24054_AJACC Auto_Soil Import from Dynatech Review Package_20220218

February 18, 2022
Sent Via E-mail Mason Ellerbe Josh Glover
Abacus Company Greystar Development East, LLC
1200 E Morehead St, Suite 280 421 E Morehead Rd, Suite 400 Charlotte, North Carolina 28204 Charlotte, NC 28202 [e-mail] [e-mail]
Subject: Brownfields Property Soil Transfer Approval
Dynatech Properties and AJACC Auto Brownfields Property Charlotte, Mecklenburg County Brownfields Project No. 25001-21-060, 25067-21-060 and 24054-20-060
Mr. Ellerbe and Mr. Glover,
The North Carolina Department of Environmental Quality (DEQ) Brownfields Program received and reviewed a request to export approximately 17,000 cubic yards of soil from Dynatech Brownfields Properties to AJACC Auto Brownfields Property. This request was submitted on
your behalf by Ms. Haley Martin of Hart & Hickman (H&H) in her email dated February 11. 2022,
titled 25001&25067- Dynatech- Soil Export Request. DEQ understands the redevelopment on the Dynatech II Brownfield Property (25001-21-060) and Dynatech III Brownfields Property (25067-21-060) will be done jointly under the DEQ-approved Environmental Management Plan (EMP) dated January October 19, 2021.
DEQ Brownfields reviewed the analytical data and site maps provided in the correspondence. The request is to export up to 17,000 cubic yards of soil from the Dynatech Brownfields Properties from the following sections FCC-2B, FCC-3A/B, FCC-4A/B, FCC-5A/B, FCC-8B, and FCC-9. Based on a review of the DEQ Risk Calculator which incorporated data from both properties did
not increase risk at the receiving AJACC Auto Brownfield Property. Therefore, DEQ Brownfields approves up to 17,000 cubic yards of soil to be exported to the AJACC Auto Brownfields Property. All soil export must be conducted under a DEQ Brownfields approved Environmental
Management Plan (EMP). Soils should be field screened during excavation prior to export from
the property. If unanticipated impacts are identified during excavation, please refer to the EMP for further actions and cease transfer until appropriate characterization can be completed In addition, in accordance with the approved EMPs, annual Redevelopment Summary Reports will be submitted to DEQ Brownfields. Details related to the disposition of this soil including but not
limited to, total volume, general description of field screening efforts, etc. should be included with
each Property’s Redevelopment Summary Report.
February 18, 2022 Page 2
Please be advised that this approval does not waive any applicable requirement to obtain any necessary permits, licenses, or certifications which may be required from other state or local entities. If you have questions about this correspondence or require additional information, please feel free to contact me by phone at 704-661-0330 or by email at [e-mail].

Sincerely,
Carolyn Minnich Peter Doorn
Project Manager Project Manager
Brownfields Program Brownfields Program ec: Doorn, Peter L [e-mail] Cody Cannon [e-mail]
Haley Martin [e-mail]
Ralph McGee [e-mail] Chris Hustek, [e-mail]
1
Doorn, Peter L
From:Minnich, Carolyn
Sent:Wednesday, February 16, 2022 3:13 PM
To:Doorn, Peter L
Subject:FW: [External] 25001 & 25067 - Dynatech - Soil Export Request
Attachments:Dynatech - Export Request Package.pdf
Request to send soils to 24054.  I will review and copy you on my  conclusion.  I just sent a TEAMS message about 
cumulative risk cal. 

From: Haley Martin [mailto:[e-mail]]  
Sent: Friday, February 11, 2022 3:59 PM 
To: Minnich, Carolyn <[e-mail]> 
Cc: Ralph McGee <[e-mail]> 
Subject: [External] 25001 & 25067 ‐ Dynatech ‐ Soil Export Request  

CAUTION: External email. Do not click links or open attachments unless you verify. Send all suspicious email as an attachment to 
Report Spam. 

Carolyn,  

H&H understands that the AJACC Auto Brownfields property (BPN 24054‐20‐060) located off of Verbena Street in 
Charlotte is planning import of up to 17,000 cubic yards of fill material as part of the proposed redevelopment.  The PDs 
for the Dynatech II and Dynatech III Brownfields properties (BPNs 25001‐21‐060 and 25067‐21‐060) are requesting 
approval to transfer excess soil generated during mass grading activities in the areas of in situ soil characterization areas 
FCC‐2B (12‐18 feet below ground surface [ft bgs]), FCC‐3A/3B (4‐14 ft bgs), FCC‐4A/4B (4‐14 ft bgs), FCC‐5A/5B (5‐13 ft 
bgs), FCC‐8B (6‐8 ft bgs), and FCC‐9 (6‐8 ft bgs) to the AJACC Auto Brownfields property.  The soil characterization areas 
to be exported from the Dynatech Brownfields properties are outlined in green on the attached Figure.  In accordance 
with the DEQ‐approved Environmental Management Plan (EMP), excess soil in these soil characterization areas can be 
transferred to another Brownfields property for use as fill material, with concurrence from DEQ Brownfields. It is of note 
that shallow soils from evaluation areas FCC‐2 (0‐5 ft bgs), FCC‐3 (0‐4 ft bgs), and FCC‐4 (0‐4 ft bgs) will not be exported 
from the Dynatech Brownfields properties without prior DEQ approval.   

