Document v6EJJe820xY5o1Leko1wnbk49
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY REGION 5
77 WEST JACKSON BOULEVARD CHICAGO, ILLINOIS 60604
DATE: SUBJECT: FROM: THRU: TO:
See date of Section Chief signature
CLEAN AIR ACT INSPECTION REPORT Waste Connections Winnebago Landfill, Rockford, IL
Daniel Heins, Environmental Scientist AECAB (IL/IN)
Nathan Frank, Section Chief AECAB (IL/IN)
File
BASIC INFORMATION
Facility Name: Waste Connections Winnebago Landfill
Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109
Date of Inspection: Virtual Opening Conference: May 10, 2021 On Site Inspection: June 1, 2021 Closing Conference: June 1, 2021
EPA Inspector(s): 1. Daniel Heins, Environmental Scientist 2. Vicky Mei, Environmental Engineer 3. Karina Kuc, Environmental Engineer 4. Konstantinos Loukeris, Environmental Engineer
Other Attendees: 1. Lacy Ballard, District Manager - Waste Connections 2. Dominic Remmes, Region Engineer - Waste Connections 3. Matt Crockett, Region Engineer - Waste Connections 4. Ryan Daniels, Environmental Specialist - Waste Connections 5. Connor Riordan, Technician - Waste Connections (on-site inspection only) 6. Tom Hibbert, Region Engineer - Waste Connections (on-site inspection only) 7. Josh Hay, SEM Technician - Andrews Engineering (on-site inspection only)
8. John Perkey, Counsel / Director of Air Compliance - Waste Connections (remote conference only)
9. Kaare Jacobsen, Solid Waste Division - Illinois EPA (IEPA)
Contact Email Address: Lacy.Ballard@wasteconnections.com
Purpose of Inspection: To determine Clean Air Act (CAA) compliance and perform a comparative Surface Emissions Monitoring (SEM) survey
Facility Type: Muncipal solid waste (MSW) landfill
Regulations Central to Inspection: 40 C.F.R. Part 60, Subpart XXX; 40 C.F.R. Part 63, Subpart AAAA, Title V Permit Requirements
Virtual Conference (5/10) Start Time: 14:30 Virtual Conference (5/10) End Time: 16:30 On Site (6/1) Arrival Time: 9:15 On Site (6/1) Departure Time: 16:30
Inspection Type: Unannounced Inspection Announced Inspection
OPENING CONFERENCE
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 Provided CBI warning to facility
The following information was obtained verbally from Waste Connections representatives.
Process Description: Winnebago Landfill (the Landfill) is a municipal solid waste (MSW) landfill located in Rockford, Illinois. The Landfill is made up of four discontiguous pieces: the combined North Unit and South Expansion Units (NU, SEU), the Northern Expansion Unit (NEU), West Expansion Unit (WEU) and the East Expansion Unit (EEU). Waste received is approximately 60% MSW, 20% construction and demolition (C&D), and 20% soils, with small amounts of special wastes. Tarps, wood chips, processed landscaping waste, contaminated soils, and foundry sands are used as alternate daily cover (ADC). C&D fines are no longer used for ADC, though it historically was used at the WEU and NEU.
The NU was the original landfill at the site and was closed and capped in the 2000s. It is a presubtitle D landfill with an asphalt liner. The SEU has a liner that is an overlay onto the south side
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of NU and began filling in the 1990s as an expansion to the NU. Its final closure was in 2009. The two units are continuous and together have about 60 wells producing up to about 1000 cubic feet per minute (cfm) of landfill gas (LFG).
The NEU received MSW from 2009 to 2015. It still receives contaminated soils and asbestos, with approximately 5 years left in its life based on current acceptance rates. The NEU receives anywhere from 0 to 6,000 tons per day of soils. Contaminated soils are profiled and analyzed to ensure they are non-hazardous. Intermediate cover can be up to 30 feet thick with the contaminated soils. Temporary geomembrane scrims were installed on the south and southwest facing slopes in 2021 and 2019, respectively. This has been to address odor concerns. So far, 24 acres have been placed under composite membrane with protective soils, though this is not a full final cap. The NEU has approximately 130 wells which collect approximately 3,000 cfm of LFG.
The WEU stopped receiving waste at the end of 2020. Currently 10 acres are under composite membrane with protective soils. An additional 47 acres are being graded and prepared for being placed under membrane this year. The final cover with vegetative layer is planned for 2022. The WEU has approximately 88 vertical wells, as well as a handful of toe collectors that will be removed with closure. These all together collect up to around 3,300 cfm of LFG.
