HomeMy WebLinkAbout26077 - Pattons Facility - Kick-Off Meeting PresentationRedevelopment Now Kick-Off Meeting
Former Pattons Facility
3119, 3127, 3201, 3205, 3207, 3209, and 3215 South Boulevard
and 3232/3234 Weston Street
Charlotte, Mecklenburg County
BF Project No. 26077-22-060
Monday, March 27, 2023
Site
Site Location
•Approximately 2 miles southeast of Uptown Charlotte
•Located along the Lynx Blue Line between Scaleybark and New Bern Stations
•Rapidly densifying LoSoneighborhood
Site Location and
Current Uses
•2 parcels of land
•Collectively total approximately 2.9
acres
•Anchor Parcel
•asphalt and concrete-paved
parking areas
•concrete building slabs
•buildings demolished by former property owner in early 2023 (prior to PD ownership)
•Southern Site Parcel
•vacant duplex
•Surrounding Properties
•residential
•commercial retail/officeN
Former Press Club Cleaners
BPN 25101-21-060
Radio Center
BPN 19072-15-060
Former Pattons Facility
BPN 26077-22-060
Site History and Development
Brownfields Property
•Late 1930s -Developed with four
residences and associated ancillary
structures
•1945 –Initial development associated
with the Pattons facility constructed in
the eastern portion of the Site
•1951 –Duplex constructed on the
southern Site parcel
•1960 through 1990s –Pattons
operations expanded east along South
Boulevard with other commercial uses in
the 1960s
•2020 –Pattons operations ceased and
vacated the property in 2021-2022
1938 Aerial Photograph
2017 Aerial Photograph
1965 Aerial Photograph
Historical Site Occupants
3119 South Boulevard
•Tidewater Oil Co. (1953)•Tire recapping facility (late 1950s-1960s)
3127 South Boulevard
•Queen City Tire Co. (1959)•various retailers (1959 –mid-1960s)
3201 South Boulevard
•Dixie Wile Meat Co. (1949)
•Novelty Manufacturing & Sales (1949)•Pattons / Air Compressors Inc. (1969-2020)
3205 South Boulevard
•Universal Winding Co. (1959)•Pattons / Air Compressors Inc. (1969-2020)
1963 Sanborn Map
RCRA CESQG –NCD981861164
1980s and 1990s -Pattons used mineral spirits to clean air compressor parts.
Waste materials were disposed off-Site by Safety Kleen
Non-Generator in September 2021
No RCRA compliance violations or release incidents
LUST Incident No. 40296
1960s –Pattons installed one 2,000-gallon gasoline UST
Early 1970s –Pattons installed one 6,000-gallon gasoline and two 4,000-gallon gasoline USTs
June 1988 –All four USTs removed
January 2013 –Phase II ESA
•Northern UST Basin –TPH-GRO 19 mg/kg
•Southern UST Basin –TPH-GRO up to 1,100 mg/kg
LSA Sample Analysis (October 2014)
•Northern UST Basin
o VOC and VPH < MSCCs
o Naphthalene and C9-C10 aromatics above the 2L Standards
•Southern UST Bain
o VOC and VPH above Soil-to-Groundwater MSCCs, but below Residential and Commercial/Industrial MSCCs
o Benzene, naphthalene, 1,2,4-trimethylbenzene, total xylenes, C5-C8 aliphatics, and C9-C10 aromatics above 2L Standards
December 16, 2019 –UST Section NFA Letter
•NORP recorded on deed states groundwater is not suitable for water supply
•NORP will be superseded through Brownfields process
Obtained from Limited Site Assessment prepared by H&H dated October 20, 2014.
N
Impacts Near Duplex in Southeast Corner of Site
Press Club Cleaners DSCA#DC600090 located approximately 350 ft southwest of the Site.
Drycleaning operations from 1945-2021
Entered the DSCA Program in 2016
Brownfields Project No. 25101-21-060
Groundwater –December 2020
•PCE, TCE, 1,2-DCA, and IPE in MW-5 just west of duplex parcel above 2L Standards
•MW-5 abandoned in December 2020
Exterior Soil Gas –October 2017 (over 5 years ago)
•PCE (up to 73,000 µg/m3)
•TCE (up to 16,000 µg/m3)
Duplex Crawlspace Air –December 2017
•PCE (6.3 µg/m3) below Residential IASLs
•PCE (3.8 µg/m3) also detected in background air sample
•LICR and HI within DEQ-acceptable levels
•No Vapor Intrusion Action Needed Per DSCA
Previous Assessments –2022 H&H Phase I ESA Findings
REC
•Documented CVOCs in groundwater on adjacent and cross-gradient properties and in soil gas samples collected from the southern Site parcel
CREC
•NFA on LUST Incident No. 40296N
Preliminary Redevelopment Plan
Lower Level Floor Plan
Site Plans prepared by Axiom Architecture dated November 30, 2022.