We have prepared the attached Soil Export Request Package which includes a tabular summary of the highest 
concentrations detected at both the Dynatech II and III Brownfields properties and the AJACC Auto Brownfields 
property, a figure depicting the location of the soil characterization areas at the Dynatech properties, and cumulative 
worst‐case risk calculations. In summary, no organic compounds were detected in soil samples collected in the in situ 
soil characterization areas FCC‐2B, FCC‐3A/3B, FCC‐4A/4B, FCC‐5A/5B, FCC‐8B, and FCC‐9 at concentrations above the 
2
DEQ IHSB Protection of Groundwater or Residential PSRGs.  In addition, detected concentrations of metals at the 
Dynatech properties appear to be consistent with those detected at the AJACC Auto Brownfields property.  

H&H calculated the cumulative risks using the highest concentration of any compound at either Brownfields property to 
model hypothetical “worst‐case” exposure scenarios under a residential, non‐residential, construction worker, and 
trespasser scenario.  As expected, risk calculations indicate that direct exposure soil pathway for a resident, non‐
residential worker, construction worker, and trespasser do not exceed the threshold criteria for carcinogenic or non‐
carcinogenic risks.   

The export package also includes email confirmation from the PD of AJACC Auto, Greystar Development East, LLC, 
indicating they are willing to accept the proposed export material from the Dynatech properties.  Based on the detected 
compound concentrations below the DEQ IHSB Residential PSRGs and the results of the worst‐case risk calculations, the 
PD requests DEQ approval to transport material from in situ soil characterization areas FCC‐2B, FCC‐3A/3B, FCC‐4A/4B, 
FCC‐5A/5B, FCC‐8B, and FCC‐9 to the AJACC Auto Brownfields property.  

As you may know, grading construction work is ongoing. We appreciate your reviewing this data to assist in keeping the 
construction schedule on track. In the meantime, please let us know if you have any questions or concerns. 

Thank you,  
Haley 

Haley Martin, PG, Senior Project Geologist
Hart & Hickman, PC
2923 S Tryon Street, Suite 100 ꞏ Charlotte, NC 28203
Direct: 704-526-2045 ꞏ Mobile: [phone]
www.harthickman.com   

