sampling and analysis can confirm or deny their asbestos content.

Laboratory analytical reports related to the asbestos sampling are included in Appendix B.

Five (5) of the six (6) bulk materials sampled and analyzed as part of this survey were found to contain lead in a concentration exceeding the detection limit, but less than 5,000 PPM which would render the material “Lead-Containing” and be considered a potential hazard by OSHA.

n L-01 – The light gray on light green paint material applied to select plaster and brick walls in the building was found to contain 2,100 ppm lead. Where observed, this material was found to be in good condition.

n L-03 – The black paint material applied to the metal hand rails in the building was found to contain 420 ppm lead. Where observed, this material was found to be in good condition.

n L-04 – The black on red paint materials applied to the concrete beams in the building was found to contain 120 ppm lead. Where observed, this material was found to be in good condition.

n L-05 – The green paint material applied to the metal doors and door frames of the

January 25, 2016 ■ Terracon Project No. 88157214

Responsive ■ Resourceful ■ Reliable 7 building was found to contain 1,500 ppm lead. Where observed, this material was found to be in good condition.

n L-06 – The beige paint material applied to the concrete exterior walls of the building was found to contain 31 ppm lead. Where observed, this material was found to be in good condition.

The single remaining surface coating sampled and analyzed as part of this survey was found to contain lead in a concentration exceeding 5,000 PPM, which would be considered “Lead-Based Paint” and disturbance would likely pose a potential workforce hazard:

n L-02 – The gray on light gray on dark green paint materials applied to select brick walls in the building was found to contain 30,000 ppm lead. Where observed, this material was found to be in good condition.

In areas where the Client does not intend to renovate or demolish the facility, the lead-containing/lead-based paint materials, which will remain in the facility, should be managed in place. It is recommended that this in-place management should include such operations as stabilizing or repairing any damaged materials, protecting the remaining containing paint materials from further damage, and developing a plan to periodically monitor the condition of the lead-based/containing paint materials. Notification of the presence of the materials should also be made to employees and outside contractors so that they do not inadvertently disturb the remaining lead-containing paint materials.

In areas where the renovation/demolition project which could disturb the lead-containing/lead-based paint materials within the facility is to be conducted, it is recommended that contracting personnel who may disturb the paint materials within the facility be made aware of the lead content in the materials so that they may exercise proper OSHA procedures for personnel monitoring and possibly employ protective procedures when working with the coatings.

It is recommended if impacted by renovation or demolition activities, any painted metal building components which are to be removed from the facility be segregated from the waste stream and be transferred to a suitable metal recycling facility. As the facility is a public facility rather than Target Housing, HUD and TDSHS lead regulations do not apply to removal operations within the facility. It is, however, recommended that they be consulted as a general guideline for occupant protection and that OSHA notification be made to all employees or contractors working on any repair, renovation or demolition projects within the facility.

Compliance with applicable OSHA lead regulations is the responsibility of the contractor performing the work and it is recommended that they be required to communicate potential lead hazards to their workforce and utilize lead-safe work practices such as outlined in the

January 25, 2016 ■ Terracon Project No. 88157214

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EPA Renovation, Repair, and Painting (RRP) Final Rule (40 CFR 745) or applicable portions of the Structural Steel Painting Council (SSPC) Guidelines. It is further recommended that activities such as flame/torch dismantling, dry sanding and/or dry grinding of any components with lead-containing materials applied should be prohibited as part of any repair, renovation or demolition activity.

6.0 GENERAL COMMENTS

This asbestos survey and LCP survey was conducted in a manner consistent with the level of care and skill ordinarily exercised by members of the profession currently practicing under similar conditions in the same locale. The results, findings, conclusions and recommendations expressed in this report are based on conditions observed during our survey of the buildings.

The information contained in this report is relevant to the date on which this survey was performed, and should not be relied upon to represent conditions at a later date. This report has been prepared on behalf of and exclusively for use by the Hidalgo County Irrigation District No. 1 for specific application to their project as discussed. This report is not a bidding document. Contractors or consultants reviewing this report must draw their own conclusions regarding further investigation or remediation deemed necessary. Terracon does not warrant the work of regulatory agencies, laboratories or other third parties supplying information which may have been used in the preparation of this report. No warranty, express or implied is made.

