Document G5eJGdd5pqGoebYzKvdEy9wjv
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY OFFICE OF ENFORCMENT AND COMPLIANCE ASSURANCE
DATE: SUBJECT: FROM: THRU: TO:
See date of Section Chief signature
CLEAN AIR ACT INSPECTION REPORT Republic Services McCarty Road Landfill, Houston, TX
Daniel Heins, Environmental Scientist Stationary Source Enforcement Branch, EPA OECA
Gregory Fried, Branch Chief Stationary Source Enforcement Branch, EPA OECA
File
BASIC INFORMATION
Facility Name: Republic Services McCarty Road Landfill
Facility Location: 5757 Oates Road, Houston, TX 77078
Date of Inspection: On Site Inspection: March 14, 2023 Virtual Conference: May 2, 2023
EPA Inspector(s): 1. Daniel Heins, Environmental Scientist, EPA OECA a,b 2. Daniel Hoyt, Environmental Engineer, EPA OECA a,b 3. Colleen McCarthy, Life Scientist, EPA Region 6 b 4. Kenneth McPherson, Life Scientist, EPA Region 6 b 5. Benjamin Rosenthal, Air Inspector, EPA Region 6 a,b
Other Attendees: 1. Nathanial Wells, Environmental Manager for McCarty Road, Republic Services a,b 2. Scott Trebus, Area Environmental Manager for the State of Texas, Republic Services a 3. Nikki Wuestenberg, Senior Manager Air Compliance, Republic Services a 4. Angie Vandergriff, Project Director, Weaver a 5. Matt Stutz, Senior Engineer, Weaver a 6. Joe Mosier, Landfill Manager for McCarty Road, Republic Services b 7. Tyler Tandy, Environmental Specialist for McCarty Road, Republic Services b 8. Kevin Vasquez, Operation Manager for McCarty Road, Republic Services b
a Attended conference b Attended surface emissions monitoring (SEM)
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Contact Email Address: nwells2@republicservices.com
Purpose of Inspection: Surface monitoring and partial compliance evaluation for the Clean Air Act
Facility Type: Muncipal solid waste (MSW) landfill
Regulations Central to Inspection: 40 C.F.R. Part 60, Subpart WWW; 40 C.F.R. Part 62, Subpart OOO; 40 C.F.R. Part 63, Subpart AAAA; 40 C.F.R. Part 98, Subpart HH
On Site (3/14) Arrival Time: 11:00 Central On Site (3/14) Departure Time: 16:30 Central Virtual Conference (5/2) Start Time: 14:00 Central Virtual Conference (5/2) End Time: 16:00 Central
Inspection Type: Unannounced Inspection Announced Inspection
SITE OVERVIEW
The following information was obtained verbally from Republic Services representatives, including their consultants, during the virtual conference.
Company Ownership: The McCarty Road Landfill ("the Landfill") is operated as McCarty Road Landfill TX, LP, which ultimately is owned by Republic Services. The Landfill previously was operated under BFI and then Allied Waste prior to their eventual merger with Republic.
Operations Overview: The Landfill began operations around 1970, and currently has approximately 388 acres with waste in place, fully utilizing the permitted footprint. There is no further capacity for expansion and there is approximately 15 years remaining in capacity, pending market conditions. The Landfill accepts approximately 6,000 tons per day of waste. Waste includes MSW, construction and demolition (C&D) waste, class 2 non-hazardous industrial waste (plant trash), and contaminated soils. C&D waste from storms affects the year-to-year tonnage. The site does accept asbestos waste. The Landfill does deposit solidified liquids.
Of the 388 acres, approximately 50 acres are post RCRA Subtitle D in the southeast of the site. Overliner has been installed on top of older pre-RCRA sections. Leachate in lined portions of the landfill goes from sumps to holding tanks. Disposal from the tanks is both trucked off site or directly sent to the Houston Publicly Owned Treatment Works, pending volumes.
There is approximately 117 acres of final cover on some of the side slopes. Intermediate cover is 12" of soil, required to be put in place if not filling for 6 months in an area by their Solid Waste
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Permit. Daily cover requires soils if in place for more than 24 hours. Alternative daily cover includes tarps, petroleum contaminated soils, and a half auto shredder fluff half soil blend.