Table 1 Summary of Highest Detected ConcentrationsDynatech II and IIICharlotte, North CarolinaH&H Job No. ABS-002Sample LocationDynatech II and III3AJACC Auto4Sample IDFCC-2B, FCC-3A/3B, FCC- 4A/4B, FCC-5A/5B, FCC-8B, and FCC-9SB-1 through SB-5Sample DateJune 2021 April 2021Range MeanVOCs (8260)Acetone 0.103 J 0.037 25 12,000 140,000-- --Ethyl tert butyl etherND0.0008 J NE NE NE-- --Methyl Ethyl Ketone ND0.002 J 17 5,500 40,000-- --Methyl tert-Butyl EtherND 0.019 0.09 49 220-- --Naphthalene 0.0237ND0.39 2.1 8.8-- --p-Isopropyltoluene 0.0053 JNDNE NE NE-- --Toluene 0.0360ND8.3 990 9,700-- --1,2,3-Trichlorobenzene 0.0091ND0.33 13 190-- --1,2,4-Trimethylbenzene 0.0082ND12 63 370-- --m&p-Xylene 0.0182ND9.8 120 500-- --o-Xylene 0.0104ND9.8 140 590-- --Xylenes (Total) 0.0286ND9.9 120 530-- --SVOCs (8270)Benzo(a)anthraceneND0.059 J 0.35 1.1 21-- --Benzo(a)pyreneND0.087 J 0.12 0.11 2.1-- --Benzo(b)fluoranthene 0.184 J 0.126 J 1.2 1.1 21-- --Benzo(g,h,i)peryleneND0.057 J NE NE NE-- --Fluoranthene 0.306 J 0.117 J 670 480 6,000-- --Indeno(1,2,3-cd)pyreneND0.045 J 3.9 1.1 21-- --2-MethylnaphthaleneND0.028 J 3.1 48 600-- --NaphthaleneND0.021 J 0.39 2.1 8.8-- --Phenanthrene 0.221 J 0.065 J NE NE NE-- --Pyrene 0.303 J 0.105 J 440 360 4,500-- --Metals (6020/7471/7199)Arsenic 1.1 J 3.4 5.8 0.68 3 1.0 - 18 4.8Barium 323 633 580 3,100 47,000 50 - 1,000 356Cadmium 0.14 0.281 J 3 14 200 1.0 - 10 4.3Chromium (total) 113 59.3 NS NS NS 7.0 - 300 65Chromium (trivalent) 111.7 58.73 360,000 23,000 350,000 NS NSChromium (hexavalent)1.30 0.57 J3.8 0.31 6.5 NS NSLead 49.4 56.3 270 400 800 ND - 50 16Mercury 0.091 0.0587 J 1 2.3 9.7 0.03 - 0.52 0.121Selenium 2.5 5.48 2.1 78 1,200 <0.1 - 0.8 0.42SilverND0.0705 J 3.4 78 1,200 ND - 5.0 NSNotes:1) North Carolina Department of Environmental Quality (DEQ) Inactive Hazardous Sites Branch (IHSB) Preliminary Soil Remediation Goals (PSRGs) dated June 20212) Range and mean values of background metals taken from Elements in North American Soils by Dragun and Chekiri, 2005. Cd and Ag concentrations were taken from Southeastern Conterminous U.S. Soils (Dragun and Chekiri, 2005). 3) Dynatech II and III data was obtained from the NCDEQ Brownfields approved Environmental Management Plan prepared by Hart & Hickman, PC dated October 19, 2021.4) AJACC Auto data was obtained from the NCDEQ Brownfields approved Environmental Management Plan prepared by Froehling & Robertson, Inc. dated August 10, 2021.Laboratory analytical methods are shown in parentheses.Bold values exceed the Residential PSRG and background concentrations in the case of metals.VOCs = volatile organic compounds; SVOCs = semi-volatile organic compounds; NS = not specified; NE = not established; ND = non-detect; -- = not applicableJ = Compound was detected above the laboratory method detection limit, but below the laboratory reporting limit resulting in a laboratory estimated concentration. Regional Background Metals In Soil2Screening CriteriaProtection of Groundwater PSRGs1Residential PSRGs1Industrial/ Commercial PSRGs1https://harthick.sharepoint.com/sites/MasterFiles-1/Shared Documents/AAA-Master Projects/Abacus Capital (ABS)/Dynatech II/Site Work/BF to BF Transfer Request/ABS-002 Data Tables.xlsxTable 1 (Page 1 of 1)Hart & Hickman, PC
REVISION NO. 0
JOB NO. ABS-002
DATE: 9-27-21
FIGURE NO. 2
DYNATECH II, III, & IV
TOOMEY AVENUE AND WEST TREMONT AVENUE
CHARLOTTE, NORTH CAROLINA
SITE AND SAMPLE LOCATION MAP
LEGEND
BROWNFIELDS PROPERTY BOUNDARY
PARCEL BOUNDARY
SOIL CHARACTERIZATION AREA
SOIL BORING LOCATION
SOIL CHARACTERIZATION ALIQUOT
BORING LOCATION
CO-LOCATED SOIL AND GROUNDWATER
SAMPLE LOCATION
SOIL GAS 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 GeologyTOOMEY AVE
N
UE
W TREMONT AVENU
E WOODCREST AVENUE
FC-24
FC-22
FC-20
FC-21
FC-23
FC-25
FC-19
FC-18
FC-17
FC-26
FC-27
FC-28
FC-29
FC-32
FC-31
FC-30
FC-15
FC-16
FC-1
FC-5
FC-12
FC-14
FC-13
FC-9
FC-10FC-11
FC-7 FC-8
FC-2
FC-4
FC-3
FC-6
B-9
B-10
B-7
B-8/MW-3
B-6/MW-2
B-5/MW-1
MW-4/4R
B-2/B-2GW
B-1/B-1GW
B-4B-4GW
B-3/B-3GW
FCC-8
FCC-7
FCC-6
FCC-9
FCC-5
FCC-2 FCC-4
FCC-3
FCC-1
NOTES:
1.PARCEL DATA AND AERIAL IMAGERY OBTAINED FROM
MECKLENBURG COUNTY GIS, 2021.
2.SOIL SAMPLES B-1* THROUGH B-3*, GROUNDWATER
