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HomeMy WebLinkAbout20527_Pharr Yarns-Lowell EMP_20240417#C-1269 Engineering #C-245 Geology Environmental Management Plan Pharr Yarns – Lowell 700 West 1st Street Lowell, North Carolina Brownfields Project No. 25027-21-036 April 17, 2024 H&H Job No. HNY-001 Environmental Management Plan Pharr Yarns – Lowell 700 West 1st Street Lowell, North Carolina Brownfields Project No. 25027-21-036 H&H Job No. HNY-001 CONTENTS Completed EMP Template Form Tables Table 1 Summary of Soil Analytical Data Table 2 Summary of Well Construction and Depth to Groundwater Data Table 3 Summary of Groundwater Analytical Data Table 4 Summary of Exterior Soil Gas Analytical Data Figures Figure 1 Site Location Map Figure 2 Site Map Figure 3 Sample Location Map Figure 4 Soil Impacts Above PSRGs Figure 5 Groundwater Impacts Above PSRGs Figure 6 Summary of Vapor Intrusion Risk Appendices Appendix A Redevelopment Plan Appendix B Cut/Fill Analysis     1  EMP Version 3, March 2023   NORTH CAROLINA BROWNFIELDS REDEVELOPMENT SECTION   ENVIRONMENTAL MANAGEMENT PLAN    This form is to be used to prepare an Environmental Management Plan (EMP) for projects in  the North Carolina Brownfields Redevelopment Section at the direction of a Brownfields  project manager.    The EMP is a standard requirement of a Brownfields Agreement (BFA).  Its purpose is to clarify  actions to be taken during demolition and construction at Brownfields properties in an effort  to avoid delays in the event of the discovery of new contamination sources or other  environmental conditions.  The EMP provides a means to document redevelopment plans and  environmental data for each applicable environmental medium to inform regulatory‐compliant  decision‐making at the site.  As much detail as possible should be included in the EMP,  including contingency planning for unknowns.  Consult your project manager if you have  questions.    Prospective Developers and/or their consultants must complete and submit this form and all  pertinent attachments, see checklist below, to their Brownfields project manager prior to any  earthmoving or other development‐related activities that have the potential to disturb soil at  the Brownfields Property, including demolition.  For the EMP to be valid for use, it must be  completed, reviewed by the Section, signed by all parties working on the project, and  approved by the Brownfields project manager.  Failure to comply with the requirements of the  EMP could jeopardize project eligibility, or in the event of a recorded agreement, be cause for  a reopener.      The EMP is valid only for the scope of work described herein and must be updated to be  applicable for new phases of redevelopment or after significant changes in applicable  regulatory guidance.  Risk characterization of a Brownfields Property to DEQ’s written  satisfaction is required prior to EMP approval.    Voluntary Metrics Tab  The NC Brownfields Redevelopment Section updates estimated capital investment (from the Brownfields Property Application) and estimated jobs created (from the Brownfields Agreement) whenever possible. As a voluntary measure, you may opt to complete the below information for capital investment and jobs created as estimated by your final redevelopment plans for the Brownfields Property: 1. Estimated capital investment in redevelopment project: 2. Estimated jobs created: a. Construction Jobs: b. Full Time Post-Redevelopment Jobs:         2  EMP Version 3, March 2023   Table of Contents NORTH CAROLINA BROWNFIELDS REDEVELOPMENT SECTION .................................................................. 1  ENVIRONMENTAL MANAGEMENT PLAN .................................................................................................... 1  GENERAL INFORMATION ........................................................................................................................ 4  COMMUNICATIONS ................................................................................................................................ 4  NOTIFICATIONS TO THE BROWNFIELDS REDEVELOPMENT SECTION ..................................................... 5  REDEVELOPMENT PLANS ........................................................................................................................ 5  CONTAMINATED MEDIA ......................................................................................................................... 7  PART 1. SOIL ........................................................................................................................................ 8  PART 2. GROUNDWATER .................................................................................................................. 19  PART 3. SURFACE WATER .................................................................................................................. 21  PART 4. SEDIMENT ............................................................................................................................ 21  PART 5.  SOIL VAPOR ......................................................................................................................... 21  PART 6. INDOOR AIR ......................................................................................................................... 23  VAPOR INTRUSION MITIGATION SYSTEM ............................................................................................. 23  CONTINGENCY PLAN ............................................................................................................................. 24  POST‐REDEVELOPMENT REPORTING ..................................................................................................... 26  APPROVAL SIGNATURES ....................................................................................................................... 27            3  EMP Version 3, March 2023   So that the EMP provides value in protecting Brownfields eligibility and public health, the  preparer shall ensure that the following steps have been completed prior to submitting the  EMP for review.  Any EMP prepared without completing all of the following is premature and may  be returned without comment.      ☒ Site sampling and assessment that meets Brownfields’ objectives is complete and has  been reviewed and approved by the Brownfields project manager.  ☒ Specific redevelopment plans, even if conceptual, have been developed for the project,  submitted and reviewed by the Brownfields project manager.    Please submit, along with the completed EMP form, the following attachments, as relevant  and applicable to the proposed redevelopment:    ☒ A set of redevelopment plans, including architectural/engineering plans, if available; if  not, conceptual plans may suffice if updated when detailed plans are drafted.    ☐ A figure overlaying redevelopment plans on a map of the extent of contamination for  each media.    ☒ Site grading plans that include a cut and fill analysis.    ☐ A figure showing the proposed location and depth of impacted soil that would remain  onsite after construction grading.    ☐ Any necessary permits for redevelopment (i.e., demolition, etc.).    ☒ A detailed construction schedule that includes timing and phases of construction.    ☒ Tabulated data summaries for each impacted media (i.e., soil, groundwater, soil gas,  etc.) applicable to the proposed redevelopment.    ☒ Figures with the sampling locations and contamination extents for each impacted media  applicable to the proposed redevelopment.    ☐ A full final grade sampling and analysis plan, if the redevelopment plan is final.    ☐ If known, information about each proposed potential borrow soil source, such as aerial  photos, historic site maps, historic Sanborn maps, a site history, necessary for  Brownfields approval.    ☐ Information and, analytical data if required, for quarries, or other borrow sources,  detailing the type of material proposed for import to the Brownfields Property.      4  EMP Version 3, March 2023   ☐ A work plan for the sampling and analysis of soil to be brought onto the Brownfields  Property.  Refer to Issue Resolution 15 in Brownfields Redevelopment Section  Guidelines.    ☐ A map of the Brownfields Property showing the location of soils proposed for export  and sampling data from those areas.    ☐ If a Vapor Intrusion Mitigation System (VIMS) is required by the Brownfields  Redevelopment Section, the VIMS plan will be signed and sealed by a NC Professional  Engineer.  The VIMS Plan may also be submitted under separate cover.    GENERAL INFORMATION      Date: 4/17/2024 Revision Date (if applicable):     Brownfields Assigned Project Name: Pharr Yarns – Lowell    Brownfields Project Number: 25027‐21‐036    Brownfields Property Address: 700 West 1st Street, Lowell, Gaston County, North Carolina (see Figures  1 and 2)    Brownfields Property Area (acres): 17.45 acres  Is Brownfields Property Subject to RCRA Permit?.......................☐ Yes   ☒ No  If yes enter Permit No.:   Is Brownfields Property Subject to a Solid Waste Permit….……..☐ Yes   ☒ No  If yes, enter Permit No.:       COMMUNICATIONS    A copy of this EMP shall be distributed to all the parties below as well as any contractors or site workers  that may be exposed to site vapors, soil, groundwater, and/or surface water.  Additionally, a copy of the  EMP shall be maintained at the Brownfields Property during redevelopment activities in an area that is  prominently accessible to site workers.  NOTE, THE EMP DOES NOT TAKE THE PLACE OF A SITE‐SPECIFIC  HEALTH AND SAFETY PLAN.    Prospective Developer (PD): Lowell OZB, LLC    Contact Person: Rob Pressley   Phone Numbers:   Office: 704‐971‐9000 Mobile: 704‐904‐4053   Email: rob.pressley@cbcmeca.com            5  EMP Version 3, March 2023   Contractor for PD:  Edison Foard Construction  Contact Person: Edison Cassels  Phone Numbers:   Office: 704‐329‐8000 Mobile: 704‐622‐6787   Email: ecassels@edisonfoard.com     Environmental Consultant: Hart & Hickman, PC     Contact Person: Bo Cappleman, PG  Phone Numbers:   Office: 704‐586‐0007 Mobile: 980‐200‐7911    Email: bcappleman@harthickman.com     Brownfields Redevelopment Section Project Manager:  Bill Schmithorst  Phone Numbers:   Office: 919‐707‐8159 Mobile: 919‐441‐3606    Email: william.schmithorst@deq.nc.gov; BFPropertyManagement@deq.nc.gov      Other DEQ Program Contacts (if applicable, i.e., UST Section, Inactive Hazardous Site Branch,  Hazardous Waste, Solid Waste):   Not applicable    NOTIFICATIONS TO THE BROWNFIELDS REDEVELOPMENT SECTION    Written advance Notification Times to Brownfields project manager: Check each box to accept  minimum advance notice periods (in calendar days) for each type of onsite task:    On‐site assessment or remedial activities:……………………………………….…… 10 days Prior        ☒    Construction or grading start:……………………………………….………………………. 10 days Prior       ☒    Discovery of stained soil, odors, USTs, buried drums or waste, landfill, or other signs of previously  unknown contamination: ……………………………….……………………………………. Within 48 hours   ☒   Implementation of emergency actions (e.g. dewatering, flood or soil erosion control measures in  area of contamination, ventilation of work zones):…………….……….……… Within 48 hours  ☒    Installation of mitigation systems:………………………….………………….……….. 10 days Prior         ☒   Other notifications as required by local, state or federal agencies to implement redevelopment  activities: (as applicable): ……………………….…………………………………………..… Within 30 days     ☒  REDEVELOPMENT PLANS    1) Type of Redevelopment (check all that apply):  ☐Residential ☐Townhomes (Prior written DEQ approval REQUIRED regardless of ownership  structure) ☐Recreational ☐Institutional  ☒Commercial  ☒Office  ☐Retail  ☒Industrial      6  EMP Version 3, March 2023   ☒Other specify:  Parking    2) Check the following activities that will be conducted prior to commencing earth‐moving activities  at the site:  ☒ Review of historic maps (Sanborn Maps, facility maps)  ☒ Conducting geophysical surveys to evaluate the location of suspect UST, fuel lines, utility  lines, etc.  ☐ Interviews with employees/former employees/facility managers/neighbors    3) Summary of Redevelopment Plans (MANDATORY: attach detailed plans or conceptual plans, if  detailed plans are not available. EMP review without such information would be premature):   Provide brief summary of redevelopment plans, including demolition, removal of building  slabs/pavement, grading plans and planned construction of new structures:   Planned redevelopment at the Brownfields property includes construction of an industrial park  with three office and warehouse buildings on the north side of the Brownfields property and two  multi‐tenant commercial/industrial flex buildings on the south side.  A Site Redevelopment Plan  is included as Appendix A.      4) Do plans include demolition of structure(s)?:      ☒ Yes  ☐ No ☐ Unknown   ☒ If yes, please check here to confirm that demolition will be conducted in accordance with  applicable legal requirements, including without limitation those related to lead and asbestos  abatement that are administered by the Health Hazards Control Unit within the Division of Public  Health of the North Carolina Department of Health and Human Services.  If available, please  provide a copy of your demolition permit.     5) Are sediment and erosion control measures required by federal, state, or local regulations?   S&EC requirements can be found at: https://deq.nc.gov/about/divisions/energy‐mineral‐and‐land‐ resources/erosion‐and‐sediment‐control/erosion‐and‐sediment‐control‐laws‐and‐rules    ☒ Yes    ☐ No    ☐ Unknown   ☒  If yes, please check here to confirm that earth‐work will be conducted in accordance with  applicable legal requirements.  If soil disturbance is necessary to install sediment and erosion  control measures, they may not begin until this EMP is approved.     6) Which category of risk‐based screening level is used or is anticipated to be specified in the  Brownfields Agreement?  Note: If children frequent the property, residential screening levels shall  be cited in the Brownfields Agreement for comparison purposes.  ☐ Residential   ☒ Non‐Residential or Industrial/Commercial    7) Schedule for Redevelopment (attach construction schedule):  a) Construction start date: 6/1/2024     b) Anticipated duration (specify activities during each phase):       7  EMP Version 3, March 2023   The estimated schedule for primary construction tasks is provided below.    Northern Portion of Brownfields Property  Clearing/Grading:  June to August 2024  Subgrade Utility Installation: June to July 2024  Foundations: August to October 2024  Vertical Construction: November 2024 to April 2025  Paving/Landscaping: April 2025    Southern Portion of Brownfields Property  Clearing/Grading:  June to August 2024  Subgrade Utility Installation: Q4 2025  Foundations: Q1 2026  Vertical Construction: Q1 to Q4 2026  Paving/Landscaping: Q4 2026    c) Additional phases planned? ☐ Yes  ☒ No          If yes, specify the start date and/or activities if known:   Start Date:       Planned Activity:    Start Date:       Planned Activity:          Start Date:      Planned Activity:    a) Provide the planned date of occupancy for new buildings: 4/1/2025                       CONTAMINATED MEDIA  Please fill out the sections below, using detailed site plans, if available, or estimate using known areas  of contaminated soil and a conceptual redevelopment plan.  Provide a figure overlaying new  construction onto figure showing contaminated soil and groundwater locations.    1) Contaminated Media on the Brownfields Property  Part 1. Soil:        ☒  Yes   ☐ No   ☐ Suspected  ☐ Unknown  Part 2. Groundwater: .................................... ☒  Yes   ☐ No   ☐ Suspected  ☐ Unknown  Part 3. Surface Water:     ☐  Yes   ☒ No   ☐ Suspected  ☐ Unknown  ☒ N/A      8  EMP Version 3, March 2023   Part 4. Sediment: .......................................... ☐  Yes   ☒ No   ☐ Suspected  ☐ Unknown  ☒ N/A  Part 5. Soil Vapor: ......................................... ☒  Yes   ☐ No   ☐ Suspected  ☐ Unknown  Part 6. Sub‐Slab Soil Vapor: .......................... ☐  Yes   ☐ No   ☐ Suspected  ☒ Unknown  Part 7. Indoor Air: ......................................... ☐  Yes   ☐ No   ☐ Suspected  ☒ Unknown    2) For the Area of Proposed Redevelopment on the Brownfields Property, attach tabulated data  summaries for each impacted media and figure(s) with sample locations.   PART 1. SOIL  1) Known or suspected contaminants in soil (list general groups of contaminants):  A tabular summary of soil analytical data in comparison to the July 2023 North Carolina  Department of Environmental Quality (DEQ) Residential and Industrial/Commercial Preliminary  Soil Remediation Goals (PSRGs) is included as Table 1.  Soil sample locations are shown on  Figures 2 and 3A.  A brief summary of the results is provided below.      Volatile Organic Compounds (VOCs) and Semi‐Volatile Organic Compounds (SVOCs)  Volatile organic compounds (VOCs) have not been detected in soil samples at concentrations  above Residential or Industrial/Commercial PSRGs.  TCE was not detected above the laboratory  method detection limits (MDLs) in any soil samples collected from the site.    The polynuclear aromatic hydrocarbons (PAHs) benzo(a)anthracene (up to 12.3 milligrams per  kilogram [mg/kg]), benzo(a)pyrene (up to 9.14 mg/kg), benzo(b)fluoranthene (up to 13.2 mg/kg),  dibenz(a,h)anthracene (up to 2.27 mg/kg), and/or indeno(1,2,3‐cd)pyrene (5.63 mg/kg) were  detected in composite soil samples CS‐1, CS‐2 and its duplicate (SB‐DUP), and CS‐7 at  concentrations above the Residential PSRGs of 1.1 mg/kg, 0.11 mg/kg, 1.1 mg/kg, 0.11 mg/kg,  and 1.1 mg/kg, respectively.  The detected concentrations of benzo(a)pyrene and  dibenz(a,h)anthracene in soil sample CS‐1 also exceed the Industrial/Commercial PSRGs of 2.1  mg/kg and 2.1 mg/kg, respectively.  No other SVOCs have been detected above Residential or  Industrial/Commercial PSRGs in soil samples collected at the site.      Metals  Hexavalent chromium was detected in soil samples CS‐1 through CS‐7 collected in areas of  proposed buildings at concentrations exceeding the Residential PSRG of 0.31 mg/kg but below  the Industrial/Commercial PSRG of 6.5 mg/kg.  The detected hexavalent chromium  concentrations are generally consistent with site‐specific background concentrations and  concentrations detected at numerous properties across North Carolina, including undeveloped  properties.  Arsenic was also detected above the Industrial/Commercial PSRGs in samples CS‐1  through CS‐7.  However, the arsenic detections are generally consistent with site‐specific  background concentrations and are within the range of published regional background levels.   The detected hexavalent chromium and arsenic concentrations are likely naturally occurring.    Polychlorinated Biphenyls (PCBs)      9  EMP Version 3, March 2023   No PCBs were detected at concentrations above the MDLs in sample SG‐3 (1‐3 ft), which was  collected at a former electrical substation in the central portion of the Brownfields property.    2) Depth of known or suspected contaminants (feet):  Soil impacts have been confirmed at depths of approximately 0‐2 feet below ground surface  (bgs).      3) Area of soil disturbed by redevelopment (square feet):  Based on the cut/fill plans provided in Appendix B, approximately 15 acres (653,400 square feet)  of the 17.45‐acre site is expected to be disturbed during grading and construction activities.   Areas excluded from disturbance include wooded land and portions of an electrical powerline  right‐of‐way in the northwestern portion of the site and portions of a railroad right‐of‐way in the  southern portion of the site.    4) Depths of soil to be excavated (feet):  Planned cut depths as part of mass grading are expected to range from approximately 0.5 to  10 ft below current grade elevations.  Additional excavation within a similar depth range is  anticipated at proposed utility trenches, building foundations, and stormwater/sediment basins.    5) Estimated volume of soil (cubic yards) to be excavated (attach grading plan):  Grading activities for the proposed redevelopment at the site will generate approximately  19,700 cubic yards of cut and approximately 23,870 cubic yards of fill to achieve proposed  final grade elevations.  To the extent possible, cut material will be reused as fill if the material  is structurally suitable.        6) Estimated volume of excavated soil (cubic yards) anticipated to be impacted by contaminants:              The volume of impacted soil to be excavated at the site is unknown.      7) Estimated volume of contaminated soil expected to be disposed of offsite, if applicable:    See answer to Part 1 Section 6 above.  Soil management (including potential off‐site disposal)  will be based on stockpile soil sample analytical data and risk evaluation by the Brownfields  Redevelopment Section if excess soil cannot be re‐used as fill material.        PART 1.A. MANAGING ONSITE SOIL  If soil is anticipated to be excavated from the Brownfield Property, relocated on the Brownfields  Property, or otherwise disturbed during site grading or other redevelopment activities, please  provide a grading plan that clearly illustrates areas of cut and fill (approximate areas & volumes are  acceptable, if only preliminary data available).      1) HAZARDOUS WASTE DETERMINATION:       10  EMP Version 3, March 2023   a) Does the soil contain a LISTED WASTE as defined in the North Carolina Hazardous  Waste Section under 40 CFR Part 261.31‐261.35?....................................... ☐Yes   ☒No  ☐ If yes, explain why below, including the level of knowledge regarding processes  generating the waste (include pertinent analytical results as needed).      ☐ If yes, do the soils exceed the “Contained‐Out” levels in Attachment 1 of the  North Carolina Contained‐In Policy?................................................. ☐ Yes   ☐ No      b) NOTE: IF SOIL MEETS THE DEFINITION OF A LISTED HAZARDOUS WASTE AND EXCEEDS  THE CONTAINED‐OUT LEVELS IN ATTACHMENT 1 TO THE NORTH CAROLINA  CONTAINED‐IN POLICY, THE SOIL MAY NOT BE RE‐USED ONSITE AND MUST BE  DISPOSED OF IN ACCORDANCE WITH DEQ HAZARDOUS WASTE SECTION RULES AND  REGULATIONS.      c)  Does the soil contain a CHARACTERISTIC WASTE?.................................... ☐ Yes   ☒ No  ☐ If yes, mark reason(s) why below (and include pertinent analytical results).  ☐ Ignitability                  ☐ Corrosivity Click or tap here to enter text.  ☐ Reactivity Click or tap here to enter text.  ☐ Toxicity Click or tap here to enter text.  ☐ TCLP results Click or tap here to enter text.  ☐ Rule of 20 results (20 times total analytical results for an individual  hazardous constituent on TCLP list cannot, by test method, exceed regulatory  TCLP standard)      ☒ If no, explain rationale:   Based on results of soil assessment activities and the “Rule of 20”, no  compounds have been identified at characteristically hazardous levels.    d) NOTE: IF SOIL MEETS THE DEFINITION OF A CHARACTERISTIC HAZARDOUS WASTE, THE  SOIL MAY NOT BE RE‐USED ONSITE AND MUST BE DISPOSED OF IN ACCORDANCE WITH  DEQ HAZARDOUS WASTE SECTION RULES AND REGULATIONS.    2) Screening criteria by which soil disposition decisions will be made (e.g., left in place, capped in  place with low permeability barrier, removed to onsite location and capped, removed offsite):        ☐ Preliminary Health‐Based Residential SRGs         ☒ Preliminary Health‐Based Industrial/Commercial SRGs              ☒ Division of Waste Management Risk Calculator (For Brownfields Properties Only)      ☐ Site‐specific risk‐based cleanup level. Please provide details of methods used for      11  EMP Version 3, March 2023   determination/explanation.       Additional comments:       3) If known impacted soil is proposed to be reused within the Brownfields Property boundary,  please check the measures that will be utilized to ensure safe placement and documentation of  same.   Please attach a proposed location diagram/site map.           ☒ Provide documentation of analytical report(s) to Brownfields project manager.  ☒ Provide documentation of final location, thickness and depth of relocated soil onsite map to  Brownfields project manager once known.  ☒ Geotextile to mark depth of fill material.   Provide description of material:   The use of a geotextile is not planned but will be considered.    ☒ Manage soil under impervious cap ☒  or clean fill ☒   ☒ Describe cap or fill:   Should potentially impacted soil or fill materials be encountered during redevelopment that  do not require removal for geotechnical or construction purposes, the potentially impacted  soil may be placed beneath impervious surfaces (asphalt pavement, sidewalks, access  roads, buildings, etc.) or a minimum of 2 ft of clean fill.     ☒ Confer with NC BF project manager if Brownfield Plat must be revised (or re‐recorded if  actions are Post‐Recordation).                 ☒ GPS the location and provide site map with final location.  ☐ Other. Please provide a description of the measure:        4) Please describe the following action(s) to be taken during and following excavation and  management of site soils:  ☒ Check to confirm that management of fugitive dust from site activities will be handled in  accordance with applicable local, state, and federal requirements.    Field screening of site soil  At a minimum, contractors shall be made aware of protocols should impacted soils (e.g. staining,  unusual odors, fill materials) be identified.     Describe the field screening method, frequency of field screening, person conducting field  screening:   During soil disturbance at the site, the workers or contractors will observe soils for  evidence of potential impacts.  Evidence of potentially impacted soil includes a distinct  unnatural color, strong odor, or filled or previously disposed materials of concerns (i.e.,        12  EMP Version 3, March 2023   chemicals, tanks, drums, etc.).  Should the above be noted during site work, the  contractor will contact the project environmental professional to observe the suspect  condition.  If the project environmental professional confirms that the material may be  impacted, then the procedures below will be implemented.  In addition, the DEQ  Brownfields project manager will be contacted within 48 hours to advise of the condition.    Soil sample collection  ☒ Yes  The PD may perform in‐situ composite or stockpile sampling to characterize soil for export  purposes.  The proposed methodology and scope of work for in‐situ soil sampling will be outlined in  a Work Plan, which will be submitted to DEQ for approval prior to conducting in‐situ composite  sampling activities.  Stockpile soil sampling will consist of 3‐point composite samples and a grab  sample for VOC analysis as specified in Part 1.C. (Soil Export).     ☒ Not anticipated ‐ In order to avoid delays in construction, a plan shall be in place for sampling  of suspect soils should they be encountered during redevelopment.  If soil sample collection is  not anticipated but the need to do so is identified during redevelopment, notify the Brownfields  project manager of the anticipated sample and report dates for scheduling purposes.    Describe the sampling method (e.g., in‐situ grab, composite, stockpile, etc.) and confirm that all  procedures outlined in applicable DEQ guidance for assessment shall be followed Typically, at  least one representative sample (per 500 yd3 for residential and 1,000 yd3 for commercial)  consisting of a 3 to 5‐point composite sample with grab sample for VOCs based on the highest PID  reading is required to determine soil management options:   If impacted soil is encountered during grading and/or installation or removal of utilities,  excavation will proceed only as far as needed to allow grading or other construction‐ related activity to continue and/or only as far as needed to allow alternate corrective  measures as described below.  Suspect impacted soil excavated during redevelopment  activities may be stockpiled and covered in a secure area to allow construction to  progress.  Suspect impacted soil will be stockpiled in accordance with Figure 1, NCBP  Diagram for Temporary Containment of Impacted or Potentially Impacted Soil.  At least  one representative soil sample (no less than 3 aliquot soil samples) at a sample ratio of 1  soil sample per every approximately 500 cubic yards of soil will be collected for analysis of  total VOCs, SVOCs, RCRA metals, and hexavalent chromium.  