GENERATOR FUEL RELEASES MONITORING REPORT YEAR 1, …

GENERATOR FUEL RELEASES MONITORING REPORT

YEAR 1, QUARTER 4 FOR TUPPERWARE IT BUILDING

TUPPERWARE BRANDS CORPORATION 14901 SOUTH ORANGE BLOSSOM TRAIL

ORLANDO, FLORIDA

FDEP Facility I. D. No. 48‐8521966

JANUARY 2019

Prepared for:

Tupperware Brands Corporation 14901 South Orange Blossom Trail Orlando, Orange County, FL 32837

Prepared by:

HSW Engineering, Inc. 605 E. Robinson St., Suite 308

Orlando, Florida 32801 (407) 872‐6893

HSW Project No: 6CN800101

(407) 872‐6893 ■ 605 E. Robinson St.., Suite 308 ■ Orland, FL 32801 ■ www.hsweng.com Engineering and Scientific solutions within your reach…

P:\6CN800101 Tupperware\08 Reports ‐ Submittals ‐ Permits\Quarterly Report Y1Q4\Tupperware Y1Q4 Status Report_2019 01 15.docx

January 15, 2019 Orange County Environmental Protection Department (OCEPD) Attn: Mr. Kevin Thornton Senior Environmental Specialist 3165 McCrory Place, Suite 200 Orlando, Florida 32803 Re: Generator Fuel Releases Year 1, Quarter 4 Monitoring Report for Tupperware IT Building

Tupperware Brands Corporation 14901 South Orange Blossom Trail Orlando, Florida 32837 FDEP FAC ID No: 48‐8521966

HSW Project No: 6CN800101 Dear Mr. Thornton: HSW Engineering, Inc. (HSW) appreciates the opportunity to submit this Report to OCEPD on behalf of Tupperware Brands Corporation (Tupperware) after performing a fourth quarter of diesel fuel recovery via product, contact water, and absorbents removal and sub‐slab soil vapor ventilation, along with vapor and groundwater sampling activities at the referenced facility. If you have any questions, please do not hesitate to contact us. Sincerely, HSW Engineering, Inc. Jason P. Cicchetti Andrew M. Lawn, M.S., P.G. Project Engineer Principal Hydrogeologist ACE/JPC/AML Attachments cc: Kimberly Bauman at [email protected], Tupperware Brands Corporation

Tupperware Brands Corporation Year 1, Annual Status Report

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CONTENTS

STATEMENT OF PROFESSIONAL REVIEW .............................................................. I

1. PROJECT BACKGROUND ................................................................................. 1

2. FIELD ACTIVITIES ............................................................................................ 5

2.1 Waste Disposal ................................................................................................................ 5

2.2 Absorbent Socks .............................................................................................................. 5

2.3 Free Product Gauging ...................................................................................................... 5

2.4 Sub‐Slab Soil Vapor Exhaust System Air Monitoring....................................................... 5

2.5 Groundwater Sampling ................................................................................................... 5

3. FINDINGS ....................................................................................................... 6

3.1 Absorbent Socks .............................................................................................................. 6

3.2 Free Product Gauging ...................................................................................................... 6

3.3 Sub‐Slab Soil Vapor Monitoring Laboratory Analytical Results ...................................... 6

3.4 Groundwater Flow Direction ........................................................................................... 6

3.5 Groundwater Laboratory Analytical Results ................................................................... 6

4. CONCLUSIONS AND RECOMMENDATIONS ..................................................... 7

TABLES

1. Absorbent Sock Product Thickness Summary

2. Free Product Measurement Summary

3. Air Sample Analytical Summary

4. Groundwater Elevation Summary

5A. Groundwater Monitoring Well Analytical Summary – VOAs, EDB, and Lead

5B. Groundwater Monitoring Well Analytical Summary – PAHs and TRPH


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FIGURES

1. Aerial Map

2. Site Map

3. Groundwater Contour Map, December 2018

4. Groundwater Quality (August and December 2018)

APPENDICES

A. OCEPD Approval Letter dated November 15, 2018 and Drum Manifest

B. Field Notes for Absorbent Sock and Free Product Gauging Events

C. Groundwater Sampling Logs with Equipment Calibration Logs

D. Air Laboratory Analytical Report

E. Groundwater Laboratory Analytical Report


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1. PROJECT BACKGROUND

The site assessment area, hereto referred as the “Site,” is located on the eastern side of the south wall of the IT Building associated with Tupperware located at 3175 N Orange Blossom Trail, Kissimmee, Osceola County, Florida. The Site is located along the southern boundary of the overall Tupperware campus and is bounded directly to the north by the IT building, to the south by a wooded area, and to the west and east by ponds. An aerial map indicating the approximate Site location is provided as Figure 1. A Site Map illustrating the location of buildings, ponds, monitoring wells, and other Site features is provided as Figure 2. According to a Florida Department of Environmental Protection (FDEP) Storage Tank Facility Discharge Site Inspection Report dated February 13, 2017, on February 10, 2017, approximately 750 gallons of diesel fuel spilled outside the IT generator room and impacted groundwater due to a failure of the generator day tank fill level device. Immediately following the release, on February 10, 2017, SWS Environmental Services (SWS) was contracted through Triumvirate Environmental, Inc. (TEI) to mobilize to the Site and perform emergency response (ER) activities. These activities were summarized in an Incident Report dated April 21, 2017 prepared by SWS and submitted to TEI. Based on this report, from February 10 through 15, 2017, SWS removed approximately 36.96 tons of diesel‐impacted soil and approximately 155 gallons of diesel‐impacted water, including approximately 100 gallons of free‐floating diesel fuel. In addition, SWS collected three confirmatory side wall samples (CS‐1 through CS‐3) for laboratory analysis from the east, west, and south walls of the excavation prior to backfilling. Results of the confirmation soil samples indicated that no contaminants of concern were found to exceed Soil Cleanup Target Levels (SCTLs) for residential, commercial, or leachability standards, per Chapter 62‐777 F.A.C., Table II. On March 28, 2017, SWS transported this waste to Clark Environmental, Incorporated (Clark) for thermal treatment. On February 17, 2017, HSW conducted a site visit and observed that a portion of the soil source removal excavation along the building remained open to allow on‐going recovery of diesel fuel free product (which apparently spread beneath the building) that accumulated on the exposed groundwater surface. Free product floating on groundwater at a depth of approximately 3 to 4 feet below ground surface was observed at two areas where groundwater had been exposed near the wall of the building. Utility lines, including fiber optics, were also observed in the open excavation area. HSW submitted a Site Assessment Report (SAR) dated October 9, 2017 to OCEPD detailing source removal and site assessment activities performed at the Site from April 12 through June 5, 2017. Activities included installation and operation of a dual phase extraction (DPE) system that recovered 3,126 gallons of free product and petroleum contact water (PCW), monitoring well installation, installation of a solar‐powered sub‐slab vapor extraction system (SSVES) that recovered an estimated mass of 12.68 lbs. of total petroleum hydrocarbons (TPH), soil vapor sampling, free product gauging, and groundwater sampling. Based on results of the assessment activities, HSW recommended the following:

Continued operation of the SSVES monthly for one quarter, then quarterly, with extracted vapor sampling for laboratory analysis using EPA Method 18 until two consecutive, non‐detect results are obtained;

Free product gauging coupled with installation and removal/disposal of absorbent socks in MPE wells exhibiting presence of residual product, if any, monthly for six months and quarterly




thereafter, thru seasonal changes of one year, or until product is no longer apparent, or a different remedy is devised, if necessary; and

Quarterly groundwater monitoring for a minimum of one year to prove residual contaminants are not migrating and are expected to naturally attenuate, followed by determination of closure with controls, or continued long‐term monitoring, or no further action.

This report was approved by OCEPD in a letter dated November 3, 2017. HSW submitted a Y1Q1 Status Report dated June 13, 2018 detailing Site activities performed from January 24 through March 28, 2018. Activities included free product gauging coupled with installation and removal/disposal of absorbent socks in MPE wells, SSVES sampling, and groundwater sampling. Based on the Y1Q1 results, the following conclusions were made:

FP more than 0.01‐ft. was not observed in MPE wells throughout this quarter;

Approximately 0.81 gallons of FP was absorbed by the PIGs;

The SSVES effectively captured accumulated vapors beneath the IT building and removed about 8.5 pounds of TPH;

Residual diesel fuel remained beneath the IT building; and

Contaminant concentrations in samples collected from monitoring wells DW‐1 and MW‐1 through MW‐4 were below their respective GCTLs for each analyte sampled.

Based on these conclusions, HSW recommended the following:

Continued operation of the SSVES with quarterly air sampling for laboratory analysis using EPA Method 18 until two consecutive, non‐detect results are obtained;

Continued free product gauging coupled with installation and removal/disposal of absorbent socks in MPE wells monthly for the next quarter; and

Continued quarterly groundwater monitoring as required by Florida Administrative Code (FAC) Rule 62‐780.680(3)(c)2.

This report was approved by OCEPD in a letter dated July 18, 2018. HSW submitted the Y1Q2 Status Report, dated August 3, 2018 detailing Site activities performed from April 2018 through June 2018. Activities included free product gauging coupled with installation and removal/disposal of absorbent socks (PIGs) in MPE wells, SSVES sampling, and groundwater sampling. Based on the results of the Y1Q2 field activities, HSW concluded the following:

FP more than 0.01‐ft. was not observed any MPE wells throughout the quarter;

Approximately 1.02 gallons of FP was absorbed by the PIGs;

The SSVES is effectively capturing accumulated vapors from residual diesel fuel beneath the IT building; and

Contaminant concentrations detected in samples from monitoring wells DW‐1 and MW‐1 through MW‐4 were below their respective GCTLs for each analyte sampled.





Continued operation of the SVSES with quarterly air sampling from the effluent sample port for laboratory analysis using EPA Method 18 until two consecutive, non‐detect results are obtained;

Continued free product gauging coupled with installation and removal/disposal of PIGs in MPE wells quarterly for the next two quarters; and

Continued quarterly groundwater monitoring as required by FAC Rule 62‐780.680(3)(c)2 for a minimum of one year to prove residual contaminants are not migrating and are expected to naturally attenuate, followed by determination of closure with controls, or continued long‐term monitoring, or no further action.

This report was approved by OCEPD in a letter dated August 17, 2018. On August 14, 2018, Tupperware submitted a Discharge Report Form (DRF) to the FDEP detailing the release of approximately 300 gallons of diesel fuel due to a mechanical failure of the backup generator’s day tank float system. Following the release, Petrotech Southeast, Inc. (Petrotech) and HSW were contacted to perform ER services, as detailed below. Email correspondence between Tupperware and OCEPD dated August 17, 2018, indicated the release occurred inside the generator room in which approximately two inches of diesel product was visible on the floor and appeared to have migrated between the wall and floor to the subsurface beneath the building. Leakage from the door of the room appeared to be undetectable. Included in the Y1Q2 Status Report review letter from OCEPD dated August 17, 2018, OCEPD indicated they were aware of the second release and recommended that quarterly groundwater monitoring be discontinued, and source removal efforts be implanted in accordance with Rule 62‐780.500, F.A.C. HSW submitted a Source Removal Report Form with attachments dated October 16, 2018 to OCEPD providing volumes of soil and liquid removed including field notes, manifests and weigh tickets, summary tables, and laboratory analytical results. Approval or correspondence from OCEPD regarding this submittal has not been received. HSW submitted a Y1Q3 Status Report, dated November 1, 2018 detailing Site activities performed from July 2018 through September 2018. Activities included free product gauging coupled with installation and removal/disposal of absorbent socks in MPE wells, SSVES sampling, groundwater sampling, and ER/source removal activities. HSW estimated that of the 750 gallons of diesel from the February 2017 spill, 27 to 195 gallons remained in the subsurface, and, of the 300 gallons of diesel from the August 2018 spill, 67 to 164 gallons remains in the subsurface. Based on the results of the Y1Q3 field activities, HSW concluded the following:

An estimated total of 94 to 359 gallons of diesel fuel remained in the subsurface following the February 2017 and August 2018 releases.