The gas collection and control system (GCCS) contains approximately 500 wells. These are primarily vertical wells. The entire landfill is subject to gas collection requirements. In active areas, Republic may add horizontals as they are filling and then add vertical wells when the area is done being filled for that period. Horizontals vary from 75 to 125' vertical spacing, and pending fill sequence 30-50'. Vertical wells are typically spaced 200' apart though this is variable. Wellhead spacing is decided by the design engineers, typically consultants from Weaver and SCS. Leachate risers can have vacuum pulled on them for gas collection, this is done on an "as needed" basis. All collected gas goes to a common header, and all gas collection is active. Typical collection is in the range of approximately 9000 to 9500 standard cubic feet per minute (scfm) normalized to 50% methane.
Collected gas goes to a blower/flare system. Connections from the blower can discharge to two separate renewable natural gas (RNG) plants, and gas volumes beyond what the plants accept is flared off. There is typically an amount of gas being flared. The exact same gas is routed to the flares as two each of the plants. Ameresco operates one of the plants, and typically takes approximately 4500 scfm of gas. Montauk/GSF operates the other plant, and can take up to approximately 5500 scfm but more typically takes around 4500 scfm. There are two enclosed flares with 6000 scfm capacity each, and one candlestick with a 3000 scfm capacity. When the plants are operating, the candlestick usually handles the excess gas to accommodate so that the lower flows can still be adequately handled minding the turndown ratio for each flare.
SITE TOUR -- MARCH 14, 2023
Presented Credentials Stated authority and purpose of inspection Provided Small Business Resource Information Sheet Small Business Resource Information Sheet not provided. Reason: Not a small business Asked the facility representatives to identify any confidential business information (CBI) that was provided, observed, or discussed during the inspection. No CBI was identified.
Data Collected and Observations: EPA conducted an abbreviated SEM survey of the facility. EPA used three ThermoFisher Toxic Vapor Analyzers 2020 (TVA2020) to perform EPA Reference Method 21 for the SEM. EPA monitored in two teams, with the third instrument moving between the two teams to provide confirmation readings for each exceedance point. GPS tracks were recorded for the confirmation instrument. Ben Rosenthal and Daniel Hoyt took primary readings, with Dan Heins providing confirmations.
EPA monitoring focused on part of the northern area of the Landfill, an area that had not seen any recent construction or waste deposition activity, covering an area of less than 40 acres. See Appendix C for maps. EPA inspectors identified 55 total points above 500 ppm methane. Only two points were not able to be confirmed.
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While driving around the landfill to take upwind and downwind measurements, EPA noted an elevated area of methane. This was a widespread area of exceedance by ES-2, with exceedances at gaskets and from the base and top of nearby survey posts.
In the main area of SEM survey on the northern portion of the Landfill, exceedances were found primarily at penetrations and areas of erosion/exposed waste.
Photos and/or Videos: were taken during the inspection. See Appendix A. Field Measurements: were taken during this inspection. See Appendix B.
INSPECTION CONFERENCE -- MAY 2, 2023
Provided U.S. EPA point of contact to the facility Asked the facility representatives to identify any CBI provided, observed, or discussed during the inspection. No CBI was identified.
EPA showed facility representatives a map of the path walked during the on-site SEM survey and the exceedances detected.
Staff Interview: The Landfill was previously operating under NSPS Subpart WWW until the Federal Plan Subpart OOO came into effect. The Landfill has a Design Capacity of greater than 2.5 million Mg and cubic meters, has an uncontrolled emission rate of NMOC of greater than 50 Mg, and has been subject to GCCS requirements for greater than five years.
The Landfill checks perimeter probes quarterly for gas migration. There is an active soil vapor extraction system tied into the GCCS to control migration, primarily located on the north and east side of the landfill. Probes are located outside these extractors.
Some gas wells have dewatering pumps, with the operations and maintenance contractors deciding when to add or remove the pumps. Liquid levels are checked quarterly. There are no defined action levels, pumps are added based on design engineer recommendations.
The wellfield is manually tuned, with wells checked twice a month. All adjustments are logged.
There are not specific contract limits on gas quality for the RNG plants. If either plant sees rising oxygen/nitrogen levels, they will call the landfill and the operations/maintenance contractors will try to find the source of the issue, which may be from weather, construction, or a need for rebalancing.