If the soil sample laboratory  analytical results indicate that the soil could potentially exceed toxicity characteristic  hazardous waste criteria, then the soil will also be analyzed by TCLP for those compounds  that could exceed the toxicity characteristic hazardous waste criteria.  Impacted soil will  be handled in the manner described below based upon the laboratory analyses:  i. If no organic compounds or metals are detected in a sample (other than which are  attributable to sampling or laboratory artifacts or which are consistent with  background levels for metals) above protection of groundwater or Residential  PSRGs (whichever is lower for the detected compounds), the TCLP concentrations  are below hazardous waste criteria, and the cumulative risk calculator results are  acceptable, then the soil will be deemed suitable for use as on‐site fill or as off‐ site fill with DEQ approval.  The proposed location(s) for off‐site placement of soil      13  EMP Version 3, March 2023   (other than a Municipal Solid Waste Landfill [MSWLF] or other permitted facility)  along with the receiving facility’s written approval for acceptance of the soil will  be provided to DEQ for approval prior to taking the soil off‐site.  ii. If detectable levels of compounds are found which do not exceed  Industrial/Commercial PSRGs (other than which are attributable to sampling or  laboratory artifacts or which are consistent with background levels for metals)  and the TCLP concentrations are below hazardous waste criteria, then the soil  may be used on‐site as fill without conditions.  iii. If detectable levels of compounds are found which exceed the Industrial/Commercial  PSRGs (other than which are attributable to sampling or laboratory artifacts or  which are consistent with background levels for metals) and the TCLP  concentrations are below hazardous waste criteria, then the soil, with DEQ’s  written approval, may be used on‐site as fill below an impervious surface, at least  2 ft of compacted demonstrably clean soil, or overlain by a geotechnical fabric  and at least 1 ft of demonstrably clean soil.  If the impacted soil with  concentrations above Industrial/Commercial PSRGs is moved to an on‐site  location, its location and depth will be documented and provided to DEQ and the  impacted soil will be placed beneath at least 2 ft of compacted demonstrably  clean soil, an impervious surface, or covered by a geotechnical fabric.  iv. Impacted soil may be transported to a MSWLF or DEQ permitted landfarm provided  that the soil is accepted at the disposal facility.  DEQ Solid Waste Section and DEQ  Brownfields Redevelopment Section approval will be requested for any potential  export to an off‐Site facility other than a MSWLF or DEQ permitted landfarm.  If  soil is transported to a MSWLF or DEQ permitted landfarm, the facility’s written  approval in the form of waste manifests or similar will be included with the  annual redevelopment report.  In the unlikely event that the sample data  indicates concentrations above TCLP hazardous waste criteria, then the soil must  be transported off‐Site to a MSWLF that can accept or treat hazardous waste.    * Please note that should the PD elect to transport export soil to a MSWLF, DEQ  permitted landfarm, or to a DEQ Brownfields pre‐approved receiving facility, soil will be  direct‐loaded onto trucks for transport off‐site.    Check applicable chemical analytes for soil samples:  ☒ Minimum Sample Requirements: Volatile organic compounds (VOCs) by EPA Method  8260; Semi‐volatile organic compounds (SVOCs) by EPA Method 8270; and Metals RCRA  List + Hexavalent Chromium by EPA Method 6020/7199    ☐ Pesticides: Specify Analytical Method Number(s):     ☐ PCBs: Specify Analytical Method Number(s):         14  EMP Version 3, March 2023   ☐ Other Constituents & Respective Analytical Method(s) (e.g. Herbicides):    ☒ Check to confirm that by the owner’s signature and the North Carolina Professional  Engineer/Geologist sealing this EMP the consultant understands that no work plan for suspect  soil sample collection will be submitted beyond this EMP, and that it is the responsibility of the  sealing professional and property owner to ensure that all applicable guidelines and  methodologies are followed and reported to DEQ for determination and approval of soil  placement prior to final relocation.       If impacted soils above applicable PSRGs and/or site specific risk thresholds are proposed to be  relocated on‐site, prior to final placement on‐site, the following shall be submitted for DEQ  review/approval  ‐ Analytical data that has been sampled in accordance with the above referenced frequency and  following procedures outlined in the most recent Brownfields Redevelopment Section  Environmental Site Assessment Work Plan Minimum Requirements Checklist (Checklist) and in  accordance with DEQ IHSB Guidelines for Assessment and Cleanup of Contaminated Sites  (Guidelines)  ‐ Figure outlining planned soil placement and any future site features including  buildings/hardscape/open areas  ‐ A North Carolina PE/PG recommendation of placement    Impacts  Options  Onsite Placement without  conditions  Onsite placement under 2 ft  of cap or clean fill1, 2  All Constituents below applicable  PSRGs X   Constituents3 below applicable  PSRGs; Metals below background  but above PSRGs  X   Constituents3 below applicable  PSRGs; Metals above Background  /PSRGs   X  Constituents above Applicable  PSRGs  X  1: Requires Prior Written DEQ Approval  2: VOC impacted soils above applicable PSRGs shall not be placed directly beneath building footprints  without prior written DEQ approval.  3: Constituents indicate any samples evaluated for other than metals.    ☒ Check to confirm that stockpiling of known or suspected impacted soils will be conducted in  accordance with Figure 1 of this EMP.  Stockpile methodology should provide erosion control,  prohibiting contact between surface water/precipitation and contaminated soil, and preventing  contaminated runoff.  Explain any variances or provide additional details as needed:         15  EMP Version 3, March 2023   ☒ Final grade sampling of exposed native soil (i.e., soil that will not be under buildings or  permanent hardscape). Select chemical analyses for final grade samples with check boxes below  (Check all that apply):  ☒ Minimum Sample Requirements: Volatile organic compounds (VOCs) by EPA Method  8260; Semi‐volatile organic compounds (SVOCs) by EPA Method 8270; and Metals RCRA  List + Hexavalent Chromium by EPA Method 6020/7199    ☐ Pesticides: Specify Analytical Method Number(s):     ☐ PCBs: Specify Analytical Method Number(s):   ☐ Other Constituents & Respective Analytical Method(s) (e.g. Herbicides):    Please provide a scope of work for final grade sampling, including a diagram of soil  sampling locations, number of samples to be collected, and brief sampling methodology.   Samples should be collected from 0‐2 ft below ground surface, with the exception of VOCs  which should be taken from 1‐2 ft below ground surface.  Alternatively, indicate if a work  plan for final grade sampling may be submitted under separate cover.  A Final Grade Sampling Plan will be prepared following review of final  landscape/hardscape plans for the site.  The work plan will be submitted to DEQ  Brownfields Redevelopment Section under separate cover.  If no areas exist that warrant  final grade sampling, documentation will be provided to the DEQ Brownfields project  manager and/or the DEQ Brownfields Property Management Unit.  ☐ If final grade sampling was NOT selected, please explain rationale:      PART 1.B. IMPORTED FILL SOIL    NO SOIL MAY BE BROUGHT ONTO THE BROWNFIELDS PROPERTY WITHOUT PRIOR APPROVAL FROM  THE BROWNFIELDS REDEVELOPMENT SECTION.  According to the Brownfields IR 15, “Documenting  imported soil (by sampling, analysis, and reporting in accordance with review and written approval  in advance by the Brownfields Redevelopment Section), will safeguard the liability protections  provided by the brownfields agreement and is in the best interest of the prospective  developer/property owner.”    Requirements for importing fill:  ☒ Check to confirm that the import volumes outlined below have been confirmed based on  geotechnical evaluations.    1) Will fill soil be imported to the site?................................................ ☒ Yes  ☐ No  ☐ Unknown    2) If yes, what is the estimated volume of fill soil to be imported?   Approximately 4,200 cubic yards of fill will need to be imported into the site for mass grading  activities during redevelopment of the Brownfields property.      16  EMP Version 3, March 2023     3) If yes, what is the anticipated depth that fill soil will be placed at the property? (If a range  of depths, list the range.)  The anticipated depth that fill soil will be placed at the Brownfield property ranges from  approximately 0 to 9 ft.     PRIOR TO SOIL PLACEMENT AT THE BROWNFIELDS PROPERTY, a Soil Import Request must be  submitted for DEQ Brownfields review and approval. The request shall consist of a data  package that details:     ‐ Fill source location/history (Phase I if available, current aerials, etc.)  ‐ Analytical data that has been sampled in accordance with the below frequency and  following procedures outlined in the most recent Brownfields Redevelopment Section  Environmental Site Assessment Work Plan Minimum Requirements Checklist (Checklist)  and in accordance with DEQ IHSB Guidelines for Assessment and Cleanup of  Contaminated Sites (Guidelines)  ‐ A table comparing the import soil to existing site concentrations  ‐ A PE/PG recommendation of import  ‐ All relevant attachments listed in the Checklist    Soil Import Sampling Requirements:  Source Sample Frequency Sample Analysis  Virgin Material from DEQ  Brownfields Pre‐ approved Quarry  None (Contact Brownfields project manager for list of pre‐ approved Quarries  DEQ Permitted Quarry  (Not Brownfields Pre‐ approved)  At least one  representative sample  from area of planned  import  VOCs, SVOCs, RCRA  Metals, any site specific  COCs (e.g. pesticides,  PCBs, etc.)  Other NC DEQ  Brownfields Property  At least one  representative sample  per 1,000 yd3 consisting  of a 3‐point composite  sample with grab sample  for VOCs based on the  highest PID reading  VOCs, SVOCs, RCRA  Metals, any site specific  COCs (e.g. pesticides,  PCBs, etc.)  Off‐site  unpermitted/regulated  property  Bulk Landscape Material  from Commercial Vendor  (i.e. topsoil)  No Sampling Required    If other special considerations apply, discuss:       ☒ Check to confirm that by the owner’s signature and the North Carolina Professional  Engineer/Geologist sealing this EMP the consultant understands that no work plan for suspect soil  sample collection will be submitted beyond this EMP, and that it is the responsibility of the sealing  professional and property owner to ensure that all applicable guidelines are followed and reported in      17  EMP Version 3, March 2023   the Soil Import Request for DEQ approval. Failure to meet these requirements could result in  resampling and/or failure to approve import.     PART 1.C. SOIL EXPORT    NO SOIL MAY LEAVE THE BROWNFIELDS PROPERTY WITHOUT APPROVAL FROM THE  BROWNFIELDS REDEVELOPMENT SECTION.  Failure to obtain approval may violate a brownfields  agreement causing a reopener or jeopardizing eligibility in the Section, endangering liability  protections and making said action possibly subject to enforcement.  Justifications provided  below must be approved by the Section in writing prior to completing transport activities.  Refer  to Brownfields IR 15 for additional details.     1) If export from the Brownfields Property is anticipated, export soil must be sampled at a  frequency of one sample per 1,000 yd3 consisting of a 3‐point composite sample with a  grab sample for VOCs based on the highest PID reading.  Samples shall be analyzed at a  minimum for VOCs, SVOCs, and RCRA metals plus any site specific COCs.      PRIOR TO EXPORT FROM THE BROWNFIELDS PROPERTY, a Soil Export Request must be  submitted for DEQ Brownfields review and approval. The request shall consist of a Data  Package that details:     ‐ Proposed Receiving Facility  ‐ Analytical data that has been sampled in accordance with the above referenced  frequency and following procedures outlined in the most recent Brownfields  Redevelopment Section Environmental Site Assessment Work Plan Minimum  Requirements Checklist (Checklist) and in accordance with DEQ IHSB Guidelines for  Assessment and Cleanup of Contaminated Sites (Guidelines)  ‐ A table comparing the export soil to concentrations on the receiving site concentrations  including risk comparison (Note that calculated risk cannot be increased on the receiving  site)  ‐ A North Carolina PE/PG recommendation of export  ‐ Written approval from the receiving site property owner representative for export  ‐ All relevant attachments listed in the Checklist    Soil Export Options  Impacts  Options  Use as  Beneficial Fill  Off‐site disposal at  other Brownfields  Property2,6,7  Off‐site disposal  at LCID/CD  Landfill1, 3  Off‐site disposal at Subtitle  D MSW/Permitted  Landfarm4  All Constituents below  applicable PSRGs X X X X  Constituents5 below  applicable PSRGs; Metals  below background but  above PSRGs  X X X X  Constituents5 below  applicable PSRGs; Metals  X X X      18  EMP Version 3, March 2023   above Background /PSRGs  Constituents above  Applicable PSRGs  X   X  1: Requires Prior Written DEQ Approval  2: VOC impacted soils above applicable PSRGs shall not be placed directly beneath building footprints  without prior written DEQ approval.  3: Requires comparison to site specific metals concentrations.  4: Facility to determine if they can accept soil within their permit.  5: Constituents indicate any samples evaluated for other than metals.  6: Requires written approval from receiving site property owner representative.  7. Site COCs must be in comparable concentrations to receiving site and not significantly raise risk of  the receiving site.    ☒ Check to confirm that by the owner’s signature and the North Carolina Professional  Engineer/Geologist sealing this EMP the consultant understands that no work plan for suspect soil  sample collection will be submitted beyond this EMP, and that it is the responsibility of the sealing  professional and property owner to ensure that all applicable guidelines are followed and reported in  the Soil Export Request for DEQ approval. Failure to meet these requirements could result in  resampling and/or failure to approve export.     