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HomeMy WebLinkAbout22016 Quality Products VIMS Install Report_20220810 i S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report VIMS Installation Completion Report Quality Products Company 1515 S. Mint Street Charlotte, North Carolina Brownfields Project No. 22016-18-060 H&H Job No. LEH-004 Table of Contents 1.0 Introduction ..............................................................................................................................1 2.0 VIMS Installation and Influence Testing ..............................................................................4 2.1 VIMS Installation ...................................................................................................................4 2.2 VIMS Influence Testing .........................................................................................................6 3.0 Sub-Slab Soil Gas Assessment Activities ...............................................................................6 3.1 Sub-Slab Soil Gas Sampling...................................................................................................7 3.2 Sub-Slab Soil Gas Sampling Results ......................................................................................8 4.0 Summary and Conclusions ...................................................................................................10 List of Tables Table 1 Summary of Sub-Slab Soil Gas Analytical Data List of Figures Figure 1 Site Redevelopment Map ii S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report List of Appendices Appendix A Historical Data Summary Tables and Sample Location Maps Appendix B Geo-Seal EV20s Submittal Package Appendix C VIMS As-Built Drawings Appendix D Product Specification Sheets Appendix E VIMS Installation Photographs Appendix F Field Forms and Field Data Appendix G Laboratory Analytical Report Appendix H DEQ Risk Calculator Summary Pages 1 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report VIMS Installation Completion Report Quality Products Company 1515 S. Mint Street Charlotte, North Carolina Brownfields Project No. 22016-18-060 H&H Job No. LEH-004 1.0 Introduction On behalf of LEH NC Mint, LLC (the Prospective Developer or PD), Hart & Hickman, PC (H&H) has prepared this report to document vapor intrusion mitigation system (VIMS) installation, influence testing, and post-construction sub-slab soil gas assessment activities completed at a portion of the Quality Products Company Brownfields property (Brownfields Project No. 22016- 18-060) located at 1513 S. Mint Street and 1515 S. Mint Street in Charlotte, Mecklenburg County, North Carolina (Site or subject Site). The Site is comprised of three tax parcels (Mecklenburg County Parcel ID Nos. 11908315, 11908316, and 11908317) totaling approximately 0.53-acres and is currently developed with a single-story multi-tenant commercial building with an associated gravel-covered parking area. Proposed redevelopment plans for the Site include upfit and renovations for adaptive re-use of the existing building including spaces for a restaurant and a dentist office. The remainder of the Site will generally be covered with impervious surfaces including parking areas, sidewalks and exterior patios. Renovation of the 1515 S. Mint Street tenant space is currently in progress and occupancy for the space is anticipated in mid-August. The 1513 S. Mint Street tenant space has yet to begin upfit activities and a separate VIMS Installation Completion Report will be submitted for this space once installation and post-construction sampling are completed. A redevelopment Site plan is included in Figure 1. H&H previously completed vapor intrusion assessment activities at the Site to evaluate the potential for vapor intrusion prior to redevelopment. Results of previous vapor intrusion assessment activities are documented in our Limited Phase II Environmental Site Assessment (ESA) Report (dated March 2, 2018), and the Brownfields Assessment Report (dated October 22, 2 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report 2019). Tabular summary of the vapor intrusion assessment sample results and sample location maps are provided in Appendix A for ease of reference. In addition, H&H conducted a baseline mercury sub-slab soil gas assessment at the site to establish pre-mitigation baseline mercury vapor concentrations. Results of the mercury vapor assessment are documented in H&H’s Mercury Vapor Assessment Report (dated October 27, 2020). During the assessment, four sub-slab samples were collected. Mercury was not detected in three of the samples, and was detected at an estimated concentration at one location (SSV-3, 0.52 µg/m3) well below the DEQ DWM Non-Residential Vapor Intrusion Soil Gas Screening Level of 26 µg/m3. Based on these concentrations, H&H recommended no further assessment of mercury vapor on the site. DEQ found the findings in the above report to be in compliance with the Vapor Intrusion Mitigation Plan for the property in a Mercury Assessment Report Compliance Review dated December 3, 2020. The draft Brownfields Agreement for the Site includes the following land use restriction (LUR) No. 15.g.: No enclosed building may be constructed on the Brownfields Property and no existing building, defined as those depicted on the plat component of the Notice of Brownfields Property, may be occupied until DEQ determines in writing that: i. the building is or would be protection of the building’s users, public health and the environment from risk of vapor intrusion based on site assessment data or a site-specific risk assessment approved in writing by DEQ; or ii. the building is or would be sufficiently distant from the Brownfields Property’s groundwater and/or soil contamination based on assessment data approved in writing by DEQ that the building’s users, public health and the environment will be protected from risk from vapor intrusion related to said contamination; or iii. vapor mitigation measures are installed or implemented to the satisfaction of a professional engineer licensed in North Carolina, as evidenced by said engineer’s profession seal on a report that includes photographs and a description of installation and performance of said measures. Any design specification for vapor intrusion mitigation 3 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report measured shall be approved in writing by DEQ in advance of installation and/or implementation of said measures. The design specifications shall include methodology(ies) for demonstrating performance of said measures. In accordance with the LUR No. 15.g., the DEQ Brownfields Program approved Environmental Management Plan (EMP) dated October 29, 2019, and conversations with DEQ Brownfields personnel in a meeting held on October 7, 2019, the PD has elected to install a vapor intrusion mitigation system (VIMS) in the Site building. The DEQ-approved Vapor Intrusion Mitigation Plan (VIMP), dated August 3, 2020 includes installation of a passive sub-slab depressurization system in the 1513 and 1515 S. Mint Street building and post-installation sub-slab soil gas sampling. This report documents installation of the VIMS and post-construction sub-slab soil gas assessment for the 1515 S. Mint Street tenant space. A discussion of VIMS installation activities is provided in Section 2.0, a summary of sub-slab soil gas assessment activities is provided in Section 3.0, and summary and conclusions based on the results of the VIMS installation and soil gas assessment activities are provided in Section 4.0. 4 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report 2.0 VIMS Installation and Influence Testing 2.1 VIMS Installation The DEQ-approved VIMP includes installation of a 20-mil tape-sealed vapor barrier. On August 2, 2021, DEQ approved via email the installation of the spray-sealed vapor barrier Geo-Seal® EV20 manufactured by EPRO Services, Inc. (EPRO) in lieu of the vapor barrier specified in the approved VIMP. The vapor barrier was installed above the base course layer and beneath the concrete. Geo-Seal® EV20 is an ASTM-certified 20-mil, multi-layer, chemically resistant vapor barrier, designed to minimize the migration of volatile organic compounds (VOCs). The vapor barrier was installed per manufacturer installation instructions by S&H, a certified Geo-Seal® system installation contractor. Technical specifications and installation instructions obtained from EPRO for the Geo-Seal® EV20 vapor barrier and associated accessories are provided as Appendix B. Geo-Seal® EV20 was installed to cover the base course layer below the slab area of the proposed ground floor slab. The vapor barrier was attached/sealed to concrete and masonry surfaces of footings and existing walls (see Sheet VM-2). Geo-Seal CORE was used to attach/seal the vapor barrier to concrete or masonry surfaces. Seams within the building footprint have a minimum 6- inch overlap and were sealed with Geo-Seal CORE or Geo-Seal CORE Detail. Small puncture holes were sealed with Geo-Seal CORE or Geo-Seal CORE Detail. Larger holes, tears, or other damage were repaired using a patch of vapor barrier that overlaps the damaged area a minimum of 6” and have a minimum 60 mil application of Geo-Seal CORE in the seam overlap. The VIMP also includes installation of a passive mitigation system beneath the slab of the 1515 S. Mint Street building to reduce the potential for structural vapor intrusion into the non-residential space. The passive system includes a polyvinyl chloride (PVC) piping network below the slab of the building. Three vertical exhaust risers that extend to the roof of the building were connected to the sub-slab piping network. Empire Model TV04SS (stainless steel) wind-driven turbine fans were installed in-line with the risers on the roof of the building to enhance passive vapor mitigation and discharge sub-slab vapors to the atmosphere above the roof of the building. The VIMS layout 5 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report is shown in the as-built drawings (Sheets VM-1 and VM-2) included as Appendix C. Product specification sheets for the turbine fans and sub-slab piping are included in Appendix D. To enhance sub-slab vapor transmission and collection effectiveness, a uniform layer of high permeability stone (#57 stone) was installed directly below the concrete slab to allow for air movement beneath the entirety of the slab. Sub-slab vapor collection piping (4-inch diameter) was installed completely within the high permeability stone layer. The VIMP also includes three vacuum monitoring points (depicted on the as-built sheets in Appendix C). The vacuum monitoring points were used to measure the pressure differential between ambient air and the sub-slab during influence testing activities described below, and for collection of sub-slab soil gas samples. During installation of the VIMS in the 1515 S. Mint Street tenant space, H&H conducted inspections during various phases of construction to confirm the VIMS was installed in accordance with the DEQ-approved VIMP. Inspections were completed during the following phases of installation: • after installation of sub-slab horizontal collection piping system within the gravel base; • following placement and sealing of the vapor barrier, during smoke testing, and prior to pouring the concrete building slab; • after installation of vertical exhaust riser pipe and turbine fan installations; and • following utility upfit activities, inspection of the gravel layer and repaired barrier On June 15, 2022, following installation of the concrete slab, H&H was notified of sub-slab utilities requiring upfit which would involve penetrating the concrete slab and the vapor barrier. To ensure proper repairs to the VIMS, H&H conducted inspections throughout the repair process. An inspection of the gravel layer was conducted following the sub-slab upfit repairs to confirm that clean # 57 stone was present. The certified installers then repaired the Geo-Seal® EV20 vapor barrier per the manufacturer’s installation instructions. Following completed barrier repair activities, H&H conducted a final inspection of the vapor barrier to confirm that all areas were properly sealed to prevent preferential pathways through the slab. 6 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report Based upon periodic inspections completed during VIMS installation activities, the VIMS was installed in accordance with the DEQ-approved VIMP. VIMS details and specifications, and a VIMS as-built drawing which depicts the VIMS layout are included in Appendix C. A photographic log of installed VIMS components is provided in Appendix E. 2.2 VIMS Influence Testing On May 2, 2022, H&H completed influence testing for the system to evaluate sub-slab vacuum communication and to document sufficient depressurization can be obtained below the slab should the system be activated with electric fans in the future (if warranted). DEQ considers 4 Pascals (Pa), or 0.016 inches of water column (in-WC) differential pressure the minimum vacuum needed for an active depressurization system to effectively treat potential structural vapor intrusion. VIMS vacuum influence pilot testing included use of AMG Eagle Extreme electric fans to model an active depressurization system. Differential pressure measurements were collected at each vacuum monitoring point using a Dwyer series 475 Mark III Digital manometer (capable of measuring 0.001 in-WC or 0.25 Pa) to establish baseline conditions prior to operation of the AMG Eagle Extreme electric fans. Following collection of baseline differential pressure measurements, the electric fans were turned on and differential pressure measurements were collected at each monitoring point. Results of the influence tests indicated sub-slab vacuum measured at the monitoring points ranged from 0.170 in-WC to 0.338 in-WC in the tenant space, which demonstrates sufficient vacuum can be achieved below the slab of each of this portion of the building. The locations of the permanent monitoring points (denoted by MP nomenclature) are shown in VM-1 (Appendix C). The pilot test field data is included in Appendix F. 3.0 Sub-Slab Soil Gas Assessment Activities Following successful installation of the VIMS, H&H collected two sub-slab soil gas samples for laboratory analysis from the 1515 S. Mint Street tenant space. The sub-slab assessment activities were conducted in accordance with the DEQ-approved VIMP and the DEQ DWM Vapor Intrusion Guidance (Guidance) dated March 2018. 7 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report 3.1 Sub-Slab Soil Gas Sampling On June 1, 2022, H&H collected two sub-slab soil gas samples from permanent monitoring points in the 1515 S. Mint Street tenant space. The sampling was performed following VIMS installation activities and over two weeks after both completion of the riser piping and installation of the wind- driven turbine fans. The sub-slab soil gas samples were collected from permanent monitoring point locations MP-1 and MP-3, as shown on VM-1 in Appendix C. One duplicate sub-slab soil gas sample (MP-DUP) was collected for quality assurance/quality control (QA/QC) purposes from the MP-3 parent location during the sampling event. The duplicate sample was collected utilizing a laboratory supplied stainless-steel sampling “T” which allows for the simultaneous collection of two sub-slab soil gas samples from a single location. To collect the sub-slab soil gas samples, Teflon sample tubing was secured to a 2-inch expandable well cap with a sampling port that was secured onto the PVC monitoring point. The tubing was connected to an airflow regulator and laboratory-supplied batch-certified 1.4-liter stainless steel Summa canister. The air flow regulator was preset by the laboratory to collect a soil gas sample over a period of 10 minutes. Prior to sample collection, H&H conducted a leak test at each monitoring point by placing a shroud around the monitoring point, expandable well cap, and sampling train including the Summa canister. The air within the shroud was flooded with helium gas and concentrations were measured with a calibrated helium detector. Helium concentrations within the shroud were maintained between approximately 15.8% and 16.9%. A GilAir vacuum pump was connected to the sample tubing outside of the shroud and used to purge a minimum of three volumes (monitoring point and sample train) of soil gas into a Tedlar® bag at each sampling point. The helium gas detector was used to measure helium concentrations within the Tedlar bag sample to confirm helium concentrations in the sample were less than 10% of that measured within the shroud. Results of the helium leak checks indicate that short-circuiting at the monitoring points or within the sampling train were not present. Soil gas sampling field forms completed by sampling personnel are included in Appendix F. 8 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report Following successful leak checks, the air flow regulators were opened to allow collection of the sub-slab soil gas samples. Vacuum in the Summa canisters was monitored during the sampling event to confirm adequate sample volume was collected at each monitoring point location. Upon completion of sample collection, the air flow regulator was closed to the Summa canister. The canisters were labeled with the sample identification, beginning and ending times, pressure measurements, and the requested analysis. The canisters were then placed in laboratory supplied shipping containers and delivered to Waypoint Analytical Laboratories (Waypoint) under standard chain of custody protocols for analysis of volatile organic compounds (VOCs) by EPA Method TO-15. 