Attachment_9_JIONA_Final_Lead-Based_Paint_Report_6Dec2016.pdf

Aarcher, Inc.

2635 Riva Road, Suite 100 Annapolis, MD 21401 410-897-9100 x103 T cschwartz@aarcherinc.com

Bureau of Land Management National Operations Center, OC-670 Denver Federal Center Building 50, 5th Street Denver, Colorado 80225-0047

303.236.6418 T

kmorin@blm.gov

Lead-Based Paint & Polychlorinated Biphenyls Survey Report

Jupiter Inlet Outstanding Natural Area

BPA L14PA00047

Task Order L16PB00856 / Call 091

COMPLIANCE ASSESSMENT – SAFETY, HEALTH, AND THE

ENVIRONMENT (CASHE)

Survey Date:

October 18, 2016

Report Date:

NV5, Inc.

1713 South Kings Avenue Main: 813-571-9788 Brandon, Florida 33511 www.NV5.com Fax: 813-571-9374

December 6, 2016

NV5 Project No.: 16-20155

Aarcher Institute of Environmental Training, LLC 2635 Riva Road Annapolis, Maryland 31401

Attention: Ms. Sarah Campbell, PMP

Reference: Survey for Lead-Based Paint and Polychlorinated Biphenyls (PCBs) Jupiter Inlet Outstanding Natural Area Jupiter, Florida

Dear Ms. Campbell:

A survey for Lead-Based Paint (LBP) and PCBs was performed at the above referenced facility, on October 18, 2016 by Mr. Steven A. Lipson, a Certified Industrial Hygienist (CIH) who is also an accredited lead Inspector and Risk Assessor.

Measurements of lead in paint and lead in soil content were made using an Olympus Alpha X-Ray Fluorescence (XRF) device. Additionally, three confirmatory paint chip samples and 18 bulk soil samples were collected and forwarded to EMSL Analytical, Inc., in Cinnaminson, New Jersey for analysis via Atomic Absorption Spectrometry (AAS) in accordance with Method SW 846 3050B/7000B. Paint chip samples were collected of materials found to contain inconclusive concentrations of lead via XRF measurement. A single composite soil sample was collected for each structure with subsamples collected from all sides. Lastly, a total of two bulk samples (paint and window caulk) for polychlorinated biphenyls (PCBs) were collected for laboratory analysis by EPA Method 3540C/8082A, in locations including the Radio Beacon Building, Laundry Building, and four housing facilities identified by the client at the time of the survey.

this project was formulated and completed to meet and exceed requirements of BOTH the OSHA Lead in Construction standard (29 CFR 1926.62) and the EPA's Renovation, Repair and Painting (RRP) Program.

The scope of work performed by NV5 on this project included sampling of accessible interior and exterior components of thirteen residential structures occupying between 1,200 and 1,400 square feet each; plus benches, a lighthouse, three bay garage, laundry building, and a radio beacon building occupying between 100 and 1,000 square feet each.

Jupiter Inlet Outstanding Natural Area Page #2 Jupiter, Florida NV5 Project #: 16-20155

If you should have any questions regarding this information, please do not hesitate to contact our office at (813) 571-9788.

Sincerely, Steven A. Lipson, CIH, CSP Vice President OHSE Services Certified Lead Paint Inspector and Risk Assessor

Jupiter Inlet Outstanding Natural Area Page #3

TABLE OF CONTENTS

SECTION PAGE

1.0 Scope of Work 4

2.0 Summary of Findings 5

3.0 Conclusions & Recommendations 7

4.0 Sampling Methodology 8

5.0 Estimated Abatement Costs 12

Appendices Analytical XRF Results Certifications

Jupiter Inlet Outstanding Natural Area Page #4

1.0 Scope of Work

NV5 performed a lead-based paint inspection of the facility. During the evaluation, XRF testing was performed on accessible painted surfaces throughout each sampled area.