If other special considerations apply, discuss:     PART 1.D. MANAGEMENT OF UTILITY TRENCHES    ☐ Install liner between native impacted soils and base of utility trench before filling with clean fill  (Preferred)    ☒ Last out, first in principle for impacted soils (if soil can safely be reused onsite and is not a  hazardous waste), i.e., impacted soils are placed back at approximately the depths they were  removed from such that impacted soil is not placed at a greater depth than the original depth  from which it was excavated.    ☐ Evaluate whether necessary to install barriers in conduits to prevent soil vapor transport,  and/or degradation of conduit materials due to direct impact with contaminants.  ☐ If yes, provide specifications on barrier materials or provide the results of this evaluation in the  Vapor Mitigation Plan. Note that if vapor mitigation is planned for site buildings, utility corridors  will need to be evaluated as part of mitigation designs:      ☒ If no, include rationale here:  Soil gas data for the site do not show significant impacts or a vapor intrusion concern associated  with the proposed redevelopment activities.    ☒ Unknown, details to be provided in the Vapor Mitigation Plan for site buildings      19  EMP Version 3, March 2023     Other comments regarding managing impacted soil in utility trenches:   Although not anticipated, in the event that evidence of contaminated soil and/or vapors (e.g.,  unusual odors, stained soil, or physical effects such as dizziness, lightheadedness, coughing,  difficulty breathing, etc.),) is encountered in utility trenches during redevelopment activities,  the trench will be evacuated, and appropriate safety screening of the vapors will be performed  to protect workers.  Safety screening activities include screening the soil using a PID and  monitoring the worker breathing zone with a multi‐gas monitor (or similar instrument[s]  capable of detecting VOCs and combustible gases).  If results indicate further action is  warranted in response to vapors to protect workers, then the procedures outlined in Part 1.A.  Managing On‐Site Soil above will be implemented, and appropriate engineering controls (such  as use of industrial fans) will be implemented.  In addition, the environmental professional will  contact the DEQ Brownfields project manager within 48 hours to advise that person of the  condition.  PART 2. GROUNDWATER     1) What is the depth to groundwater at the Brownfields Property?  Groundwater has been measured in temporary monitoring wells at depths ranging from  approximately 17 to 29 ft bgs.  Depth to groundwater measurements in former temporary  monitoring wells are summarized in Table 2.       2) What is the maximum depth of soil disturbance onsite?   The maximum excavation depth is estimated to be approximately 10 ft during grading  activities.  Groundwater will not likely be encountered during the Site redevelopment.  Additionally, it is not anticipated that groundwater will be allowed to accumulate such that  sampling or disposal will be required.  See below for groundwater management procedures.    3) Is groundwater known to be contaminated by ☒onsite  ☐offsite   ☐both or ☐unknown  sources?  Describe source(s):   Previous groundwater assessment at the Brownfields property included collection of 12  groundwater samples for laboratory analysis.  Locations of the groundwater samples are shown  on Figure 3, and a tabular summary of groundwater sample laboratory analytical results is  included in Table 3.  A brief summary of the groundwater assessment results is provided below.    VOCs and SVOCs  Groundwater assessment results indicate that tetrachloroethylene (PCE up to 2,100 micrograms  per liter [µg/L]), TCE (up to 7.9 µg/L), chloromethane (up to 57.6 µg/L), and methylene chloride  (up to 5.3 J µg/L) were detected above the North Carolina 2L Groundwater Standards (2L  Standards) in samples TMW‐2 through TMW‐4, TMW‐7/TMW‐DUP, TMW‐8, TMW‐9, and/or  TMW‐11.  TMW‐2 through TMW‐4 and TMW‐7/TMW‐DUP through TMW‐9 were collected in the  northern portion of the site, and TMW‐11 was collected in the southwestern portion of the site.      No SVOCs were detected in groundwater samples at concentrations above the 2L Standards.    Metals  No metals were detected at concentrations above the DEQ 2L Standards in groundwater samples  collected at the site.      20  EMP Version 3, March 2023     4) What is the direction of groundwater flow at the Brownfields Property?   North‐northwest in the northern portion of the site and likely south‐southwest in the southern  portion of the site.    5) Will groundwater likely be encountered during planned redevelopment activities (e.g.  footer/utility construction or helical pilings?)     ☐Yes    ☒No   If yes, describe these activities:  Based on the depth to groundwater data and preliminary grading plans, it is not anticipated that  groundwater will be encountered during planned redevelopment activities.     In the event that groundwater is encountered during redevelopment activities (even if no is  checked above), list activities for contingent management of groundwater (e.g., dewatering  of groundwater from excavations or foundations, containerizing, offsite disposal, discharge to  sanitary sewer, NPDES permit, or sampling procedures).   Appropriate worker safety measures will be undertaken if groundwater gathers in an open  excavation within an area determined to be impacted (based on previous sampling data, strong  odor, unnatural color, sheen, etc.) during construction activities.  The contractor will contact the  environmental professional to observe the area(s) suspected to be impacted.  The accumulated  water will be allowed to evaporate/infiltrate to the extent time for dissipation does not disrupt  the construction schedule.  Should the time needed for natural dissipation of accumulated  water be deemed inadequate, the water will be tested for the presence of VOCs, SVOCs, and  RCRA metals and disposed off‐site (if impacted), or tested and discharged to the storm sewer (if  not impacted above DEQ surface water standards) in accordance with applicable municipal and  State regulations for erosion control and construction stormwater control.  Equipment that has  been in contact with saturated soil will be cleaned before leaving the Brownfields Property.    6) Are monitoring wells currently present on the Brownfields Property?.................☐Yes   ☒No     If yes, are any monitoring wells routinely monitored through DEQ or other  agencies?..................................................................................................................☐Yes   ☐No     7) Please check methods to be utilized in the management of known and previously  unidentified wells.    ☐ Abandonment of site monitoring wells in accordance with all applicable regulations.  It  is the Brownfields Redevelopment Section’s intent to allow proper abandonment of  well(s) as specified in the Brownfields Agreement, except if required for active  monitoring through another section of DEQ or the EPA.    ☐ Location of existing monitoring wells marked  ☐ Existing monitoring wells protected from disturbance   ☒ Newly identified monitoring wells will be marked and protected from further  disturbance until notification to DEQ Brownfields can be made and approval for  abandonment is given.    8) Please provide additional details as needed:        21  EMP Version 3, March 2023     Please note, disturbance of existing site monitoring wells without approval by DEQ  is not permissible.  If monitoring wells are damaged and/or destroyed, DEQ may require that  the PD be responsible for replacement of the well.    PART 3. SURFACE WATER  1) Is surface water present at the property?  ☐ Yes ☒ No   2) If yes, attach a map showing the location of surface water at the Brownfields Property  3) Is surface water at the property known to be contaminated? ☐ Yes  ☐ No  ☐ Unknown  4) Will workers or the public be in contact with surface water during planned redevelopment  activities or as part of the final redevelopment?    ☐ Yes  ☒ No  5) In the event that contaminated surface water is encountered during redevelopment  activities, or clean surface water enters open excavations, list activities for management of  such events (e.g. flooding, contaminated surface water run‐off, stormwater impacts):  During the Brownfields assessment windshield survey, H&H did not observe a surface water  features present at the site.  If surface water run‐off gathers in an open excavation within an  area suspected to be impacted during construction activities, appropriate worker safety and  groundwater management measures will be undertaken.  The contractor will contact the  environmental professional to observe the area(s) suspected to be impacted.  The accumulated  water will be allowed to evaporate/infiltrate to the extent that the time for dissipation does not  disrupt the construction schedule.  Should the time needed for natural dissipation of  accumulated water be deemed inadequate, the water will be tested for the presence of VOCs,  SVOCs, and RCRA metals and disposed off‐site (if impacted), or tested and discharged to the  storm sewer (if not impacted above DEQ surface water standards) in accordance with applicable  municipal and State regulations for erosion control and construction stormwater control.       PART 4. SEDIMENT  1) Are sediment sources present on the property?  ☐ Yes  ☒ No  2) If yes, is sediment at the property known to be contaminated? ☐ Yes  ☐ No ☐ Unknown  3) Will workers or the public be in contact with sediment during planned redevelopment  activities?   ☐ Yes ☒ No  4) Attach a map showing the location of known contaminated sediment at the property.  5) In the event that contaminated sediment is encountered during redevelopment activities, list  activities for management of such events (stream bed disturbance):  Not applicable  PART 5.  SOIL VAPOR    1) Do concentrations of volatile organic compounds at the Brownfields property exceed the  vapor intrusion screening levels (current version) in the following media:     Groundwater Exterior Soil Vapor Sub‐Slab Soil Vapor        22  EMP Version 3, March 2023   Residential ☒ Yes ☐ No    ☐ Unknown  ☒ Yes ☐ No    ☐ Unknown  ☐ Yes ☐ No    ☒ Unknown  Commercial ☒ Yes ☐ No    ☐ Unknown  ☒ Yes ☐ No    ☐ Unknown  ☐ Yes ☐ No    ☒ Unknown    2) Attach a map showing the locations of all soil vapor samples including any soil vapor  contaminants that exceeds screening levels and overlays planned site development features.     3) If applicable, at what depth(s) is exterior soil vapor known to be contaminated?     4) If applicable, at what depth(s) is sub‐slab soil vapor known to be contaminated?  ☐0‐6 inches ☐Other, please describe:    No sub‐slab vapor sampling has been performed at the site.    5) Will workers encounter contaminated exterior or sub‐slab soil vapor during planned  redevelopment activities?  ☐ Yes  ☐ No ☒ Unknown    In the event that apparent contaminated soil vapor is encountered (based on elevated PID  readings, unusual odors, etc.) during redevelopment activities (trenches, manways, basements or  other subsurface work,) list activities for management of such contact, INCLUDING notification to  DEQ within 48 hours of identification of the issue for determination of additional requirements:   The environmental professional will remain on call on an as‐needed‐basis during redevelopment  activities at the Site.  If contaminated soil vapors are suspected during redevelopment activities  (based on unusual or strong odors, dizziness, lightheadedness, coughing, difficulty breathing,  etc.), the excavation area will immediately be evacuated, and the environmental professional will  be called to perform appropriate safety screening of the vapors.  Safety screening activities  include monitoring the worker breathing zone with a calibrated multi‐gas monitor (or similar  instrument[s] capable of detecting VOCs and combustible gases) for VOCs, methane, oxygen,  H&H collected 23 exterior soil gas samples for laboratory analysis in July 2023.  The soil gas samples  were collected at approximately 5.5 ft bgs within the footprint of the proposed buildings to evaluate  the potential for structural vapor intrusion.  Soil gas sample locations are shown on Figure 3, and a  tabular summary of the laboratory analytical data is provided in Table 4.    As shown in Table 4, VOCs benzene (up to 77.3  micrograms per cubic meter [µg/m3], chloroform (up  to 43 µg/m), ethylbenzene (up to 72 µg/m3), isopropyl alcohol (32,400 µg/m3), PCE (up to 605 µg/m3),  and/or TCE (28 µg/m3) were detected in soil gas samples SG‐2 through SG‐6, SG‐8 through SG‐10, SG‐ 13, SG‐14, SG‐19/SG‐DUP, SG‐21, and SG‐22 at concentrations exceeding the DEQ DWM Residential  SGSLs.  The detection of isopropyl alcohol in SG‐22 also exceeded the DEQ DWM Non‐Residential  SGSL.  No samples other than SG‐22 had detections above DEQ DWM Non‐Residential SGSLs.      Results of worst‐case risk calculations performed for the soil gas sampling results per individual  proposed building do not indicate a significant vapor intrusion concern for the proposed non‐ residential use.          23  EMP Version 3, March 2023   carbon dioxide, and hydrogen sulfide photoionization detector.  If results indicate further action  is warranted, appropriate engineering controls (such as use of industrial fans) will be  implemented.  In addition, the environmental professional will contact the DEQ Brownfields  project manager within 48 hours regarding the condition.    PART 6. INDOOR AIR    1) Are indoor air data available for the Brownfields Property? ☐ Yes   ☒ No  2) If applicable, attach a map showing the location(s) where indoor air contaminants exceed site  screening levels.  3) If the structures where indoor air has been documented to exceed risk‐based screening levels will  not be demolished as part of redevelopment activities, will workers encounter contaminated  indoor air during planned redevelopment activities? ☐ Yes   ☐ No   ☐ Unknown  ☒ N/A    ☐ If no, include rationale here:    4) In the event that contaminated indoor air is encountered during redevelopment activities, list  activities for management of such contact:    VAPOR INTRUSION MITIGATION SYSTEM  1) Is a vapor intrusion mitigation system (VIMS) proposed for this Brownfields  Property?  ☐ Yes   ☐ No   ☒ Unknown    ☒ If no or unknown, include rationale here as well as plans for pre‐occupancy sampling, as  necessary:  Installation of a VIMS Plan is not anticipated for this Brownfields Property based on the results of  soil gas sampling and cumulative risk calculations for each of the proposed building areas.   However, pre‐ and post‐occupancy vapor intrusion monitoring will be performed.  Sampling  requirements will be evaluated on a building‐specific basis.  If yes, ☐ VIMS Plan Attached or ☐ VIMS Plan to be submitted separately    If submitted separately provide date:   Click or tap here to enter text.    VIMS Plan shall be signed and sealed by a NC Professional Engineer and follow the DEQ  Brownfields Redevelopment Section’s Vapor Intrusion Mitigation System Design Submittal  Requirements.  Note that approval of this EMP does not imply approval with any vapor intrusion mitigation land  In the unlikely event there is evidence of potential indoor air issues (i.e., unusual odors are identified  or workers report lightheadedness or other unusual physical reaction) during future redevelopment  activities, the area will be evacuated, and appropriate safety screening of the indoor air will be  performed.  If warranted, safety screening procedures will include periodically screening indoor air  for volatile organic vapors with a calibrated PID.  If results indicate further action is warranted,  appropriate engineering controls (such as use of industrial fans) will be implemented.      24  EMP Version 3, March 2023   use restrictions or requirements of the recorded or draft Brownfields Agreement and that  separate approval of mitigation measures will be required.     CONTINGENCY PLAN     In this section, please provide actions that will be taken to identify or manage unknown  potential new sources of contamination.   During redevelopment activities, it is not uncommon  that unknown tanks, drums, fuel lines, landfills, or other waste materials are encountered.   Notification to DEQ Brownfields project manager, UST Section, Fire Department, and/or other  officials, as necessary and appropriate, is required when new potential source(s) of  contamination are discovered.  These Notification Requirements were outlined on Page 1 of this  EMP.      Should potentially impacted materials be identified that are inconsistent with known site  impacts, the DEQ Brownfields project manager will be notified, and a sampling plan will be  prepared based on the EMP requirements and site‐specific factors.  Samples will generally be  collected to document the location of the potential impacts.      Check the following chemical analysis that are to be conducted on newly identified releases:  ☒ Minimum Sample Requirements: Volatile organic compounds (VOCs) by EPA Method 8260;  Semi‐volatile organic compounds (SVOCs) by EPA Method 8270; and Metals RCRA List +  Hexavalent Chromium by EPA Method 6020/7199    ☐ Pesticides: Specify Analytical Method Number(s):       ☐ PCBs: Specify Analytical Method Number(s):       ☐ Other Constituents & Analytical Method(s) (e.g. Herbicides)  Please note, if field observations indicate the need for additional analyses, they should  be conducted, even if not listed here.     Please provide details on the proposed methods of managing the following commonly  encountered issues during redevelopment of Brownfields Properties.    Underground Storage Tanks – Note that UST Section guidelines must be followed for sample  frequency during UST closure. Unless damage to onsite structures to remain as part of  redevelopment would occur, USTs shall be removed from the Brownfields Property:  In the event a UST or impacts associated with a UST release are discovered at the Site during  redevelopment activities, the UST and/or UST related impacts will be addressed through the  Brownfields Redevelopment Section.  DEQ Brownfields will be notified within 48 hours of discovery  of the UST.      If an undocumented UST is encountered, residual fluids (if present) will be removed, sampled for      25  EMP Version 3, March 2023   VOCs, SVOCs, and RCRA metals, and transported off‐site for disposal at a suitable facility based on  the laboratory analytical results.  Following the removal of residual fluids, the tank will be removed,  and closure soil sampling will be performed.  The number of soil samples will be consistent with  DEQ UST Section guidelines.  The soil samples will be submitted for laboratory analysis of VOCs,  SVOCs, RCRA metals, and hexavalent chromium.  Impacted soil will be managed in accordance with  the Managing On‐Site Soil (Part 1.A.) section outlined above.    If the UST cannot be removed for geotechnical or construction purposes, DEQ will be notified for  approval of in‐place closure.  Following DEQ approval, closure soil sampling will be performed in  general accordance with the DEQ UST Section guidelines.  Where appropriate, the bottom of the  UST may be penetrated before abandonment to prevent fluid accumulation.  If the UST contains  residual fluids, the fluids will be removed, sampled for VOCs, SVOCs, and RCRA metals, and  transported off‐site for disposal at a suitable facility based on the laboratory analytical results.  A  survey plat update may also be needed in the event of in‐place closure of USTs.    Sub‐Grade Feature/Pit:  If a sub‐grade feature or pit is encountered and does not require removal for geotechnical or  construction purposes, it will be filled with soil or suitable fill and construction will proceed.  Where  appropriate, the bottom may be penetrated before back filling to prevent fluid accumulation.  If the  pit has waste in it, the waste may be set aside in a secure area and will be sampled for waste  disposal purposes for TCLP VOCs, TCLP SVOCs, and TCLP metals and disposed off‐site at a permitted  facility or the waste will be managed in accordance with the Managing On‐Site Soil (Part 1.A.)  section outlined above, whichever is most applicable based on the type of waste present.  If the pit  must be removed and the observed waste characteristics indicate the concrete may potentially be  contaminated to a significant degree, the concrete will be sampled and analyzed by methods  specified by the disposal facility.    Buried Waste Material – Note that if buried waste, non‐native fill, or any obviously filled materials  is encountered, the DEQ Brownfields Redevelopment Section must be notified to determine if  investigation of landfill gases is required:  If excavation into buried wastes or significantly impacted soils occurs, the contractor is instructed to  stop work in that location and notify the environmental consultant.  The environmental consultant  will observe the suspect materials and collect samples if warranted.  In this event, confirmation  sampling will be conducted at representative locations in the base and the sidewalls of the  excavation after the waste or significantly impacted soil is removed.  The confirmation samples will  be analyzed for VOCs, SVOCs, RCRA metals, hexavalent chromium (or other analyses as appropriate  based on the type of waste material).  Information will be provided to DEQ Brownfields regarding  the permitted facility used for disposal of the waste or significantly impacted soil.  Areas of  suspected contaminated soil that remain at the site after excavation is complete above the DEQ  Residential PSRGs will be managed pursuant to this plan.    Re‐Use of Impacted Soils Onsite:  Please refer to description outlined in the Managing On‐Site Soil section (Part 1.A.) of the EMP      26  EMP Version 3, March 2023   above.      If unknown, impacted soil is identified onsite, management onsite can be considered after the  project team provides the necessary information, outlined in Part 1.A. Item 11, for Brownfields  project manager approval prior to final placement onsite.     If other potential contingency plans are pertinent, please provide other details or scenarios as  needed below:      POST‐REDEVELOPMENT REPORTING    ☐  Check this box to acknowledge that a Redevelopment Summary Report will be required for the  project.  If the project duration is longer than one year, an annual update is required and will be  due by January 31 of each year, or 30 days after each one‐year anniversary of the effective date of  this EMP (as agreed upon with the project manager).  These reports will be required for as long as  physical redevelopment of the Brownfields Property continues, except that the final  Redevelopment Summary Report will be submitted within 90 days after completion of  redevelopment.  Based on the estimated construction schedule, the first Redevelopment Summary  Report is anticipated to be submitted on 1/31/2025, unless another date is specified in the  recorded Brownfields Agreement for this Brownfields Property.      The Redevelopment Summary Report shall include environment‐related activities since the last  report, with a summary and drawings, that describes:   1. actions taken on the Brownfields Property;    2. soil grading and cut and fill actions;   3. methodology(ies) employed for field screening, sampling and laboratory analysis of  environmental media;   4. stockpiling, containerizing, decontaminating, treating, handling, laboratory analysis and  ultimate disposition of any soil, groundwater or other materials suspected or confirmed  to be contaminated with regulated substances; and   5. removal of any contaminated soil, water or other contaminated materials (for example,  concrete, demolition debris) from the Brownfields Property (copies of all legally required  manifests shall be included).    ☒ Check box to acknowledge consent to provide a NC licensed P.G. or P.E. sealed, Redevelopment  Summary Report in compliance with the site’s Brownfields Agreement.        28  EMP Version 3, March 2023         Tables Table 1 Summary of Soil Analytical Data Pharr Yarns - LowellLowell, North Carolina H&H Job No. HNY-001 Evaluation Area Former Electrical Substation Former Carpentry Sho Sample ID BG-1 BG-2 BG-3 SB-1 SB-2 SB-3 SB-5 SB-6 SB-7 SB-8 SB-9 SB-10 SB-11 SB-12 SB-13 Date Depth (ft bgs)11-13 1-3 Sample Type Range Mean TPH (EPA Method 8015C)Diesel Range Organics -- --100 -- -- -- -- --4.4 J <3.5 NA NA NA NA NA <3.0 <3.1 <3.2 3.9 J <2.8 <2.7 NAGasoline Range Organics -- --50 -- -- -- -- -- <1.8 <1.8 NA NA NA NA NA <1.4 <1.8 <1.8 <2.1 <1.4 <1.0 NA VOCs (8260D)Acetone 14,000 210,000 ------------NA NA NA NA <0.0018 <0.0013 <0.0012 NA NA NA NA NA NA 0.021Benzene1.2 5.4 ------------NA NA NA NA <0.0011 <0.00078 <0.00076 NA NA NA NA NA NA <0.00079Chloromethane2399------------NA NA NA NA <0.0021 <0.0015 <0.0015 NA NA NA NA NA NA <0.0015Ethylbenzene6.1 27 ------------NA NA NA NA <0.0010 <0.00075 <0.00073 NA NA NA NA NA NA <0.00076p-Isopropyltoluene NE NE ------------NA NA NA NA <0.0017 <0.0013 <0.0012 NA NA NA NA NA NA <0.0013 Isopropylbenzene (Cumene)410 2,100 ------------NA NA NA NA <0.00080 <0.00058 <0.00057 NA NA NA NA NA NA <0.00059Naphthalene2.1 8.8 ------------NA NA NA NA <0.00070 <0.00050 <0.00049 NA NA NA NA NA NA <0.00051Tetrachloroethylene1782------------NA NA NA NA 0.0085 0.018 0.0015 J NA NA NA NA NA NA <0.00092Toluene990 9,700 ------------NA NA NA NA <0.0011 <0.00079 <0.00077 NA NA NA NA NA NA <0.000811,2,4-Trimethylbenzene 63 370 ------------NA NA NA NA <0.00073 <0.00053 <0.00052 NA NA NA NA NA NA <0.00054m&p-Xylene 120 500 ------------NA NA NA NA <0.0018 <0.0013 <0.0012 NA NA NA NA NA NA <0.0013o-Xylene 140 590 ------------NA NA NA NA <0.00073 <0.00053 <0.00052 NA NA NA NA NA NA <0.00054Xylene (Total)120 530 ------------NA NA NA NA <0.0025 <0.0018 <0.0018 NA NA NA NA NA NA <0.0018 SVOCs (8270E)Acenaphthene 720 9,000 ------------NA NA NA <0.020 NA 0.064 J <0.020 NA NA NA NA NA NA 0.027 JcenaphthyleneNENE------------NA NA NA <0.017 NA <0.017 <0.017 NA NA NA NA NA NA <0.016nthracene3,600 45,000 ------------NA NA NA <0.0097 NA 0.18 J <0.0094 NA NA NA NA NA NA 0.097 JBenzo(a)anthracene 1.1 21 ------------NA NA NA <0.011 NA 0.67 J <0.010 NA NA NA NA NA NA 0.29 JBenzo(a)pyrene 0.11 2.1 ------------NA NA NA <0.0079 NA 0.68 J <0.0076 NA NA NA NA NA NA 0.25 JBenzo(b)fluoranthene 1.1 21 ------------NA NA NA <0.0081 NA 0.79 J <0.0079 NA NA NA NA NA NA 0.31 J Benzo(g,h,i)perylene NE NE ------------NA NA NA <0.0087 NA 0.37 J <0.0084 NA NA NA NA NA NA 0.14 JBenzo(k)fluoranthene 11 210 ------------NA NA NA <0.0093 NA 0.25 J <0.0090 NA NA NA NA NA NA 0.10 JChrysene110 2,100 ------------NA NA NA <0.010 NA 0.62 J <0.010 NA NA NA NA NA NA 0.26 JDibenzo(a,h)anthracene 0.11 2.1 ------------NA NA NA <0.025 NA 0.11 J <0.025 NA NA NA NA NA NA 0.038 JDibenzofuran16230------------NA NA NA NA NA NA NA NA NA NA NA NA NA NAFluoranthene480 6,000 ------------NA NA NA <0.01 NA 1.3 <0.0097 NA NA NA NA NA NA 0.59 JFluorene480 6,000 ------------NA NA NA <0.015 NA 0.062 J <0.015 NA NA NA NA NA NA 0.029 JIndeno(1,2,3-cd)pyrene 1.1 21 ------------NA NA NA <0.025 NA 0.42 J <0.024 NA NA NA NA NA NA 0.15 J1-Methylnaphthalene 18 73 ------------NA NA NA <0.013 NA 0.092 J <0.013 NA NA NA NA NA NA <0.013 2-Methylnaphthalene 48 600 ------------NA NA NA <0.017 NA 0.13 J <0.017 NA NA NA NA NA NA <0.016Naphthalene2.1 8.8 ------------NA NA NA <0.019 NA 0.099 J <0.018 NA NA NA NA NA NA <0.018PhenanthreneNENE------------NA NA NA <0.0096 NA 0.80 J <0.0093 NA NA NA NA NA NA 0.43 JPyrene360 4,500 ------------NA NA NA <0.013 NA 1.1 <0.012 NA NA NA NA NA NA 0.48 J PCBs (EPA Method 8082A)PCB-1016 (Aroclor 1016)0.82 10 ------------NA NA <0.0073 NA NA NA NA NA NA NA NA NA NA NAPCB-1221 (Aroclor 1221)0.20 0.84 ------------NA NA <0.053 NA NA NA NA NA NA NA NA NA NA NAPCB-1232 (Aroclor 1232)0.18 0.73 ------------NA NA <0.017 NA NA NA NA NA NA NA NA NA NA NAPCB-1242 (Aroclor 1242)0.23 0.95 ------------NA NA <0.018 NA NA NA NA NA NA NA NA NA NA NAPCB-1248 (Aroclor 1248)0.23 0.94 ------------NA NA <0.013 NA NA NA NA NA NA NA NA NA NA NAPCB-1254 (Aroclor 1254)0.23 0.97 ------------NA NA <0.016 NA NA NA NA NA NA NA NA NA NA NAPCB-1254 (Aroclor 1260)0.24 0.99 ------------NA NA <0.0084 NA NA NA NA NA NA NA NA NA NA NA RCRA Metals (6020B/7471B/7199)Arsenic 0.68 3.0 --1.0 - 18 4.8 8.42 7.87 3.29 NA NA NA NA NA NA NA NA NA NA NA NA NA NABarium3,100 47,000 --50 - 1,000 356 72.5 79.9 108 NA NA NA NA NA NA NA NA NA NA NA NA NA NACadmium 1.4 20 --1.0 - 10 4.3 0.186 J <0.0989 0.452 J NA NA NA NA NA NA NA NA NA NA NA NA NA NAChromium (total) NE NE --7.0 - 300 65 82.3 52.2 21.6 NA NA NA NA NA NA NA NA NA NA NA NA NA NAChromium, Hexavalent 0.31 6.5 --NS NS <0.303 0.527 J 0.380 J NA NA NA NA NA NA NA NA NA NA NA NA NA NAChromium, Trivalent 23,000 350,000 --NS NS 82.3 51.7 21.2 NA NA NA NA NA NA NA NA NA NA NA NA NA NA Lead 400 800 --ND - 50 16 43.7 20.6 68.4 NA NA NA NA NA NA NA NA NA NA NA NA NA NAMercur4.7 70 --0.03 - 0.52 0.121 0.236 0.0708 0.112 NA NA NA NA NA NA NA NA NA NA NA NA NA NASelenium78 1,200 --<0.1 - 0.8 0.42 1.13 J 1.36 J 0.552 J NA NA NA NA NA NA NA NA NA NA NA NA NA NASilve78 1,200 --ND - 5.0 NS <0.103 <0.100 <0.0952 NA NA NA NA NA NA NA NA NA NA NA NA NA NA Notes: 1) North Carolina Department of Environmental Quality (DEQ) Preliminary Soil Remediation Goals (PSRGs) dated July 2023. 