•Grade lower to southeast allows for
ground entry into lower level units
•Slab on grade apartment units to
southeast
•Mostly podium construction with
parking garage on grade with
apartments above Level 1 Floor Plan
Phase II ESA –Scope of Work
Receptor Survey
VOCs, Semi-VOCs, RCRA Metals, Hex Cr
Soil SamplingFormer caustic degreaser and oil storage areaFormer UST basinsFormer wash padProposed areas of disturbance
Site-Wide Groundwater Sampling
Exterior and Sub-Slab Soil Gas Sampling
Receptor Survey
No water supply wells
•Former on-Site WSW abandoned in 1960s
•Consistent with Phase I LSA
Unnamed tributary of Little Hope Creek approximately 1,300 ft southeast N
Assessment Activities
N
Soil Sampling
General Site Characterization
•Five (5) samples collected
•VOCs detected above MDLs, but below the DEQ Residential PSRGs
•SVOCs <MDLs
•Metals consistent with naturally occurring background levels and below the DEQ PSRGs
Former UST Basins, Caustic Degreaser, and Oil Storage Area
•Three (3) samples
•VOCs detected above MDLs, but below DEQ Residential PSRGs
•SVOCs <MDLs
•Detected metals concentrations below PSRGs and within background levels
Former Wash Pad
•One (1) sample
•VOCs and SVOCs detected above MDLs, but below DEQ Residential PSRGs •Lead (127 mg/kg) above Rule of 20, but below DEQ
PSRGs (TCLP 0.051 mg/L)
•Remaining detected metals concentrations below PSRGs
and within background levels
N
Groundwater Sampling
Six temporary monitoring wells
•upgradient, downgradient, and cross-gradient of Site operations
•downgradient of former vapor degreaser and oil storage area
Groundwater flows generally to the southeast
TMW-1
•Installed upgradient of Site operations
•Chloroform (10.9 µg/L) above the GWSLs
TMW-4/GW-DUP
•Installed downgradient of former vapor degreaser and oil storage area
•Benzene (up to 1.17 µg/L) above 2L Standard, but below GWSLs
VOCs, SVOCs, and metals <2L Standards and GWSLs in remaining wells
N
SG/SSV Sampling
Five (5) exterior soil gas and four (4) sub-slab soil gas monitoring points installed
Petroleum-related compounds above Residential and/or Non-Residential SGSLs in several samples
No CVOCs above SGSLs
TCE not detected above MDL (typically <0.199 µg/m3)
Hypothetical Worst-Case Risk Calculations
LICR 9.1 x 10-5
HI 1.2N
Letter of Eligibility
“Given the detection of TCE on the property, additional assessment will be necessary for DEQ to determine if vapor mitigation measures can make the site safe for residential use.”
Supplemental Phase II ESA activities completed in February 2023
Supplemental Assessment Activities
N
Soil Sampling
Southern Site Parcel
•Acetone detected above MDLs, but below DEQ
Residential PSRGs
•Benzo(a)pyrene (0.239 J mg/kg) detected in SB-
11 above DEQ Residential PSRG
•Arsenic (4.40 mg/kg) in SB-11 above background metals established on nearby Brownfields properties
•Lead (300 mg/kg) and chromium (119 mg/kg) in
SB-11 above Rule of 20, but below DEQ PSRGs (TCLP 0.106 mg/L and < MDL, respectively)
•Remaining detected metals concentrations below PSRGs and within background levels
•Hypothetical Worst-Case Risk Calculations
•LICR 9.7 x 10-6
•HI 0.22 N
Groundwater Sampling
TMW-7
•PCE (88.8 µg/L), TCE (103 µg/L), 1,2-DCA
(10.1 µg/L) above 2L Standards and
GWSLs
•DIPE (86.5 µg/L) above 2L Standard, but
below GWSLs
•Chloroform (1.88 µg/L) above
Residential GWSL, but below 2L
Standard
•SVOCs <MDLs
•Metals not detected at concentrations
above the 2L Standards N
N
Soil Gas Sampling
Five (5) additional exterior soil gas soil gas monitoring points installed
Benzene (up to 30.2 µg/m3) above Residential SGSL, but below Non-Residential SGSL in three samples
PCE (409 µg/m3) above Residential SGSL, but below Non-Residential SGSL in SG-14
TCE not detected above MDLs (<0.199 µg/m3)
Risk Calculator for Worst-Case Southeast Data
Cumulative LICR 8.4 x 10-6
Cumulative HI 0.44
No TCE in Soil Gas
Total of 14 soil gas and SSV monitoring points
TCE not detected above MDLs during 2022 and 2023 assessment activities
Propose Passive Vapor Intrusion Mitigation System (with potential to go active)N
Assessment Summary
Shallow soil impacts limited to metals and select low-level PAHs in the southern portion of the Site
Low level impacts in Site groundwater at concentrations above the 2L Standards and/or DWM Vapor Intrusion GWSLs are limited to the southern portion of the Site and downgradient of the former oil storage area
Results of the exterior soil gas and SSV assessment activities identified several compounds at concentrations above the Residential SGSLs
PCE was detected in one (1) sample at a concentration above the Residential SGSL
TCE was not detected above laboratory MDLs
Schedule and Milestones
Brownfields Property Application submittal (November 3, 2022)
Brownfields Program Letter of Eligibility (January 12, 2023)
Kick-off/Data Gap Meeting (March 27, 2023)
Need Confirmation of Residential Use (March 27, 2023)
EMP Approval by July 2023
1st VIMP Submittal August 2023
Draft BFA and Negotiation (October 2023)
Begin Public Comment (November 2023)
Record BFA (January 2024)