The facility contains former U.S. Coast Guard housing and associated buildings and was constructed between 1905 and 1962. The XRF testing was conducted using an Olympus Alpha XRF lead paint analyzer. A surface-by-surface visual assessment of the painted and/or finished surfaces was also conducted to determine overall material condition and the potential for risk to occupant and/or worker health.

Confirmatory paint chip samples were collected and forwarded to EMSL Analytical, Inc., in Cinnaminson, New Jersey for analysis via Atomic Absorption Spectrometry (AAS) in accordance with Method SW 846 3050B/7000B. Samples were collected of materials found to contain either inconclusive or highest concentrations of lead via XRF measurement.

LBP (Lead-Based Paint) is defined under the US Department of Housing and Urban Development (HUD) and the Environmental Protection Agency (EPA) as paint or other surface coating with lead content equal to or greater than 1.0 mg/cm² of surface area by XRF or 0.5 percent lead by weight (5,000 parts per million (ppm)) by paint chip analysis.

Multiple XRF measurements and three paint chip samples were collected throughout the facility. Of the XRF measurements collected, several locations measured lead content greater than 1.0 mg/cm2, and therefore -ssed using an XRF instrument. Additionally, paint chip samples were collected for any XRF results found to be inconclusive.

Additionally, a single composite soil sample was collected for each structure with subsamples collected from all sides. Lastly, a total of two bulk samples (paint and window caulk) for polychlorinated biphenyls (PCBs) were collected for laboratory analysis by EPA Method 3540C/8082A, in locations including the Radio Beacon Building, Laundry Building, and four housing facilities identified by the client at the time of the survey.

Jupiter Inlet Outstanding Natural Area Page #5

2.0 SUMMARY OF FINDINGS

The following materials were found via XRF to contain lead concentrations above

1.0 mg/cm2, thus meeting the definition of Lead-Based Paint (LBP).

Materials Documented as LBP Condition of LBP Building H: Brown Interior Wall Paint Intact

Building G: Brown Hallway Walls Intact Building D: Wall Adjacent to Entry Doorway, Hallway Bedroom Wall, and Patio Ledge Poor to Good

Building C: Dining Room Window Frame and Patio Ledge

Poor to Good

Building B: Window Frames Throughout and Patio Ledge

Poor to Good

Cable Building 1: Entire Grey Concrete Exterior Poor Cable Building 2: Entire Grey Concrete Exterior Poor

Radio Beacon: Entire Interior (White and Blue on Concrete)

Poor

3 Bay Garage: Interior Brown and White Walls and Red Floor

Poor

Building 2: Kitchen Wall at Pantry (White Over Plaster)

Intact

Laundry Building: White Exterior Walls, White and Red Interior Walls, and Red Interior Floor

Poor to Intact

NV5 collected paint chip samples from three painted surfaces within the interior of the facilities, wherein XRF testing results were inconclusive. The following is the list of surfaces tested, locations, and results.

Location / Material Color Square Footage

Substrate Condition Lab Results

(ppm) Building H Interior Walls /

Paint White SF Plaster Good 260

Building G Interior Walls / Paint

Brown SF Plaster Good 490

Building G Patio Ledges / Paint

White SF Concrete Poor 300

None of the samples were reported with a lead content greater than 5,000 ppm. The samples documented lead concentrations of 260 to 490 ppm. Although not designated as Lead-Based Paint (LBP) under the EPA definition, workers impacting these materials may be subject to OSHA regulations.

Jupiter Inlet Outstanding Natural Area Page #6

NV5 collected a single composite soil sample for each structure with subsamples collected from all sides. The following is the list of surfaces tested, locations, and results.

Location / Material Lab Results

(ppm) Cable #1 / Soil Composite <40 Cable #2 / Soil Composite 230 Building I / Soil Composite <40 Building H / Soil Composite <40 Building G / Soil Composite <40 Building F / Soil Composite <40 Building E / Soil Composite <40 Building D / Soil Composite <40 Building C / Soil Composite <40 Building B / Soil Composite <40 Building A / Soil Composite 90 Building 1 / Soil Composite 85 Building 2 / Soil Composite <40

Radio Beacon / Soil Composite 360 Laundry Building / Soil Composite 100 3 Bay Garage / Soil Composite 3600

Benches / Soil Composite 91 Lighthouse / Soil Composite 520

NV5 collected a total of two bulk samples (paint and window caulk) to be analyzed for polychlorinated biphenyls (PCBs) within six separate buildings, as defined by the Client in the project scope of work. The following is the list of the parameters tested, locations, and results.