2) Action Levels obtained from the NC DEQ Division of Waste Management (DWM) Underground Storage Tank (UST) Section Guidance for Site Checks, Tank Closure, and Initial Reponse and Abatement (May 2021). 3) Range and mean values for regional background metals are published in Elements in North American Soils by Dragun and Chekiri dated 2005. 4) North Carolina background levels are not specified; therefore, background values are reported for soils of the southeastern United States. 5) North Carolina background levels are not specified; therefore, background values are reported for soils of the conterminous United States. 6) Chromium PSRGs are not specified for total chromium. Refer to speciated chromium for PSRGs.7) Trivalent chromium concentrations were calculated by subtracting hexavalent chromium from total chromium concentrations.Bold values exceed the Residential PSRG. Underlined values exceed the Industrial/Commercial PSRGs. Metals detections that are generally consistent with published or site-specific background concentrations are not shown in bold. Compound concentrations are reported to the laboratory detection limits. With the exception of metals, only constituents detected in at least one sample are shown.Compound concentrations are reported in milligrams per kilogram (mg/kg) Laboratory analytical methods are shown in parentheses. VOCs = volatile organic compounds; SVOCs = semi-VOCs; RCRA = Resource Conservation and Recovery Act; TPH = total petroleum hydrocarbons; PCBs = polychlorinated biphenyls UST = underground storage tank; NS = not specified; NA = not analyzed; NE = not established; -- = not applicable; ND = non-detect; ft bgs = feet below ground surfaceJ = estimated concentration between the laboratory method detection limit and the laboratory reporting limit. Grab Grab 10-12 1-3 3-5 10-12 1/11/2021 Former Office Building UST Location Mill Building No. 1 Former Fuel Oil USTs Industrial/ Commercial PSRGs (1) Screening Criteria Regional Background Metals in Soil (3) Residential PSRGs (1) DEQ UST Section Action Levels (2) Former UST 0-2 Grab Site-Specific Background 7/17/2023 Mill Building No. 2 Former Fuel Oil USTs Mill Building No. 1 Former Coal Trestle Mill Building No. 1 Machine Shop SB-4 1/11/2021 https://harthick.sharepoint.com/sites/MasterFiles‐1/Shared Documents/AAA‐Master Projects/Henley Capital LLC (HNY)/HNY‐001 ‐ Lowell, NC ESA/EMP/Tables/Data Tables ‐ EMP Table 1 (Page 1 of 2) Hart & Hickman, PC Table 1 Summary of Soil Analytical Data Pharr Yarns - LowellLowell, North Carolina H&H Job No. HNY-001 Evaluation Area Proposed Buidling A - North Proposed Building C - North Proposed Building A - South Sample ID CS-1 CS-3 CS-4 CS-5 CS-6 CS-7 Date Depth (ft bgs) Sample Type Range Mean TPH (EPA Method 8015C)Diesel Range Organics -- --100 -- -- NA NA NA NA NA NA NA NAGasoline Range Organics -- --50 -- -- NA NA NA NA NA NA NA NA VOCs (8260D)Acetone 14,000 210,000 ------ <0.0382 <0.0452 <0.0443 <0.0498 <0.0465 <0.0505 <0.0539 <0.0492Benzene1.2 5.4 ------<0.0024 <0.0028 <0.0027 <0.0031 <0.0029 <0.0031 <0.0033 0.0044 JChloromethane2399--0.0055 J <0.0059 <0.0058 <0.0065 0.0061 J <0.0066 <0.0071 0.0070 JEthylbenzene6.1 27 ------ <0.0028 <0.0033 <0.0032 0.0154 <0.0034 <0.0037 <0.0039 0.0159p-Isopropyltoluene NE NE ------ <0.0029 <0.0035 <0.0034 0.0039 J <0.0036 <0.0039 <0.0041 <0.0038 Isopropylbenzene (Cumene)410 2,100 ------ <0.0020 <0.0024 <0.0023 0.0083 <0.0025 <0.0027 <0.0029 0.0048 JNaphthalene2.1 8.8 ------0.111 0.0098 0.0063 J 0.13 <0.0038 0.0054 J 0.0097 0.0472Tetrachloroethylene1782------ <0.0019 <0.0022 <0.0022 <0.0025 <0.0023 <0.0025 <0.0027 <0.0024Toluene990 9,700 ------0.0057 J <0.0049 <0.0048 0.0225 <0.0050 0.0073 J 0.0059 J 0.02621,2,4-Trimethylbenzene 63 370 ------0.0039 J <0.0042 <0.0041 0.0289 <0.0043 <0.0047 <0.0050 0.0193m&p-Xylene 120 500 ------0.0064 J <0.0048 <0.0047 0.0956 <0.0050 0.0069 J <0.0057 0.0622o-Xylene 140 590 ------0.0032 J <0.0031 <0.0030 0.0648 <0.0032 <0.0035 <0.0037 0.0424Xylene (Total)120 530 ------0.0096 J <0.0040 <0.0039 0.16 <0.0041 0.0069 J <0.0048 0.105 SVOCs (8270E)720 9,000 ------2.05 0.246 J 0.174 J <0.153 <0.148 <0.143 <0.142 <0.140NENE------0.464 <0.144 <0.141 <0.153 <0.148 <0.143 <0.142 <0.1403,600 45,000 ------5.84 0.485 0.408 <0.142 <0.138 <0.133 <0.132 0.295 J1.1 21 ------12.3 1.36 1.32 <0.145 <0.141 <0.136 <0.134 0.9010.11 2.1 ------9.14 1.21 1.15 <0.150 <0.146 <0.140 <0.139 0.741.1 21 ------13.2 1.68 1.52 <0.145 <0.141 <0.136 <0.134 1.01 NE NE ------6.38 0.925 0.871 <0.168 <0.164 <0.158 <0.156 0.55611210------5.00 0.704 0.584 <0.153 <0.148 <0.143 <0.142 0.353 J110 2,100 ------12.6 1.53 1.42 <0.158 <0.153 <0.148 <0.146 0.9150.11 2.1 ------2.27 0.27 J 0.256 J <0.167 <0.162 <0.157 <0.155 0.15716230------1.75 0.192 J <0.145 <0.157 <0.152 <0.147 <0.145 <0.143480 6,000 ------24.1 2.98 2.64 <0.149 <0.144 <0.139 0.177 J 1.74480 6,000 ------2.42 0.194 J <0.141 <0.153 <0.148 <0.143 <0.142 <0.140 Acenaphthene Acenaphthylene AnthraceneBenzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(g,h,i)perylene Benzo(k)fluoranthene ChryseneDibenz(a,h)anthracene Dibenzofuran Fluoranthene FluoreneIndeno(1,2,3-cd)pyrene 1.1 21 ------5.63 0.829 0.757 <0.171 <0.166 <0.160 <0.159 0.4851-Methylnaphthalene 18 73 ------0.478 <0.144 <0.141 <0.153 <0.148 <0.143 <0.142 <0.1402-Methylnaphthalene 48 600 ------0.683 <0.164 <0.161 <0.174 <0.169 <0.163 <0.161 <0.159Naphthalene2.1 8.8 ------1.39 <0.139 <0.137 <0.147 <0.143 <0.138 <0.137 <0.135PhenanthreneNENE------22.5 2.85 1.96 <0.142 <0.138 <0.133 0.258 J 1.17Pyrene360 4,500 ------20.5 2.63 2.49 <0.176 <0.171 <0.165 <0.164 1.58 PCBs (EPA Method 8082A)PCB-1016 (Aroclor 1016)0.82 10 ------NA NA NA NA NA NA NA NAPCB-1221 (Aroclor 1221)0.20 0.84 ------NA NA NA NA NA NA NA NAPCB-1232 (Aroclor 1232)0.18 0.73 ------NA NA NA NA NA NA NA NAPCB-1242 (Aroclor 1242)0.23 0.95 ------NA NA NA NA NA NA NA NAPCB-1248 (Aroclor 1248)0.23 0.94 ------NA NA NA NA NA NA NA NAPCB-1254 (Aroclor 1254)0.23 0.97 ------NA NA NA NA NA NA NA NAPCB-1254 (Aroclor 1260)0.24 0.99 ------NA NA NA NA NA NA NA NA RCRA Metals (6020B/7471B/7199)Arsenic 0.68 3.0 --1.0 - 18 4.8 8.65 6.01 11.8 6.76 6.8 7.09 7.32 9.14Barium3,100 47,000 --50 - 1,000 356 109 34.9 27.1 50.4 36.8 61.6 79.4 69.9Cadmium1.4 20 --1.0 - 10 4.3 0.433 J 0.145 J 0.211 J <0.109 <0.112 <0.105 0.127 J 0.170 JChromium (total) NE NE --7.0 - 300 65 35.4 29.6 31.3 30.1 28.1 26.5 21.4 25.1Chromium, Hexavalent 0.31 6.5 --NS NS 0.512 J 0.969 J 1.44 1.34 0.922 J 0.936 J 0.648 J 0.953 JChromium, Trivalent 23,000 350,000 --NS NS 34.9 28.6 29.9 28.8 27.2 25.6 20.8 24.1 Lead 400 800 --ND - 50 16 52.0 22.1 11.8 16.1 11.2 33.1 39.3 45.4Mercur4.7 70 --0.03 - 0.52 0.121 0.0815 0.0251 J 0.0698 0.0273 J 0.120 0.119 0.124 0.113Selenium78 1,200 --<0.1 - 0.8 0.42 1.40 J 1.07 J 2.14 J 1.23 J 1.57 J 1.17 J 1.24 J 1.21 JSilve78 1,200 --ND - 5.0 NS <0.101 <0.104 <0.109 <0.111 <0.113 <0.106 <0.108 <0.101 Notes: 1) North Carolina Department of Environmental Quality (DEQ) Preliminary Soil Remediation Goals (PSRGs) dated July 2023. 2) Action Levels obtained from the NC DEQ Division of Waste Management (DWM) Underground Storage Tank (UST) Section Guidance for Site Checks, Tank Closure, and Initial Reponse and Abatement (May 2021). 3) Range and mean values for regional background metals are published in Elements in North American Soils by Dragun and Chekiri dated 2005. 4) North Carolina background levels are not specified; therefore, background values are reported for soils of the southeastern United States. 5) North Carolina background levels are not specified; therefore, background values are reported for soils of the conterminous United States. 6) Chromium PSRGs are not specified for total chromium. Refer to speciated chromium for PSRGs.7) Trivalent chromium concentrations were calculated by subtracting hexavalent chromium from total chromium concentrations.Bold values exceed the Residential PSRG. Underlined values exceed the Industrial/Commercial PSRGs. Metals detections that are generally consistent with published or site-specific background concentrations are not shown in bold. Compound concentrations are reported to the laboratory detection limits. With the exception of metals, only constituents detected in at least one sample are shown.Compound concentrations are reported in milligrams per kilogram (mg/kg) Laboratory analytical methods are shown in parentheses. VOCs = volatile organic compounds; SVOCs = semi-VOCs; RCRA = Resource Conservation and Recovery Act; TPH = total petroleum hydrocarbons; PCBs = polychlorinated biphenyls UST = underground storage tank; NS = not specified; NA = not analyzed; NE = not established; -- = not applicable; ND = non-detect; ft bgs = feet below ground surfaceJ = estimated concentration between the laboratory method detection limit and the laboratory reporting limit. Composite 0-2 7/18/2023 Regional Background Metals in Soil (3) Screening Criteria Residential PSRGs (1) Industrial/ Commercial PSRGs (1) DEQ UST Section Action Levels (2) Proposed Building B - North Proposed Building B - South 7/19/2023 CS-2/SB-DUP https://harthick.sharepoint.com/sites/MasterFiles‐1/Shared Documents/AAA‐Master Projects/Henley Capital LLC (HNY)/HNY‐001 ‐ Lowell, NC ESA/EMP/Tables/Data Tables ‐ EMP Table 1 (Page 2 of 2) Hart & Hickman, PC Table 2 Summary of Well Construction and Depth to Groundwater Data Pharr Yarns - Lowell Lowell, North Carolina H&H Job No. HNY-001 Well ID Date of DTW Measurement Total Depth (ft bgs) Screen Interval (ft bgs) Ground Surface Elevation (ft) TOC Elevation (ft) Depth to Groundwater Below TOC Groundwater Elevation (ft) TMW-7 30 15-30 93.37 93.28 22.51 70.77 TMW-8 30 15-30 89.60 89.35 20.00 69.35 TMW-9 25 10-25 NM NM 23.16 NM TMW-10 30 15-30 105.31 104.98 29.12 75.86 TMW-11 7/21/2023 30 15-30 NM NM 23.20 NM TMW-12 7/20/2023 30 15-30 NM NM 21.88 NM Notes: Top of casing (TOC)/ground surface elevations were surveyed by H&H relative to an arbitrary datum of 100 ft set at an on-site benchmark. ft bgs = feet below ground surface; DTW = depth to water; NM = not measured due to the presence of dense vegetation 7/20/2023 https://harthick.sharepoint.com/sites/MasterFiles-1/Shared Documents/AAA-Master Projects/Henley Capital LLC (HNY)/HNY-001 - Lowell, NC ESA/Brownfields Assessment/Tables/Data Tables (08-18-23) DJH QC 9/6/2023 Table 2 (Page 1 of 1) Hart & Hickman, PC Table 3 Summary of Groundwater Analytical Data Pharr Yarns - Lowell Lowell, North Carolina H&H Job No. HNY-001 Evaluation Area Mill Building No. 2 Former Fuel Oil USTs Mill Building No. 1 Former Coal Trestle/ Downgradient of former Machine Shop Mill Building No. 1 Former Fuel Oil USTs Former Office Building UST Location Former UST Former Carpentry Shop Sample ID TMW-1 TMW-2 TMW-3 TMW-4 TMW-5 TMW-6 Sample Date VOCs (8260D) Acetone 6,000 NE NE <0.31 <3.1 <0.31 <0.31 <0.31 <0.31Chloroform70 0.81 3.6 <0.076 <0.76 <0.076 <0.076 <0.076 <0.076Chloromethane3 52 220 <0.079 <0.79 <0.079 <0.079 <0.079 <0.079 1,2-Dichlorobenzene 20 530 2,200 <0.076 <0.76 0.51 <0.076 <0.076 <0.0762-Hexanone 40 1,600 6,900 <0.065 <0.65 <0.065 <0.065 <0.065 <0.065Methylene Chloride 5 760 4,000 <0.083 <0.83 <0.083 <0.083 <0.083 <0.083Methyl tert-butyl ether (MTBE)20 450 2,000 <0.042 <0.42 <0.042 <0.042 <0.042 <0.042Naphthalene6 4.6 20 3.0 <3.0 <0.30 <0.30 <0.30 <0.30Tetrachloroethylene0.7 12 48 <0.098 2,100 6.6 5.6 <0.098 0.70Toluene600 3,800 16,000 <0.044 <0.44 <0.044 <0.044 <0.044 <0.044Trichloroethylene3 1 4.4 <0.078 7.9 <0.078 <0.078 <0.078 <0.078Trichlorofluoromethane2,000 NE NE <0.062 <0.62 <0.062 <0.062 <0.062 <0.062 1,2,4-Trimethylbenzene 400 50 210 0.84 <0.54 <0.054 <0.054 <0.054 <0.0541,3,5-Trimethylbenzene 400 35 150 0.22 J <0.76 <0.076 <0.076 <0.076 <0.076m,p-Xylene 500 71 300 0.30 J <1.2 <0.12 <0.12 <0.12 <0.12Xylene (total)500 77 320 0.30 J <1.5 <0.15 <0.15 <0.15 <0.15 SVOCs (8270E) Benzoic Acid 30,000 NE NE NA NA NA NA NA NADiethyl Phthalate 6,000 NE NE NA NA NA NA NA NA Naphthalene 6 4.6 20 1.6 J <1.3 <2.7 <1.3 <1.3 <1.4 RCRA Metals (6020B/7470A)Arsenic 10 NE NE NA NA NA NA NA NA Barium 700 NE NE NA NA NA NA NA NACadmium2NENENANANANANANA Chromium (Total)10 NE NE NA NA NA NA NA NALead15NENENANANANANANA Mercur 1 0.18 0.75 NA NA NA NA NA NA Selenium 20 NE NE NA NA NA NA NA NASilve20NENENANANANANANA Notes: 1 North Carolina Department of Environmental Qualit NCDEQ or DEQ 15A NCAC 02L.0202 Groundwater Standards 2L Standards or Interim Maximum Allowable Concentrations IMACs , dated April 2022.2 DEQ Department of Waste Mana ement DWM Residential and Non Residential Vapor Intrusion Ground Water Screenin Levels GWSLs , TCR=1E-6; THQ=0.2, dated Jul 2023.Bold values exceed the DEQ 2L Standard. Underlined values exceed the Residential GWSL.Bold and Underlined concentrations exceed the 2L Standard and Residential GWSL. Compound concentrations are reported to the laborator detection limits. Concentrations are reported in micro rams per liter µ/L .Laborator anal tical methods are shown in parentheses. With the exception of metals, onl constituents detected in at least one sample are shown. VOCs = volatile or anic compounds; SVOCs = semi-VOCs; RCRA = Resource Conservation and Recover Act;J = estimated concentration between the laborator method detection limit and the laborator reportin limit NE = not established; NA = not anal zed; TCR = tar et cancer risk; THQ = tar et hazard quotient; UST = under round stora e tank Bold and Highlighted