SAMPLES B-1GW* THROUGH B3-GW*, AND SOIL GAS
SAMPLES SG-1 THROUGH SG-3 WERE COLLECTED ON
THE WESTERN SITE PARCEL BY PARTNER IN
DECEMBER 2020.
3.SOIL SAMPLES B-1 THROUGH B-4, GROUNDWATER
SAMPLES B-1GW THROUGH B-4GW, AND MSVG-1
THROUGH MSVG-7 WERE COLLECTED ON THE
EASTERN SITE PARCELS BY PARTNER IN JANUARY
2021.
4.BORINGS B-5 THROUGH B-10 AND FC-1 THROUGH FC-32
ADVANCED BY PARTNER IN JUNE 2021.
5.MONITORING WELLS MW-1 THROUGH MW-3 WERE
INSTALLED BY PARTNER IN JUNE 2021. WELLS MW-4
AND MW-4R WERE INSTALLED BY OTHERS IN
SEPTEMBER 2000.
6.SOIL GAS SAMPLES MSG-4 THROUGH MSG-22 WERE
COLLECTED BY PARTNER IN MAY AND JUNE 2021.
7.BPN = BROWNFIELDS PROJECT NUMBER
B-2*/B-2GW*
B-1*/B-1GW*
B-3*/B-3GW*
SG-2
SG-1SG-3
MSVG-5
MSVG-7
MSVG-6
MSVG-1
MSVG-2
MSVG-3
MSVG-4
MSG-15
MSG-19
MSG-16
MSG-17
704 W. TREMONT AVENUE2325 TOOMEY AVENUE
728 W. TREMONT AVENUE
2213 TOOMEY AVENUE
2330 TOOMEY AVENUE
POWERS SITE BROWNFIELDS PROPERTY
(BPN 20045-16-060)
MSG-1
MSG-2
MSG-3
MSG-22
MSG-21
MSG-20
MSG-18
MSG-14
MSG-12
MSG-13
MSG-10
MSG-11
MSG-9
MSG-8
MSG-7
MSG-4
MSG-5
MSG-6
M:\AAA_DRAFTING\ABS-002\Site Map.dwg, FIGURE 2, 9/27/2021 1:03:21 PM, sperry
Version Date:
Basis:
Site Name:
Site Address:
DEQ Section:
Site ID:
Exposure Unit ID:
Submittal Date:
Reviewed By:
Prepared By:HHM
RWM
Site Wide - Cumulative Hypothetical Worst-Case
North Carolina Department of Environmental Quality
Risk Calculator
Dynatech II and III and AJACC Auto
Charlotte, Mecklenburg County
DWM Brownfields Program
25001-21-060, 25067-21-060, and 24054-20-060
June 2021
May 2021 EPA RSL Table
North Carolina DEQ Risk Calculator
Complete Exposure Pathways
Version Date: June 2021
Basis: May 2021 EPA RSL Table
Site ID: 25001-21-060, 25067-21-060, and 24054-20-060
Exposure Unit ID: Site Wide - Cumulative Hypothetical 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
Input Form 1A
VAPOR INTRUSION PATHWAYS
DIRECT CONTACT SOIL AND WATER PATHWAYS
Resident
Non-Residential Worker
Recreator/Trespasser
Resident
Non-Residential Worker
CONTAMINANT MIGRATION PATHWAYS
Groundwater
Surface Water
North Carolina DEQ Risk Calculator
Exposure Point ConcentrationsVersion Date: June 2021Basis: May 2021 EPA RSL TableSite ID: 25001-21-060, 25067-21-060, and 24054-20-060Exposure Unit ID: Site Wide - Cumulative Hypothetical Worst-Case NOTE: 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 calculationsExposure Point Concentration (mg/kg)Notes: CAS NumberChemicalFor the chemicals highlighted in blue, data entry notes are provided in the PSRG Table link on the Main MenuMinimum Concentration (Qualifier)Maximum Concentration (Qualifier)UnitsLocation of Maximum ConcentrationDetection FrequencyRange of Detection LimitsConcentration Used for ScreeningBackground ValueScreening Toxicity Value (Screening Level) (n/c)Potential ARAR/TBC ValuePotential ARAR/TBC SourceCOPC Flag (Y/N)Rationale for Selection or Deletion0.103 67-64-1Acetonemg/kg3.4 7440-38-2Arsenic, Inorganicmg/kg633 7440-39-3Bariummg/kg0.281 7440-43-9Cadmium (Diet)mg/kg111.7 16065-83-1Chromium(III), Insoluble Saltsmg/kg1.3 18540-29-9Chromium(VI)mg/kg56.3 7439-92-1~Lead and Compoundsmg/kg0.091 7487-94-7~Mercuric Chloride (and other Mercury salts)mg/kg0.002 78-93-3Methyl Ethyl Ketone (2-Butanone)mg/kg0.019 1634-04-4Methyl tert-Butyl Ether (MTBE)mg/kg0.059 56-55-3~Benz[a]anthracenemg/kg0.087 50-32-8~Benzo[a]pyrenemg/kg0.184 205-99-2~Benzo[b]fluoranthenemg/kg0.306 206-44-0~Fluoranthenemg/kg0.045 193-39-5~Indeno[1,2,3-cd]pyrenemg/kg0.028 91-57-6~Methylnaphthalene, 2-mg/kg0.0237 91-20-3~Naphthalenemg/kg0.303 129-00-0~Pyrenemg/kg5.48 7782-49-2Seleniummg/kg0.0705 7440-22-4Silvermg/kg0.036 108-88-3Toluenemg/kg0.0091 87-61-6Trichlorobenzene, 1,2,3-mg/kg0.0082 95-63-6Trimethylbenzene, 1,2,4-mg/kg0.0286 1330-20-7 Xylenesmg/kgInput Form 2ASoil Exposure Point Concentration TableDescription of Exposure Point Concentration Selection:North Carolina DEQ Risk Calculator
Risk for Individual Pathways Output Form 1A
Version Date: June 2021
Basis: May 2021 EPA RSL Table
Site ID: 25001-21-060, 25067-21-060, and 24054-20-060
Exposure Unit ID: Site Wide - Cumulative Hypothetical Worst-Case
Receptor Pathway
Carcinogenic
Risk Hazard Index Risk exceeded?
Soil 1.0E-05 1.7E-01 NO