Location / Material Parameter Lab Results

(mg/Kg) Laundry / Paint Aroclor-1016 ND

Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND Lead 1600

Radio Beacon / Caulk Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND

Jupiter Inlet Outstanding Natural Area Page #7

Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND

Radio Beacon / Paint Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 28 Aroclor-1260 3.8 Aroclor-1262 ND Aroclor-1268 ND Lead 8300

Building 1 / Caulk Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND

Building 1 / Paint Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND Lead ND

Building B / Caulk Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND

Building B / Paint Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND

Jupiter Inlet Outstanding Natural Area Page #8

Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND Lead 81

Building E / Caulk Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND

Building E / Paint Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND Lead 99

Building H / Caulk Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND

Building H / Paint Aroclor-1016 ND Aroclor-1221 ND Aroclor-1232 ND Aroclor-1242 ND Aroclor-1248 ND Aroclor-1254 ND Aroclor-1260 ND Aroclor-1262 ND Aroclor-1268 ND Lead 52

Samples collected from painted surfaces on the exterior of the Radio Beacon Building were found to be LBP and contain PCB concentrations. The EPA states that the

Jupiter Inlet Outstanding Natural Area Page #9 is designated by a finding exceeding 50 ppm (mg/kg). These results therefore document that the sampled materials are not regulated under EPA standards as PCB, however;

the material IS designated as LBP.

3.0 CONCLUSIONS, DISCUSSION AND RECOMMENDATIONS

None of the sampled materials were found to contain excessive levels of PCBs.

NV5 has no recommendations regarding PCB in caulk or exterior paints.

Soil sampling documented elevated lead concentrations around the 3-Bay Garage and the Lighthouse, as compared to the HUD standard (24 CFR part 35 and 40 CFR part 745) for bare soil in playground areas (<400 ppm). Notably, a standard also exists in this regulation for bare soil in non-playground areas (<1,200 ppm).

Neither of these sampled areas meets The noted standards are published for HUD housing and areas where children congregate. As the facility does not fall under either category, the standards are not applicable from a regulatory standpoint. Additionally, no State of Florida regulations exist, that would be applicable to lead in soils within the facility. As such, the client has no regulatory requirement for abatement of soils within the facility. Should the client choose to engage in abatement of the soils for reasons other than regulatory requirements, a cost estimate for such abatement is included in section 5.0 below.

A total of 919 XRF measurements were collected throughout the facility. Of the XRF measurements collected, several measurements yielded a lead content greater than 1.0 mg/cm2, as noted in the tables provided in Section 2.0. As previously noted, HUD regulatory standards do not apply to this facility, and there are no applicable State of Florida standards with respect to lead-in-paint at the facility. As such, only the EPA Renovation Repair and Painting (RRP) Rule and OSHA standards for worker exposure would be applicable to the identified lead-based paints and lead-containing paints.

Some of the collected measurements indicated detectable concentrations of lead below involving these materials may fall under OSHA regulations.

NV5 recommends that the materials be handled under safe working protocols, as established and published by applicable governing agencies.

Jupiter Inlet Outstanding Natural Area Page #10

For buildings designated to remain in place: stabilization of peeling and chipping painted surfaces must be performed by a properly trained contractor working under the EPA RRP (Renovation, Repair and Painting Program) rule or an EPA licensed lead-paint abatement contractor. NV5 further recommends that stabilization activities should be monitored under the direction of a Certified Industrial Hygienist (CIH). Although complete abatement of these materials is an available option, NV5 does not recommend such work at this time due to cost and lack of regulatory requirement.