Wells designated as "odor control wells" are the soil vapor extractors and gas collection on the leachate system; Republic was uncertain if any interior wells were labeled as such. Wells designated as "nonproducing" are from older areas with low gas production that Republic does not want to remove. They are still monitored monthly, but there is no synthetic liner or geomembrane.
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Tetra Tech performs the SEM for the site, currently using an IRwin. Republic stated that they have the calibration information and should have the map of where the technicians walk. There is no list of all penetration points for monitoring, the technicians identify them while walking. Active operations and construction areas (including GCCS construction) are excluded as dangerous areas. Republic has not recently identified slopes as being too steep to monitor and has not excluded areas based on high vegetation. Corrective actions are typically done by the operations team but may be contracted. There is no formal log of corrective actions.
Monthly cover integrity monitoring is performed in coordination with the wellfield operations/maintenance team. There are formal logs for this monitoring and corrective actions.
The landfill does not currently have elevated temperature areas. There was a subsurface oxidation event from a localized airline break that was resolve approximately a year and a half ago.
Collection shutdowns identified as "General Alarm" in their semiannual reports could be a pressure drop, electric issue, or high or low temperature alert from the flare. That is the general output from the monitoring program Republic uses.
EPA asked if Republic was aware of Carbon Mapper flyover data for the facility. They stated that Carbon Mapper had flown the site recently and that Republic believed the plumes measured came from the active area. Republic stated that the delay in receiving data from the June 2022 flyover made it hard to identify potential cause and respond.
Reviewed documents: Prior to inspection (available publicly online):
October 2022 Semi-Annual Report, including 2022 Q2 & Q3 SEM results o Q2 SEM 68 exceedances total Fewer than 20 in the approximate area of EPA survey o Q3 SEM 60 exceedances total Fewer than 10 in the approximate area of EPA survey
February 2022 Subpart OOO Initial Report, including 2021 Q3 SEM results o 2021 Q3 SEM 45 exceedances total Fewer than 5 in the approximate area of EPA survey
Requested documents: After discussing preference between a Section 114 Request For Information Letter and an emailed list of documents associated with the inspection, Republic expressed a preference for the latter.
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Concerns:
EPA noted the disparity between the number of exceedances they had found compared with the reviewed recent SEM surveys, indicating possible concerns with the quality of the SEM surveys
EPA noted that erosion and exposed waste was seen across the survey area EPA noted that some of the pneumatic pump outlets were venting landfill gas (and
condensate), and that the carbon cannisters being utilized did not effectively control the emissions
DIGITAL SIGNATURES
_________________________________ Daniel Heins, Lead Inspector
GREGORY Digitally signed by GREGORY FRIED
FRIED
Date: 2023.06.30 09:04:51 -04'00'
__________________________________
Gregory Fried, Supervisor
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APPENDICES AND ATTACHMENTS Appendix A: Digital Image Log Appendix B: Field Measurement Appendix C: Maps
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APPENDIX A: DIGITAL IMAGE LOG
Inspector Name: Colleen McCarthy
Archival Record Location: US EPA SharePoint
Images (1 of 2)
Image
#
File Name