Continued operation of the SVSES with quarterly air sampling from the effluent sample port for laboratory analysis using EPA Method 18 until two consecutive, non‐detect results are obtained;

Continued free product gauging coupled with installation and removal/disposal of absorbent socks in MPE wells monthly until no free product as defined in Chapter 62‐780.680(3)(c)2; and

Continued quarterly groundwater monitoring; and

Perform Site Assessment to determine the extent of diesel impacted soil and groundwater in the immediate vicinity of the generator room, including inside the generator room and rooms to the north and west.

This report was approved by OCEPD in a letter dated November 15, 2018 with a request for updated information in a report due January 15, 2019 (Appendix A).




2. FIELD ACTIVITIES

2.1 Waste Disposal

On December 10, 2018, Petrotech Southeast removed two drums of soil from the August 2018 release and one drum of absorbent socks from the site. A new 55‐gallon drum was delivered to the site for future adsorbent socks. A copy of the drum manifest is provided in Appendix A.

2.2 Absorbent Socks

HSW continued maintenance of 1.5‐inch diameter x 18‐inch long monitoring well skimmer socks in each of the thirteen MPE wells. The socks are made of polypropylene and designed to act as skimmers that float on top of the oil/water interface and absorb only oils and oil‐based liquids. On November 21, December 13, 2018, and January 3, 2019, HSW mobilized to the Site to remove the socks from MPE‐1 through MPE‐13 and measure staining. Each sock was disposed in a DOT‐approved drum staged on Site for disposal off‐Site at a later date. During the groundwater sampling event on December 6, 2018, HSW also measured and replaced the socks in wells MPE‐9 and ‐12 due to the large amount of product during the free product gauging event on November 28, 2018. Field notes for each activity are provided in Appendix B.

2.3 Free Product Gauging

Free product thickness measurements were made approximately one week following sock removal to allow product to equilibrate in MPE wells. On November 28, December 20, 2018, and January 10, 2019, HSW mobilized to the Site and made product thickness measurements from wells MPE‐1 through ‐13 using an oil/water interface probe. Field notes are provided in Appendix B.

2.4 Sub-Slab Soil Vapor Exhaust System Air Monitoring

On December 6, 2018, HSW collected an air sample, Exhaust Fan‐Month 12, from the solar‐powered SSVES. The sample was collected by extracting air at a rate of approximately 200 ml/min from a sample port installed on the effluent PVC pipe using a peristaltic pump in two 1‐liter Tedlar® bags and delivered to TestAmerica for analysis of volatile organic compounds (VOCs) using EPA Method TO‐18. Field notes are provided in Appendix B.

2.5 Groundwater Sampling

On December 6, 2018 HSW mobilized to the Site and collected groundwater samples from monitoring wells MW‐1 through MW‐4 and DW‐1. Prior to collecting groundwater samples, HSW collected static depth to water measurements from the wells. Each monitoring well was purged with a peristaltic pump in accordance with the Florida Department of Environmental Protection (FDEP) Standard Operating Procedures for Field Activities, DEP‐SOP‐001/01, FS‐2200, and Groundwater Sampling Variances and Clarifications for Bureau of Petroleum Storage Systems Sites, PCS‐005. Following purging, each groundwater sample was placed in laboratory supplied containers, stored on wetted ice and transported to TestAmerica under proper chain‐of‐custody documentation for analysis of benzene, toluene, ethylbenzene, xylenes and methyl‐tert‐butyl ether (BTEX/MTBE) using EPA Method 8260, PAHs by EPA Method 8270D_SIM, and TRPH by the FL‐PRO Method. Purge water generated during sampling was spread on an impervious surface for volatilization. Groundwater sampling and equipment calibration logs are provided in Appendix C.




3. FINDINGS

3.1 Absorbent Socks

According to the manufacturer, each sock can absorb approximately 17 ounces (oz.) or .13 gallons of oil equating to approximately 0.007 gallons per inch (gal/in). Based on this, a total of approximately 1.73 gallons of free product was absorbed from the MPE wells during the fourth quarter. The sock staining measurements and approximate adsorbed volumes are tabulated on Table 1.

3.2 Free Product Gauging

Based on these measurements, product as defined in Chapter 62‐780.200(20) F.A.C as non‐aqueous phase liquid in excess of 0.01‐foot thickness, was most‐recently found in wells MPE‐3, ‐9, ‐10, and ‐12. Following product measurements, new socks were installed in each MPE well. Product measurements are tabulated on Table 2.

3.3 Sub-Slab Soil Vapor Monitoring Laboratory Analytical Results

Results of the December 2018 air sampling event indicated that detectable levels of petroleum hydrocarbons still exist within the vadose zone beneath the IT building. Based on these results and using an 8‐hour operational period in which the solar panels were exposed to the sun, results of the air samples indicated approximately 40 lbs. of total petroleum hydrocarbons (TPH) were extracted during the third and fourth quarter of operation. Results of the air samples are summarized on Table 3 and the laboratory analytical reports are provided in Appendix D.

3.4 Groundwater Flow Direction

Based on groundwater elevations measured on December 6, 2018, the groundwater flow direction was toward the west from the eastern pond, and toward the northwest from the wooded area, suggesting low expected mobility of impacted groundwater (Figure 3). DTW and water table elevation summaries are provided in Table 4.

3.5 Groundwater Laboratory Analytical Results

Results of the December 6, 2018 groundwater sampling event indicate that constituents in each monitoring well sample were below their respective groundwater cleanup target levels (GCTLs) cited in Chapter 62‐777 F.A.C., Table I. Groundwater analytical results are summarized in Tables 5A and 5B and illustrated on Figure 4. A copy of the laboratory analytical report is provided in Appendix E.




4. CONCLUSIONS AND RECOMMENDATIONS

Based on the findings above, the following conclusions can be made:

FP more than 0.01‐ft. was most‐recently observed in wells MPE‐3, ‐9, ‐10, and ‐12;

Approximately 1.73 gallons of FP was absorbed by well socks;

The SSVES is capturing accumulated vapors from residual diesel fuel beneath the IT building; and


Based on these conclusions, HSW recommends the following:

Continued operation of the SSVES with quarterly air sampling from the effluent sample port for laboratory analysis using EPA Method 18 until two consecutive, non‐detect results are obtained;

Continued free product gauging coupled with installation and removal/disposal of absorbent socks in MPE wells monthly until free product as defined in FAC Rule 62‐780.200(20) is not detected; and

Continued groundwater monitoring, on a semi‐annual frequency; and

Delineation of diesel impacted soil and groundwater beneath the generator room and rooms to the north and west to facilitate determination of whether additional remedial actions are warranted to achieve administrative closure.






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TABLES

Florida Department of Environmental Protection -- Bureau of Petroleum Storage Systems -- Preapproval Program

Facility Name: Tupperware Brands CorporationFacility Address: 14901 S. Orange Blossom Trail, Orlando, FloridaFacility ID#: 49/8521966

Well No.Diameter (inches) 2.00 2.00 2.00 2.00

Well Depth 5.87 5.37 5.06 4.83

Screen Interval 5 5 5 4.83

DATE Thickness (Inches)

Thickness (Inches)

Thickness (Inches)

Thickness (Inches)

06/13/2017 7.00 2.00 9.00 17.00

06/30/2017 7.00 4.00 4.00 8.00

12/14/2017 7.00 7.50 13.50 16.50

01/24/2018 6.50 7.00 7.00 7.00

2/19/2018 5.75 6.00 6.00 6.00

03/21/2018 2.00 3.00 1.00 -

4/20/2018 7.00 6.75 6.50 8.25

05/23/2018 6.75 7.25 7.50 4.50

06/20/2018 7.00 6.75 7.25 8.50

08/30/2018 4.00 4.50 4.00 10.00

09/21/2018 5.00 5.50 5.25 5.75

11/21/2018 5.00 5.50 3.50 4.00

12/13/2018 5.50 9.00 5.50 10.50

01/03/2019 6.50 0.00 7.00 5.500.05 0.05 0.04

0.05 0.05 0.05 0.06

0.03

0.04

0.03 0.03 0.07

0.030.02

0.04 0.04 0.04 0.04

0.04

0.05 0.05 0.05 0.03

0.04 0.04 0.04 0.04

0.01 0.02 0.01 -

0.12

0.05 0.03 0.03 0.06

0.05 0.05 0.05 0.06

0.05 0.05 0.09 0.12

0.05 0.05 0.05 0.05

0.05 0.01 0.06

TABLE 1: ABSORBENT SOCK PRODUCT THICKNESS SUMMARY

MPE-1 MPE-2 MPE-3 MPE-4

Volume (gallons) Volume (gallons) Volume (gallons) Volume (gallons)

0.00

0.06 0.070.040.04

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Well No.Diameter (inches)Well DepthScreen Interval


Thickness (Inches)

Thickness (Inches)

06/13/2017 1.00 0.50 7.00

06/30/2017 0.00 0.00 3.00

12/14/2017 12.50 8.50 13.00

01/24/2018 6.25 6.50 6.50

2/19/2018 5.50 6.00 5.50

03/21/2018 1.50 1.00 3.50

4/20/2018 7.00 7.00 7.00

05/23/2018 6.50 6.75 7.00

06/20/2018 6.75 6.25 8.00

08/30/2018 5.00 8.00 7.00

09/21/2018 6.00 6.00 5.00

11/21/2018 0.00 0.00 0.00

12/13/2018 7.00 6.00 5.50

01/03/2019 6.00 1.00 6.000.04 0.01 0.04

0.05 0.05

0.05 0.05 0.05 0.32

0.34

0.05 0.04 0.06 0.35

0.04

0.00

0.06 0.05 0.47

0.520.04 0.04 0.04

0.00 0.00

0.06 0.09 0.55

0.04 0.05 0.05 0.33

0.05 0.35

2.0 2.0 2.0

5.55

0.57

MPE-5 MPE-6 MPE-7

5 5 5

0.04 0.29

0.01 0.01 0.02 0.08

0.09

0.05 0.04 0.04 0.82

5.93 5.00

Volume Absorbed(gallons)

0.01 0.00 0.05 0.30

0.00 0.00 0.02 0.18

0.04 0.04

Volume (gallons) Volume (gallons) Volume (gallons)



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Well No.Diameter (inches) 2.00 2.00 2.00 2.00

Well Depth 6.92 6.92 7.79 7.75

Screen Interval 5 5 5 5


Thickness (Inches)

Thickness (Inches)

Thickness (Inches)