3.2 Sub-Slab Soil Gas Sampling Results The sub-slab soil gas sample analytical results are summarized in Table 1. The results were compared to the DEQ DWM Residential Vapor Intrusion Sub-Slab and Exterior Soil Gas Screening Levels (SGSLs) dated January 2022. The laboratory analytical report with chain of custody record is provided as Appendix G. The monitoring point soil gas sample analytical results indicate that several compounds were detected at concentrations above laboratory method detection limits (MDLs) in each sample, but below the DEQ DWM Residential and Non-Residential Vapor Intrusion SGSLs. Naphthalene was detected at concentrations above DEQ DWM Residential Vapor Intrusion SGSLs but below Non- Residential Vapor Intrusion SGSLs in samples MP-3 and MP-DUP. Trichloroethene (TCE) was detected at concentrations above DEQ DWM Residential Vapor Intrusion SGSLs but below Non- Residential Vapor Intrusion SGSLs in sample MP-1. TCE was also detected at concentrations above DEQ DWM Non-Residential Vapor Intrusion SGSLs in samples MP-3 and MP-DUP. No other compounds were detected above DEQ DWM Residential or Non-Residential Vapor Intrusion SGSLs. The DEQ DWM Vapor Intrusion SGSLs are very conservative and based on a target carcinogenic risk (TCR) for potential carcinogenic risks of 1 x 10-6 and a hazard quotient (HQ) of 0.2 for potential non-carcinogenic risks. The DEQ and EPA acceptable risk level for potential 9 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report carcinogenic risks is a cumulative lifetime incremental cancer risk (LICR) of 1 x 10-4 or less and the acceptable level for non-carcinogenic risks is a cumulative hazard index (HI) of 1 or less. The HI is the sum of HQs for each target analyte. H&H utilized the DEQ Risk Calculator (January 2022) to confirm that there are no potential vapor intrusion risks at unacceptable levels. H&H modeled a worst-case scenario by using the highest concentrations of any compound detected below the slab in the 1515 S. Mint Street tenant space based on a non-residential use scenario to conservatively evaluate potential vapor intrusion risks. The calculated cumulative LICR and HI values are provided in Table 1, and a copy of the completed DEQ Risk Calculator is provided in Appendix H. As shown in Table 1, results of the worst-case risk calculations indicate a calculated cumulative LICR of 1.9 x 10-6 and a HI value of 0.38. The calculated cumulative residential use LICR and HI values are within the DEQ and EPA acceptable levels. These risk calculator results confirm that compound concentrations detected below the slab do not pose vapor intrusion risks at unacceptable levels within the 1515 S. Mint Street tenant space with a passive VIMS. 10 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report 4.0 Summary and Conclusions Upfit of the 1515 S. Mint Street tenant space has been completed at the Quality Products Company Brownfields property (Brownfields Project No. 22016-18-060) located in Charlotte, Mecklenburg County. The 1513 S. Mint Street tenant space has not yet been redeveloped and a separate report will be submitted to document installation of the VIMS in this space once complete. During redevelopment of the space, H&H conducted VIMS installation inspections to confirm the system was installed as designed and completed post-installation sub-slab soil gas sampling activities to evaluate efficacy of the system. The VIMS installation inspections and post- installation sampling activities were completed in general accordance with the DEQ-approved VIMP. A brief summary of the VIMS installation and post-installation soil gas assessment activities is provided below. VIMS Installation VIMS installation has been completed for 1515 S. Mint Street tenant space and consists of a passive sub-slab depressurization system with vertical extraction piping to the roof connected to wind-driven turbine fans. During installation of the VIMS, H&H personnel, under direction of a North Carolina licensed Professional Engineer, conducted inspections during each stage of installation. Results of the installation inspections indicate that the VIMS was successfully installed in general accordance with the DEQ-approved VIMP. Influence testing for the space confirmed that adequate vacuum is obtainable for the purpose of active vapor mitigation (if warranted in the future). Sub-Slab Vacuum H&H completed vacuum influence pilot testing in May 2022 following installation of the VIMS piping network, but prior to installation of the wind-driven fans. Vacuum measurements collected during the pilot testing activities (range from 0.170 in-WC to 0.338 in-WC) indicated that vacuum communication beneath the slab was achieved with adequate differential pressure levels. 11 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Report Sub-Slab Soil Gas Assessment Following installation of the VIMS and completion of interior construction activities, H&H collected three sub-slab soil gas samples from the 1515 S. Mint Street tenant space to evaluate potential vapor intrusion risks. Laboratory analytical results of the sub-slab soil gas samples indicate that naphthalene and TCE were detected at concentrations above the DEQ DWM Residential Vapor Intrusion SGSLs in samples MP-3/DUP and MP-1, respectively. TCE was also detected above DEQ DWM Non-Residential Vapor Intrusion SGSLs in samples MP-3/DUP. H&H utilized the DEQ Risk Calculator (January 2022) to calculate the cumulative carcinogenic and non-carcinogenic risks under a hypothetical worst-case residential-use scenario by utilizing the highest concentration of each compound detected in the tenant space sub-slab soil gas samples. Although TCE was detected above DEQ DWM Non-Residential Vapor Intrusion SGSLs in samples MP-3/DUP, hypothetical worst-case non-residential use risk calculator results indicate a calculated cumulative LICR of 1.9 x 10-6 and a calculated cumulative HI of 0.38. The calculated cumulative residential use LICR and HI values are within the DEQ and EPA acceptable levels. Based on the VIMS installation inspections, influence testing, and post-installation sub-slab soil gas sampling results, the VIMS is effectively mitigating potential vapor intrusion risks at the Site. The sub-slab soil gas to indoor air risk calculator results confirm that risks are below acceptable levels. Table 1 Summary of Sub-Slab Soil Gas Analytical Data Quality Products Co. 1515 South Mint Street Charlotte, North Carolina Brownfields Project No. 22016-18-060 H&H Job No. Project #LEH-004 Sample ID MP-1 Date Units VOCs (TO-15) Acetone 1380 694 701 NE NE Carbon Disulfide 7.72 J <0.608 2.71 J 4,900 61,000Cyclohexane<1.61 164 169 42,000 530,000 Ethyl Acetate <1.36 27.3 <1.36 490 6,100 Ethylbenzene 9.55 J 10.3 J 10.7 J 37 490 4-Ethyltoluene <1.28 5.06 J 4.92 J NE NEHeptane<1.43 49.3 54.1 2,800 35,000 Isopropyl Alchohol <1.39 24.3 J <1.39 1,400 18,000 Methyl Ethyl Ketone (MEK)1950 4050 3680 35,000 440,000 Methylene Chloride 5.63 J <4.89 <4.89 3,400 53,000Naphthalene<1.83 31.5 31.2 2.8 36 Styrene 33.1 24.9 25.2 7,000 88,000 Tetrachloroethene 9.36 J 12.4 J 12.1 J 280 3,500 Tetrahydrofuran 534 876 777 14,000 180,000Toluene16.8 J 14.1 J 13.9 J 35,000 440,000 Trichloroethene 83.5 302 306 14 180 Trichlorofluoromethane <1.30 5.84 J <1.30 NE NE 1,2,4-Trimethylbenzene 12.3 J 19.7 J 19.6 J 420 5,300 1,3,5-Trimethylbenzene <2.36 5.95 J 6.39 J 420 5,300 Vinyl Chloride <1.27 <1.27 <1.27 5.6 280 o-Xylene 8.9 J 9.03 J 9.21 J 700 8,800mp-Xylene 19.4 J 19.9 J 18.6 J 700 8,800Xylene (Total)28.3J 28.9 J 27.8 J 700 8,800 DEQ Cumulative Risk Calculator(2)Acceptable Risk Levels Acceptable Risk Levels Carcinogenic Risk (LICR)<1 x 10-4 <1 x 10-4 Non-Carcinogenic Hazard Index (HI)<1.0 <0.2 Notes: 1) NC Department of Environmental Quality (DEQ) Division of Waste Management (DWM) Vapor Intrusion Sub-slab and Exterior Soil Gas Screening Levels (SGSLs) dated January 2022 and based upon TCR = 1 x 10-6 and THQ = 0.2.2) NC DEQ DWM Cumulative Risk Calculator dated January 2022. Compound concentrations are reported in micrograms per cubic meter (μg/m3) Compound concentrations are reported to the laboratory method detection limits. Only those compounds detected in at least one sample, and select chlorinated solvents, are shown in the table above. Laboratory analytical method shown in parentheses.Bold indicates compound concentration exceeds Residential SGSLs. Underline indicates compound concentration exceeds Non-Residential SGSLs. VOCs = Volatile Organic Compounds; NE = Not Established. TCR = Target Cancer Risk; THQ = Target Hazard Quotient. LICR = Lifetime Incremental Cancer Risk; HI = Hazard Index. Cumulative LICR and HI calculated using the residential worst-case scenario for each building and compared to DEQ and EPA acceptable risk levels for carcinogenic and non carcinogenic risks. J = Compound was detected above the laboratory method detection limit, but below the laboratory reporting limit resulting in a laboratory estimated concentration. Non-Residential SGSLs(1) 1.9 x 10-6 0.38 Non-Residential Worst Case Residential SGSLs(1) µg/m3 6/1/2022 MP-3 / MP-DUP https://harthick.sharepoint.com/sites/MasterFiles-1/Shared Documents/AAA-Master Projects/Lischerong Enterprises and Holdings (LEH)/S. Mint St/1513-1521 Assessments/VIMS Install Report/Tables/Sub Slab Sampling Data 7/29/2022 Table 1 (Page 1 of 1) Hart & Hickman, PC CCDNE S SDNEBBCCCCCBBOOOBBBBOOOOBBBUILDING 15375,328 SFFFE: 719.12BUILDING 15294,036 SFFFE: 721.41FFE: 723.54BUILDING 15257,235 SFFFE: 723.00FFE: 725.00BUILDING 15156,788 SFFFE: 725.27BUILDING 15135,248 SFFFE: 725.27725722724 72 3 726 729 728720717721 724 720719723 724725 726 719SOUTH MINT STREETWESTWOOD AVENUE720721 722 7237237 2 0 718719 721722723723 725725 723723723 724724 725 726 727 PROP. CONCRETE PAVEMENTTO BE FLUSH WITH EX.CONCRETE PAVEMENT, TYP.2% MAXIMUM CROSSSLOPE ON CROSSWALK.DUMPSTER PAD SHALLSLOPE TOWARDS ACCESSDRIVE AT 2.00% MAX SLOPE.SLOPE FOR HANDICAP ACCESSIBLESPACES SHALL NOT EXCEED 2% INANY DIRECTION, TYP.2:1 SLOPE MAX.BACKFLOW PREVENTERAREA SHALL BE GRADEDAT 2% MAX SLOPE.CONTRACTOR SHALL SLOPE CURB ANDGUTTER TO ENSURE POSITIVE DRAINAGETO DOWNSTREAM INLETS, TYP.PROP. DI-1RIM: 722.50INV OUT: 719.00 (MH-1)38.19 LF of 15"RCP @ 4.11%PROP. MH-1RIM: 719.37INV IN: 717.43 (DI-1)2% MAXIMUM CROSSSLOPE ON CROSSWALK.2% MAXIMUM CROSSSLOPE ON CROSSWALK.BACKFLOW PREVENTERAREA SHALL BE GRADEDAT 2% MAX SLOPE.DUMPSTER PAD SHALLSLOPE TOWARDS ACCESSDRIVE AT 2.00% MAX SLOPE.SLOPE FOR HANDICAP ACCESSIBLESPACES SHALL NOT EXCEED 2% INANY DIRECTION, TYP.EX: 718.20EX: 722.17EX: 722.56EX: 718.56EX: 723.20EX: 722.83EX: 723.17EX: 724.58EX: 727.98EX: 726.39EX: 726.97EX: 725.14EX: 722.92719.07719.07719.47719.12718.99719.67EX: 719.28719.87719.59719.61719.66720.92722.80723.25723.33723.50723.50723.50723.41722.49723.77723.78723.43EX: 723.15EX: 722.67EX: 720.37EX: 723.16721.40EX: 721.81721.41720.66719.24719.19719.15719.12719.12EX: 723.65EX: 723.45EX: 722.89EX: 722.02EX: 721.65EX: 721.62EX: 722.26EX: 721.16EX: 723.40EX: 723.94EX: 724.51EX: 724.80EX: 724.98722.81723.21723.00723.10723.00724.85725.00725.00724.90725.00724.95724.81725.42725.41725.54725.54725.21725.37725.53725.36EX: 719.15EX: 718.91EX: 718.79EX: 718.73EX: 718.99719.16719.22719.78725.27725.27724.98724.86725.26725.26BW: 725.27TW: 727.28725.27725.17724.96725.19725.40725.16725.40725.20724.11723.92723.73724.40723.87723.91723.97723.44723.70723.30722.73723.20LP: 722.65LP: 722.70CONTRACTOR SHALLENSURE SMOOTH VERTICALCURVES ARE USED AT ALLHIGH AND LOW POINTS.TYPICAL IN ALL AREAS.PROP. ASPHALT PAVEMENT TO BEFLUSH WITH EX. CONCRETE PAVEMENTALONG CLEAN SAWCUT, TYP.720.06PROP. BUILDING STAIRS, SEEARCHITECTURAL DETAILSTC: 723.08BC: 722.58TC: 721.22BC: 720.72stamp / seal:REVISIONSDATENO.DESCRIPTIONDisclaimer ©2019:Information contained in this document is the property of Bloc Design, PLLC.and the project client listed on this document.The reproduction, copying, and other use without written consent isprohibited and may be subject to legal action to the fullest extent possible.N.T.S.NS. Mint StreetRedevelopment1513, 1515, 1525, 1529 &1537 S. Mint St.Charlotte, NC 28203CHECKED BY:MPIC:CCB11/22/19DATE:DRAWN BY:PROJECT NUMBER:00658.01SCALE:TITLE:SHEET NO.:VICINITY MAPSURVEY DISCLAIMERTOPOGRAPHIC SURVEY DATED AUGUST 25, 2019 PROVIDED BY R.B.PHARR & ASSOSIATES, P.A., 420 HAWTHORNE LANE, CHARLOTTE,N.C. 28204. PHONE: 704.376.2186P-1007C-390S:\Projects\00658 Mint St Redevelopment\Plans\Production DWGs\00658_CG-100 - Grading and Drainage Plan.dwg, 11/25/2019 8:37:54 AM, nic vesely, Bloc DesignISSUED FOR CONSTRUCTIONMANAGING PARTNER (PE): DATE:MANAGING PARTNER (LA):DATE:CIVIL ENGINEER/DESIGNER:DATE:LANDS. ARCHITECT/DESIGNER:DATE:2923 S. Tryon Street, Suite 320Charlotte, NC 28203phone: 704-940-2883www.bloc-nc.comlandscape architecture I planning I civil engineering1.CONTRACTOR IS RESPONSIBLE FOR PLACEMENT OF ALL BARRICADES,SIGNAGE, FLAGGERS, SHORING, ETC., TO ENSURE THE SAFETY OF WORKERSAND THE PUBLIC.2.ALL PAVEMENT CUTS SHALL BE REPLACED ACCORDING TO NORTH CAROLINADEPARTMENT OF TRANSPORTATION AND CHARLOTTE WATER.PLAN NORTHTRUE NORTHNNLischerongDevelopment Group310 Arlington AveSuite #402-ACharlotte, NC 28203704-750-0368lischerongdevelopment.comREEENGINSEFOR P LANOISSEAL35711EXISTING CONTOURPROPOSED INDEX CONTOURPROPOSED SPOT ELEVATIONPROPOSED HIGH POINTHPSYMBOLEXISTING SPOT ELEVATIONPROPOSED DRAINAGE FLOW PATTERN625.00625.00LEGENDDETAILPROPOSED INTERIOR CONTOUR625624-/--/--/--/--/--/--/-GRADING NOTES:1.ANY GRADING BEYOND THE DENUDED LIMITS INDICATED ON THE CONSTRUCTIONDOCUMENTS IS A VIOLATION AND IS SUBJECT TO A FINE.2.GRADING MORE THAN ONE ACRE WITHOUT AN APPROVED EROSION CONTROL PLANIS A VIOLATION AND IS SUBJECT TO A FINE.3.CONTRACTOR SHALL MAINTAIN 0.50% SLOPE MINIMUM ON THE CURB AND GUTTERS4.THE AUTHORITIES HAVING JURISDICTION HAVE NOT REVIEWED AND ASSUME NORESPONSIBILITY FOR THE STRUCTURAL STABILITY OF ANY EXISTING RETAININGWALLS ONSITE.5.ALL PAVED AREAS (SIDEWALKS, PLAZAS, PATIOS, ETC.) SHALL SLOPE AWAY FROMTHE BUILDING AT 2.00% MINIMUM.6.SPOT GRADE ELEVATIONS ARE TAKEN AT FINISHED GRADE (ASPHALT, CONCRETE,TURF) UNLESS OTHERWISE NOTED.7.TC = TOP OF CURB ELEVATIONBC = BOTTOM OF CURB ELEVATION (GUTTER FLOW LINE)HP = HIGH POINTLP = LOW POINTEX = EXISTING SPOT ELEVATIONSCALE:020'40'10'1"= 20'PROPOSED STORM DRAINAGEPROPOSED CATCH BASIN INLETCBNCDOT 300.01NCDOT 840.02CCBNTVDSK1"=20'GRADING & DRAINAGE PLANCG-101 SSSSSSSDSDSDEWWWEEEEE WSDSDSDSSSSSSWGEGES33o16'59"E 150.03'S33o17'59"E 150.04'S33o18'53"E 150.04'N33o16'34"W 150.04N33o16'36"W 150.04'(M)50.08' (M)49.86 (M)50.01 (M)50.01' (M)N56o40'13"E 199.96' (T) (M)50.08' (M)49.87 (M)49.97' (M)49.97' (M)S56o40'07E 199.99' (T) (M)20' FRONT SETBACK10' SIDE SETBACKTAX PARCEL 119-083-01LOT 6, BLOCK 4WESTWOOD PARKM.B. 332, PG. 361MARTHA F. GAINEYD.B. 25356, PG.701SOUTH MINT STREETWESTWOOD AVENUETAX PARCEL 19-083-01LOT 8, BLOCK 4WESTWOOD PARKM.B. 332, PG. 361BEVERLY WELCHD.B. 1588, PG. 43110' ALLEYM.B.332, PG. 36110' ALLEYM.B.332, PG. 361EXISTING SINGLE STORYU SHELL BUILDING -PROPOSED BUILD-OUT PROPOSED METAL LANDING & EGRESS STAIR FROM NEW MEZZININE IN SHELL BUILDING TO EX'G COURTYARD BELOW.ASHPALT PARKING LOTEGRESS PATH OF TRAVELTAX PARCEL 119-083-102LOT 5, BLOCK 4WESTWOOD PARKM.B. 332, PG. 361MARTHA F GAINEYD.B. 25356, PG. 701S46o25'35"E 32.00'N56o40'07"E 99.94 (M)C1-485' RADIUS; 45.78' ARC LENGTH; N35o59'07"W CHORD BEARING ; 45.77' CHORD LENGTH N35o09'03"W 99.94 (M)S33o16'34"E 199.99' (T) (M)S56118'0"W 155.50' (M)20' SETBACK10' SETBACKEXISTING SINGLE-STORY BUILDINGEXISTING SINGLE-STORY BUILDINGEGRESS PATH OF TRAVEL20' - 0 1/8"5' - 9 1/8"5' - 2"10' - 1 1/2"17' - 6 1/4"17' - 8 11/16"10' - 6"EXISTING COURTYARD6' TALL WOOD FENCEPROPOSED ADDITIONPROJECT BUILDINGPROJECT ADDITIONEXISTING BUILDINGSPROJECT PARKINGLEGEND1513 SOUTH MINT STREET1515 SOUTH MINT STREETDUMPSTERNFile:Date:PROJECT NO.SCALEISSUED:DATE: FOR:SCHEMATIC DESIGNDESIGN DEVELOPMENTBIDDINGRELEASED FOR CONSTRUCTION© CopyrightDesign BIM Group LLCAll rights reserved.ADDENDUM #1Design BIM Group LLC2615 George Busbee PkwySuite 11 - 357Kennesaw, Georgia 30144-1981Phone: 770.855.8059REVISIONS:NO: DESCRIPTION:DATE:PROJECT NAME:CLIENT:Robert Herring Architect778 Registry Run NWKennesaw, Georgia 30152Phone: 404.376.8605C:\Users\deanh\Documents\2-12-2022_2161_Hospitality Build Services_Trio_CF_AR_dhogencampXZBQQ.rvt2/15/2022 10:46:21 AM1" = 20'-0"ARCHITECTURALSITE PLAN2161A03090% SUBMITTAL- Not Released for Construction2022Hospitality Build ServicesTrio Concert Hall1513 S. Mint StreetCharlotte, NC 28203SCALE:1" = 20'-0"A0301ARCHITECTURAL SITE PLAN Appendix A Historical Data Summary Tables and Sample Location Maps Table 1 (Page 1 of 2)Summary of Sub-Slab Soil Vapor Analytical Data1515-1521 South Mint StreetCharlotte, North CarolinaH&H Job No. LEH.004AcetoneBenzene2-Butanone (MEK)Carbon DisulfideChlorobenzeneChloroform1,3-Dichlorobenzene1,4-DichlorobenzeneDichlorodifluoromethane (Freon 12)1,1-Dichloroethane1,1-Dichloroethylenecis-1,2-Dichloroethylenetrans-1,2-DichloroethyleneEthanolEthylbenzene4-EthyltolueneHeptaneSSV-1 QPC finished product shipping 8 4 01/26/18600 7.8 56 J 56 J<5.8728.4 J<8.3 <7.5140<5.8260 550 330 6.3 J<6.4430SSV-2 Former die stamping room 6 2-3 01/26/18200<4.118 J<4.2 <5.848<7.2 <8.3 <7.5 <5.7 <5.88.4<6.0150<5.8 <6.4 <5.4SSV-3 Former machine shop 8 4 01/26/18340 4.7 44 J 60 4.4 J<3.6 <3.6 <4.2 <3.734<2.980 46 120<2.97.0 3.8 JSSV-4 QPC finishing room 8 3 01/26/18240 1.0 22 J<0.42 <0.58 <0.712.4 1.7 2.3<0.578.1<0.54 <0.60140 0.73 J<0.640.92220,000 120 35,000 4,900 350 41 NE 85 700 580 1,400 NE NE NE 370 NE 2,8002,700,000 1,600 440,000 61,000 4,400 530 NE 1,100 8,800 7,700 18,000 NE NE NE 4,900 NE 35,000Notes: 1) North Carolina Department of Environmental Quality (DEQ) Division of Waste Management (DWM) Residential and Non-Residential Sub-Slab and Exterior Soil Gas Screening Levels (SGSLs) dated October 2017Only compounds detected in at least one sample are shownBold indicates concentration exceeds Residential SGSLUnderline indicates concentration exceeds Non-Residential SGSLJ = Detected concentration is above the laboratory method detection limit, but below the laboratory reporting limit. Therefore, the reported concentration is an estimated value.Z = compound fails the United States Environmental Protection Agency method requirement of 70-130% recovery, but passes the Con-Test Laboratory internal standard of 50-150%.µg/m3 = micrograms per cubic meter; NE = not established; in = inchesQPC = Quality Products Company, Inc., a metal stamping business that operated on the Site from approximately the 1950s until the 1980s Residential Soil Gas Screening Level1 Non-Residential Soil Gas Screening Level1Sample IDSample LocationSampling Date Analytical MethodTO-15Sample Depth (in)Slab Thickness (in)µg/m³File: S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint Street\Phase II\Tables\SubSlab_SoilVapor_TableDate: 2/9/2018Table 1 (Page 1 of 2)Hart & Hickman, PC Table 1 (Page 2 of 2)Summary of Sub-Slab Soil Vapor Analytical Data1515-1521 South Mint StreetCharlotte, North CarolinaH&H Job No. LEH.004Hexane2-Hexanone (MBK)Isopropanol4-Methyl-2-pentanone (MIBK)NaphthalenePropeneTetrachloroethylene (PCE)TetrahydrofuranToluene1,1,1-TrichloroethaneTrichloroethylene (TCE)Trichlorofluoromethane (Freon 11)1,2,4-Trimethylbenzene1,3,5-TrimethylbenzeneVinyl AcetateTotal XylenesSSV-1 QPC finished product shipping 8 4 01/26/18320<4.9120 J<7.0 <9.176 J 50 17 22 1,5007,700<9.429 9.4 J<4.335SSV-2 QPC die stamping room 6 2-3 01/26/18<12 <4.945 J<7.0 <9.114 J 21 4.7 J 5.3 J 5412,000<9.4 <6.4 <6.7 <4.3<16.4SSV-3 QPC machine shop 8 4 01/26/18<6.2 <2.456 J<3.522 Z22 J<4.18.8 8.2 18160<4.773 34<2.117.8SSV-4 QPC finishing room 8 3 01/26/18<1.20.84 53 1.4 1.5 Z<1.12904.5 2.6 880381.2 J 3.6<0.671.6 J3.74,900 210 1,400 21,000 21 21,000 280 14,000 35,000 35,000 14 NE 420 420 1,400 70061,000 2,600 18,000 260,000 260 260,000 3,500 180,000 440,000 440,000 180 NE 5,300 5,300 18,000 8,800Notes: 1) North Carolina Department of Environmental Quality (DEQ) Division of Waste Management (DWM) Residential and Non-Residential Sub-Slab and Exterior Soil Gas Screening Levels (SGSLs) dated October 2017Only compounds detected in at least one sample are shownBold indicates concentration exceeds Residential SGSLUnderline indicates concentration exceeds Non-Residential SGSLJ = Detected concentration is above the laboratory method detection limit, but below the laboratory reporting limit. Therefore, the reported concentration is an estimated value.Z = compound fails the United States Environmental Protection Agency method requirement of 70-130% recovery, but passes the Con-Test Laboratory internal standard of 50-150%.µg/m3 = micrograms per cubic meter; NE = not established; in = inchesQPC = Quality Products Company, Inc., a metal stamping business that operated on the Site from approximately the 1950s until the 1980sTO-15 Residential Soil Gas Screening Level1 Non-Residential Soil Gas Screening Level1µg/m³Sample IDSample LocationSample Depth (in)Slab Thickness (in)Sampling Date Analytical MethodFile: S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint Street\Phase II\Tables\SubSlab_SoilVapor_TableDate: 2/9/2018Table 1 (Page 2 of 2)Hart & Hickman, PC Table 4Summary of Indoor Air Analytical ResultsQuality Products Company1513, 1515 and 1521 South Mint StreetCharlotte, North CarolinaH&H Job No. LEH.004Sample IDIAS-1IAS-3 IAS-4 BKG-1Sample LocationPirtek Lobby/ShowroomRCI Equipment/Storage AreaPirtek WorkshopWestern Property BoundarySampling Date 12/19/18 12/19/18 12/19/18 12/19/18UnitsVOCs (TO-15)Acetone1,900 290 290 350 4,100 296,500 27,000Benzene2.92.32.33.13.91.53.6162-Butanone (MEK)<0.167.4 J8.0 J9.6 J1102.9 J1,0004,400Carbon Disulfide0.72 J<0.21<0.21<0.21<0.43<0.075150610Carbon Tetrachloride<0.0720.33 J0.40 J0.53 J<0.410.454.720Chloroform<0.0640.36 J0.40 J0.562.10.11 J1.25.3Chloromethane<0.0491.51.92.03.51.51979Cyclohexane<0.0864.95.25.61300.761,3005,300Dichlorodifluoromethane (Freon 12)1.63.03.12.92.72.021881,2-Dichloroethane<0.054<0.15<0.15<0.15<0.310.080 J1.14.7Ethanol1703940469312NENEEthylbenzene3.33.63.74.65.10.6911494-Ethyltoluene4.83.23.34.55.20.80NENEHeptane2201616135002.883 350Hexane195.2 J5.6 J8.8 J432.7 J150610Isopropanol<0.114.1 J, L-034.4 J, L-035.5 J, L-034.5 J, L-034.3 L-0342180Methylene Chloride382.2 J3.0 J8.81.3 J131305304-Methyl-2-pentanone (MIBK)4.3<0.20<0.20<0.202.9<0.0696302,600Naphthalene2.51.01.21.5<0.800.250.632.6Styrene1.20.35 J0.460.60<0.530.42210880Tetrachloroethylene (PCE)1.8<0.38<0.38<0.381.2 J0.358.335Tetrahydrofuran<0.0692.42.74.5<0.390.244201,800Toluene1,6001301301103,000311,0004,400Trichloroethylene (TCE)4.415165.01.6<0.0760.42 1.8Trichlorofluoromethane (Freon 11)1.92.2 J2.32.1 J1.8 J1.8NENE1,1,2-Trichloro-1,2,2-trifluoroethane (Freon 113)0.68 J0.48 J0.48 J<0.46<0.930.67 J1,0004,4001,2,4-Trimethylbenzene6.83.94.15.56.80.8813531,3,5-Trimethylbenzene1.70.991.11.41.60.251353m&p-Xylene12141420192.32188o-Xylene4.95.76.07.86.70.932188Notes: 1) North Carolina Department of Environmental Quality (DEQ) Division of Waste Management (DWM) Indoor Air Screening Levels (IASLs) dated Feburary 2018Only compounds detected in at least one sample are shownLaboratory analytical method shown in parentheses.Bold indicates concentration exceeds Residential IASLUnderline indicates concentration exceeds Non-Residential IASLJ = compound detected above the laboratory method detection limit, but below the laboratory reporting limit resulting in an estimated concentration.L-03 = Laboratory fortified blank/laboratory control sample recovery is outside of control limits. Reported value for this compound is likely to be biased on the low side.µg/m3 = micrograms per cubic meter; NE = not establishedµg/m3IAS-2 (DUP-1 ) Residential IASL1 Non-Residential IASL1RCI Demolition Office Space12/19/18File: S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint Street\1513-1521 Assessments\Brownfields Assessment\Report\Tables\Indoor Air_Table - amDate: 10/21/2019Table 4 (Page 1 of 1)Hart & Hickman, PC PIRTEK SOUTHEND SSV-1 SSV-4 SSV-3 SSV-2 SB-1RCI DEMOL I T IONVACAN T REVISION NO. 0DATE: 10-17-19 LEGEND BROWNFIELDS PROPERTY BOUNDARY FORMER BUILDING FOOTPRINT PREVIOUS SOIL GAS SAMPLE LOCATION PREVIOUS SOIL SAMPLE LOCATION 2923 South Tryon Street-Suite 100 Charlotte, North Carolina 28203 704-586-0007(p) 704-586-0373(f) License # C-1269 / #C-245 Geology JOB NO. LEH-004 FIGURE NO. 3 QUALITY PRODUCTS COMPANY 1513, 1515, AND 1521 S. MINT STREET CHARLOTTE, NORTH CAROLINA PREVIOUS SAMPLE LOCATION MAP NOTES: 1.AERIAL IMAGERY OBTAINED FROM MECKLENBURG CO. GIS (2019). 2.PREVIOUS SAMPLES COLLECTED BY H&H ON 1/26/18. W . S U M M I T S T R E E T WESTWOOD AVENUE S. MI N T S T R E E T FORMER MACHINE REPAIR FACILITY FORMER RAY'S GULF/ RAY'S AUTO FORMER AUTOMOTIVE REPAIR FACILITY FORMER AUTOMOTIVE JUNKYARD SALES OFFICE FORMER AUTOMOTIVE REPAIR FACILITY FORMER FURNACE ROOM (1950s-1980s) FORMER DIE STAMPING AREA (1940s-1980s) FORMER TIN SHOP (1940s & 1950s) FINISHING ROOM (1960s-1980s) FORMER MACHINE SHOP (1960s-1980s) FORMER AUTOMOTIVE REPAIR FACILITY FORMER AUTOMOTIVE REPAIR FACILITY FORMER AUTOMOTIVE JUNKYARD STORAGE YARD FORMER MACHINE SHOP FORMER PAINT BOOTH (1960s-1980s) FORMER FINISHED PRODUCT & SHIPPING (1960s-1980s) OBSERVED STAINING S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint Street\1513-1521 Assessments\Brownfields Assessment\Report\Figures\Brownfields Assessment Maps.dwg, 10/18/2019 8:57:20 AM, amckenzie IAS-3 IAS-4 IAS-2 IAS-1BKG-1 RCI DEMOL I T IONVACAN T REVISION NO. 0DATE: 10-17-19 LEGEND BROWNFIELDS PROPERTY BOUNDARY FORMER BUILDING FOOTPRINT INDOOR AIR SAMPLE / BACKGROUND SAMPLE LOCATION 2923 South Tryon Street-Suite 100 Charlotte, North Carolina 28203 704-586-0007(p) 704-586-0373(f) License # C-1269 / #C-245 Geology JOB NO. LEH-004 FIGURE NO. 7 QUALITY PRODUCTS COMPANY 1513, 1515, AND 1521 S. MINT STREET CHARLOTTE, NORTH CAROLINA INDOOR AIR SAMPLE LOCATION MAP NOTES: 1. AERIAL IMAGERY OBTAINED FROM MECKLENBURG CO. GIS (2019). 2. INDOOR AIR SAMPLES COLLECTED BY H&H ON 12/19/18. S. MI N T S T R E E T W . S U M M I T S T R E E T WESTWOOD AVENUE PIRTEK SOUTHEND S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint Street\1513-1521 Assessments\Brownfields Assessment\Report\Figures\FIGS 5, 6, 7 - SOIL AND GW SAMPLE LOCATION MAP, POTENTIOMETRIC SURFACE MAP, AND INDOOR AIR LOCATION MAP.dwg, 10/17/2019 9:00:22 AM, amckenzie Appendix B Geo-Seal EV20s Submittal Package Geo-Seal® EV20 Product Data Sheet EPRO Services, Inc. (800) 882-1896 eproinc.com Product Description Basic Use: Geo-Seal EV20 is a standalone EVOH passive barrier to mitigate vapor intrusion for sites deemed to be low risk. Users can also use Geo-Seal EV20 in conjunction with an active sub- slab depressurization (SSD) system to increase system efficiency and add redundancy to the SSD system. Geo-Seal CORE is applied within the Geo-Seal EV20 seam overlap, around pipe penetrations, and at termination points to eliminate the need for challenging tape. Combining a sheet membrane with detailing spray helps increase installation efficiency while ensuring a robust seal in critical areas. Composition: Geo-Seal EV20 is a 20-mil composite EVOH geomembrane. Geo-Seal EV20 also exceeds all Class A, B, and C vapor barrier requirements. Benefits • 20 mil EVOH membranes have the same chemical diffusive properties as 60 and 80 mil HDPE liners. • Spray applied seams enhance seam integrity and increase the rate of production. Taped seams’ integrity can be compromised in cold or wet conditions. • Geo-Seal EV20 is smoke tested to ensure proper installation. • Meets class A, B, and C vapor barrier standards Limitations • Thinner mil vapor intrusion barriers are less durable than thicker composite systems. • Additional cushion geotextile may be required to protect Geo-Seal EV20 from additional aggregate layers. • Additional weight should be used during application in windy conditions to secure the system in place. • A more robust composite system should be utilized for sites with elevated risk or more complex applications. Technical Data Properties: See physical properties table Coverages: One roll covers 1500 square feet, not including overlaps or waste Specification Writer: Contact EPRO before writing specifications on this product Installation Preparation: Please refer to manufacturer’s specifications for substrate requirements. Rolls should be inspected for cosmetic damage prior to application. Application: Please refer to manufacturer’s specifications. Overlap the seams of Geo-Seal EV20 a minimum of 6” and with a 60 mil application of Geo-Seal CORE in the seam overlap. Availability and Packaging Contact a local EPRO installer or authorized applicator (www.eproinc.com). Roll Size: 10’ x 150’, 5‘ wide folded rolls Warranty Limited Warranty: EPRO Services, Inc. believes to the best of its knowledge that performance tables are accurate and reliable. EPRO warrants this product to be free from defects. EPRO makes no other warranties with respect to this product, express or implied, including without limitation the implied warranties of MERCHANTABILITY OR FITNESS FOR PARTICULAR PURPOSE. EPRO’s liability shall be limited in all events to supplying sufficient product to retreat the specific areas to which defective product has been applied. EPRO shall have no other liability, including liability for incidental or resultant damages, whether due to breach of warranty or negligence. This warranty may not be modified or extended by representatives of EPRO or its distributors. Equipment Seaming: AD-55 Sprayer, available through EPRO for application of Geo-Seal CORE in seam overlaps, or by hand using Geo-Seal CORE Detail. Smoke Testing: EPRO Smoke Test Machine for underslab applications Technical Services and Information Complete technical services and information are available by contacting EPRO at 800.882.1896 or www.eproinc.com. Geo-Seal® EV20 Product Data Sheet EPRO Services, Inc. (800) 882-1896 eproinc.com Physical Property Test Method Value Film Material .....................................................................................................................................Polyethylene & EVOH Film Color ..........................................................................................................................................Blue Weight................................................................................................................................................498 g/m² Film Thickness ...................................................................................................................................20 Mil Classification .......................................................ASTM E1745 ........................................................Class A, B & C Water Vapor Permeance ...................................ASTM E96 ............................................................0.0098 perms Tensile Strength ..................................................ASTM D882 ..........................................................58 lbf Puncture Resistance ...........................................ASTM D1709 ........................................................2600 grams Life Expectancy ...................................................ASTM E154 ..........................................................Infinite Low Temp. Impact ..............................................ASTM D1790 ........................................................Resistant to 105° C Methane Gas Permeance .................................ASTM D1434 ........................................................3.68 x 10-12 m/s Benzene Gas Permeance ..................................Queens University1 .............................................1.13 x 10-10 m2/sec TCE Gas Permeance ..........................................Queens University1 .............................................7.66 x 10-11 m2/sec PCE Gas Permeance ..........................................Queens University1 .............................................7.22 x 10-11 m2/sec Ethylbenzene Permeance ..................................Queens University1 .............................................1.23 x 10-10 m2/sec Toluene Permeance............................................Queens University1 .............................................1.57 x 10-10 m2/sec Radon Diffusion Coeffiecent .............................K124/02/95 ..........................................................7.22 x 10-11 m2/sec 1 Queens University testing results are not directly comparable to other permeation/diffusion testing methods. Dimensions: 10’ x 150’ Weight: 102 lbs. Typical Physical Properties Product Data Sheet EPRO Services, Inc. (800) 882-1896 eproinc.com Geo-Seal® CORE Product Description Basic Use: Geo-Seal CORE is a polymer modified asphalt (PMA) applied to nominal dry thicknesses depending on the configuration of the Geo-Seal system vapor intrusion barrier system. Spray applied to form a seamless barrier, Geo-Seal CORE is an integral component to all Geo-Seal systems due to its ability to bond to and seam high density polyethylene (HDPE), polyolefin sheets. Geo-Seal CORE is applied with a proprietary self-contained sprayer designed to produce a high build, monolithic, and rapidly curing membrane. Composition: Geo-Seal CORE is a non-hazardous, low-viscosity, water-based, anionic asphalt emulsion modified with a blend of synthetic polymerized rubbers and proprietary additives. Geo-Seal CORE is highly stable during transit and proper storage, but becomes highly reactive during the spray application to form a rapidly cured membrane with exceptional bonding, elongation, and hydrophobic characteristics. Benefits • Provides a layer of seamless protection and redundancy in all Geo-Seal system assemblies • Hydrophobic and resistant to methane gas • Non-toxic, non-hazardous, non-flammable, and VOC free • Forms a tenacious bond to HDPE sheets • Application to damp substrates is acceptable • Can be applied in below freezing temperatures with proper equipment Limitations • Surfaces shall be free of dirt and debris • Material should be stored above 40°F and not allowed to freeze • Not a traffic bearing surface, additional protection required • Must not be applied to ponded water • Direct foot traffic should be limited when ambient air temperatures are greater than 100°F Technical Data Shelf life: 6 months. The ability to apply the product beyond its estimated shelf life is dependent on storage conditions and homogeneity of the product. Storing material in an enclosed temperature controlled environment that maintains a minimum ambient temperature of 65° Fahrenheit will likely extend the shelf life beyond 6 months. Properties: See physical properties table Specification Writer: Contact EPRO before writing specifications on this product. Geo-Seal system assemblies should be reviewed in order to meet project specific site conditions. Additional test information available upon request. Installation EPRO Authorized Applicators must be approved in writing by EPRO prior to receiving a contract in order to qualify for a warranty for this product and system assembly. Surface Preparation: All surfaces shall be prepared in accordance to manufacturer’s specifications. Surfaces shall be uniform, free of loose materials, and surface contaminants. Contaminant and loose debris shall be removed prior to application by suitable methods. Application: Please refer to manufacturer’s specifications. Geo-Seal CORE shall be spray applied to the specified nominal mil thickness. When properly applied, Geo-Seal CORE will set up immediately on the surface and promptly start the curing process. Light foot traffic is acceptable, but must be limited to the authorized Geo-Seal applicator. The initial cure is complete when Geo-Seal CORE is no longer ejecting moisture, 12 to 48 hours depending on ambient air conditions. Availability and Packaging Contact EPRO sales representative for local distributors or authorized applicators (www.eproinc.com). Geo-Seal CORE is available in the following packaging options: 55 gallon drum 275 gallon tote 330 gallon tote Product Data Sheet EPRO Services, Inc. (800) 882-1896 eproinc.com Geo-Seal® CORE Physical Property Test Method Results Tensile Strength - Core only .............................ASTM 412 ...........................................................32 psi Tensile Strength - Geo-Seal System ................ASTM 412 ...........................................................662 psi Elongation ..........................................................ASTM 412 ...........................................................4140% Resistance to Decay .........................................ASTM E 154 Section 13 .....................................4% Perm Loss Accelerated Aging ............................................ASTM G 23 .........................................................No Effect Moisture Vapor Transmission ...........................ASTM E 96 ...........................................................026 g/ft2/hr Hydrostatic Water Pressure .............................ASTM D 751 .......................................................26 psi Perm rating ........................................................ASTM E 96 (US Perms) ......................................0.21 Methane transmission rate ..............................ASTM D 1434 .....................................................Passed Adhesion to Concrete & Masonry ...................ASTM C 836 & ASTM C 704 .............................11 lbf./inch Hardness ............................................................ASTM C 836 .......................................................80 Crack Bridging ...................................................ASTM C 836 .......................................................No Cracking Heat Aging ........................................................ASTM D 4068 .....................................................Passed Environmental Stress Cracking ........................ASTM D 1693 .....................................................Passed Oil Resistance ....................................................ASTM D543 .........................................................Passed Soil Burial ...........................................................ASTM D 4068 .....................................................Passed Low Temp. Flexibility .........................................ASTM C 836-00 ..................................................No Cracking at –20°C Resistance to Acids Acetic ................................................................................................................................................30% Sulfuric and Hydrochloric ...............................................................................................................13% Temperature Effect Stable ...............................................................................................................................................248°F Flexible .............................................................................................................................................13°F Typical Physical Properties Warranty Limited Warranty: EPRO Services, Inc. believes to the best of its knowledge that performance tables are accurate and reliable. EPRO warrants this product to be free from defects. EPRO makes no other warranties with respect to this product, express or implied, including without limitation the implied warranties of MERCHANTABILITY OR FITNESS FOR PARTICULAR PURPOSE. EPRO’s liability shall be limited in all events to supplying sufficient product to retreat the specific areas to which defective product has been applied. EPRO shall have no other liability, including liability for incidental or resultant damages, whether due to breach of warranty or negligence. This warranty may not be modified or extended by representatives of EPRO or its distributors. Equipment Spray System: AD-55 Sprayer is available through EPRO. To discuss alternative spray machine options, please contact EPRO directly. Smoke Testing: EPRO Smoke Test Machine for underslab applications Technical Services and Information Complete technical services and information are available by contacting EPRO at 800.882.1896 or www.eproinc.com. e.roll Product Data Sheet EPRO Services Inc. (800) 882-1896 eproinc.com Product Description Basic Use: e.roll is a key component to EPRO’s redundant field installed composite design concept and is a roller applied version of e.spray. It is designed to be used for system detailing, repairs, and in areas where the required clearance for e.spray cannot be achieved. e.roll is most commonly used in conjunction with e.poly to reinforce system penetrations, terminations, seams, cracks, and membrane transitions. e.roll is used on decks, over- excavated walls, blindside vertical walls, and underslab E.Series assemblies. e.roll can be applied to a wide range of materials/ substrates, high density polyethylene (HDPE), polyolefin sheets, geotextile fabric, wood, metal, foam insulation, and concrete based surfaces (green concrete, shotcrete and concrete masonry units (CMU)). Composition: e-roll is a medium viscosity water-based, polymer- modified anionic asphalt emulsion, which exhibits exceptional bonding, elongation and waterproofing characteristics. Benefits • e.roll is a single component material, no additional blending is required • Provides the ability to easily detail and repair assemblies without the use of a spray pump • Non-toxic, non-hazardous, non-flammable, and VOC free • Forms both a mechanical and ionic bond directly to concrete • Application to damp substrates is acceptable Limitations • Surfaces shall be free of dirt and debris • Material should be stored above 40°F and not allowed to freeze • Not a traffic bearing surface, additional protection required • Must not be applied to ponded water • Cold temperatures will prolong cure time Technical Data Shelf life: 1 year. The ability to apply the product beyond its estimated shelf life is dependent on storage conditions and homogeneity of the product. Storing material in an enclosed temperature controlled environment that maintains a minimum ambient temperature of 65° Fahrenheit will likely extend the shelf life beyond 1 year. Properties: See physical properties table Specification Writer: Contact EPRO before writing specifications on this product. E.Series system assemblies should be reviewed in order to meet project specific site conditions. Installation Surface Preparation: All surfaces shall be prepared in accordance to manufacturer’s specifications. In general, this means all surfaces shall be uniform, free of loose materials, and surface contaminants. Contaminant and loose debris shall be removed prior to application by suitable methods. A test should always be done prior to application using the same cleaning preparation and application procedures to be used on the project. Application: Please refer to manufacturer’s specifications. e.roll shall be spray applied to the specified nominal mil thickness. e.roll may be applied by roller or brush. Cleaning: Clean all tools, hoses, spray guns, and tips with kerosene and/or equivalent. Availability and Packaging Contact EPRO sales representative for local distributors or authorized applicators (www.eproinc.com). e.roll is available in 5 gallon or 1 gallon containers. Warranty Limited Warranty: EPRO Services, Inc. believes to the best of its knowledge that performance tables are accurate and reliable. EPRO warrants this product to be free from defects. EPRO makes no other warranties with respect to this product, express or implied, including without limitation the implied warranties of MERCHANTABILITY OR FITNESS FOR PARTICULAR PURPOSE. EPRO’s liability shall be limited in all events to supplying sufficient product to retreat the specific areas to which defective product has been applied. EPRO shall have no other liability, including liability for incidental or resultant damages, whether due to breach of warranty or negligence. This warranty may not be modified or extended by representatives of EPRO or its distributors. e.roll Product Data Sheet EPRO Services Inc. (800) 882-1896 eproinc.com Physical Property Test Method Value Color ..................................................................................................................................................Brown to Black Solvent Content.................................................................................................................................No Solvents Shelf Life ............................................................................................................................................6 months Tensile Strength ..................................................ASTM D412 ..........................................................32 psi Elongation ...........................................................ASTM D412 ..........................................................3860% Resistance to Decay ...........................................ASTM E154 SECTION 13 .....................................9% Perm Loss Accelerated Aging .............................................ASTM G23 ...........................................................No Effect Moisture Vapor Transmission ............................ASTM E96 ............................................................0.071 g/ft²/hr Hydrostatic Water Pressure ...............................ASTM D751 ..........................................................28 psi Perm Rating.........................................................ASTM E96 ............................................................0.17 perms Methane Transmission Rate ..............................ASTM D14334 ......................................................0 Adhesion to Concrete & Masonry ....................ASTM C836 ..........................................................1 lbf/inch Hardness .............................................................ASTM C836 ..........................................................85 Crack Bridging ....................................................ASTM C836 ..........................................................No Cracking Low Temp. Flexibility ..........................................ASTM C836-00 .....................................................No Cracking at -20°C Packaging: 5 gallon bucket Typical Physical Properties Equipment No special equipment is necessary. Technical Services and Information Complete technical services and information are available by contacting EPRO at 800.882.1896 or www.eproinc.com. This product was formally known as Ecoline-R. e.poly Product Data Sheet EPRO Services, Inc. (800) 882-1896 eproinc.com Product Description Basic Use: e.poly is a polyester fabric that is designed to reinforce membrane terminations, transitions, penetrations, seams, and general repair areas. Used in every E.Series assembly, e.poly is installed between two layers of e.roll or e.spray. Composition: e.poly is a 100% polyester textile material composed of staple fibers hydraulically entangled. Benefits • Excellent conformability and elongation • Exceptional tear resistance and high tensile strength • Open weave allows complete saturation and integration Limitations • Not suitable for expansion joints or areas where movement is desired Technical Data Properties: See physical properties table Coverages: 6”, 12” and 40” rolls cover 150, 300, and 1,080 square feet, respectively Specification Writer: Contact EPRO before writing specifications on this product. E.Series system assemblies should be reviewed in order to meet project specific site conditions. Installation Preparation: Please refer to manufacturer’s specifications for substrate requirements. Application of e.poly should be done when weather conditions meet the requirement of e.roll or e.spray. Installation: Please refer to manufacturer’s specifications. Install specified thickness of e.roll or e.spray and immediately embed e.poly into the initial layer of e.roll or e.spray. Once firmly pressed into the uncured membrane, fully saturate with additional layer of e.roll or e.spray to the specified thickness. Availability and Packaging Contact EPRO sales representative for local distributors or authorized applicators (www.eproinc.com). Roll: 6” x 300’, 12” x 300’, and 40” x 324’ rolls are available Warranty Limited Warranty: EPRO Services, Inc. believes to the best of its knowledge that performance tables are accurate and reliable. EPRO warrants this product to be free from defects. EPRO makes no other warranties with respect to this product, express or implied, including without limitation the implied warranties of MERCHANTABILITY OR FITNESS FOR PARTICULAR PURPOSE. EPRO’s liability shall be limited in all events to supplying sufficient product to retreat the specific areas to which defective product has been applied. EPRO shall have no other liability, including liability for incidental or resultant damages, whether due to breach of warranty or negligence. This warranty may not be modified or extended by representatives of EPRO or its distributors. Equipment No special equipment is needed. Technical Services and Information Complete technical services and information are available by contacting EPRO at 800.882.1896 or www.eproinc.com. This product was formally known as Polyester. e.poly Product Data Sheet EPRO Services, Inc. (800) 882-1896 eproinc.com Physical Property Test Method Value Weight................................................................................................................................................3 oz. Bursting Strength ...............................................ASTM D3786 ........................................................177 lbs. Tensile Strength .................................................ASTM D1682 ........................................................57.1 psi Tear Strength .......................................................ASTM D1117 ........................................................16.1 lbs Elongation ..........................................................ASTM D1682 ........................................................62.0% Conformability ..................................................................................................................................Excellent Ease of saturation ............................................................................................................................Excellent Dimensions: 6” x 300’, 12” x 300’, and 40” x 324’ rolls are available Typical Physical Properties Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 1 Applications: Slab On Grade Gas Containment Vapor Intrusion Barrier With Spray Applied Seams Spec Version: EproGSEV20.VB.v1.08.20gs Date issued: September 22, 2020 Note: This specification may be superseded at any time. Check eproinc.com for the most up to date version of this specification. SECTION 02 56 16 GAS CONTAINMENT SECTION 02 56 19.13 FLUID APPLIED GAS BARRIER Geo-Seal EV20s EVOH Vapor Intrusion Barrier Guide Specification Slab On Grade Geo-Seal EV20s is comprised of an EVOH membrane that is highly chemically resistant, easy to install, while also providing better protection during the installation process. Geo-Seal EV20s utilizes Geo-Seal CORE spray membrane to seal seams, detail penetrations, and terminate the membrane to concrete surfaces. This guide specification has been prepared according to the principles established in the Manual of Practice published by the Construction Specification Institute. Note: If areas will be subjected to water and/or hydrostatic conditions, contact EPRO for appropriate system recommendations. For additional questions, your local EPRO technical representative can be contacted through: EPRO Services, Inc., Wichita KS; 1.800.882.1896; www.eproinc.com. Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 2 GEO-SEAL EV20s SLAB ON GRADE EVOH VAPOR INTRUSION BARRIER WITH SPRAY APPLIED SEAMS SPECIFICATION VERSION 1.0 SECTION 02 56 16 – GAS CONTAINMENT SECTION 02 56 19.13 – FLUID-APPLIED GAS BARRIER PART 1 - GENERAL 1.1 RELATED DOCUMENTS A. Drawings and general provisions of the contract, including general and supplementary conditions, and Division 1 specification section, apply to this section. 1.2 SECTION INCLUDES A. The installation of materials designed to provide vapor intrusion protection when installed per project specification, this section covers the methane mitigation and vapor intrusion membrane, along with the following: 1. Surface preparation and substrate treatment 2. Auxiliary materials 3. Prefabricated drainage mat (if applicable) 4. Foundation drain (if applicable) 1.3 RELATED SECTIONS A. Section 02 24 00: Environmental Assessment B. Section 02 32 00: Geotechnical Investigation C. Section 03 15 00: Concrete Accessories D. Section 03 30 00: Cast-in-Place Concrete E. Section 03 40 00: Precast Concrete F. Section 07 90 00: Joint Protection G. Section 31 30 00: Earthwork Methods H. Section 33 41 00: Subdrainage 1.4 PERFORMANCE REQUIREMENTS A. General: Provide a vapor mitigation system that prevents the passage of methane gas, contaminant vapors including chlorinated solvents and petroleum hydrocarbons, and complies with the physical requirements as demonstrated by testing performed by an independent testing agency. Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 3 1.5 SUBMITTALS A. Product Data: Submit manufacturer's printed technical data, tested physical and performance properties, instructions for evaluating, preparing, and treating substrates, and installation instructions. B. Shop Drawings: Project specific drawings showing locations and extent of vapor intrusion barrier system, details for overlaps, penetrations, transitions, and termination conditions. C. Samples: Submit two standard size samples of the each of the following: 1. Individual components of the specified vapor intrusion barrier system. D. Applicator Certification: Submit written confirmation at the time of bid that applicator is currently approved by the membrane manufacturer. 1.6 QUALITY ASSURANCE A. Applicator Qualifications: System applicator shall be an EPRO Authorized Applicator who is trained to perform work that in accordance with EPRO standards and policies. B. Manufacturer Qualification: Obtain vapor intrusion barrier materials and system components from a single manufacturer source, EPRO. Manufacturer must have 20 years of experience in the manufacture of vapor intrusion barrier systems. C. Third Party Inspection: Independent inspection of the system installation may be required based on project conditions and desired warranty coverage, or as required based on local building code/government agency jurisdiction. Inspection reports shall be submitted directly to the vapor intrusion barrier manufacturer and made available to other parties per the owner’s direction. D. Pre-Construction Meeting: A meeting shall be held prior to application of the barrier system to assure proper substrate preparation, confirm installation conditions, and any additional project specific requirements. Attendees of the meeting shall include, but are not limited to the following: 1. EPRO authorized applicator 2. Third party inspector 3. General contractor 4. Owner’s representative 5. Architect and Engineer 6. Concrete/Shotcrete contractor 7. Rebar contractor 8. All appropriate related trades E. Field Sample: Apply vapor intrusion barrier system field sample to 100 ft2 (9.3 m2) of each assembly to demonstrate proper application techniques and standard of workmanship. Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 4 1. Notify membrane system manufacturer’s representative, architect, certified inspector, and other appropriate parties one week in advance of the dates and times when field sample will be prepared. 2. If architect and certified inspector determines that field sample does not meet requirements; reapply membrane system until field sample is approved. 3. Retain and maintain approved field sample during construction in an undisturbed condition as a standard for judging the completed membrane system. An undamaged field sample may become part of the completed work. 1.7 DELIVERY, STORAGE AND HANDLING A. Delivery: Deliver materials to site labeled with manufacturer's name, product brand name, material type, and date of manufacture. Upon the arrival of materials to the jobsite, inspect materials to confirm material has not been damaged during transit. B. Storage: Proper storage of onsite materials is the responsibility of the certified applicator. Consult product data sheets to confirm storage requirements. Storage area shall be clean, dry, and protected from the elements. If ambient air temperatures are expected to fall below 40°F, precautions will need to be taken to protect any emulsion product from near freezing temperatures. Protect stored materials from direct sunlight. C. Disposal: Remove and replace any material that cannot be properly applied in accordance with local regulations and specification section 01 74 19. 1.8 PROJECT CONDITIONS A. Substrate Review: Substrates shall be reviewed and accepted by the certified applicator and independent inspector prior to application. B. Penetrations: All plumbing, electrical, mechanical, and structural items to be passing through the membrane system shall be properly spaced, positively secured in their proper positions, and appropriately protected prior to system application and throughout the construction phase. Braided grounding rods are not allowed to pass through the vapor intrusion barrier. C. Reinforcement Steel and Concrete Forms: Vapor intrusion barrier shall be installed before placement of reinforcing steel. When penetrations post system installation occurs, it is the responsibility of the general contractor to notify the vapor intrusion barrier applicator to immediately make repairs prior to the placement of overburden, this includes the use of solid plastic “VaporStakes” used to secure concrete forms. D. Clearance: Minimum clearance of 24 inches is required for application of spray applied polymer modified asphalt, Geo-Seal CORE. For areas with less than 24-inch clearance, the product may be applied by hand using Geo-Seal CORE Detail. E. Overspray: Protect all adjacent areas not receiving the barrier application. Masking is necessary to prevent unwanted overspray from adhering to, or staining, areas not receiving the membrane. Once Geo-Seal CORE adheres to a surface it is extremely difficult to remove. F. Weather Limitations: Perform work only when existing and forecast weather conditions are within manufacturer's recommendations. Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 5 1. Spray Applied Polymer Modified Asphalt Membrane: Minimum ambient temperature should be 40°F (7°C) and rising. For applications temperatures below 38°F, but greater than +19ºF/-7ºC, special equipment and material handling is required. Substrate shall be clean and free from standing moisture. 2. EPRO applicators reserve the right not to install product when application conditions might be within manufactures acceptance, but ambient conditions may limit a successful application. 1.9 WARRANTY A. Special Warranty: Submit a written warranty signed by vapor intrusion barrier manufacturer agreeing to replace system materials that do not conform to manufacturer’s published specifications or are deemed to be defective. Warranty does not include failure of vapor intrusion barrier due to failure of soil substrate prepared and treated according to requirements or formation of new joints and cracks in the concrete that exceed 1/8 inch (3.175 mm) in width. 1. Warranty Period: 1 years after date of substantial completion. Longer warranty periods are available upon request. 