Section 229.142  Initial Performance Testing and Establishment of Operating Parameters for All HMIWIs

 

a)         Before January 1, 2014, each owner or operator of an HMIWI as defined in Section 229.110(a)(1) of this Part, subject to the emissions limits under Section 229.125(a) or Section 229.126(a) of this Part, shall comply with the following requirements:

 

1)         Except as provided in Section 229.115(a)(2)(B)(v) of this Part, conduct an initial performance test on their HMIWI by September 15, 2000.

 

2)         Except as provided in subsection (a)(3) of this Section, in the initial performance test, test for all pollutants limited pursuant to Subpart E of this Part.

 

3)         During the initial performance test, rural HMIWIs are not required to test for HCl, Pb or Cd.

 

4)         If an HMIWI is equipped with a dry scrubber followed by a fabric filter, a wet scrubber, or a dry scrubber followed by a fabric filter and wet scrubber, or a selective noncatalytic reduction system, establish the appropriate maximum and minimum operating parameter values indicated in Appendix B of this Part for the relevant control system during the initial performance test, provided that the performance test demonstrates compliance with the emission limits specified in Section 229.125 of this Part.

 

5)         If air pollution control equipment other than a dry scrubber followed by a fabric filter, a wet scrubber, a dry scrubber followed by a fabric filter and a wet scrubber, or a selective noncatalytic reduction system is used to comply with the emission limits under Section 229.125 of this Part, the initial performance test may not be conducted until site-specific operating parameters that will be monitored to demonstrate compliance with this Part have been established by the Agency in a construction permit and approved by USEPA.

 

6)         For rural HMIWI, establish the maximum charge rate and minimum secondary chamber temperature as site-specific parameters during the initial performance test, provided that the performance test demonstrates that the HMIWI is in compliance with the emission limits specified in Section 229.126 of this Part.

 

b)         On and after January 1, 2014, each owner or operator of an HMIWI, as defined in Section 229.110(a)(1) or (a)(2) of this Part, and subject to the emissions limits under Section 229.125(c) as applicable, or Section 229.126(c) of this Part, shall comply with the following requirements:

 

1)         Except as provided in Section 229.115(b)(2)(B)(v) of this Part, conduct an initial performance test on its HMIWI by January 1, 2014.

 

2)         Except as provided for in subsection (b)(6), in the initial performance test, test for all pollutants to demonstrate compliance with Section 229.125(c) or Section 229.126(c) emissions limits, as applicable, pursuant to Subpart E of this Part.

 

3)         If an HMIWI is equipped with a dry scrubber followed by a fabric filter, a wet scrubber, a dry scrubber followed by a fabric filter and wet scrubber, or a selective noncatalytic reduction system, establish the appropriate maximum and minimum operating parameter values indicated in Appendix B of this Part for the relevant control system during the initial performance test, provided that the performance test demonstrates compliance with the emission limits specified in Section 229.125 or 229.126 of this Part.

 

4)         If an air pollution control device other than a dry scrubber followed by a fabric filter, a wet scrubber, a dry scrubber followed by a fabric filter and a wet scrubber, or a selective noncatalytic reduction system is used to comply with the emission limits under Section 229.125 or Section 229.126 of this Part, the initial performance test may not be conducted until site-specific operating parameters that will be monitored to demonstrate compliance with this Part have been established by the Agency in a construction permit and approved by USEPA.

 

5)         For a rural HMIWI that is not equipped with an air pollution control device, establish the maximum charge rate and minimum secondary chamber temperature as site-specific parameters during the initial performance test, provided that the performance test demonstrates that the HMIWI is in compliance with the emission limits specified in Section 229.126(c) of this Part.

 

6)         The owner or operator of an HMIWI may use results of previous performance tests for initial compliance demonstration with the applicable emissions limits, provided the following conditions are met:

 

A)        The previous emissions tests were conducted using procedures and test methods listed in Section 229.140 of this Part or USEPA-accepted voluntary consensus standards;

 

B)        The test results are certified as representative of current operations; and

 

C)        The previous emissions tests were conducted no earlier than 1996.

 

7)         The owner or operator of an HMIWI that cannot certify and/or whose previous performance test results do not demonstrate compliance with one or more of the revised emission limits must conduct another performance test for those pollutants.

 

8)         The owner or operator of an HMIWI, as defined in Section 229.110(a)(1) or (a)(2) of this Part, and subject to the emissions limits under Section 229.125(c) as applicable, or Section 229.126(c) of this Part, as applicable, shall determine compliance with the visible emissions limit for fugitive emissions from ash handling in Sections 229.125(g) and 229.126(e) by conducting an initial performance test using Method 22, at 40 CFR 60, appendix A, incorporated by reference at Section 229.104(d) of this Part.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.144  Subsequent Performance Testing for All HMIWIs

 

a)         The owner or operator of an HMIWI may conduct a repeat performance test at any time to establish new site specific operating values for the HMIWI.  Such new site specific operating parameter values may not be relied upon until approved by the Agency as a permit condition.

 

b)         The Agency or the USEPA may request that the owner or operator of an HMIWI conduct a new performance test at any time.

 

Section 229.146  Annual Testing for Opacity

 

Following the date on which the initial performance test is completed, as required by Section 229.142 of this Section, the owners or operators of all HMIWIs shall conduct an annual opacity test, in accordance with Section 229.140 of this Part.  The opacity test schedules are as follows:

 

a)         By September 15 of each year for an HMIWI as defined in Section 229.110(a)(1) of this Part and subject to the emissions limits under Section 229.125(a) or Section 229.126(a) of this Part; and

 

b)         By January 1 of each year for an HMIWI, as defined in Section 229.110(a)(1) or (a)(2) of this Part and subject to the emissions limits under Section 229.125(c) as applicable, or Section 229.126(c) of this Part.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.148  Annual Performance Testing for All HMIWIs

 

Following the date on which the initial performance test is completed, as required by Section 229.142 of this Part, each owner or operator of an HMIWI, as applicable, shall conduct an annual performance test to determine compliance with the applicable PM, CO and HCl emission limits specified in Section 229.125 or 229.126 of this Part, using the applicable test procedures and methods specified in Section 229.140 of this Part.

