7407_Pitt_C&DLandfillInc_CDLF_Phase1_Phase2_Phase3_Permit_LFGMP_FID1664530_20220414

Attachment
Landfill Gas Monitoring Plan
Site Study and Permit to Construct Application
Egg Landfill, Inc. Phases 3 and 4
Greenville, North Carolina

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DocuSign Envelope ID: ECOE65B7-3C24-4AA3-8A77-FAB2631 D56132
Landfill Gas Monitoring Plan
Phases 1, 2 and 3
Egg Landfill, Inc.
Greenville, North Carolina
Prepared for:
COD Landfill, Inc.
Greenville, North Carolina
March 2022
VLIC.NU. E-iM (ENGINEERING)
SMITH GARDNER
14 N. Boylan Avenue, Raleigh NC 27603 191g.B28.0577
4 PRINTED ON MI RECYCLED PAPER
O = Smith Gardner, Inc.
This document is intended for the sole use of the client for which it was prepared and
for the purpose agreed upon by the client and Smith Gardner, Inc.

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Landfill Gas Monitoring Plan
Phases 1, 2 and 3
CAD Landfill, Inc.
Greenville, North Carolina
Prepared For:
COD Landfill, Inc.
Greenville, North Carolina
S+G Project No. EJE-20-1
ED
ocuSigned by:can c— iZlcl�ct�5
RR305C97RFA4Fft
Seth Rickerts, P.G.
Staff Geologist
DocuSigned by: ;
ERA��R ti
Joan A. Smyth, P.G.
Senior Hydrogeologist
March 2022
NCLIUC.Fim (ENGINEERING)
SMITH GARDNER
14 N. Boylan Avenue, Raleigh NC 27503 1 919.028.0577

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EGO Landfill, Inc.
Greenville, North Carolina
Landfill Gas Monitoring Plan
Table of Contents
Page
1.0 INTRODUCTION........................................................................................................... 1
1.1
Regulatory Requirements - C&D Landfills.............................................................. 1
1.2
Guidance Document.................................................................................................. 2
1.3
Contact Information..................................................................................................2
1.3.1 Owner............................................................................................................2
1.3.2 Engineer........................................................................................................2
1.3.3 North Carolina Department of Environmental Quality................................3
1.4
Existing Site Conditions.............................................................................................3
1.4.1 Site Geology...................................................................................................3
1.4.2 Local Groundwater Regime..........................................................................3
2.0 MONITORING
PROGRAM.............................................................................................. 4
2.5
Monitoring of Facility Structures..............................................................................4
2.6
Monitoring and Reporting.........................................................................................4
2.6.1 Frequency......................................................................................................4
2.6.2 Personnel......................................................................................................4
2.6.3 Equipment..................................................................................................... 5
2.6.4 Procedures....................................................................................................5
2.6.5 Precautionary Action Plan............................................................................6
2.6.6 Record Keeping.............................................................................................7
2.7
Maintenance.............................................................................................................. 7
3.0 CONTINGENCY PLAN................................................................................................... 8
3.1
Immediate Action Plan..............................................................................................8
3.1.1 Reporting and Documentation......................................................................8
3.2
Remediation Plan......................................................................................................8
FIGURES
Figure 1 Existing Landfill Gas Monitoring Locations
Figure 2 Flowchart of Methane Monitoring Requirements
APPENDIX
Appendix A Reporting Forms
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DocuSign Envelope ID: ECOE65B7-3C24-4AA3-8A77-FAB2631 D56132
1.0 INTRODUCTION
This Landfill Gas (LFG) Monitoring Plan (plan) was prepared by Smith Gardner, Inc. to describe
the LFG monitoring program at C&D Landfill, Inc. INC Solid Waste Permits 7407-CDLF-2001 and
7407-CDLF-2009), which is located at 802 Recycling Lane in Greenville, North Carolina. The
facility contains two active, unlined construction & demolition (C&D) landfill units. The Facility
was developed in two non-contiguous footprints, Phases 1 and 2 approximately midway between
US 264, i.e., a localized topographic divide, and Grindle Creek. The phases became operational in
May 2001 and August 2009, respectively. Phase 1 was the regional repository for flood -damage
debris after Hurricane Floyd in 1999. Phase 2 was a staging area, where flood -debris was stored
temporarily. Both areas were used for agriculture, and a former railroad corridor traverses the
site, including the northern Phase 2 footprint. A permit to begin construction on Phase 3 is
currently being drafted. Upon approval, Phase 3 will also be included under this Landfill Gas
Monitoring Plan. This plan describes the necessary procedures to satisfy applicable regulatory
requirements (see Section 1.1) for landfill gas monitoring.
The Engineer has utilized the best available site data, practices, experience, and judgment to
develop this plan. However, the plan may require modifications over time to accommodate
changing landfill conditions, changing receptors in areas adjacent to and around the landfill, or
other conditions that cannot be fully anticipated.
Uncontrolled migration of LFG (particularly methane (CH4)) can result in, loss of life, injury, loss
of property, vegetative damage, and intolerable odors. Landfill monitoring includes exposure to
explosive gases. Monitoring personnel should be specifically trained in the management and
response for situations such as fire or explosion and confined space entry and possess an
awareness of changing conditions around the landfill.
Note that this plan does not address landfill gas collection and control, air quality, or other related
landfill gas regulations or requirements which may be applicable to this site at present or in the
future.
1.1 Regulatory Requirements — CEO Landfills
Rule 15A NCAC 13B .0544(d) of the North Carolina Solid Waste Management Rules
requires the following for facilities having a C&D landfill:
• Owners or operators of C&D landfill units must ensure that:
o the concentration of methane gas or other explosive gases generated by
the facility does not exceed 25% of the lower explosive limit (LEL) for
methane (1.25% methane) in on -site facility structures (excluding gas
control or recovery system components);
o the concentration of methane gas or other explosive gases does not exceed
the LEL for methane (5% methane) at the facility property boundary; and
o the facility does not release methane gas or other explosive gases in any
concentration that can be detected in off -site structures.
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• Owners or operators of C&D landfill units must implement a routine methane
monitoring program and perform monitoring on at least a quarterly basis.
• If regulatory limits for methane gas concentrations are exceeded, a contingency
plan must be implemented for the protection of human health and safety.
1.2 Guidance Document
This plan was developed generally following the Landfill Gas Monitoring Guidance
document prepared by the North Carolina Department of Environmental (NC DEQ),
Division of Waste Management (DWM)'.
1.3 Contact Information
Correspondence and questions concerning this plan should be directed to the appropriate
contact below:
1.3.1 Owner
C&D Landfill, Inc.
802 Recycling Lane
Greenville, NC 27834
Phone: [phone]
Contacts: Judson Whitehurst, Landfill Owner
iudson.ejerecycling(agmail.com
1.3.2 Engineer
Smith Gardner, Inc.
14 N. Boylan Avenue
Raleigh, North Carolina 27603
Phone: [phone]
Contacts: Joan A. Smyth, P.G., Senior Hydrogeologist
0oan(asmithgardnerinc.com
Michael W. Brinchek, P.E., Project Manager
mikefasmithgardnerinc.com
NC DENR DWM (2010), "Landfill Gas Monitoring Guidance", NC DENR DWM Solid Waste Section,
November 2010.
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1.3.3 North Carolina Department of Environmental Duali
Division of Waste Management (DWM) - Solid Waste Section:
North Carolina DEQ — Raleigh Central Office (RCO)
217 W Jones Street
Raleigh, North Carolina 27603
Phone: [phone]
Contact: Ms. Jaclynne Drummond
iaclvnne.drummondfdncdenr.aov
1.4 Existing Site Conditions
The facility is located approximately twelve miles east of downtown Greenville on US-264
E. Area development is mixed agricultural, industrial, and rural residential.
The permitted facility is bordered to the north by US-264 E. and to the south by Grindle
Creek. A mix of wooded marshlands and agricultural lands border the eastern and
western boundaries of the facility. Grindle Creek and smaller streams create a natural
barrier to LFG migration to the south and west.
Ground surface elevations range from approximately El. 16 (feet above mean sea level)
along Grindle Creek to El. 120 at the top of the Phase 2B cell.
1.4.1 Site Geology
Historical literature and available geologic maps indicate that C&D Landfill, Inc.
sits within the NC Coastal Plain. The coastal plain is characterized as an
eastward thickening wedge of sedimentary layers that alternate between sandy
aquifers an aquitards. Information taken from The Geologic Map of North
Carolina, 1985 shows that the C&D landfill is underlain by the Yorktown
Formation, which is described as "fossillifferous clay with varying amounts of
fine-grained sand, silty sand, sandy silt, silty clay, and blueish gray shell
material"
1.4.2 Local Groundwater Reoime
Ground water depths generally range from 3 ft to 9 ft below ground surface (bgs)
across the facility. Ground water generally flows south and west toward Grindle
Creek to the southwest of the site. There are minor seasonal variations in the flow
pattern, but overall flow direction is consistent.