2. Coverage: Manufacturer will guarantee that the material provided is free of defects for the warranty period. B. Additional Warranty Options: Upgraded warranties are available by contacting the manufacturer. These warranties may have additional requirements and approval must be granted in accordance to the manufacturer’s warranty requirements. Additional warranty options include: 1. Waterproofing Warranties: For below grade projects that require vapor intrusion barriers and below grade waterproofing for foundation walls, single source warranties are available from EPRO. PART 2 - PRODUCTS 2.1 MANUFACTURERS A. Acceptable Manufacturer: EPRO Services, Inc. (EPRO), P.O. Box 347; Derby, KS 67037; Tel: (800) 882-1896; www.eproinc.com B. Basis of Design: Geo-Seal EV20s (20 mils) – Geo-Seal EV20, Geo-Seal CORE (for detailing seams, terminations and penetrations) 2.2 VAPOR INTRUSION BARRIER MATERIALS A. EVOH Sheet Membrane 1. Geo-Seal EV20: Geo-Seal EV20 is an extremely durable, high strength co-polymer EVOH sheet vapor barrier. PROPERTIES TEST METHOD VALUE Film Material Polyethylene & EVOH Film Color Blue Thickness 20 Mil Weight 498 g/m2 Classification ASTM E1745 Class A, B & C Water Vapor Transmission ASTM E96 0.033 perms Water Permeance ASTM E96 0.0098 perms (US) Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 6 Tensile Strength ASTM D882 58 lbf Puncture Resistance ASTM D1709 2600 grams Life Expectancy ASTM E 154 Infinite Low Temperature Impact ASTM D 1790 Resistant to 105 °C Methane Gas Permeance ASTM D1434 3.68 x 10-12 m/s Benzene Vapor Permeance Queens University 1.13 x 10-10 m2/s TCE Vapor Permeance Queens University 7.66 x 10-11 m2/s PCE Vapor Permeance Queens University 7.22 x 10-11 m2/s Weight: 102 pounds Dimensions: 10’ x 150' B. Polymer Modified Asphalt 1. Geo-Seal CORE: Geo-Seal CORE is a non-hazardous, low-viscosity, water-based, anionic asphalt emulsion modified with a blend of synthetic polymerized rubbers and proprietary additives. Geo-Seal CORE is highly stable during transit and when properly stored but becomes highly reactive during the spray application to form a rapidly cured membrane with exceptional bonding, elongation, and hydrophobic characteristics. PROPERTIES TEST METHOD VALUE Color Brown to Black Solvent Content No Solvents Shelf Life 6 months Tensile Strength ASTM 412 32 psi Elongation ASTM 412 4140% Resistance to Decay ASTM E 154 Section 13 4% Perm Los Accelerated Aging ASTM G 23 No Effect Moisture Vapor Transmission ASTM E 96 0.026 g./sq. ft./hr. Hydrostatic Water Pressure ASTM D 751 26 psi Perm Rating ASTM E 96 (US Perms) 0.21 Methane Transmission Rate ASTM D 1434 0 Adhesion to Concrete & Masonry ASTM C 836 & C 704 20 lbf./inch Adhesion to HDPE ASTM C 836 28.363 lbf./inch Adhesion to Polypropylene Fabric ASTM C 836 31.19 lbf./inch Hardness ASTM C 836 80 Crack Bridging ASTM C 836-00 No Cracking Low Temp. Flexibility No Cracking at -20° C Packaging: 55 gallon drum, 275 gallon tote, 330 gallon tote 2. Geo-Seal CORE Detail: Geo-Seal CORE Detail is single component, medium viscosity, water-based, polymer-modified anionic asphalt emulsion, which exhibits exceptional bonding, elongation and hydrophobic characteristics. PROPERTIES TEST METHOD VALUE Color Brown to Black Solvent Content No Solvents Shelf Life 6 months Tensile Strength ASTM 412 32 psi Elongation ASTM 412 3860% Resistance to Decay ASTM E 154 SECTION 13 9% Perm Loss Accelerated Aging ASTM G 23 No Effect Moisture Vapor Transmission ASTM E 96 0.071 g/sq. ft./hr. Hydrostatic Water Pressure ASTM D 751 28 psi Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 7 Perm Rating ASTM E 96 (US Perms) 0.17 Methane Transmission Rate ASTM D 14334 0 Adhesion to Concrete & Masonry ASTM C 836 1 lbf/inch Hardness ASTM C 836 85 Crack Bridging ASTM C 836 No Cracking Low Temp. Flexibility ASTM C 836-00 No Cracking at -20° C Packaging: 5 gallon bucket 2.3 AUXILIARY MATERIALS A. General: All accessory products shall be provided by the specified vapor intrusion barrier manufacturer. Auxiliary products used in lieu of, or in addition to, the manufactures products must be approved in writing by EPRO prior to installation. B. Reinforcement Fabric: Manufacturer’s polyester fabric, Geo-Seal Reinforcement Fabric is available in 6 inch, 12 inch, and 40 inch widths. C. Detailing Material: Geo-Seal CORE Detail, a roller applied, water based, high viscosity, polymer modified asphaltic material. D. Backer Rod: Closed cell polyethylene foam E. Termination Bar: e.term hd, or approved alternate. PART 3 - EXECUTION 3.1 EXAMINATION A. Comply with project documents, manufacturer’s product information, including product application and installation guidelines, pre-job punch list, as well as, manufacturer’s shipping and storage recommendations. 3.1.2 SURFACE PREPARATION A. The general contractor shall engage the certified vapor intrusion barrier contractor and certified inspector to ensure surfaces are prepared in accordance with manufacturer’s instructions. Unless, explicitly stated in the contract documents, the vapor intrusion barrier contractor is not responsible for surface preparation. B. Examine all substrates, areas, and conditions under which the membrane system will be installed, applicator and inspector must be present. Do not proceed with installation until unsatisfactory conditions have been corrected and surface prepration requirements have been met. If conditions exist that are not addressed in this section, notify inspector and contact EPRO for additional clarification. C. Soil and Sand Substrates: Native soil and sand substrates shall be uniformly compacted to meet structural and building code requirements. All surfaces shall be free from protrusions and debris that may compromise the membrane system. Free standing water must be removed prior to application. Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 8 D. Aggregate Substrates: Aggregate substrates shall be compacted to meet structural and building code requirements and then rolled flat to provide a uniform substrate. ¾ inch minus aggregate with no more than one fractured face is recommended, but other aggregates substrates may be approved by the manufacturer provided they do not create sharp angular protrusions that may compromise the vapor intrusion system. E. Working Slab: Mud slab, rat slab, or other concrete working slab shall have a uniform plane with a light broom or light trowel finish. F. Concrete Surfaces: Clean and prepare concrete surface to manufacturer’s recommendations. In general, only apply the Geo-Seal CORE material to dry, clean and uniform concrete substrates with a light trowel, light broom, or equivalent finish. G. Cast-in-Place or Shotcrete Walls: Application to green concrete is acceptable provided the substrate is prepared in accordance with manufacturers specifications and published instructions. 1. Provide clean, dust-free, and dry substrate for vapor intrusion barrier application. 2. Surfaces shall be power washed to remove grease, oil, form release agents, or any other penetrating contaminants from the concrete. 3. Remove all fins, ridges, and other protrusions. 4. Fill honeycomb, aggregate pockets, tie holes, and other voids with hydraulic cement, or rapid-set grout. 3.2 VAPOR INTRUSION BARRIER INSTALLATION A. General: The underslab vapor intrusion system shall be installed under strict accordance with the manufacturer’s guidelines and project specifications. 3.2.2 EVOH GEOCOMPOSITE SHEET MEMBRANE – GEO-SEAL EV20 A. Whenever possible roll out Geo-Seal EV20 in the same direction over the substrate with geotextile side facing down, away from the installer. When multiple pours will occur, extend the Geo-Seal EV20 a minimum of 2 feet past the pour joint. B. Overlap Geo-Seal EV20 a minimum of 6 inches. C. At the seam overlap, peel back the top layer of Geo-Seal EV20 and apply 60 mils into the overlapping seam, making certain to apply Geo-Seal CORE to both the top of the bottom sheet and the bottom of the top sheet. Embed the top sheet into the bottom sheet. D. Visually verify there are no gaps/fish-mouths in seams. 3.2.3 POLYMER MODIFED ASPHALT MEMBRANE – GEO-SEAL CORE A. Mask off adjoining surfaces where unwanted Geo-Seal CORE polymer modified asphalt membrane may be exposed on finished surfaces or impact other construction trades. B. Commence application of Geo-Seal CORE polymer modified asphalt when ambient air temperatures are within manufacturer recommendations. C. Surfaces that will receive the membrane must be clean and free from standing moisture. D. Start installing Geo-Seal CORE in presence of approved 3rd party inspector or required city inspector. Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 9 E. Apply one application of Geo-Seal CORE membrane in accordance to manufacturer’s instructions in order to obtain a seamless membrane with a minimum dry film thickness of 60 mils (1.5 mm). F. Apply Geo-Seal CORE/Geo-Seal CORE Detail in and around penetrations and cavities to ensure the formation of monolithic seal around all penetrations. G. Apply Geo-Seal CORE/Geo-Seal CORE Detail to prepared wall terminations and vertical surfaces to heights indicated according to manufacturer’s recommendations and details. (if applicable) 3.2.4 TERMINATION SEQUENCE A. System Termination: The termination process is appropriate for terminating the membrane onto exterior footings, pile caps, interior footings and grade beams. When terminating the membrane to stem walls or vertical surfaces the same process should be used. 1. Concrete surfaces that are not a light trowel, light broom or equivalent finish, will need to be repaired. 2. Terminations on horizontal and vertical surfaces should extend 6” onto the termination surface. Job specific conditions may prevent a 6” termination. 3. Apply 60 mils of Geo-Seal CORE to the terminating surface and then embed the Geo- Seal EV20 layer by pressing it firmly into the Geo-Seal CORE layer. 4. Apply 30 mils of Geo-Seal CORE over the edge of termination. For further clarification, refer to the termination detail provided by the manufacturer. 3.2.5 SEALING OF PENETRATIONS A. Sealing of Standard Pipe Penetrations: Prepare membrane penetrations so they are free of any material that will inhibit a direct bond to the penetration surface: foam, insulation, protective coatings, etc. 1. Trim Geo-Seal EV20 to within 1/8 inch of the penetration. 2. Apply Geo-Seal CORE Detail 3 inches horizontally and 3 inches vertically around the base of the penetration. 3. Embed Geo-Seal Reinforcement Fabric reinforcement fabric 3 inches horizontally and 3 inches vertically around the base of the penetration. 4. Apply a second layer of Geo-Seal CORE Detail to reinforcement fabric until the reinforcement fabric is fully saturated. Secure Geo-Seal Reinforcement Fabric reinforcement fabric to penetration with a cable tie. For further clarification, refer to the termination detail provided by manufacturer. 3.3 FIELD QUALITY CONTROL A. Smoke Test: Conduct smoke test on all underslab areas upon installation of the Geo-Seal EV20 sheet, the sealing of all penetrations, terminations, and sheet membrane overlaps. All deficient areas shall be noted, marked for repair, and repairs verified. Refer to manufactures smoke testing protocol for additional guidance. B. Field Inspection: Contact EPRO for independent certification process. Ó2020 EPRO Services, Inc. EproGSEV20.VB.v1.08.20gs 10 C. Take care to prevent contamination and damage during application stages and curing. Machinery, additional trades, or general construction shall NOT take place over the membrane until inspection is complete and concrete has been placed. The membrane shall always be properly protected when equipment is operated near the membrane. D. Prevent damage during the placement of reinforcement steel and overburden. E. Damage Observation: Prior to the placement of concrete a visual inspection to confirm no damage has occurred from construction traffic or during the placement of reinforcement steel is recommended. 3.4 REPAIRS A. Underslab: 1. Inspect damaged area to determine which system components have been damaged. 2. If the Geo-Seal EV20 sheet has not been compromised, patch only the areas that have been damaged by re-installing the damaged materials. The patch should extend 6 inches beyond the damaged area in all directions. 3. If the Geo-Seal EV20 sheet has been breached but no additional system components have been installed, install a patch below and above the base sheet that extends 6 inches beyond the damaged area. Area shall be sealed using the specified method for sealing the base sheet. 4. Refer to manufacturer’s detail for further repair clarification. End of Section GEO-SEAL FILM EV20 AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB ASSEMBLY SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.100.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.100.1 GEO-SEAL EV20 UNDERSLAB ASSEMBLY.dwg [Detail] December 09, 2021 - 12:08pm GEO-SEAL EV20 GEO-SEAL CORE - 60 MIL 6" OVERLAP 3"AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE EV20 OVERLAP SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.110.4 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.110.4 GEO-SEAL EV20 BASE OVERLAP.dwg [Detail] December 09, 2021 - 12:09pm GEO-SEAL CORE - 30 MIL REINFORCEMENT FABRIC ZIP TIE GEO-SEAL FILM EV20 AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB PIPE PENETRATION SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.120.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.120.1 GEO-SEAL EV20 UNDERSLAB PIPE PENETRATION.dwg [Detail] December 09, 2021 - 12:09pm 6" GEO-SEAL CORE - 60 MIL GEO-SEAL FILM EV20 3"AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB GRADE BEAM 6" TERMINATION SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.130.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.130.1 GEO-SEAL EV20 UNDERSLAB GRADE BEAM 6 TERMINATION.dwg [Detail] December 09, 2021 - 12:09pm GEO-SEAL CORE - 60 MIL 6" 3" GEO-SEAL FILM EV20 AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE VERTICAL TERMINATION SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.131.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.131.1 VERTICAL TERMINATION.dwg [Detail] December 09, 2021 - 12:09pm GEO-SEAL FILM EV20 AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB PERIMETER FOOTING TERMINATION SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.132.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.132.1 UNDERSLAB GEO-SEAL EV20 PERIMETER FOOTING TERMINATION.dwg [Detail] December 09, 2021 - 12:09pm GEO-SEAL CORE 60 MIL GEO-SEAL CORE 60 MIL 6" OVERLAP GEO-SEAL FILM EV20 6" CENTERED ON SEAM AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB ASSEMBLY REPAIR SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.170.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.170.1 UNDERSLAB ASSEMBLY REPAIR.dwg [Detail] December 09, 2021 - 12:09pm GEO-SEAL FILM EV20 GEO-SEAL CORE - 30 MIL REINFORCEMENT FABRIC ZIP TIE STEP 1 STEP 2 STEP 3 STEP 4 REINFORCEMENT FABRIC REINFORCEMENT FABRIC GEO-SEAL FILM EV20 GEO-SEAL CORE - 30 MIL GEO-SEAL FILM EV20 GEO-SEAL CORE - 30 MIL GEO-SEAL FILM EV20 GEO-SEAL CORE - 30 MIL AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB PIPE PENETRATION SEQUENCE SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.900.1-MOD DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.900.1 UNDERSLAB PIPE PENETRATION SEQUENCE.dwg [Detail] December 09, 2021 - 12:09pm 6"6" 6" 3" STEP 1 STEP 2 STEP 3 GEO-SEAL FILM EV20 GEO-SEAL CORE - 60 MILGEO-SEAL CORE - 60 MIL GEO-SEAL CORE - 60 MIL GEO-SEAL FILM EV20 GEO-SEAL CORE - 60 MIL AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB TERMINATION @ PERIMETER FOOTING SEQUENCE SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.901.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.901.1 UNDERSLAB TERMINATION @ PERIMETER FOOTING SEQUENCE.dwg [Detail] December 09, 2021 - 12:09pm STEP 1 STEP 2 STEP 3 GEO-SEAL CORE - 60 MIL 6" MIN. GEO-SEAL CORE - 60 MIL 6" GEO-SEAL CORE - 60 MIL 6" 3" GEO-SEAL FILM EV20 GEO-SEAL FILM EV20 AS A SUPPLIER OF FINISHED RPODUCTS ONLY, EPRO SERVICES, INC. DOES NOT ASSUME RESPONSIBILITY FOR ERRORS IN DESIGN, ENGINEERING OR DIMENSIONS.THE PROJECT TEAM MUST VERIFY ALL DIMENSIONS AND SUITABILITY OF DETAILS. THE PRODUCTS LISTED ARE TRADEMARKS OF EPRO SERVICES, INC.PAGE 1 OF 1 1328 E. KELLOGG DRIVE WICHITA, KS 67211 1-800-882-1896 EPROINC.COM RJT NTS DRAWN BY SCALE DATE UNDERSLAB TERMINATION @ WALL SEQUENCE SYSTEM DESCRIPTION GEO-SEAL EV20 SYSTEM NAME 49.902.1 DRAWIMG NUMBER 04/08/2021 G:\My Drive\Epro Master Folder\Drafting\Details\Underslab\Geo-Seal EV20\49.902.1 UNDERSLAB TERMINATION @ WALL SEQUENCE.dwg [Detail] December 09, 2021 - 12:09pm Appendix C VIMS As-Built Drawings SEE DETAIL 1/VM-2 SEE DETAIL 6 & 8/VM-2 SEE DETAIL 5/VM-2 SEE DETAIL 3/VM-2 SEE DETAIL 4 & 8/VM-2 SEE DETAIL 2/VM-2 SEE DETAIL 7/VM-2 1515 S. MINT ST TENANT SPACE NEW CONCRETE FOOTING 1513 S. MINT ST TENANT SPACE PREVIOUSLY EXISTING SUB-GRADE INTERIOR RAMP REMOVED AND BROUGHT TO GRADE USING BACKFILL AND BASE COURSE TO MATCH SURROUNDINGS - VIMS PIPING IS ON SAME GRADE AS REST OF VIMS PIPING. SEE DETAIL 2/VM-2 SEE DETAIL 9/VM-2 SEE DETAIL 9/VM-2 SEE DETAIL 9/VM-2 REVISION NO. 1DATE: 7-29-22 2923 South Tryon Street-Suite 100 Charlotte, North Carolina 28203 704-586-0007(p) 704-586-0373(f) License # C-1269 / #C-245 Geology JOB NO. LEH-004 FIGURE NO. VM-1 1513-1515 S. MINT STREET CHARLOTTE, NORTH CAROLINA VIMS AS-BUILT LAYOUT VIMS SPECIFICATIONS 1.VIMS VAPOR BARRIER IS GEO-SEAL EV20S MANUFACTURED BY EPRO SERVICES, INC. THE VAPOR BARRIER WAS INSTALLED AS SPECIFIED HEREIN AND PER MANUFACTURER INSTALLATION INSTRUCTIONS TO CREATE A CONTINUOUS BARRIER BELOW GROUND FLOOR SLABS AND ATTACHED/SEALED TO CONCRETE SURFACES OF FOOTINGS AND EXTERIOR/EXISTING WALLS. A MINIMUM 5-INCH THICK BASE COURSE CONSISTING OF CLEAN #57 STONE WASINSTALLED BENEATH THE VIMS VAPOR BARRIER. 2.HORIZONTAL COLLECTION PIPE CONSISTS OF 4-INCH SCH 40 PVC (OR OTHERWISE NOTED IN THE DRAWINGS). SUB-SLAB SLOTTED VAPOR COLLECTION PIPE IS THREADED FLUSH JOINT OR SLIPJOINT 4-INCH SCH 40 PVC PIPE WITH 0.020-INCH SLOT WIDTH AND 1/8-INCH SLOT SPACING. VIMS BELOW AND ABOVE GRADE SOLID PIPING IS NOT TRAPPED AND IS SLOPED A MINIMUM OF 1/8 UNITVERTICAL IN 12 UNITS HORIZONTAL (1% SLOPE) TO GRAVITY DRAIN. SOLID SECTIONS OF HORIZONTAL COLLECTION PIPE WAS SUPPORTED TO PREVENT PIPE SAG OR LOW POINT AND MAINTAIN 1% SLOPE TOWARD SLOTTED SECTIONS TO DRAIN CONDENSATION. TRACER WIRE WAS PLACED ALONG HORIZONTAL PIPE BELOW VAPOR BARRIER TO LOCATE PIPE DURING FUTURE BUILDING MODIFICATIONS. 3.4-INCH CAST IRON RISER DUCT PIPING WAS INSTALLED TO CONNECT EACH SLAB PENETRATIONLOCATION TO A ROOFTOP EXHAUST DISCHARGE POINT WITH TURBINE FAN (SEE SPECIFICATION #4). ABOVE-SLAB RISER DUCT PIPE RUNS BETWEEN THE SLAB PENETRATION AND THE ROOFTOPEXHAUST DISCHARGE WAS INSTALLED PER APPLICABLE BUILDING CODE AND AS SPECIFIED IN THE CONSTRUCTION DOCUMENTS AND DRAWINGS. 4.RISER DUCT PIPING EXTENDS IN A VERTICAL ORIENTATION THROUGH THE BUILDING ROOF ANDTERMINATES A MINIMUM OF 2 FT ABOVE ANY WALLS, PARAPETS, ETC. IN THE VICINITY OF THE RISER/FAN. AN EMPIRE MODEL TV04SS TURBINE VENTILATOR FAN WAS INSTALLED ON THEEXHAUST DISCHARGE END OF EACH MINIMUM OF 10 FT FROM ANY OPERABLE OPENING OR AIR INTAKE INTO THE BUILDING. NOTE THAT DISCHARGE LOCATIONS ON THE ROOFTOP DEPICTED INTHE VAPOR MITIGATION PLAN MAY HAVE BEEN REPOSITIONED AS LONG AS THE NEW POSITION MET THE REQUIREMENTS PRESENTED ABOVE. A 4-INCH COUPLING WAS INSTALLED AT THEDISCHARGE END OF THE 4-INCH RISER DUCT PIPE AND THE FAN IS SECURED TO THE PVC RISER IN A VERTICAL ORIENTATION. AN ELECTRICAL JUNCTION BOX (120V, 60HZ AC REQUIRED) WAS INSTALLED NEAR THE FAN LOCATION ON THE ROOFTOP FOR CONVERSION TO ELECTRIC FANS, IF REQUIRED. ALL WIRING AND ELECTRICAL WAS INSTALLED PER APPLICABLE BUILDING AND ELECTRICAL CODES. 5.ABOVE-SLAB ACCESSIBLE RISER DUCT PIPING IS PERMANENTLY IDENTIFIED BY MEANS OF A TAG OR STENCIL AT A MINIMUM OF ONCE EVERY 10-LINEAR FT WITH "VAPOR SYSTEM - CONTACT OWNER.” LABELS ARE ALSO FIXED TO THE TURBINE FANS IN AN ACCESSIBLE LOCATION ON THE ROOFTOP. 