 

a)         Annual performance test schedules are as follows: 

 

1)         Before January 1, 2014, each owner or operator of a small, medium, or large HMIWI as defined in Section 229.110(a)(1), subject to the emissions limits under  Section 229.125(a) of this Part, shall complete an annual performance test by September 15 of each year; and

 

2)         On and after January 1, 2014, an owner or operator of a small, rural, medium, or large HMIWI, as defined in Section 229.110(a)(1) or (a)(2), subject to the emissions limits under Section 229.125(c) as applicable, or in Section 229.126(c) of this Part, shall complete an annual performance test by January 1 of each year.

 

b)         If all 3 annual performance tests over a 3-year period indicate compliance with the applicable emission limits for PM, CO, or HCl specified in Section 229.125 of this Part, the owner or operator of an HMIWI may forego a performance test for that pollutant during the next 2 years.  If the next performance test conducted every third year indicates compliance with the emission limits for PM, CO, or HCl specified in Section 229.125 of this Part, the owner or operator of an HMIWI may forego a performance test for that pollutant for an additional 2 years from the date of the previous performance test.

 

c)         If any performance test indicates noncompliance with the respective emission limit, the owner or operator of an HMIWI shall conduct a performance test for that pollutant annually until all annual performance tests over a 3-year period indicate compliance with the respective emission limits.

 

d)         The owner or operator of an HMIWI may use any of the following types of continuous emission monitoring systems (CEMS), as provided in Section 229.152 of this Part, to substitute for annual performance tests and parameter monitoring to demonstrate compliance with applicable emissions limits:

 

1)         PM CEMS:  replace annual PM testing and opacity testing and monitoring of pressure drop across the wet scrubber, if applicable;

 

2)         CO CEMS:  replace annual CO testing and monitoring of minimum secondary chamber temperature;

 

3)         HCl CEMS:  replace annual HCl testing and monitoring of minimum HCl sorbent flow rate and minimum scrubber liquor pH.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.150  Compliance with Operating Parameter Values

 

a)         Following the date on which the initial performance test is completed, or is required to be completed under Section 229.142 of this Subpart, whichever date comes first, an HMIWI, using a dry scrubber followed by a fabric filter, a wet scrubber, or a dry scrubber followed by a fabric filter and a wet scrubber to comply with the emission limits of this Part shall not operate above any of the applicable maximum or below any of the applicable minimum operating parameters values specified in Appendix B of this Part.  All operating parameters shall be measured as a 3-hour rolling average (calculated each hour as a 3-hour rolling average of the previous 3 operating hours) at all times.  For batch HMIWIs, the charge rate shall be measured on a per batch basis.

 

b)         Except as provided in Section 229.164 of this Subpart, for an HMIWI equipped with a selective noncatalytic reduction system, operation of the HMIWI above the maximum charge rate, below the minimum secondary chamber temperature, and below the minimum reagent flow rate simultaneously shall constitute a violation of the NO_x emissions limit.

 

c)         For HMIWIs using air pollution control equipment other than a dry scrubber followed by a fabric filter, a wet scrubber, or dry scrubber followed by a fabric filter and a wet scrubber to comply with the emission limits under Section 229.125 or Section 229.126 of this Part, following the date on which the initial performance test is completed, as provided in Section 229.142 of this Part, an HMIWI shall not operate above any applicable maximum or below any applicable minimum operating parameter values established in its CAAPP permit.

 

d)         Operating parameter limits do not apply during performance tests.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.152  Compliance Requirements for HMIWIs using CEMS

 

The owner or operator of an HMIWI may use a CEMS to demonstrate compliance with any of the emission limits under Section 229.125 or Section 229.126 of this Part, if provided for in its permit.

 

a)         Any HMIWI that is allowed to use a CEMS to demonstrate compliance with the emission limits of this Part shall:

 

1)         Determine compliance with the applicable emission limits using a 12-hour rolling average, calculated each hour as the average of the previous 12 operating hours; and

 

2)         Operate all CEMS in accordance with the applicable procedures under appendices B and F of 40 CFR 60, incorporated by reference at Section 229.104(e) of this Part.

 

b)         In the case of CEMS for which USEPA has not published performance specifications, the option to use the CEMS takes effect on the date of publication of the performance specifications in the Federal Register or after site-specific operating parameters used to demonstrate compliance with this Part have been established by the Agency in a construction permit and approved by USEPA.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.154  Violations by HMIWIs Equipped with a Dry Scrubber Followed by a Fabric Filter

 

Except as provided in Section 229.164 of this Subpart, for an HMIWI equipped with a dry scrubber followed by a fabric filter:

 

a)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum secondary chamber temperature (each measured on a 3-hour rolling average) shall be a violation of the CO emissions limit;

 

b)         Simultaneous operation of an HMIWI above the maximum fabric filter inlet temperature, above the maximum charge rate, and below the minimum dioxin/furan sorbent flow rate (each measured on a 3-hour rolling average) shall be a violation of the dioxin/furan emissions limit;

 

c)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum HCl sorbent flow rate (each measured on a 3-hour rolling average) shall be a violation of the HCl emissions limit;

 

d)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum Hg sorbent flow rate (each measured on a 3-hour rolling average) shall be a violation of the Hg emissions limit;

 

e)         Use of the bypass stack at any time during operation of an HMIWI is a violation of the PM, dioxin/furan, HCl, Pb, Cd and Hg emissions limits;

 

f)         If a CO CEMS is used to determine compliance with a CO emissions limit, operation of the HMIWI above the CO emissions limit as measured by the CO CEMS shall be a violation of the emissions limit;