Groundwater Use* NC NC NC
Soil 1.4E-06 1.2E-02 NO
Groundwater Use* NC NC NC
Construction Worker Soil 5.6E-07 1.4E-01 NO
Soil 5.7E-06 9.6E-02 NO
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 NC NC NC
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
DIRECT CONTACT SOIL AND WATER CALCULATORS
Resident
Non-Residential Worker
Recreator/Trespasser
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:
North Carolina DEQ Risk Calculator
DEQ Risk Calculator - Direct Contact - Resident Soil
Version Date: June 2021
Basis: May 2021 EPA RSL Table
Site ID: 25001-21-060, 25067-21-060, and 24054-20-060
Exposure Unit ID: Site Wide - Cumulative Hypothetical Worst-Case
* - Note that inhalation on this calculator refers to outdoor inhalation of volatiles and particulates, not indoor inhalation associated with vapor intrusion.
CAS # Chemical Name:
Ingestion
Concentration
(mg/kg)
Dermal
Concentration
(mg/kg)
Inhalation
Concentration
(mg/kg)*
Ingestion
Carcinogenic
Risk
Dermal
Carcinogenic
Risk
Inhalation
Carcinogenic
Risk*
Calculated
Carcinogenic
Risk
Ingestion
Hazard
Quotient
Dermal
Hazard
Quotient
Inhalation
Hazard
Quotient*
Calculated Non-
Carcinogenic
Hazard
Quotient
67-64-1 Acetone 0.103 0.103 0.103 1.5E-06 2.2E-07 1.7E-06
7440-38-2 Arsenic, Inorganic 3.4 3.4 3.4 4.4E-06 6.2E-07 8.8E-11 5.0E-06 8.7E-02 1.0E-02 3.7E-06 9.7E-02
7440-39-3 Barium 633 633 633 4.0E-02 2.0E-05 4.0E-02
7440-43-9 Cadmium (Diet) 0.281 0.281 0.281 3.0E-12 3.0E-12 3.6E-03 3.4E-04 4.5E-07 3.9E-03
16065-83-1 Chromium(III), Insoluble Salts 111.7 111.7 111.7 9.5E-04 9.5E-04
18540-29-9 Chromium(VI) 1.3 1.3 1.3 4.2E-06 1.8E-09 4.2E-06 5.5E-03 2.1E-07 5.5E-03
7439-92-1 ~Lead and Compounds 56.3 56.3 56.3 <SL** <SL** <SL**
7487-94-7 ~Mercuric Chloride (and other Mercury salts) 0.091 0.091 0.091 3.9E-03 4.9E-09 3.9E-03
78-93-3 Methyl Ethyl Ketone (2-Butanone) 0.002 0.002 0.002 4.3E-08 3.0E-08 7.2E-08
1634-04-4 Methyl tert-Butyl Ether (MTBE) 0.019 0.019 0.019 4.9E-11 3.4E-10 3.9E-10 1.2E-06 1.2E-06
56-55-3 ~Benz[a]anthracene 0.059 0.059 0.059 3.9E-08 1.3E-08 7.4E-10 5.2E-08
50-32-8 ~Benzo[a]pyrene 0.087 0.087 0.087 5.7E-07 1.9E-07 8.7E-13 7.6E-07 3.7E-03 1.1E-03 7.0E-07 4.9E-03
205-99-2 ~Benzo[b]fluoranthene 0.184 0.184 0.184 1.2E-07 4.0E-08 1.8E-13 1.6E-07
206-44-0 ~Fluoranthene 0.306 0.306 0.306 9.8E-05 3.0E-05 1.3E-04
193-39-5 ~Indeno[1,2,3-cd]pyrene 0.045 0.045 0.045 2.9E-08 9.8E-09 4.5E-14 3.9E-08
91-57-6 ~Methylnaphthalene, 2- 0.028 0.028 0.028 8.9E-05 2.8E-05 1.2E-04
91-20-3 ~Naphthalene 0.0237 0.0237 0.0237 4.1E-09 1.5E-09 5.8E-09 1.1E-08 1.5E-05 4.7E-06 1.5E-04 1.7E-04
129-00-0 ~Pyrene 0.303 0.303 0.303 1.3E-04 4.0E-05 1.7E-04
7782-49-2 Selenium 5.48 5.48 5.48 1.4E-02 4.4E-09 1.4E-02
7440-22-4 Silver 0.0705 0.0705 0.0705 1.8E-04 1.8E-04
108-88-3 Toluene 0.036 0.036 0.036 5.8E-06 1.5E-06 7.3E-06
87-61-6 Trichlorobenzene, 1,2,3- 0.0091 0.0091 0.0091 1.5E-04 1.5E-04
95-63-6 Trimethylbenzene, 1,2,4- 0.0082 0.0082 0.0082 1.0E-05 1.6E-05 2.6E-05
1330-20-7 Xylenes 0.0286 0.0286 0.0286 1.8E-06 4.5E-05 4.7E-05
Cumulative: 1.0E-05 1.7E-01
Output Form 2A
** - Note that the EPA has no consensus on reference dose or cancer slope factor values for lead, therefore it is not possible to calculate cancer risk or hazard quotient. Lead concentrations are compared to the EPA screening level
of 400 mg/kg for residential soil.
North Carolina DEQ Risk Calculator
DEQ Risk Calculator - Direct Contact - Non-Residential Worker Soil
Version Date: June 2021
Basis: May 2021 EPA RSL Table
Site ID: 25001-21-060, 25067-21-060, and 24054-20-060
Exposure Unit ID: Site Wide - Cumulative Hypothetical Worst-Case
* - Note that inhalation on this calculator refers to outdoor inhalation of volatiles and particulates, not indoor inhalation associated with vapor intrusion.
CAS # Chemical Name:
Ingestion
Concentration
(mg/kg)
Dermal
Concentration
(mg/kg)
Inhalation
Concentration
(mg/kg)*
Ingestion
Carcinogenic
Risk
Dermal
Carcinogenic
Risk
Inhalation
Carcinogenic
Risk
Calculated
Carcinogenic
Risk
Ingestion
Hazard
Quotient
Dermal
Hazard
Quotient
Inhalation
Hazard
Quotient
Calculated
Non-
Carcinogenic
Hazard
Quotient
67-64-1 Acetone 0.103 0.103 0.103 9.8E-08 5.2E-08 1.5E-07