6.MONITORING POINTS CONSIST OF 2-INCH DIAMETER SCH 40 PVC PIPE WITH A 90-DEGREE ELBOW TO FORM AN "L" SHAPE. A MINIMUM OF 6" SECTION OF PIPING IS SET WITHIN THE BASE COURSE LAYER WITH AN OPEN-ENDED PIPE OR PIPE PROTECTION SCREEN AT THE TERMINATION. THE PIPE TERMINATION IS ENCASED WITHIN THE BASE COURSE LAYER. THE HORIZONTAL PIPING WAS SLOPED A MINIMUM OF 1/8 UNIT VERTICAL BY 12 UNITS HORIZONTAL (1% SLOPE) TO GRAVITY DRAIN TOWARDS THE PIPE TERMINATION AND PREVENT MOISTURE FROM COLLECTING AT THE 90-DEGREE ELBOW. A 4-INCH DIAMETER ADJUSTABLE FLOOR CLEAN-OUT (ZURN INDUSTRIES MODEL #CO2450-PV4, OR EQUIVALENT) WAS INSTALLED AND SET FLUSH WITH THE FINISHEDCONCRETE SURFACE. MONITORING POINT INTAKE IS A MINIMUM 5-FT FROM EXTERIOR FOOTING. 7.THIS VIMS PLAN WAS INTENDED TO BE USED FOR DIRECTION OF VIMS COMPONENT INSTALLATION ONLY AND WAS NOT INTENDED TO GUIDE CONSTRUCTION OF STRUCTURAL COMPONENTS NOT RELATED TO THE VIMS. CONSTRUCTION CONTRACTOR VERIFIED CONSISTENCY OF VIMS DETAILS WITH APPLICABLE STRUCTURAL, ARCHITECTURAL, MECHANICAL, AND PLUMBING PLANS ANDRESOLVED ANY INCONSISTENCIES PRIOR TO VIMS INSTALLATION. 8.INSPECTIONS: INSPECTIONS OF EACH COMPONENT OF THE VIMS WAS CONDUCTED BY THE ENGINEER, OR ENGINEER'S DESIGNEE, TO CONFIRM VIMS COMPONENTS WERE INSTALLED PER THE APPROVED DESIGN. THE REQUIRED INSPECTION COMPONENTS INCLUDED: (1) INSPECTION OF SUB-SLAB PIPING LAYOUT, (2) GRAVEL PLACEMENT, AND (3) MONITORING POINT PLACEMENTPRIOR TO INSTALLING VAPOR BARRIER; (4) INSPECTION OF VAPOR BARRIER PRIOR TO POURING CONCRETE; (5) INSPECTION OF ABOVE-GRADE PIPING LAYOUT; AND (6) INSPECTION OF TURBINEFANS AND RISER DUCT PIPE CONNECTIONS. INSPECTIONS WERE COMBINED WHEN POSSIBLE DEPENDING ON THE CONSTRUCTION SEQUENCE/SCHEDULE. THE CONSTRUCTIONCONTRACTOR(S) COORDINATED WITH THE ENGINEER TO PERFORM THE REQUIRED INSPECTIONS. DEQ WAS CONTACTED 48-HOURS PRIOR TO THE INSPECTION BEING CONDUCTED. FIELD NOTES,PHOTOGRAPHS, AND ANY ADDITIONAL INSPECTION DOCUMENTATION ARE INCLUDED IN THE FINAL DELIVERABLE TO DEQ. 9.CONSTRUCTION CONTRACTORS AND SUB-CONTRACTORS USED "LOW OR NO VOC" PRODUCTSAND MATERIALS, WHEN POSSIBLE. THE CONSTRUCTION CONTRACTOR AND SUB-CONTRACTORS PROVIDED SAFETY DATA SHEETS (SDS) TO THE ENGINEER FOR PRODUCTS AND MATERIALS USEDDURING CONSTRUCTION. SDS SHEETS ARE INCLUDED IN FINAL REPORTING TO DEQ. 10.CONSTRUCTION CONTRACTORS AND SUB-CONTRACTORS AVOIDED THE USE OF TEMPORARY FORM BOARDS OR HOLLOW PIPING (TYPICALLY USED TO SUPPORT UTILITIES PRIOR TO SLAB POURS) THAT PENETRATE THE VAPOR BARRIER WHERE POSSIBLE. IF TEMPORARY FORM BOARDS WERE USED, THE SIZE AND NUMBER OF PENETRATIONS THROUGH THE VAPOR BARRIER WERELIMITED AND SMALL DIAMETER STAKES (I.E. METAL STAKES) WERE USED. IN ALL CASES, AS FORM BOARDS ARE REMOVED, THE CONTRACTOR OR SUB-CONTRACTORS SEALED ALL PENETRATIONSIN ACCORDANCE WITH VAPOR BARRIER MANUFACTURER INSTALLATION INSTRUCTIONS. LEGEND EXTENT OF VAPOR BARRIER - SEE SPECIFICATION #1 4-INCH SLOTTED SCH 40 PVC PIPE 4-INCH SOLID SCH 40 PVC PIPE 4-INCH SOLID CAST IRON RISER WITH WIND DRIVEN TURBINE AT TERMINUS ON ROOF 2" DIA SOLID PVC PRESSURE MONITORING POINT WITH FLUSH-MOUNTED COVER (INTAKE POSITIONED MINIMUM 5-FT FROM EXTERIOR FOOTING) PORTION OF BUILDING CURRENTLY UNDER CONSTRUCTION (1513 S. MINT STREET) 07/29/22 MP-3 MP-2 MP-1 F-2 F-1F-3 S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Figures\Figures_VMP_As-Built.dwg, VM-1, 7/29/2022 12:28:55 PM, SVincent VIMS AT EXTERIOR WALL (TYPICAL) NTS 3 CONCRETE FLOOR SLAB BASE COURSE (SEE SPECIFICATION #1) EXISTING CONCRETE FOOTING (FIELD VERIFY) EXISTING CMU WALL EXISTING EXTERIOR BRICK WALL SUBBASE VAPOR BARRIER (SEE SPECIFICATION #1)VAPOR BARRIER SEALED TO CONCRETE PER MANUFACTURERS INSTRUCTIONS VM-2 VIMS AT EXTERIOR WALL WITH RISER PIPE PENETRATION (TYPICAL) NTS 4 CONCRETE FLOOR SLAB EXISTING CONCRETE FOOTING (FIELD VERIFY) EXISTING CMU WALL EXISTING EXTERIOR BRICK WALL SUBBASE VAPOR BARRIER PENETRATION SEALED TO PIPE PER MANUFACTURERS INSTRUCTIONS TO EXHAUST POINT ON ROOF 4" SCH 40 PVC 90° ELBOW BASE COURSE (SEE SPECIFICATION #1) 4" SCH SOLID PVC PIPE SET WITHIN 5" BASE COURSE (SEE SPECIFICATION #2) VAPOR BARRIER SEALED TO CONCRETE PER MANUFACTURERS INSTRUCTIONS 4" CAST IRON PIPE VM-2 VIMS AT EXISTING INTERIOR CMU WALL (TYPICAL) NTS 5 CONCRETE FLOOR SLAB BASE COURSE (SEE SPECIFICATION #1) EXISTING CMU WALL SUBBASE VAPOR BARRIER (SEE SPECIFICATION #1) VAPOR BARRIER SEALED TO CONCRETE PER MANUFACTURERS INSTRUCTIONS VM-2 VIMS VAPOR BARRIER AND BASE COURSE (TYPICAL)1 BASE COURSE - CLEAN #57 STONE MIN 5" THICK BENEATH VAPOR BARRIER (SEE SPECIFICATION #1) VAPOR BARRIER (SEE SPECIFICATION #1) CONCRETE FLOOR SLAB SUBBASE NTSVM-2 VIMS SLOTTED COLLECTION PIPE (TYPICAL)2 4" SCH 40 THREADED FLUSH JOINT SLOTTED PVC PIPE (0.020" SLOT WIDTH, 1/8" SLOT SPACING) SET WITHIN MIN 5" BASE COURSE (SEE SPECIFICATION #2) VAPOR BARRIER (SEE SPECIFICATION #1) SUBBASE NTS CONCRETE FLOOR SLAB VM-2 VIMS AT EXISTING INTERIOR CMU WALL WITH RISER PIPE PENETRATION (TYPICAL) NTS 6 EXISTING CMU WALL SUBBASE VAPOR BARRIER SEALED TO CONCRETE PER MANUFACTURERS INSTRUCTIONS BASE COURSE (SEE SPECIFICATION #1) 4" SCH 40 PVC 90° ELBOW 4" SCH SOLID PVC PIPE SET WITHIN 5" BASE COURSE (SEE SPECIFICATION #2) VAPOR BARRIER PENETRATION SEALED TO PIPE PER MANUFACTURERS INSTRUCTIONS VAPOR BARRIER (SEE SPECIFICATION #1) CONCRETE FLOOR SLAB TO EXHAUST POINT ON ROOF TO SLOTTED HORIZONTAL COLLECTION PIPING 4" CAST IRON PIPE VM-2 VIMS TURBINE FAN & EXHAUST (TYPICAL)8 NTS TURBINE FAN (EMPIRE MODEL TV04SS OR APPROVED EQUIVALENT) ELECTRICAL JUNCTION BOX FOR POTENTIAL FUTURE VACUUM FAN (SEE SPECIFICATION #4) 4" SCH 40 PVC THROUGH ROOF FLASHING ROOFTOP VM-2 4" SCH SOLID PVC PIPE SET WITHIN 5" BASE COURSE (SEE SPECIFICATION #2) VAPOR BARRIER PENETRATION SEALED TO PIPE PER MANUFACTURERS INSTRUCTIONS 4" SCH 40 PVC 90° ELBOW TO EXHAUST POINT ON ROOF TO SLOTTED HORIZONTAL COLLECTION PIPING VIMS AT STEEL COLUMN (TYPICAL) NTS 7 VM-2 EXTERIOR GRADE STEEL COLUMN ANCHORED TO FOOTING 4" CAST IRON PIPE VAPOR BARRIER (SEE SPECIFICATION #1) BASE COURSE (SEE SPECIFICATION #1) SUBBASE NEW FOOTING FINISHED FLOOR SLAB 2" SCH 40 PVC SET WITHIN GRAVEL LAYER 2" DRAIN EXPANSION TEST PLUG VIMS MONITORING POINT - TYPICAL DETAIL VIEW NTS 9 VM-2 VAPOR BARRIER PENETRATION SEALED TO PIPE PER MANUFACTURER INSTRUCTIONS 2" SCH 40 PVC 90 DEGREE ELBOW FLOOR CLEANOUT, ADJUSTABLE, 4" DIA ZURN INDUSTRIES MODEL #CO2450-PV4 (OR ENGINEER APPROVED EQUIVALENT) FLUSH WITH FINISHED FLOOR BASE COURSE 4" x 2" FLUSH REDUCER BUSHING OPEN-ENDED PIPE REVISION NO. 1DATE: 7-29-22 2923 South Tryon Street-Suite 100 Charlotte, North Carolina 28203 704-586-0007(p) 704-586-0373(f) License # C-1269 / #C-245 Geology CROSS SECTION DETAILS JOB NO. LEH-004 FIGURE NO. VM-2 1513-1515 S. MINT STREET CHARLOTTE, NORTH CAROLINA 07/29/22 VIMS SPECIFICATIONS 1.VIMS VAPOR BARRIER IS GEO-SEAL EV20S MANUFACTURED BY EPRO SERVICES, INC. THE VAPOR BARRIER WAS INSTALLED AS SPECIFIED HEREIN AND PER MANUFACTURER INSTALLATION INSTRUCTIONS TO CREATE A CONTINUOUS BARRIER BELOW GROUND FLOOR SLABS AND ATTACHED/SEALED TO CONCRETE SURFACES OF FOOTINGS AND EXTERIOR/EXISTING WALLS. A MINIMUM 5-INCH THICK BASE COURSE CONSISTING OF CLEAN #57 STONE WAS INSTALLED BENEATH THE VIMS VAPOR BARRIER. 2.HORIZONTAL COLLECTION PIPE CONSISTS OF 4-INCH SCH 40 PVC (OR OTHERWISE NOTED IN THE DRAWINGS). SUB-SLAB SLOTTED VAPOR COLLECTION PIPE IS THREADED FLUSH JOINT OR SLIP JOINT 4-INCH SCH 40 PVC PIPE WITH 0.020-INCH SLOT WIDTH AND 1/8-INCH SLOT SPACING. VIMS BELOW AND ABOVE GRADE SOLID PIPING IS NOT TRAPPED AND IS SLOPED A MINIMUM OF 1/8 UNIT VERTICAL IN 12 UNITS HORIZONTAL (1% SLOPE) TO GRAVITY DRAIN. SOLID SECTIONS OF HORIZONTAL COLLECTION PIPE WAS SUPPORTED TO PREVENT PIPE SAG OR LOW POINT AND MAINTAIN 1% SLOPE TOWARD SLOTTED SECTIONS TO DRAIN CONDENSATION. TRACER WIRE WAS PLACED ALONG HORIZONTAL PIPE BELOW VAPOR BARRIER TO LOCATE PIPE DURING FUTURE BUILDING MODIFICATIONS. 3.4-INCH CAST IRON RISER DUCT PIPING WAS INSTALLED TO CONNECT EACH SLAB PENETRATION LOCATION TO A ROOFTOP EXHAUST DISCHARGE POINT WITH TURBINE FAN (SEE SPECIFICATION #4). ABOVE-SLAB RISER DUCT PIPE RUNS BETWEEN THE SLAB PENETRATION AND THE ROOFTOP EXHAUSTDISCHARGE WAS INSTALLED PER APPLICABLE BUILDING CODE AND AS SPECIFIED IN THE CONSTRUCTION DOCUMENTS AND DRAWINGS. 4.RISER DUCT PIPING EXTENDS IN A VERTICAL ORIENTATION THROUGH THE BUILDING ROOF AND TERMINATES A MINIMUM OF 2 FT ABOVE ANY WALLS, PARAPETS, ETC. IN THE VICINITY OF THE RISER/FAN. AN EMPIRE MODEL TV04SS TURBINE VENTILATOR FAN WAS INSTALLED ON THE EXHAUST DISCHARGE END OF EACH MINIMUM OF 10 FT FROM ANY OPERABLE OPENING OR AIR INTAKE INTO THE BUILDING. NOTE THAT DISCHARGE LOCATIONS ON THE ROOFTOP DEPICTED IN THE VAPOR MITIGATION PLAN MAY HAVE BEEN REPOSITIONED AS LONG AS THE NEW POSITION MET THE REQUIREMENTS PRESENTED ABOVE. A 4-INCH COUPLING WAS INSTALLED AT THE DISCHARGE END OF THE 4-INCH RISER DUCT PIPE AND THE FAN IS SECURED TO THE PVC RISER IN A VERTICAL ORIENTATION. AN ELECTRICAL JUNCTION BOX (120V, 60HZ AC REQUIRED) WAS INSTALLED NEAR THE FAN LOCATION ON THE ROOFTOP FOR CONVERSION TO ELECTRIC FANS, IF REQUIRED. ALL WIRING AND ELECTRICAL WAS INSTALLED PER APPLICABLE BUILDING AND ELECTRICAL CODES. 5.ABOVE-SLAB ACCESSIBLE RISER DUCT PIPING IS PERMANENTLY IDENTIFIED BY MEANS OF A TAG OR STENCIL AT A MINIMUM OF ONCE EVERY 10-LINEAR FT WITH "VAPOR SYSTEM - CONTACT OWNER.” LABELS ARE ALSO FIXED TO THE TURBINE FANS IN AN ACCESSIBLE LOCATION ON THE ROOFTOP. 6.MONITORING POINTS CONSIST OF 2-INCH DIAMETER SCH 40 PVC PIPE WITH A 90-DEGREE ELBOW TO FORM AN "L" SHAPE. A MINIMUM OF 6" SECTION OF PIPING IS SET WITHIN THE BASE COURSE LAYER WITH AN OPEN-ENDED PIPE OR PIPE PROTECTION SCREEN AT THE TERMINATION. THE PIPE TERMINATION IS ENCASED WITHIN THE BASE COURSE LAYER. THE HORIZONTAL PIPING WAS SLOPED A MINIMUM OF 1/8 UNIT VERTICAL BY 12 UNITS HORIZONTAL (1% SLOPE) TO GRAVITY DRAIN TOWARDS THE PIPE TERMINATION AND PREVENT MOISTURE FROM COLLECTING AT THE 90-DEGREE ELBOW. A 4-INCH DIAMETER ADJUSTABLE FLOOR CLEAN-OUT (ZURN INDUSTRIES MODEL #CO2450-PV4, OR EQUIVALENT) WAS INSTALLED AND SET FLUSH WITH THE FINISHED CONCRETE SURFACE. MONITORING POINT INTAKE ISA MINIMUM 5-FT FROM EXTERIOR FOOTING. 7.THIS VIMS PLAN WAS INTENDED TO BE USED FOR DIRECTION OF VIMS COMPONENT INSTALLATION ONLY AND WAS NOT INTENDED TO GUIDE CONSTRUCTION OF STRUCTURAL COMPONENTS NOT RELATED TO THE VIMS. CONSTRUCTION CONTRACTOR VERIFIED CONSISTENCY OF VIMS DETAILS WITH APPLICABLE STRUCTURAL, ARCHITECTURAL, MECHANICAL, AND PLUMBING PLANS AND RESOLVED ANYINCONSISTENCIES PRIOR TO VIMS INSTALLATION. 8.INSPECTIONS: INSPECTIONS OF EACH COMPONENT OF THE VIMS WAS CONDUCTED BY THE ENGINEER, OR ENGINEER'S DESIGNEE, TO CONFIRM VIMS COMPONENTS WERE INSTALLED PER THE APPROVED DESIGN. THE REQUIRED INSPECTION COMPONENTS INCLUDED: (1) INSPECTION OF SUB-SLAB PIPING LAYOUT, (2) GRAVEL PLACEMENT, AND (3) MONITORING POINT PLACEMENT PRIOR TO INSTALLING VAPOR BARRIER; (4) INSPECTION OF VAPOR BARRIER PRIOR TO POURING CONCRETE; (5) INSPECTION OF ABOVE-GRADE PIPING LAYOUT; AND (6) INSPECTION OF TURBINE FANS AND RISER DUCT PIPECONNECTIONS. INSPECTIONS WERE COMBINED WHEN POSSIBLE DEPENDING ON THE CONSTRUCTION SEQUENCE/SCHEDULE. THE CONSTRUCTION CONTRACTOR(S) COORDINATED WITH THE ENGINEER TOPERFORM THE REQUIRED INSPECTIONS. DEQ WAS CONTACTED 48-HOURS PRIOR TO THE INSPECTION BEING CONDUCTED. FIELD NOTES, PHOTOGRAPHS, AND ANY ADDITIONAL INSPECTION DOCUMENTATION ARE INCLUDED IN THE FINAL DELIVERABLE TO DEQ. 9.CONSTRUCTION CONTRACTORS AND SUB-CONTRACTORS USED "LOW OR NO VOC" PRODUCTS AND MATERIALS, WHEN POSSIBLE. THE CONSTRUCTION CONTRACTOR AND SUB-CONTRACTORS PROVIDEDSAFETY DATA SHEETS (SDS) TO THE ENGINEER FOR PRODUCTS AND MATERIALS USED DURING CONSTRUCTION. SDS SHEETS ARE INCLUDED IN FINAL REPORTING TO DEQ. 10.CONSTRUCTION CONTRACTORS AND SUB-CONTRACTORS AVOIDED THE USE OF TEMPORARY FORM BOARDS OR HOLLOW PIPING (TYPICALLY USED TO SUPPORT UTILITIES PRIOR TO SLAB POURS) THAT PENETRATE THE VAPOR BARRIER WHERE POSSIBLE. IF TEMPORARY FORM BOARDS WERE USED, THESIZE AND NUMBER OF PENETRATIONS THROUGH THE VAPOR BARRIER WERE LIMITED AND SMALL DIAMETER STAKES (I.E. METAL STAKES) WERE USED. IN ALL CASES, AS FORM BOARDS ARE REMOVED,THE CONTRACTOR OR SUB-CONTRACTORS SEALED ALL PENETRATIONS IN ACCORDANCE WITH VAPOR BARRIER MANUFACTURER INSTALLATION INSTRUCTIONS.S:\AAA-Master Projects\Lischerong Enterprises and Holdings (LEH)\S. Mint St\1513-1521 Assessments\VIMS Install Report\Figures\VIMP-Details_As-Built.dwg, VM-2, 7/29/2022 12:26:59 PM, SVincent Appendix D Product Specification Sheets TURBINE VENTILATORS CONSTRUCTION SPECIFICATIONS “A” THROAT SIZE GUAGE NO. OF BRACES BRACE MATERIALCROWN GALV.BLADE GALV.THROAT GALV. 4 24 28 26 3 ALUMINUM 6 24 28 26 3 ALUMINUM 8 24 28 26 3 ALUMINUM 10 24 28 26 3 ALUMINUM 12 24 28 24 3 ALUMINUM 14 22 26 24 3 ALUMINUM 16 22 26 24 3 STEEL 18 22 26 24 4 STEEL 20 20 26 24 4 STEEL 24 20 26 22 4 STEEL DIMENSIONAL AND PERFORMACE DATA “A” THROAT SIZE “B” HEIGHT “C” OVERALL WIDTH EXHAUSTED CAPACITY* APPROX. SHIPPING WEIGHT 4 12 10 1/4 125 5 6 14 1/2 12 3/4 147 7 8 15 14 1/4 255 8 10 16 1/4 16 1/4 425 11 12 17 19 631 13 14 19 3/4 22 3/4 700 21 16 21 3/4 25 1/2 950 31 18 24 29 1200 38 20 25 1/4 31 5/8 1700 46 24 28 1/4 35 3/4 2350 58 *4 MPHWIND CFM Dimensional Data (inches and [ mm ]) are Subject to Manufacturing Tolerances and Change Without Notice SPECIFICATION SHEET TAG _______ * Regularly furnished unless otherwise specified. Zurn Industries, LLC | Light Commercial Plumbing Products 1801 Pittsburgh Avenue, Erie, PA U.S.A. 16502 · Ph. 855-663-9876, Fax 814-454-7929 In Canada | Zurn Industries Limited 3544 Nashua Drive, Mississauga, Ontario L4V 1L2 · Ph. 905-405-8272, Fax 905-405-1292 www.zurn.com Rev. C Date:12/13/17 C.N. No.139307 Prod. | Dwg. No.CO2450 CO-2450 ADJUSTABLE FLOOR CLEANOUT Typical Installation 'A' Connections 'B' CO‐2450‐PV2 2 [51] PVC Hub 1‐3/4 [44] CO‐2450‐PV3 3 [76] PVC Hub 3 [76] CO‐2450‐PV4 4 [102] PVC Hub 3‐7/16 [87] CO‐2450‐AB2 2 [51] ABS Hub 1‐3/4 [44] CO‐2450‐AB3 3 [76] ABS Hub 3 [76] CO‐2450‐AB4 4 [102] ABS Hub 3‐7/16 [87] Product Dimensions in In [mm]Engineering Specification: Zurn CO-2450 Adjustable Floor Cleanout, recommended for foot traffic and light-duty applications. This cleanout is furnished with a PVC or ABS body, with an adjustable nickel cover and an ABS taper thread plug. OPTIONS (Check/specify appropriate options) PRODUCT ____ CO-2450-PV2 ____ CO-2450-PV3 ____ CO-2450-PV4 ____ CO-2450-AB2 ____ CO-2450-AB3 ____ CO-2450-AB4 SUFFIXES ____-CM Carpet Marker ____-VP Vandal Proof Applies to PV3, PV4 AB3 and AB4 Appendix E VIMS Installation Photographs Photograph 2: Close-up view of one of the three monitoring points and adequate gravel layer located in the space.LEH-0042923 S. Tryon Street, Suite 100 Charlotte, NC 28203704.586.0007(p) 704.586.0373(f) Photograph 1: General view of the stone base and sub-slab piping network in the 1515 S. Mint Street tenant space. QUALITY PRODUCTS CO.1515 SOUTH MINT STREETCHARLOTTE, NORTH CAROLINA LEH-0042923 S. Tryon Street, Suite 100 Charlotte, NC 28203704.586.0007(p) 704.586.0373(f) Photograph 3A & 3B: Representative over view of EPRO Geo-Seal® 20 vapor barrier and smoke testing completed by qualified contractor. QUALITY PRODUCTS CO.1515 SOUTH MINT STREETCHARLOTTE, NORTH CAROLINA Photograph 4: Close-up view of representative seal accomplished around penetrations to the vapor barrier. Photograph 6: Representative view of utility upfit area with repaired vapor barrier.LEH-0042923 S. Tryon Street, Suite 100 Charlotte, NC 28203704.586.0007(p) 704.586.0373(f) QUALITY PRODUCTS CO.1515 SOUTH MINT STREETCHARLOTTE, NORTH CAROLINA Photograph 5: Representative view of utility upfit area with clean gravel placed. Photograph 8A & 8B: Representative view of turbine ventilator installed on roof.LEH-0042923 S. Tryon Street, Suite 100 Charlotte, NC 28203704.586.0007(p) 704.586.0373(f) QUALITY PRODUCTS CO.1515 SOUTH MINT STREETCHARLOTTE, NORTH CAROLINA Photograph 7: Representative view of risers installed with adequate labels and pitched to ensure proper drainage. “Vapor Mitigation System – Contact Maintenance” Appendix F Field Forms and Field Data Table 1VIMS Pilot Test Vacuum MonitoringQuality Products Co.1515 South Mint StreetCharlotte, North CarolinaBrownfields Project No. 22016-18-060H&H Job No. LEH-004Baseline Initial Reading10 minute readingF‐1 0.000‐2.438‐2.742F‐2 0.000‐1.866‐1.796F‐3 0.000‐2.857‐2.435MP‐1 0.000‐0.170‐0.171MP‐2 0.000‐0.337‐0.338MP‐3 0.000‐0.242‐0.243Notes1) American Eagle Extreme fans were used on all risers during testing.Point IDVacuum Measurements (in‐WC)Date Point Type May 2, 2022FanMonitoring Pointhttps://harthick.sharepoint.com/sites/MasterFiles-1/Shared Documents/AAA VIMS/LEH-004 - Juliana/Pilot Test 05-02-22/1515 Pilot Test DataR17/29/2022Hart & Hickman, PC 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,QGRRU3DUDPHWHUV2XWGRRU3DUDPHWHUV6DPSOLQJ3HULRGEŽƚĞ͗WĞƌEYtDsĂƉŽƌ/ŶƚƌƵƐŝŽŶ'ƵŝĚĂŶĐĞ͕ƐŚƵƚͲŝŶƚĞƐƚĂŶĚŚĞůŝƵŵůĞĂŬĐŚĞĐŬŵƵƐƚďĞƉĂƐƐĞĚďĞĨŽƌĞƐĂŵƉůŝŶŐ͗͘ͰhƐĞƌƐͰŵǀĂǁƚĞƌͰƌŽƉďŽdžͰLJKƚŚĞƌͰ&ŽƌŵĚŝƚƐͰ/YͲ^^sͰsĂƉŽƌ^ĂŵƉůŝŶŐ&ŽƌŵƐͺsϲ͘Ϭ^ƵďͲ^ůĂďͬ^Žŝů'ĂƐ^ĂŵƉůŝŶŐsĂƉŽƌ^ĂŵƉůŝŶŐ&ŝĞůĚ&Žƌŵ,ĂƌƚΘ,ŝĐŬŵĂŶ͕WLEH.004 ELL 81 F, sunnyMP-3/DUP1.4 L5858/60076/1/22 10140 mL/m0954 -1781 60 60142960959 -50949 -2678MP-11.4 L1038 -27113666/1/22 101043 -1982 60 78 60140 mL/m162191050 -5 Appendix G Laboratory Analytical Report   Laboratory's liability in any claim relating to analyses performed shall be limited to, at laboratory's option, repeating the analysis in question at laboratory's expense, or the refund of the charges paid for performance of said analysis.   6/13/2022 Hart & Hickman (Charlotte) Juliana Lima 2923 South Tryon St. Ste 100 Charlotte, NC, 28203 Ref: Analytical Testing Lab Report Number: 22-153-0001 Client Project Description: LEH-004 Dear Juliana Lima: Waypoint Analytical, LLC (Charlotte) received sample(s) on 6/1/2022 for the analyses presented in the following report. The above referenced project has been analyzed per your instructions. The analyses were performed in accordance with the applicable analytical method. The analytical data has been validated using standard quality control measures performed as required by the analytical method. Quality Assurance, method validations, instrumentation maintenance and calibration for all parameters were performed in accordance with guidelines established by the USEPA (including 40 CFR 136 Method Update Rule May 2021) unless otherwise indicated. Certain parameters (chlorine, pH, dissolved oxygen, sulfite...) are required to be analyzed within 15 minutes of sampling. Usually, but not always, any field parameter analyzed at the laboratory is outside of this holding time. Refer to sample analysis time for confirmation of holding time compliance. The results are shown on the attached Report of Analysis(s). Results for solid matrices are reported on an as-received basis unless otherwise indicated. This report shall not be reproduced except in full and relates only to the samples included in this report. Please do not hesitate to contact me or client services if you have any questions or need additional information. Sincerely, Angela D Overcash Senior Project Manager Page 1 of 24 Certification Summary Laboratory ID: WP CNC: Waypoint Analytical Carolina, Inc. (C), Charlotte, NC State Program Lab ID Expiration Date 07/31/202237735State ProgramNorth Carolina 12/31/2022402State ProgramNorth Carolina 07/31/202299012State ProgramSouth Carolina 12/31/202299012State ProgramSouth Carolina Page 1 of 1 00016/22-153-0001 Page 2 of 24 Report Number: Sample Summary Table Client Project Description: 22-153-0001 LEH-004 Lab No Client Sample ID Matrix Date Collected Date Received 06/01/2022 09:49Air 91183 MP-3 06/01/2022 15:13 06/01/2022Air 91184 DUP 06/01/2022 15:13 06/01/2022 10:38Air 91185 MP-1 06/01/2022 15:13 Page 3 of 24 Summary of Detected Analytes QualifiersAnalyzedUnitsResult Report Number: Client Sample ID Method Parameters Lab Sample ID 22-153-0001 Report Limit Project:LEH-004 V 91183MP-3 694 06/03/2022 20:57TO-15 Acetone µg/m3 2.02 164 06/03/2022 20:57TO-15 Cyclohexane µg/m3 1.61 27.3 06/03/2022 20:57TO-15 Ethyl Acetate µg/m3 1.36 J10.3 06/03/2022 20:57TO-15 Ethylbenzene µg/m3 1.06 J5.06 06/03/2022 20:57TO-15 4-Ethyltoluene µg/m3 1.28 49.3 06/03/2022 20:57TO-15 Heptane µg/m3 1.43 J24.3 06/03/2022 20:57TO-15 Isopropyl Alchohol µg/m3 1.39 4050 06/07/2022 12:42TO-15 Methyl Ethyl Ketone (MEK)µg/m3 22.3 31.5 06/03/2022 20:57TO-15 Naphthalene µg/m3 1.83 24.9 06/03/2022 20:57TO-15 Styrene µg/m3 1.24 J12.4 06/03/2022 20:57TO-15 Tetrachloroethene µg/m3 1.81 876 06/07/2022 12:42TO-15 Tetrahydrofuran µg/m3 10.7 J14.1 06/03/2022 20:57TO-15 Toluene µg/m3 0.899 302 06/03/2022 20:57TO-15 Trichloroethene µg/m3 1.99 J5.84 06/03/2022 20:57TO-15 Trichlorofluoromethane µg/m3 1.30 J19.7 06/03/2022 20:57TO-15 1,2,4-Trimethylbenzene µg/m3 1.10 J5.95 06/03/2022 20:57TO-15 1,3,5-Trimethylbenzene µg/m3 2.36 J9.03 06/03/2022 20:57TO-15 o-Xylene µg/m3 1.57 J19.9 06/03/2022 20:57TO-15 m,p-Xylene µg/m3 2.17 J28.9 06/03/2022 20:57TO-15 Xylene (Total)µg/m3 1.57 V 91184DUP 701 06/03/2022 21:36TO-15 Acetone µg/m3 2.02 J2.71 06/03/2022 21:36TO-15 Carbon Disulfide µg/m3 0.608 169 06/03/2022 21:36TO-15 Cyclohexane µg/m3 1.61 J10.7 06/03/2022 21:36TO-15 Ethylbenzene µg/m3 1.06 J4.92 06/03/2022 21:36TO-15 4-Ethyltoluene µg/m3 1.28 54.1 06/03/2022 21:36TO-15 Heptane µg/m3 1.43 3680 06/07/2022 13:20TO-15 Methyl Ethyl Ketone (MEK)µg/m3 22.3 31.2 06/03/2022 21:36TO-15 Naphthalene µg/m3 1.83 25.2 06/03/2022 21:36TO-15 Styrene µg/m3 1.24 J12.1 06/03/2022 21:36TO-15 Tetrachloroethene µg/m3 1.81 777 06/07/2022 13:20TO-15 Tetrahydrofuran µg/m3 10.7 J13.9 06/03/2022 21:36TO-15 Toluene µg/m3 0.899 306 06/03/2022 21:36TO-15 Trichloroethene µg/m3 1.99 J19.6 06/03/2022 21:36TO-15 1,2,4-Trimethylbenzene µg/m3 1.10 J6.39 06/03/2022 21:36TO-15 1,3,5-Trimethylbenzene µg/m3 2.36 Page 4 of 24 Summary of Detected Analytes QualifiersAnalyzedUnitsResult Report Number: Client Sample ID Method Parameters Lab Sample ID 22-153-0001 Report Limit Project:LEH-004 V 91184DUP J9.21 06/03/2022 21:36TO-15 o-Xylene µg/m3 1.57 J18.6 06/03/2022 21:36TO-15 m,p-Xylene µg/m3 2.17 J27.8 06/03/2022 21:36TO-15 Xylene (Total)µg/m3 1.57 V 91185MP-1 1380 06/06/2022 15:22TO-15 Acetone µg/m3 40.4 J7.72 06/03/2022 22:15TO-15 Carbon Disulfide µg/m3 0.608 J9.55 06/03/2022 22:15TO-15 Ethylbenzene µg/m3 1.06 1950 06/06/2022 15:22TO-15 Methyl Ethyl Ketone (MEK)µg/m3 44.8 J5.63 06/03/2022 22:15TO-15 Methylene Chloride µg/m3 4.89 33.1 06/03/2022 22:15TO-15 Styrene µg/m3 1.24 J9.36 06/03/2022 22:15TO-15 Tetrachloroethene µg/m3 1.81 534 06/06/2022 15:22TO-15 Tetrahydrofuran µg/m3 21.4 J16.8 06/03/2022 22:15TO-15 Toluene µg/m3 0.899 83.5 06/03/2022 22:15TO-15 Trichloroethene µg/m3 1.99 J12.3 06/03/2022 22:15TO-15 1,2,4-Trimethylbenzene µg/m3 1.10 J8.90 06/03/2022 22:15TO-15 o-Xylene µg/m3 1.57 J19.4 06/03/2022 22:15TO-15 m,p-Xylene µg/m3 2.17 J28.3 06/03/2022 22:15TO-15 Xylene (Total)µg/m3 1.57 Page 5 of 24   Client: Hart & Hickman (Charlotte) CASE NARRATIVE Project: LEH-004 Lab Report Number: 22-153-0001 Date: 6/13/2022 Volatile Organic Compounds in Air- GC/MS Method TO-15 Sample 91183 (MP-3) QC Batch No: V19620/V19615 The sample was diluted due to the nature of the sample matrix. Reporting limits have been adjusted accordingly. Sample 91184 (DUP) QC Batch No: V19620/V19615 The sample was diluted due to the nature of the sample matrix. Reporting limits have been adjusted accordingly. Sample 91185 (MP-1) QC Batch No: V19620/V19615 The sample was diluted due to the nature of the sample matrix. Reporting limits have been adjusted accordingly. Page 6 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:MP-3 91183 Matrix: 6/1/2022 9:49 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19713 06/08/22 09:00 694 µg/m3 2.02 47.5Acetone 10 06/03/22 20:57 V19620ENM <0.733 µg/m3 0.733 16.0Benzene 10 06/03/22 20:57 V19620ENM <1.48 µg/m3 1.48 104Benzyl Chloride 10 06/03/22 20:57 V19620ENM <1.50 µg/m3 1.50 33.5Bromodichloromethane 10 06/03/22 20:57 V19620ENM <1.53 µg/m3 1.53 51.7Bromoform 10 06/03/22 20:57 V19620ENM <1.15 µg/m3 1.15 19.4Bromomethane 10 06/03/22 20:57 V19620ENM <3.28 µg/m3 3.28 11.11,3-Butadiene 10 06/03/22 20:57 V19620ENM <0.608 µg/m3 0.608 62.3Carbon Disulfide 10 06/03/22 20:57 V19620ENM <1.55 µg/m3 1.55 31.5 Carbon Tetrachloride 10 06/03/22 20:57 V19620ENM <1.07 µg/m3 1.07 23.0Chlorobenzene 10 06/03/22 20:57 V19620ENM <2.08 µg/m3 2.08 42.6Chlorodibromomethane 10 06/03/22 20:57 V19620ENM <1.64 µg/m3 1.64 13.2Chloroethane 10 06/03/22 20:57 V19620ENM <0.864 µg/m3 0.864 24.4Chloroform 10 06/03/22 20:57 V19620ENM <0.671 µg/m3 0.671 10.3Chloromethane 10 06/03/22 20:57 V19620ENM 164 µg/m3 1.61 34.4Cyclohexane 10 06/03/22 20:57 V19620ENM <1.51 µg/m3 1.51 38.4 1,2-Dibromoethane 10 06/03/22 20:57 V19620ENM <0.963 µg/m3 0.963 30.11,2-Dichlorobenzene 10 06/03/22 20:57 V19620ENM <1.73 µg/m3 1.73 1201,3-Dichlorobenzene 10 06/03/22 20:57 V19620ENM <1.86 µg/m3 1.86 30.11,4-Dichlorobenzene 10 06/03/22 20:57 V19620ENM <1.34 µg/m3 1.34 24.7Dichlorodifluoromethane 10 06/03/22 20:57 V19620ENM <1.01 µg/m3 1.01 20.21,1-Dichloroethane 10 06/03/22 20:57 V19620ENM <1.29 µg/m3 1.29 20.21,2-Dichloroethane 10 06/03/22 20:57 V19620ENM Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 7 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:MP-3 91183 Matrix: 6/1/2022 9:49 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19713 06/08/22 09:00 <1.07 µg/m3 1.07 19.81,1-Dichloroethene 10 06/03/22 20:57 V19620ENM <0.954 µg/m3 0.954 19.8cis-1,2-Dichloroethene 10 06/03/22 20:57 V19620ENM <1.08 µg/m3 1.08 19.8trans-1,2-Dichloroethene 10 06/03/22 20:57 V19620ENM <2.05 µg/m3 2.05 23.11,2-Dichloropropane 10 06/03/22 20:57 V19620ENM <6.23 µg/m3 6.23 35.01,2-Dichlorotetrafluoroethane 10 06/03/22 20:57 V19620ENM <1.78 µg/m3 1.78 22.7cis-1,3-Dichloropropene 10 06/03/22 20:57 V19620ENM <1.78 µg/m3 1.78 22.7trans-1,3-Dichloropropene 10 06/03/22 20:57 V19620ENM <4.35 µg/m3 4.35 18.01,4-Dioxane 10 06/03/22 20:57 V19620ENM 27.3 µg/m3 1.36 18.0 Ethyl Acetate 10 06/03/22 20:57 V19620ENM 10.3 J µg/m3 1.06 21.7Ethylbenzene 10 06/03/22 20:57 V19620ENM 5.06 J µg/m3 1.28 24.64-Ethyltoluene 10 06/03/22 20:57 V19620ENM <5.61 µg/m3 5.61 38.31,1,2-Trichloro-1,2,2-trifluoroethane 10 06/03/22 20:57 V19620ENM 49.3 µg/m3 1.43 20.5Heptane 10 06/03/22 20:57 V19620ENM <3.30 µg/m3 3.30 53.3Hexachlorobutadiene 10 06/03/22 20:57 V19620ENM <0.471 µg/m3 0.471 17.6n-Hexane 10 06/03/22 20:57 V19620ENM <2.85 µg/m3 2.85 20.5 2-Hexanone 10 06/03/22 20:57 V19620ENM 24.3 J µg/m3 1.39 49.2Isopropyl Alchohol 10 06/03/22 20:57 V19620ENM 4050 µg/m3 22.3 147Methyl Ethyl Ketone (MEK)100 06/07/22 12:42 V19717ENM <0.336 µg/m3 0.336 18.0Methyl tert-butyl ether (MTBE)10 06/03/22 20:57 V19620ENM <1.21 µg/m3 1.21 20.54-Methyl-2-Pentanone 10 06/03/22 20:57 V19620ENM <4.89 µg/m3 4.89 17.4Methylene Chloride 10 06/03/22 20:57 V19620ENM 31.5 µg/m3 1.83 26.2Naphthalene 10 06/03/22 20:57 V19620ENM Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 8 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:MP-3 91183 Matrix: 6/1/2022 9:49 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19713 06/08/22 09:00 <2.42 µg/m3 2.42 8.61Propene 10 06/03/22 20:57 V19620ENM 24.9 µg/m3 1.24 21.3Styrene 10 06/03/22 20:57 V19620ENM <1.04 µg/m3 1.04 34.31,1,2,2-Tetrachloroethane 10 06/03/22 20:57 V19620ENM 12.4 J µg/m3 1.81 33.9Tetrachloroethene 10 06/03/22 20:57 V19620ENM 876 µg/m3 10.7 147Tetrahydrofuran 100 06/07/22 12:42 V19717ENM 14.1 J µg/m3 0.899 18.8Toluene 10 06/03/22 20:57 V19620ENM <2.09 µg/m3 2.09 37.11,2,4-Trichlorobenzene 10 06/03/22 20:57 V19620ENM <1.44 µg/m3 1.44 27.31,1,1-Trichloroethane 10 06/03/22 20:57 V19620ENM <0.877 µg/m3 0.877 27.3 1,1,2-Trichloroethane 10 06/03/22 20:57 V19620ENM 302 µg/m3 1.99 21.5Trichloroethene 10 06/03/22 20:57 V19620ENM 5.84 J µg/m3 1.30 28.1Trichlorofluoromethane 10 06/03/22 20:57 V19620ENM 19.7 J µg/m3 1.10 24.61,2,4-Trimethylbenzene 10 06/03/22 20:57 V19620ENM 5.95 J µg/m3 2.36 24.61,3,5-Trimethylbenzene 10 06/03/22 20:57 V19620ENM <2.24 µg/m3 2.24 17.6Vinyl Acetate 10 06/03/22 20:57 V19620ENM <1.27 µg/m3 1.27 12.8Vinyl Chloride 10 06/03/22 20:57 V19620ENM 9.03 J µg/m3 1.57 21.7 o-Xylene 10 06/03/22 20:57 V19620ENM 19.9 J µg/m3 2.17 56.5m,p-Xylene 10 06/03/22 20:57 V19620ENM 28.9 J µg/m3 1.57 21.7Xylene (Total)10 06/03/22 20:57 V19620 Surrogate: 4-Bromofluorobenzene 103 Limits: 70-130%06/03/22 20:5710 ENM V19620 Surrogate: 4-Bromofluorobenzene 95.0 Limits: 70-130%06/07/22 12:42100 ENM V19717 Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 9 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:DUP 91184 Matrix: 6/1/2022 0:00 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19713 06/08/22 09:00 701 µg/m3 2.02 47.5Acetone 10 06/03/22 21:36 V19620ENM <0.733 µg/m3 0.733 16.0Benzene 10 06/03/22 21:36 V19620ENM <1.48 µg/m3 1.48 104Benzyl Chloride 10 06/03/22 21:36 V19620ENM <1.50 µg/m3 1.50 33.5Bromodichloromethane 10 06/03/22 21:36 V19620ENM <1.53 µg/m3 1.53 51.7Bromoform 10 06/03/22 21:36 V19620ENM <1.15 µg/m3 1.15 19.4Bromomethane 10 06/03/22 21:36 V19620ENM <3.28 µg/m3 3.28 11.11,3-Butadiene 10 06/03/22 21:36 V19620ENM 2.71 J µg/m3 0.608 62.3Carbon Disulfide 10 06/03/22 21:36 V19620ENM <1.55 µg/m3 1.55 31.5 Carbon Tetrachloride 10 06/03/22 21:36 V19620ENM <1.07 µg/m3 1.07 23.0Chlorobenzene 10 06/03/22 21:36 V19620ENM <2.08 µg/m3 2.08 42.6Chlorodibromomethane 10 06/03/22 21:36 V19620ENM <1.64 µg/m3 1.64 13.2Chloroethane 10 06/03/22 21:36 V19620ENM <0.864 µg/m3 0.864 24.4Chloroform 10 06/03/22 21:36 V19620ENM <0.671 µg/m3 0.671 10.3Chloromethane 10 06/03/22 21:36 V19620ENM 169 µg/m3 1.61 34.4Cyclohexane 10 06/03/22 21:36 V19620ENM <1.51 µg/m3 1.51 38.4 1,2-Dibromoethane 10 06/03/22 21:36 V19620ENM <0.963 µg/m3 0.963 30.11,2-Dichlorobenzene 10 06/03/22 21:36 V19620ENM <1.73 µg/m3 1.73 1201,3-Dichlorobenzene 10 06/03/22 21:36 V19620ENM <1.86 µg/m3 1.86 30.11,4-Dichlorobenzene 10 06/03/22 21:36 V19620ENM <1.34 µg/m3 1.34 24.7Dichlorodifluoromethane 10 06/03/22 21:36 V19620ENM <1.01 µg/m3 1.01 20.21,1-Dichloroethane 10 06/03/22 21:36 V19620ENM <1.29 µg/m3 1.29 20.21,2-Dichloroethane 10 06/03/22 21:36 V19620ENM Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 10 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:DUP 91184 Matrix: 6/1/2022 0:00 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19713 06/08/22 09:00 <1.07 µg/m3 1.07 19.81,1-Dichloroethene 10 06/03/22 21:36 V19620ENM <0.954 µg/m3 0.954 19.8cis-1,2-Dichloroethene 10 06/03/22 21:36 V19620ENM <1.08 µg/m3 1.08 19.8trans-1,2-Dichloroethene 10 06/03/22 21:36 V19620ENM <2.05 µg/m3 2.05 23.11,2-Dichloropropane 10 06/03/22 21:36 V19620ENM <6.23 µg/m3 6.23 35.01,2-Dichlorotetrafluoroethane 10 06/03/22 21:36 V19620ENM <1.78 µg/m3 1.78 22.7cis-1,3-Dichloropropene 10 06/03/22 21:36 V19620ENM <1.78 µg/m3 1.78 22.7trans-1,3-Dichloropropene 10 06/03/22 21:36 V19620ENM <4.35 µg/m3 4.35 18.01,4-Dioxane 10 06/03/22 21:36 V19620ENM <1.36 µg/m3 1.36 18.0 Ethyl Acetate 10 06/03/22 21:36 V19620ENM 10.7 J µg/m3 1.06 21.7Ethylbenzene 10 06/03/22 21:36 V19620ENM 4.92 J µg/m3 1.28 24.64-Ethyltoluene 10 06/03/22 21:36 V19620ENM <5.61 µg/m3 5.61 38.31,1,2-Trichloro-1,2,2-trifluoroethane 10 06/03/22 21:36 V19620ENM 54.1 µg/m3 1.43 20.5Heptane 10 06/03/22 21:36 V19620ENM <3.30 µg/m3 3.30 53.3Hexachlorobutadiene 10 06/03/22 21:36 V19620ENM <0.471 µg/m3 0.471 17.6n-Hexane 10 06/03/22 21:36 V19620ENM <2.85 µg/m3 2.85 20.5 2-Hexanone 10 06/03/22 21:36 V19620ENM <1.39 µg/m3 1.39 49.2Isopropyl Alchohol 10 06/03/22 21:36 V19620ENM 3680 µg/m3 22.3 147Methyl Ethyl Ketone (MEK)100 06/07/22 13:20 V19717ENM <0.336 µg/m3 0.336 18.0Methyl tert-butyl ether (MTBE)10 06/03/22 21:36 V19620ENM <1.21 µg/m3 1.21 20.54-Methyl-2-Pentanone 10 06/03/22 21:36 V19620ENM <4.89 µg/m3 4.89 17.4Methylene Chloride 10 06/03/22 21:36 V19620ENM 31.2 µg/m3 1.83 26.2Naphthalene 10 06/03/22 21:36 V19620ENM Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 11 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:DUP 91184 Matrix: 6/1/2022 0:00 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19713 06/08/22 09:00 <2.42 µg/m3 2.42 8.61Propene 10 06/03/22 21:36 V19620ENM 25.2 µg/m3 1.24 21.3Styrene 10 06/03/22 21:36 V19620ENM <1.04 µg/m3 1.04 34.31,1,2,2-Tetrachloroethane 10 06/03/22 21:36 V19620ENM 12.1 J µg/m3 1.81 33.9Tetrachloroethene 10 06/03/22 21:36 V19620ENM 777 µg/m3 10.7 147Tetrahydrofuran 100 06/07/22 13:20 V19717ENM 13.9 J µg/m3 0.899 18.8Toluene 10 06/03/22 21:36 V19620ENM <2.09 µg/m3 2.09 37.11,2,4-Trichlorobenzene 10 06/03/22 21:36 V19620ENM <1.44 µg/m3 1.44 27.31,1,1-Trichloroethane 10 06/03/22 21:36 V19620ENM <0.877 µg/m3 0.877 27.3 1,1,2-Trichloroethane 10 06/03/22 21:36 V19620ENM 306 µg/m3 1.99 21.5Trichloroethene 10 06/03/22 21:36 V19620ENM <1.30 µg/m3 1.30 28.1Trichlorofluoromethane 10 06/03/22 21:36 V19620ENM 19.6 J µg/m3 1.10 24.61,2,4-Trimethylbenzene 10 06/03/22 21:36 V19620ENM 6.39 J µg/m3 2.36 24.61,3,5-Trimethylbenzene 10 06/03/22 21:36 V19620ENM <2.24 µg/m3 2.24 17.6Vinyl Acetate 10 06/03/22 21:36 V19620ENM <1.27 µg/m3 1.27 12.8Vinyl Chloride 10 06/03/22 21:36 V19620ENM 9.21 J µg/m3 1.57 21.7 o-Xylene 10 06/03/22 21:36 V19620ENM 18.6 J µg/m3 2.17 56.5m,p-Xylene 10 06/03/22 21:36 V19620ENM 27.8 J µg/m3 1.57 21.7Xylene (Total)10 06/03/22 21:36 V19620 Surrogate: 4-Bromofluorobenzene 101 Limits: 70-130%06/03/22 21:3610 ENM V19620 Surrogate: 4-Bromofluorobenzene 91.9 Limits: 70-130%06/07/22 13:20100 ENM V19717 Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 12 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:MP-1 91185 Matrix: 6/1/2022 10:38 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19646 06/06/22 09:00 1380 µg/m3 40.4 950Acetone 200 06/06/22 15:22 V19647ENM <0.733 µg/m3 0.733 16.0Benzene 10 06/03/22 22:15 V19620ENM <1.48 µg/m3 1.48 104Benzyl Chloride 10 06/03/22 22:15 V19620ENM <1.50 µg/m3 1.50 33.5Bromodichloromethane 10 06/03/22 22:15 V19620ENM <1.53 µg/m3 1.53 51.7Bromoform 10 06/03/22 22:15 V19620ENM <1.15 µg/m3 1.15 19.4Bromomethane 10 06/03/22 22:15 V19620ENM <3.28 µg/m3 3.28 11.11,3-Butadiene 10 06/03/22 22:15 V19620ENM 7.72 J µg/m3 0.608 62.3Carbon Disulfide 10 06/03/22 22:15 V19620ENM <1.55 µg/m3 1.55 31.5 Carbon Tetrachloride 10 06/03/22 22:15 V19620ENM <1.07 µg/m3 1.07 23.0Chlorobenzene 10 06/03/22 22:15 V19620ENM <2.08 µg/m3 2.08 42.6Chlorodibromomethane 10 06/03/22 22:15 V19620ENM <1.64 µg/m3 1.64 13.2Chloroethane 10 06/03/22 22:15 V19620ENM <0.864 µg/m3 0.864 24.4Chloroform 10 06/03/22 22:15 V19620ENM <0.671 µg/m3 0.671 10.3Chloromethane 10 06/03/22 22:15 V19620ENM <1.61 µg/m3 1.61 34.4Cyclohexane 10 06/03/22 22:15 V19620ENM <1.51 µg/m3 1.51 38.4 1,2-Dibromoethane 10 06/03/22 22:15 V19620ENM <0.963 µg/m3 0.963 30.11,2-Dichlorobenzene 10 06/03/22 22:15 V19620ENM <1.73 µg/m3 1.73 1201,3-Dichlorobenzene 10 06/03/22 22:15 V19620ENM <1.86 µg/m3 1.86 30.11,4-Dichlorobenzene 10 06/03/22 22:15 V19620ENM <1.34 µg/m3 1.34 24.7Dichlorodifluoromethane 10 06/03/22 22:15 V19620ENM <1.01 µg/m3 1.01 20.21,1-Dichloroethane 10 06/03/22 22:15 V19620ENM <1.29 µg/m3 1.29 20.21,2-Dichloroethane 10 06/03/22 22:15 V19620ENM Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 13 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:MP-1 91185 Matrix: 6/1/2022 10:38 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19646 06/06/22 09:00 <1.07 µg/m3 1.07 19.81,1-Dichloroethene 10 06/03/22 22:15 V19620ENM <0.954 µg/m3 0.954 19.8cis-1,2-Dichloroethene 10 06/03/22 22:15 V19620ENM <1.08 µg/m3 1.08 19.8trans-1,2-Dichloroethene 10 06/03/22 22:15 V19620ENM <2.05 µg/m3 2.05 23.11,2-Dichloropropane 10 06/03/22 22:15 V19620ENM <6.23 µg/m3 6.23 35.01,2-Dichlorotetrafluoroethane 10 06/03/22 22:15 V19620ENM <1.78 µg/m3 1.78 22.7cis-1,3-Dichloropropene 10 06/03/22 22:15 V19620ENM <1.78 µg/m3 1.78 22.7trans-1,3-Dichloropropene 10 06/03/22 22:15 V19620ENM <4.35 µg/m3 4.35 18.01,4-Dioxane 10 06/03/22 22:15 V19620ENM <1.36 µg/m3 1.36 18.0 Ethyl Acetate 10 06/03/22 22:15 V19620ENM 9.55 J µg/m3 1.06 21.7Ethylbenzene 10 06/03/22 22:15 V19620ENM <1.28 µg/m3 1.28 24.64-Ethyltoluene 10 06/03/22 22:15 V19620ENM <5.61 µg/m3 5.61 38.31,1,2-Trichloro-1,2,2-trifluoroethane 10 06/03/22 22:15 V19620ENM <1.43 µg/m3 1.43 20.5Heptane 10 06/03/22 22:15 V19620ENM <3.30 µg/m3 3.30 53.3Hexachlorobutadiene 10 06/03/22 22:15 V19620ENM <0.471 µg/m3 0.471 17.6n-Hexane 10 06/03/22 22:15 V19620ENM <2.85 µg/m3 2.85 20.5 2-Hexanone 10 06/03/22 22:15 V19620ENM <1.39 µg/m3 1.39 49.2Isopropyl Alchohol 10 06/03/22 22:15 V19620ENM 1950 µg/m3 44.8 295Methyl Ethyl Ketone (MEK)200 06/06/22 15:22 V19647ENM <0.336 µg/m3 0.336 18.0Methyl tert-butyl ether (MTBE)10 06/03/22 22:15 V19620ENM <1.21 µg/m3 1.21 20.54-Methyl-2-Pentanone 10 06/03/22 22:15 V19620ENM 5.63 J µg/m3 4.89 17.4Methylene Chloride 10 06/03/22 22:15 V19620ENM <1.83 µg/m3 1.83 26.2Naphthalene 10 06/03/22 22:15 V19620ENM Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 14 of 24 , REPORT OF ANALYSISReport Number : Project Information : NC 28203 22-153-0001 01102 Hart & Hickman (Charlotte) 2923 South Tryon St. Ste 100 Juliana Lima Charlotte Received : 06/01/2022 LEH-004 Report Date : 06/13/2022 Sample ID : Lab No : Sampled:MP-1 91185 Matrix: 6/1/2022 10:38 Air Analytical Method: Prep Method: Test Results Units MDL MQL By Analytical Batch Date / Time Analyzed DF TO-15 Prep TO-15 Prep Batch(es):V19615 06/03/22 09:00 V19646 06/06/22 09:00 <2.42 µg/m3 2.42 8.61Propene 10 06/03/22 22:15 V19620ENM 33.1 µg/m3 1.24 21.3Styrene 10 06/03/22 22:15 V19620ENM <1.04 µg/m3 1.04 34.31,1,2,2-Tetrachloroethane 10 06/03/22 22:15 V19620ENM 9.36 J µg/m3 1.81 33.9Tetrachloroethene 10 06/03/22 22:15 V19620ENM 534 µg/m3 21.4 295Tetrahydrofuran 200 06/06/22 15:22 V19647ENM 16.8 J µg/m3 0.899 18.8Toluene 10 06/03/22 22:15 V19620ENM <2.09 µg/m3 2.09 37.11,2,4-Trichlorobenzene 10 06/03/22 22:15 V19620ENM <1.44 µg/m3 1.44 27.31,1,1-Trichloroethane 10 06/03/22 22:15 V19620ENM <0.877 µg/m3 0.877 27.3 1,1,2-Trichloroethane 10 06/03/22 22:15 V19620ENM 83.5 µg/m3 1.99 21.5Trichloroethene 10 06/03/22 22:15 V19620ENM <1.30 µg/m3 1.30 28.1Trichlorofluoromethane 10 06/03/22 22:15 V19620ENM 12.3 J µg/m3 1.10 24.61,2,4-Trimethylbenzene 10 06/03/22 22:15 V19620ENM <2.36 µg/m3 2.36 24.61,3,5-Trimethylbenzene 10 06/03/22 22:15 V19620ENM <2.24 µg/m3 2.24 17.6Vinyl Acetate 10 06/03/22 22:15 V19620ENM <1.27 µg/m3 1.27 12.8Vinyl Chloride 10 06/03/22 22:15 V19620ENM 8.90 J µg/m3 1.57 21.7 o-Xylene 10 06/03/22 22:15 V19620ENM 19.4 J µg/m3 2.17 56.5m,p-Xylene 10 06/03/22 22:15 V19620ENM 28.3 J µg/m3 1.57 21.7Xylene (Total)10 06/03/22 22:15 V19620 Surrogate: 4-Bromofluorobenzene 103 Limits: 70-130%06/03/22 22:1510 ENM V19620 Surrogate: 4-Bromofluorobenzene 95.0 Limits: 70-130%06/06/22 15:22200 ENM V19647 Qualifiers/ Definitions Estimated valueJDilution FactorDF Method Quantitation LimitMQL Page 15 of 24 Quality Control Data 22-153-0001Report No: Project Description: Client ID:Hart & Hickman (Charlotte) LEH-004 QC Prep Batch Method: Volatile Organic Compounds in Air- GC/MS TO-15 V19620QC Analytical Batch(es): Analysis Method: Analysis Description: TO-15 Prep QC Prep:V19615 Associated Lab Samples: 91183, 91184, 91185 LRB-V19615 Matrix: AIRLab Reagent Blank Parameter AnalyzedMQLMDLBlank ResultUnits % Recovery % Rec Limits 06/03/22 11:184.750.202<0.202µg/m3Acetone 06/03/22 11:181.600.0733<0.0733µg/m3Benzene 06/03/22 11:1810.40.148<0.148µg/m3Benzyl Chloride 06/03/22 11:183.350.150<0.150µg/m3Bromodichloromethane 06/03/22 11:185.170.153<0.153µg/m3Bromoform 06/03/22 11:181.940.115<0.115µg/m3Bromomethane 06/03/22 11:181.110.328<0.328µg/m31,3-Butadiene 06/03/22 11:186.230.0608<0.0608µg/m3Carbon Disulfide 06/03/22 11:183.150.155<0.155µg/m3Carbon Tetrachloride 06/03/22 11:182.300.107<0.107µg/m3Chlorobenzene 06/03/22 11:184.260.208<0.208µg/m3Chlorodibromomethane 06/03/22 11:181.320.164<0.164µg/m3Chloroethane 06/03/22 11:182.440.0864<0.0864µg/m3Chloroform 06/03/22 11:181.030.0673<0.0673µg/m3Chloromethane 06/03/22 11:183.440.161<0.161µg/m3Cyclohexane 06/03/22 11:183.840.151<0.151µg/m31,2-Dibromoethane 06/03/22 11:183.010.0963<0.0963µg/m31,2-Dichlorobenzene 06/03/22 11:1812.00.174<0.174µg/m31,3-Dichlorobenzene 06/03/22 11:183.010.186<0.186µg/m31,4-Dichlorobenzene 06/03/22 11:182.470.134<0.134µg/m3Dichlorodifluoromethane 06/03/22 11:182.020.101<0.101µg/m31,1-Dichloroethane 06/03/22 11:182.020.129<0.129µg/m31,2-Dichloroethane 06/03/22 11:181.980.107<0.107µg/m31,1-Dichloroethene 06/03/22 11:181.980.0955<0.0955µg/m3cis-1,2-Dichloroethene 06/03/22 11:181.980.108<0.108µg/m3trans-1,2-Dichloroethene 06/03/22 11:182.310.205<0.205µg/m31,2-Dichloropropane 06/03/22 11:183.500.623<0.623µg/m31,2-Dichlorotetrafluoroethane Page 1 of 7Date:06/13/2022 04:34 PM Page 16 of 24 Quality Control Data 22-153-0001Report No: Project Description: Client ID:Hart & Hickman (Charlotte) LEH-004 QC Prep Batch Method: Volatile Organic Compounds in Air- GC/MS TO-15 V19620QC Analytical Batch(es): Analysis Method: Analysis Description: TO-15 Prep QC Prep:V19615 Associated Lab Samples: 91183, 91184, 91185 LRB-V19615 Matrix: AIRLab Reagent Blank Parameter AnalyzedMQLMDLBlank ResultUnits % Recovery % Rec Limits 06/03/22 11:182.270.178<0.178µg/m3cis-1,3-Dichloropropene 06/03/22 11:182.270.178<0.178µg/m3trans-1,3-Dichloropropene 06/03/22 11:181.800.435<0.435µg/m31,4-Dioxane 06/03/22 11:181.800.136<0.136µg/m3Ethyl Acetate 06/03/22 11:182.170.106<0.106µg/m3Ethylbenzene 06/03/22 11:182.460.128<0.128µg/m34-Ethyltoluene 06/03/22 11:183.830.561<0.561µg/m31,1,2-Trichloro-1,2,2-trifluoroethane 06/03/22 11:182.050.143<0.143µg/m3Heptane 06/03/22 11:185.330.330<0.330µg/m3Hexachlorobutadiene 06/03/22 11:181.760.0472<0.0472µg/m3n-Hexane 06/03/22 11:182.050.285<0.285µg/m32-Hexanone 06/03/22 11:184.920.1392.04µg/m3Isopropyl Alchohol 06/03/22 11:181.800.0336<0.0336µg/m3Methyl tert-butyl ether (MTBE) 06/03/22 11:182.050.121<0.121µg/m34-Methyl-2-Pentanone 06/03/22 11:181.740.489<0.489µg/m3Methylene Chloride 06/03/22 11:182.620.183<0.183µg/m3Naphthalene 06/03/22 11:180.8610.242<0.242µg/m3Propene 06/03/22 11:182.130.124<0.124µg/m3Styrene 06/03/22 11:183.430.104<0.104µg/m31,1,2,2-Tetrachloroethane 06/03/22 11:183.390.1810.665µg/m3Tetrachloroethene 06/03/22 11:181.880.0901<0.0901µg/m3Toluene 06/03/22 11:183.710.209<0.209µg/m31,2,4-Trichlorobenzene 06/03/22 11:182.730.144<0.144µg/m31,1,1-Trichloroethane 06/03/22 11:182.730.0877<0.0877µg/m31,1,2-Trichloroethane 06/03/22 11:182.150.199<0.199µg/m3Trichloroethene 06/03/22 11:182.810.130<0.130µg/m3Trichlorofluoromethane 06/03/22 11:182.460.110<0.110µg/m31,2,4-Trimethylbenzene Page 2 of 7Date:06/13/2022 04:34 PM Page 17 of 24 Quality Control Data 22-153-0001Report No: Project Description: Client ID:Hart & Hickman (Charlotte) LEH-004 QC Prep Batch Method: Volatile Organic Compounds in Air- GC/MS TO-15 V19620QC Analytical Batch(es): Analysis Method: Analysis Description: TO-15 Prep QC Prep:V19615 Associated Lab Samples: 91183, 91184, 91185 LRB-V19615 Matrix: AIRLab Reagent Blank Parameter AnalyzedMQLMDLBlank ResultUnits % Recovery % Rec Limits 06/03/22 11:182.460.236<0.236µg/m31,3,5-Trimethylbenzene 06/03/22 11:181.760.224<0.224µg/m3Vinyl Acetate 06/03/22 11:181.280.127<0.127µg/m3Vinyl Chloride 06/03/22 11:182.170.157<0.157µg/m3o-Xylene 06/03/22 11:185.650.217<0.217µg/m3m,p-Xylene 06/03/22 11:184-Bromofluorobenzene (S)94.9 70-130 LCS-V19615Laboratory Control Sample Parameter LCS %RecLCS Result Spike Conc.Units % Rec Limits 89.910.711.9µg/m3Acetone 70-130 88.114.116.0µg/m3Benzene 70-130 87.622.725.9µg/m3Benzyl Chloride 70-130 88.629.733.5µg/m3Bromodichloromethane 70-130 90.546.851.7µg/m3Bromoform 70-130 91.717.819.4µg/m3Bromomethane 70-130 87.79.7411.1µg/m31,3-Butadiene 70-130 93.514.615.6µg/m3Carbon Disulfide 70-130 84.126.531.5µg/m3Carbon Tetrachloride 70-130 90.820.923.0µg/m3Chlorobenzene 70-130 93.840.042.6µg/m3Chlorodibromomethane 70-130 87.111.513.2µg/m3Chloroethane 70-130 88.921.724.4µg/m3Chloroform 70-130 94.39.7210.3µg/m3Chloromethane 70-130 83.714.417.2µg/m3Cyclohexane 70-130 92.135.438.4µg/m31,2-Dibromoethane 70-130 89.727.030.1µg/m31,2-Dichlorobenzene 70-130 Page 3 of 7Date:06/13/2022 04:34 PM Page 18 of 24 Quality Control Data 22-153-0001Report No: Project Description: Client ID:Hart & Hickman (Charlotte) LEH-004 QC Prep Batch Method: Volatile Organic Compounds in Air- GC/MS TO-15 V19620QC Analytical Batch(es): Analysis Method: Analysis Description: TO-15 Prep QC Prep:V19615 LCS-V19615Laboratory Control Sample Parameter LCS %RecLCS Result Spike Conc.Units % Rec Limits 83.325.130.1µg/m31,3-Dichlorobenzene 70-130 78.723.730.1µg/m31,4-Dichlorobenzene 70-130 88.221.824.7µg/m3Dichlorodifluoromethane 70-130 93.018.820.2µg/m31,1-Dichloroethane 70-130 90.018.220.2µg/m31,2-Dichloroethane 70-130 95.418.919.8µg/m31,1-Dichloroethene 70-130 95.418.919.8µg/m3cis-1,2-Dichloroethene 70-130 91.918.219.8µg/m3trans-1,2-Dichloroethene 70-130 88.320.423.1µg/m31,2-Dichloropropane 70-130 89.131.235.0µg/m31,2-Dichlorotetrafluoroethane 70-130 90.320.522.7µg/m3cis-1,3-Dichloropropene 70-130 90.320.522.7µg/m3trans-1,3-Dichloropropene 70-130 78.314.118.0µg/m31,4-Dioxane 70-130 87.715.818.0µg/m3Ethyl Acetate 70-130 89.419.421.7µg/m3Ethylbenzene 70-130 89.822.124.6µg/m34-Ethyltoluene 70-130 92.135.338.3µg/m31,1,2-Trichloro-1,2,2-trifluoroethane 70-130 89.218.320.5µg/m3Heptane 70-130 91.949.053.3µg/m3Hexachlorobutadiene 70-130 89.215.717.6µg/m3n-Hexane 70-130 83.917.220.5µg/m32-Hexanone 70-130 87.810.812.3µg/m3Isopropyl Alchohol 70-130 83.815.118.0µg/m3Methyl tert-butyl ether (MTBE)70-130 84.817.420.5µg/m34-Methyl-2-Pentanone 70-130 82.714.417.4µg/m3Methylene Chloride 70-130 84.322.126.2µg/m3Naphthalene 70-130 88.97.668.61µg/m3Propene 70-130 Page 4 of 7Date:06/13/2022 04:34 PM Page 19 of 24 Quality Control Data 22-153-0001Report No: Project Description: Client ID:Hart & Hickman (Charlotte) LEH-004 QC Prep Batch Method: Volatile Organic Compounds in Air- GC/MS TO-15 V19620QC Analytical Batch(es): Analysis Method: Analysis Description: TO-15 Prep QC Prep:V19615 LCS-V19615Laboratory Control Sample Parameter LCS %RecLCS Result Spike Conc.Units % Rec Limits 85.418.221.3µg/m3Styrene 70-130 94.732.534.3µg/m31,1,2,2-Tetrachloroethane 70-130 90.830.833.9µg/m3Tetrachloroethene 70-130 88.216.618.8µg/m3Toluene 70-130 91.634.037.1µg/m31,2,4-Trichlorobenzene 70-130 84.623.127.3µg/m31,1,1-Trichloroethane 70-130 92.325.227.3µg/m31,1,2-Trichloroethane 70-130 88.423.826.9µg/m3Trichloroethene 70-130 92.526.028.1µg/m3Trichlorofluoromethane 70-130 91.022.424.6µg/m31,2,4-Trimethylbenzene 70-130 95.123.424.6µg/m31,3,5-Trimethylbenzene 70-130 85.215.017.6µg/m3Vinyl Acetate 70-130 90.611.612.8µg/m3Vinyl Chloride 70-130 96.721.021.7µg/m3o-Xylene 70-130 92.840.343.4µg/m3m,p-Xylene 70-130 99.44-Bromofluorobenzene (S)70-130 Page 5 of 7Date:06/13/2022 04:34 PM Page 20 of 24 Quality Control Data 22-153-0001Report No: Project Description: Client ID:Hart & Hickman (Charlotte) LEH-004 QC Prep Batch Method: Volatile Organic Compounds in Air- GC/MS TO-15 V19647QC Analytical Batch(es): Analysis Method: Analysis Description: TO-15 Prep QC Prep:V19646 Associated Lab Samples: 91185 LRB-V19646 Matrix: AIRLab Reagent Blank Parameter AnalyzedMQLMDLBlank ResultUnits % Recovery % Rec Limits 06/06/22 11:114.750.2021.67µg/m3Acetone 06/06/22 11:111.470.224<0.224µg/m3Methyl Ethyl Ketone (MEK) 06/06/22 11:111.470.107<0.107µg/m3Tetrahydrofuran 06/06/22 11:114-Bromofluorobenzene (S)97.7 70-130 LCS-V19646Laboratory Control Sample Parameter LCS %RecLCS Result Spike Conc.Units % Rec Limits 92.411.011.9µg/m3Acetone 70-130 87.813.014.8µg/m3Methyl Ethyl Ketone (MEK)70-130 90.413.314.7µg/m3Tetrahydrofuran 70-130 1034-Bromofluorobenzene (S)70-130 Page 6 of 7Date:06/13/2022 04:34 PM Page 21 of 24 Quality Control Data 22-153-0001Report No: Project Description: Client ID:Hart & Hickman (Charlotte) LEH-004 QC Prep Batch Method: Volatile Organic Compounds in Air- GC/MS TO-15 V19717QC Analytical Batch(es): Analysis Method: Analysis Description: TO-15 Prep QC Prep:V19713 Associated Lab Samples: 91183, 91184 LRB-V19713 Matrix: AIRLab Reagent Blank Parameter AnalyzedMQLMDLBlank ResultUnits % Recovery % Rec Limits 06/07/22 11:231.470.224<0.224µg/m3Methyl Ethyl Ketone (MEK) 06/07/22 11:231.470.107<0.107µg/m3Tetrahydrofuran 06/07/22 11:234-Bromofluorobenzene (S)97.2 70-130 LCS-V19713Laboratory Control Sample Parameter LCS %RecLCS Result Spike Conc.Units % Rec Limits 10315.314.8µg/m3Methyl Ethyl Ketone (MEK)70-130 93.813.814.7µg/m3Tetrahydrofuran 70-130 98.34-Bromofluorobenzene (S)70-130 Page 7 of 7Date:06/13/2022 04:34 PM Page 22 of 24 Fed Ex UPS US Postal Client Lab Courier Other : Shipment Receipt Form Customer Number: Customer Name: Report Number:22-153-0001 Hart & Hickman (Charlotte) 01102 Shipping Method Shipping container/cooler uncompromised? Thermometer ID:NA Chain of Custody (COC) present?Yes No Yes No Not Present Yes No Not Present Yes No COC agrees with sample label(s)? Yes No COC properly completed Samples in proper containers? Sample containers intact? Sufficient sample volume for indicated test(s)? All samples received within holding time? Cooler temperature in compliance? Yes No Yes No Yes No Yes No Yes No Yes NoCooler/Samples arrived at the laboratory on ice. Samples were considered acceptable as cooling process had begun. Yes No Yes No N/A Yes No N/A Yes No N/ASoil VOA method 5035 – compliance criteria met Water - Sample containers properly preserved Water - VOA vials free of headspace Yes No N/A Trip Blanks received with VOAs Low concentration EnCore samplers (48 hr) High concentration pre-weighed (methanol -14 d) Low conc pre-weighed vials (Sod Bis -14 d) High concentration container (48 hr) Custody seals intact on shipping container/cooler? Custody seals intact on sample bottles? Number of coolers/boxes received Yes No 1 Signature:Paula Blakeborough Date & Time:06/02/2022 09:54:04 Special precautions or instructions included? Comments: Page 23 of 24 Page 24 of 24 Appendix H DEQ Risk Calculator Summary Pages Version Date: Basis: Site Name: Site Address: DEQ Section: Site ID: Exposure Unit ID: Submittal Date: Reviewed By: Sub-Slab Worst Case North Carolina Department of Environmental Quality Risk Calculator Quality Products Co. 1515 South Mint Street, Charlotte, North Carolina DWM Brownfields 22016-18-060 January 2022 November 2021 EPA RSL Table 6/15/2022 Prepared By:Juliana Lima Hart & Hickman North Carolina DEQ Risk Calculator Table of Contents Version Date: January 2022 Basis: November 2021 EPA RSL Table Site ID: 22016-18-060 Exposure Unit ID: Sub-Slab Worst Case Form No. Input Form 1A Complete Exposure Pathways Input Form 1B Exposure Factors and Target Risks Input Form 1C Contaminant Migration Parameters Input Form 1D Sample Statistics Input Form 2A Soil Exposure Point Concentration Table Input Form 2B Groundwater Exposure Point Concentration Table Input Form 2C Surface Water Exposure Point Concentration Table Input Form 2D Soil Gas Exposure Point Concentration Table Input Form 2E Indoor Air Exposure Point Concentration Table Output Form 1A Risk for Individual Pathways Output Form 1B Sitewide Risk Output Form 2A Resident Soil Output Form 2B Resident Groundwater Use Output Form 2C Non-Residential Worker Soil Output Form 2D Non-Residential Worker Groundwater Use Output Form 2E Construction Worker Soil Output Form 2F Recreator/Trespasser Soil Output Form 2G Recreator/Trespasser Surface Water Output Form 3A Resident Groundwater to Indoor Air Output Form 3B Resident Soil Gas to Indoor Air Output Form 3C Resident Indoor Air Output Form 3D Non-Residential Worker Groundwater to Indoor Air Output Form 3E Non-Residential Worker Soil Gas to Indoor Air Output Form 3F Non-Residential Worker Indoor Air Output Form 4A Soil to Groundwater - Forward Mode Output Form 4B Groundwater to Groundwater - Forward Mode Output Form 4C Soil to Surface Water - Forward Mode Output Form 4D Groundwater to Surface Water - Forward Mode Output Form 4E Soil to Groundwater - Backward Mode Output Form 4F Groundwater to Groundwater - Backward Mode Output Form 4G Soil to Surface Water - Backward Mode Output Form 4H Groundwater to Surface Water - Backward Mode Output Section 4 - Contaminant Migration Worksheets Output Section 3 - Vapor Intrusion Calculators TOC Description DATA INPUT SHEETS Check box if included Input Section 1 - Exposure Pathways & Parameters Input Section 2 - Exposure Point Concentrations DATA OUTPUT SHEETS Output Section 1 - Summary Output for All Calculators Output Section 2 - Direct Contact Soil and Groundwater Calculators North Carolina DEQ Risk Calculator Complete Exposure Pathways Version Date: January 2022 Basis: November 2021 EPA RSL Table Site ID: 22016-18-060 Exposure Unit ID: Sub-Slab Worst Case Note: Risk output will only be calculated for complete exposure pathways. Receptor Pathway Check box if pathway complete Soil Groundwater Use Soil Groundwater Use Construction Worker Soil Soil Surface Water Groundwater to Indoor Air Soil Gas to Indoor Air Indoor Air Groundwater to Indoor Air Soil Gas to Indoor Air Indoor Air Source Soil Source Groundwater Source Soil Source Groundwater Resident Non-Residential Worker CONTAMINANT MIGRATION PATHWAYS Groundwater Surface Water Input Form 1A VAPOR INTRUSION PATHWAYS DIRECT CONTACT SOIL AND WATER PATHWAYS Resident Non-Residential Worker Recreator/Trespasser North Carolina DEQ Risk Calculator Exposure Point Concentrations Version Date: January 2022 Basis: November 2021 EPA RSL Table Site ID: 22016-18-060 Exposure Unit ID: Sub-Slab Worst Case Description of Exposure Point Concentration Selection: Exposure Point Concentration (ug/m3) Notes:CAS Number Chemical Minimum Concentration (Qualifier) Maximum Concentration (Qualifier) Units Location of Maximum Concentration Detection Frequency Range of Detection Limits Concentration Used for Screening Background Value Screening Toxicity Value (Screening Level) (n/c) Potential ARAR/TBC Value Potential ARAR/TBC Source COPC Flag (Y/N) Rationale for Selection or Deletion 1380 67-64-1 Acetone ug/m3 7.72 75-15-0 Carbon Disulfide ug/m3 169 110-82-7 Cyclohexane ug/m3 27.3 141-78-6 Ethyl Acetate ug/m3 10.7 100-41-4 Ethylbenzene ug/m3 876 109-99-9 ~Tetrahydrofuran ug/m3 54.1 142-82-5 Heptane, N-ug/m3 24.3 67-63-0 Isopropanol ug/m3 4050 78-93-3 Methyl Ethyl Ketone (2-Butanone)ug/m3 5.63 75-09-2 Methylene Chloride ug/m3 31.5 91-20-3 ~Naphthalene ug/m3 33.1 100-42-5 Styrene ug/m3 12.4 127-18-4 Tetrachloroethylene ug/m3 16.8 108-88-3 Toluene ug/m3 306 79-01-6 Trichloroethylene ug/m3 5.84 75-69-4 Trichlorofluoromethane ug/m3 19.7 95-63-6 Trimethylbenzene, 1,2,4-ug/m3 6.39 108-67-8 Trimethylbenzene, 1,3,5-ug/m3 19.9 108-38-3 Xylene, m-ug/m3 9.21 95-47-6 Xylene, o-ug/m3 Input Form 2D Soil Gas Exposure Point Concentration Table Note: Chemicals highlighted in orange are non-volatile chemicals. Since these chemicals do not pose a vapor intrusion risk, no risk values are calculated for these chemicals.If the chemical list is changed from a prior calculator run, remember to select "See All Chemicals" on the data output sheet or newly added chemicals will not be included in risk calculations North Carolina DEQ Risk Calculator Risk for Individual Pathways Output Form 1A Version Date: January 2022 Basis: November 2021 EPA RSL Table Site ID: 22016-18-060 Exposure Unit ID: Sub-Slab Worst Case Receptor Pathway Carcinogenic Risk Hazard Index Risk exceeded? Soil NC NC NC Groundwater Use*NC NC NC Soil NC NC NC Groundwater Use*NC NC NC Construction Worker Soil NC NC NC Soil NC NC NC Surface Water*NC NC NC Receptor Pathway Carcinogenic Risk Hazard Index Risk exceeded? Groundwater to Indoor Air NC NC NC Soil Gas to Indoor Air NC NC NC Indoor Air NC NC NC Groundwater to Indoor Air NC NC NC Soil Gas to Indoor Air 1.9E-06 3.8E-01 NO Indoor Air NC NC NC Pathway Source Source Soil NC Source Groundwater NC Source Soil NC Source Groundwater NC 3. NM = Not Modeled 4. NC = Pathway not calculated 2. * = If concentrations in groundwater exceed the NC 2L Standards or IMAC, or concentrations in surface water exceed the NC 2B Standards, appropriate remediation and/or institutional control measures will be necessary to be eligible for a risk-based closure. Surface Water Exceedence of 2B at Receptor? Exceedence of 2B at Receptor? VAPOR INTRUSION CALCULATORS Resident Non-Residential Worker CONTAMINANT MIGRATION CALCULATORS Target Receptor Concentrations Exceeded? Groundwater Exceedence of 2L at Receptor? Exceedence of 2L at Receptor? 1. If lead concentrations were entered in the exposure point concentration tables, see the individual calculator sheets for lead concentrations in comparison to screening levels. Note that lead is not included in cumulative risk calculations. Notes: DIRECT CONTACT SOIL AND WATER CALCULATORS Resident Non-Residential Worker Recreator/Trespasser North Carolina DEQ Risk Calculator DEQ Risk Calculator - Vapor Intrusion - Non-Residential Worker Soil Gas to Indoor Air Version Date: January 2022 Basis: November 2021 EPA RSL Table Site ID: 22016-18-060 Exposure Unit ID: Sub-Slab Worst Case CAS #Chemical Name: Soil Gas Concentration (ug/m3) Calculated Indoor Air Concentration (ug/m3) Target Indoor Air Conc. for Carcinogens @ TCR = 1E-06 Target Indoor Air Conc. for Non- Carcinogens @ THQ = 0.2 Calculated Carcinogenic Risk Calculated Non-Carcinogenic Hazard Quotient 67-64-1 Acetone 1380 13.8 -- 75-15-0 Carbon Disulfide 7.72 0.0772 -6.1E+02 2.5E-05 110-82-7 Cyclohexane 169 1.69 -5.3E+03 6.4E-05 141-78-6 Ethyl Acetate 27.3 0.273 -6.1E+01 8.9E-04 100-41-4 Ethylbenzene 10.7 0.107 4.9E+00 8.8E+02 2.2E-08 2.4E-05 109-99-9 ~Tetrahydrofuran 876 8.76 -1.8E+03 1.0E-03142-82-5 Heptane, N-54.1 0.541 -3.5E+02 3.1E-0467-63-0 Isopropanol 24.3 0.243 -1.8E+02 2.8E-0478-93-3 Methyl Ethyl Ketone (2-Butanone)4050 40.5 -4.4E+03 1.8E-0375-09-2 Methylene Chloride 5.63 0.0563 1.2E+03 5.3E+02 4.6E-11 2.1E-05 91-20-3 ~Naphthalene 31.5 0.315 3.6E-01 2.6E+00 8.7E-07 2.4E-02 100-42-5 Styrene 33.1 0.331 -8.8E+02 7.6E-05 127-18-4 Tetrachloroethylene 12.4 0.124 4.7E+01 3.5E+01 2.6E-09 7.1E-04 108-88-3 Toluene 16.8 0.168 -4.4E+03 7.7E-06 79-01-6 Trichloroethylene 306 3.06 3.0E+00 1.8E+00 1.0E-06 3.5E-0175-69-4 Trichlorofluoromethane 5.84 0.0584 --95-63-6 Trimethylbenzene, 1,2,4-19.7 0.197 -5.3E+01 7.5E-04108-67-8 Trimethylbenzene, 1,3,5-6.39 0.0639 -5.3E+01 2.4E-04 108-38-3 Xylene, m-19.9 0.199 -8.8E+01 4.5E-04 95-47-6 Xylene, o-9.21 0.0921 -8.8E+01 2.1E-04 Cumulative:1.9E-06 3.8E-01 All concentrations are in ug/m3 Output Form 3E Carcinogenic risk and hazard quotient cells highlighted in orange are associated with non-volatile chemicals. Since these chemicals do not pose a vapor intrusion risk, no risk values are calculated for these chemicals. North Carolina DEQ Risk Calculator