 

g)         If a bag leak detection system is used, failure to initiate corrective action within one hour after the bag leak detection system alarm, or failure to operate and maintain the fabric filter so that the alarm is not engaged for more than 5 percent of the total operating time in a 6-month block reporting period, shall be a violation of the PM emissions limit;

 

h)         If a bag leak detection system is used to demonstrate compliance with the opacity limit, failure to initiate corrective action within one hour after the bag leak detection system alarm shall be a violation of the opacity emissions limit;

 

i)          If a CEMS is used to determine compliance with a PM, HCl, Pb, Cd, and/or Hg emissions limit, operation of the HMIWI above the applicable emissions limit as measured by the CEMS shall be a violation of the emissions limit;

 

j)          If a continuous automated sampling system is used, operation of the HMIWI above the dioxin/furan emissions limit as measured by the continuous automated sampling system shall be a violation of the dioxin/furan emissions limit; or

 

k)         If a continuous automated sampling system is used, operation of the HMIWI above the Hg emissions limit as measured by the continuous automated sampling system shall be a violation of the Hg emissions limit.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.156  Violations by HMIWIs Equipped with a Wet Scrubber

 

Except as provided in Section 229.164 of this Subpart, for an HMIWI equipped with a wet scrubber:

 

a)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum pressure drop across the wet scrubber or below the minimum horsepower or amperage to the system (each measured on a 3-hour rolling average) is a violation of the PM emissions limit;

 

b)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum secondary chamber temperature (each measured on a 3-hour rolling average) is a violation of the CO emissions limit;

 

c)         Simultaneous operation of an HMIWI above the maximum charge rate, below the minimum secondary chamber temperature and below the minimum scrubber liquor flow rate (each measured on a 3-hour rolling average) is a violation of the dioxin/furan emissions limit;

 

d)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum scrubber liquor pH (each measured on a 3-hour rolling average) is a violation of the HCl emissions limit;

 

e)         Simultaneous operation of an HMIWI above the maximum flue gas temperature and above the maximum charge rate (each measured on a 3-hour rolling average) is a violation of the Hg emissions limit;

 

f)         Use of the bypass stack at any time during operation of an HMIWI is a violation of the PM, dioxin/furan, HCl, Pb, Cd and Hg emissions limits;

 

g)         If a CO CEMS is used to determine compliance with a CO emissions limit, operation of the HMIWI above the CO emissions limit as measured by the CO CEMS shall be a violation of the emissions limit;

 

h)         If a CEMS is used to determine compliance with a PM, HCl, Pb, Cd, and/or Hg emissions limit, operation of the HMIWI above the applicable emissions limit as measured by the CEMS shall be a violation of the emissions limit;

 

i)          If a continuous automated sampling system is used, operation of the HMIWI above the dioxin/furan emissions limit as measured by the continuous automated sampling system shall be a violation of the dioxin/furan emissions limit; or

 

j)          If a continuous automated sampling system is used, operation of the HMIWI above the Hg emissions limit as measured by the continuous automated sampling system shall be a violation of the Hg emissions limit.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.158  Violations by HMIWIs Equipped with a Dry Scrubber Followed by a Fabric Filter and a Wet Scrubber

 

Except as provided in Section 229.164 of this Subpart, for an HMIWI equipped with a dry scrubber followed by a fabric filter and a wet scrubber:

 

a)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum secondary chamber temperature (each measured on a 3-hour rolling average) is a violation of the CO emissions limit;

 

b)         Simultaneous operation of an HMIWI above the maximum fabric filter inlet temperature, above the maximum charge rate and below the minimum dioxin/furan sorbent flow rate (each measured on a 3-hour rolling average) is a violation of the dioxin/furan emissions limit;

 

c)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum scrubber liquor pH (each measured on a 3-hour rolling average) is a violation of the HCl emissions limit;

 

d)         Simultaneous operation of an HMIWI above the maximum charge rate and below the minimum Hg sorbent flow rate (each measured on a 3-hour rolling average) is a violation of the Hg emissions limit; or

 

e)         Use of the bypass stack at any time during operation of an HMIWI is a violation of the PM, dioxin/furan, HCl, Pb, Cd and Hg emissions limits;

 

f)         If CO CEMS is used to determine compliance with a CO emissions limit, operation of the HMIWI above the CO emissions limit as measured by the CO CEMS shall be a violation of the emissions limit;

 

g)         If a bag leak detection system is used, failure to initiate corrective action within one hour after the bag leak detection system alarm, or failure to operate and maintain the fabric filter so that the alarm is not engaged for more than 5 percent of the total operating time in a 6-month block reporting period, shall be a violation of the PM emissions limit;

 

h)         If a bag leak detection system is used to demonstrate compliance with the opacity limit, failure to initiate corrective action within one hour after the bag leak detection system alarm shall be a violation of the opacity emissions limit;

 

i)          If CEMS is used to determine compliance with a PM, HCl, Pb, Cd, and/or Hg emissions limit, operation of the HMIWI above the applicable emissions limit as measured by the CEMS shall be a violation of the emissions limit;

 

j)          If a continuous automated sampling system is used, operation of the HMIWI above the dioxin/furan emissions limit as measured by the continuous automated sampling system shall be a violation of the dioxin/furan emissions limit; or

 

k)         If a continuous automated sampling system is used, operation of the HMIWI above the Hg emissions limit as measured by the continuous automated sampling system shall be a violation of the Hg emissions limit.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.160  Compliance Requirements for Rural HMIWIs

 

a)         Prior to January 1, 2014, the requirements set forth in subsections (c) through (e) of this Section shall apply to all rural HMIWIs subject to the emissions limits under Section 229.126 of this Part.

 

b)         On and after January 1, 2014, the requirements set forth in subsections (c) through (e) of this Section shall apply to all rural HMIWIs that are not equipped with an air pollution control device and that are subject to the emissions limits under Section 229.126 of this Part.