APPENDIX A

ASBESTOS SURVEY SAMPLE SUMMARY

Pump Station

East Old Military Road Penitas, Texas

Terracon Project No. 88157214

Responsive ■ Resourceful ■ Reliable

SAMPLE

NUMBER

MATERIAL

DESCRIPTION

HOMOGENEOUS AREA

SAMPLE

LOCATION

LAB

RESULTS

01 Plaster – Gray with Medium Texture

Utilized on the interior walls of the Pump Station

Pump Station – Northwest Corner

None Detected

02 Plaster – Gray with Medium Texture

Utilized on the interior walls of the Pump Station

Pump Station – Southwest Corner

None Detected

03 Plaster – Gray with Medium Texture

Utilized on the interior walls of the Pump Station

Pump Station – Southeast Corner

None Detected

04 Plaster – Gray with Medium Texture

Utilized on the interior walls of the Pump Station

Pump Station – Northeast Corner

None Detected

05 Plaster – Gray with Medium Texture

Utilized on the interior walls of the Pump Station

Pump Station – North Middle Portion

None Detected

06 Cloth Pipe Insulation – Off- White (no mastic)

Utilized on the majority of exhaust piping of the pump engines in the

Pump Station

Pump Engine - Northwest of Pump

Station

None Detected

07 Cloth Pipe Insulation – Off- White (no mastic)

Utilized on the majority of exhaust piping of the pump engines in the

Pump Station Pump Engine – Middle of West Wall None

Detected

08 Cloth Pipe Insulation – Off- White (no mastic)

Utilized on the majority of exhaust piping of the pump engines in the

Pump Station

Pump Engine – Southwest of Pump

Station

None Detected

09 Pipe Insulation – Silver (no mastic)

Utilized on a portion of the exhaust piping of the pump engines in the

Pump Station

Pump Engine – Middle of West Wall

None Detected

10 Pipe Insulation – Silver (no mastic)

Utilized on a portion of the exhaust piping of the pump engines in the

Pump Station Pump Engine – Middle of West Wall None

Detected

11 Pipe Insulation – Silver (no mastic)

Utilized on a portion of the exhaust piping of the pump engines in the

Pump Station

Pump Engine – Northwest of Pump

Station

None Detected

12 Window Caulking Utilized on the windows on the north wall of the Pump Station

Window – Northeast of Pump Station

None Detected

Pump Station

East Old Military Road Penitas, Texas

Terracon Project No. 88157214

Responsive ■ Resourceful ■ Reliable

SAMPLE

NUMBER

MATERIAL

DESCRIPTION

HOMOGENEOUS AREA

SAMPLE

LOCATION

LAB

RESULTS

13 Window Caulking Utilized on the windows on the north wall of the Pump Station

Window – Middle of North Wall of Pump

Station

None Detected

14 Window Caulking Utilized on the windows on the north wall of the Pump Station

Window – Northwest of Pump Station

None Detected

15 Plaster - Beige Utilized on exterior elevations of the Pump Station

Pump Station – Northeast Corner

None Detected

16 Plaster - Beige Utilized on exterior elevations of the Pump Station

Pump Station – Northeast Corner

None Detected

17 Plaster - Beige Utilized on exterior elevations of the Pump Station

Pump Station – Middle of North elevation

None Detected

18 Plaster - Beige Utilized on exterior elevations of the Pump Station

Pump Station – Northwest Corner

None Detected

19 Plaster - Beige Utilized on exterior elevations of the Pump Station

Pump Station – Southwest Corner

None Detected

APPENDIX B

ASBESTOS ANALYTICAL LABORATORY REPORT

PLM Summary Report

Client :

Project :

Project # :

Identification :

Test Method :

Terracon - Pharr

Penitas Pump Station

88157214

Asbestos, Bulk Sample Analysis

Sample Number Client Sample Description / Location Asbestos Content

Sample Date :