1 IMG_4004.JPG 2 IMG_4006.JPG 3 IMG_4007.JPG 4 IMG_4008.JPG
5 IMG_4009.JPG 6 IMG_4010.JPG
7 IMG_4011.JPG 8 IMG_4012.JPG
9 IMG_4013.JPG
10 IMG_4014.JPG 11 IMG_4015.JPG 12 IMG_4016.JPG
13 IMG_4017.JPG 14 IMG_4018.JPG
15 IMG_4021.JPG
16 IMG_4022.JPG 17 IMG_4023.JPG 18 IMG_4024.JPG 19 IMG_4025.JPG
20 IMG_4026.JPG
21 IMG_4027.JPG 22 IMG_4028.JPG
23 IMG_4029.JPG 24 IMG_4030.JPG 25 IMG_4031.JPG 26 IMG_4032.JPG 27 IMG_4033.JPG
Description A3 erosion gulley with exposed waste
A2 penetration
A4 EW295A
A5 EW501 A6 Erosion with exposed waste
A7 EW500 A8 Erosion gullies with exposed waste
A9 EW427A A9 EW427A closeup on pneumatic leaking gas & condensate A10 Erosion/exposed waste
A11 EW423
A12 LI423 Leachate breakout/distressed vegetation
A13 Well A14 Erosion gullies with exposed waste A15 Erosion gullies with exposed waste
A16 EW407
A17 LI378
A18 EW375A A19 Erosion with exposed waste A20 Erosion with exposed waste
A21 EW374 A22 Bare earth/discolored soils
A23 EW385
A24 EW383
A25 EW404
A26 EW410
Date/time (Central)
2023:03:14 12:34:58 2023:03:14 12:35:26 2023:03:14 12:38:23 2023:03:14 12:43:50
2023:03:14 12:45:44 2023:03:14 12:48:50
2023:03:14 12:51:19 2023:03:14 12:53:28
2023:03:14 12:53:35
2023:03:14 12:59:07 2023:03:14 13:01:02 2023:03:14 13:03:03
2023:03:14 13:05:37 2023:03:14 13:14:04
2023:03:14 13:16:41
2023:03:14 13:18:48 2023:03:14 13:28:20 2023:03:14 13:53:51 2023:03:14 13:57:12
2023:03:14 14:02:30
2023:03:14 14:06:50 2023:03:14 14:11:48
2023:03:14 14:18:42 2023:03:14 14:24:35 2023:03:14 14:36:24 2023:03:14 14:39:58 2023:03:14 14:47:34
Latitude
29.83149 29.83153 29.83471 29.83106
29.83122 29.83088
29.83083 29.83091
29.83089
29.83098 29.83095 29.83094
29.83114 29.83052
29.8305
29.83054 GPS Error
29.83151 29.8311
29.83142
29.8312 29.83107
29.83086 29.83062 29.83024 29.83024 29.83017
Longitude
-95.235336 -95.235139 -95.235611 -95.235594
-95.235961 -95.236075
-95.236336 -95.236581
-95.23655
-95.236856 -95.237014 -95.237022
-95.237672 -95.238031
-95.238183
-95.238425 GPS Error -95.240662 -95.240953
-95.240914
-95.241212 -95.2415
-95.241775 -95.241714
-95.24105 -95.240334 -95.239731
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Images (2 of 2) Image
# File Name 28 IMG_4034.JPG
29 IMG_4035.JPG 30 IMG_4037.JPG
31 IMG_4038.JPG
Description
A27 EW419A A28 EW424A with carbon can on pneumatic outlet
A29 Erosion gulley 5cm spacer on instrument
Date/time (Central) 2023:03:14 14:57:55
Latitude Longitude 29.8301 -95.238487
2023:03:14 15:08:00 2023:03:14 15:21:40
29.83041 -95.23735 29.8317 -95.236131
2023:03:14 17:57:47 NA
NA
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APPENDIX B: FIELD MEASUREMENT DATA
Measured Exceedances (1 of 2)
EPA
EPA
Reading Confirmation
Flag (ppm / %) (ppm / %)
A1
894
A2
910
A3
1100
A4
903
A5
650
A6
1622
A7
1138
A8
4600
2100 1900 640 1300 670 2000 1400 2500
A9
4838
2500
A10
827
760
A11
857
960
2.5% / Flame
A12
2900 out
A13
870
2200
A14
6900
2800
A15
2900
6900
A16
1100
900
A17
4200 3200
A18
5900
6200
A19
790
900
A20
1000
1050
A21
2500
1100
A22
819
730
A23
3790
2900
A24
1000
1100
A25
1200
1300
A26
1240
540
A27
2600
3500
A28
2300 750
Description/notes Multiple points throughout mound and well at penetration of riser erosion/exposed waste EW 295A at pipe EW-501 at leaking ball valve exposed waste in erosion gulley EW-500, base of well erosion/exposed waste EW-427A, pump pneumatic outlet leaking gas/condensate erosion/exposed waste EW 423 at base
LI 423 uncapped at seal on wellhead erosion/exposed waste erosion/exposed waste EW-407 LI-378 at top of wellhead and at ground level. 1% & flame out at top. EW 375A erosion/exposed waste erosion/exposed waste EW 374 at pipe erosion EW385 (no flag) EW 383 (at base of mount and on top) EW 404 at base of well EW410 at penetration above cover, south side of well EW419A both at wellhead and lateral line EW424A base and pneumatic outlet (2.5% & flameout at outlet, still read over 1% at outlet of replaced carbon can)