 

c)         Following the date on which the initial performance test is completed or is required to be completed under Section 229.142 of this Subpart, whichever date comes first, the owners or operators of rural HMIWI shall not operate their HMIWI either above the maximum charge rate or below the minimum secondary chamber temperature measured as 3-hour rolling averages (calculated each hour as the average of the previous 3 operating hours) at all times.

 

d)         Operating parameter limits do not apply during performance tests.

 

e)         Except as provided in Section 229.164 of this Subpart, the simultaneous operation of a rural HMIWI above the maximum charge rate and below the minimum secondary chamber temperature (calculated as a 3-hour rolling average) shall constitute a violation of the PM, CO and dioxin/furan emission limits.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.162  Inspection Requirements for All HMIWIs

 

a)         Before January 1, 2014, each owner or operator of a rural HMIWI subject to the emission limits under Section 229.126 of this Part shall inspect the HMIWI according to the following schedule:

 

1)         An initial inspection shall be conducted by September 15, 2000; and

 

2)         An annual inspection shall be conducted by September 15 of each year thereafter.

 

b)         Each equipment inspection shall be conducted to ensure the proper operation of the HMIWI and, at a minimum, shall consist of the following steps:

 

1)         An inspection of all burners, pilot assemblies, and pilot sensing devices, cleaning the pilot flame sensor, as necessary;

 

2)         An inspection of the primary and secondary chamber combustion air flow, adjusting, as necessary;

 

3)         An inspection of the hinges and door latches, lubricating, as necessary;

 

4)         An inspection of dampers, fans, and blowers;

 

5)         An inspection of the HMIWI door and door gaskets;

 

6)         An inspection of all HMIWI motors;

 

7)         An inspection of the primary chamber refractory lining, cleaning, repairing or replacing the lining, as necessary;

 

8)         An inspection of the incinerator shell for corrosion or hot spots;

 

9)         An inspection of the secondary/tertiary chamber and stack, cleaning as necessary;

 

10)         Where applicable, an inspection of the mechanical loader, including limit switches;

 

11)         A visual inspection of the waste bed (grates), repairing or sealing, as necessary;

 

12)         Where applicable, an inspection of air pollution control devices to ensure their proper operation;

 

13)         Where applicable, an inspection of the waste heat boiler systems;

 

14)         An inspection of all bypass stack components;

 

15)         Calibration of thermocouples, sorbent feed systems and monitoring equipment; and

 

16)         A general inspection of all equipment to ensure that it is maintained in good operating condition.

 

c)         The owner or operator of an HMIWI shall document that, during the burn cycle immediately following the inspection required by this Section, the HMIWI is operating properly and make any necessary adjustments.

 

d)         All maintenance, adjustments, or repairs identified during the equipment inspection required under this Section shall be completed within 10 days after the inspection. The owner or operator of an HMIWI may have a longer period of time in which to complete any repairs identified as a result of the inspection required by this Section, provided that it makes this request to the Agency in writing, and the Agency approves the owner or operator of an HMIWI's request in writing.

 

e)         The owner or operator of a small, rural, medium, or large HMIWI subject to the emission limits under Section 229.125(c) as applicable, or Section 229.126 of this Part, shall inspect the HMIWI as outlined in subsection (b) of this Section, according to the following schedule:

 

1)         An initial equipment inspection shall be conducted by January 1, 2014; and

 

2)         An annual equipment inspection shall be conducted by January 1 of each year thereafter.

 

f)         The owner or operator of an HMIWI subject to the emissions limits under Section 229.125(c) as applicable, or Section 229.126(c) of this Part, shall inspect the air pollution control devices, according to the following schedule:

 

1)         An initial air pollution control device inspection shall be conducted by January 1, 2014; and

 

2)         An annual air pollution control device inspection shall be conducted by January 1 of each year thereafter.

 

g)         Each air pollution control device inspection, as applicable, shall be conducted to ensure the proper operation of the device and, at a minimum, shall consist of the following steps:

 

1)         Where applicable, an inspection of the thermocouples, sorbent feed systems, and any other monitoring equipment, adjusting applicable calibrations, as necessary; and

 

2)         A general inspection of the equipment to ensure that it is maintained in good operating condition.

 

h)         All maintenance, adjustments, or repairs identified during an air pollution control device inspection required under this Section shall be completed within 10 days after the inspection. The owner or operator of an HMIWI may have a longer period of time in which to complete any repairs identified as a result of the inspection required by this Section, provided that it makes this request to the Agency in writing and the Agency approves the request in writing.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.164  Optional Performance Testing to Address Actual or Potential Violations

 

The owner or operator of an HMIWI may conduct another performance test within 30 days after exceeding an applicable operating parameter value in order to demonstrate that an HMIWI is not in violation of the applicable emission limits.  In addition to the applicable performance testing provisions under this Part, any performance test conducted pursuant to this Section shall meet the following conditions:

 

a)         All tests shall use the same operating parameter values that indicated a violation under Section 229.154, 229.156, 229.158 or 229.160 of this Subpart;

 

b)         The owner or operator of an HMIWI shall notify the Agency in writing at least 21 days before the date of any optional performance test;

 

c)         The owner or operator of an HMIWI shall notify the Agency in writing of its intent to proceed with the optional performance test 5 days prior to conducting the test; and

 

d)         The owner or operator of an HMIWI shall conduct the optional performance test using the same approved performance test plan that was used for the performance test in which the violated operating parameter values were established.

SUBPART I: MONITORING REQUIREMENTS

 

Section 229.166  Monitoring Requirements for All HMIWIs

 

a)         Each owner or operator of an HMIWI subject to the emissions limits under Section 229.125(c) as applicable, or Section 229.126(c) of this Part, shall comply with requirements of this Section according to the following schedule:

 

1)         Before January 1, 2014, for a small, medium or large HMIWI;

 

2)         On and after January 1, 2014, except as provided for in Section 229.115(b)(3) or Section 229.116(c)(4), for a small, medium or large HMIWI and a rural HMIWI that is equipped with an air pollution control device.

