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HomeMy WebLinkAbout23001_Decision Memo_ESTUL_11.15.2019DECISION MEMORANDUM DATE: November 15, 2019 FROM: Cody Cannon TO: Brownfields Assessment File RE: ESTUL Tools & Manufacturing 215 North Ames Street Matthews, Mecklenburg County BF # 23001-19-060 Based on the following information, it has been determined that the above referenced site, whose intended use is for no uses other than industrial, office, open space, retail, restaurant, brewery, parking, and, with prior written DEQ approval, other commercial uses, can be made suitable for such uses. Residential use is prohibited, but may be reconsidered and authorized under DEQ written approval after DEQ’s site-specific review of owner-proposed plans and the then-current conditions of the Brownfields Property. Introduction: The Brownfields Property comprises a single parcel totaling 2.05 acres. The property contains a single 33,000 square foot warehouse which is currently vacant. The Brownfields Property is bordered to the north by Matthews Building Supply, West Matthews Street, and undeveloped vacant land; to the east by North Ames Street followed by two commercial office parks separated by West Matthews Street; and to the south by a railway operated by CSX Transportation followed by two residential properties. Redevelopment Plans: The current tenant, who is the Prospective Developer (PD), plans to purchase the property and to renovate the existing warehouse building for a mixed use application including a brewery/restaurant, retail, and office spaces. Long term plans may include multi-family residential with prior written DEQ approval. Site History: The Brownfields Property was developed with a residence from at least 1938. The residential structure was removed by 1948. A small commercial warehouse was constructed by ESTUL Tools & Manufacturing (ESTUL) in 1954 when they began metal stamping and fabrication operations at the property. During the fabrication process, cutting oils were used to lubricate and cool metal components. Scrap metal generated during this process was placed in an uncovered dumpster located outside of the northwest corner of the Site building. ESTUL expanded the warehouse several times during its occupancy of the property until the current 32,500 square-foot building configuration was completed, as seen in a 1983 aerial photograph. ESTUL continued to operate at the property until an unknown date in the 2000s. The property was then utilized as a motorcycle dealership (Estridge Motorsports) until December 2016 and a storage facility through February 2017. Environmental Assessment History The North Carolina Department of Environment and Natural Resources (NCDENR) collected groundwater samples from several water supply wells in the vicinity of the Brownfields Property in early to mid-1990 in response to complaints made by several nearby business of a chemical odor in water coming from their water supply wells. Analytical results of the groundwater samples indicated the presence of several volatile organic compounds (VOCs), including benzene, tetrachloroethylene (PCE), trichloroethylene (TCE), and vinyl chloride. DEM issued a Notice of Violation (NOV) to ESTUL on October 22, 1990. A second NOV was also issued to ESTUL on September 27, 1991. A Subsurface Contaminant Assessment Report was completed by ESE Biosciences, Inc. in October, 1991. Three soil borings were installed to 15 feet below land surface (ft BLS), and one monitoring well (MW-1) was installed to 25 ft BLS in the vicinity of the scrap metal dumpster located outside of the northwest corner