7440-38-2 Arsenic, Inorganic 3.4 3.4 3.4 9.4E-07 2.0E-07 2.0E-11 1.1E-06 5.8E-03 1.2E-03 8.7E-07 7.1E-03
7440-39-3 Barium 633 633 633 2.7E-03 4.9E-06 2.7E-03
7440-43-9 Cadmium (Diet) 0.281 0.281 0.281 7.0E-13 7.0E-13 2.4E-04 4.1E-05 1.1E-07 2.8E-04
16065-83-1 Chromium(III), Insoluble Salts 111.7 111.7 111.7 6.4E-05 6.4E-05
18540-29-9 Chromium(VI) 1.3 1.3 1.3 2.0E-07 1.5E-10 2.0E-07 3.7E-04 5.0E-08 3.7E-04
7439-92-1 ~Lead and Compounds 56.3 56.3 56.3 <SL** <SL** <SL**
7487-94-7 ~Mercuric Chloride (and other Mercury salts) 0.091 0.091 0.091 2.6E-04 1.2E-09 2.6E-04
78-93-3 Methyl Ethyl Ketone (2-Butanone) 0.002 0.002 0.002 2.9E-09 7.0E-09 9.9E-09
1634-04-4 Methyl tert-Butyl Ether (MTBE) 0.019 0.019 0.019 1.0E-11 7.7E-11 8.8E-11 2.8E-07 2.8E-07
56-55-3 ~Benz[a]anthracene 0.059 0.059 0.059 1.8E-09 9.9E-10 6.2E-11 2.9E-09
50-32-8 ~Benzo[a]pyrene 0.087 0.087 0.087 2.7E-08 1.5E-08 7.2E-14 4.1E-08 2.5E-04 1.4E-04 1.7E-07 3.9E-04
205-99-2 ~Benzo[b]fluoranthene 0.184 0.184 0.184 5.6E-09 3.1E-09 1.5E-14 8.7E-09
206-44-0 ~Fluoranthene 0.306 0.306 0.306 6.5E-06 3.6E-06 1.0E-05
193-39-5 ~Indeno[1,2,3-cd]pyrene 0.045 0.045 0.045 1.4E-09 7.6E-10 3.7E-15 2.1E-09
91-57-6 ~Methylnaphthalene, 2- 0.028 0.028 0.028 6.0E-06 3.3E-06 9.3E-06
91-20-3 ~Naphthalene 0.0237 0.0237 0.0237 8.7E-10 4.8E-10 1.3E-09 2.7E-09 1.0E-06 5.6E-07 3.7E-05 3.8E-05
129-00-0 ~Pyrene 0.303 0.303 0.303 8.6E-06 4.8E-06 1.3E-05
7782-49-2 Selenium 5.48 5.48 5.48 9.4E-04 1.1E-09 9.4E-047440-22-4 Silver 0.0705 0.0705 0.0705 1.2E-05 1.2E-05
108-88-3 Toluene 0.036 0.036 0.036 3.9E-07 3.6E-07 7.5E-07
87-61-6 Trichlorobenzene, 1,2,3- 0.0091 0.0091 0.0091 9.7E-06 9.7E-06
95-63-6 Trimethylbenzene, 1,2,4- 0.0082 0.0082 0.0082 7.0E-07 3.7E-06 4.4E-06
1330-20-7 Xylenes 0.0286 0.0286 0.0286 1.2E-07 1.1E-05 1.1E-05
Cumulative: 1.4E-06 1.2E-02
Output Form 2C
** - Note that the EPA has no consensus on reference dose or cancer slope factor values for lead, therefore it is not possible to calculate cancer risk or hazard quotient. Lead concentrations are compared to the EPA screening level of 800
mg/kg for commercial/industrial soil.
North Carolina DEQ Risk Calculator
DEQ Risk Calculator - Direct Contact - Construction Worker Soil
Version Date: June 2021
Basis: May 2021 EPA RSL Table
Site ID: 25001-21-060, 25067-21-060, and 24054-20-060
Exposure Unit ID: Site Wide - Cumulative Hypothetical Worst-Case
* - Note that inhalation on this calculator refers to outdoor inhalation of volatiles and particulates, not indoor inhalation associated with vapor intrusion.
CAS # Chemical Name:
Ingestion Concentration
(mg/kg)
Dermal Concentration
(mg/kg)
Inhalation Concentration
(mg/kg)*
Ingestion Carcinogenic
Risk
Dermal Carcinogenic
Risk
Inhalation Carcinogenic
Risk
Calculated Carcinogenic
Risk
Ingestion Hazard
Quotient
Dermal Hazard
Quotient
Inhalation Hazard
Quotient
Calculated
Non-Carcinogenic
Hazard
Quotient
67-64-1 Acetone 0.103 0.103 0.103 1.5E-07 2.6E-07 4.1E-07
7440-38-2 Arsenic, Inorganic 3.4 3.4 3.4 1.2E-07 2.0E-08 4.5E-08 1.9E-07 2.0E-02 3.2E-03 5.1E-02 7.4E-02
7440-39-3 Barium 633 633 633 9.3E-03 2.8E-02 3.8E-02
7440-43-9 Cadmium (Diet) 0.281 0.281 0.281 1.6E-09 1.6E-09 1.7E-03 2.1E-04 6.3E-03 8.2E-03
16065-83-1 Chromium(III), Insoluble Salts 111.7 111.7 111.7 2.2E-04 5.0E-03 5.2E-03
18540-29-9 Chromium(VI) 1.3 1.3 1.3 2.6E-08 3.4E-07 3.6E-07 7.7E-04 9.7E-04 1.7E-03
7439-92-1 ~Lead and Compounds 56.3 56.3 56.3 <SL** <SL** <SL**
7487-94-7 ~Mercuric Chloride (and other Mercury salts) 0.091 0.091 0.091 1.3E-04 6.8E-05 2.0E-04
78-93-3 Methyl Ethyl Ketone (2-Butanone) 0.002 0.002 0.002 2.9E-09 1.7E-07 1.8E-07
1634-04-4 Methyl tert-Butyl Ether (MTBE) 0.019 0.019 0.019 1.4E-12 1.5E-11 1.6E-11 1.9E-07 1.6E-06 1.8E-06
56-55-3 ~Benz[a]anthracene 0.059 0.059 0.059 2.4E-10 9.9E-11 2.3E-11 3.6E-10
50-32-8 ~Benzo[a]pyrene 0.087 0.087 0.087 3.5E-09 1.5E-09 1.6E-10 5.1E-09 8.5E-04 3.6E-04 9.8E-03 1.1E-02
205-99-2 ~Benzo[b]fluoranthene 0.184 0.184 0.184 7.4E-10 3.1E-10 3.4E-11 1.1E-09
206-44-0 ~Fluoranthene 0.306 0.306 0.306 9.0E-06 3.8E-06 1.3E-05
193-39-5 ~Indeno[1,2,3-cd]pyrene 0.045 0.045 0.045 1.8E-10 7.6E-11 8.3E-12 2.7E-10
91-57-6 ~Methylnaphthalene, 2- 0.028 0.028 0.028 2.1E-05 8.6E-06 2.9E-05
91-20-3 ~Naphthalene 0.0237 0.0237 0.0237 1.1E-10 4.8E-11 2.5E-10 4.2E-10 1.2E-07 4.9E-08 1.8E-04 1.8E-04
129-00-0 ~Pyrene 0.303 0.303 0.303 3.0E-06 1.2E-06 4.2E-06
7782-49-2 Selenium 5.48 5.48 5.48 3.2E-03 6.2E-05 3.3E-03
7440-22-4 Silver 0.0705 0.0705 0.0705 4.2E-05 4.2E-05
108-88-3 Toluene 0.036 0.036 0.036 1.3E-07 1.8E-06 1.9E-06
87-61-6 Trichlorobenzene, 1,2,3- 0.0091 0.0091 0.0091 3.4E-06 3.4E-06
95-63-6 Trimethylbenzene, 1,2,4- 0.0082 0.0082 0.0082 6.0E-07 5.5E-06 6.1E-06
1330-20-7 Xylenes 0.0286 0.0286 0.0286 2.1E-07 1.3E-05 1.3E-05
Cumulative: 5.6E-07 1.4E-01
Output Form 2E
** - Note that the EPA has no consensus on reference dose or cancer slope factor values for lead, therefore it is not possible to calculate cancer risk or hazard quotient. Lead concentrations are compared to the EPA screening level of 800 mg/kg
for commercial/industrial soil.
North Carolina DEQ Risk Calculator
DEQ Risk Calculator - Direct Contact - Recreator/Trespasser Soil Output Form 2F
Version Date: June 2021
Basis: May 2021 EPA RSL Table
Site ID: 25001-21-060, 25067-21-060, and 24054-20-060
Exposure Unit ID: Site Wide - Cumulative Hypothetical Worst-Case
* - Note that inhalation on this calculator refers to outdoor inhalation of volatiles and particulates, not indoor inhalation associated with vapor intrusion.
Receptor Type:
CAS # Chemical Name:
Ingestion Concentration
(mg/kg)
Dermal Concentration
(mg/kg)
Inhalation Concentration
(mg/kg)*
Ingestion Carcinogenic
Risk
Dermal Carcinogenic
Risk
Inhalation Carcinogenic
Risk
Calculated Carcinogenic
Risk
Ingestion Hazard
Quotient
Dermal Hazard
Quotient
Inhalation Hazard
Quotient
Calculated
Non-Carcinogenic
Hazard
Quotient
67-64-1 Acetone 0.103 0.103 0.103 8.2E-07 1.0E-08 8.3E-07
7440-38-2 Arsenic, Inorganic 3.4 3.4 3.4 2.5E-06 3.4E-07 4.1E-12 2.8E-06 4.8E-02 5.7E-03 1.7E-07 5.4E-02
7440-39-3 Barium 633 633 633 2.3E-02 9.5E-07 2.3E-02
7440-43-9 Cadmium (Diet) 0.281 0.281 0.281 1.4E-13 1.4E-13 2.0E-03 1.9E-04 2.1E-08 2.2E-03
16065-83-1 Chromium(III), Insoluble Salts 111.7 111.7 111.7 5.3E-04 5.3E-04
18540-29-9 Chromium(VI) 1.3 1.3 1.3 2.4E-06 8.4E-11 2.4E-06 3.1E-03 9.8E-09 3.1E-03
7439-92-1 ~Lead and Compounds 56.3 56.3 56.3 <SL** <SL** <SL**
7487-94-7 ~Mercuric Chloride (and other Mercury salts) 0.091 0.091 0.091 2.2E-03 2.3E-10 2.2E-03
78-93-3 Methyl Ethyl Ketone (2-Butanone) 0.002 0.002 0.002 2.4E-08 1.4E-09 2.5E-08
1634-04-4 Methyl tert-Butyl Ether (MTBE) 0.019 0.019 0.019 2.7E-11 1.6E-11 4.3E-11 5.4E-08 5.4E-08
56-55-3 ~Benz[a]anthracene 0.059 0.059 0.059 2.1E-08 7.2E-09 3.5E-11 2.9E-08
50-32-8 ~Benzo[a]pyrene 0.087 0.087 0.087 3.2E-07 1.1E-07 4.0E-14 4.2E-07 2.1E-03 6.4E-04 3.3E-08 2.7E-03
205-99-2 ~Benzo[b]fluoranthene 0.184 0.184 0.184 6.7E-08 2.2E-08 8.5E-15 8.9E-08
206-44-0 ~Fluoranthene 0.306 0.306 0.306 5.4E-05 1.7E-05 7.1E-05
193-39-5 ~Indeno[1,2,3-cd]pyrene 0.045 0.045 0.045 1.6E-08 5.5E-09 2.1E-15 2.2E-08
91-57-6 ~Methylnaphthalene, 2- 0.028 0.028 0.028 5.0E-05 1.5E-05 6.5E-05
91-20-3 ~Naphthalene 0.0237 0.0237 0.0237 2.3E-09 8.3E-10 2.7E-10 3.4E-09 8.4E-06 2.6E-06 7.1E-06 1.8E-05
129-00-0 ~Pyrene 0.303 0.303 0.303 7.2E-05 2.2E-05 9.4E-05
7782-49-2 Selenium 5.48 5.48 5.48 7.8E-03 2.1E-10 7.8E-03
7440-22-4 Silver 0.0705 0.0705 0.0705 1.0E-04 1.0E-04
108-88-3 Toluene 0.036 0.036 0.036 3.2E-06 7.0E-08 3.3E-06
87-61-6 Trichlorobenzene, 1,2,3- 0.0091 0.0091 0.0091 8.1E-05 8.1E-05
95-63-6 Trimethylbenzene, 1,2,4- 0.0082 0.0082 0.0082 5.8E-06 7.2E-07 6.6E-06
1330-20-7 Xylenes 0.0286 0.0286 0.0286 1.0E-06 2.1E-06 3.1E-06
Cumulative: 5.7E-06 9.6E-02
** - Note that the EPA has no consensus on reference dose or cancer slope factor values for lead, therefore it is not possible to calculate cancer risk or hazard quotient. Lead concentrations are compared to the EPA screening level of 400
mg/kg for residential soil.
North Carolina DEQ Risk Calculator
From:Chris Hustek
To:Cody Cannon
Cc:Michael Innominato
Subject:RE: Brownfields Soil Transfer - DynaTech to AJACC Auto (ELAN LoSo)
Date:Monday, December 27, 2021 9:41:12 PM
Attachments:image002.png
Cody,
Yes, please go ahead and see if you can get the dirt/source below approved for the LOSO project. Let
Mike and I know what you need if anything. Mike I is the main contact but please keep me CC’d.