 

b)         Once the initial performance test required by Section 229.142 of this Part has been performed, and the site-specific minimum and maximum operating parameter values have been established, the owner or operator of an HMIWI, as applicable, shall continuously monitor those parameters.

 

c)         The owner or operator of an HMIWI, as applicable, shall comply with the following monitoring requirements:

 

1)         Install, calibrate according to manufacturer's specifications, maintain, and operate devices or establish methods for monitoring the applicable maximum and minimum operating parameters specified in Appendix B of this Part (unless CEMS are used as a substitute for certain parameters as specified) so that these devices or methods measure and record values for these operating parameters at the frequencies indicated in Appendix B of this Part at all times;

 

2)         Install, calibrate according to manufacturer's specifications, maintain, and operate a device or establish a method for identifying the use of the bypass stack, including date, time, and duration of use;

 

3)         If control equipment other than a dry scrubber followed by a fabric filter, a wet scrubber, a dry scrubber followed by a fabric filter and a wet scrubber, or a selective noncatalytic reduction system is used to comply with the applicable emissions limits under Section 229.125(c) as applicable, or Section 229.126(c) of this Part, install, calibrate according to manufacturer's specifications, maintain, and operate the equipment necessary to monitor the site-specific operating parameters developed and approved pursuant to Section 229.142(a)(5) or (b)(5) of this Part; and

 

4)         Record monitoring data at all times during HMIWI operation, except during the periods of monitoring equipment malfunction, calibration, or repair.  At a minimum, valid monitoring data shall be recorded for 75 percent of the operating hours per day for 90 percent of the operating days per calendar quarter that an HMIWI is combusting hospital waste or medical/infectious waste.

 

d)         If an HMIWI is equipped with an air pollution control device that includes a fabric filter and a PM CEMS is not used to demonstrate compliance, the owner or operator of the HMIWI may use a bag leak detection system to determine compliance with the PM emissions limit.  The owner or operator shall meet the following requirements for each bag leak detection system installed:

 

1)         Each triboelectric bag leak detection system may be installed, calibrated, operated, and maintained according to the "Fabric Filter Bag Leak Detection Guidance," as incorporated by reference in Section 229.104;

 

2)         The bag leak detection system shall be certified by the manufacturer as being capable of detecting PM emissions at concentrations of 10 milligrams per actual cubic meter (0.0044 grains per actual cubic foot) or less;

 

3)         The bag leak detection system sensor shall provide an output of relative PM loadings;

 

4)         The bag leak detection system shall be equipped with a device to continuously record the output signal from the sensor;

 

5)         The bag leak detection system shall be equipped with an audible alarm system that sounds automatically when an increase in relative PM emissions over a preset level is detected.  The alarm shall be located where it is easily heard by plant operating personnel;

 

6)         For positive pressure fabric filter systems, a bag leak detector shall be installed in each baghouse compartment or cell;

 

7)         For negative pressure or induced air fabric filters, a bag leak detector shall be installed downstream of the fabric filter;

 

8)         If multiple bag leak detectors are required, the bag leak detection system's instrumentation and alarm may be shared among detectors;

 

9)         The baseline output shall be established by adjusting the range and the averaging period of the device and establishing the alarm set points and the alarm delay time according to section 5.0 of the "Fabric Filter Bag Leak Detection Guidance," as incorporated by reference in Section 229.104;

 

10)         Following initial adjustment of the system, the sensitivity or range, averaging period, alarm set points, or alarm delay time may not be adjusted.  Increasing the sensitivity by more than 100 percent or decreasing by more than 50 percent over a 365-day period is a violation, unless the adjustment follows a complete fabric filter inspection that demonstrates that the fabric filter is in good operating condition. Each adjustment shall be recorded;

 

11)         Records of the results of each inspection, calibration, and validation check shall be maintained; and

 

12)         The fabric filter must be operated and maintained so that the bag leak detection system alarm is not engaged for more than 5 percent of the total operating time in a 6-month block reporting period; however, corrective action must be initiated within 1 hour after the alarm.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.168  Monitoring Requirements for Rural HMIWIs

 

a)         Each owner or operator of a rural HMIWI subject to the emissions limits under Section 229.126 of this Part shall comply with requirements of this Section according to the following schedule:

 

1)         Before January 1, 2014, for a rural HMIWI; and

 

2)         On and after January 1, 2014, except as provided for in Section 229.115(b)(3) or Section 229.116(c)(4), for a rural HMIWI that is not equipped with an air pollution control device.

 

b)         The owner or operator of each rural HMIWI shall comply with the following monitoring requirements:

 

1)         Install, calibrate according to manufacturer's specifications, maintain and operate a device measuring and recording the temperature of the secondary chamber on a continuous basis, the output of which shall be recorded, at a minimum, once every minute of operation;

 

2)         Install, calibrate according to manufacturer's specifications, maintain, and operate a device that automatically measures and records the date, time, and weight of each charge fed into an HMIWI; and

 

3)         Record monitoring data at all times during HMIWI operation, except during periods of monitoring equipment malfunction, calibration, or repair.  At a minimum, valid monitoring data shall be recorded for 75 percent of the operating hours per day for 90 percent of the operating hours per calendar quarter that an HMIWI is combusting hospital waste or medical/infectious waste.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

SUBPART J: REQUIREMENTS FOR HMIWI OPERATORS

 

Section 229.170  Operator Training and Qualification Requirements

 

a)         No HMIWI shall be operated unless a trained and qualified HMIWI operator, as specified in this Section, is available on-site to operate or supervise the operation of the HMIWI.

 

b)         To become a trained and qualified operator, a person shall complete a training program that, at a minimum, meets the criteria specified in subsection (c) of this Section, pass the examination administered in accordance with subsection (c)(2) of this Section and have either 6 months experience as an HMIWI operator or have completed 2 burn cycles under the observation of 2 trained and qualified HMIWI operators.