The site is surrounded by wetlands and perennial streams on the east, south and
west sides. The shallow groundwater in the wetlands and surface water in the
streams is a natural barrier to landfill gas migration. This has been considered in
evaluating the proposed network.
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2.0 MONITORING PROGRAM
The plan contained herein includes landfill gas monitoring wells to monitor subsurface landfill
gas migration. There are no structures close enough to the landfills to warrant structure
monitoring. The current LFG monitoring network, consisting of 6 landfill gas monitoring wells, is
shown on Figure 1, and the table below.
Probe
Relative
Location
GP-1
Northern edge
of Phase 2
GP-2
Northern edge
of Phase 2
GP-3
Northern edge
of Phase 2
GP-4
Northern edge
of Phase 2
GP-10
North of Phase 1
GP-11
East of Phase 2
GP-12
Northeast of
(proposed)
Phase 3
GP-13
Northwest of
(proposed)
Phase 3
2.5 Monitoring of Facility Structures
No structures are close enough to the landfills to warrant structure monitoring at this
time. If landfill gas exceedances are noted in the LFG monitoring network, structural
monitoring will be considered, if necessary.
2.6 Monitoring and Reporting
Monitoring and reporting of LFG concentrations will be performed as outlined below.
2.6.1 Frequency
Routine LFG monitoring will be conducted on a quarterly basis.
2.6.2 Personnel
LFG monitoring will be performed by personnel who are familiar with the
requirements of this plan and who are trained in LFG hazards and explosive gas
meter use. As practical, a designated technician will be assigned to regular LFG
monitoring duty.
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2.6.3 Equipment
An Elkins Earthworks, LLC ENVISION infrared portable gas analyzer (or
equivalent) will be used to collect measurements from the landfill gas monitoring
network. This analyzer, which is calibrated to methane (CH4), operates using the
infrared spectral property of methane to measure concentrations in air.
Measurements of oxygen (02) and carbon dioxide (CO2) will also be made with this
meter. Additionally hydrogen sulfide (H2S) will be monitored. This meter may be
used in oxygen deficient areas (less than 10% 02) since oxygen is not required for
a chemical combustion of flammable gases within the meter.
On the day of monitoring, prior to monitoring activities, the meter(s) will be field
calibrated. Additionally, all monitoring equipment should be regularly calibrated
in accordance with manufacturer's specifications and operated only as instructed.
2.6.4 Procedures
Prior to each monitoring event, the portable gas analyzer will be calibrated with a
known calibration standard in accordance with manufacturer's recommendations.
General information related to the monitoring event, equipment used, calibration
procedures, weather conditions, and results for each monitoring event will be
recorded on the landfill gas monitoring data form (see Appendix A).
The following steps outline the procedure for the monitoring of LFG wells and
facility structures:
• Check calibration date on the meter and calibrate according to
manufacturers instructions; allowing equipment to warm up properly prior
to use, per manufacturers direction.
• Purge sample tube for one minute before monitoring.
LFG Monitoring Wells:
o Connect instrument tubing to sample port on the monitoring well
without removing the cap.
o Open the valve and record both the initial and stabilized methane
concentrations. A stabilized concentration will not vary more than
0.5 percent by volume on the instrument's scale. Also record the
oxygen concentration (at two percent per volume or less to indicate
air is not being drawn into the system and providing false readings)
and the carbon dioxide concentration.
o Close the valve and disconnect the tubing.
o Record monitoring data on the LFG monitoring data form provided
in Appendix A.
o If any methane concentration is greater than 50% of the LEL (2.5%
CH41, monitoring personnel should implement the Precautionary
Action Plan (see Section 2.3.5).
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o If both initial and stabilized methane concentrations are less than
50% of the LEL (2.5% CH4), move to next LFG monitoring well.
Structures:
o Walk through the facility structure with a methane analyzer and
monitor the perimeter wall interface of the structure, the floor to
wall interface in hallways and rooms, and any floor penetrations in
the structure. Record the initial and stabilized methane
concentrations, oxygen concentration and carbon dioxide
concentration.
o Record monitoring data on the LFG monitoring data form provided
in Appendix A.
o Notify the Solid Waste Operations Manager and the Engineer for
any methane concentration greater than 5% of the LEL and any H2S
concentration greater than 10 ppm.
IFA STABILIZED METHANE CONCENTRA TION IS GREA TER THAN 100% OF THE
LEL IN A LFG MONI TORINO WEL L OR GREA TER THAN 25% OF THE LEL OR
HYDROGEN SULFIDE IS GREATER THAN 20 PPM IN A FACILITY STRUCTURE,
THE FOLLOWING ACTIONS WILL BE IMPLEMENTED:
1) Recalibrate monitoring equipment and confirm results.
2) If results are confirmed, IMMEDIATELY contact the Owner and Consulting
Engineer.
3) Implement the Compliance Action Plan located in Section 3.1.
A flowchart of propsed action for noted exceedances is presented as Figure 2.
2.6.5 Precautionary Action Plan
If an initial or stabilized methane concentration is equal to or greater than 50% of
the LEL in a LFG monitoring well, monitoring personnel should perform the
following additional steps at this location:
• Measure gas pressure in the well head (in inches of water) using
magnehelic gauge or other appropriate metering device.
• Record at least one additional methane and/or hydrogen sulfide
concentration measurement, inside the well just below the top of casing.
• Evaluate the surrounding area for potential receptors to or signs of LFG
migration. LFG can stress vegetation and can kill trees and grass by root
asphyxiation. Note stressed/dead vegetation areas on the monitoring
form.
• Notify the Owner and the Engineer for further evaluation.
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DocuSign Envelope ID: ECOE65B7-3C24-4AA3-8A77-FAB2631 D56132
2.6.6 Record Keeping
Routine LFG monitoring events will be documented on the LFG monitoring data
form provided in Appendix A. Completed forms will be placed in the landfill
operating record located at the landfill office at 802 Recycling Lane, Greenville,
North Carolina 27834. These forms will be available for review by DWM personnel
on request.
Documentation of any contingency plan actions (see Section 3.0) will also be kept
in the operating record.
2.7 Maintenance
Periodic maintenance and site observations will be conducted routinely to address
monitoring program components (at a minimum):
• Maintain access to LFG monitoring locations.
• Perform LFG monitoring well maintenance (maintain well locks, steel casing,
concrete pad, etc.).
• Observe landfill cover conditions, areas of dead vegetation, leachate seeps, odors,
etc. as indications of potential LFG-related problems.
Note deficiencies on the monitoring forms and report to the Owner for repair or
replacement as necessary.
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3.0 CONTINGENCY PLAN
If a stabilized methane concentration is greater than 100% of the LEL in a LFG monitoring well
or greater than 25% of the LEL or if hydrogen sulfide is greater than 20 ppm in a facility
structure, Site Personnel will perform both an immediate action and plan and a remediation plan
as described below and as summarized on Figure 2.
3.1 Immediate Action Plan
The Solid Waste Operations Manager will perform the following actions for the protection
of human health and safety:
1) Evacuate affected facility structures and the immediately surrounding area.
2) Determine nearby potential receptors (facility and off -site structures).
3) Perform monitoring in any other facility structure near the monitoring location
having the high concentration.
4) Verbally notify the Owner, or his/her designee.
5) Verbally notify the NCDEQ DWM (see Section 1.1) as soon as practical.
6) Investigate and identify the potential source(s) and conduit(s) for LFG migration
that may have caused the high concentration (i.e. the path the LFG may be
following to the monitoring location).
7) Identify the LFG extent using bar hole punch sampling methodology or other
applicable alternative method as practical.
8) As appropriate, evaluate corrective actions to control methane concentrations in
structures surrounding the landfill site.
3.1.1 Regortlno and Documentation
Within seven days of the high methane concentration detection, site personnel will
prepare and submit an Environmental Monitoring Reporting Form (see Appendix
A) with the monitoring event results to the DWM. Site Personnel will also place a
description of the actions performed to protect human health in the operating
record.
3.2 Remediation Plan
Within sixty days of a high methane concentration detection, a remediation plan describing
the problem nature, extent, and proposed remedy will be prepared and submitted to
NCDEQ for approval. Following approval, the plan will be implemented and a copy will be
placed in the operating record. The DWM will also be notified once the plan has been
implemented.
An extension may be requested from the DWM depending on severity of the situation.
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Figures
Landfill Gas Monitoring Plan — Phases 1, 2 and 3
CGD Landfill, Inc.
Greenville, North Carolina

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DocuSign Envelope ID: 560557E8-52C6-4A1A-B027-6BA6EC58FB6B
2
a
0
N
N
N
0
N
OD
1. IMMEDIATELY:
TAKE STEPS TO ENSURE
PROTECTION OF HUMAN
HEALTH AND SAFETY
SMITH+ NOTIFY THE
ENGINEER AND
GARDNER DIVISION WITHIN
24 HOURS
EVALUATE THE NEED FOR
ADDITIONAL MONITORING
[=MONITORING FREQUENCY
RTERLY
METHANE CONCENTRATION MUST NOT EXCEED:
1. 25% OF THE LEL IN FACILITY STRUCTURES; AND
2. 100% OF THE LEL AT THE FACILITY PROPERTY BOUNDARY.
IF METHANE CONCENTRATION EXCEEDS EITHER OF THE ABOVE,
THE OWNER MUST:
i
RECALIBRATE METER AND CONFIRM READINGS
(SEE SECTION 2.3.4 OF LFG MANAGEMENT PLAN)
IF CONFIRMED READINGS EXCEED LIMITS,
(SEE SECTION 3.0 OF THE LFG MANAGEMENT PLAN) AND::
2. WITHIN 7 DAYS.
PLACE THE METHANE
READINGS AND STEPS TAKEN
TO PROTECT HUMAN HEALTH
IN THE OPERATING RECORD
LANDFILL GAS MONITORING REQUIREMENTS
FLOW CHART
CRD LANDFILL, INC.
GREENVILLE, NC
C.T.J. I J.A.S. I N.T.S
WITHIN 60 DAYS:
PREPARE A REMEDIATION
PLAN. SUBMIT PLAN TO
NCDENR FOR APPROVAL. UPON
APPROVAL, IMPLEMENT PLAN.
PLACE A COPY OF THE
REMEDIATION PLAN IN THE
OPERATING RECORD, AND
1
NOTIFY THE DIVISION THAT
THE PLAN HAS BEEN
IMPLEMENTED
NO LIC. NO. F-1370 [ENGINEERING]
SC COA NO. C01488
SMITH+GARONER
14 N. Boylan Avenue, Raleigh NC 27603 1919.828.0577
1526 Richland St., Columbia SC 29201
Apr 2021 I EJE 20-1 I 2 I EJE-A0010
© 2021 Smith Gardner, Inc.

DocuSign Envelope ID: 560557E8-52C6-4A1A-B027-6BA6EC58FB6B
Appendix A
Reporting Forms
Landfill Gas Monitoring Plan — Phases 1, 2 and 3
COD Landfill, Inc.
Greenville, North Carolina

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NC Division of Waste Management - Solid Waste Section
Landfill Gas Monitoring Data Form
Notice: This form and any information attached to it are 'Public Records" as defined in NC General Statute 132-1. As such, these documents are
available for inspection and examination by any person upon request (NC General Statute 132-6).
Facility Name: Permit Number:
Sampling Date: NC Landfill Rule (.0500 or.1600):
Sample Collector Name & Position:
Gas Meter Type & Serial Number:
Field Calibration Date & Time:
Field Calibration Gas Type (15115 or 35/5
Gas Meter Pump Rate:
Gas Meter Calibration Date:
eld Calibration Gas Canister Expiration Date:
Ambient Air Temperature: Barometric Pressure (in. or mm Hg): Weather Conditions:
Instructions: Under "Location or LFG Well", list monitoring well # or describe monitoring location (e.g., inside field office).
Attach a test location map or drawing. Report methane readings as both % LEL and % CH4 by volume.
Convert % CH4 (by volume) to % LEL as follows: % methane (by volume)/20 = % LEL.
*Hydrogen Sulfide (H2S) gas monitoring may be required for Construction & Demolition Landfills (CDLFs). See
individual permit conditions and/or Facility LFG monitoring plan.
Location or
LFG Well ID
S ample
Tube
Purge
Time of
Day
Time
Pumped
(sec)
Initial
% LEL
Stabilized
% LEL
% CH4
( volume )
% 02
(volume)
% CO2
(volume)
% H2S*
(volume)
NOTES
NOTE: If needed, attach additional data forms to include additional LFG monitoring data locations for the facility.
ACTION LEVELS: Methane: >1.25% by volume (inside structures) AND >5% by volume (at facility boundary)
Hydrogen Sulfide: >1% by volume (inside structures) AND >4% by volume (at facility boundary)
Certification
To the best of my knowledge, the information reported and statements made on this data submittal and attachments
are true and correct. I am aware that there are significant penalties for making any false statement, representation,
or certification including the possibility of a fine and imprisonment.
SIGNATURE
TITLE
Revised — March 6, 2017

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Envelope Id: 560557E852C64A1AB0276BA6EC58FB6B
Subject: Please DocuSign: FINAL C&D Disposal, Inc. LFG Monitoring Plan April 2021.pdf
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Seth C. Rickerts
[e-mail]
Smith Gardner, Inc.
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Joan Smyth
[e-mail]
Vice President
Smith Gardner, Inc.
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