values exceed the 2L Standard and Non-Residential GWSL. Screening Criteria 2L Standards (1) Residential GWSLs (2) Non- Residential GWSLs (2)1/12/2021 https://harthick.sharepoint.com/sites/MasterFiles‐1/Shared Documents/AAA‐Master Projects/Henley Capital LLC (HNY)/HNY‐001 ‐ Lowell, NC ESA/EMP/Tables/Data Tables ‐ EMP 9/7/2023 Table 3 (Page 1 of 2) Hart & Hickman, PC Table 3 Summary of Groundwater Analytical Data Pharr Yarns - Lowell Lowell, North Carolina H&H Job No. HNY-001 Evaluation Area Proposed Building A - North Proposed Building B - North Proposed Building A - South Proposed Building B - South Sample ID TMW-8 TMW-9 TMW-10 TMW-11 TMW-12 Sample Date 7/21/2023 7/20/2023 VOCs (8260D) Acetone 6,000 NE NE <12.8 <12.8 <5.1 <5.1 8.3 J <5.1 <5.1Chloroform70 0.81 3.6 <1.1 <1.1 0.51 J <0.43 <0.43 1.6 <0.43Chloromethane3 52 220 <1.4 <1.4 0.74 J 43.4 0.80 J 57.6 1.6 1,2-Dichlorobenzene 20 530 2,200 <0.85 <0.85 <0.34 <0.34 <0.34 <0.34 <0.342-Hexanone 40 1,600 6,900 <1.2 <1.2 <0.48 0.55 J 0.59 J <0.48 <0.48 Methylene Chloride 5 760 4,000 <4.9 5.3 J <2.0 <2.0 <2.0 <2.0 <2.0Methyl tert-butyl ether (MTBE)20 450 2,000 <1.1 <1.1 <0.42 <0.42 <0.42 4.0 <0.42 Naphthalene 6 4.6 20 <1.6 <1.6 <0.64 <0.64 <0.64 <0.64 <0.64Tetrachloroethylene0.7 12 48 307 327 71.8 <0.29 <0.29 <0.29 <0.29 Toluene 600 3,800 16,000 <0.60 <0.60 <0.24 <0.24 <0.24 <0.24 <0.24Trichloroethylene3 1 4.4 <0.96 1.1 J 6.1 <0.38 <0.38 <0.38 <0.38Trichlorofluoromethane2,000 NE NE <0.74 <0.74 2.8 <0.30 <0.30 <0.30 <0.30 1,2,4-Trimethylbenzene 400 50 210 NA NA NA NA NA NA NA1,3,5-Trimethylbenzene 400 35 150 NA NA NA NA NA NA NAm,p-Xylene 500 71 300 <1.8 <1.8 <0.71 <0.71 <0.71 <0.71 <0.71 Xylene (total)500 77 320 <0.84 <0.84 <0.34 <0.34 <0.34 <0.34 <0.34 SVOCs (8270E) Benzoic Acid 30,000 NE NE 41.2 J 22.0 J 47.3 J 46.0 J <22.0 <20.0 41.3 JDiethyl Phthalate 6,000 NE NE <1.8 <1.8 <2.0 3.8 J 5.1 J <1.9 <1.7 Naphthalene 6 4.6 20 <1.8 <1.8 <2.1 <2.1 <2.1 <1.9 <1.7 RCRA Metals (6020B/7470A)Arsenic 10 NE NE 0.74 J 0.79 J 0.17 J 0.28 J 0.29 J 0.17 J 0.18 J Barium 700 NE NE 53.3 46.7 61.1 127 80.5 128 19.0Cadmium2NENE0.37 0.38 0.080 J 0.10 J 0.067 J 0.085 J 0.060 J Chromium (Total)10 NE NE 0.62 J 0.71 J <0.50 0.61 J 0.69 J 0.94 J 0.92 JLead15NENE<0.077 0.079 J <0.077 0.091 J <0.077 <0.077 0.25 J Mercur 1 0.18 0.75 <0.12 <0.12 <0.12 <0.12 <0.12 <0.12 <0.12 Selenium 20 NE NE 2.2 2.2 0.86 J 2.4 0.28 J <0.072 <0.072Silve20NENE<0.070 <0.070 <0.070 <0.070 <0.070 <0.070 <0.070 Notes: 1 North Carolina Department of Environmental Qualit NCDEQ or DEQ 15A NCAC 02L.0202 Groundwater Standards 2L Standards or Interim Maximum Allowable Concentrations IMACs , dated April 2022.2 DEQ Department of Waste Mana ement DWM Residential and Non Residential Vapor Intrusion Ground Water Screenin Levels GWSLs , TCR=1E-6; THQ=0.2, dated Jul 2023.Bold values exceed the DEQ 2L Standard. Underlined values exceed the Residential GWSL.Bold and Underlined concentrations exceed the 2L Standard and Residential GWSL.Bold and Highlighted values exceed the 2L Standard and Non-Residential GWSL.Compound concentrations are reported to the laborator detection limits. Concentrations are reported in micro rams per liter µ/L .Laborator anal tical methods are shown in parentheses. With the exception of metals, onl constituents detected in at least one sample are shown. VOCs = volatile or anic compounds; SVOCs = semi-VOCs; RCRA = Resource Conservation and Recover Act;J = estimated concentration between the laborator method detection limit and the laborator reportin limit NE = not established; NA = not anal zed; TCR = tar et cancer risk; THQ = tar et hazard quotient; UST = under round stora e tank 7/20/2023 TMW-7/TMW-DUP Northern Site Boundary 2L Standards (1) Residential GWSLs (2) Non- Residential GWSLs (2) Screening Criteria https://harthick.sharepoint.com/sites/MasterFiles‐1/Shared Documents/AAA‐Master Projects/Henley Capital LLC (HNY)/HNY‐001 ‐ Lowell, NC ESA/EMP/Tables/Data Tables ‐ EMP 9/7/2023 Table 3 (Page 2 of 2) Hart & Hickman, PC Table 4 Summary of Exterior Soil Gas Analytical Data Pharr Yarns - Lowell Lowell, North Carolina H&H Job No. HNY-001 Evaluation Area Sample ID SG-1 SG-2 SG-3 SG-4 SG-5 SG-6 SG-7 SG-8 SG-9 SG-10 SG-11 SG-12 SG-13 SG-14 SG-15 SG-16 SG-17 SG-18 SG-20 SG-21 SG-22 SG-23 Sample Date VOCs (TO-15) Acetone NE NE 15.4 58.0 25.0 53.2 37.1 23.1 34.9 51.8 54.7 30.4 17.2 28.8 30.7 17.8 18.9 18.0 14.6 13.3 30.4 J 28.5 J 19.1 28.8 1,570 21.0 Benzene 12 160 7.09 38.3 14.7 30.6 20.2 7.86 15.9 31.7 53.7 77.3 27.8 25.7 28.9 68.4 6.04 13.6 15.4 15.7 17.2 18.2 9.58 34.5 54.6 J 30.4 Bromodichloromethane 2.5 33 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 1.39 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <0.471 <47.1 <0.471 1,3-Butadiene 3.1 41 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 1.88 J <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <0.230 <23.0 <0.230 Carbon Disulfide 4,900 61,000 5.98 58.5 33.3 167 59.1 <0.317 34.2 77.8 183 208 <0.317 201 <0.317 166 6.44 17.1 13.8 30.2 28.7 30.0 25.0 129 43.4 J 54.2 Carbon Tetrachloride 16 200 <0.461 <0.461 <0.461 <0.461 <0.461 <0.461 0.585 J <0.461 <0.461 <0.461 <0.461 <0.461 <0.461 0.642 J <0.461 <0.461 <0.461 <0.461 <0.461 <0.461 <0.461 0.584 J <46.1 <0.461 Chlorobenzene 350 4,400 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 0.568 J <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <0.385 <38.5 <0.385 Chloroethane 28,000 350,000 <0.263 <0.263 <0.263 <0.263 0.353 J <0.263 0.327 J 0.353 J 0.351 J 0.372 J 0.372 J 0.514 J <0.263 0.493 J <0.263 <0.263 <0.263 <0.263 <0.263 <0.263 <0.263 <0.263 <26.3 <0.263 Chloroform 4.1 53 2.64 1.59 16.1 <0.349 9.59 9.93 1.33 6.91 11.0 31.8 4.74 4.08 19.7 43.0 17.1 9.10 37.3 22.6 <0.349 <0.349 0.579 J <0.349 <34.9 <0.349 Chloromethane 630 7,900 1.35 0.314 J 0.547 1.04 1.18 0.795 1.68 0.717 0.872 0.568 0.483 0.671 0.500 0.341 J <0.213 0.374 J 0.628 <0.213 <0.213 <0.213 2.01 5.87 <21.3 0.921 Cyclohexane 42,000 530,000 1.18 18.9 6.20 59.2 10.8 3.58 11.2 16.5 54.4 38.6 23.3 23.7 17.9 27.2 1.35 10.9 6.99 14.7 <0.259 <0.259 3.65 <0.259 80.2 <0.259 Dichlorodifluoromethane 700 8,800 0.989 J 1.96 1.58 2.07 1.59 1.06 2.00 1.86 1.90 1.84 1.58 2.64 1.85 <0.678 1.29 1.77 1.70 1.71 <0.678 <0.678 1.22 2.71 <67.8 2.43 1,1-Dichloroethane 58 770 <0.290 <0.290 0.291 J <0.290 <0.290 0.323 J <0.290 0.513 J <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <0.290 <29.0 <0.290 1,1-Dichloroethene 1,400 18,000 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 0.472 J <0.302 <0.302 <0.302 <0.302 <0.302 <0.302 <30.2 <0.302 cis-1,2-Dichloroethene 280 3,500 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 <0.311 0.749 J <31.1 <0.311 trans-1,2-Dichloroethene 280 3,500 <0.267 1.32 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 <0.267 0.307 J <0.267 <26.7 <0.267 Ethanol NE NE 27.5 26.8 42.8 79.2 99.9 32.4 25.3 32.1 76.9 74.3 23.9 70.0 33.9 15.0 36.6 21.9 69.8 53.5 27.0 JB 57.7 27.7 108 2,920 76.2 Ethyl acetate 490 6,100 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 <0.360 1.62 <36.0 1.01 Ethylbenzene 37 490 6.50 27.3 12.8 35.2 18.4 6.55 <0.362 21.1 43.8 72.0 24.8 25.3 27.7 68.1 23.6 13.8 20.0 9.06 22.9 25.2 B 21.1 36.6 63.3 J 32.2 4-Ethyltoluene NE NE 1.29 3.80 2.38 5.06 5.20 1.70 2.46 3.21 7.21 11.4 3.95 3.71 4.09 12.7 6.18 2.19 4.45 1.31 <0.384 <0.384 4.08 5.20 <38.4 5.45 n-Heptane 2,800 35,000 9.86 198 52.8 274 87.9 31.2 56.4 113 275 386 344 355 252 182 13.2 83.4 90.0 141 99.4 95.3 63.0 203 285 163 n-Hexane 4,900 61,000 2.93 76.5 16.6 93.1 36.0 7.97 23.1 98.0 106 145 104 94.8 70.9 36.7 2.49 38.8 22.8 45.5 <0.726 12.0 J 7.54 62.4 4,340 58.2 2-Hexanone 210 2,600 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <0.544 <54.4 4.54 J Isopropylbenzene (Cumene)2,800 35,000 1.44 4.76 2.32 7.18 7.82 4.43 1.21 2.50 14.9 10.1 5.01 5.41 5,41 9.14 3.80 4.02 3.89 3.26 <0.382 <0.382 3.55 <0.382 <38.2 <0.382 Isopropyl Alcohol (2-Propanol)1,400 18,000 6.10 5.75 5.53 16.5 18.5 5.51 5.41 <0.649 9.29 9.86 4.52 17.1 5.46 4.50 5.48 2.88 J 7.52 6.10 <0.649 10.7 J 6.83 19.3 32,400 E 10.1 2-Butanone (MEK)35,000 440,000 3.39 J 14.7 4.84 10.5 5.93 3.98 4.42 7.55 10.5 4.04 2.82 J <0.240 6.72 3.39 J 2.95 J 5.51 2.36 J 2.77 J 9.61 J 4.84 J 7.73 6.61 174 J 5.28 4-Methyl-2-pentanone (MIBK)21,000 260,000 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 <0.313 226 J <0.313 Methylene Chloride 3,400 53,000 0.712 1.08 <0.340 8.65 3.14 <0.340 1.14 1.51 1.50 1.38 <0.340 2.97 1.73 0.990 1.21 0.833 4.13 3.58 <0.340 <0.340 0.819 3.24 270 1.78 Methyl methacrylate 4,900 61,000 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 <0.359 647 <0.359 Naphthalene 2.8 36 <1.83 2.37 J <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <1.83 <183 <1.83 Propylene 21,000 260,000 <0.160 9.68 1.84 J 115 14.6 <0.160 16.1 84.2 52.0 55.8 27.4 53.0 22.0 7.06 <0.160 5.06 1.83 J <0.160 <0.160 <0.160 <0.160 29.6 <16.0 12.3 Styrene 7,000 88,000 <0.335 0.766 J 0.570 J 1.15 1.56 0.966 0.506 J 1.82 2.18 1.24 0.944 1.15 0.863 0.659 J 0.424 J 0.519 J 0.425 J 1.33 <0.335 <0.335 0.966 <0.335 69.8 J 7.53 Tetrachloroethene 280 3,500 97.8 277 143 267 111 88.9 94.4 227 384 605 273 226 284 551 109 99.1 139 151 292 327 208 363 355 243 Tetrahydrofuran 14,000 180,000 0.455 J 1.52 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <0.216 <21.6 <0.216 Toluene 35,000 440,000 67.1 246 123 277 148 67.4 112 182 372 505 209 213 241 512 127 113 142 98.7 217 225 149 268 433 216 1,1,1-Trichloroethane 35,000 440,000 <0.400 <0.400 <0.400 <0.400 <0.400 1.51 <0.400 <0.400 <0.400 <0.400 <0.400 <0.400 <0.400 <0.400 <0.400 1.82 <0.400 <0.400 <0.400 <0.400 <0.400 0.480 J <40.0 <0.400 Trichloroethene 14 180 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 <0.364 27.8 <36.4 2.75 Trichlorofluoromethane NE NE 32.5 10.6 120 127 34.1 26.1 2.03 487 10.7 2.23 9.33 2.17 3.43 1.57 1.35 1.43 1.48 51.4 <0.460 <0.460 1.29 7.14 <46.0 7.47 1,1,2-Trichlorotrifluoroethane 35,000 440,000 <0.608 <0.608 <0.608 <0.608 <0.608 1200 <0.608 <0.608 <0.608 <0.608 1200 <0.608 600 <0.608 <0.608 <0.608 <0.608 <0.608 <0.608 <0.608 <0.608 1.02 J <60.8 0.742 J 1,2,4-Trimethylbenzene 420 5,300 4.31 11.2 9.18 17.7 17.9 6.82 8.83 11.6 26.8 30.0 10.7 11.8 11.6 35.4 26.3 7.71 13.1 4.15 <0.375 13.8 12.1 22.7 86.4 J 20.9 1,3,5-Trimethylbenzene 420 5,300 1.48 3.21 2.97 6.38 5.25 1.63 2.44 3.96 7.75 9.96 3.50 3.71 3.79 12.4 7.71 2.52 4.50 1.40 <0.382 3.90 J 3.29 6.38 <38.2 7.41 2,2,4-Trimethylpentane NE NE 4.09 134 40.6 157 64.9 19.3 51.4 94.8 221 307 221 212 168 64.5 5.56 60.7 56.5 81.3 41.9 39.7 26.2 122 144 99.5 Vinyl acetate 1,400 18,000 <0.408 <0.408 <0.408 <0.408 <0.408 8.13 <0.408 74.3 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <0.408 <40.8 <0.408 o-Xylene 700 8,800 7.98 25.7 14.0 31.1 19.3 8.06 12.4 22.3 47.3 61.6 22.1 20.0 25.5 65.0 27.6 13.0 18.9 8.89 24.5 23.3 20.4 34.1 76.3 J 30.9 m&p-Xylene 700 8,800 20.6 70.7 38.6 95.4 55.9 20.3 34.6 65.5 124 194 68.5 65.0 75.4 188 72.0 37.8 56.8 25.4 61.6 73.7 58.1 104 215 93.2 DEQ Cumulative Risk Calculations Residential LICR Residential Non-Carcinogenic HI Non-Residential LICR Non-Residential Non-Carcinogenic HI Notes: 1) North Carolina Department of Environmental Quality (DEQ) Division of Waste Management (DWM) Sub-Slab & Exterior Soil Gas Screening Levels (SGSLs), TCR = 1E-6; THQ=0.2, dated July 2023. Bold values exceed the Residential SGSL or acceptable risk level. Bold and underlined values exceed the Non-Residential SGSL. Compound concentrations are reported to the laboratory method detection limits. Only constituents detected in at least one sample are shown. Compound concentrations are reported in micrograms per cubic meter (μg/m3). Laboratory analytical methods are shown in parentheses. VOCs = volatile organic compounds; LICR = lifetime incremental cancer risk; HI = hazard index; THQ = target cancer risk; THQ = target hazard quotient; NE = not established J = estimated concentration between the laboratory method detection limit and the laboratory reporting limit B = analyte was detected in the associated method blank E = analyte concentration exceeded the laboratory calibration range. The reported result is estimated. 0.46 1.1 x 10-6 5.8 1.5 x 10-5 0.015 9.2 x 10 -7 0.18 1.2 x 10-5 SG-19/SG-DUP 7/20/20237/20/2023 7/21/2023 Screening Criteria Residential SGSLs (1) Non-Residential SGSLs (1) Proposed Building A - South Proposed Building B - SouthProposed Building A - North Proposed Building B - North Proposed Building C - North 9.7x10-6 0.35 7.4x10-7 0.028 0.053 7.7x10-7 0.66 1.0x10-5 0.052 1.5 x 10-6 0.65 2.0 x 10-5 <1.0 x 10-4 <1.0 Acceptable Risk Levels <1.0 x 10-4 <1.0 https://harthick.sharepoint.com/sites/MasterFiles‐1/Shared Documents/AAA‐Master Projects/Henley Capital LLC (HNY)/HNY‐001 ‐ Lowell, NC ESA/Brownfields Assessment/Tables/Data Tables (08‐18‐23) DJH QC 9/7/2023 Table 4 (Page 1 of 1) Hart & Hickman, PC Figures SITE LOCATION MAP PHARR YARNS - LOWELL 700 WEST 1ST STREET LOWELL, NORTH CAROLINA DATE: 11-29-24 JOB NO: HNY-001 REVISION NO: 0 FIGURE NO: 1 2923 South Tryon Street - Suite 100 Charlotte, North Carolina 28203 704-586-0007 (p) 704-586-0373 (f) License # C-1269 / # C-245 Geology TITLE PROJECT 0 2,000 4,000 SCALE IN FEET SITE Pa t h : S : \ A A A - M a s t e r P r o j e c t s \ H e n l e y C a p i t a l L L C ( H N Y ) \ H N Y - 0 0 1 - L o w e l l , N C \ B r o w n f i e l d s A s s e s s m e n t \ F i g u r e s \ G I S F i l e s \ F i g u r e 1 . a p r x N U.S.G.S. QUADRANGLE MAP MOUNT HOLLY, NORTH CAROLINA 2022 QUADRANGLE 7.5 MINUTE SERIES (TOPOGRAPHIC) REVISION NO. 0 JOB NO. HNY-001 DATE: 1-29-24 FIGURE NO. 2 PHARR YARNS - LOWELL 700 WEST 1ST STREET LOWELL, NORTH CAROLINA SITE MAP LEGEND BROWNFIELDS BOUNDARY PROPERTY PARCEL BOUNDARY RAILROAD HISTORIC BUILDING FOOTPRINT PROPOSED BUILDING FOOTPRINT FORMER UNDERGROUND STORAGE TANK LOCATION VENT PIPE POLE-MOUNTED TRANSFORMER 2923 South Tryon Street-Suite 100 Charlotte, North Carolina 28203 704-586-0007(p) 704-586-0373(f) License # C-1269 / #C-245 Geology WES T 1 S T S T R E E T NOR T H C L A Y S T R E E T BIR C H S T R E E T POT T S S T R E E T NOTES: 1.PARCEL DATA OBTAINED FROM GASTON COUNTY GIS DEPARTMENT, 2022. 