 

c)         An operator training program shall satisfy all of the following criteria:

 

1)         Consist of at least 24 hours of training covering the following subjects:

 

A)        Work safety procedures;

 

B)        Pre-startup procedures;

 

C)        Environmental concerns, including pathogen destruction and types of emissions;

 

D)        Basic combustion principles, including combustion byproducts;

 

E)        Instruction in the proper operation of the same type of incinerator that will be used by the operator, including proper startup, waste charging, and shutdown procedures;

 

F)         Combustion controls and monitoring;

 

G)        Operation of air pollution control equipment and factors affecting performance;

 

H)        Methods for monitoring pollutants, both by CEMS and by monitoring of HMIWI and air pollution control device operating parameters, and monitoring instrument calibration procedures;

 

I)         Inspection and maintenance of an HMIWI, air pollution control equipment, and CEMS;

 

J)         Corrective measures to remedy malfunctions and conditions that may lead to malfunction;

 

K)        Characteristics of and proper handling procedures for bottom and fly ash;

 

L)        Recordkeeping procedures; and

 

M)       Applicable Federal, State, and local regulations.

 

2)         Administer an examination designed by the course instructor; and

 

3)         Provide reference materials covering all of the course topics specified in subsection (c)(1) of this Section.

 

d)         Operator qualification is valid from the date on which the examination specified in subsection (c)(2) of this Section is passed, or the completion of the experience requirements set forth in subsection (b) of this Section, whichever is later.

 

e)         In order for an operator that has been qualified in accordance with subsection (b) of this Section to maintain the necessary qualification status, the operator shall:

 

1)         Complete and pass an annual review course of at least 4 hours in length that, at a minimum, covers the following subjects:

 

A)        An update of applicable regulations;

 

B)        Proper incinerator operation, including startup and shutdown procedures;

 

C)        Proper incinerator inspection and maintenance;

 

D)        Responses to malfunctions and conditions that may lead to malfunction; and

 

E)        A discussion of operating problems encountered by attendees.

 

2)         If an operator fails to either take or to complete and pass the annual review course, the operator's qualification will lapse.

 

3)         If the operator's qualification lapses for less than 3 years, qualification may be reinstated by taking and passing the annual review course, as provided under subsection (e)(1) of this Section.

 

4)         If there is a 3 year or greater lapse in an operator's qualification, then the operator shall take and pass an operator training course, as provided for under subsection (c) of this Section, in order to reinstate the qualification.

 

Section 229.172  Documentation To Be Maintained On-Site for Employees Operating HMIWIs

 

a)         The owner or operator of an HMIWI shall maintain the following information on-site for the use and reference of HMIWI operators:

 

1)         A summary of the applicable requirements under this Part;

 

2)         A description of basic combustion theory applicable to HMIWIs;

 

3)         Procedures for receiving, handling, and charging waste;

 

4)         Procedures for startup and shutdown of the HMIWI;

 

5)         Procedures for maintaining proper combustion air supply levels;

 

6)         Procedures for operating the HMIWI and associated air pollution control systems within the standards established under this Part;

 

7)         Procedures for responding to periodic malfunction or conditions that may lead to malfunction;

 

8)         Procedures for monitoring HMIWI emissions;

 

9)         Recordkeeping and reporting procedures; and

 

10)         Procedures for handling ash.

 

b)         The owner or operator of an HMIWI shall establish a program for the annual review of all of the information listed under subsection (a) of this Section by all employees that operate an HMIWI.

 

1)         The initial review of the information listed in  subsection (a) of this Section shall be conducted by September 15, 2000, or prior to assuming responsibilities for operating an HMIWI, whichever is later;

 

2)         Subsequent reviews of the information contained in subsection (a) of this Section shall be conducted annually.

 

c)         The information identified in subsection (a) of this Section shall be kept in a location readily accessible to all HMIWI operators.

SUBPART K: WASTE MANAGEMENT PLAN REQUIREMENTS

 

Section 229.176  Waste Management Plan Requirements for Hospitals Using On-Site Incinerators

 

a)         The owner or operator of a hospital subject to the requirements in this Part shall submit to the Agency, in accordance with Section 229.184(b) of this Part, a waste management plan.  Such plans shall outline technically and economically feasible policies and practices for reducing the amount and toxicity of hospital and medical/infectious waste incinerated at the hospital. The waste management plan shall include the following components:

 

1)         The name and location of the facility;

 

2)         A written policy statement setting forth management support for waste management and implementation of the plan;

 

3)         A statement of goals for reducing the volume and toxicity of waste, expressed numerically where feasible;

 

4)         Identification of the staff responsible for development and implementation of the plan, as well as a description of their roles and responsibilities;

 

5)         A description of communication and education programs to make employees aware of the waste management program and their responsibilities;

 

6)         A summary of existing waste management policies and practices;

 

7)         Identification of technically and economically feasible waste management policies and practices to be implemented and, where practical, a schedule for the implementation of the selected measures; and

 

8)         Procedures for tracking implementation of the plan and progress toward achieving the goals.

 

b)         Prior to the development of the waste management plan, the hospital shall assess:

 

1)         Current waste management practices;

 

2)         All of the available data that it has collected on the types, quantities, and sources of its waste;

 

3)         Technical information on alternative waste management practices, such as the American Hospital Association publication entitled "An Ounce of Prevention: Waste Management Strategies for Health Care Facilities," incorporated by reference at Section 229.104(a) of this Part; and

 

4)         The feasibility of implementing additional waste management policies and practices, taking into account such considerations as:

 

A)        The effectiveness of existing policies and practices;

 

B)        The costs of additional measures;

 

C)        The potential effects on patient care and worker safety;

 

D)        The environmental benefits and savings;

 

E)        The recycling options available in the area; and

 

F)         The availability of products or equipment needed to implement alternative measures.

 

c)         The following measures, at a minimum, shall be considered when evaluating alternative waste management practices and developing waste management policies and procedures:

 

1)         Segregating waste streams;

 

2)         Phasing out the use of products containing toxic materials;

 

3)         Reusing products and equipment;

 

4)         Reducing the use of packaging and disposable items;

 

5)         Collecting recyclable materials; and

 

6)         Improving inventory control, training and housekeeping practices.

 

d)         Any waste management plan that has been developed by a hospital subject to the requirements of this Part prior to May 15, 1999 may be incorporated into the waste management plan required by this Section for that hospital, to the extent that such a plan is consistent with the requirements of this Section.

 

e)         The owner or operator of each affected hospital shall submit a waste management plan to the Agency at the same time site-specific operating parameters are reported, as specified in Section 229.184(b) of this Part.

 

f)         The waste management plan shall be updated every 5 years to coincide with either the issuance or renewal of the facility's CAAPP permit.

 

g)         The owner or operator of each affected hospital shall submit a waste management progress report to the Agency annually, along with the annual emissions report required by 35 Ill. Adm. Code 201.302 and 254.  The progress report shall include the following elements:

 

1)         A description of progress made during the previous calendar year toward meeting the goals established in the plan;

 

2)         A summary of the waste management practices that were implemented; and

 

3)         Any amendments to the plan along with a brief explanation of the need for the amendments.

 

h)         Upon written request, the affected hospital shall make the waste management plan and annual progress reports available for public review during normal business hours.

 

Section 229.178  Waste Management Plan Requirements for Hospitals Transporting Waste Off-Site to an HMIWI  

 

a)         By September 15, 2000, the owner or operator of any hospital that transfers hospital or medical/infectious waste off-site to an HMIWI shall conduct an assessment of its current waste management program and consider additional technically and economically feasible measures for reducing the volume and toxicity of waste to be incinerated.

 

b)         In identifying additional technically and economically feasible waste management practices, the owner or operator shall consider:

 

1)         Segregating waste streams;

 

2)         Phasing out the use of products containing toxic materials;

 

3)         Reusing products and equipment;

 

4)         Reducing the use of packaging and disposable items;

 

5)         Collecting recyclable materials; and

 

6)         Improving inventory control, training and housekeeping practices.

 

c)         Within 1 year after the assessment conducted pursuant to subsection (a) of this Section, and annually thereafter, affected hospitals shall submit a waste management progress report to the Agency.  The progress report shall summarize any waste management policies and practices that were implemented in the previous calendar year.

 

Section 229.180  Waste Management Requirements for Commercial HMIWIs

 

a)         The owner or operator of any commercial HMIWI that accepts hospital waste or medical/infectious waste generated off-site shall:

 

1)         Provide hospital, medical or infectious waste customers with written information at least once a year concerning the availability of waste management practices for reducing the volume and toxicity of waste to be incinerated;

 

2)         Conduct training and education programs in waste segregation for each of the company's waste generator customers;

 

3)         Ensure that each waste generator customer prepares its own waste management plan that includes, at a minimum, the following elements:

 

A)        Segregation of recyclable wastes such as paper products, glass, batteries and metals;

 

B)        Segregation of non-recyclable wastes such as polyvinyl chloride plastics, pharmaceutical waste, and mercury-containing waste; and

 

C)        Purchasing recycled or recyclable products;

 

4)         Submit a waste management plan to the Agency, in accordance with Section 229.184(b) of this Part, that outlines the efforts that will be undertaken to implement the requirementsspecified in subsections (a)(1) through (a)(3) of this Section.

 

b)         Paper or electronic copies of the materials disseminated under this Section shall be made available to the Agency upon written request.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.181  Waste Management Plan Requirements for Other HMIWIs

 

The owner or operator of an HMIWI that is subject to emission limits in Subpart E of this Part, but is not subject to the waste management plan provisions of Section 229.176 or 229.180 of this Subpart, shall develop a waste management plan in accordance with this Section.

 

(a)        The owner or operator of an HMIWI subject to this Section shall conduct an assessment of its current waste management program and submit a waste management plan to the Agency, in accordance with Section 229.184(b) of this Part, that:

 

1)         Identifies, pursuant to subsection (b) of this Section, the additional technically and economically feasible measures for reducing the volume and toxicity of the waste to be incinerated; and

 

2)         Where practical, outlines a schedule for the implementation of the selected measures.

 

(b)        In identifying additional technically and economically feasible waste management practices, the owner or operator shall consider:

 

1)         Segregating waste streams;

 

2)         Phasing out the use of products containing toxic materials;

 

3)         Reusing products and equipment;

 

4)         Reducing the use of packaging and disposable items;

 

5)         Collecting recyclable materials; and

 

6)         Improving inventory control, training, and housekeeping practices.

 

(c)        In assessing its current waste management practices, the facility shall consider technical information on alternative waste management practices, such as the American Hospital Association publication entitled "An Ounce of Prevention: Waste Management Strategies for Health Care Facilities," incorporated by reference at Section 229.104(a) of this Part.

 

(d)       Any waste management plan that has been developed by a facility subject to this Section before May 15, 1999 may be incorporated into the waste management plan required for that facility, to the extent that such a plan is consistent with the requirements of this Section.

 

(e)        The waste management plan shall be updated every 5 years to coincide with either the issuance or renewal of the facility's CAAPP permit.