of the warehouse building. Detections of oil & grease and total VOCs were observed in soil samples at a depth of 13.5 to 15 ft BLS. Several VOCs were detected above the current (July 2016) North Carolina Administrative Code (NCAC) Title 15A Subchapter 2L groundwater standards (2L standards) including 1,1,1-trichoroethane (1,1,1-TCA), 1,1,2-trichloroethane (1,1,2-TCA), 1,1-dichloroethylene (1,1-DCE), trans-1,2-dichloroethylene, benzene, carbon tetrachloride, chloroform, methylene chloride, and PCE. A third NOV was issued to ESTUL on April 26, 1996, which was followed by a Notice of Regulatory Requirements (NORR) on June 19, 1996. ESE Environmental, Inc. (ESE) completed a Subsurface Investigation Report in September, 1996. Eight soil borings ranging in depth from 12 to 16 ft BLS were installed surrounding the location of the former scrap metal dumpster to assess lateral and vertical impacts in soil. VOCs were detected in several soil samples but no exceedances of the current (February 2018) Residential or Industrial Preliminary Soil Remediation Goals (PSRGs) were observed. A groundwater sample was collected from monitoring well MW-1, and several VOCs were detected at concentrations exceeding the 2L standards including PCE and TCE at 360 and 420 µg/L, respectively. The water supply well located at the neighboring (north) Matthew Building Supply (MBS) facility was also sampled. Several VOCs were detected but only 1,1-DCE exceeded the 2L standard. Additionally, a well survey with a 1,500-foot radius from the Brownfields Property was conducted. Of the five wells identified, three were associated with the MBS facility (1 supply, 1 injection, and 1 AC system). The two remaining wells are owned by Matthews Country Club and not used for human consumption. One of the wells was used to the fill the swimming pool and the other for the restroom facilities. VOCs were detected in the Matthews Country Club well but at concentrations below the 2L standards. Apex Companies, LLC completed a Vapor Intrusion Assessment Report for the former ESTUL facility on March 15, 2017. Potential vapor intrusion conditions were evaluated based on the 1991 and 1996 groundwater data as well as data reportedly collected from three exterior monitoring wells (including MW-1) in 2007 by ATC Associates of North Carolina, PC (ATC). No sample locations or data were provided but groundwater reportedly contained VOCs, including chlorinated solvents, at concentrations exceeding both 2L standards and the Non- Residential Vapor Intrusion Screening Levels (VISLs). Five indoor air samples and three sub- slab soil gas samples were collected in February, 2017. Several VOCs were detected in the sub- slab soil gas samples but only chloroform exceeded the Non-Residential VISL in one sample (SS- 1) located in the southernmost portion of the building at a concentration of 640 µg/m3. TCE was detected at concentrations exceeding the Non-Residential Indoor Air Screening Level (IASL) in three indoor air samples located in the central to northern sections of the building. The highest TCE concentration (2.6 µg/m3) was observed in sample IA-5 in the northwestern section of the building nearest to the former scrap metal dumpster. Benzene was detected at concentrations exceeding the Non-Residential VISL in all five indoor air samples and can likely be attributed to the many gasoline-powered vehicles being stored in the facility during sampling. DEQ Brownfields issued a request for additional assessment letter to the PD on March 4, 2019. A Brownfields Assessment Report was completed by Hart & Hickman, PC on June 25, 2019 and