Any questions or Concerns please let me know.

Thank you!

Chris Hustek | Senior Project Manager, Construction
Greystar 521 E Morehead | St #400 | Charlotte, NC 28202
M [phone] | [e-mail]

Overture Cary | Site Address
1055 Hatches Pond Lane
Cary, NC 27560

Elan Indian Trail | Site Address
13700 Independence BLVD or 100 Chestnut Parkway
Indian Trail, NC 28079

From: Cody Cannon <[e-mail]>
Sent: Monday, December 27, 2021 1:03 PM
To: Chris Hustek <[e-mail]>
Subject: [EXTERNAL] FW: Brownfields Soil Transfer - DynaTech to AJACC Auto (ELAN LoSo)

From: Cody Cannon
Sent: Tuesday, December 21, 2021 10:39 AM
To: [e-mail]
Cc: Kirill Vladimirovich <[e-mail]>
Subject: Brownfields Soil Transfer - DynaTech to AJACC Auto (ELAN LoSo)

Good Morning Chris,

Thanks for taking time to discuss the opportunity for a Brownfields-to-Brownfields soil transfer
opportunity for your development at the AJACC Auto (24054-20-060) Brownfields property. The
prospective developer (PD) for the DynaTech II, III, and IV (25001-21-060, 25067-21-060, and 25068-
21-060) Brownfields properties located near the corner of Toomey Avenue and W. Tremont Avenue
in Charlotte, is seeking to get rid of approximately 22,000 cubic yards (CY) of soils from upcoming
excavation areas.

Per the NCDEQ-approved Environmental Management Plan (Link) for the DynaTech properties,
several areas (FCC-2B, FCC-3, FCC-4, FCC-5, FCC-8B, and FCC-9) have been identified as favorable for
transfer to another Brownfields property provided written approval by NCDEQ Brownfields of a soil
transfer request. We are estimating between 10,000 – 15,000 CY of soils will be generated from
these areas, but we will have more precise numbers soon as we progress through the approval
process.

Please reply to this email to confirm your interest in receiving these materials provided they meet
your requirements and a transfer request is approved by the NCDEQ Brownfields Program.

Best,