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HomeMy WebLinkAboutAQ_F_0800044_20191218_CMPL_InspRpt NORTH CAROLINA DIVISION OF Washington Regional Office AIR QUALITY Avoca LLC NC Facility ID 0800044 Stack Test Observation Report County/FIPS:Bertie/015 Date: 12/19/2019 Facility Data Compliance Data Avoca LLC Observation Date 12/18/2019 841 Avoca Farm Road Observer's Name Robert Bright Merry Hill,NC 27957 Operating Status Operating Lat: 36d 0.0030m Long: 76d 42.6550m Action Code PCE and Stack Test Observed SIC: 2087/Flavoring Extracts And Syrups,nec NAILS: 31193/Flavoring Syrup and Concentrate Manufacturing Contact Data Permit Data Facility Contact Authorized Contact Technical Contact Permit 01819/T53 Brian Conner Augustinus Gerritsen Brian Conner Issued 8/6/2019 Environmental Health& Vice President Environmental Health& Expires 12/31/2021 Safety Manager (252)482-2133 Safety Manager Classification Title V (252)482-2133 (252)482-2133 Permit Status Active Inspector's Signature: 1����/fj' Comments: Boiler MACT DDDDD(CO,HCI,Hg and PM) 2019-311ST Date of Signature: De tuber 20,2019 On 12/18/19,I observed the emissions testing performed on boiler ES-BB1 and ES-13132 (20.3 MMBtu/hr max.heat input)to demonstrate compliance with 40 CFR Part 63, Subpart DDDDD, as referenced in permit specific condition 2.I.A.E. Avoca contracted McHale Environmental (Mike Dickerson) to conduct the tests. Avoca submitted a protocol on 10/15/2019, and DAQ approved the protocol by letter on 11/21/2019. Volumetric Flow,Molecular Weight,and Moisture Methods 1-4 Filterable Particulate Method 5 Carbon Monoxide Method 10 Mercury Method 30B Hydrochloric Acid Method 26A The emission limits are provided in permit condition 2.1.A.E. HCI 2.2E-02 pounds per million Btu of heat input Mercury 8.0E-07 pounds per million Btu heat input CO 620 ppm by volume on a dry basis corrected to 3 percent oxygen,3- run average Filterable PM(or TSM) 3.0E-02 pounds per million Btu heat input or(2.6E-05 pounds per million Btu heat input I arrived on-site just before the end of Run 1 of M5, M26A and M30B had already finished as they were each two hours in duration. The first CO run per Method 10 had been completed and Mike was going through the post run calibrations and bias/drift checks. Methods S and 26A Observations Metering box M-5 was used (OH - 1.89; Y— 1.023; Calibration date: 4/18/2019). Each test run was two hours in duration. Eight sampling points were used across two traverses,with sampling times of eight minutes per point. Readings were taken every four minutes(two per point). Over 100 cubic feet was pulled for each run. I observed the post-run leak checks and probe acetone rinses for runs 1 and 2 and the results are given below: Run 1: 0.002 CFM at 10"Hg(2.5"Hg was the highest vacuum during the run) https://neconnect.sharepoint.com/sites/DAQ-WaRO/FacilitiesBertieo8/00044/Stack Testing/20191218 BBI and BB2_DDDDD.stk.docx1 Steam production was around 21,000 pounds per hour and no VE was observed. The filter appeared very clean. The isokinctic rate was 105%. Run 2: 0.020 CFM at 12"Hg(8"Hg was the highest vacuum during the run) Steam production was around 24,000 pounds per hour and no VE was observed. The filter had more accumulation than that observed during run 1. Method 30B Observations Metering box HG-220-2116 was used with two activated carbon traps, A and B. The sample rate was targeted at 1 liter/minute. I was present during runs 1 and 2 and observed the following leak checks. Post run 1:A-0.011 CFM at 10"Hg and B—0.012 CFM at 10"Hg Pre-run 2:A-0.022 CFM at 10"Hg and B—0.024 CFM at 10"Hg Post run 2:A-0.007 CFM at 10"Hg and B—0.020 CFM at 10"Hg Method 10 Observations All the cylinders used for CO,CO2 and 02 were within their respective expiration date. I was onsite for runs 1 and 2 and the post run calibrations and bias/drift were within their respective limitations. Comments,Conclusions and Recommendations The stack test appeared to be conducted in accordance with the EPA methods/procedures. WaRO waits on Stationary Source Compliance Branch acceptance before pursuing any compliance action that may result from any stack tests performed. No visible emissions were observed from any other Avoca emission sources during the inspection. NORTH CAROLINA DIVISION OF Washington Regional Office AIR QUALITY Avoca LLC NC Facility ID 0800044 Stack Test Observation Report County/FIPS:Bertie/015 Date: 12/19/2019 Facility Data Compliance Data Avoca LLC Observation Date 12/18/2019 841 Avoca Farm Road Observer's Name Robert Bright Merry Hill,NC 27957 Operating Status Operating Lat: 36d 0.0030m Long: 76d 42.6550m Action Code PCE and Stack Test Observed SIC: 2087/Flavoring Extracts And Syrups,nec NAILS: 31193/Flavoring Syrup and Concentrate Manufacturing Contact Data Permit Data Facility Contact Authorized Contact Technical Contact Permit 01819/T53 Brian Conner Augustinus Gerritsen Brian Conner Issued 8/6/2019 Environmental Health& Vice President Environmental Health& Expires 12/31/2021 Safety Manager (252)482-2133 Safety Manager Classification Title V (252)482-2133 (252)482-2133 Permit Status Active Inspector's Signature: 1����/fj' Comments: Boiler MACT DDDDD(CO,HCI,Hg and PM) 2019-311ST Date of Signature: De tuber 20,2019 On 12/18/19,I observed the emissions testing performed on boiler ES-BB1 and ES-13132 (20.3 MMBtu/hr max.heat input)to demonstrate compliance with 40 CFR Part 63, Subpart DDDDD, as referenced in permit specific condition 2.I.A.E. Avoca contracted McHale Environmental (Mike Dickerson) to conduct the tests. Avoca submitted a protocol on 10/15/2019, and DAQ approved the protocol by letter on 11/21/2019. Volumetric Flow,Molecular Weight,and Moisture Methods 1-4 Filterable Particulate Method 5 Carbon Monoxide Method 10 Mercury Method 30B Hydrochloric Acid Method 26A The emission limits are provided in permit condition 2.1.A.E. HCI 2.2E-02 pounds per million Btu of heat input Mercury 8.0E-07 pounds per million Btu heat input CO 620 ppm by volume on a dry basis corrected to 3 percent oxygen,3- run average Filterable PM(or TSM) 3.0E-02 pounds per million Btu heat input or(2.6E-05 pounds per million Btu heat input I arrived on-site just before the end of Run 1 of M5, M26A and M30B had already finished as they were each two hours in duration. The first CO run per Method 10 had been completed and Mike was going through the post run calibrations and bias/drift checks. Methods S and 26A Observations Metering box M-5 was used (OH - 1.89; Y— 1.023; Calibration date: 4/18/2019). Each test run was two hours in duration. Eight sampling points were used across two traverses,with sampling times of eight minutes per point. Readings were taken every four minutes(two per point). Over 100 cubic feet was pulled for each run. I observed the post-run leak checks and probe acetone rinses for runs 1 and 2 and the results are given below: Run 1: 0.002 CFM at 10"Hg(2.5"Hg was the highest vacuum during the run) https://neconnect.sharepoint.com/sites/DAQ-WaRO/FacilitiesBertieo8/00044/Stack Testing/20191218 BBI and BB2_DDDDD.stk.docx1 Steam production was around 21,000 pounds per hour and no VE was observed. The filter appeared very clean. The isokinctic rate was 105%. Run 2: 0.020 CFM at 12"Hg(8"Hg was the highest vacuum during the run) Steam production was around 24,000 pounds per hour and no VE was observed. The filter had more accumulation than that observed during run 1. Method 30B Observations Metering box HG-220-2116 was used with two activated carbon traps, A and B. The sample rate was targeted at 1 liter/minute. I was present during runs 1 and 2 and observed the following leak checks. Post run 1:A-0.011 CFM at 10"Hg and B—0.012 CFM at 10"Hg Pre-run 2:A-0.022 CFM at 10"Hg and B—0.024 CFM at 10"Hg Post run 2:A-0.007 CFM at 10"Hg and B—0.020 CFM at 10"Hg Method 10 Observations All the cylinders used for CO,CO2 and 02 were within their respective expiration date. I was onsite for runs 1 and 2 and the post run calibrations and bias/drift were within their respective limitations. Comments,Conclusions and Recommendations The stack test appeared to be conducted in accordance with the EPA methods/procedures. WaRO waits on Stationary Source Compliance Branch acceptance before pursuing any compliance action that may result from any stack tests performed. No visible emissions were observed from any other Avoca emission sources during the inspection.