included additional soil, sub-slab soil-gas, groundwater, and indoor air assessment. A shallow soil sample was collected from the former scrap metal dumpster area, the former loading dock area, and a background location south of the southern corner of the building. Soil samples were analyzed for VOCs, semi-volatile organic compounds (SVOCs), and resource conservation and recovery act (RCRA) metals. Concentrations of total chromium and arsenic exceed the non- residential PSRGs but are within a range of naturally occurring background levels for the region. Groundwater samples were collected from monitoring well MW-1 and from temporary monitoring wells located near the southern and eastern corners of the property. VOCs were present at concentrations exceeding 2L standards in MW-1 but concentrations for all constituents had decreased significantly since 1996 with concentrations of PCE decreasing from 360 µg/L to 95 µg/L and TCE decreasing from 420 µg/L to 33 µg/L. Only PCE exceeded the 2L standard in temporary monitoring well TMW-2 at an estimated concentration of 0.94 µg/L. Approximately two weeks prior to sub-slab soil gas and indoor air assessment, cracks in the existing building slab were filled with epoxy sealants. Horizontal cracks were sealed with MM-80 (VOC-Free) and vertical cracks were sealed with Dymeric 240 (Low VOC). Five indoor air samples and two sub-slab soil samples were collected in the vicinity of the 2007 samples. One additional sub-slab sample (SS-4) was collected near the southern corner of the building. TCE was detected at concentrations exceeding the Residential Indoor Air Screening Level (IASL) in four of the five indoor air samples while none of the detections exceeded the Non-Residential IASL. Concentrations of PCE and TCE exceeded the Residential VISL in samples SS-3A in the northwestern portion of the warehouse and the Industrial VISL in sample SS-2A in the north- central portion of the warehouse. Potential Receptors: Potential receptors are: construction workers, on-site workers, visitors, and trespassers. A Brownfields Receptor survey was completed as part of the 2019 Brownfields Assessment Report. Two water supply wells were identified within 1,500-feet of the Brownfields Property. Both wells are located on the neighboring MBS property to the north. Neither well is operational and the MBS property is serviced by municipal water. Contaminated Media: DEQ has evaluated data collected from the following media at the subject property: soil, soil-gas, groundwater and indoor air. DEQ relies on the following data to base its conclusions regarding the subject property and its suitability for its intended reuse. Soil The concentration of arsenic exceeded the non-residential PSRG in 2019 soil sample SB-13 near the former loading dock. Concentrations of total chromium exceeded the non-residential PSRG in 2019 samples SB-12, SB-13, and SB-14. Groundwater Several VOCs including 1,1-dichloroethane, cis-1,2-dichloroethylene, PCE, TCE, and 1,1,2- TCA, and 1,4-Dioxane exceed the 2L standard in monitoring well MW-1. PCE also exceeded the 2L standard in temporary monitoring well TMW-2. Soil Vapor Concentrations of PCE and TCE (7,600 µg/m3 and 410 µg/m3, respectively) exceed the Non- Residential VISLs in sample SS-2A in the north-central portion of the warehouse. Additionally, 1,1-dichloroethylene (5,000 µg/m3) exceeds the Residential VISL in sample SS-2A. Concentrations of PCE and TCE (480 µg/m3 and 130 µg/m3) exceed the Residential VISLs in the sample SS-3A in the northwestern portion of the warehouse. Indoor Air Concentrations of TCE exceed the Residential IASL in all areas of the warehouse tested besides the southeastern corner. Concentrations ranged from 1.1 µg/m3 in the central portion of the warehouse to 1.7 in northwestern portion of the warehouse. Risk Calculations: Medium Site Area Non-Residential Worker LICR HI Groundwater Exposure Entire Site 5.2E-05 17 Groundwater to Indoor Air Entire Site 8.6E-06 2.9 Soil Exposure Entire Site 2.5E-06 3.3E-02 Sub-Slab Soil Gas Entire Site 3.4E-06 9.6E-01 Medium Site Area Resident LICR HI Groundwater Exposure Entire Site 2.5E-04 73 Groundwater to Indoor Air Entire Site 4.7E-05 12 Soil Exposure Entire Site 2.5E-06 3.3E-02 Sub-Slab Soil Gas Entire Site 1.1E-05 3.0E-01 Medium Site Area Non-Residential Worker LICR HI Indoor Air Entire Site 1.5E-06 2.4E-01 Medium Site Area Resident LICR HI Indoor Air Entire Site 7.8E-06 1.0 Medium Site Area Construction Worker LICR HI Soil Exposure Entire Site 4.2E-07 2.4E-01 Red shading LICR> 1E-04 or HI> 1. LICR = Lifetime Incremental Cancer Risk HI = Hazard Index Due to the results of the risk calculators, restrictions are in place regarding soil and groundwater exposure and use at the Brownfields Property. Required Land Use Restrictions: Based on the site-specific data provided to the Brownfield program, the site reuse is suitable for the site as long as the agreed upon land use restrictions in the BFA are abided by. 1. No use other than for industrial, office, retail, brewery, restaurant, parking, open space, and with prior written DEQ approval commercial uses. Residential use is prohibited, but may be reconsidered and authorized under DEQ written approval after DEQ’s site-specific review of owner-proposed plans and the then-current conditions of the Brownfields Property. 2. No groundwater use 3. No disturbing slab without DEQ approval (written notice to DEQ)/work for EMP; Confirmation indoor air sampling required after slab repairs. 4. Required Indoor Air Sampling of locations IA-1A, IA-2A, IA-3A, IA-4A, and IA-5A.  If VIMS installed: occupancy sampling plus biannual sampling. Terminate if 2 consecutive events result in NDs for COCs.  If no VIMS: annual sampling until stabilization or decreasing trend established (minimum 3 sampling events). 5. Final grade soil sampling. 6. Soil Import/Export. 7. No new buildings until DEQ says indoor air is safe/no VI issues/VI protection installed. 8. No disturbance of existing slab without DEQ approval. 9. Annual inspections/repairs of the slab crack repairs per sealant product specifications. Annual LURU update included. 10. EMP 11. Access to Brownfields Property for environmental assessment. 12. NBP reference in deed 13. No contaminants on property except for de minimis amounts, fluid in vehicles, fuels for generators/equipment 14. LURU submission January 1st JOB NO. BPP-003 FIGURE NO. 1 DATE: 5/16/2019 REVISION NO. 0 2923 South Tryon Street- Suite 100Charlotte, North Carolina 28203704-586-0007 (p) 704-586-0373 (f)License # C-1269 / #C-245 Geology SITE LOCATION MAP ESTUL TOOLS & MANUFACTURING COMPANY215 N. AMES STREET MATTHEWS, NORTH CAROLINA 0 2,000 4,000 SCALE IN FEET APPROXIMATEÜ U.S.G.S QUADRANGLE MAP MATTHEWS, NORTH CAROLINA, 2016 QUADRANGLE 7.5 MINUTE SERIES (TOPOGRAPHIC) SITE WAREHOUSE AREA FORMERLOADING DOCK RECEPTIONOFFICE & LOBBY REVISION NO. 0 JOB NO. BPP-003 DATE: 6-12-19 FIGURE NO. 2 ESTUL TOOLS & MANUFACTURING COMPANY215 N. AMES STREET MATTHEWS, NORTH CAROLINA SITE MAP LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL LINES RAILROAD APPROXIMATE RAILROAD RIGHT OF WAY FORMER DUMPSTER (APPROXIMATE) 2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)License # C-1269 / #C-245 Geology