Stabilization of painted surfaces requires the following:

Work must be performed by individuals trained as either EPA lead abatement workers, or EPA RRP trained workers.

Workers must undergo pre- and post- abatement lead blood level monitoring.

Workers must use personal protective equipment (PPE) including, but not limited to: eye protection, P-100 filtered respirators, protective clothing, and gloves.

OSHA personal exposure monitoring for workers is required to lower respiratory protection levels.

HEPA vacuuming for decontamination is adequate but must include washing of hands and faces with soap prior to eating, drinking, smoking or application of cosmetics.

Work practices should be designed by a CIH, and should include such items as debris containment, proper disposal and safe work practices.

No regulations currently in-place would require removal of soils from the areas identified discretion.

For buildings scheduled to be demolished: no physical abatement or removal of leaded paints prior to demolition activities is required, although worker protection rules regarding worker exposure monitoring and/or protection of workers during the demolition process do apply. All demolition work may be performed by any Florida Licensed General Contractor. Work requiring the disturbance of lead-containing materials fall under OSHA protection requirements. These requirements may include:

worker awareness training, safe work practices, worker personal exposure monitoring, personal respiratory protective equipment, and worker blood lead level monitoring. Air sampling during demolition procedures may limit the scope of these requirements.

As none of the facilities are scheduled to be occupied by children or financed by HUD, no Risk Assessment is required.

When conducting construction, renovation or demolition activities which disturb lead in any amount or create a potential for elevated lead exposure to workers, the employer is required to provide worker protection and conduct exposure assessments. Employers

Jupiter Inlet Outstanding Natural Area Page #11 standards for complete requirements prior to construction or demolition activities.

Notification must be given to all other contractors at the work site prior to the start of activities that may create a lead hazard. Characterization and disposal of lead-containing waste materials (LCWMs) must comply with federal, state and local authorities. As such, for any areas where lead paint abatement is conducted, TCLP waste sampling must be performed prior to disposal of generated waste.

For buildings scheduled to be demolished, TCLP sampling would not be necessary in accordance with Florida and EPA standards for all buildings with the exception of Cable Building #2. This building contained high lead levels on all exterior surfaces, representing a significant portion of the overall building. As such, Cable Building #2 presents a potential risk for hazardous waste content and should be sampled accordingly prior to disposal.

Contractors must maintain current licenses as required by applicable state or local jurisdictions for the removal, transport, disposal of LCWMs, or other regulated lead-based paint activities.

Damaged paint or deteriorated paint containing any lead should undergo corrective action to stabilize the paint, if and wherever found, for buildings not subject to demolition. This work should be conducted by an EPA Licensed Abatement Contractor, or RRP certified contractor utilizing lead-safe work practices. Paint stabilization usually involves removing loose and flaking paint, and repainting with a layer of protective non- LBP. If any construction or renovation work is conducted on the subject property, contractors and tenants should be notified about the presence, and location of identified lead-based paint.

Work activities impacting materials containing lead concentrations may pose a potential exposure risk for workers and/or building occupants. Workers trained in proper safety and respiratory protective techniques should perform renovation activities that may impact any lead-containing materials. Under the EPA Lead Renovation, Repair, and Painting Rule, contractors performing renovation, repair and painting projects that disturb lead-based paint in homes, child care facilities, and schools built before 1978 must be certified and must follow specific work practices to prevent lead contamination.

Applicable HUD regulations also require this practice.

The potential exists for additional suspect lead-containing materials to be exposed during demolition and/or renovation activities. Such materials should be sampled and analyzed for lead content prior to any renovation and/or demolition activities that could impact these materials.

Jupiter Inlet Outstanding Natural Area Page #12

4.0 SAMPLING METHODOLOGY & XRF PROTOCOL

The scope of work employed in the XRF testing of these areas was performed in accordance with HUD protocols listed in the Guidelines for the Evaluation and Control of Lead-based Paint Hazards in Housing, published June 1995, Chapter 7, revised 1997;

and 40 CFR Part 745 Lead-Based Paint Poisoning Prevention in Certain Residential Structures. Combined with the Paint Chip sampling, the scope of work was generated to comply and exceed applicable standards presented by both OSHA and the EPA RRP Rule.

During the course of the property visit, the NV5 representative performed a review of accessible areas of the subject buildings for the presence of suspect LBP.

As part of the survey, NV5 inspected surfaces throughout each sampled area to determine which surfaces were coated with paint. Painted surfaces were sampled via XRF to determine lead-based paint presence. Additionally, confirmatory paint chip samples were collected and forwarded to EMSL Analytical, Inc., in Indianapolis, Indiana for analysis via Atomic Absorption Spectrometry (AAS) in accordance with Method SW 846 3050B/7000B. Samples were collected of materials found to contain either inconclusive or highest concentrations of lead via XRF measurement.

In order to collect a measurement, the XRF aperture is held flush (as possible) against the sampled surface and held in place until the meter provides notification of a completed measurement. This task generally takes from seven to thirty seconds. The XRF uses an X-

-ray fluorescence radiation energy. The radiation detector within the XRF then translates these x-rays into a quantitative measure of lead concentration. If present, the XRF will determine the amount of lead in paint with a 95% confidence level. The lead concentrations are reported in milligrams per square centimeter (mg/cm2).

With respect to the protocol employed by NV5 on this LBP inspection, measurements were collected within building units on representative accessible painted building surfaces.

XRF analysis yields the total lead content of a painted surface, thereby not distinguishing between individual concentrations of painted layers. The XRF was calibrated with a National Institute of Standards and Testing (NIST) calibration surface prior to and post analysis of painted surfaces. Additional calibration measurements were collected periodically, at the discretion of the surveyor.

Section 1017 of the HUD Guidelines, Residential LBP Reduction Act of 1992, otherwise

Jupiter Inlet Outstanding Natural Area Page #13 exposure to lead that would result -contaminated dust, bare, lead-contaminated soil, and/or lead-contaminated paint that is deteriorated or present on accessible, friction, or impact surfaces. Therefore, under Title X, intact LBP on most although the paint should be maintained and its condition monitored to ensure that it does not deteriorate and become a hazard.

template, in accordance with HUD and RRP standard methodologies. Collected paint chip samples were forwarded to an AIHA ELLAP accredited laboratory for analysis via Flame Atomic Absorption Spectrometry, under method SW 846 3050B/7000B.

Jupiter Inlet Outstanding Natural Area Page #14

5.0 ESTIMATED ABATEMENT COSTS

Per the project scope of services, as outlined by the Owner, the below includes estimated costs to remove LBP and lead-contaminated soils in buildings that are expected to remain and be renovated. Abatement estimates are not included for buildings expected to be demolished. Per correspondence from the client, only the structures noted below are to be renovated, and therefore, only in these facilities will identified LBP will be abated.

The following are cost estimates for abatement by a Florida Licensed Lead Abatement Contractor, with specification development and air and project monitoring performed under the direction of a Certified Industrial Hygienist (CIH). It should be noted that costs for abatement and monitoring can vary widely; depending upon time of year, local conditions, recent weather patterns, insurance requirements and abatement crew size. As such, the following is an estimate only and should not be taken as a bid or an offer to perform the services. The below estimates assume that all areas are awarded and can be abated concurrently. Estimates also assume that results of the required TCLP testing (cost included) does not require materials to be disposed as hazardous materials. Estimates assume that the work would include stabilization of LBP in non-residential buildings, as opposed to complete abatement (not required).

Stabilization specification development and contractor bid assistance (pre-bid meeting, pre-qualification of contractors, recommendation for bid award, etc.) - $1,800.00

Building C: Dining Room Window Frame ($500.00) and Patio Ledge ($5,500.00)

Building B: Window Frames Throughout ($3,500.00) and Patio Ledge ($5,500.00)

3 Bay Garage: Interior Brown and White Walls and Red Floor ($25,000.00)

*3-Bay Garage Surrounding Soil ($6,000.00)

Radio Beacon Building (Throughout Interior) ($25,000.00)

Laundry Building: Interior and exterior walls and floors ($18,000.00)

Cable Building 1 (Exterior) ($7,500.00)

*Lighthouse Surrounding Soil ($9,600.00)

Total Remediation Cost Estimate - $ 107,900.00

* Optional - Not required by applicable regulations

Jupiter Inlet Outstanding Natural Area (JIONA) Jupiter, Florida Photo Log 10/17-19/2016

1- View of Jupiter Inlet Lighthouse Outstanding

Natural Area (JIONA).

2- General overview of the JIONA Property.

3- General overview of the JIONA Property.

4- View of a typical housing unit on the property.

5- Lead based paint identified in the green layer on patios

6- Identified lead-based paint green pain on patio door frame.

Jupiter Inlet Outstanding Natural Area (JIONA) Jupiter, Florida Photo Log 10/17-19/2016

7- Confirmed LBP Beacon Building Interior

8- General View of Laundry Building Interior and exterior paint all identified LBP

9- Laundry Building Exterior Paint

Phillip Worby, Chemistry Laboratory Manager

Approved By:

Fax: (813) 571-9374 Phone: (813) 571-9788

The following analytical report covers the analysis performed on samples submitted to EMSL Analytical, Inc. on 10/20/2016. The results are tabulated on the attached data pages for the following client designated project:

JIONA

The reference number for these samples is EMSL Order #011607032. Please use this reference when calling about these samples. If you have any questions, please do not hesitate to contact me at (856) 303-2500.

11/4/2016Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

The test results contained within this report meet the requirements of NELAP and/or the specific certification program that is applicable, unless otherwise noted.

NELAP Certifications: NJ 03036, NY 10872, PA 68-00367

The samples associated with this report were received in good condition unless otherwise noted. This report relates only to those items tested as received by the laboratory. The QC data associated with the sample results meet the recovery and precision requirements established by the NELAP, unless specifically indicated. All results for soil samples are reported on a dry weight basis, unless otherwise noted. This report may not be reproduced except in full and without written approval by EMSL Analytical, Inc.

EMSL Analytical, Inc.

200 Route 130 North, Cinnaminson, NJ 08077

Phone: (856) 303-2500 Fax: (856) 858-4571 Email: EnvChemistry2@emsl.com

EMSL Analytical does not hold PCB SHW certification in the state of Florida.

The reporting limits for the PCB analysis for sample -0001, -0007, -0009 & -0010 are elevated due to matrix interference from chlordane.

EMSL Analytical, Inc.

200 Route 130 North, Cinnaminson, NJ 08077

Phone/Fax: (856) 303-2500 / (856) 858-4571 http://www.EMSL.com EnvChemistry2@emsl.com

011607032

CustomerID: AIRQ22

CustomerPO: 16-20155

ProjectID:

EMSL Order:

Analytical Results

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 9:30 AM

JIONA

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

Client Sample Description Lab ID:1 0001

Laundry

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/3/20164.9 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/3/20164.9 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/3/20164.9 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3050B/6010C Lead BE1600 mg/Kg 10/29/201612 10/25/2016 LY

Client Sample Description Lab ID:2 0002

Radio Beacon

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

Client Sample Description Lab ID:3 0003

Radio Beacon

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1254 EH28 mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1260 EH3.8 mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

Page 2 of 6ChemSmplw/RDL/NELAC-7.21.0 Printed: 11/4/2016 11:50:01 AM

Phone/Fax: (856) 303-2500 / (856) 858-4571 http://www.EMSL.com EnvChemistry2@emsl.com

011607032

CustomerID: AIRQ22

CustomerPO: 16-20155

ProjectID:

EMSL Order:

Analytical Results

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 9:30 AM

JIONA

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

Client Sample Description Lab ID:3 0003

Radio Beacon

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3050B/6010C Lead BE8300 mg/Kg 10/29/201661 10/25/2016 LY