On 12/23/2015, nineteen (19) bulk material samples were submitted by Eloy Palacios of Terracon - Pharr for asbestos analysis by PLM/DS. The PLM

Detail Report is attached; additional information may be found therein. The results are summarized below:

Lab Job No. :

Report Date :

15B-15818

12/22/2015

12/28/2015

NVLAP Lab Code 102056-0

TDSHS License No. 30-0084

Polarized Light Microscopy / Dispersion Staining (PLM/DS)

EPA Method 600 / R-93 / 116

2051 Valley View Lane

Farmers Branch, TX 75234 Phone: (972) 241-8460

1 Interior Plaster on Motor (Grey Medium Texture), NWC of

Pump House

None Detected - Plaster

2 Interior Plaster on Motor (Grey Medium Texture), SWC of

Pump House

None Detected - Plaster

3 Interior Plaster on Motor (Grey Medium Texture), SEC of

Pump House

None Detected - Plaster

4 Interior Plaster on Motor (Grey Medium Texture), NEC of

Pump House

None Detected - Plaster

5 Interior Plaster on Motor (Grey Medium Texture), North

Middle of Pump House

None Detected - Plaster

6 Cloth Pipe Wrap (Off-White), Northwest Motor Pipe None Detected - Glass Fiber Wrap

7 Cloth Pipe Wrap (Off-White), Middle West Motor Pipe None Detected - Glass Fiber Wrap

8 Cloth Pipe Wrap (Off-White), Southwest Motor Pipe None Detected - Glass Fiber Wrap

9 Pipe Wrap (Silver), Middle West Motor Pipe None Detected - Thermal Insulation

None Detected - Foil Wrap

10 Pipe Wrap (Silver), Middle West Motor Pipe None Detected - Thermal Insulation

None Detected - Foil Wrap

11 Pipe Wrap (Silver), Northwest Motor Pipe None Detected - Thermal Insulation

None Detected - Foil Wrap

12 Window Caulking, Northeast Window None Detected - Caulking

13 Window Caulking, Middle Window None Detected - Caulking

14 Window Caulking, Northwest Window None Detected - Caulking

15 Exterior Plaster over Motor, Paint (Beige), NEC of

Building

None Detected - Plaster

None Detected - Paint / Texture

16 Exterior Plaster over Motor, Paint (Beige), NEC of

Building

None Detected - Plaster

None Detected - Paint / Texture

PLM Summary Report

Client :

Project :

Project # :

Identification :

Test Method :

Terracon - Pharr

Penitas Pump Station

88157214

Asbestos, Bulk Sample Analysis

Sample Number Client Sample Description / Location Asbestos Content

Sample Date :

On 12/23/2015, nineteen (19) bulk material samples were submitted by Eloy Palacios of Terracon - Pharr for asbestos analysis by PLM/DS. The PLM

Detail Report is attached; additional information may be found therein. The results are summarized below:

Lab Job No. :

Report Date :

15B-15818

12/22/2015

12/28/2015

NVLAP Lab Code 102056-0

TDSHS License No. 30-0084

Polarized Light Microscopy / Dispersion Staining (PLM/DS)

EPA Method 600 / R-93 / 116

2051 Valley View Lane

Farmers Branch, TX 75234 Phone: (972) 241-8460

17 Exterior Plaster over Motor, Paint (Beige), Middle North of Building

None Detected - Plaster

None Detected - Paint / Texture

18 Exterior Plaster over Motor, Paint (Beige), NWC of

Building

None Detected - Plaster

None Detected - Paint / Texture

19 Exterior Plaster over Motor, Paint (Beige), NWC of

Building

None Detected - Plaster

None Detected - Paint / Texture

Heather LopezAnalyst(s):

Lab Director : Bruce Crabb Approved Signatory :

Thank you for choosing Moody Labs

Lab Manager : Heather Lopez Approved Signatory :

These samples were analyzed by layers. Quantification, unless otherwise noted, is performed by calibrated visual estimate. The test report shall not be reproduced, except in full, without written approval of the laboratory. The results relate only to the items tested. These test results do not imply endorsement by NVLAP or any agency of the U.S.