NOTES: 1.AERIAL IMAGERY OBTAINED FROM MECKLENBURG COUNTY GIS (2017).N. AMES STREETW . M A T T H EW S S T R E E T W. C H A R L E S S T R E E T MULTI-TENNANT BUILDING OLD NORTH STATE MASONRY(201 W. MATTHEWS STREET) RENFROW FARMS RESIDENTIAL MATTHEWS BUILDING SUPPLY(225 & 325 W. MATTHEWS ST.) WATER SUPPLYWELL HOUSE \\HHFS01\MasterFiles\AAA-Master Projects\Bat and Pick Partners (BPP)\BPP-003 215 N. Ames Street\Brownfields Assessment Report\Figures\Figures_5.13.19.dwg, FIG 2, 6/12/2019 10:18:43 AM,SVincent MW-1 SB-14 SB-13 SB-12 IA-3A SS-2A IA-4A IA-5A SS-3A TMW-2 TMW-3 SB-11 SB-1 SB-10 SB-9 SB-6 SB-8 SB-2 SB-7 SB-4 SB-5 SB-3 IA-4 SS-2 IA-3 SS-3IA-5 IA-2 SS-1IA-2A WAREHOUSE AREA FORMERLOADING DOCK SS-4 IA-1AIA-1 RECEPTIONOFFICE & LOBBY REVISION NO. 0 JOB NO. BPP-003 DATE: 6-12-19 FIGURE NO. 3 ESTUL TOOLS & MANUFACTURING COMPANY215 N. AMES STREET MATTHEWS, NORTH CAROLINA SAMPLE LOCATION MAP LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL LINES RAILROAD APPROXIMATE RAILROAD RIGHT OF WAY FORMER DUMPSTER (APPROXIMATE) MONITORING WELL (ESE 1991, ESE 1996, AND H&H 2019) TEMPORARY GROUNDWATER MONITORING WELLLOCATION (H&H 2019) SOIL BORING LOCATION (H&H 2019) HISTORICAL SOIL BORING LOCATION(ESE 1991 AND 1996) SUB-SLAB SOIL GAS SAMPLE LOCATION (H&H 2019) HISTORICAL SUB-SLAB SOIL GAS SAMPLE LOCATION (APEX 2017) INDOOR AIR SAMPLE LOCATION (H&H 2019) HISTORICAL AIR SAMPLE LOCATION (APEX 2017) 2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)License # C-1269 / #C-245 Geology NOTES: 1. AERIAL IMAGERY OBTAINED FROM MECKLENBURGCOUNTY GIS (2017). 2. HISTORICAL SAMPLING LOCATIONS ARE APPROXIMATEAND BASED ON INFORMATION PROVIDED IN HISTORICALASSESSMENT REPORTS COMPLETED BY ESEBIOSCIENCES, INC (ESE) IN 1991 AND 1996 AND APEXCOMPANIES LLC (APEX) IN 2017. 3. MONITORING WELL, SUB-SLAB SOIL GAS, AND INDOORAIR SAMPLE LOCATIONS COLLECTED USING A TRIMBLEGPS UNIT OR MEASURED BY H&H. 4. H&H COLLECTED SOIL AND GROUNDWATER SAMPLES ON4/9/19, INDOOR AIR SAMPLES ON 4/24/19, AND SUB-SLAB GAS SAMPLES ON 4/25/19 AND 4/26/19. 5. MONITORING WELL MW-1 AND TEMPORARY MONITORINGWELLS TMW-2 & TMW-3 WERE ABANDONED FOLLOWINGAPRIL 2019 SAMPLING EVENT.N. AMES STREETW . M A T T H EW S S T R E E T W. C H A R L E S S T R E E T MULTI-TENNANT BUILDING OLD NORTH STATE MASONRY(201 W. MATTHEWS STREET) RENFROW FARMS RESIDENTIAL MATTHEWS BUILDINGSUPPLY(325 W. MATTHEWS ST.) WATER SUPPLYWELL HOUSE \\HHFS01\MasterFiles\AAA-Master Projects\Bat and Pick Partners (BPP)\BPP-003 215 N. Ames Street\Brownfields Assessment Report\Figures\Figures_5.13.19.dwg, FIG 3, 6/12/2019 10:19:19 AM,SVincent MW-1 TMW-2 TMW-3 WAREHOUSE AREA FORMERLOADING DOCK 89 90 91 92 92 91 90 89 (88.23) (90.20) (92.68) RECEPTIONOFFICE & LOBBY REVISION NO. 0 JOB NO. BPP-003 DATE: 5-20-19 FIGURE NO. 5 ESTUL TOOLS & MANUFACTURING COMPANY215 N. AMES STREET MATTHEWS, NORTH CAROLINA GROUNDWATER POTENTIOMETRICSURFACE MAP LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL LINES RAILROAD APPROXIMATE RAILROAD RIGHT OF WAY FORMER DUMPSTER (APPROXIMATE) MONITORING WELL (ESE 1991, ESE 1996, AND H&H 2019) TEMPORARY GROUNDWATER MONITORING WELLLOCATION (H&H 2019) GROUNDWATER ELEVATION (FT MSL) GROUNDWATER ELEVATION CONTOUR (FT MSL)(DASHED WHERE INFERRED) INFERRED GROUNDWATER FLOW DIRECTION 2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)License # C-1269 / #C-245 Geology NOTES: 1. DEPTH-TO-WATER MEASUREMENTS COLLECTED ON4/9/19. 2. ELEVATIONS ARE MEASURED RELATIVE TO ANARBITRARY DATUM OF 100 FT (MW-1 TOC). 3. MSL = MEAN SEA LEVELTOC = TOP OF CASING N. AMES STREETW . M A T T H EW S S T R E E T W. C H A R L E S S T R E E T MULTI-TENNANT BUILDING OLD NORTH STATE MASONRY(201 W. MATTHEWS STREET) RENFROW FARMS RESIDENTIAL MATTHEWS BUILDINGSUPPLY(325 W. MATTHEWS ST.) WATER SUPPLYWELL HOUSE 90 (90.20)\\HHFS01\MasterFiles\AAA-Master Projects\Bat and Pick Partners (BPP)\BPP-003 215 N. Ames Street\Brownfields Assessment Report\Figures\Figures_5.13.19.dwg, FIG 5, 5/20/2019 2:02:36 PM,SVincent MW-1 TMW-2 TMW-3 WAREHOUSE AREA FORMERLOADING DOCK RECEPTIONOFFICE & LOBBY TMW-2 PCE 0.94 J REVISION NO. 0 JOB NO. BPP-003 DATE: 5-21-19 FIGURE NO. 6 ESTUL TOOLS & MANUFACTURING COMPANY215 N. AMES STREET MATTHEWS, NORTH CAROLINA GROUNDWATER CONTAMINANTCONCENTRATION MAP LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL LINES RAILROAD APPROXIMATE RAILROAD RIGHT OF WAY FORMER DUMPSTER (APPROXIMATE) MONITORING WELL (ESE 1991, ESE 1996, AND H&H 2019) TEMPORARY GROUNDWATER MONITORING WELLLOCATION (H&H 2019) 2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)License # C-1269 / #C-245 Geology NOTES: 1. GROUNDWATER SAMPLES WERE COLLECTED ON 4/9/19. 2. ONLY CONSTITUENTS DETECTED ABOVE THE 15A NCAC02L.0202 GROUNDWATER STANDARDS (2L STANDARDS)ARE SHOWN. 3. J = ESTIMATED CONCENTRATION BETWEEN METHODDETECTION LIMIT AND LABORATORY REPORTING LIMIT* = ANALYTE CONCENTRATION REPRESENTATIVE OFDUPLICATE SAMPLE<2L = LESS THAT THE 2L STANDARD 4. DCA = DICHLOROETHANE DCE = DICHLOROETHENEPCE = TETRACHLOROETHENE TCA = TRICHLOROETHANETCE = TRICHLOROETHENEN. AMES STREETW . M A T T H EW S S T R E E T W. C H A R L E S S T R E E T MULTI-TENNANT BUILDING OLD NORTH STATE MASONRY(201 W. MATTHEWS STREET) RENFROW FARMS RESIDENTIAL MATTHEWS BUILDINGSUPPLY(325 W. MATTHEWS ST.) WATER SUPPLYWELL HOUSE MW-1 1,1-DCA 29* CIS-1,2-DCE 150* PCE 100* 1,1,2-TCA 22* TCE 36* 1,4-DIOXANE 33 TMW-2 PCE 0.94 J TMW-3 ALL CONSTITUENTS <2L SAMPLE ID CONSTITUENT CONCENTRATION(µg/L)\\HHFS01\MasterFiles\AAA-Master Projects\Bat and Pick Partners (BPP)\BPP-003 215 N. Ames Street\Brownfields Assessment Report\Figures\Figures_5.13.19.dwg, FIG 6, 5/21/2019 9:57:32 AM,SVincent IA-3A SS-2A IA-4A IA-5A SS-3A IA-2A WAREHOUSE AREA FORMERLOADING DOCK SS-4 IA-1A RECEPTIONOFFICE & LOBBY IA-3A (4/24/19) CR 1.1E-06 HI 1.6E-01 REVISION NO. 0 JOB NO. BPP-003 DATE: 6-12-19 FIGURE NO. 7 ESTUL TOOLS & MANUFACTURING COMPANY215 N. AMES STREET MATTHEWS, NORTH CAROLINA NON-RESIDENTIAL CUMULATIVE VAPORINTRUSION RISK MAP LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL LINES RAILROAD APPROXIMATE RAILROAD RIGHT OF WAY FORMER DUMPSTER (APPROXIMATE) SUB-SLAB SOIL GAS SAMPLE LOCATION (H&H 2019) INDOOR AIR SAMPLE LOCATION (H&H 2019) 2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)License # C-1269 / #C-245 GeologyN. AMES STREETW . M A T T H EW S S T R E E T W. C H A R L E S S T R E E T MULTI-TENNANT BUILDING OLD NORTH STATE MASONRY(201 W. MATTHEWS STREET) RENFROW FARMS RESIDENTIAL MATTHEWS BUILDINGSUPPLY(325 W. MATTHEWS ST.) WATER SUPPLYWELL HOUSE IA-1A (4/24/19) CR 1.2E-06 HI 1.6E-01 SAMPLE ID & DATE RISK TYPE RISK LEVEL SS-4 (4/26/19) CR 5.8E-08 HI 1.4E-02 IA-2A (4/24/19) CR 5.7E-07 HI 7.0E-02 IA-3A (4/24/19) CR 1.1E-06 HI 1.6E-01 SS-2A (4/25/19) CR 3.3E-06 HI 9.6E-01 IA-4A (4/24/19) CR 1.1E-06 HI 1.6E-01 IA-5A (4/24/19) CR 1.4E-06 HI 2.5E-01* SS-3A (4/25/19) CR 6.8E-07* HI 1.8E-01* NOTES: 1. INDOOR AIR SAMPLES WERE COLLECTED ON 4/24/19 ANDSUB-SLAB SOIL GAS SAMPLES WERE COLLECTED ON 4/25/19 AND 4/26/19. 2. CR = CARCINOGENIC RISKHI = NON-CARCINOGENIC HAZARD INDEX* = CUMULATIVE RISK REPRESENTATIVE OF DUPLICATESAMPLE \\HHFS01\MasterFiles\AAA-Master Projects\Bat and Pick Partners (BPP)\BPP-003 215 N. Ames Street\Brownfields Assessment Report\Figures\Figures_5.13.19.dwg, FIG 7, 6/12/2019 10:21:24 AM,SVincent