Latitude
29.831450 29.831516 29.831462 29.831358 29.831007 29.831185 29.830878 29.830801
29.830874 29.830907 29.830983
29.830977 29.830507 29.830517 29.830544 29.830955
29.831501 29.831100 29.831161 29.831174 29.831178 29.830867 29.830613
29.830253 29.830261
29.830178
29.830099
29.830431
Longitude
-95.234580 -95.235137 -95.235343 -95.235387 -95.235600 -95.236006 -95.236069 -95.236365
-95.236563 -95.236880 -95.237058
-95.237086 -95.238071 -95.238188 -95.238424 -95.238371
-95.240688 -95.240992 -95.241118 -95.241228 -95.241641 -95.241731 -95.241738
-95.241018 -95.240268
-95.239706
-95.238462
-95.237328
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Measured Exceedances (2 of 2)
EPA EPA
Reading Confirmation
Flag (ppm / %)
(ppm / %)
A29
1600
2600
B1
600 Unconfirmed
Flameout
B2 (>5%)
NA
B3
700
1100
B4
1020
1100
B5
1150
3400
B6
1090
571
B7
615
610
B8
655
700
B9
585 Unconfirmed
B10
905
1200
B11
985
1100
B12
770
880
B13
720
1400
B14
610
822
B15
650
959
B16
1100
875
B17
1139
800
B18
6100
6600
B19
900
1300
B20
850
1500
B21
1350
970
B22
4800
5000
B23
650
850
B24
560
720
B25
600
1700
C1
5000 NA
Description/notes Erosion gulley EW212A (Confirmation not attempted to avoid flame out) Already flagged "22" EW211A EW421 Already flagged "33"
Bare soil Already flagged "38" Ground penetration Ground penetration Ground penetration Ground penetration Ground penetration Ground penetration Ground penetration EW338A Ground penetration EW373 EW436 EW372A EW384 EW438 EW382 Ground penetration EW413 ES-2 (by gaskets) and at bases and tops of nearby survey posts. (No confirmation reading attempted)
Latitude 29.831664 29.831796
Longitude -95.236212 -95.234953
29.831742 29.831736 29.831803 29.831369 29.831380 29.831366 29.831290 29.831431 29.831433 29.831468 29.831338 29.831154 29.831467 29.831448 29.831377 29.831075 29.830958 29.830590 29.830482 29.830671 29.830461 29.830619 29.830416 29.830214
-95.235135 -95.235231 -95.235594 -95.235976 -95.236636 -95.237161 -95.238161 -95.238618 -95.238964 -95.239502 -95.239663 -95.239913 -95.240520 -95.241400 -95.242170 -95.242254 -95.242168 -95.242091 -95.242304 -95.241206 -95.241112 -95.240640 -95.240218 -95.239095
29.822670 -95.235720
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Calibration and Instrument Information EPA used three ThermoFisher Toxic Vapor Analyzers 2020 (TVA2020), numbered 202017092712, 202023016408, and 202016081525 (and designated as TVAs "Green", "Red" and "Black"). The EPA TVA2020 response times are approximately 4.5 seconds. EPA calibrated with 500 ppm methane in air, 10,000 ppm methane in air, and zero gas at the TCEQ Houston office prior to arrival on site.
Morning Calibration Bump Checks
TVA 500 ppm cal 10,000 ppm cal
gas
gas
Black 485 ppm
9,620 ppm
Red 481 ppm
10,500 ppm
Green 493 ppm
9,900 ppm
Upwind and downwind readings were less than 10 ppm.
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APPENDIX C: MAPS Site Overview Map
Blue line shows main EPA survey coverage, tracing the confirmation reading instrument. C1 marks the additional exceedance separately from main survey. Active area in central eastern portion of landfill at time of survey. Satellite imagery dated to April 2022 as shown on Google Earth.
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Map of Detected Exceedances
Blue line roughly shows EPA survey coverage, tracing the confirmation reading instrument. Exceedance locations labeled with their flag numbers. Yellow line is 100m, north is up. Satellite imagery dated to April 2022 as shown on Google Earth. Survey area covered less than 40 acres.
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