2.AERIAL IMAGERY OBTAINED FROM ESRI GIS SERVICES, 2019. RESIDENTIAL RESIDENTIAL FORMER TOWN OF LOWELL WATER TOWER FORMER OFFICE BUILDING NON-POTABLE WATER SUPPLY WELL FORMER DUKE POWER SUB-STATION FORMER WASTE HOUSE MILL BUILDING NO. 2 MILL BUILDING NO. 1 COTTON WAREHOUSE COTTON WAREHOUSE HIGHWAY 7 COOL JUNK (607 WEST 1ST STREET) MULTI-TENANT COMMERCIAL (510 WEST 1ST STREET) LOWELL CHURCH OF GOD (800 WEST 1ST STREET) FORMER WATER RESERVOIR RAIL R O A D S T R E E T AS H S T R E E T PHI L L I P S S T R E E T FORMER MACHINE SHOP FORMER CARPENTER SHOP FORMER RESIDENTIAL PROPERTIES FORMER RESIDENTIAL PROPERTIES FORMER STORES BUILDING B BUILDING C BUILDING A BUILDING B RESIDENTIAL FORMER MACHINE SHOP FORMER COAL TRESTLEBUILDING A S: \ A A A - M a s t e r P r o j e c t s \ H e n l e y C a p i t a l L L C ( H N Y ) \ H N Y - 0 0 1 - L o w e l l , N C \ E M P \ F i g u r e s \ H N Y . 0 0 1 - 5 2 0 2 4 0 1 2 9 . d w g , F I G 2 , 1 / 2 9 / 2 0 2 4 7 : 3 7 : 1 4 A M , s h a y n e s SB-12/TMW-5 SB-9 SB-10/TMW-4 SB-8/TMW-3 SB-6 SB-5 SB-4/TMW-2 SB-2 SB-3 SB-13/TMW-6 SB-1/TMW-1 SB-7 SB-11 REVISION NO. 0 JOB NO. HNY-001 DATE: 1-29-24 FIGURE NO. 3 PHARR YARNS - LOWELL 700 WEST 1ST STREET LOWELL, NORTH CAROLINA SAMPLE LOCATION MAP LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL BOUNDARY RAILROAD PROPOSED BUILDING FOOTPRINT FORMER UNDERGROUND STORAGE TANK LOCATION (UST) VENT PIPE POLE-MOUNTED TRANSFORMER TEMPORARY MONITORING WELL LOCATION BACKGROUND SOIL BORING LOCATION CO-LOCATED TEMPORARY MONITORING WELL AND SOIL BORING LOCATION CO-LOCATED SOIL BORING AND SOIL GAS SAMPLE LOCATION SOIL BORING 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 WES T 1 S T S T R E E T NOR T H C L A Y S T R E E T POT T S S T R E E T NOTES: 1.PARCEL DATA OBTAINED FROM GASTON COUNTY GIS DEPARTMENT, 2022. 2.AERIAL IMAGERY OBTAINED FROM ESRI GIS SERVICES, 2019. 3.PROPOSED REDEVELOPMENT PLAN BASED ON SITE PLAN PREPARED BY DESIGN RESOURCE GROUP DATED APRIL 21, 2022. 4.GROUNDWATER SAMPLES TMW-1 THROUGH TMW-6 COLLECTED BY H&H IN JANUARY 2021. GROUNDWATER SAMPLES TMW-7 THROUGH TMW-12 COLLECTED BY H&H ON JULY 20 & 21, 2023. 5.SOIL SAMPLES SB-1 THROUGH SB-13 COLLECTED BY H&H IN JANUARY 2021. SOIL SAMPLES CS-1 THROUGH CS-7 AND BG-1 THROUGH BG-3 COLLECTED BY H&H BETWEEN JULY 17 AND 19, 2023. 6.SOIL GAS SAMPLES SG-1 THROUGH SG-23 COLLECTED BY H&H ON JULY 20 AND 21, 2023. RESIDENTIAL RESIDENTIAL HIGHWAY 7 COOL JUNK (607 WEST 1ST STREET) LOWELL CHURCH OF GOD (800 WEST 1ST STREET) RAIL R O A D S T R E E T AS H S T R E E T PHI L L I P S S T R E E T CS-2 CS-3 CS-3C / SG-10 CS-3B / SG-9 CS-3A / SG-8 CS-2A / SG-5 CS-2B / SG-6 CS-2C / SG-7 CS-1C / SG-3 CS-1A / SG-1 CS-1B / SG-2 CS-1D / SG-4CS-1 CS-4A / SG-11 CS-4B / SG-12 CS-4D / SG-14 CS-4C / SG-13 CS-4 CS-7C / SG-23 CS-7B / SG-22 CS-7A / SG-21 CS-6C / SG-20 CS-6B / SG-19 CS-6A / SG-18 CS-5A / SG-15 CS-5B / SG-16 CS-5C / SG-17 CS-5 CS-6 CS-7 BUILDING A BUILDING B BUILDING C BUILDING A BUILDING B TMW-7 TMW-8 TMW-11 TMW-12 TMW-10 TMW-9 RESIDENTIAL MULTI-TENANT COMMERCIAL (510 WEST 1ST STREET) BIR C H S T R E E T FORMER DUKE POWER SUB-STATION FORMER MACHINE SHOP FORMER COAL TRESTLE BG-3 BG-2 BG-1 S: \ A A A - M a s t e r P r o j e c t s \ H e n l e y C a p i t a l L L C ( H N Y ) \ H N Y - 0 0 1 - L o w e l l , N C \ E M P \ F i g u r e s \ H N Y . 0 0 1 - 5 2 0 2 4 0 1 2 9 . d w g , F I G 3 , 1 / 2 9 / 2 0 2 4 7 : 3 9 : 1 8 A M , s h a y n e s SB-6 SB-5 SB-2 SB-3 SB-11 REVISION NO. 0 JOB NO. HNY-001 DATE: 2-8-24 FIGURE NO. 4 PHARR YARNS - LOWELL 700 WEST 1ST STREET LOWELL, NORTH CAROLINA SOIL IMPACTS ABOVE PSRGs LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL BOUNDARY RAILROAD PROPOSED BUILDING FOOTPRINT FORMER UNDERGROUND STORAGE TANK LOCATION (UST) VENT PIPE POLE-MOUNTED TRANSFORMER BACKGROUND SOIL BORING LOCATION SOIL BORING 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 WES T 1 S T S T R E E T NOR T H C L A Y S T R E E T POT T S S T R E E T NOTES: 1.PARCEL DATA OBTAINED FROM GASTON COUNTY GIS DEPARTMENT, 2022. 2.AERIAL IMAGERY OBTAINED FROM ESRI GIS SERVICES, 2019. 3.BOLD VALUES EXCEED THE RESIDENTIAL PSRG. BOLD AND UNDERLINED VALUES EXCEED THE INDUSTRIAL/COMMERCIAL PSRGs. 4.mg/kg = MILLIGRAMS PER KILOGRAM FT = FEET 5.J = LABORATORY ESTIMATED CONCENTRATION 6.PSRG = PRELIMINARY SOIL REMEDIATION GOAL RESIDENTIAL RESIDENTIAL HIGHWAY 7 COOL JUNK (607 WEST 1ST STREET) MULTI-TENANT COMMERCIAL (510 WEST 1ST STREET) LOWELL CHURCH OF GOD (800 WEST 1ST STREET) RAIL R O A D S T R E E T AS H S T R E E T PHI L L I P S S T R E E T BG-3 BG-2 BG-1 CS-3 CS-3C CS-3B CS-3A CS-2A CS-2B CS-2C CS-1C CS-1A CS-1B CS-1D CS-4A CS-4B CS-4D CS-4C CS-4 CS-7C CS-7B CS-7A CS-6C CS-6B CS-6A CS-5A CS-5B CS-5C CS-5 CS-6 CS-1 (0-2 FT)7/19/23 BENZO(A)ANTHRACENE 12.3 BENZO(A)PYRENE 9.14 BENZO(B)FLUORANTHENE 13.2 DIBENZO(A,H)ANTHRACENE 2.27 INDENO(1,2,3-CD)PYRENE 5.63 CONSTITUENT CONCENTRATION (mg/kg) SAMPLE ID & DATE CS-1 (0-2 FT)7/19/23 BENZO(A)ANTHRACENE 12.3 BENZO(A)PYRENE 9.14 BENZO(B)FLUORANTHENE 13.2 DIBENZO(A,H)ANTHRACENE 2.27 INDENO(1,2,3-CD)PYRENE 5.63 CS-1 CS-2/SB-DUP (0-2 FT)7/19/23 BENZO(A)ANTHRACENE 1.36; 1.32 BENZO(A)PYRENE 1.21; 1.15 BENZO(B)FLUORANTHENE 1.68; 1.52 DIBENZO(A,H)ANTHRACENE 0.27J; 0.256J CS-2 CS-7 (0-2 FT)7/18/23 BENZO(A)PYRENE 0.74 DIBENZO(A,H)ANTHRACENE 0.157 CS-7 COMPOUND RESIDENTIAL PSRG INDUSTRIAL/ COMMERCIAL PSRG BENZO(A)ANTHRACENE 1.1 21 BENZO(A)PYRENE 0.11 2.1 BENZO(B)FLUORANTHENE 1.1 21 DIBENZO(A,H)ANTHRACENE 0.11 2.1 INDENO(1,2,3-CD)PYRENE 1.1 21 SB-1 SB-4 SB-8 SB-10 SB-12 SB-13 BUILDING A BUILDING B BUILDING C BUILDING A BUILDING B SB-9 SB-7 BIR C H S T R E E T SB-5 (3-5 FT)1/11/21 BENZO(A)PYRENE 0.58J S: \ A A A - M a s t e r P r o j e c t s \ H e n l e y C a p i t a l L L C ( H N Y ) \ H N Y - 0 0 1 - L o w e l l , N C \ E M P \ F i g u r e s \ F I G 5 - 6 _ 2 0 2 4 0 2 0 8 . d w g , F I G 4 , 2 / 8 / 2 0 2 4 2 : 5 5 : 5 5 P M , d r a b u r n REVISION NO. 0 JOB NO. HNY-001 DATE: 2-8-24 FIGURE NO. 5 PHARR YARNS - LOWELL 700 WEST 1ST STREET LOWELL, NORTH CAROLINA GROUNDWATER IMPACTS ABOVE NC 2L STANDARDS LEGEND BROWNFIELDS PROPERTY BOUNDARY PARCEL BOUNDARY RAILROAD PROPOSED BUILDING FOOTPRINT TEMPORARY MONITORING WELL 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 WES T 1 S T S T R E E T NOR T H C L A Y S T R E E T POT T S S T R E E T NOTES: 1. PARCEL DATA OBTAINED FROM GASTON COUNTY GIS DEPARTMENT, 2022. 2. AERIAL IMAGERY OBTAINED FROM ESRI GIS SERVICES, 2019. 3.BOLD VALUES EXCEED THE 2L STANDARDS OR IMACs. 4. μg/L = MICROGRAMS PER LITER 5. J FLAG INDICATES AN ESTIMATED CONCENTRATION BETWEEN THE LABORATORY METHOD DETECTION LIMIT AND THE LABORATORY REPORTING LIMIT. RESIDENTIAL RESIDENTIAL HIGHWAY 7 COOL JUNK (607 WEST 1ST STREET) MULTI-TENANT COMMERCIAL (510 WEST 1ST STREET) LOWELL CHURCH OF GOD (800 WEST 1ST STREET) RAIL R O A D S T R E E T AS H S T R E E T PHI L L I P S S T R E E T TMW-8 TMW-7 TMW-10 TMW-9 TMW-12 TMW-11 TMW-5 TMW-4 TMW-3 TMW-2 TMW-6 TMW-1 TMW-2 1/12/21 TETRACHLOROETHYLENE 2,100 TRICHLOROETHYLENE 7.9CONSTITUENT CONCENTRATION (µg/L) SAMPLE ID & DATE COMPOUND NC 2L STANDARD CHLOROMETHANE 3 METHYLENE CHLORIDE 5 TETRACHLOROETHYLENE 0.7 TRICHLOROETHYLENE 3 TMW-2 1/12/21 TETRACHLOROETHYLENE 2,100 TRICHLOROETHYLENE 7.9 TMW-3 1/12/21 TETRACHLOROETHYLENE 6.6 TMW-4 1/12/21 TETRACHLOROETHYLENE 5.6 TMW-7/TMW-DUP 7/20/23 METHYLENE CHLORIDE <4.9; 5.3 J TETRACHLOROETHYLENE 307; 327 TMW-8 7/20/23 TETRACHLOROETHYLENE 71.8 TRICHLOROETHYLENE 6.1 TMW-9 7/20/23 CHLOROMETHANE 43.4 TMW-11 7/21/23 CHLOROMETHANE 57.6 BUILDING A BUILDING B BUILDING C BUILDING A BUILDING B BIR C H S T R E E T S: \ A A A - M a s t e r P r o j e c t s \ H e n l e y C a p i t a l L L C ( H N Y ) \ H N Y - 0 0 1 - L o w e l l , N C \ E M P \ F i g u r e s \ F I G 5 - 6 _ 2 0 2 4 0 2 0 8 . d w g , F I G 5 , 2 / 8 / 2 0 2 4 2 : 5 9 : 0 3 P M , d r a b u r n REVISION NO. 0 JOB NO. HNY-001 DATE: 1-29-24 FIGURE NO. 6 PHARR YARNS - LOWELL 700 WEST 1ST STREET LOWELL, NORTH CAROLINA VAPOR INTRUSION RISK LOCATION MAP LEGEND SITE PROPERTY BOUNDARY PARCEL BOUNDARY RAILROAD PROPOSED BUILDING FOOTPRINT 2923 South Tryon Street-Suite 100 Charlotte, North Carolina 28203 704-586-0007(p) 704-586-0373(f) License # C-1269 / #C-245 Geology WES T 1 S T S T R E E T NOR T H C L A Y S T R E E T BIR C H S T R E E T POT T S S T R E E T NOTES: 1.PARCEL DATA OBTAINED FROM GASTON COUNTY GIS DEPARTMENT, 2022. 2.AERIAL IMAGERY OBTAINED FROM ESRI GIS SERVICES, 2019. 3. VAPOR INTRUSION RISK CALCULATED USING THE DEQ RISK CALCULATOR (JULY 2023 VERSION). 4.LICR = LIFETIME INCREMENTAL CANCER RISK; HI = HAZARD INDEX 5. THE DEQ ACCEPTABLE LICR IS 1.0 X 10-4 OR LESS, AND THE DEQ ACCEPTABLE HI IS 1.0 OR LESS. BOLD VALUES EXCEED THE DEQ ACCEPTABLE RISK LEVEL. RESIDENTIAL RESIDENTIAL HIGHWAY 7 COOL JUNK (607 WEST 1ST STREET) MULTI-TENANT COMMERCIAL (510 WEST 1ST STREET) LOWELL CHURCH OF GOD (800 WEST 1ST STREET) RAIL R O A D S T R E E T AS H S T R E E T PHI L L I P S S T R E E T BUILDING A - SOUTH LICR (WORST-CASE RESIDENTIAL)1.2x10-5 NON-CARCINOGENIC HI (WORST-CASE RESIDENTIAL)0.18 LICR (WORST-CASE NON-RESIDENTIAL)9.2x10-7 NON-CARCINOGENIC HI (WORST-CASE NON-RESIDENTIAL)0.015 BUILDING B - SOUTH LICR (WORST-CASE RESIDENTIAL)1.5x10-5 NON-CARCINOGENIC HI (WORST-CASE RESIDENTIAL)5.8 LICR (WORST-CASE NON-RESIDENTIAL)1.1x10-6 NON-CARCINOGENIC HI (WORST-CASE NON-RESIDENTIAL)0.46 BUILDING A - NORTH LICR (WORST-CASE RESIDENTIAL)9.7x10-6 NON-CARCINOGENIC HI (WORST-CASE RESIDENTIAL)0.35 LICR (WORST-CASE NON-RESIDENTIAL)7.4x10-7 NON-CARCINOGENIC HI (WORST-CASE NON-RESIDENTIAL)0.028 BUILDING B - NORTH LICR (WORST-CASE RESIDENTIAL)1.0x10-5 NON-CARCINOGENIC HI (WORST-CASE RESIDENTIAL)0.66 LICR (WORST-CASE NON-RESIDENTIAL)7.7x10-7 NON-CARCINOGENIC HI (WORST-CASE NON-RESIDENTIAL)0.053 BUILDING C - NORTH LICR (WORST-CASE RESIDENTIAL)2.0x10-5 NON-CARCINOGENIC HI (WORST-CASE RESIDENTIAL)0.65 LICR (WORST-CASE NON-RESIDENTIAL)1.5x10-6 NON-CARCINOGENIC HI (WORST-CASE NON-RESIDENTIAL)0.052 S: \ A A A - M a s t e r P r o j e c t s \ H e n l e y C a p i t a l L L C ( H N Y ) \ H N Y - 0 0 1 - L o w e l l , N C \ E M P \ F i g u r e s \ H N Y . 0 0 1 - 5 2 0 2 4 0 1 2 9 _ D A T A . d w g , F I G 6 , 1 / 2 9 / 2 0 2 4 7 : 5 9 : 1 0 A M , s h a y n e s Appendix A Redevelopment Plan CL A Y S T R E E T RAILROAD STREET AS H S T R E E T FFE2.00 0.00 2.00-2.00 0.00 POTTS ST . 68' DUKE ROW PH I L L I P S T . POTTS ST . BI R C H S T . 68' DUKE ROW Copyright © 2023 Design Resource Group, PA This plan or drawing and any accompanying documents or calculations are the property of Design Resource Group, PA; and are intended solely for the use of the recipient noted. No third party use or modification is permitted without written authorization. SCALE: 1" = 80' PROJECT #: 607-008DRAWN BY:CHECKED BY: 80 PRELIMINARY SITE PLAN SHEET 1 APRIL 21, 2022 REVISIONS: LANDSCAPE ARCHITECTURECIVIL ENGINEERINGTRANSPORTATION PLANNING 2459 Wilkinson Blvd, Ste 200 Charlotte, NC 28208704.343.0608www.drgrp.com N040 LO W E L L 7 N O R T H & S O U T H LO W E L L , N O R T H C A R O L I N A LO W E L L O Z B , L L C 23 2 0 W E S T M O R E H E A D S T R E E T 2N D F L O O R CH A R L O T T E , N O R T H C A R O L I N A 2 8 2 0 8 OPW LOWELL 7 NORTHSITE DATAPARCEL #: 306362 (DB 4156, PG 304)PIN #: 3576102310ZONING : INDSITE AREATOTAL: 10.35 ACRES ASH STREET DEDICATION: 0.30 ACRESWITHIN DUKE EASEMENT: 1.09 ACRESNET AREA: 8.96 ACRES PROPOSED BUILDINGS:BUILDING A = 20,150 SF(2,500 OFFICE AND REMAINING WAREHOUSE) BUILDING B = 51,000 SFBUILDING C = 26,000 SFPROPOSED PARKING: TOTAL SPACES = 170 (STANDARD, ACCESSIBLE AND SPECIALTY TRUCK)TREE CONSERVATION AREA: NET SITE AREA: 8.96 ACRES = 3% (0.27 ACRES) LOWELL 7 SOUTH SITE DATAPARCEL #: 306363 and 127737PIN #: 3576007133 and 3575190862 ZONING : INDSITE AREATOTAL: 7.11 ACWITHIN RAILROAD ROW: 2.36 AC WITHIN DUKE ROW: 0.31 ACNET AREA: 4.44 ACPROPOSED BUILDINGS: BUILDING A = 18,200 SFBUILDING B = 35,000 SFPROPOSED PARKING: TOTAL SPACES = 113 (71 STANDARD, 8 ACCESSIBLE and 34 REAR)TREE CONSERVATION AREA: NET SITE AREA: 4.44 ACRES = 1.5% (0.07 ACRES) Appendix B Cut/Fill Analysis SCALE: 1" = 40' 20 0 N2040 BY: DATE: CUT:18,780 CY FILL:10,405 CY 12 IN 344,868 SF 7.92 ACRE 36 % 8,175 CY 4,598 CY TOP SOIL VOLUME 12,773 CY LIGHT DUTY PVMT 8 IN THICKNESS AREA:27,000 SF HEAVY DUTY PVMT 12 IN THICKNESS AREA: 100,000 SF BUILDING SLAB 8 IN THICKNESS AREA:96,000 SF SIDEWALK SLAB 4 IN THICKNESS AREA:12,000 SF 48 % 52 % 3,307 CY 3,582 CY 1343 CY CUT AVAILABLE:13,912 CY REQUIRED:11,421 CY 0%15% CUT GENERATED:13,912 CY FILL NEEDED:13,134 CY 2,121 CY 0.17 ft 11,430 CY 13,551 CY 1.06 ft This estimate does not account for the following: wall back fill, rock swell, building footings, etc. EARTHWORK RESULTS(INCLUDE TOPSOIL RESPREAD ONSITE): HAUL OFF REQ'D:Raise the site to balance EARTHWORK VOLUME ESTIMATE KK 07/20/23 APPROXIMATE % OF DENUDED AREA IN CUT: IMPERVIOUS AREA ADJUSTMENT Raise the site to balance STRIPPING ADJUSTMENT INCREASE VOLUME OF FILL REQUIRED BY PROJECT NAME: PROJECT NUMBER: ADJUSTED VOLUMES 607-008 North Site 607-008 APPROXIMATE % OF PVM'T/ BLDG AREA IN FILL: INCREASE VOLUME OF CUT AVAILABLE BY APPROXIMATE % OF PVM'T/ BLDG AREA IN CUT: DECREASE VOLUME OF FILL REQUIRED BY DENUDED AREA: UNADJUSTED VOLUMES APPROXIMATE % OF DENUDED AREA IN FILL: HAUL OFF REQ'D: TOPSOIL HAUL-OFF: DEPTH OF STRIPPING: DECREASE VOLUME OF CUT AVAILABLE BY SWELL FACTOR: EARTHWORK RESULTS(TOPSOIL NOT USED ONSITE): 4" OF TOPSOIL USED ON RESPREAD: SHRINKAGE FACTOR: SCALE: 1" = 50' BY:  DATE:  CUT:8,087 CY FILL:10,379 CY 8 IN 249,394 SF 5.73 ACRE 38 % 62 % 2,340 CY 3,818 CY TOP SOIL VOLUME 6,158 CY LIGHT DUTY PVMT 8 IN THICKNESS AREA:SF HEAVY DUTY PVMT 12 IN THICKNESS AREA:94,849 SF BUILDING SLAB 8 IN THICKNESS AREA:54,600 SF SIDEWALK SLAB 4 IN THICKNESS AREA:SF 0 % 100 % 0 CY 4,861 CY 1222 CY CUT AVAILABLE:5,747 CY REQUIRED:9,336 CY 0%15% CUT GENERATED:5,747 CY FILL NEEDED:10,736 CY 3,768 CY -0.41 ft OR 0 CY 0.00 ft Raise the site to balance 4,936 CY 0.13 ft This estimate does not account for the following: wall back fill, rock swell, building footings, etc. EARTHWORK VOLUME ESTIMATE Raise the site if all top soil is utilized JO 09/26/22 APPROXIMATE % OF DENUDED AREA IN CUT: IMPERVIOUS AREA ADJUSTMENT Lower the site to balance STRIPPING ADJUSTMENT INCREASE VOLUME OF FILL REQUIRED BY PROJECT NAME: PROJECT NUMBER: ADJUSTED VOLUMES LOWELL 607-008 APPROXIMATE % OF PVM'T/ BLDG AREA IN CUT: DECREASE VOLUME OF FILL REQUIRED BY APPROXIMATE % OF PVM'T/ BLDG AREA IN FILL: INCREASE VOLUME OF CUT AVAILABLE BY DENUDED AREA: UNADJUSTED VOLUMES TOPSOIL HAUL OFF AFTER RESPREAD : APPROXIMATE % OF DENUDED AREA IN FILL: BORROW REQ'D: HAUL OFF REQ'D: DEPTH OF STRIPPING: DECREASE VOLUME OF CUT AVAILABLE BY SWELL FACTOR: EARTHWORK RESULTS: 4" OF TOPSOIL USED ON RESPREAD: SHRINKAGE FACTOR: