HomeMy WebLinkAbout16017_Carolina Medical Electronics_EMP Final_2021Jul07#C-1269 Engineering
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Environmental Management Plan
Carolina Medical Electronics
Brownfields Project No. 16017-12-085
157 Industrial Drive
King, North Carolina
H&H Job No. DMM-001
Revised July 6, 2021
CONTENTS
Completed EMP Template Form
Figures
Figure 1 Site Location Map
Figure 2 Redevelopment Plan with Sampling Locations
Appendices
Appendix A Redevelopment Plan
Appendix B Grading Plan and Cut-Fill Analysis
Appendix C Historical Report Excerpts
Appendix D Grading Plan for Soil Borrow Source
Appendix E Historic Aerial Photographs for Soil Borrow Source
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NORTH CAROLINA BROWNFIELDS PROGRAM
ENVIRONMENTAL MANAGEMENT PLAN
This form is to be used to prepare an Environmental Management Plan (EMP) for projects in
the North Carolina Brownfields Program at the direction of a Brownfields project manager.
The EMP is a typical requirement of a Brownfields Agreement (BFA). Its purpose is to clarify
actions to be taken during the 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 resultant EMP to be valid for use, it
must be completed, reviewed by the program, 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 completed 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.
Voluntary Metrics Tab
The NC Brownfields Program 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: Approximately $3,500,000
(building only)
2. Estimated jobs created:
a. Construction Jobs: 150
b. Full Time Post-Redevelopment Jobs: 35
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Table of Contents
NORTH CAROLINA BROWNFIELDS PROGRAM ENVIRONMENTAL MANAGEMENT PLAN ........................... 1
GENERAL INFORMATION ........................................................................................................................ 4
COMMUNICATIONS ................................................................................................................................ 4
NOTIFICATIONS TO THE BROWNFIELDS PROGRAM ............................................................................... 5
REDEVELOPMENT PLANS ........................................................................................................................ 5
CONTAMINATED MEDIA ......................................................................................................................... 7
PART 1. Soil ......................................................................................................................................... 7
PART 2. GROUNDWATER ................................................................................................................. 19
PART 3. SURFACE WATER .................................................................................................................. 20
PART 4. SEDIMENT ............................................................................................................................ 21
PART 5. SOIL VAPOR ......................................................................................................................... 21
PART 6. SUB-SLAB SOIL VAPOR ........................................................................................................ 22
PART 7. INDOOR AIR ......................................................................................................................... 23
VAPOR INTRUSION MITIGATION SYSTEM ............................................................................................. 23
CONTINGENCY PLAN – encountering unknown tanks, drums, or other waste materials ..................... 24
POST-REDEVELOPMENT REPORTING..................................................................................................... 26
APPROVAL SIGNATURES ....................................................................................................................... 28
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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 these steps is premature.
☒ 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
on site 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 importation to the Brownfields Property.
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☐ A work plan for the sampling and analysis of soil to be brought onto the Brownfields
Property. Refer to Issue Resolution 15 in Brownfields Program Guidelines.
☐ A map of the Brownfields Property showing the location of soils proposed for export
and sampling data from those areas.
☒ If a Vapor Mitigation System is required by the Brownfields Program, the Vapor
Intrusion Mitigation System (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: 1/29/2021 Revision Date (if applicable): 7/6/2021
Brownfields Assigned Project Name: Carolina Medical Electronics
Brownfields Project Number: 16017-12-085
Brownfields Property Address: 157 Industrial Drive, King, NC (Figure 2)
Brownfields Property Area (acres): 6.24 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. NOTE, THE EMP
DOES NOT TAKE THE PLACE OF A SITE-SPECIFIC HEALTH AND SAFETY PLAN.
Prospective Developer (PD): Dynamic Real Estate Development, LLC (DRED)
Contact Person: Joseph H. Landry/ President
Phone Numbers: Office: (336) 362-2884 Mobile:
Email: joe.landry@dmxm.com
Contractor for PD: Triad Builders of King, NC
Contact Person: James Smith
Phone Numbers: Office: (336) 983-9400 x104 Mobile: (336) 978-6456
Email: jsmith@triadbuilders.com
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Environmental Consultant: Hart & Hickman, PC
Contact Person: Mr. Justin Ballard
Phone Numbers: Office: (919) 847-4241 Mobile: (252) 548-9191
Email: jballard@harthickman.com
Brownfields Program Project Manager: Mr. David Peacock
Phone Numbers: Office: (910) 796-7401 Mobile: (919) 280-3408
Email: david.peacock@ncdenr.gov
Other DEQ Program Contacts (if applicable, i.e., UST Section, Inactive Hazardous Site Branch,
Hazardous Waste, Solid Waste):
Ms. Jordan Thompson; jordan.thompson@ncdenr.gov; (704) 223-6549
NOTIFICATIONS TO THE BROWNFIELDS PROGRAM
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 ☐Recreational ☐Institutional ☐Commercial ☒Office ☐Retail ☒Industrial
☒Other specify:
Parking
2) Check the following activities that will be conducted prior to commencing earth-moving activities
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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:
Proposed redevelopment plans for the Brownfields property include construction of an
approximately 35,000 square foot (sq ft) industrial building with office space (Figure 3).
Remaining portions of the Site will be improved with utilities, parking, and asphalt access drives.
As part of grading activities, existing asphalt and concrete surfaces will be removed for off-Site
disposal. A copy of the current redevelopment Site plan is included in Appendix A, and a grading
plan is included in Appendix B.
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?
☒ Yes ☐ No ☐ Unknown
☒ If yes, please check here to confirm that demolition 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: 7/12/2021
b) Anticipated duration (specify activities during each phase):
Redevelopment activities are expected to take up to approximately ten months to complete.
A copy of the current construction schedule is included in Appendix C.
c) Additional phases planned? ☒ Yes ☐ No
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If yes, specify the start date and/or activities if known:
Start Date: Unknown
Planned Activity:
Proposed redevelopment plans could potentially include expansion of the new building by
approximately 12,000 sq ft (Figure 3).
Start Date: N/A
Planned Activity:
N/A
Start Date:
Planned Activity:
N/A
d) Provide the planned date of occupancy for new buildings: 3/1/2022
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
Part 4. Sediment:.……………...……..…………………… ☐ Yes ☒ No ☐ Suspected ☐ Unknown
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 release of tetrachlorethylene (PCE) was identified at the Brownfields property in 1996
following removal of two tanks associated with a former septic system (Figure 3). As part of
corrective action following removal of the tanks, soil was excavated from the tank areas and land
applied on an adjacent field. Sampling results of the excavated soil did not indicate evidence of
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impact according to an Environmental Response Actions: Carolina Medical report dated
December 1996.
Addition soil sampling in the holding tank excavation area was completed as part of assessment
activities document in a February 22, 2010 Comprehensive Site Assessment Report and a
September 13, 2010 Comprehensive Site Assessment Report Addendum prepared by Mineral
Springs Environmental, P.C.
During the assessments, PCE was detected in soil samples 1D-5 (estimated 0.0013 J milligrams
per kilogram [mg/kg]) and B-2 (0.0139 mg/kg) collected at approximately 5 feet below ground
surface (ft bgs) and at least 10 ft bgs, respectively. The PCE concentrations are below the July
2021 DEQ Industrial/Commercial Preliminary Soil Remediation Goal (PSRG) of 82 mg/kg. Other
than lab contaminants, no other volatile organic compounds (VOCs) were detected at
concentrations above laboratory method detection limits. Analyses for semi-VOCs (SVOCs)
and/or metals was not performed as part of the soil assessments. However, the PD proposes to
conduct additional soil sampling to determine Site-specific levels of naturally occurring metals
(see Imported Fill Section 1.B.) Excerpts from the 1996 and 2010 reports are included in
Appendix D.
2) Depth of known or suspected contaminants (feet):
5 to 15 ft bgs
3) Area of soil disturbed by redevelopment (square feet):
Based on the grading plan (Appendix B), approximately 153,000 sq ft (approximately 3.5 acres) is
expected to be disturbed during redevelopment activities.
4) Depths of soil to be excavated (feet):
Proposed grading activities are expected to include excavations of up to approximately 2 to 3 ft
bgs for installation of footers and utilities.
5) Estimated volume of soil (cubic yards) to be excavated (attach grading plan):
Up to approximately 7,500 cubic yards of soil are planned to be excavated and re-used on-Site as
beneficial fill during grading activities.
6) Estimated volume of excavated soil (cubic yards) anticipated to be impacted by contaminants:
Excavation of impacted soil is not anticipated based on results of soil sampling conducted in the
redevelopment area following excavation activities. See No. 1 above for additional information.
7) Estimated volume of contaminated soil expected to be disposed of offsite, if applicable:
Excavation of impacted soil is not anticipated.
Part 1.A. MANAGING ONSITE SOIL
If soil is anticipated to be excavated from the Brownfield Property, relocated on the Brownfields
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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:
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 ON SITE 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
☐ Reactivity
☐ Toxicity
☐ TCLP results
☐ 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:
Soil analytical data does not indicate detections capable of exceeding toxicity
characteristic leaching procedure (TCLP) criteria using the Rule of 20.
d) NOTE: IF SOIL MEETS THE DEFINITION OF A CHARACTERISTIC HAZARDOUS WASTE, THE
SOIL MAY NOT BE RE-USED ON SITE 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):
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☐ 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
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 on site map
to Brownfields Project Manager once known
☐ Geotextile to mark depth of fill material.
Provide description of material:
☐ Manage soil under impervious cap ☐ or clean fill ☐
☐ Describe cap or 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:
Management of fugitive dust from site
☒ Yes, describe the method will include:
During soil disturbance at the Site, the workers or contractors will observe soils for evidence of
potential impacted soil, such as a distinct unnatural color, strong odor, or filled or previously disposed
materials of concerns (i.e., 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 environmental professional will
contact the DEQ Brownfields project manager within two business days to advise that person of the
condition.
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The grading contractor will consider conditions such as wind speed, wind direction, and
moisture content of soil during grading and stockpiling (if warranted) activities to minimize
dust generation. In the unlikely event that contaminated soil is encountered during Site
redevelopment that requires excavation, particular attention will be paid by contractors to
implement dust control measures as needed based on Site and atmospheric conditions (i.e.,
by controlled water application, hydro-seeding, and/or mulch, stone, or plastic cover).
Potentially impacted soil will be managed as described below.
☐ No, explain rationale:
Field Screening of site soil
☒ Yes, 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 impacted soil, such as a distinct unnatural color, strong odor, or filled
or previously disposed materials of concerns (i.e., 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 environmental professional will contact the DEQ
Brownfields project manager within two business days to advise that person of the
condition.
☐ No, explain rationale:
Soil Sample Collection
☐ Yes, describe the sampling method (e.g., in-situ grab, composite, stockpile, etc.):
☒ No, explain rationale:
Collection of additional soil samples is not anticipated based on results of previous Site
assessment activities. If significant soil impact is encountered during grading and/or
installation or removal of utilities, excavation will proceed only as far as needed to allow
grading and/or construction of the utility to continue and/or only as far as needed to
allow alternate corrective measures described below. Suspect significantly impacted soil
excavated during grading and/or utility line installation or removal may be stockpiled and
covered in a secure area to allow construction to progress. Suspect impacted soil will be
underlain by and covered with minimum 10-mil plastic sheeting. At least one
representative sample of the soil will be collected for analysis of VOCs, SVOCs, and RCRA
metals. If the results of analysis of the sample 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
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waste criteria. Impacted soil will be handled in the manner described below based upon
the laboratory analyses:
i. If no organic compounds are detected in a sample (other than which are
attributable to sampling or laboratory artifacts]) and metals are below Residential PSRGs
or are consistent with Site-specific and/or published background ranges for North
Carolina soils, then the soil will be deemed suitable for use as on-Site fill or as off-Site fill.
The proposed location(s) for off-Site placement of soil (other than a permitted facility),
other applicable off-Site information (i.e., sampling results, if available), and 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 the DEQ IHSB
Industrial/Commercial PSRGs (other than which are attributable to sampling or laboratory
artifacts or which are consistent with Site-specific and/or published background ranges
for metals in North Carolina soils) 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 DEQ IHSB
Industrial/Commercial PSRGs (other than which are attributable to sampling or laboratory
artifacts or which are consistent with Site-specific and/or published background ranges
for metals in North Carolina soils) 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, or at least 2 ft of compacted clean soil. If the impacted soil
with concentrations above Residential PSRGs is moved to an on-Site location, its location
and depth will be documented, covered with a geotextile fabric so that its location can be
identified if encountered in the future, and its location will be provided to DEQ.
iv. Impacted soil may be transported to a permitted facility such as a Subtitle D, LCID,
and/or C&D landfill provided that the soil is accepted at the disposal facility and DEQ
approval to non-Subtitle D facilities. If soil is transported to a permitted facility, the
permitted facility’s written approval to dispose of soil from the Site will be included with
the final EMP report and/or the annual redevelopment summary 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 permitted disposal facility that can accept
or treat hazardous waste.
If soil samples are collected for analysis, please check the applicable chemical analytes:
☒ Volatile organic compounds (VOCs) by EPA Method 8260
☒ Semi-volatile organic compounds (SVOCs) by EPA Method 8270
☒ Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium
and silver): Specify Analytical Method Number(s): EPA Methods 6020/7471
☐ Pesticides: Specify Analytical Method Number(s):
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☐ PCBs: Specify Analytical Method Number(s):
☐ Other Constituents & Respective Analytical Method(s) (i.e. Hexavalent Chromium, Herbicides, etc.): Specify Analytical Method Number(s):
☒ 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:
☒ 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):
☒ Volatile organic compounds (VOCs) by EPA Method 8260
☒ Semi-volatile organic compounds (SVOCs) by EPA Method 8270
☒ Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium and silver): Specify Analytical Method Number(s): EPA Methods 6020/7471
☐ Pesticides: Specify Analytical Method Number(s):
☐ PCBs: Specify Analytical Method Number(s):
☒ Other Constituents & Respective Analytical Method(s) (i.e. Hexavalent Chromium, Herbicides, etc.):
Soil samples will be collected for hexavalent chromium and put on hold for
potential analysis by EPA Method 7199. The laboratory will be directed to hold
all hexavalent chromium analyses pending the results of the total chromium
analyses. If total chromium is detected in any of the soil samples above the
current hexavalent chromium Industrial/Commercial PSRG, the sample
exhibiting the highest total chromium concentration will be analyzed for
hexavalent chromium. If hexavalent chromium is detected in that sample above
the current hexavalent chromium Industrial/Commercial PSRG, the remaining
soil samples may be analyzed for hexavalent chromium subject to approval by
DEQ Brownfields.
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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.
☐ If final grade sampling was NOT selected, please explain rationale:
Following completion of soil disturbance for any discrete future Site development (i.e.,
after grading and utility construction), an environmental professional will be contracted to
assess the development area for areas that are not covered with a minimum of 2 ft of
clean fill soil or topsoil, building foundations, sidewalks, asphalt or concrete parking areas,
driveways or other impervious surfaces. If such areas exist, a Work Plan will be prepared
for final grade sampling for DEQ review and approval. If no such areas exist,
documentation will be provided to DEQ.
Part 1.B. IMPORTED FILL SOIL
NO SOIL MAY BE BROUGHT ONTO THE BROWNFIELDS PROPERTY WITHOUT PRIOR APPROVAL
FROM THE BROWNFIELDS PROGRAM. 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 Program), 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:
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 15,000 cy of soil will be imported to the Site to reach final proposed grades.
3) If yes, what is the anticipated depth that fill soil will be placed at the property? (If a range
of depths, please list the range.)
Fill soils are planned to be placed at the Site in select locations at depths up to approximately 12
feet. A copy of the grading plan, which indicates areas of fill, is included in Appendix B.
4) Provide the source of fill, including: location, site history, nearby environmental concerns,
etc. Attach aerial photos, maps, historic Sanborn maps and a borrow source site history:
Approximately 15,000 cy of soil is proposed for import to the Site from an undeveloped property
located south of Peachtree Lane in King, Stokes County, NC. The approximately 4.25-acre parcel
(Stokes County Parcel No. 6901391053.000) is owned by Merritt Land Company LLC (Merritt).
According to a representative of Merritt, the property has been vacant wooded land for at least
approximately 40 years. Recently, the land was cleared of vegetation in anticipation of future
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residential development, which is consistent with the surrounding properties. A proposed
grading plan is included in Appendix E.
For import to the Site, the borrow source property owner indicated that soil will be excavated and
direct-loaded onto trucks for export to the Brownfields property. Copies of aerial photographs
dating back to 1998 are included in Appendix F.
5) PRIOR TO ITS PLACEMENT AT THE BROWNFIELDS PROPERTY, provide a plan to analyze fill
soil to demonstrate that it meets acceptable standards applicable to the site and can be
approved for use at the Brownfields property.
See No. 7 below for details outlining the proposed plan to demonstrate import soil (not topsoil)
meets acceptable standards to the Site.
6) Please check the applicable chemical analytes for fill soil samples. (Check all that apply):
☒ Volatile organic compounds (VOCs) by EPA Method 8260
☒ Semi-volatile organic compounds (SVOCs) by EPA Method 8270
☒ Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium and silver): Specify Analytical Method Number(s): EPA Methods 6020/7471
☐ Pesticides: Specify Analytical Method Number(s):
☐ PCBs: Specify Analytical Method Number(s):
☒ Other Constituents & Respective Analytical Method(s) (i.e. Hexavalent Chromium, Herbicides, etc.): Hexavalent Chromium by EPA Method 7199
7) The scope of work for import fill sampling may be provided below or in a Work Plan
submitted separately for DEQ review and approval. Attach specific location maps for in-situ
borrow sites. If using a quarry, provide information on the type of material to be brought
onto the Brownfields Property.
The PD plans to import virgin fill material from the off-Site borrow source property referenced
above. The borrow source is not a permitted quarry, and is not recycled material from a DEQ
Brownfields pre-approved borrow source. The borrow source will be sampled in general
accordance with the most recent versions of the U.S. Environmental Protection Agency (EPA)
Region IV Science and Ecosystem Support Division (SESD) Field Branches Quality System and
Technical Procedures guidance. The PD will follow the procedures outlined below to demonstrate
import soil meets acceptable criteria for Site use.
Soil samples will be collected from the borrow source for laboratory analysis at a general rate of
approximately one sample per 1,000 cy for the first approximately 5,000 cy, and then
approximately one sample per 5,000 cy for the balance (7 total samples). A proposed grading
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plan with proposed soil sample locations is included in Appendix E. Specifically, composite soil
samples will be collected using a decontaminated hand auger. Each composite sample will be
comprised of soil from four grab sample locations (i.e., aliquots) at depths of up to proposed cut
(to be determined in the field with the borrow source property owner, but not expected to
exceed approximately 5 ft bgs) that are combined to form one sample for laboratory analysis.
Continuous soil samples will be collected from the center of the hand auger bucket at each boring
and logged for lithological description and field screened for indication of potential impacts by
observation for staining, unusual odors, and the presence of volatile organic vapors using a
calibrated photoionization detector (PID). VOC samples will be collected as grab samples using a
decontaminated stainless-steel hand auger from the general area of the aliquot which exhibits the
highest indication of impact during field screening.
The soil samples will be placed in dedicated laboratory-supplied sample containers, covered with
ice, and shipped to a North Carolina-certified laboratory under standard chain of custody
protocols for laboratory analysis of VOCs by EPA Method 8260, SVOCs by EPA Method 8270 and
RCRA metals plus hexavalent chromium by EPA Methods 6020/7471/7199. H&H will request a
Level II QA/QC data package from the laboratory and the laboratory will report values to the
laboratory-specified method detection limits using J-flags. To evaluate the reproducibility of the
sample results, H&H will collect one duplicate soil sample, which will be submitted for the same
laboratory analysis as their respective parent sample.
Following sampling activities, the soil borings will be properly abandoned by placing soil cuttings
back in their respective boreholes. The surface will then be repaired similar to pre-sampling
conditions. Additionally, the soil sample locations will be estimated using a hand-held Global
Positioning System (GPS) unit.
Fill soil will be considered suitable for use at the Site if it does not contain compound
concentrations above the lowest DEQ PSRGs (for compounds not known to exist at the
Brownfields property), DEQ Industrial/Commercial PSRGs (for compounds present in soil at the
Brownfields property), DWM Risk Calculator risk thresholds, and/or typical metals concentrations
which are consistent with Site-specific and/or published background ranges for metals in regional
soils. To determine Site-specific background ranged for metals, two soil samples will be collected
from the Brownfields property for laboratory analysis of RCRA metals plus hexavalent chromium
by EPA Methods 6020/7471/7199. The background soil samples will be collected as grab samples
from approximately 3 ft bgs using the aforementioned sampling methodologies. Proposed
background soil sample locations are identified in Figure 3.
DEQ approval of the import soil analytical results will be obtained prior to exporting soil to the
Brownfields property.
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Part 1.C. EXPORTED SOIL
NO SOIL MAY LEAVE THE BROWNFIELDS PROPERTY WITHOUT APPROVAL FROM THE
BROWNFIELDS PROGRAM. FAILURE TO OBTAIN APPROVAL MAY VIOLATE A BROWNFIELDS
AGREEMENT CAUSING A REOPENER OR JEOPARDIZING ELIGIBILITY IN THE PROGRAM,
ENDANGERING LIABILITY PROTECTIONS AND MAKING SAID ACTION POSSIBLY SUBJECT TO
ENFORCEMENT. JUSTIFICATIONS PROVIDED BELOW MUST BE APPROVED BY THE PROGRAM IN
WRITING PRIOR TO COMPLETING TRANSPORT ACTIVITIES. Please refer to Brownfields IR 15 for
additional details.
1) If export from a Brownfields Property is anticipated, please provide details regarding the
proposed export actions. Volume of exported soil, depths, location from which soil will
be excavated on site, related sampling results, etc. Provide a site map with locations of
export and sampling results included.
Export soil is not anticipated at this time. Should soil need to be exported from the Brownfields
property during redevelopment, soil will be sampled in general accordance with the most recent
versions of the EPA Region IV SESD Field Branches Quality System and Technical Procedures
guidance.
Samples will be collected from export soil at a rate of one (1) sample per every approximately
1,000 cy of export for laboratory analysis of VOCs by EPA Method 8260, SVOCs by EPA Method
8270, and RCRA metals plus hexavalent chromium by EPA Methods 6020/7471/7199. SVOCs and
metals will be collected as composite samples using a decontaminated stainless-steel hand
auger. Soil samples will also be collected for hexavalent chromium and placed on hold for
potential analysis by EPA Method 7199. The laboratory will be directed to hold all hexavalent
chromium analyses pending the results of the total chromium analyses. If total chromium is
detected in any of the soil samples above the current hexavalent chromium Residential PSRG,
the sample exhibiting the highest total chromium concentration will be analyzed for hexavalent
chromium. If hexavalent chromium is detected in that sample above the current hexavalent
chromium Residential PSRG, the remaining soil samples may be analyzed for hexavalent
chromium subject to approval by DEQ Brownfields.
The composite samples will consist of three sample aliquots that are combined to form one
sample for laboratory analysis. Each aliquot will be field screened for the presence of VOCs using
a calibrated PID. VOC samples will be collected as grab samples using a decontaminated
stainless-steel hand auger from the general area of the aliquot which exhibits the highest
indication of impact during field screening. The soil samples will be placed in dedicated
laboratory-supplied sample containers, covered with ice, and shipped to a North Carolina-
certified laboratory under standard chain of custody protocols.
DEQ approval of the analytical results will be obtained prior to transporting export soil from the
Site. Based on analytical results of soil samples collected from the export soil, the soil will be
transported off-Site to a suitable location. The PD will notify DEQ Brownfields of the location
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receiving the export soil. If not a Subtitle D permitted facility, DEQ Brownfields approval and
written approval from the receiving facility will be obtained prior to transporting the soil off-Site.
2) To what type of facility will the export Brownfields soil be sent?
☒ Subtitle D/Municipal Solid Waste Landfill (analytical program to be determined by
landfill)
☒ Permitted but Unlined Landfill (i.e. LCID, C&D, etc.) Analytical program to be
determined by the accepting Landfill;
☒ Landfarm or other treatment facility
☒ Use as fill at another suitable Brownfields Property – determination that a
site is suitable will require, at a minimum, that similar concentrations of the same or
similar contaminants already exist at both sites, use of impacted soil will not increase
the potential for risk to human health and the environment at the receiving Brownfields
property, and that a record of the acceptance of such soil from the property owner of
the receiving site is provided to Brownfields. Please provide additional details below.
☒ Use as Beneficial Fill off-site at a non-Brownfields Property - Please provide
documentation of approval from the property owner for receipt of fill material. This will
also require approval by the DEQ Solid Waste Section. Additional information is
provided in IR 15. Please provide additional details below.
3) Additional Details: (if transfer of soil to another property is requested above, please provide
details related to the proposed plans).
The environmental professional will contact DEQ Brownfields to obtain DEQ Brownfields and
DEQ Solid Waste approval prior to exporting soil to a non-Brownfields property.
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:
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☐ If no, include rationale here:
☒ Unknown, details to be provided in the Vapor Mitigation Plan for site buildings
Other comments regarding managing impacted soil in utility trenches:
Results of soil assessment activities indicated that VOC concentrations do not exceed
Industrial/Commercial PSRGs. Although not anticipated, in the event contaminated soil and/or vapors
(based on unusual odors) are 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. If results indicate further action is warranted in response to vapors to protect workers,
appropriate engineering controls (such as use of industrial fans) will be implemented.
The contractor and workers will observe soil for potential impacts during utility installation activities.
Evidence of potential impacted soil includes a distinct unnatural color, strong odor, or filled or
previously disposed materials of concerns (i.e., chemicals, tanks, drums, etc.). Should the above be
noted during utility 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 outlined Managing On-Site Soil above will be implemented. In
addition, the environmental professional will contact the DEQ Brownfields project manager within
two business days to advise that person of the condition.
PART 2. GROUNDWATER
1) What is the depth to groundwater at the Brownfields Property?
Based upon groundwater assessment activities conducted by MSE in 2010, depth to
groundwater on the Brownfields property was measured from approximately 47 to 55 ft bgs.
2) Is groundwater known to be contaminated by ☒onsite ☐offsite ☐both or ☐unknown
sources? Describe source(s):
Groundwater assessment activities conducted at the Brownfields property have identified PCE at
concentrations (up to 660 micrograms per liter [ug/L]) above the DEQ 2L Groundwater Quality
Standard (2L Standard).
3) What is the direction of groundwater flow at the Brownfields Property?
Area topography and previous investigations suggest that groundwater flow is likely towards the
northwest towards Crooked Run Creek.
4) Will groundwater likely be encountered during planned redevelopment activities?
☐Yes ☒No
If yes, describe these activities:
Groundwater is not expected to be encountered during redevelopment activities. However, if
groundwater is encountered, the PD or the PD’s contractor will contact the project
environmental professional. The environmental professional will update the DEQ Brownfields
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project manager within two business days. Regardless of the answer; in the event that contaminated 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).
Although not anticipated at this time, appropriate worker safety measures will be undertaken if
groundwater gathers in an open excavation within an area determined to be impacted during
construction activities. The accumulated water will be allowed to evaporate, tested 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.
5) 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
6) 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 Program’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.
7) Please provide additional details as needed:
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 ☐ Unknown
According to a previously DEQ-approved EMP dated January 29, 2021, the Brownfields Program has
granted preliminary approval to abandon monitoring wells located in the proposed area of
disturbance that hinder construction and grading activities. Monitoring wells located outside of the
area of disturbance will be marked and protected.
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2) 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
4) Will workers or the public be in contact with surface water during planned redevelopment
activities? ☐ 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):
If surface water run-off gathers in an open excavation within an area determined to be impacted
during construction activities, appropriate worker safety measures will be undertaken. The
accumulated water will be allowed to evaporate/infiltrate to the extent time for dissipation does
not disrupt the construction schedule. Should the time be needed for natural dissipation of
accumulated water be deemed inadequate, the water will be tested 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 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 following vapor intrusion screening levels (current version) in the following media:
IHSB Residential Screening Levels:
Soil Vapor:………..☐ Yes ☐ No ☒ Unknown
Groundwater:.….☒ Yes ☐ No ☐ Unknown
IHSB Industrial/Commercial Screening Levels:
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Soil Vapor:………..☐ Yes ☐ No ☒ Unknown
Groundwater:…..☒ Yes ☐ No ☐ Unknown
2) Attach a map showing the locations of soil vapor contaminants that exceed site
screening levels.
3) If applicable, at what depth(s) is soil vapor known to be contaminated?
4) Will workers encounter contaminated soil vapor during planned redevelopment activities?
☐ Yes ☐ No ☒ Unknown In the event that contaminated soil vapor is encountered during
redevelopment activities (trenches, manways, basements or other subsurface work,) list
activities for management of such contact:
In the unlikely event impacted soil vapors (based on unusual odors) are encountered during
future redevelopment activities, worker breathing zone will be monitored using a calibrated PID.
If results indicate further action is warranted, appropriate engineering controls (such as use of
industrial fans) will be implemented.
PART 6. SUB-SLAB SOIL VAPOR
1) Do concentrations of volatile organic compounds at the Brownfields property exceed the
following vapor intrusion screening levels (current version) in sub-slab soil vapor:
IHSB Residential Screening Levels:
Soil Vapor:………..☒ Yes ☐ No ☐ Unknown
Groundwater:.….☒ Yes ☐ No ☐ Unknown
IHSB Industrial/Commercial Screening Levels:
Soil Vapor:………..☒ Yes ☐ No ☐ Unknown
2) Groundwater:…..☒ Yes ☐ No ☐ Unknown If data indicate that sub-slab soil vapor
concentrations exceed screening levels, attach a map showing the location of these exceedances.
3) At what depth(s) is sub-slab soil vapor known to be contaminated? ☒0-6 inches ☐Other, please
describe:
4) Will workers encounter contaminated sub-slab soil vapor during planned redevelopment
activities? ☐ Yes ☐ No ☒ Unknown
☐ If no, include rationale here:
5) In the event that contaminated soil vapor is encountered during redevelopment activities, list
activities for management of such contact
In the unlikely event impacted soil vapors are encountered during future redevelopment
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activities, worker breathing zone will be monitored using a calibrated PID. If results indicate
further action is warranted, appropriate engineering controls (such as use of industrial fans) will
be implemented.
PART 7. INDOOR AIR
1) Are indoor air data available for the Brownfields Property? ☒ Yes ☐ No ☐ Unknown
2) 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
☐ 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
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:
If yes, ☐ VIMS Plan Attached or ☒ VIMS Plan to be submitted separately
If submitted separately provide date:
VIMS details will be provided to DEQ Brownfields under separate cover.
In the unlikely event there is evidence of potential indoor air issues (i.e., unusual odors) 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 photoionization detector and calibrated
methane gas detector. If results indicate further action is warranted, appropriate engineering
controls (such as use of industrial fans) will be implemented.
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VIMS Plan shall be signed and sealed by a NC Professional Engineer If no, please provide a brief rationale as to why no vapor mitigation plan is warranted:
Note that approval of this EMP does not imply approval with any vapor intrusion mitigation land
use restrictions or requirements of the recorded or draft Brownfields Agreement and that
separate approval of mitigation measures will be required.
CONTINGENCY PLAN – encountering unknown tanks, drums, or other waste materials
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:
☒ Volatile organic compounds (VOCs) by EPA Method 8260
☒ Semi-volatile organic compounds (SVOCs) by EPA Method 8270
☒ Metals RCRA List (8) (arsenic, barium, cadmium, chromium, mercury, lead, selenium and
silver)
EPA Method 6020 and EPA Method 7471
☐ Pesticides: Specify Analytical Method Number(s):
☐ PCBs: Specify Analytical Method Number(s):
☒ Other Constituents & Analytical Method(s) (i.e. Hexavalent Chromium, Herbicides, etc.)
Please note, if field observations indicate the need for additional analyses, they should
be conducted, even if not listed here.
Hexavalent Chromium by EPA Method 7196 Please provide details on the proposed methods of managing the following commonly
encountered issues during redevelopment of Brownfields Properties.
During construction activities, contractors may encounter unknown sub-surface environmental
conditions (i.e., tanks, drums, or waste materials) that if encountered, will require proper
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management. Prior to beginning Site work, H&H will attend a pre-construction meeting with the PD
and the redevelopment contractors to discuss the DEQ approved EMP and various scenarios when it
would be appropriate and necessary to notify H&H of the discovery of unknown subsurface features
or potentially impacted media at the Site.
In the event that such conditions are encountered during Site development activities, the
environmental actions noted below will be used to direct environmental actions to be taken during
these activities and sampling data for potentially impacted soil and the disposition of impacted soil
will be provided to DEQ when the data becomes available.
Underground Storage Tanks:
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 Program.
If a UST is encountered, the UST will be removed and transported off-Site for disposal at a suitable
facility. If the UST contains residual fluids, the fluids will be sampled for VOCs, SVOCs, and RCRA
metals, and transported off-Site for disposal at a suitable facility based on the laboratory analytical
results prior to removing the UST from the ground. If a UST is encountered outside of the new
building footprint that cannot be removed or does not require removal for geotechnical or
construction purposes, with DEQ prior approval it will be abandoned in-place and construction will
proceed. Impacted soil in the vicinity of the UST will be managed in accordance with the Managing
On-Site Soil section outlined above in the EMP. If a UST will be left in-place, DEQ Brownfields will be
notified.
Sub-Grade Feature/Pit:
If a sub-grade feature or pit is encountered outside of the new building footprint 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 will 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 section outlined above in the EMP, 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, 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 Program must be notified to determine if investigation of
landfill gases is required:
If excavation into buried wastes or impacted soils occurs, the contractor is instructed to stop work
in that location and notify the environmental consultant. The environmental consultant will review
the materials, discuss with DEQ Brownfields, and collect samples if warranted. In this event,
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confirmation sampling will be conducted at representative locations in the base and the sidewalls of
the excavation after the waste or impacted soil is removed. The confirmation samples will be
analyzed for VOCs, SVOCs, and RCRA metals. Areas of suspected contaminated soil that remain at
the Site after excavation is complete above the DEQ IHSB Industrial/Commercial PSRGs will be
managed pursuant to this plan.
Re-Use of Impacted Soils On-Site:
Please refer to description outlined in the Managing On-Site Soil section of the EMP above.
If unknown, impacted soil is identified on-site, management on-site 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 on-site.
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 1/31/2022
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).
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☒ 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.
July 7, 2021
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USGS The National Map: National Boundaries Dataset, 3DEP ElevationProgram, Geographic Names Information System, National HydrographyDataset, National Land Cover Database, National Structures Dataset,and National Transportation Dataset; USGS Global Ecosystems; U.S.Census Bureau TIGER/Line data; USFS Road Data; Natural Earth Data;U.S. Department of State Humanitarian Information Unit; and NOAANational Centers for Environmental Information, U.S. Coastal ReliefModel. Data refreshed May, 2020.
SITE LOCATION MAP
CAROLINA MEDICAL ELECTRONICS157 INDUSTRIAL DRIVEKING, NORTH CAROLINA
DATE: 5-25-21
JOB NO: DMM-001
REVISION NO: 0
FIGURE NO: 2
2923 South Tryon Street - Suite 100Charlotte, North Carolina 28203704-586-0007 (p) 704-586-0373 (f)License # C-1269 / # C-245 Geology
TITLE
PROJECT
0 2,000 4,000
SCALE IN FEET
SITE
Path: S:\AAA-Master Projects\Dynamic Machining x Manufacturing (DMM)\Drawings\Figure-1.mxdN
U.S.G.S. QUADRANGLE MAP
PINNACLE, NORTH CAROLINA 2019KING, NORTH CAROLINA 2019
QUADRANGLE7.5 MINUTE SERIES (TOPOGRAPHIC)
US H
IGHW
AY
5
2
INDU
STR
I
A
L
DR
I
VE
SG-1
SG-2
SG-3
MW-1
MW-1D/1D-5
MW-2
MW-3
MW-4
MW-6
MW-8
MW-7
MW-5
MW-9
MW-10
B-1
B-2
B-4
B-3
REVISION NO. 0
JOB NO. DMM-001
REDEVELOPMENT PLAN WITH
SAMPLING LOCATIONS
3921 Sunset Ridge Road, Suite 301Raleigh, North Carolina 27607919-847-4241(p) 919-847-4261(f)
License # C-1269 / #C-245 Geology
NOTES:
1. AERIAL IMAGERY OBTAINED FROM NC ONEMAP
SERVICES (2018).
2. SUBJECT PARCEL DATA OBTAINED FROM SURVEY PLAT
DATED 5/24/2012. OTHER BASE DATA OBTAINED FROM
STOKES COUNTY GIS (2018).
3. SOIL BORING AND MONITORING WELL LOCATIONS
APPROXIMATED FROM FIGURES INCLUDED IN MINERAL
SPRINGS ENVIRONMENTAL, P.C.'S FEBRUARY 22, 2010
COMPREHENSIVE SITE ASSESSMENT REPORT AND
SEPTEMBER 13, 2010 COMPREHENSIVE SITE
ASSESSMENT REPORT ADDENDUM.
4. SUB-SLAB VAPOR SAMPLE LOCATIONS APPROXIMATED
FROM FIGURES INCLUDED IN BY ECS CAROLINAS, LLP'S
APRIL 26, 2012 REPORT OF SUB-SLAB GAS SAMPLING.
DATE: 6-30-21
FIGURE NO. 3
CAROLINA MEDICAL ELECTRONICS
157 INDUSTRIAL DRIVE
KINGS, NORTH CAROLINA
LEGEND
SITE PROPERTY BOUNDARY
PARCEL LINE
FUTURE BUILDING
MONITORING WELL LOCATION
DEEP MONITORING WELL LOCATION
SOIL BORING LOCATION
SUB-SLAB VAPOR SAMPLE LOCATION
PROPOSED BACKGROUND SOIL
SAMPLE LOCATION
FORMER 100-GALLON
HOLDING TANK
FORMER 200-GALLON
SEPTIC TANK
POTENTIAL FUTURE EXPANSION AREA - NOT
PART OF CURRENT REDEVELOPMENT PLANS
M:\AAA_DRAFTING\DMM\DMM-001\Figures_20210630.dwg, FIG3, 7/1/2021 9:26:58 AM, shaynes
Appendix A
Redevelopment Plans
40% DESIGNDEVELOPMENT setNOT forconstructionPLAN -
40% DESIGNDEVELOPMENT setNOT forconstructionPLAN -
40% DESIGNDEVELOPMENT setNOT forconstructionPLAN -
40% DESIGNDEVELOPMENT setNOT forconstructionPLAN -
Appendix B
Grading Plan
1" BENT IRON PIPEWITNESSED BY TALL 5/8"REBARIRON FOUNDDRIVEN IRON FOUND; 5/8"IRON REBAR FOUNDS29°10'03"E, 0.35' FROM IRON1" IRON PIPEFOUND3/4" IRON PIPE FOUND;WITNESSED BY 3/4" LAIDOVER IRON PIPE1" BENT IRON PIPE FOUND;WITNESSED BY NAIL SET ATBASE OF 6" WILD CHERRYSNAG1085108
0
10751070
1085108020' BUILDING SETBACKPIPE END NOT FOUND(shown for direction)4" PVC TOP= 1085.03'INV. IN=UNKNOWNCATCH BASIN TOP=1080.75'15" RCP INV. IN=1079.13'15" RCP INV. OUT=1079.04'CATCH BASIN TOP=1080.79'15" RCP INV. IN=1079.20'15" RCP INV. OUT=1078.96'12" HDPEINV. IN=1063.64'INV. OUT=1061.73'18" RCP INV.OUT=1078.13'1085EIP - EXISTING IRON FOUNDNIP - NEW IRON PIPE PLACEDPT. - POINT NOT SETNOTESRECORD REFERENCESLEGEND1. THIS MAP IS OF A CURRENT FIELD SURVEY ANDIS ORIENTED TO NC GRID (NAD 83) 2011.2. ALL MEASUREMENTS ARE HORIZONTALSURFACE MEASUREMENTS.3. THIS PROPERTY IS LOCATED IN FLOOD ZONE XAS SHOWN ON FLOOD MAP# 3710599100K, PANEL#5991 WITH AN EFFECTIVE DATE OF 1-2-2009.4. THIS SURVEY IS OF EXISTING PARCELS OWNEDBY DYNAMIC REAL ESTATE DEVELOPMENT LLC5. THIS PROPERTY IS SUBJECT TO BROWNFIELDSAGREEMENT RECORDED IN PB 11 PG 197. PLATRECORDED IN PB 11 PG 196 & 197. MONITORINGWELLS ARE FIELD LOCATED LOCATIONS ANDSCALED MAPPING LOCATIONS OF MONITORINGWELLS FROM THE BROWNFIELDS PLAT.DYNAMIC REAL ESTATEDEVELOPMENT LLCPO BOX 429KING, NC 27021OWNER/DEVELOPERPP. - POWER POLEOVERHEAD ELECTRIC WIRESZone: L-IFront: 30'Side: 15'Rear: 20'Height: 50'Required minimum lot size: 20,000 sq ftSITE DATAPROPERTY LINESRIGHT-OF-WAY LINESMINIMUM BUILDING SETBACK LINES60D CONTROLN:919224.047E:1595217.784Elevation:1080.570Conv.:-0.79247778Point Scale:1.0000298360D CONTROLN:918753.704E:1595525.625Elevation:1082.65Conv.:-0.79186111Point Scale:1.00002943MONITORING WELL LOCATED OR SCALED FROM PB 11 PG 196MINOR (1') CONTOURMAJOR (5') CONTOUR1/2" IRON PIPE FOUNDON LINE @ 300.03'RAILROAD SPIKEFOUND INPAVEMENT10831085OVERHEAD ELECTRIC EASEMENTNO CATCH BASIN4" PVC INV. IN.=1079.52'15" RCP INV. IN=1078.89'18" RCP INV. OUT=1078.32'UNDERGROUND ELECTRIC LINEUNDERGROUND COMMUNICATION LINE108810871086108
4
108310
8
3
108210811
0
7
9
1
0
7
8
1
0
7
7
1
0
7
6
1074
1073
10721071106910691066
1079
1079
1078
10821
0
8
4
108410831085
10
8
5
10
8
6
10
8
7
108810881087108610841083108210811062
1077PROPOSED MAJOR (1') CONTOURPROPOSED MINOR (5') CONTOUR10851083PROPOSED 12" HDPE 30 L.F.INV. IN = 1078.5'INV. OUT = 1078.0'Catch Basin #1Top Grate = 1081.5'12" HDPE out = 1078.5'Catch Basin #2Top Grate=1081.5'12" Inv. In = 1076.812" Inv. out = 1076.7'PROPOSED 12"INV. OUT=1068.0'SKIMMER BASIN #1Size @ bottom = 2400 SFDisturbed Area = 2.64 AcresSurface Area Req. = 4028 SFSurface Area Provided @ 1069 = 4400 SFVolume Req. = 4752 cu ft (176 cu yd)Volume Provided = 6805 cu ftTop Dam Elev. = 1070.0Bottom Basin Elev. = 1067.0Riser Outlet with SkimmerSkimmer Inv. In = 1067.0Top Riser = 1069.0Inv Outlet Pipe = 1065.0UNDERGROUND WATER LINE10701075 106810691071107210731074 106510641064Catch Basin #3Top Grate=1080.512" Inv. In = 1074.412" Inv. out = 1074.35Proposed Sewer ManholeInstalled by CityTop Rim = 1076.0Invert = 1073.0N = 918,935.28E = 1,594,907.86Sewer @ 1077.0±1084
1082 108210
8
2
10
8
1
1080 107910821082
1
0
8
5
1083
108210811080108010751070108010671070107010801075
10821085PROPOSED 12" HDPE, 106 L.F.INV. IN = 1078.5'INV. OUT = 1076.8'PROPOSED 12" HDPE, 134 L.F.INV. IN = 1076.8'INV. OUT = 1074.4'PROPOSED 12" HDPE, 208 L.F.INV. IN = 1074.4INV. OUT = 1068.0RIP-RAP SLOPEPROTECTIONSCHEMATIC SITE PLANforDYNAMIC MACHINING
CITY OF KINGSTOKES COUNTY, NORTH CAROLINA
Appendix C Construction Schedule
Cr
ea DM2 Design Build
EntTraid Builders of King Inc.
EntJames Smith
Th
e 1
Ce
Th
is TASK ASSIGNED
TO PROGRESS START END
Ce
ll Mobilization and Erosion Control
Ce
ll Mobilize equipment, materials and temp items 0% 7/12/21 7/13/21
R
o Install erosion control 0% 7/14/21 7/22/21
Th
e Grading, Utilities, and Storm Drainage
Grading 0% 7/22/21 9/6/21
Utilities 0% 8/10/21 8/20/21
Storm drainage 0% 8/9/21 8/20/21
Sam Foundation and Building Slab
Foundation 0% 9/7/21 9/30/21
Building slab 0% 10/1/21 10/15/21
Site final prep 0% 10/16/21 10/30/21
Sam Pre‐Engineered Steel Building Delivery and Erection
Estimated building delivery 0% 1/5/22 1/7/22
Building erection 0% 1/10/22 2/18/22
Interior Buildout, Electrical, Mechanical, and Office Upfit
Office Upfit 0% 2/21/22 3/25/22
HVAC 0% 2/21/22 4/15/22
Plumbing 0% 2/21/22 4/8/22
Electrical 0% 2/21/22 4/29/22
Final Sitework, Paving, and Landscaping 0% 5/2/22 5/13/22
Mon, 7/12/2021Project Start:
Display Week:
Appendix D Assessment Analytical Data Summaries
• Comprehensive Site Assessment Report, Mineral Springs Environmental, P.C., February 2010
• Comprehensive Site Assessment Report Addendum, Mineral Springs Environmental, P.C., September 2010
• Report of Sub-Slab Soil Gas Sampling, ECS Carolinas, LLP, April 2012
BK00011 PG:0197
LAND USE RESTRICTIONS
N.C.G.S.130A-310.35{a)requires recordation of a Notice of Brownfields Property ("Notice")that identifies any restrictions on the current and future use ofa Brownfields Property thatare necessary or
useful to maintain the level of protection appropriate for the designated current or future use of the property and that are designated in a Brownfields Agreement pertaining to the property.This survey plat
constitutes one of two components of the Notice pertaining to the Brownfields Property depicted on this plat and recorded at the Iredell County Registerof Deeds'office.The other component ofthe Notice
is a document,to which the Brownfields Agreement for the subject property is attached as ExhibitA;a reduced version ofthis survey platconstitutes Exhibit B to that document.The following Land Use
Restrictions,excerpted verbatim from the Notice,are hereby imposed on the Brownfields Property and shall remain inforce in perpetuityunless canceled bythesecretary ofthe North carolina Department
of Environment and Natural Resources (or its successor in function),or his/her designee,after the hazards have been eliminated,pursuant to N.C.G.S.§130A-310.35(e):
1.No use may be madeof the Property other than industrial and,if DENR issues prior written approval,other purposes.For purposes ofthis restriction,"Industrial"refers to the manufacturing,processing,
assembly,storage and distribution of goods or materials.
2.Surface water and groundwater at the Property may not be used for any purpose without the priorwritten approval of DENR.
3:Soil disturbances must be handled in accordance with an approved Soil Management Plan including subsequent DENR approved modifications to that plan.
4.No bUilding may be constructed on the Property and no existing building,defined as those depicted on the plat componentof this document,may be occupied until DENR determines in writing that
a.the building would be sufficientty distant from the Property's groundwater and/or soil contamination that the building's users,public health and the environment will be protected from risk fromvapor
intrusion related to said contamination;or .
b.vapor mitigation measures are designed and installed or implemented to the written satisfaction of DENR in accordancewith a plan,including methodology{ies)for demonstrating performance ofthe
vapor mitigation measures,approved in writing by DENR in advance,and DENR has been provided a reportthat includes photographs and a description of the installation and performance
assessment of said measures:
5.None of the contaminants known to be present in the environmental media at the Property,including those appearing in Tables A,B and C ofthis pial,may be used orstored at the Property without the
prior written approval of DENR,except in de minimis amounts for cleaning and other routine housekeeping activities.
6.The Property may not be used as an outdoor park orfor outdoor sports ofany kind without the priorwritten approval ofDENR.
7.The Property may not be used fur agriculture or grazing.
8.The Property may not be used as a playground,or for clhild care centers or schools without the priorwritten approval ofDENR.
9.The owner of any portion ofthe Property where any existing,or subsequently installed,DENR-approved monitoring well is damaged shall be responsible for repair ofany suchwells to DENR's written
satisfaction and within a time period acceptable to DENR.
10.NeitherDENR,norany party conducting environmental assessment or remediation at the Property at the directionof.or pursuant to a permit,order or agreement issued or entered into by DENR.may
be denied access to the Property for purposes of conducting such assessment or remediation,which is to be conducted using reasonable efforts to minimize interference with authorized uses ofthe
Property.
11.During January of each year after the year in which the Notice is recorded,the owner ofany partof the Property as ofJanuary 1stofthatyear shall submita notarized land Use Restrictions Update
("LURU")to DENR,and to the chief public health and environmental officials of Stokes County,certifying that,as ofsaid.January 1st,the Notice ofBrownfields Property containing these land use
restrictions remains recorded at the Stokes County Registerof Deeds office and the land use restrictions are being oompliedwith,and stating:
a.the name,mailing address,telephone and facsimile numbers,and contact person's e-mail address ofthe owner submitting the LURU ifsaid owner acquired any part of the Property in fee during the
previous calendar year;and
b.the transferee's name,mailing address,telephone and facsimile numbers,and contact person's e-mail address,if said ownertransferred any part ofthe Property in fee dUring the previous
calendar year.
GROUNDWATER
Groundwater contaminants in micrograms per liter (the equivalentofparts per billion),the standards for
which are conlained in Title 15A of the North Carolina Administrative Code,Subchapter 2L,Rule
.0202{2L).(January 1,2010 version):
TableA -Groundwater
Concentration AbcNe Unrestricted Use Standard
Results in ugll
Groundwater Sample Dateof Concentration Standard
Contaminant Location sampling Exceeding.(ugIL)
Standard (uglL)
Perchloroethylene MW-1 1010712009 751 7
MW-1D 1010712010 125
MW-2 10/07/2010 52.4
MW-3 10/07/2010 23.4
MW-4 10/07/2010 660 -
MW-6 12/0612009 228
MW-8 12/16/2009 107
MW-9 12/16/2009 108
SUB-SLAB SOIL GAS
Sub-slab soil gas contaminants in miaograms per cubic meterofair.the screening levels for which are
derivedfrom the Industrial Vapor Intrusion Screening Levels ofthe Inactive Hazardous Sites Branch of
DENR's Superfund Section (July,2012 versian):
Table B -Sub-slab Soil Gas
Concentration Aboooe Industrial SCreening Level
ReslIItsin uglm3
-PIl.OSPECTIVEDEVELOPERordOWNER-
!:XHIBrT B to Ik Noli«ofBrownfields Proper~'-SURVEY PLAT
Dynamic Real Estate Development,lLC
157 Industrial drive
King,NC 27021
",,.SICMltAlIO bAlE DRAWN BY FIBbPAR1Y
1:20,_fJ5I2II2012 ELC IELC
ERICL au1Ili"R,LANDSURYEYINGoP.O.BOX ID7S 0-
1ClN6.NC 27021
PH.(336)969-4505 blssurw:~.i"ds"ea,,_
J'08/DW6.NO.
1232-3
SHEET
2012
\\\\\\1\11111/11
"",'"CAR
1
11//~9c-'\.0<.///~.fl....~t:.SSJ"·"./A~~""i'<'o o.,..',:-Y ~
/7?iJ :<l.SEAL~\~
L f,..6,.L-3462 :=~"~.k:=
/"."'"~o ::::~.:~..-~A·...sU\t •••2.....~~"..."....//lC ~'$:.~
,/1/L ~~,....""III •VC'".",'1/11111\\\\\\\
.\t>:?l'"A"Ued :for ~Jglet.t"..t.J,,",......,.-,..bwtIIL.
Z-S <!·p-IJ and regi.~.r.d in BOOk.iL
I~i ."
Paee ~.~hJg;.;;Of D ,,~Nt •
IndoorAir Sample Date of Concentration Industrial
Contaminants Location Sampling Exceeding Saeening
Screening Level ,
Level (uglm3)
.(uglm3)
1,4 DichJoroibenzene 1A-2 8114/2012 3.1 1.1
1A-3 stl4/2012 3.7
1A-4 stl4l2012 3.8
1A-5 stl4l2012 2.8
Chloroform 1A-3 stl4l2012 2.0 0.53
Ethylbenzene 1A-5 stl4l2012 16 4.9
Trichloroethylene .1A-3 8f1412012 .5.90 1.76
Sub-slab Soil Gas Sample Date of Sampling Concentration Industrial
Contaminant Location Exceeding 5aeening
Screening Level Level 1
(uglm3)(uglm3)
Tetrachloroethylene SG-1 311212012 5,600 350
SG-2 311212012 3,000
,screening levels displayed fur non-earcinogens are for a hazardquotient equal to02.5aeening levels
displayed fur carcinogens are for a 1.1lE-5 lifetime incremental cancer risk.
,Screening levels displayed for non-earcinogens are for a hazard quotient equal to 0.2.Screening levels
displayed fur carcinogens are for a 1.0E-5lifetime incremental cancer risk..
INDOORAIR
Indoor air contaminant screening levels in micrograms percubic meterofair,the screening.levels for
which are derived from the Industrial Vapor Intrusion Screening Levels ofthe Inactive Hazardous Sites
Branch ofDENR's Superfund Section (July,2012version):
Table C -IndoorAir
Concentration Above Industrial SCreening Level
Rest*:in uglm3
Feb 05,2013
10:36 am
00011
0197
0197
00616
FILED
STOKES COUNTY
KATHY YOUNG
REGISTER OF DEEDS
FILED'
AT
BOOK
START PAGE
END PAGE
INSTRUMENT #
~
NC
CQUNlY
S1OICE5
-TITlj;SOURCE-
DB 634,PG 1000
PIN 5991.()7-&-2808
1\~r:."..~forlhe purposes of N.C.G.5.§13OA-310.35
uf~.~pe*~~"h I ~\~
DM!Iion ofWaste Managements_of North Carolina
eo..tyofWake
lQWN5HIP
YADIaN
Appendix E
Grading Plan for Soil Borrow Source
Appendix F
Historic Aerial Photographs for Soil Borrow Source
STOKES COUNTY PIN:
6901391053.000PEACHTREE LANEREVISION NO. 0
JOB NO. DMM-001
DATE: 6-30-21
APPENDIX: D-4
LEGEND
BORROW SOURCE PROPERTY BOUNDARY
PARCEL LINE
3921 Sunset Ridge Road, Suite 301Raleigh, North Carolina 27607919-847-4241(p) 919-847-4261(f)
License # C-1269 / #C-245 Geology
NOTES:
1. AERIAL IMAGERY OBTAINED FROM GOOGLE EARTH PRO
SERVICES.
2. BASE DATA OBTAINED FROM STOKES COUNTY GIS (2018).
BORROW SOURCE LOCATION MAP
HISTORICAL AERIAL (1998)
CAROLINA MEDICAL ELECTRONICS
157 INDUSTRIAL DRIVE
KINGS, NORTH CAROLINA
M:\AAA_DRAFTING\DMM\DMM-001\Figures_20210630.dwg, APP-4, 7/1/2021 9:36:13 AM, shaynes
STOKES COUNTY PIN:
6901391053.000PEACHTREE LANEREVISION NO. 0
JOB NO. DMM-001
DATE: 6-30-21
APPENDIX: D-3
LEGEND
BORROW SOURCE PROPERTY BOUNDARY
PARCEL LINE
3921 Sunset Ridge Road, Suite 301Raleigh, North Carolina 27607919-847-4241(p) 919-847-4261(f)
License # C-1269 / #C-245 Geology
NOTES:
1. AERIAL IMAGERY OBTAINED FROM GOOGLE EARTH PRO
SERVICES.
2. BASE DATA OBTAINED FROM STOKES COUNTY GIS (2018).
BORROW SOURCE LOCATION MAP
HISTORICAL AERIAL (2005)
CAROLINA MEDICAL ELECTRONICS
157 INDUSTRIAL DRIVE
KINGS, NORTH CAROLINA
M:\AAA_DRAFTING\DMM\DMM-001\Figures_20210630.dwg, APP-3, 7/1/2021 9:35:17 AM, shaynes
STOKES COUNTY PIN:
6901391053.000PEACHTREE LANEREVISION NO. 0
JOB NO. DMM-001
DATE: 6-30-21
APPENDIX: D-2
LEGEND
BORROW SOURCE PROPERTY BOUNDARY
PARCEL LINE
3921 Sunset Ridge Road, Suite 301Raleigh, North Carolina 27607919-847-4241(p) 919-847-4261(f)
License # C-1269 / #C-245 Geology
NOTES:
1. AERIAL IMAGERY OBTAINED FROM GOOGLE EARTH PRO
SERVICES.
2. BASE DATA OBTAINED FROM STOKES COUNTY GIS (2018).
BORROW SOURCE LOCATION MAP
HISTORICAL AERIAL (2012)
CAROLINA MEDICAL ELECTRONICS
157 INDUSTRIAL DRIVE
KINGS, NORTH CAROLINA
M:\AAA_DRAFTING\DMM\DMM-001\Figures_20210630.dwg, APP-2, 7/1/2021 9:34:25 AM, shaynes
STOKES COUNTY PIN:
6901391053.000PEACHTREE LANEREVISION NO. 0
JOB NO. DMM-001
DATE: 6-30-21
APPENDIX: D-1
LEGEND
BORROW SOURCE PROPERTY BOUNDARY
PARCEL LINE
3921 Sunset Ridge Road, Suite 301Raleigh, North Carolina 27607919-847-4241(p) 919-847-4261(f)
License # C-1269 / #C-245 Geology
NOTES:
1. AERIAL IMAGERY OBTAINED FROM GOOGLE EARTH PRO
SERVICES.
2. BASE DATA OBTAINED FROM STOKES COUNTY GIS (2018).
BORROW SOURCE LOCATION MAP
HISTORICAL AERIAL (2020)
CAROLINA MEDICAL ELECTRONICS
157 INDUSTRIAL DRIVE
KINGS, NORTH CAROLINA
M:\AAA_DRAFTING\DMM\DMM-001\Figures_20210630.dwg, APP-1, 7/1/2021 9:33:28 AM, shaynes