08/30/2018 4.00 4.00 4.00 4.00

09/21/2018 8.00 5.00 6.00 6.00

11/21/2018 3.00 18.00 7.00 2.50

12/13/2018 7.00 6.50 5.25 26.00

01/03/2019 6.00 6.00 5.50 8.00

Well No.Diameter (inches) 2.00 2.00

Well Depth 7.58 7.17

Screen Interval 5 5


Thickness (Inches)

08/30/2018 4.00 4.00

09/21/2018 5.50 5.50

11/21/2018 0.00 0.00

12/13/2018 18.00 5.00

01/03/2019 13.50 10.50

Note:Conversion Factor - inches of staining is converted to absorbent volume by multiplying by 0.007

Quarter 4

0.04 0.04 0.04 0.06

0.06 0.04 0.04 0.04

0.03 0.03 0.03 0.03

0.02

0.03

Volume (gallons) Volume (gallons)

0.13 0.04

0.09 0.07

0.00

0.04 0.04

0.03

0.00

MPE-12 MPE-13

MPE-8 MPE-9 MPE-10 MPE-11

Volume (gallons) Volume (gallons) Volume (gallons) Volume (gallons)

0.05 0.05 0.04 0.18

0.13 0.05 0.02



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Facility Name: Tupperware Brands Corporation All Measurements = Feet

Facility Address: 14901 S. Orange Blossom Trail, Orlando, Florida Blank = No Data

Facility ID#: 49/8521966

Well No. MPE-1 MPE-2 MPE-3 MPE-4Diameter (inches) 2.00 2.00 2.00 2.00

Well Depth (ft bls) 5.87 5.37 5.06 4.83

Screen Length (ft) 5 5 5 4.83

DATE DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

4/14/2017 5.89 5.45 0.44 5.03 5.02 0.01 4.52 4.51 0.01 4.41 NP 0

4/20/2017 5.60 -- 0.00 5.24 5.22 0.02 4.72 -- 0.00 4.36 4.20 0.16

5/9/2017 Dry @ 5.87 (TD) Dry @ 5.37 (TD) Dry @ 5.06 (TD) Dry @ 4.83 (TD)

6/5/2017 4.14 -- 0.00 4.02 -- 0.00 5.02 -- 0.00 3.12 2.99 0.13

6/13/2017 3.09 -- 0.00 2.68 -- 0.00 2.20 -- 0.00 1.69 -- 0.00

6/20/2017 2.19 -- 0.00 1.82 1.81 0.01 1.34 1.33 0.01 0.85 -- 0.00

6/30/2017 1.65 -- 0.00 1.72 -- 0.00 1.43 -- 0.00 0.90 -- 0.00

12/20/2017 3.16 -- 0.00 2.76 -- 0.00 2.35 -- 0.00 1.83 -- 0.00

1/31/2018 1.90 -- 0.00 2.87 -- 0.00 1.41 -- 0.00 1.85 -- 0.00

2/26/2018 3.49 -- 0.00 3.03 -- 0.00 2.65 -- 0.00 -- -- --

3/30/2018 4.41 -- 0.00 4.10 -- 0.00 3.70 -- 0.00 5.05 5.03 0.02

04/27/2018 4.69 -- 0.00 4.30 -- 0.00 3.89 -- 0.00 5.21 -- 0.00

5/31/2018 2.90 -- 0.00 2.39 -- 0.00 2.13 -- 0.00 3.41 3.40 0.01

6/27/2018 1.66 -- 0.00 1.71 -- 0.00 1.41 1.40 0.01 2.75 -- 0.00

8/24/2018 4.10 -- 0.00 3.58 3.575 0.005 3.22 -- 0.00 3.07 3.06 0.01

9/24/2018 3.85 -- 0.00 3.41 3.40 0.01 2.98 -- 0.00 2.81 -- 0.00

11/28/2018 4.46 -- 0.00 4.12 -- 0.00 3.75 -- 0.00 3.905 3.86 0.04

12/20/2018 3.98 -- 0.00 3.46 3.45 0.01 3.08 -- 1.00 3.23 -- 0.00

1/10/2019 4.10 -- 0.00 3.62 -- 0.00 3.18 -- 0.00 3.32 3.31 0.01

TABLE 2: FREE PRODUCT MEASUREMENT SUMMARY


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Well No. MPE-5 MPE-6 MPE-7 TankDiameter (inches) 2.00 2.00 2.00

Well Depth (ft bls) 5.55 5.93 5

Screen Length 5 5 5

DATE DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

4/14/2017 5.20 4.62 0.58 4.75 -- -- 4.73 -- --

4/20/2017 4.72 -- 0.00 5.65 5.2 0.45 5.25 5.1 0.15 4.59

5/9/2017 5.47 -- 0.00 5.91 -- 0.00 5.79 5.75 0.04

6/5/2017 3.45 -- 0.00 3.72 -- 0.00 3.68 -- 0.00

6/13/2017 2.20 -- 0.00 2.49 -- 0.00 2.45 2.43 0.02

6/20/2017 1.30 -- 0.00 1.59 -- 0.00 1.56 1.55 0.01

6/30/2017 1.43 -- 0.00 1.93 -- 0.00 2.28 -- 0.00

12/20/2017 2.33 -- 0.00 2.63 -- 0.00 2.58 -- 0.00

1/31/2018 1.33 -- 0.00 1.63 -- 0.00 2.60 -- 0.00

2/26/2018 2.61 -- 0.00 2.90 -- 0.00 2.88 -- 0.00

3/30/2018 3.67 -- 0.00 3.91 -- 0.00 3.88 -- 0.00

04/27/2018 3.85 -- 0.00 4.11 -- 0.00 4.08 -- 0.00

5/31/2018 2.06 -- 0.00 2.33 -- 0.00 2.06 -- 0.00

6/20/2018 1.45 -- 0.00 1.81 -- 0.00 2.27 -- 0.00

8/24/2018 3.22 -- 0.00 3.49 3.47 0.02 3.49 -- 1.00

9/24/2018 3.05 -- 0.00 3.17 -- 0.00 3.25 3.24 0.01

11/28/2018 3.76 -- 0.00 3.94 -- 0.00 4.05 -- 0.00

12/20/2018 3.08 -- 0.00 3.26 -- 0.00 3.29 -- 0.00

1/10/2019 3.19 -- 0.00 3.38 -- 0.00 3.50 -- 0.00

Visible product but not

enough to measure



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Well No. MPE-8 MPE-9 MPE-10 MPE-11Diameter (inches) 2.00 2.00 2.00 2.00

Well Depth (ft bls)Screen Length 5 5 5 5

DATE DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

8/24/2018 5.71 -- 0.00 5.64 -- 0.00 5.49 -- 0.00 5.55 -- 0.00

9/24/2018 5.37 -- 0.00 5.40 -- 0.00 5.28 -- 0.00 5.33 -- 0.00

11/28/2018 6.22 -- 0.00 6.78 0.67 6.11 6.07 -- 0.00 6.09 -- 0.00

12/20/2018 5.51 5.50 0.01 5.49 5.41 0.08 5.37 5.36 0.01 5.48 5.41 0.07

1/10/2019 5.64 -- 0.00 5.61 5.59 0.02 5.48 5.46 0.02 5.50 5.49 0.01

Well No. MPE-12 MPE-13Diameter (inches) 2.00 2.00

Well Depth (ft bls)Screen Length 5 5

DATE DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

DTW DTPFP

Thickness (ft)

8/24/2018 5.47 -- 0.00 4.45 -- 0.00

9/24/2018 5.68 5.25 0.43 5.47 5.46 0.01

11/28/2018 6.96 1.1 5.86 5.78 -- 0.00

12/20/2018 5.30 5.27 0.03 5.04 -- 0.00

1/10/2019 5.40 5.31 0.09 5.00 -- 0.00

Notes: FP = Free Product

DTP = Depth to product

DTW = Depth to water

ft = feet

ft bls = feet below land surface

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Page 3 of 3Rev. 07/26/18


Facility Name: Tupperware Brands Corporation

Facility Address: 14901 S. Orange Blossom Trail, Orlando, Florida


Influent Samples

Sample Sample Sample Estimated

TPH

Emissions

Cumulative

Mass

RecoveredI.D. Date Time Air Flow (scfm) Benzene Toluene Ethylbenzene Xylenes Total BTEX MTBE TPH (lb/day) (lbs)

Pre-Carbon-Startup 4/13/2017 5:20 PM 150 1.0 U 3.0 2.2 15.8 21.0 1.0 U 430 5.80 0.00

Pre-Carbon-Week 1 4/20/2017 8:35 AM 150 1.0 U 1.0 U 1.0 U 3.0 U 0.0 1.0 U 59 0.80 23.09

Pre-Carbon-Week 2 4/27/2017 8:45 AM 160 1.0 U 1.0 U 1.0 U 3.0 U 0.0 1.0 U 16 0.23 26.68

Exhaust Fan On 6/8/2017

Exhaust Fan-1 6/30/2017 10:50 AM 50 1.0 U 1.0 U 1.0 U 1.3 1.3 1.0 U 260 0.39 29.53

Exhaust Fan-Month 1 1/24/2018 2:35 PM 50 0.44 U 1.0 U 0.36 U 1.27 U 0.0 0.32 U J3 10 U 0.01 43.56

Exhaust Fan-Month 2 2/19/2018 12:32 PM 50 0.44 U 1.0 U 0.36 U 2.7 2.7 0.32 U 440 0.66 46.48

Exhaust Fan-Month 3 3/28/2018 9:40 AM 50 0.44 U 1.0 U 0.36 U 0.46 I 0.46 0.32 U J3 170 0.25 52.12

SVE Effluent-Month 6 6/20/2018 10:00 AM 50 0.44 U 1.0 U 0.36 U 0.59 I 0.59 0.32 U 400 0.60 64.08

Exhaust Fan-Month 12 12/6/2018 12:30 PM 50 1.6 I 2.7 I 1.1 I 4.4 9.80 0.32 U 540 0.81 103.76

Effluent Samples

Sample Sample Sample Estimated

*TPH

Emissions

*Cumulative

Mass

RecoveredI.D. Date Time Air Flow (scfm) Benzene Toluene Ethylbenzene Xylenes Total BTEX MTBE TPH (lb/day) (lbs)

Post Carbon-Startup 4/13/2017 5:30 PM 150 1.0 U 1.0 U 1.0 U 3.0 U 0.0 1.0 U 10 0.13 0.00

Post Carbon-Week 1 4/20/2017 8:40 AM 150 1.0 U 1.0 U 1.0 U 3.0 U 0.0 1.0 U 10 0.13 0.94

Post Carbon-Week 2 4/27/2017 8:55 AM 160 1.0 U 1.0 U 1.0 U 3.0 U 0.0 1.0 U 10 0.14 1.92

Notes:

Total BTEX - Sum of benzene, toluene, ethylbenzene and total xylenes

MTBE - methyl tert-butyl ether

TPH - total petroleum hydrocarbons via US EPA Method TO3

scfm - standard cubic feet per minute

* = Based on an 8-hour operational time

TABLE 3: AIR SAMPLE ANALYTICAL SUMMARY

Hydrocarbon Concentrations (mg/m3)

Hydrocarbon Concentrations (mg/m3)

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Well No. DW-1 MW-1 MW-2 MW-3 MW-4

Diameter (inches) 1.5 1.5 1.5 1.5 1.5

Well Depth 20.00 12.00 12.00 7.50 11.00

Screen Interval 15 - 20 2 - 12 2 - 12 2.5 - 7.5 1 - 11

TOC Elevation 100.10 100.00 100.11 99.84 99.78

DATE ELEV DTWFP

DepthELEV DTW FP ELEV DTW FP ELEV DTW FP ELEV DTW FP

04/20/2017 - 94.50 5.50 94.67 5.44 94.06 5.78 94.24 5.54

06/05/2017 95.49 4.61 95.76 4.24 95.77 4.34 95.78 4.06 95.14 4.64

10/18/2017 96.10 4.00 97.47 2.53 97.49 2.62 97.46 2.38 97.48 2.30

3/28/2018 95.84 4.26 95.60 4.40 95.80 4.31 95.19 4.65 95.39 4.39

6/27/2018 96.40 3.70 97.62 2.38 97.68 2.43 97.54 2.30 97.59 2.19

8/24/2018 97.32 2.78 97.38 2.62 97.40 2.71 97.31 2.53 97.33 2.45

12/6/2018 96.85 3.25 97.13 2.87 96.76 3.35 96.82 3.02 96.81 2.97

TABLE 4: GROUNDWATER ELEVATION SUMMARY


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See notes at end of table.

BenzeneEthyl-

benzeneMTBE Toluene

Total

Xylenes

Total

VOAsEDB

Total

Lead

Location Date (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L)

1 30 20 40 20 -- 0.02 15

100 300 200 400 200 --

6/5/2017 0.50 U 0.44 U 0.44 U 0.51 U 2.3 I 2.3 NS NS

3/28/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.99 I NS NS NS

6/27/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.53 I NS NS NS

8/24/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.76 I NS NS NS

12/6/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.54 I NS NS NS

6/5/2017 0.50 U 0.44 U 0.51 U 1.45 U 0.01 U 2.2 U

3/28/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

6/27/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

8/24/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

12/6/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

6/5/2017 0.50 U 0.44 U 0.44 U 0.51 U 0.50 U 1.89 U NS NS

3/28/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

6/27/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

8/24/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

12/6/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

6/5/2017 0.50 U 0.44 U 0.44 U 0.51 U 0.50 U 1.89 U NS NS

3/28/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

6/27/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

8/24/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

12/6/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

TABLE 5A: GROUNDWATER MONITORING WELL ANALYTICAL SUMMARY - VOAs, EDB AND

LEAD

MW-1

MW-2

MW-3

Sample

DW-1

GCTL

NADC

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See notes at end of table.

BenzeneEthyl-

benzeneMTBE Toluene

Total

Xylenes

Total

VOAsEDB

Total

Lead

Location Date (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L)

1 30 20 40 20 -- 0.02 15

100 300 200 400 200 --

TABLE 5A: GROUNDWATER MONITORING WELL ANALYTICAL SUMMARY - VOAs, EDB AND

LEAD

Sample

DW-1

GCTL

NADC

6/5/2017 0.50 U 0.44 U 0.44 U 0.51 U 0.50 U 1.89 U NS NS

3/28/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

6/27/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

8/24/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

12/6/2018 0.25 U 0.27 U 0.44 U 0.24 U 0.50 U NS NS NS

Notes: NA = Not Available.

NS = Not Sampled.

GCTLs = Groundwater Cleanup Target Levels specified in Table I of Chapter 62-777, F.A.C.

NADCs = Natural Attenuation Default Source Concentrations specified in Table V of Chapter 62-777, F.A.C.

** = As provided in Chapter 62-550, F.A.C.

I = Indicates a result greater than or equal to method detection limit but less than practical quanitation limit.

U = Indicates a result less than method detection limit.

Bold indicates exceedance of GCTLs. Shaded box indicates exceedance of NADCs

Current Data

MW-4

P:\6CN800101 Tupperware\13 Tables\ Reporting TablesT5A-Groundwater VOCs & Metals



Rev. 09/7/18





5,000 28 28 20 210 2100 0.05 0.2 0.05 210 0.5 4.8 0.005 280 280 0.05 14 210 210

50,000 280 280 200 2,100 21,000 5 20 5 21,000 50 480 0.5 2,800 2,800 5 140 2,100 2,100

Location Date (mg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L)

2/14/2017 0.10 U 0.047 U 0.044 U 0.037 U 0.036 U 0.036 U 0.037 U 0.043 U 0.059 U 0.040 U 0.046 U 0.051 U 0.026 U 0.051 U 0.038 U 0.037 U 0.035 U 0.039 U 0.048 U



6/27/2018 0.33 U 0.24 U 0.24 U 0.24 U 0.077 U 0.086 U 0.048 U 0.070 U 0.048 U 0.067 U 0.080 U 0.065 U 0.074 U 0.25 I 0.24 U 0.048 U 1.3 U 0.86 I 0.14 I



6/5/2017 0.20 I 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.045 U 0.22 U 0.045 U 0.22 U 0.22 U 0.22 U 0.032 U 0.22 U 0.22 U 0.045 U 0.22 U 0.22 U 0.22 U





6/5/2017 0.16 U 0.22 U 0.22 I 0.22 U 0.22 U 0.22 U 0.045 U 0.22 U 0.045 U 0.22 U 0.22 U 0.22 U 0.032 U 0.22 U 0.22 U 0.045 U 0.37 I 0.22 U 0.22 U





6/5/2017 0.16 U 0.22 U 0.22 U 0.22 I 0.22 U 0.22 U 0.045 U 0.22 U 0.045 U 0.22 U 0.22 U 0.22 U 0.032 U 0.22 U 0.22 U 0.045 U 2.1 V 0.22 U 0.22 U

3/28/2018 0.32 U 0.22 U 0.22 U 0.24 I 0.072 U 0.080 U 0.045 U 0.065 U 0.045 U 0.062 U 0.047 U 0.061 U 0.068 U 0.21 U 0.22 U 0.045 U 3.7 0.77 U 0.088 U

6/27/2018 0.33 U 0.24 U 0.24 U 0.24 U 0.077 U 0.18 I 0.048 U 0.070 U 0.048 U 0.067 U 0.080 U 0.065 U 0.074 U 0.22 U 0.24 U 0.048 U 1.5 I 0.83 U 0.095 U


12/6/2018 0.32 U 0.24 U 0.24 U 0.24 U 0.077 U 0.088 I 0.048 U 0.070 U 0.048 U 0.067 U 0.080 U 0.065 U 0.074 U 0.22 U 0.24 U 0.048 U 1.3 U 0.83 U 0.095 U






Benzo[a]

pyrene

Acenapht

hylene

Anthrace

ne

Fluoranth

ene

Acenapht

hene

Benzo[b]

fluoranth

ene

TABLE 5B: GROUNDWATER MONITORING WELL ANALYTICAL SUMMARY - PAHs AND TRPHs

Fluorene

Indeno[1,

2,3-

cd]pyren

e

Naphthal

ene

Benzo[g,

h,i]peryle

ne

Benzo[k]f

luoranthe

ne

Chrysene

Dibenz(a,

h)anthrac

ene

Phenanth

rene

2-

Methylna

phthalen

e

Pyrene

Benzo[a]

anthrace

ne

Sample TRPHs

1-

Methylna

phthalen

e

MW-1

MW-2

MW-3

MW-4

DW-1

Pond #1

NADCs

GCTLs

P:\6CN800101 Tupperware\13 Tables\ Reporting TablesT5B-Groundwater PAHs & TRPHs



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5,000 28 28 20 210 2100 0.05 0.2 0.05 210 0.5 4.8 0.005 280 280 0.05 14 210 210

50,000 280 280 200 2,100 21,000 5 20 5 21,000 50 480 0.5 2,800 2,800 5 140 2,100 2,100

Location Date (mg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L) (µg/L)

Benzo[a]

pyrene

Acenapht

hylene

Anthrace

ne

Fluoranth

ene

Acenapht

hene

Benzo[b]

fluoranth

ene

TABLE 5B: GROUNDWATER MONITORING WELL ANALYTICAL SUMMARY - PAHs AND TRPHs

Fluorene

Indeno[1,

2,3-

cd]pyren

e

Naphthal

ene

Benzo[g,

h,i]peryle

ne

Benzo[k]f

luoranthe

ne

Chrysene

Dibenz(a,

h)anthrac

ene

Phenanth

rene

2-

Methylna

phthalen

e

Pyrene

Benzo[a]

anthrace

ne

Sample TRPHs

1-

Methylna

phthalen

e

Pond #1

NADCs

GCTLs

Notes: NA = Not Available.

NS = Not Sampled.

GCTLs = Groundwater Cleanup Target Levels specified in Table I of Chapter 62-777, F.A.C.

NADCs = Natural Attenuation Default Source Concentrations specified in Table V of Chapter 62-777, F.A.C.

** = As provided in Chapter 62-550, F.A.C.

I = Indicates a result greater than or equal to method detection limit but less than practical quanitation limit.

U = Indicates a result less than method detection limit.

Bold indicates exceedance of GCTLs. Shaded box indicates exceedance of NADCs

Current Data

V = Indicates that the analyte was detected at or above the method detection limit in both the sample and the associated method blank and the value of 10 times the blank value was

P:\6CN800101 Tupperware\13 Tables\ Reporting TablesT5B-Groundwater PAHs & TRPHs



Rev. 09/7/18




FIGURES

Source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS,USDA, USGS, AEX, Getmapping, Aerogrid, IGN, IGP, swisstopo, and the GISUser Community

.0 450225

Ft

Tupperware Brand CorporationSouth Orange Blossom Trail

Orlando, Florida

FIGURE 1Aerial Map

LEGENDApproximate Site Location (IT Building)Approximate Property Boundary

N Orange Blossom Trail

Mary Louis LN




APPENDIX A

OCEPD Approval Letter dated November 15, 2018 and Drum Manifest




APPENDIX B

Field Notes for Absorbent Sock and Free Product Gauging Events




APPENDIX C

Groundwater Sampling Logs with Equipment Calibration Logs




APPENDIX D

Air Laboratory Analytical Report

ANALYTICAL REPORTTestAmerica Laboratories, Inc.TestAmerica Tampa6712 Benjamin RoadSuite 100Tampa, FL 33634Tel: (813)885-7427

TestAmerica Job ID: 660-91193-1Client Project/Site: Tupperware

For:HSW Engineering, Inc.605 E. Robinson St.Suite 308Orlando, Florida 32801

Attn: Mr. Jason Cicchetti

Authorized for release by:12/12/2018 4:36:57 PM

Matt Jones, Project Manager I(850)[email protected]

The test results in this report meet all 2003 NELAC and 2009 TNI requirements for accreditedparameters, exceptions are noted in this report. This report may not be reproduced except in full,and with written approval from the laboratory. For questions please contact the Project Managerat the e-mail address or telephone number listed on this page.

This report has been electronically signed and authorized by the signatory. Electronic signature isintended to be the legally binding equivalent of a traditionally handwritten signature.

Results relate only to the items tested and the sample(s) as received by the laboratory.

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http://www.testamericainc.com/AskTheExpert/Expert_index.htm

http://www.testamericainc.com

mailto:[email protected]

Table of Contents

Client: HSW Engineering, Inc.Project/Site: Tupperware

TestAmerica Job ID: 660-91193-1

Page 2 of 13TestAmerica Tampa

12/12/2018

Cover Page . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1

Table of Contents . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2

Sample Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3

Definitions/Glossary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4

Detection Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5

Client Sample Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6

QC Sample Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7

QC Association Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8

Lab Chronicle . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9

Method Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10

Certification Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11

Chain of Custody . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12

Receipt Checklists . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13

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Sample SummaryTestAmerica Job ID: 660-91193-1Client: HSW Engineering, Inc.

Project/Site: Tupperware

Lab Sample ID Client Sample ID ReceivedCollectedMatrix

660-91193-1 Exhaust Fan-Month 12 Air - Tedlar Bag 12/06/18 12:30 12/07/18 09:35

TestAmerica Tampa

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Definitions/GlossaryTestAmerica Job ID: 660-91193-1Client: HSW Engineering, Inc.


Qualifiers

Air - GC/MS VOA

Qualifier Description

I The reported value is between the laboratory method detection limit and the laboratory practical quantitation limit.

Qualifier

U Indicates that the compound was analyzed for but not detected.

J3 Estimated value; value may not be accurate. Spike recovery or RPD outside of criteria.

Glossary

These commonly used abbreviations may or may not be present in this report.

¤ Listed under the "D" column to designate that the result is reported on a dry weight basis

Abbreviation

%R Percent Recovery

CFL Contains Free Liquid

CNF Contains No Free Liquid

DER Duplicate Error Ratio (normalized absolute difference)

Dil Fac Dilution Factor

DL Detection Limit (DoD/DOE)

DL, RA, RE, IN Indicates a Dilution, Re-analysis, Re-extraction, or additional Initial metals/anion analysis of the sample

DLC Decision Level Concentration (Radiochemistry)

EDL Estimated Detection Limit (Dioxin)

LOD Limit of Detection (DoD/DOE)

LOQ Limit of Quantitation (DoD/DOE)

MDA Minimum Detectable Activity (Radiochemistry)

MDC Minimum Detectable Concentration (Radiochemistry)

MDL Method Detection Limit

ML Minimum Level (Dioxin)

NC Not Calculated

ND Not Detected at the reporting limit (or MDL or EDL if shown)

PQL Practical Quantitation Limit

QC Quality Control

RER Relative Error Ratio (Radiochemistry)

RL Reporting Limit or Requested Limit (Radiochemistry)

RPD Relative Percent Difference, a measure of the relative difference between two points

TEF Toxicity Equivalent Factor (Dioxin)

TEQ Toxicity Equivalent Quotient (Dioxin)

TestAmerica Tampa

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Detection SummaryTestAmerica Job ID: 660-91193-1Client: HSW Engineering, Inc.


Client Sample ID: Exhaust Fan-Month 12 Lab Sample ID: 660-91193-1

Benzene

PQL

2.0 mg/m3

MDL

0.44

Analyte Result Qualifier Unit Dil Fac D Method Prep Type

Total/NA1I1.6 EPA-18

Ethylbenzene 2.0 mg/m30.36 Total/NA11.1 I EPA-18

m-Xylene & p-Xylene 3.0 mg/m30.89 Total/NA11.1 I EPA-18

o-Xylene 2.0 mg/m30.38 Total/NA13.7 EPA-18

Toluene 3.0 mg/m31.0 Total/NA12.7 I EPA-18

Total Hydrocarbons 30 mg/m310 Total/NA1540 EPA-18

TestAmerica Tampa

This Detection Summary does not include radiochemical test results.

Page 5 of 13 12/12/2018

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Client Sample ResultsTestAmerica Job ID: 660-91193-1Client: HSW Engineering, Inc.


Lab Sample ID: 660-91193-1Client Sample ID: Exhaust Fan-Month 12Matrix: Air - Tedlar BagDate Collected: 12/06/18 12:30

Date Received: 12/07/18 09:35

Method: EPA-18 - Volatile Organic CompoundsPQL MDL

Benzene 1.6 I 2.0 0.44 mg/m3 12/08/18 14:40 1

Analyte Dil FacAnalyzedPreparedUnit DResult Qualifier

2.0 0.36 mg/m3 12/08/18 14:40 1Ethylbenzene 1.1 I

1.0 0.32 mg/m3 12/08/18 14:40 1Methyl tert-butyl ether 0.32 U

3.0 0.89 mg/m3 12/08/18 14:40 1m-Xylene & p-Xylene 1.1 I

2.0 0.38 mg/m3 12/08/18 14:40 1o-Xylene 3.7

3.0 1.0 mg/m3 12/08/18 14:40 1Toluene 2.7 I

30 10 mg/m3 12/08/18 14:40 1Total Hydrocarbons 540

TestAmerica Tampa

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QC Sample ResultsTestAmerica Job ID: 660-91193-1Client: HSW Engineering, Inc.


Method: EPA-18 - Volatile Organic Compounds

Client Sample ID: Method BlankLab Sample ID: MB 660-204396/8

Matrix: Air - Tedlar Bag Prep Type: Total/NA

Analysis Batch: 204396

PQL MDL

Benzene 0.44 U 2.0 0.44 mg/m3 12/08/18 11:57 1

MB MB

Analyte Dil FacAnalyzedPreparedDUnitResult Qualifier

0.36 U 0.362.0 mg/m3 12/08/18 11:57 1Ethylbenzene

0.32 U 0.321.0 mg/m3 12/08/18 11:57 1Methyl tert-butyl ether

0.89 U 0.893.0 mg/m3 12/08/18 11:57 1m-Xylene & p-Xylene

0.38 U 0.382.0 mg/m3 12/08/18 11:57 1o-Xylene

1.0 U 1.03.0 mg/m3 12/08/18 11:57 1Toluene

10 U 1030 mg/m3 12/08/18 11:57 1Total Hydrocarbons

Client Sample ID: Lab Control SampleLab Sample ID: LCS 660-204396/6



Total Hydrocarbons 900 817 mg/m3 91 66 - 126

Analyte

LCS LCS

DUnitResult Qualifier %Rec

Spike

Added

%Rec.

Limits

Client Sample ID: Exhaust Fan-Month 12Lab Sample ID: 660-91193-1 DU



Benzene 1.6 I 1.30 I mg/m3 20 30

Analyte

DU DU

DUnitResult Qualifier

Sample

Result

Sample

Qualifier LimitRPD

RPD

Ethylbenzene 1.1 I 0.557 I J3 mg/m3 67 30

Methyl tert-butyl ether 0.32 U 0.32 U mg/m3 NC 30

m-Xylene & p-Xylene 1.1 I 0.89 U mg/m3 NC 30

o-Xylene 3.7 1.97 I J3 mg/m3 62 30

Toluene 2.7 I 1.83 I J3 mg/m3 40 30

Total Hydrocarbons 540 362 J3 mg/m3 39 30

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QC Association SummaryTestAmerica Job ID: 660-91193-1Client: HSW Engineering, Inc.


Air - GC/MS VOA


Lab Sample ID Client Sample ID Prep Type Matrix Method Prep Batch

Air - Tedlar Bag EPA-18660-91193-1 Exhaust Fan-Month 12 Total/NA

Air - Tedlar Bag EPA-18MB 660-204396/8 Method Blank Total/NA

Air - Tedlar Bag EPA-18LCS 660-204396/6 Lab Control Sample Total/NA

Air - Tedlar Bag EPA-18660-91193-1 DU Exhaust Fan-Month 12 Total/NA

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Lab ChronicleClient: HSW Engineering, Inc. TestAmerica Job ID: 660-91193-1


Client Sample ID: Exhaust Fan-Month 12 Lab Sample ID: 660-91193-1Matrix: Air - Tedlar BagDate Collected: 12/06/18 12:30


Analysis EPA-18 12/08/18 14:40 ECC1 204396 TAL TAM

Type

Batch Batch

MethodPrep Type LabAnalystRun

Prepared

or Analyzed

Batch

Number

Dilution

Factor

Total/NA

Laboratory References:

TAL TAM = TestAmerica Tampa, 6712 Benjamin Road, Suite 100, Tampa, FL 33634, TEL (813)885-7427

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Method SummaryTestAmerica Job ID: 660-91193-1Client: HSW Engineering, Inc.


Method Method Description LaboratoryProtocol

EPAEPA-18 Volatile Organic Compounds TAL TAM

Protocol References:

EPA = US Environmental Protection Agency



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Accreditation/Certification SummaryClient: HSW Engineering, Inc. TestAmerica Job ID: 660-91193-1


Laboratory: TestAmerica TampaUnless otherwise noted, all analytes for this laboratory were covered under each accreditation/certification below.

Authority Program EPA Region Identification Number Expiration Date

Florida E842824NELAP 06-30-19

The following analytes are included in this report, but the laboratory is not certified by the governing authority. This list may include analytes for which

the agency does not offer certification.

Analysis Method Prep Method Matrix Analyte

EPA-18 Air - Tedlar Bag Benzene

EPA-18 Air - Tedlar Bag Ethylbenzene

EPA-18 Air - Tedlar Bag Methyl tert-butyl ether

EPA-18 Air - Tedlar Bag m-Xylene & p-Xylene

EPA-18 Air - Tedlar Bag o-Xylene

EPA-18 Air - Tedlar Bag Toluene

EPA-18 Air - Tedlar Bag Total Hydrocarbons

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Login Sample Receipt Checklist

Client: HSW Engineering, Inc. Job Number: 660-91193-1

Login Number: 91193

Question Answer Comment

Creator: Edwards, Erricka

List Source: TestAmerica Tampa

List Number: 1

N/ARadioactivity wasn't checked or is </= background as measured by a survey

meter.

TrueThe cooler's custody seal, if present, is intact.

TrueSample custody seals, if present, are intact.

TrueThe cooler or samples do not appear to have been compromised or

tampered with.

TrueSamples were received on ice.

TrueCooler Temperature is acceptable.

TrueCooler Temperature is recorded.

TrueCOC is present.

TrueCOC is filled out in ink and legible.

TrueCOC is filled out with all pertinent information.

TrueIs the Field Sampler's name present on COC?

TrueThere are no discrepancies between the containers received and the COC.

TrueSamples are received within Holding Time (excluding tests with immediate

HTs)

TrueSample containers have legible labels.

TrueContainers are not broken or leaking.

TrueSample collection date/times are provided.

TrueAppropriate sample containers are used.

TrueSample bottles are completely filled.

TrueSample Preservation Verified.

TrueThere is sufficient vol. for all requested analyses, incl. any requested

MS/MSDs

N/AContainers requiring zero headspace have no headspace or bubble is

<6mm (1/4").

TrueMultiphasic samples are not present.

TrueSamples do not require splitting or compositing.

N/AResidual Chlorine Checked.

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APPENDIX E

Groundwater Laboratory Analytical Report

ANALYTICAL REPORTTestAmerica Laboratories, Inc.TestAmerica Tampa6712 Benjamin RoadSuite 100Tampa, FL 33634Tel: (813)885-7427

TestAmerica Job ID: 660-91201-1Client Project/Site: Tupperware

For:HSW Engineering, Inc.605 E. Robinson St.Suite 308Orlando, Florida 32801

Attn: Mr. Jason Cicchetti

Authorized for release by:12/13/2018 11:04:18 AM

Matt Jones, Project Manager I(850)[email protected]

The test results in this report meet all 2003 NELAC and 2009 TNI requirements for accreditedparameters, exceptions are noted in this report. This report may not be reproduced except in full,and with written approval from the laboratory. For questions please contact the Project Managerat the e-mail address or telephone number listed on this page.

This report has been electronically signed and authorized by the signatory. Electronic signature isintended to be the legally binding equivalent of a traditionally handwritten signature.

Results relate only to the items tested and the sample(s) as received by the laboratory.

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https://secure.testamericainc.com/TotalAccess/login.aspx

http://www.testamericainc.com/AskTheExpert/Expert_index.htm

http://www.testamericainc.com

mailto:[email protected]

Table of Contents

Client: HSW Engineering, Inc.Project/Site: Tupperware

TestAmerica Job ID: 660-91201-1

Page 2 of 24TestAmerica Tampa

12/13/2018

Cover Page . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1

Table of Contents . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2

Sample Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3

Case Narrative . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4

Definitions/Glossary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5

Detection Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6

Client Sample Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7

QC Sample Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12

QC Association Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17

Lab Chronicle . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 19

Method Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21

Certification Summary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22

Chain of Custody . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 23

Receipt Checklists . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 24

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Sample SummaryTestAmerica Job ID: 660-91201-1Client: HSW Engineering, Inc.


Lab Sample ID Client Sample ID ReceivedCollectedMatrix

660-91201-1 DW-1 Water 12/06/18 11:21 12/07/18 09:35

660-91201-2 MW-1 Water 12/06/18 10:26 12/07/18 09:35

660-91201-3 MW-2 Water 12/06/18 10:00 12/07/18 09:35

660-91201-4 MW-3 Water 12/06/18 09:27 12/07/18 09:35

660-91201-5 MW-4 Water 12/06/18 08:56 12/07/18 09:35

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Case NarrativeClient: HSW Engineering, Inc. TestAmerica Job ID: 660-91201-1Project/Site: Tupperware

Job ID: 660-91201-1

Laboratory: TestAmerica Tampa

Narrative

Job Narrative660-91201-1

Comments

No additional comments.

Receipt

The samples were received on 12/7/2018 9:35 AM; the samples arrived in good condition, properly preserved and, where required, on ice.

The temperature of the cooler at receipt was 2.4º C.

GC/MS VOA No analytical or quality issues were noted, other than those described in the Definitions/Glossary page.

GC/MS Semi VOA No analytical or quality issues were noted, other than those described in the Definitions/Glossary page.

GC Semi VOA Method(s) FL-PRO: Two surrogates are used for this analysis. The laboratory's SOP allows one of these surrogates to be outside

acceptance criteria without performing re-extraction/re-analysis. The following samples contained an allowable number of surrogate compounds outside limits: DW-1 (660-91201-1), MW-1 (660-91201-2), MW-2 (660-91201-3), MW-3 (660-91201-4), MW-4 (660-91201-5), (LCS 660-204451/2-A), (MB 660-204451/1-A), (660-91206-C-1-A), (660-91206-D-1-A MS), (660-91206-C-2-A) and (660-91206-D-2-A DU). These results have been reported and qualified.

No additional analytical or quality issues were noted, other than those described above or in the Definitions/Glossary page.

Organic Prep No analytical or quality issues were noted, other than those described in the Definitions/Glossary page.


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Definitions/GlossaryTestAmerica Job ID: 660-91201-1Client: HSW Engineering, Inc.


Qualifiers

GC/MS VOA



Qualifier


GC/MS Semi VOA



Qualifier


GC Semi VOA


J1 Estimated value; value may not be accurate. Surrogate recovery outside of criteria.

Qualifier


Glossary

These commonly used abbreviations may or may not be present in this report.

¤ Listed under the "D" column to designate that the result is reported on a dry weight basis

Abbreviation

%R Percent Recovery

CFL Contains Free Liquid

CNF Contains No Free Liquid

DER Duplicate Error Ratio (normalized absolute difference)

Dil Fac Dilution Factor

DL Detection Limit (DoD/DOE)

DL, RA, RE, IN Indicates a Dilution, Re-analysis, Re-extraction, or additional Initial metals/anion analysis of the sample

DLC Decision Level Concentration (Radiochemistry)

EDL Estimated Detection Limit (Dioxin)

LOD Limit of Detection (DoD/DOE)

LOQ Limit of Quantitation (DoD/DOE)

MDA Minimum Detectable Activity (Radiochemistry)

MDC Minimum Detectable Concentration (Radiochemistry)

MDL Method Detection Limit

ML Minimum Level (Dioxin)

NC Not Calculated

ND Not Detected at the reporting limit (or MDL or EDL if shown)

PQL Practical Quantitation Limit

QC Quality Control

RER Relative Error Ratio (Radiochemistry)

RL Reporting Limit or Requested Limit (Radiochemistry)

RPD Relative Percent Difference, a measure of the relative difference between two points

TEF Toxicity Equivalent Factor (Dioxin)

TEQ Toxicity Equivalent Quotient (Dioxin)

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Detection SummaryTestAmerica Job ID: 660-91201-1Client: HSW Engineering, Inc.


Client Sample ID: DW-1 Lab Sample ID: 660-91201-1

m-Xylene & p-Xylene

PQL

2.0 ug/L

MDL

0.36


Total/NA1I0.54 8260B

Xylenes, Total 4.0 ug/L0.50 Total/NA10.54 I 8260B

Client Sample ID: MW-1 Lab Sample ID: 660-91201-2

No Detections.


No Detections.


Anthracene

PQL

0.48 ug/L

MDL

0.086


Total/NA1I0.088 8270D SIM


No Detections.

TestAmerica Tampa

This Detection Summary does not include radiochemical test results.

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Lab Sample ID: 660-91201-1Client Sample ID: DW-1Matrix: WaterDate Collected: 12/06/18 11:21


Method: 8260B - Volatile Organic Compounds (GC/MS)PQL MDL

Benzene 0.25 U 1.0 0.25 ug/L 12/12/18 13:47 1


1.0 0.27 ug/L 12/12/18 13:47 1Ethylbenzene 0.27 U

2.0 0.44 ug/L 12/12/18 13:47 1Methyl tert-butyl ether 0.44 U

2.0 0.36 ug/L 12/12/18 13:47 1m-Xylene & p-Xylene 0.54 I

2.0 0.50 ug/L 12/12/18 13:47 1o-Xylene 0.50 U

1.0 0.24 ug/L 12/12/18 13:47 1Toluene 0.24 U

4.0 0.50 ug/L 12/12/18 13:47 1Xylenes, Total 0.54 I

4-Bromofluorobenzene 98 70 - 130 12/12/18 13:47 1

Surrogate Dil FacAnalyzedPreparedQualifier Limits%Recovery

Dibromofluoromethane 100 12/12/18 13:47 170 - 130

Toluene-d8 (Surr) 100 12/12/18 13:47 170 - 130

Method: 8270D SIM - Semivolatile Organic Compounds (GC/MS SIM)PQL MDL

Acenaphthene 0.24 U 0.72 0.24 ug/L 12/08/18 10:15 12/10/18 08:25 1


0.48 0.077 ug/L 12/08/18 10:15 12/10/18 08:25 1Acenaphthylene 0.077 U

0.48 0.086 ug/L 12/08/18 10:15 12/10/18 08:25 1Anthracene 0.086 U

0.48 0.048 ug/L 12/08/18 10:15 12/10/18 08:25 1Benzo[a]anthracene 0.048 U

0.48 0.070 ug/L 12/08/18 10:15 12/10/18 08:25 1Benzo[a]pyrene 0.070 U

0.48 0.048 ug/L 12/08/18 10:15 12/10/18 08:25 1Benzo[b]fluoranthene 0.048 U

0.48 0.067 ug/L 12/08/18 10:15 12/10/18 08:25 1Benzo[g,h,i]perylene 0.067 U

0.48 0.080 ug/L 12/08/18 10:15 12/10/18 08:25 1Benzo[k]fluoranthene 0.080 U

0.48 0.065 ug/L 12/08/18 10:15 12/10/18 08:25 1Chrysene 0.065 U

0.48 0.074 ug/L 12/08/18 10:15 12/10/18 08:25 1Dibenz(a,h)anthracene 0.074 U

0.72 0.22 ug/L 12/08/18 10:15 12/10/18 08:25 1Fluoranthene 0.22 U

0.72 0.24 ug/L 12/08/18 10:15 12/10/18 08:25 1Fluorene 0.24 U

0.48 0.048 ug/L 12/08/18 10:15 12/10/18 08:25 1Indeno[1,2,3-cd]pyrene 0.048 U

0.72 0.24 ug/L 12/08/18 10:15 12/10/18 08:25 11-Methylnaphthalene 0.24 U


3.8 1.3 ug/L 12/08/18 10:15 12/10/18 08:25 1Naphthalene 1.3 U

2.9 0.83 ug/L 12/08/18 10:15 12/10/18 08:25 1Phenanthrene 0.83 U

0.48 0.095 ug/L 12/08/18 10:15 12/10/18 08:25 1Pyrene 0.095 U

Fluoranthene-d10 58 35 - 140 12/08/18 10:15 12/10/18 08:25 1


2-methylnaphthalene-d10 42 12/08/18 10:15 12/10/18 08:25 119 - 110

Method: FL-PRO - Florida - Petroleum Range Organics (GC)PQL MDL

Total Petroleum Hydrocarbons

(C8-C40)

0.31 U 0.89 0.31 mg/L 12/11/18 06:38 12/11/18 14:12 1


o-Terphenyl 75 J1 82 - 142 12/11/18 06:38 12/11/18 14:12 1


n-C39 74 12/11/18 06:38 12/11/18 14:12 142 - 193

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Lab Sample ID: 660-91201-2Client Sample ID: MW-1Matrix: WaterDate Collected: 12/06/18 10:26



Benzene 0.25 U 1.0 0.25 ug/L 12/12/18 14:24 1




2.0 0.36 ug/L 12/12/18 14:24 1m-Xylene & p-Xylene 0.36 U

2.0 0.50 ug/L 12/12/18 14:24 1o-Xylene 0.50 U

1.0 0.24 ug/L 12/12/18 14:24 1Toluene 0.24 U

4.0 0.50 ug/L 12/12/18 14:24 1Xylenes, Total 0.50 U




Toluene-d8 (Surr) 99 12/12/18 14:24 170 - 130





0.48 0.086 ug/L 12/08/18 10:15 12/10/18 09:05 1Anthracene 0.086 U






0.48 0.065 ug/L 12/08/18 10:15 12/10/18 09:05 1Chrysene 0.065 U



0.72 0.24 ug/L 12/08/18 10:15 12/10/18 09:05 1Fluorene 0.24 U






0.48 0.095 ug/L 12/08/18 10:15 12/10/18 09:05 1Pyrene 0.095 U

Fluoranthene-d10 52 35 - 140 12/08/18 10:15 12/10/18 09:05 1





(C8-C40)

0.32 U 0.93 0.32 mg/L 12/11/18 06:38 12/11/18 14:31 1


o-Terphenyl 67 J1 82 - 142 12/11/18 06:38 12/11/18 14:31 1


n-C39 77 12/11/18 06:38 12/11/18 14:31 142 - 193

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Benzene 0.25 U 1.0 0.25 ug/L 12/12/18 15:20 1





2.0 0.50 ug/L 12/12/18 15:20 1o-Xylene 0.50 U

1.0 0.24 ug/L 12/12/18 15:20 1Toluene 0.24 U





Toluene-d8 (Surr) 102 12/12/18 15:20 170 - 130





0.46 0.083 ug/L 12/08/18 10:15 12/10/18 07:55 1Anthracene 0.083 U






0.46 0.063 ug/L 12/08/18 10:15 12/10/18 07:55 1Chrysene 0.063 U



0.69 0.23 ug/L 12/08/18 10:15 12/10/18 07:55 1Fluorene 0.23 U






0.46 0.091 ug/L 12/08/18 10:15 12/10/18 07:55 1Pyrene 0.091 U

Fluoranthene-d10 46 35 - 140 12/08/18 10:15 12/10/18 07:55 1





(C8-C40)

0.32 U 0.93 0.32 mg/L 12/11/18 06:38 12/11/18 14:50 1


o-Terphenyl 59 J1 82 - 142 12/11/18 06:38 12/11/18 14:50 1


n-C39 55 12/11/18 06:38 12/11/18 14:50 142 - 193

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Benzene 0.25 U 1.0 0.25 ug/L 12/12/18 15:39 1





2.0 0.50 ug/L 12/12/18 15:39 1o-Xylene 0.50 U

1.0 0.24 ug/L 12/12/18 15:39 1Toluene 0.24 U





Toluene-d8 (Surr) 102 12/12/18 15:39 170 - 130





0.48 0.086 ug/L 12/08/18 10:15 12/10/18 08:16 1Anthracene 0.088 I






0.48 0.065 ug/L 12/08/18 10:15 12/10/18 08:16 1Chrysene 0.065 U



0.72 0.24 ug/L 12/08/18 10:15 12/10/18 08:16 1Fluorene 0.24 U






0.48 0.095 ug/L 12/08/18 10:15 12/10/18 08:16 1Pyrene 0.095 U

Fluoranthene-d10 44 35 - 140 12/08/18 10:15 12/10/18 08:16 1





(C8-C40)

0.32 U 0.93 0.32 mg/L 12/11/18 06:38 12/11/18 15:09 1


o-Terphenyl 56 J1 82 - 142 12/11/18 06:38 12/11/18 15:09 1


n-C39 52 12/11/18 06:38 12/11/18 15:09 142 - 193

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Benzene 0.25 U 1.0 0.25 ug/L 12/12/18 15:57 1





2.0 0.50 ug/L 12/12/18 15:57 1o-Xylene 0.50 U

1.0 0.24 ug/L 12/12/18 15:57 1Toluene 0.24 U





Toluene-d8 (Surr) 100 12/12/18 15:57 170 - 130





0.46 0.083 ug/L 12/08/18 10:15 12/10/18 08:37 1Anthracene 0.083 U






0.46 0.063 ug/L 12/08/18 10:15 12/10/18 08:37 1Chrysene 0.063 U



0.69 0.23 ug/L 12/08/18 10:15 12/10/18 08:37 1Fluorene 0.23 U






0.46 0.091 ug/L 12/08/18 10:15 12/10/18 08:37 1Pyrene 0.091 U

Fluoranthene-d10 48 35 - 140 12/08/18 10:15 12/10/18 08:37 1





(C8-C40)

0.33 U 0.96 0.33 mg/L 12/11/18 06:38 12/11/18 15:28 1


o-Terphenyl 61 J1 82 - 142 12/11/18 06:38 12/11/18 15:28 1


n-C39 65 12/11/18 06:38 12/11/18 15:28 142 - 193

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Method: 8260B - Volatile Organic Compounds (GC/MS)

Client Sample ID: Method BlankLab Sample ID: MB 660-204510/6Matrix: Water Prep Type: Total/NAAnalysis Batch: 204510

PQL MDL

Benzene 0.25 U 1.0 0.25 ug/L 12/12/18 11:38 1

MB MB


0.27 U 0.271.0 ug/L 12/12/18 11:38 1Ethylbenzene

0.44 U 0.442.0 ug/L 12/12/18 11:38 1Methyl tert-butyl ether

0.36 U 0.362.0 ug/L 12/12/18 11:38 1m-Xylene & p-Xylene

0.50 U 0.502.0 ug/L 12/12/18 11:38 1o-Xylene

0.24 U 0.241.0 ug/L 12/12/18 11:38 1Toluene

0.50 U 0.504.0 ug/L 12/12/18 11:38 1Xylenes, Total


MB MB

Surrogate Dil FacPrepared AnalyzedQualifier Limits%Recovery

100 12/12/18 11:38 1Dibromofluoromethane 70 - 130

102 12/12/18 11:38 1Toluene-d8 (Surr) 70 - 130

Client Sample ID: Lab Control SampleLab Sample ID: LCS 660-204510/4Matrix: Water Prep Type: Total/NAAnalysis Batch: 204510

Benzene 10.0 10.0 ug/L 100 69 - 131

Analyte

LCS LCS


Spike

Added

%Rec.

Limits

Ethylbenzene 10.0 10.1 ug/L 101 77 - 130

Methyl tert-butyl ether 10.0 9.95 ug/L 99 66 - 130

m-Xylene & p-Xylene 10.0 10.2 ug/L 102 65 - 130

o-Xylene 10.0 9.64 ug/L 96 63 - 130

Toluene 10.0 9.96 ug/L 100 77 - 130

4-Bromofluorobenzene 70 - 130

Surrogate

96

LCS LCS

Qualifier Limits%Recovery

99Dibromofluoromethane 70 - 130

101Toluene-d8 (Surr) 70 - 130

Client Sample ID: MW-1Lab Sample ID: 660-91201-2 MSMatrix: Water Prep Type: Total/NAAnalysis Batch: 204510

Benzene 0.25 U 10.0 10.6 ug/L 106 69 - 131

Analyte

MS MS


Spike

Added

Sample

Result

Sample

Qualifier

%Rec.

Limits

Ethylbenzene 0.27 U 10.0 10.3 ug/L 103 77 - 130

Methyl tert-butyl ether 0.44 U 10.0 10.6 ug/L 106 66 - 130

m-Xylene & p-Xylene 0.36 U 10.0 10.9 ug/L 109 65 - 130

o-Xylene 0.50 U 10.0 10.2 ug/L 102 63 - 130

Toluene 0.24 U 10.0 10.8 ug/L 108 77 - 130


Surrogate

102

MS MS




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Method: 8260B - Volatile Organic Compounds (GC/MS) (Continued)

Client Sample ID: DW-1Lab Sample ID: 660-91201-1 DUMatrix: Water Prep Type: Total/NAAnalysis Batch: 204510

Benzene 0.25 U 0.25 U ug/L NC 30

Analyte

DU DU


Sample

Result

Sample

Qualifier LimitRPD

RPD

Ethylbenzene 0.27 U 0.27 U ug/L NC 30

Methyl tert-butyl ether 0.44 U 0.44 U ug/L NC 30

m-Xylene & p-Xylene 0.54 I 0.554 I ug/L 3 30

o-Xylene 0.50 U 0.50 U ug/L NC 30

Toluene 0.24 U 0.24 U ug/L NC 30

Xylenes, Total 0.54 I 0.554 I ug/L 3 30


Surrogate

100

DU DU




Method: 8270D SIM - Semivolatile Organic Compounds (GC/MS SIM)

Client Sample ID: Method BlankLab Sample ID: MB 660-204402/1-AMatrix: Water Prep Type: Total/NAAnalysis Batch: 204419 Prep Batch: 204402

PQL MDL


MB MB


0.081 U 0.0810.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Acenaphthylene

0.090 U 0.0900.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Anthracene

0.050 U 0.0500.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Benzo[a]anthracene

0.073 U 0.0730.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Benzo[a]pyrene

0.050 U 0.0500.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Benzo[b]fluoranthene

0.070 U 0.0700.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Benzo[g,h,i]perylene

0.083 U 0.0830.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Benzo[k]fluoranthene

0.068 U 0.0680.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Chrysene

0.077 U 0.0770.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Dibenz(a,h)anthracene

0.23 U 0.230.75 ug/L 12/08/18 10:15 12/10/18 07:45 1Fluoranthene

0.25 U 0.250.75 ug/L 12/08/18 10:15 12/10/18 07:45 1Fluorene

0.050 U 0.0500.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Indeno[1,2,3-cd]pyrene

0.25 U 0.250.75 ug/L 12/08/18 10:15 12/10/18 07:45 11-Methylnaphthalene

0.25 U 0.250.75 ug/L 12/08/18 10:15 12/10/18 07:45 12-Methylnaphthalene

1.3 U 1.34.0 ug/L 12/08/18 10:15 12/10/18 07:45 1Naphthalene

0.86 U 0.863.0 ug/L 12/08/18 10:15 12/10/18 07:45 1Phenanthrene

0.099 U 0.0990.50 ug/L 12/08/18 10:15 12/10/18 07:45 1Pyrene

Fluoranthene-d10 52 35 - 140 12/10/18 07:45 1

MB MB

Surrogate

12/08/18 10:15

Dil FacPrepared AnalyzedQualifier Limits%Recovery

39 12/08/18 10:15 12/10/18 07:45 12-methylnaphthalene-d10 19 - 110

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Method: 8270D SIM - Semivolatile Organic Compounds (GC/MS SIM) (Continued)

Client Sample ID: Lab Control SampleLab Sample ID: LCS 660-204402/2-AMatrix: Water Prep Type: Total/NAAnalysis Batch: 204419 Prep Batch: 204402

Acenaphthene 20.0 10.6 ug/L 53 19 - 110

Analyte

LCS LCS


Spike

Added

%Rec.

Limits

Acenaphthylene 20.0 10.6 ug/L 53 21 - 110

Anthracene 20.0 11.3 ug/L 56 27 - 110

Benzo[a]anthracene 20.0 11.6 ug/L 58 28 - 120

Benzo[a]pyrene 20.0 11.5 ug/L 57 36 - 114

Benzo[b]fluoranthene 20.0 11.2 ug/L 56 32 - 116

Benzo[g,h,i]perylene 20.0 13.0 ug/L 65 24 - 118

Benzo[k]fluoranthene 20.0 12.2 ug/L 61 31 - 111

Chrysene 20.0 11.9 ug/L 60 30 - 113

Dibenz(a,h)anthracene 20.0 13.2 ug/L 66 28 - 116

Fluoranthene 20.0 11.9 ug/L 59 23 - 110

Fluorene 20.0 11.1 ug/L 56 23 - 110

Indeno[1,2,3-cd]pyrene 20.0 14.2 ug/L 71 27 - 118

1-Methylnaphthalene 20.0 8.96 ug/L 45 19 - 110

2-Methylnaphthalene 20.0 9.16 ug/L 46 18 - 110

Naphthalene 20.0 9.55 ug/L 48 19 - 110

Phenanthrene 20.0 11.1 ug/L 55 25 - 110

Pyrene 20.0 9.73 ug/L 49 27 - 113

Fluoranthene-d10 35 - 140

Surrogate

59

LCS LCS


432-methylnaphthalene-d10 19 - 110

Client Sample ID: DW-1Lab Sample ID: 660-91201-1 MSMatrix: Water Prep Type: Total/NAAnalysis Batch: 204419 Prep Batch: 204402

Acenaphthene 0.24 U 17.9 8.42 ug/L 47 19 - 110

Analyte

MS MS


Spike

Added

Sample

Result

Sample

Qualifier

%Rec.

Limits

Acenaphthylene 0.077 U 17.9 8.36 ug/L 47 21 - 110

Anthracene 0.086 U 17.9 9.12 ug/L 51 27 - 110

Benzo[a]anthracene 0.048 U 17.9 8.90 ug/L 50 28 - 120

Benzo[a]pyrene 0.070 U 17.9 7.65 ug/L 43 36 - 114

Benzo[b]fluoranthene 0.048 U 17.9 7.98 ug/L 45 32 - 116

Benzo[g,h,i]perylene 0.067 U 17.9 5.28 ug/L 30 24 - 118

Benzo[k]fluoranthene 0.080 U 17.9 8.16 ug/L 46 31 - 111

Chrysene 0.065 U 17.9 9.08 ug/L 51 30 - 113

Dibenz(a,h)anthracene 0.074 U 17.9 7.99 ug/L 45 28 - 116

Fluoranthene 0.22 U 17.9 9.79 ug/L 55 23 - 110

Fluorene 0.24 U 17.9 8.72 ug/L 49 23 - 110

Indeno[1,2,3-cd]pyrene 0.048 U 17.9 7.13 ug/L 40 27 - 118

1-Methylnaphthalene 0.24 U 17.9 7.29 ug/L 41 19 - 110

2-Methylnaphthalene 0.24 U 17.9 7.51 ug/L 42 18 - 110

Naphthalene 1.3 U 17.9 7.75 ug/L 43 19 - 110

Phenanthrene 0.83 U 17.9 9.07 ug/L 51 25 - 110

Pyrene 0.095 U 17.9 7.78 ug/L 44 27 - 113

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Method: 8270D SIM - Semivolatile Organic Compounds (GC/MS SIM) (Continued)

Client Sample ID: DW-1Lab Sample ID: 660-91201-1 MSMatrix: Water Prep Type: Total/NAAnalysis Batch: 204419 Prep Batch: 204402


Surrogate

54

MS MS



Client Sample ID: MW-1Lab Sample ID: 660-91201-2 DUMatrix: Water Prep Type: Total/NAAnalysis Batch: 204419 Prep Batch: 204402

Acenaphthene 0.24 U 0.23 U ug/L NC 25

Analyte

DU DU


Sample

Result

Sample

Qualifier LimitRPD

RPD

Acenaphthylene 0.077 U 0.075 U ug/L NC 25

Anthracene 0.086 U 0.083 U ug/L NC 24

Benzo[a]anthracene 0.048 U 0.046 U ug/L NC 19

Benzo[a]pyrene 0.070 U 0.067 U ug/L NC 20

Benzo[b]fluoranthene 0.048 U 0.046 U ug/L NC 20

Benzo[g,h,i]perylene 0.067 U 0.064 U ug/L NC 21

Benzo[k]fluoranthene 0.080 U 0.077 U ug/L NC 20

Chrysene 0.065 U 0.063 U ug/L NC 20

Dibenz(a,h)anthracene 0.074 U 0.071 U ug/L NC 22

Fluoranthene 0.22 U 0.22 U ug/L NC 24

Fluorene 0.24 U 0.23 U ug/L NC 25

Indeno[1,2,3-cd]pyrene 0.048 U 0.046 U ug/L NC 21

1-Methylnaphthalene 0.24 U 0.23 U ug/L NC 25

2-Methylnaphthalene 0.24 U 0.23 U ug/L NC 30

Naphthalene 1.3 U 1.2 U ug/L NC 35

Phenanthrene 0.83 U 0.80 U ug/L NC 27

Pyrene 0.095 U 0.091 U ug/L NC 21


Surrogate

55

DU DU



Method: FL-PRO - Florida - Petroleum Range Organics (GC)

Client Sample ID: Method BlankLab Sample ID: MB 660-204451/1-AMatrix: Water Prep Type: Total/NAAnalysis Batch: 204455 Prep Batch: 204451

PQL MDL


(C8-C40)

0.34 U 1.0 0.34 mg/L 12/11/18 06:38 12/11/18 11:19 1

MB MB


o-Terphenyl 65 J1 82 - 142 12/11/18 11:19 1

MB MB

Surrogate

12/11/18 06:38

Dil FacPrepared AnalyzedQualifier Limits%Recovery

69 12/11/18 06:38 12/11/18 11:19 1n-C39 42 - 193

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Method: FL-PRO - Florida - Petroleum Range Organics (GC) (Continued)

Client Sample ID: Lab Control SampleLab Sample ID: LCS 660-204451/2-AMatrix: Water Prep Type: Total/NAAnalysis Batch: 204455 Prep Batch: 204451


(C8-C40)

6.80 3.74 mg/L 55 55 - 118

Analyte

LCS LCS


Spike

Added

%Rec.

Limits

o-Terphenyl J1 82 - 142

Surrogate

52

LCS LCS


69n-C39 42 - 193

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GC/MS VOA



Water 8260B660-91201-1 DW-1 Total/NA

Water 8260B660-91201-2 MW-1 Total/NA




Water 8260BMB 660-204510/6 Method Blank Total/NA

Water 8260BLCS 660-204510/4 Lab Control Sample Total/NA

Water 8260B660-91201-2 MS MW-1 Total/NA

Water 8260B660-91201-1 DU DW-1 Total/NA

GC/MS Semi VOA

Prep Batch: 204402


Water 3510C660-91201-1 DW-1 Total/NA

Water 3510C660-91201-2 MW-1 Total/NA




Water 3510CMB 660-204402/1-A Method Blank Total/NA

Water 3510CLCS 660-204402/2-A Lab Control Sample Total/NA

Water 3510C660-91201-1 MS DW-1 Total/NA

Water 3510C660-91201-2 DU MW-1 Total/NA



Water 8270D SIM 204402660-91201-1 DW-1 Total/NA

Water 8270D SIM 204402660-91201-2 MW-1 Total/NA

Water 8270D SIM 204402MB 660-204402/1-A Method Blank Total/NA

Water 8270D SIM 204402LCS 660-204402/2-A Lab Control Sample Total/NA

Water 8270D SIM 204402660-91201-1 MS DW-1 Total/NA

Water 8270D SIM 204402660-91201-2 DU MW-1 Total/NA






GC Semi VOA

Prep Batch: 204451


Water 3510C660-91201-1 DW-1 Total/NA





Water 3510CMB 660-204451/1-A Method Blank Total/NA

Water 3510CLCS 660-204451/2-A Lab Control Sample Total/NA

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GC Semi VOA (Continued)



Water FL-PRO 204451660-91201-1 DW-1 Total/NA

Water FL-PRO 204451660-91201-2 MW-1 Total/NA




Water FL-PRO 204451MB 660-204451/1-A Method Blank Total/NA

Water FL-PRO 204451LCS 660-204451/2-A Lab Control Sample Total/NA

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Lab ChronicleClient: HSW Engineering, Inc. TestAmerica Job ID: 660-91201-1Project/Site: Tupperware

Client Sample ID: DW-1 Lab Sample ID: 660-91201-1Matrix: WaterDate Collected: 12/06/18 11:21


Analysis 8260B 12/12/18 13:47 K1P1 204510 TAL TAM

Type

Batch Batch


Prepared

or Analyzed

Batch

Number

Dilution

Factor

Total/NA

Prep 3510C 204402 12/08/18 10:15 BKM TAL TAMTotal/NA

Analysis 8270D SIM 1 204419 12/10/18 08:25 MWJ TAL TAMTotal/NA

Prep 3510C 204451 12/11/18 06:38 EM TAL TAMTotal/NA

Analysis FL-PRO 1 204455 12/11/18 14:12 PC1 TAL TAMTotal/NA

Client Sample ID: MW-1 Lab Sample ID: 660-91201-2Matrix: WaterDate Collected: 12/06/18 10:26



Type

Batch Batch


Prepared

or Analyzed

Batch

Number

Dilution

Factor

Total/NA








Type

Batch Batch


Prepared

or Analyzed

Batch

Number

Dilution

Factor

Total/NA








Type

Batch Batch


Prepared

or Analyzed

Batch

Number

Dilution

Factor

Total/NA





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Lab ChronicleClient: HSW Engineering, Inc. TestAmerica Job ID: 660-91201-1Project/Site: Tupperware




Type

Batch Batch


Prepared

or Analyzed

Batch

Number

Dilution

Factor

Total/NA







TestAmerica Tampa

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Method SummaryTestAmerica Job ID: 660-91201-1Client: HSW Engineering, Inc.


Method Method Description LaboratoryProtocol

SW8468260B Volatile Organic Compounds (GC/MS) TAL TAM

SW8468270D SIM Semivolatile Organic Compounds (GC/MS SIM) TAL TAM

FL-DEPFL-PRO Florida - Petroleum Range Organics (GC) TAL TAM

SW8463510C Liquid-Liquid Extraction (Separatory Funnel) TAL TAM

SW8465030B Purge and Trap TAL TAM

Protocol References:

FL-DEP = State Of Florida Department Of Environmental Protection, Florida Administrative Code.

SW846 = "Test Methods For Evaluating Solid Waste, Physical/Chemical Methods", Third Edition, November 1986 And Its Updates.



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Accreditation/Certification SummaryClient: HSW Engineering, Inc. TestAmerica Job ID: 660-91201-1Project/Site: Tupperware

Laboratory: TestAmerica TampaThe accreditations/certifications listed below are applicable to this report.

Authority Program EPA Region Identification Number Expiration Date

Florida E842824NELAP 06-30-19

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Login Sample Receipt Checklist

Client: HSW Engineering, Inc. Job Number: 660-91201-1

Login Number: 91201

Question Answer Comment

Creator: Redding, Charles S

List Source: TestAmerica Tampa

List Number: 1

N/ARadioactivity wasn't checked or is </= background as measured by a survey meter.

TrueThe cooler's custody seal, if present, is intact.

TrueSample custody seals, if present, are intact.

TrueThe cooler or samples do not appear to have been compromised or tampered with.

TrueSamples were received on ice.

TrueCooler Temperature is acceptable.

TrueCooler Temperature is recorded.

TrueCOC is present.

TrueCOC is filled out in ink and legible.

TrueCOC is filled out with all pertinent information.

TrueIs the Field Sampler's name present on COC?

TrueThere are no discrepancies between the containers received and the COC.

TrueSamples are received within Holding Time (excluding tests with immediate HTs)

TrueSample containers have legible labels.

TrueContainers are not broken or leaking.

TrueSample collection date/times are provided.

TrueAppropriate sample containers are used.

TrueSample bottles are completely filled.

TrueSample Preservation Verified.

TrueThere is sufficient vol. for all requested analyses, incl. any requested MS/MSDs

TrueContainers requiring zero headspace have no headspace or bubble is <6mm (1/4").

TrueMultiphasic samples are not present.

TrueSamples do not require splitting or compositing.

N/AResidual Chlorine Checked.


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Documents

GENERATOR FUEL RELEASES MONITORING REPORT YEAR 1, …