Client Sample Description Lab ID:4 0004

Bldg 1

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

Client Sample Description Lab ID:5 0005

Bldg 1

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3050B/6010C Lead BEND mg/Kg 10/29/20162.5 10/25/2016 LY

Client Sample Description Lab ID:6 0006

Bldg B

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

Page 3 of 6ChemSmplw/RDL/NELAC-7.21.0 Printed: 11/4/2016 11:50:01 AM

Phone/Fax: (856) 303-2500 / (856) 858-4571 http://www.EMSL.com EnvChemistry2@emsl.com

011607032

CustomerID: AIRQ22

CustomerPO: 16-20155

ProjectID:

EMSL Order:

Analytical Results

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 9:30 AM

JIONA

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

Client Sample Description Lab ID:6 0006

Bldg B

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

Client Sample Description Lab ID:7 0007

Bldg B

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/3/20164.9 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/3/20164.9 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/3/20164.9 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3050B/6010C Lead BE81 mg/Kg 10/29/20162.4 10/25/2016 LY

Client Sample Description Lab ID:8 0008

Bldg E

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.98 11/1/2016 AB

Page 4 of 6ChemSmplw/RDL/NELAC-7.21.0 Printed: 11/4/2016 11:50:01 AM

Phone/Fax: (856) 303-2500 / (856) 858-4571 http://www.EMSL.com EnvChemistry2@emsl.com

011607032

CustomerID: AIRQ22

CustomerPO: 16-20155

ProjectID:

EMSL Order:

Analytical Results

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 9:30 AM

JIONA

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

Client Sample Description Lab ID:9 0009

Bldg E

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/3/20164.8 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/3/20164.8 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/3/20164.8 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/3/20164.8 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.96 11/1/2016 AB

3050B/6010C Lead BE99 mg/Kg 10/29/20162.4 10/25/2016 LY

Client Sample Description Lab ID:10 0010

Bldg H

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.95 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.95 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.95 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.95 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/3/201624 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/3/201624 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/3/201624 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/3/201624 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.95 11/1/2016 AB

Client Sample Description Lab ID:11 0011

Bldg H

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3540C/8082A Aroclor-1016 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1221 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1232 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1242 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1248 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1254 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1260 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1262 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

3540C/8082A Aroclor-1268 EHND mg/Kg 11/2/20160.93 11/1/2016 AB

Page 5 of 6ChemSmplw/RDL/NELAC-7.21.0 Printed: 11/4/2016 11:50:01 AM

Phone/Fax: (856) 303-2500 / (856) 858-4571 http://www.EMSL.com EnvChemistry2@emsl.com

011607032

CustomerID: AIRQ22

CustomerPO: 16-20155

ProjectID:

EMSL Order:

Analytical Results

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 9:30 AM

JIONA

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

Client Sample Description Lab ID:11 0011

Bldg H

Collected: 10/18/2016

Method Parameter Result Units Analysis Date AnalystRL

Prep Date Analyst

3050B/6010C Lead BE52 mg/Kg 10/29/20162.4 10/25/2016 LY

ND - indicates that the analyte was not detected at the reporting limit RL - Reporting Limit (Analytical)

Definitions:

Page 6 of 6ChemSmplw/RDL/NELAC-7.21.0 Printed: 11/4/2016 11:50:01 AM

Client Sample Description ConcentrationLab ID Analyzed Lead

Collected

EMSL Analytical, Inc.

200 Route 130 North, Cinnaminson, NJ 08077

Phone/Fax: (856) 303-2500 / (856) 786-5974 http://www.EMSL.com cinnaminsonleadlab@emsl.com

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 12:00 PM

16-20155 / JIONA / Jupiter ,Florida

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

10/18/2016Collected:

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

201611441

CustomerID: AIRQ22

CustomerPO:

ProjectID:

EMSL Order:

Site: Bldg H - Interior walls / White

201611441-001919 260 ppm10/21/201610/18/2016

Site: Bldg G - Interior walls / Brown

201611441-002020 490 ppm10/21/201610/18/2016

Site: Bldg G - Patio Ledges / White

201611441-002121 300 ppm10/21/201610/18/2016

Phillip Worby, Lead Laboratory Manager or other approved signatory

Test Report ChmSnglePrm/nQC-7.32.3 Printed: 10/24/2016 1:00:06 PM

*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. Cinnaminson, NJ NELAP Certifications: NJ 03036, NY 10872, PA 68-00367, AIHA-LAP, LLC ELLAP 100194, A2LA 2845.01

Initial report from 10/24/2016 13:00:06

Collected

EMSL Analytical, Inc.