Government. Accredited by the National Voluntary Laboratory Accreditation Program for Bulk Asbestos Fiber Analysis under Lab Code 102056-0.

PLM Detail Report

Project # : 88157214

Sample Number Layer Components % Of

Sample

Analysis

Date

% of

Layer Analyst

Supplement to PLM Summary Report

Client :

Project :

Terracon - Pharr

Penitas Pump Station

Lab Job No. :

Report Date :

15B-15818

12/28/2015

2051 Valley View Lane

Farmers Branch, TX 75234 Phone: (972) 241-8460

Moody Labs NVLAP Lab Code 102056-0

TDSHS License No. 30-0084

Aggregate1 Plaster (Grey) 5% 12/2465% HL

Calcite / Binders1 Plaster (Grey) 5% 12/2435% HL

Calcite1 Paint / Texture (White/Green/Grey) 95% 12/2425% HL

Pigment / Binders1 Paint / Texture (White/Green/Grey) 95% 12/2475% HL

Aggregate2 Plaster (Grey) 50% 12/2465% HL

Calcite / Binders2 Plaster (Grey) 50% 12/2435% HL

Calcite2 Paint / Texture (White/Green/Grey) 50% 12/2425% HL

Pigment / Binders2 Paint / Texture (White/Green/Grey) 50% 12/2475% HL

Aggregate3 Plaster (Grey) 50% 12/2465% HL

Calcite / Binders3 Plaster (Grey) 50% 12/2435% HL

Calcite3 Paint / Texture (White/Green/Grey) 50% 12/2425% HL

Pigment / Binders3 Paint / Texture (White/Green/Grey) 50% 12/2475% HL

Aggregate4 Plaster (Grey) 50% 12/2465% HL

Calcite / Binders4 Plaster (Grey) 50% 12/2435% HL

Talc Fibers4 Paint / Texture (White/Grey) 50% 12/24<1% HL

Calcite4 Paint / Texture (White/Grey) 50% 12/2425% HL

Pigment / Binders4 Paint / Texture (White/Grey) 50% 12/2475% HL

Aggregate5 Plaster (Grey) 5% 12/2465% HL

Calcite / Binders5 Plaster (Grey) 5% 12/2435% HL

Calcite5 Paint / Texture (White/Green/Grey) 95% 12/2425% HL

Pigment / Binders5 Paint / Texture (White/Green/Grey) 95% 12/2475% HL

Glass Wool Fibers6 Glass Fiber Wrap (White) 100% 12/24100% HL

Glass Wool Fibers7 Glass Fiber Wrap (White) 100% 12/24100% HL

Glass Wool Fibers8 Glass Fiber Wrap (White) 100% 12/24100% HL

Mineral Wool Fibers9 Thermal Insulation (White) 80% 12/24100% HL

Metal Foil9 Foil Wrap (Silver) 20% 12/24100% HL

Mineral Wool Fibers10 Thermal Insulation (White) 80% 12/24100% HL

Metal Foil10 Foil Wrap (Silver) 20% 12/24100% HL

Sample Number Layer Components % Of

Sample

Analysis

Date

% of

Layer Analyst

Supplement to PLM Summary Report

Client :

Project :

Terracon - Pharr

Penitas Pump Station

Lab Job No. :

Report Date :

15B-15818

12/28/2015

2051 Valley View Lane

Farmers Branch, TX 75234 Phone: (972) 241-8460

Moody Labs NVLAP Lab Code 102056-0

TDSHS License No. 30-0084

Mineral Wool Fibers11 Thermal Insulation (White) 80% 12/24100% HL

Metal Foil11 Foil Wrap (Silver) 20% 12/24100% HL

Sand12 Caulking (Tan) 100% 12/2435% HL

Calcite12 Caulking (Tan) 100% 12/2440% HL

Binders / Fillers12 Caulking (Tan) 100% 12/2425% HL

Sand13 Caulking (Tan) 100% 12/2435% HL

Calcite13 Caulking (Tan) 100% 12/2440% HL

Binders / Fillers13 Caulking (Tan) 100% 12/2425% HL

Calcite14 Caulking (Light Grey) 100% 12/2450% HL

Binders / Fillers14 Caulking (Light Grey) 100% 12/2450% HL

Aggregate15 Plaster (Grey) 50% 12/2465% HL

Calcite / Binders15 Plaster (Grey) 50% 12/2435% HL

Calcite15 Paint / Texture (White/Beige) 50% 12/2425% HL

Pigment / Binders15 Paint / Texture (White/Beige) 50% 12/2475% HL

Aggregate16 Plaster (Grey) 2% 12/2765% HL

Calcite / Binders16 Plaster (Grey) 2% 12/2735% HL

Talc Fibers16 Paint / Texture (White/Beige) 98% 12/27<1% HL

Calcite16 Paint / Texture (White/Beige) 98% 12/2725% HL

Pigment / Binders16 Paint / Texture (White/Beige) 98% 12/2775% HL

Aggregate17 Plaster (Grey) 2% 12/2765% HL

Calcite / Binders17 Plaster (Grey) 2% 12/2735% HL

Calcite17 Paint / Texture (White/Beige) 98% 12/2725% HL

Pigment / Binders17 Paint / Texture (White/Beige) 98% 12/2775% HL

Aggregate18 Plaster (Grey) 50% 12/2765% HL

Calcite / Binders18 Plaster (Grey) 50% 12/2735% HL

Calcite18 Paint / Texture (White/Beige) 50% 12/2725% HL

Pigment / Binders18 Paint / Texture (White/Beige) 50% 12/2775% HL

Sample Number Layer Components % Of

Sample

Analysis

Date

% of

Layer Analyst

Supplement to PLM Summary Report

Client :

Project :

Terracon - Pharr

Penitas Pump Station

Lab Job No. :

Report Date :

15B-15818

12/28/2015

2051 Valley View Lane

Farmers Branch, TX 75234 Phone: (972) 241-8460

Moody Labs NVLAP Lab Code 102056-0

TDSHS License No. 30-0084

Aggregate19 Plaster (Grey) 2% 12/2765% HL

Calcite / Binders19 Plaster (Grey) 2% 12/2735% HL

Calcite19 Paint / Texture (White/Beige) 98% 12/2725% HL

Pigment / Binders19 Paint / Texture (White/Beige) 98% 12/2775% HL

APPENDIX C

LEAD SAMPLE SUMMARY

APPENDIX C

LEAD-CONTAINING PAINT SURVEY SUMMARY

Pump Station

East Old Military Road Penitas, Texas

Terracon Project No. 88157214

SAMPLE

NO.

COMBINATION/

SUBSTRATE FUNCTIONAL AREA SAMPLE LOCATION LEAD

CONTENT

L-01 Light Gray on Light Green /

Plaster

Applied to interior concrete and brick walls

Pump Station – Northwest Corner 2,100 ppm

L-02 Gray on Light Gray on Dark

Green / Plaster

Applied to the lower portion of brick interior walls

Pump Station – North Wall, Central 30,000 ppm

L-03 Black / Metal Hand Rails

Applied to the metal rails in the Pump Station

Guardrail – Southwest Portion of Pump Station 420 ppm

L-04 Black on Red / Concrete Beam

Applied to concrete beams in the Pump Station

Pump Station – Northwest Corner 120 ppm

L-05 Green / Metal

Door Applied to the metal doors of the Pump Station Metal Door - North wall 1,500 ppm

L-06 Beige / Concrete

Wall Applied to exterior elevations of the Pump Station Pump Station – Northwest

Corner 31 ppm

APPENDIX D

LEAD ANALYTICAL LABORATORY DATA

Analysis Report

Client:

Project/Test Address:

Terracon - Pharr

7469 Whitepine Rd

Telephone: 800.347.4010

Richmond, VA 23237

Environmental Hazards Services, L.L.C.

Penitas Pump Station; Southwest of Intersection of Penitas St. and FM 1427, Penitas, Texas

Client Number:

200277

Fax Number:

956-283-8279Laboratory Results

Analyzed Date:

Client Sample Number

Lab Sample Number

Analyte: Concentration ppm (mg/kg)

Metals

12/24/2015

12/23/2015

15-12-03082

Reported Date:

Received Date:

Report Number:

1506 Mid Cities Dr Pharr, TX 78577

Narrative ID

Paint

Lead (Pb) 2100L1 12/24/201515-12-03082-001

Lead (Pb) 30000L2 12/24/201515-12-03082-002

Lead (Pb) 420L3 12/24/201515-12-03082-003

Lead (Pb) 120L4 12/24/201515-12-03082-004

Lead (Pb) 1500L5 12/24/201515-12-03082-005

Lead (Pb) 31L6 12/24/201515-12-03082-006

Page 2of1

Report Number:

Environmental Hazards Services, L.L.C

Project/Test Address:

Client Number: 15-12-03082

Penitas Pump Station; Southwest of Intersection of Penitas St. and FM 1427, Penitas, Texas

200277

Analyzed Date:

Client Sample Number

Lab Sample Number

Concentration ppm (mg/kg)

Narrative IDAnalyte:

Julie Dickerson

Laboratory Administrator

Analyst: Brittany Meyer

Method:

Sample Results denoted with a “less than” (<) sign contains less than the reporting limit for each particular metal, based on a 100mL volume.

The reporting limit for Mercury is 0.10 ug and 10ug for all other metals. To convert metals concentration (ppm) to % by weight, divide the above concentration by 10,000.

LEGEND ug = microgram ppm = parts per million mL = milliliter mg/kg = milligrams per kilogram

Reviewed By Authorized Signatory:

Mercury (Hg): EPA SW846 7471B

All other metals: EPA SW846 3050B/6010C

The condition of the samples analyzed was acceptable upon receipt per laboratory protocol unless otherwise noted on this report. Results represent the analysis of samples submitted by the client. Sample location, description, area, volume, etc., was provided by the client. If the report does not contain the result for a field blank, it is due to the fact that the client did not include a field blank with their samples. EHS sample results do not reflect blank correction. This report shall not be reproduced except in full, without the written consent of the

Environmental Hazards Service, L.L.C. California Certification #2319 NY ELAP #11714.

Page 2of2

APPENDIX E

LICENSES AND CERTIFICATIONS

AIHA Laboratory Accreditation Programs, LLC 3141 Fairview Park Drive, Suite 777, Falls Church, VA 22042 USA main +1 703-846-0736 fax +1 703-207-8558 Twitter: @AIHA_LAP_LLC

R1 04/26/2013

July 31, 2014

Laboratory ID: 100420

Julie Dickerson Environmental Hazards Services, LLC 7469 White Pine Road Richmond, VA 23237

Dear Ms. Dickerson:

Congratulations! The AIHA Laboratory Accreditation Programs (AIHA-LAP), LLC’s Analytical Accreditation Board (AAB) has approved the request of Environmental Hazards Services, LLC to add the following Field of Testing (FoT) within the Industrial Hygiene program: Gas Chromatography.

Attached, please find an updated IHLAP scope page including the new FoTs. Laboratory accreditation shall be maintained by continued compliance with IHLAP requirements (see Policy Modules 2B and 6), which includes proficient participation in AIHA-LAP, LLC approved proficiency testing, demonstration of competency, or round robin program as indicated on the AIHA-LAP “Approved PT and Round Robin” webpage, its associated PT-Scope table, and as required in Policy Module 6, for all Fields of Testing (FoTs) for which the laboratory is accredited. An accredited laboratory that wishes to expand into a new FoT must submit an updated accreditation application to AIHA-LAP, LLC for review by the AAB.

Any changes in ownership, laboratory location, personnel, FoTs, or significant procedural changes shall be reported to AIHA-LAP, LLC in writing within twenty (20) business days of the change.

The accreditation certificate and scope page is the property of AIHA-LAP, LLC and must be returned to AIHA- LAP, LLC should the laboratory withdraw or be removed from the IHLAP.

Again, congratulations. If you have any questions, please contact Lauren Maher, Laboratory Accreditation Specialist, at (703) 846-0716.

Sincerely, Cheryl O. Morton Managing Director

3141 Fairview Park Drive, Suite 777, Falls Church, VA 22042 USA main +1 703-846-0736 fax +1 703-207-8558 Twitter: @AIHA_LAP_LLC

R2 04/26/2013

April 30, 2014

Laboratory ID: 100420

Julie Dickerson Environmental Hazards Services, LLC 7469 White Pine Road Richmond, VA 23237

Dear Ms. Dickerson:

Congratulations! The AIHA Laboratory Accreditation Programs (AIHA-LAP), LLC’s Analytical Accreditation Board (AAB) has approved Environmental Hazards Services, LLC as an accredited Industrial Hygiene, Environmental Lead and Environmental Microbiology laboratory.

Accreditation documentation includes the IHLAP, ELLAP and EMLAP accreditation certificate, scope of accreditation document and a copy of the current AIHA-LAP, LLC license agreement (if your completed agreement is not on file at AIHA-LAP, LLC). The accreditation logo has been designed for use by all AIHA-LAP, LLC accredited laboratories. If your laboratory chooses to use the logo in its advertising the laboratory’s accreditation, you must complete and return the AIHA-LAP, LLC license agreement to a Laboratory Accreditation Specialist.

Once submitted, an electronic copy of the accreditation logo will be sent to you. Please inform us if your laboratory does not wish to use the logo in advertising.

Laboratory accreditation shall be maintained by continued compliance with IHLAP, ELLAP and EMLAP requirements (see Policy Modules 2B, 2C, 2D, and 6), which includes proficient participation in AIHA-LAP, LLC approved proficiency testing, demonstration of competency, or round robin program as indicated on the AIHA-LAP “Approved PT and Round Robin” webpage, its associated PT-Scope table, and as required in Policy Module 6, for all Fields of Testing (FoTs) for which the laboratory is accredited. An accredited laboratory that wishes to expand into a new FoT must submit an updated accreditation application to AIHA-LAP, LLC for review by the AAB.

Any changes in ownership, laboratory location, personnel, FoTs/Methods, or significant procedural changes shall be reported to AIHA-LAP, LLC in writing within twenty (20) business days of the change.

The accreditation certificate is the property of AIHA-LAP, LLC and must be returned to us should your laboratory withdraw or be removed from the Industrial Hygiene, Environmental Lead and Environmental Microbiology.

Again, congratulations. If you have any questions, please contact Lauren Maher, Laboratory Accreditation Specialist, at (703) 846-0716.

Sincerely, Cheryl O. Morton Managing Director

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SCOPE OF ACCREDITATION

Environmental Hazards Services, LLC Laboratory ID: 100420 7469 White Pine Road, Richmond, VA 23237 Issue Date: 07/31/2014

The laboratory is approved for those specific field(s) of testing/methods listed in the table below. Clients are urged to verify the laboratory’s current accreditation status for the particular field(s) of testing/Methods, since these can change due to proficiency status, suspension and/or withdrawal of accreditation.

Industrial Hygiene Laboratory Accreditation Program (IHLAP)

Initial Accreditation Date: 03/01/1990

A complete listing of currently accredited Industrial Hygiene laboratories is available on the AIHA-LAP, LLC website at: http://www.aihaaccreditedlabs.org

IHLAP Scope Category

Field of Testing (FoT)

Technology sub-type/ Detector

Published Reference Method/Title of In-house

Method

Method Description or Analyte

(for internal methods only)