The EEU began receiving waste in 2019 and does not have a gas collection and control system (GCCS) in place yet, as the waste is less than five years old and none of the EEU is at final grade. It will be 225 acres and is currently developed to approximately 90 acres. At current rates, this will be able to accept waste for another 15 years. The EEU typically receives up to 9,000 tons of waste per weekday, and around 2,000 tons on Saturdays.
Leachate is not recirculated and there is no direct liquid addition. Liquid waste is received, profiled, and poured into beds with absorbents prior to being deposited. The subtitle D sections of the landfill have leachate drainage systems which pumps to tanks to then be sent to the Rock River publicly owned treatment works (POTW). No pre-treatment is done. Previous issues with arsenic exceedances were corrected by mixing the different sources of leachate before sending the leachate to the POTW. Leachate volumes are increasing significantly, with 11 to 12 million gallons collected per year currently.
There are 40 wells with dewatering pumps at the NEU, with none at the WEU, NU, or SEU. Another 10 to 15 pumps are planned for the NEU. A consent order with the State of Illinois requires quarterly monitoring of depth to liquid, total liquid head, and percent of screen submerged in the gas collection wells.
Three flares are used to control the collected LFG. Gas from all of the units are co-mingled and by default all flares are operating at all times. The system capacity is 10,500 standard cubic feet per minute (scfm), with one flare at 2,500 scfm and two at 4,000 scfm. The system is typically collecting about 8,000 scfm, and so the system does not have capacity for one of the 4,000 scfm flares to go down. Some gas from the NEU and all gas from the WEU is treated to remove sulfur. The sulfur treatment has four media bed boxes, run two at a time. When one pair of boxes see sulfur breakthrough the gas is routed to the other pair. Waste Connections changes out the media of the sulfur treatment system approximately every two weeks after both pairs of boxes
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see breakthrough. When changing out the media, they stop collecting gas for 8 to 10 hours. The header vacuum at the blowers is 55 inches of water, but 25 inches are lost through the sulfur treatment system, resulting in a system vacuum of 20 to 25 inches.
Staff Interview: When EPA asked if there was any policy for when to install a de-watering pump in a well, Lacy Bollard stated that there is no prescriptive guide, but decisions are made based on water level, on-site observations, surface emissions monitoring (SEM) results, and gas quality. He agreed that it was conceivable that a well with long term 100% water obstruction would not necessarily be targeted for adding a de-watering pump if its wellhead parameters were in compliance and no SEM exceedances were found nearby. De-watering pumps are generally considered a last resort due to their technical challenges. SEM, odor detection, and cover integrity observations are used to determine whether a well is collecting all of the gas being generated near it.
The NEU has approximately 50 more wells than in the original GCCS design plan. The density of wells was originally increased so that the radius of influence and pull could be reduced to decrease air infiltration for a potential renewable natural gas (RNG) plant. Potential RNG plans have adjusted to have more flexibility with gas quality so all of the wells are being operated now with full vacuum to reduce concerns of fugitive emissions.
When EPA asked why the GCCS is shut down for when they change the carbon beds used for sulfur removal, Waste Connections stated that they cannot change the carbon media for one pair of beds while the other is running because of leaking gas creating a hydrogen sulfide exposure risk. They stated that the sulfur rich gas eats away at the valve seals resulting in leakage. Waste Connections plans on installing a new sulfur treatment system by fall 2021, which will eliminate the shutdowns at changeouts. The new system should increase GCCS system vacuum to 50 inches. Waste Connections is looking into starting a renewable natural gas facility at Winnebago, but this is not a solidified plan at this time.
Waste Connections contracts the SEM to Andrews Engineering. SEM is conducted in an enhanced program pursuant to a state consent order. The WEU and NEU are monitored monthly, while the NU/SEU is monitored quarterly. The exceedance threshold per the order is 300 parts per million (ppm), stricter than the New Source Performance Standard threshold of 500 ppm. The SEM plan requires monitoring at a grid of points as well as penetrations and at any visual indicators of potential leakage, and has an additional requirement for keeping average methane concentration below a threshold of 50 ppm averaged over grid cells designated on the landfill surface. Lacy Ballard and Josh Hay stated that historically, technicians only recorded the approximate average reading at each point, instead of recording the maximum reading observed as per Method 21.
There is one gas boundary probe on the NU, close to the boundary with the SEU on their east side, that has had problems with gas migration hits. Two other locations have been addressed with slat collectors. Waste Connections stated that they have no action plan yet for this probe.
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The Landfill has historically received a large number of complaints, typically in waves. Lately there has been a lull in complaints. When Waste Connections receives a complaint, they check the location and wind direction.
The EEU will have an entirely separate GCCS, not co-mingled with the existing flares. NSPS gas collection requirements are not yet effective for the EEU because none of the unit is at final grade and all waste there is less than 5 years old.
TOUR INFORMATION
EPA Tour of the Facility: Yes
Data Collected and Observations: EPA and IEPA conducted a partial SEM survey of the facility, with Josh Hay, a technician from Andrews Engineering confirming readings. The NEU was surveyed in the morning, and the WEU was surveyed in the afternoon. Exceedances of above 300 and 500 ppm total hydrocarbon (THC) as methane were recorded. Confirmation measurements were taken when a second instrument was available. Thirty-two SEM hits above 300 ppm were found on the NEU, of which 24 were above 500 ppm. Thirty-six hits above 300 ppm were found on the WEU, of which 35 were above 500 ppm. Hits were found both at penetrations and mid-landfill. The full SEM data and map of hits can be found in Appendix B.
WEU well #8 had a hole in the PVC header. Large portions of both the WEU and NEU were bare soil. EPA observed erosional features and leachate breakouts. Some areas of the landfill appeared to have persistently elevated methane concentrations above 100 ppm, though EPA did not evaluate if these areas were above the 50 ppm grid-average threshold from the consent order.
The instrument Josh Hay used had a length of PVC pipe affixed surrounding the probe tip. Mr. Hay stated that it was sized so when the end of the pipe was placed flush on the ground that the probe tip would be 10 centimeters from the ground. He stated that when taking a measurement at a point, he would place the probe straight down on the landfill surface and wait for two times the response time to get a reading. When asked about monitoring in areas where the temporary geomembrane scrim sat above the surface of the landfill, he said that he would try to push it down to the soil to take the reading. EPA found that this was not possible at many penetrations, as the scrim was pulled upward at the base of the wells. As a result, neither EPA nor Josh Hay were able to monitor fully around the base of many wellheads under the temporary scrims.
Clouds of dust were seen coming off of the NEU.
Photos and/or Videos: were taken during the inspection.
Field Measurements: were taken during this inspection.
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RECORDS REVIEW
Requested and reviewed prior to inspection: Cover integrity reports, from May 2020 to present PDF of the most current depiction/map of the GCCS system Map depiction of where the current working active face is located and the extent of final/intermediate cover Current GCCS Design Plan NSPS SEM reports (including any follow-up monitoring) from Q2 2020 to present with all associated recorded data Most recent depth to water measurements for each well with percent of perforation available and date of measurement, in a spreadsheet format Wellhead parameters monitoring (in spreadsheet format), including records for correction of any exceedances, from May 2020 to present Control device parameter monitoring (e.g. temperature and LFG flow to flare) in a spreadsheet format, from May 2020 to present List of any wells installed from May 2020 to present with reason for installation Waste accepted by category over the past 12 months, in a spreadsheet format if available Any performance tests for any control devices on site conducted from May 2020 to present, including but not limited to flares and any gas-to-energy engines/turbines Any gas sampling test reports (such as for HAP or for sulfur) from May 2020 to present All submitted semi-annual reports from May 2020 to present Any other records of emissions monitoring conducted over the past 12 months not included in the above Submitted applications for all active air permits A log of all citizen complaints and corresponding followup actions from May 2020 to present
CLOSING CONFERENCE
Provided U.S. EPA point of contact to the facility
Waste Connections stated that it would be interested in performing SEM monitoring via drone to reduce burden on technicians, however this would only be if it could fully replace the on-theground monitoring for compliance purposes. They additionally indicated that when they have a renewable natural gas plant that they would potentially be open to using well auto-tuning to maximize gas collection.
Requested documents: Leachate system map Copy of third party report evaluating GCCS Written operating procedures (plus correction procedures), if any, on: Cover integrity; De-watering, re-drills; Pump maintenance report from 2020 Gas and leachate flow rates by units (from the past 3 years)
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SSM logs (from the past 3 years) Media swap out logs (from the past 3 years) Odor Plan with use of scentometer/H2S measurements Documentation of repair/re-monitoring of exceedances found
Compliance Assistance: EPA gave input on how to properly conduct Method 21.
Concerns: EPA found a high rate of SEM hits, distinctly above historic rates. Some hits were at locations that were supposed to have been recently corrected. EPA was also concerned that their sulfur treatment system requires such large gas collection downtime on a regular basis.
DIGITAL SIGNATURES
DANIEL
Digitally signed by DANIEL HEINS
HEINS Date: 2021.08.02 16:56:53 -05'00'
_________________________________
Daniel Heins, Report Author
Frank,
Digitally signed by Frank, Nathan
N_a__th_a_n________D22a_:t3e_8: :21_052_-10_.50'8_0.00_'2______________
Nathan Frank, Section Chief (IL/IN)
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Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021 APPENDICES AND ATTACHMENTS Appendix A: Digital Image Log Appendix B: Field Measurement Data, Including Maps
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Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021
APPENDIX A: DIGITAL IMAGE LOG
1. Inspector Name: Daniel Heins
2. Archival Record Location: ERC Enf_WinnebagoLandfill_IL_21
Image Number 1 2 3 4 5
File Name
IMG_0313.JPG IMG_0314.JPG IMG_0315.JPG IMG_0316.JPG IMG_0317.JPG
Date/Time (Eastern) 2021-06-01 11:09 2021-06-01 14:56 2021-06-01 14:56 2021-06-01 15:08 2021-06-01 15:44
Description of Image
NEU Well 101, with leachate leak Dust clouds on NEU, as viewed from top of WEU Dust clouds on NEU, as viewed from top of WEU Leachate breakout near Well 87 (WEU) WEU Well 8, with hole in pipe.
Appendices Page 1 of 7
Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021
APPENDIX B: FIELD MEASUREMENT DATA
North Expansion Unit Hits
Well Number or Map Label A
B
C
D
F
Latitude
42.161223 42.161662 42.161754 42.162186 42.16226
Longitude
-89.05788 -89.057726 -89.057755 -89.05799 -89.057761
Reading 1 Value (ppm) 788
820
450
750
2620
105
42.163882 -89.062575 500
H (Leachate 42.161623 -89.06337 500
Riser)
I (NEU
42.159925 -89.061337 3000
Header)
4
42.160004 -89.060532 600
J (South
42.160046 -89.060286 1500
slope header
valve)
K
42.162379 -89.058211 350
L
45 36 M 29 N O L404 5 9 8 115
42.164094 -89.060831 350
42.1629
-89.06432 4000
42.162513 -89.063782 1195
42.162382 -89.063477 642
42.162286 -89.063297 430
42.162324 -89.063398 750
42.162176 -89.063302 1000
42.160401 -89.061938 1400
42.159991 -89.061222 1%
42.160546 -89.060798 3%
42.160548 -89.059938 1%
42.160669 -89.05876 1%
Reading 1 Inst
KL KL KL KL KL
KL KK
Reading 2 Value (ppm) 476
520
387
>300
558
Reading 2 Inst
KJ KJ KJ KJ KJ
450
JH
460
KL
Other Notes
Two adjacent flags
KL
2000
JH
KL
330
VM
VM
2500
KJ
VM
VM
350
KL
DJH
1.50%
KK
KL
2000
KK
KL
500
KK
KL
450
KK
KL
1000
KK
KK
670
JH
DJH
3200
JH
KK
1500
JH
KK
10000
KL
KK
4000
JH
KK
2000
JH
generally elevated area, 100 to 200 ppm verified by Connor. Area of erosion generally elevated area, 100 to 200 ppm Broken air line
Erosion trench
Appendices Page 2 of 7
Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021
North Expansion Unit Hits (continued)
Well
Latitude
Longitude
Number or
Map Label
37
42.163023 -89.058223
21
42.161302 -89.062344
R
42.1616333 -89.0578
S
42.1616833 -89.0578
T
42.1618167 -89.05775
U
42.1621667 -89.05775
W
42.1623833 -89.057867
X
42.1623333 -89.058017
95
42.161677 -89.058784
Reading 1 Value (ppm) 2% 1200 515 315 337 336 505 1902 384
Reading 1 Inst
KK DJH KJ KJ KJ KJ KJ KJ KJ
Reading 2 Value (ppm) 1200
450
Reading 2 Inst
JH JH
Other Notes
West Expansion Unit Hits
Well Number or Map Label
Latitude
D
42.152918
C
42.153208
68
42.153189
77
42.153121
B
42.154454
2
42.154478
36
42.153822
37
42.154748
49
42.154414
A
42.154331
Longitude
-89.066368 -89.06625 -89.065892 -89.073107 -89.066112 -89.066233 -89.071972 -89.069548 -89.070862 -89.0717
60
42.152764 -89.071027
23
42.152769 -89.067997
20
42.152524 -89.067284
19
42.152979 -89.067344
24
42.153215 -89.067727
84
42.15356 -89.06786
18
42.153597 -89.067555
81
42.154256 -89.067154
16
42.15451 -89.067526
Reading 1 Value (ppm) 500 360 650 13000 500 500 6000 14000 6000 8746
Reading 1 Inst
KL KL KL KL KK KK KL KL KL KJ
Reading 2 Value (ppm) 396 300 500 10000 315 430 1% 3% 12000 6000
Reading 2 Inst
KL KK KK KK KL KL KK KK KK KL
1%
KK
1000
KK
800
JH
3315
JH
1000
KK
250
JH
1800
DJH
1100
JH
2400
DJH
5800
JH
800
DJH
950
JH
5%
DJH
2500
JH
2%
DJH
1300
JH
1.30% DJH
3717
JH
Other Notes
Gurgling, possible leachate problems flag from Q1 March
Prior Flag Prior Flag Prior Flag
Appendices Page 3 of 7
Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021
West Expansion Unit Hits (continued)
Well Number or Map Label
Latitude
Longitude
35
42.154286 -89.068911
39
42.15388 -89.069742
34
42.153675 -89.069228
46
42.153918 -89.068813
27
42.153899 -89.068269
83
42.154069 -89.06785
28
42.153548 -89.068441
86
42.153377 -89.06905
40
42.153294 -89.06976
51
42.15356 -89.069993
50
42.153998 -89.070731
58
42.153705 -89.071476
E
42.1524667 -89.073817
F
42.1518333 -89.072
G
42.1518167 -89.071933
H
42.15185 -89.071817
I
42.1518667 -89.071433
Reading 1 Value (ppm) 2000 1.20% 4.20% 3% 2200 1700 4500 5% 6000 3.50% 1900 3250 503 667 1930 516 1118
Reading 1 Inst
DJH DJH DJH DJH DJH DJH DJH DJH DJH JH JH JH KJ KJ KJ KJ KJ
Reading 2 Value (ppm) 4525 8715 5.5% 2.8% 1750 1225 1503 2.6% 2300
Reading 2 Inst
JH JH JH JH JH JH JH JH JH
Other Notes
Note: Some latitude/longitude readings for hits at wellheads are approximated from a georeferenced GCCS map. Non-wellhead coordinates are derived from handheld GPS units.
Calibration and Instrument Information Karina Kuc (KK) used A56584 for the duration of the survey. Kosta Loukeris (KL) used SL1555 for the duration of the survey. Vicky Mei (VM) used A56575 until 11:10 AM, after which point Daniel Heins (DJH) used this instrument for the rest of the survey. Kaare Jacobsen (KJ) and Josh Hay (JH) used IEPA and Andrews Engineer equipment, respectively, for the duration of the survey.
8:30 AM average calibration reading with 500 ppm gas 4:00 PM drift check reading with 500 ppm gas
A56584 491
476
SL1555 A56575
493
493
450
[Instrument ran out of hydrogen gas towards
end of survey, but had all exceedances
confirmed with second instrument]
Appendices Page 4 of 7
Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021 Instrument response times were between 4 and 5 seconds. EPA calibration gases:
Air, zero grade, THC < 1 ppm, expiration 05/2026 Methane 500 ppm, expiration 05/2025 The upwind and downwind readings were taken with SL1555.
Upwind: 0.5 ppm Downwind: 0.7 ppm Map of Detected Hits SEM hit locations plotted over satellite imagery from April 7, 2019 as depicted on Google Earth. West Expansion Unit
Appendices Page 5 of 7
Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021 North Expansion Unit
Appendices Page 6 of 7
Facility Name: Winnebago Landfill Facility Location: 8403 Lindenwood Rd, Rockford, IL 61109 Date of Inspection: May 10 & June 1, 2021 North Expansion Unit west slope in detail
Appendices Page 7 of 7