200 Route 130 North, Cinnaminson, NJ 08077

Phone/Fax: (856) 303-2500 / (856) 786-5974 http://www.EMSL.com cinnaminsonleadlab@emsl.com

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 12:00 PM

16-20155 / JIONA / Jupiter ,Florida

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

10/18/2016Collected:

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

201611441

CustomerID: AIRQ22

CustomerPO:

ProjectID:

EMSL Order:

Site: Soil Composite Cable #1

201611441-00011 <40 ppm10/22/201610/18/2016

Site: Soil Composite Cable #2

201611441-00022 230 ppm10/22/201610/18/2016

Site: Soil Composite Bldg I

201611441-00033 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg H

201611441-00044 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg G

201611441-00055 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg F

201611441-00066 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg E

201611441-00077 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg D

201611441-00088 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg C

201611441-00099 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg B

201611441-001010 <40 ppm10/22/201610/18/2016

Site: Soil Composite Bldg A

201611441-001111 90 ppm10/22/201610/18/2016

Site: Soil Composite Bldg 1

201611441-001212 85 ppm10/22/201610/18/2016

Site: Soil Composite Bldg 2

201611441-001313 <40 ppm10/22/201610/18/2016

Site: Soil Composite Radio Beacon

201611441-001414 360 ppm10/22/201610/18/2016

Site: Soil Composite Laundry Bldg

201611441-001515 100 ppm10/22/201610/18/2016

Phillip Worby, Lead Laboratory Manager or other approved signatory

Test Report ChmSnglePrm/nQC-7.32.3 Printed: 10/24/2016 1:00:06 PM

*Analysis following Lead in Soil/Solids by EMSL SOP/Determination of Environmental Lead by FLAA. Reporting limit is 40 mg/kg 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. Results reported based on dry weight. "<" (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. Cinnaminson, NJ NELAP Certifications: NJ 03036, NY 10872, PA 68-00367, AIHA-LAP, LLC ELLAP 100194, A2LA 2845.01

Collected

EMSL Analytical, Inc.

200 Route 130 North, Cinnaminson, NJ 08077

Phone/Fax: (856) 303-2500 / (856) 786-5974 http://www.EMSL.com cinnaminsonleadlab@emsl.com

Attn: Steve Lipson NV5, Inc.

1713 South Kings Avenue Brandon, FL 33511

Received: 10/20/16 12:00 PM

16-20155 / JIONA / Jupiter ,Florida

Fax: (813) 571-9374

Phone: (813) 571-9788

Project:

10/18/2016Collected:

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

201611441

CustomerID: AIRQ22

CustomerPO:

ProjectID:

EMSL Order:

Site: Soil Composite 3 Bay Garage

201611441-001616 3600 ppm10/22/201610/18/2016

Site: Soil Composite Benches

201611441-001717 91 ppm10/22/201610/18/2016

Site: Soil Composite Lighthouse

201611441-001818 520 ppm10/22/201610/18/2016

Phillip Worby, Lead Laboratory Manager or other approved signatory

Test Report ChmSnglePrm/nQC-7.32.3 Printed: 10/24/2016 1:00:06 PM

*Analysis following Lead in Soil/Solids by EMSL SOP/Determination of Environmental Lead by FLAA. Reporting limit is 40 mg/kg 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. Results reported based on dry weight. "<" (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. Cinnaminson, NJ NELAP Certifications: NJ 03036, NY 10872, PA 68-00367, AIHA-LAP, LLC ELLAP 100194, A2LA 2845.01

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