Chromatography Core Gas Chromatography GC/ECD NIOSH 5503

Spectrometry Core Atomic Absorption CVAA

NIOSH 6009

OSHA ID-145

FAA NIOSH 7082 Modified Inductively-Coupled

Plasma ICP/AES

NIOSH 7300

OSHA ID-125

Asbestos/Fiber

Microscopy Core Phase Contrast

Microscopy (PCM) NIOSH 7400

Miscellaneous Core Gravimetric

NIOSH 0500

NIOSH 0600

100420_Scope_ELLAP_2014_04_30

Environmental Hazards Services, LLC Laboratory ID: 100420 7469 White Pine Road, Richmond, VA 23237 Issue Date: 04/30/2014

The laboratory is approved for those specific field(s) of testing/methods listed in the table below. Clients are urged to verify the laboratory’s current accreditation status for the particular field(s) of testing/Methods, since these can change due to proficiency status, suspension and/or withdrawal of accreditation.

The EPA recognizes the AIHA-LAP, LLC ELLAP program as meeting the requirements of the National Lead Laboratory Accreditation Program (NLLAP) established under Title X of the Residential Lead-Based Paint Hazard Reduction Act of 1992 and includes paint, soil and dust wipe analysis. Air analysis is not included as part of the NLLAP.

Environmental Lead Laboratory Accreditation Program (ELLAP)

Initial Accreditation Date: 03/01/1999

A complete listing of currently accredited Environmental Lead laboratories is available on the AIHA-LAP, LLC website at: http://www.aihaaccreditedlabs.org

Field of Testing (FoT) Method Method Description (for internal methods only)

Paint

ASTM E-1645

ASTM E1979-12

EPA SW-846 3050B

EPA SW-846 6010C

EPA SW-846 7000B

Soil

ASTM E-1645

ASTM E1979-12

EPA SW-846 3050B

EPA SW-846 6010C

EPA SW-846 7000B

Settled Dust by Wipe

ASTM E1979-12

EPA SW-846 3050B

EPA SW-846 6010C

EPA SW-846 7000B

Airborne Dust

ASTM E1979-12

EPA SW-846 7000B

NIOSH 7082

NIOSH 7300 Modified

Composited Wipes ASTM E1979-12 Modified

EPA SW-846 6010C

EPA SW-846 7000B

100420_Scope_EMLAP_2014_04_30

Environmental Hazards Services, LLC Laboratory ID: 100420 7469 White Pine Road, Richmond, VA 23237 Issue Date: 04/30/2014

The laboratory is approved for those specific field(s) of testing/methods listed in the table below. Clients are urged to verify the laboratory’s current accreditation status for the particular field(s) of testing/Methods, since these can change due to proficiency status, suspension and/or withdrawal of accreditation.

Environmental Microbiology Laboratory Accreditation Program (EMLAP)

Initial Accreditation Date: 03/01/2005

EMLAP Category Field of Testing (FoT) Method Method Description

(for internal methods only)

Fungal

Air - Direct Examination Microbiology SOP In-house: Analysis of Spore Trap Samples

Bulk - Direct Examination Microbiology SOP In-house: Analysis of IAQ Bulk Samples

Surface - Direct Examination Microbiology SOP In-house: Analysis of IAQ Surface

Samples

A complete listing of currently accredited Environmental Microbiology laboratories is available on the AIHA-LAP, LLC website at: http://www.aihaaccreditedlabs.org

APPENDIX F

SAMPLE LOCATION MAP

Ian Howes Lead License Exp 1-31-16.pdf
1.0INTRODUCTION
1.1Project Objective
2.0BUILDING DESCRIPTION
3.0FIELD ACTIVITIES
3.1Visual Assessment
3.2Physical Assessment
3.3Sample Collection
3.4Sample Analysis
4.0REGULATORY OVERVIEW
5.0FINDINGS AND RECOMMENDATIONS
6.0GENERAL COMMENTS
P-04
EHS 2016_certificate.pdf
Environmental Hazards Services, LLC
7469 White Pine Road, Richmond, VA 23237
Laboratory ID: 100420
LABORATORY ACCREDITATION PROGRAMS
ADP6E59.tmp
July 31, 2014

File details come from the government source that posted it. Updated .