SUBPART L: RECORDKEEPING AND REPORTING REQUIREMENTS

 

Section 229.182  Recordkeeping Requirements

 

a)         The owner or operator of an HMIWI subject to the emissions limits under Subpart E of this Part shall maintain records of the following information:

 

1)         The calendar date of each record;

 

2)         The following data, where applicable:

 

A)        Concentrations of all applicable pollutants listed in Section 229.125(a) or (c), or in Section 229.126(a) or (c) of this Part (as determined by the CEMS, if applicable), and any measurements of opacity as required under Section 229.125(b), (d), or (f) or Section 229.126(b) or (d);

 

B)        HMIWI charge dates, times and weights, and hourly charge rates;

 

C)        If a fabric filter is used, the fabric filter inlet temperatures during each minute of operation;

 

D)        The amount and type of dioxin/furan sorbent used during each hour of operation;

 

E)        The amount and type of Hg sorbent used during each hour of operation;

 

F)         The amount and type of HCl sorbent used during each hour of operation;

 

G)        If a selective noncatalytic reduction system is used to comply, the amount and type of NO_x reagent used during each hour of operation;

 

H)        If a selective noncatalytic reduction system is used to comply, the minimum secondary chamber temperature recorded during each minute of operation;

 

I)         The secondary chamber temperatures recorded during each minute of operation;

 

J)         The liquor flow rate to the wet scrubber inlet during each minute of operation;

 

K)        The horsepower or amperage to the wet scrubber during each minute of operation;

 

L)        Any pressure drop across the wet scrubber system during each minute of operation;

 

M)       The temperature at the outlet from the wet scrubber during each minute of operation;

 

N)        The pH at the inlet to the wet scrubber during each minute of operation;

 

O)        Identification of any use of the bypass stack, including dates, times, and the duration of such use;

 

P)         For sources complying with Section 229.166(c) of this Part, all operating parameter data collected; and

 

Q)        If a bag leak detection system is used, maintain records of the system alarm, the time of the alarm, the time corrective action was initiated and completed, and a brief description of the cause of the alarm and the corrective action taken, as applicable;

 

3)         Identification of any calendar days for which data on emissions rates or operating parameters specified under subsection (a)(2) of this Section have not been obtained, with an identification of the emissions rates or operating parameters not measured, reasons for not obtaining data, and a description of the corrective actions taken;

 

4)         Identification of any malfunctions, including the calendar date, the time and duration, and a description of the malfunction and of the corrective action taken to remedy it;

 

5)         Identification of calendar days for which data on emissions rates or operating parameters specified under subsection (a)(2) of this Section exceeded the applicable limits, with a description of the exceedences, reasons for such exceedences, and a description of the corrective actions taken;

 

6)         The results of the initial, annual, and any other subsequent performance tests conducted to determine compliance with the applicable emissions limits and/or to establish or re-establish operating parameters, as applicable, and a description, including sample calculations, of how the operating parameters were established or re-established, if applicable;

 

7)         Records of calibration of any monitoring devices as required under Sections 229.166(c)(1), (2) and (3) and 229.168 (b)(1) and (2) of this Part; and

 

8)         Identification of the names of all HMIWI operators who have met the criteria for qualification under Section 229.170 of this Part, including:

 

A)        Documentation of training and the dates of the training; and

 

B)        The date of the initial review and all subsequent annual reviews of the information specified in Section 229.172(a) of this Part, as required by Section 229.172(b) of this Part.

 

b)         The owner or operator of an HMIWI claiming an exemption from the emissions limits in this Part pursuant to Section 229.110(b) of this Part shall keep contemporaneous records identifying each period of time when only pathological waste, low-level radioactive waste, or chemotherapeutic waste is burned, including the calendar date and duration of such periods.

 

c)         The owner or operator of an HMIWI claiming an exemption pursuant to Section 229.110(c) of this Part shall keep records on a calendar quarter basis demonstrating that only pathological waste, low-level radioactive waste, or chemotherapeutic waste is burned.

 

d)         The owner or operator of a co-fired combustor claiming an exemption from the emissions limits under Section 229.110(d) of this Part shall maintain records on a calendar quarter basis of the relative weight of hospital waste and/or medical/infectious waste, and of all other fuels or waste combusted.

 

e)         The owner or operator of each HMIWI subject to the emissions limits under Section 229.125(c) or Section 229.126 of this Part shall maintain records of the annual equipment inspection required under Section 229.162 of this Part.

 

f)         The owner or operator of each HMIWI subject to the emissions limits under Section 229.125(c) or 229.126(c) of this Part shall maintain records of the annual air pollution control device inspection required under Section 229.162 of this Part.

 

g)         If a bag leak detection system is used, the owner or operator shall maintain records of the system alarm, the time of the alarm, the time corrective action was initiated and completed, a brief description of the cause of the alarm and the corrective action taken, as applicable.

 

h)         The owner or operator of each HMIWI, when applicable, shall maintain records of any required maintenance, adjustments, or repairs identified during an inspection required under Section 229.162 of this Part not completed within 10 days after the inspection or the timeframe approved in writing by the Agency.

 

i)          All records required under this Section shall be maintained onsite for a period of 5 years, in either paper copy or electronic format, unless an alternative format has been approved by the Agency in a permit condition.

 

j)          All records required to be maintained pursuant to this Section shall be made available to the Agency upon request.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.184  Reporting Requirements

 

a)         The facilities manager and the responsible official for the affected source shall certify each report required under this Section.

 

b)         The owner or operator of an HMIWI shall submit to the Agency the results of any performance test conducted on the HMIWI within 60 days after conducting the performance test.  The information submitted with the initial performance test required by Section 229.142 of this Part shall include:

 

1)         Before January 1, 2014, except as provided for in Section 229.115(b)(3) or Section 229.116(c)(4), as applicable, the test data and values for the site-specific operating parameters established pursuant to Section 229.142(a)(4), (5) or (6), as applicable, and a description, including sample calculations, of how the operating parameters were established during the initial performance test for an HMIWI subject to the emissions limits under Section 229.125(a) or 229.126(a) of this Part;

 

2)         On and after January 1, 2014, the test data and values for the site-specific operating parameters established pursuant to Section 229.142(b)(3), (4) or (5), as applicable, and a description, including sample calculations, of how the operating parameters were established during the initial performance test for an HMIWI subject to the emissions limits under Section 229.125(c) or Section 229.126(c) of this Part;

 

3)         If a bag leak detection system is used, analysis and supporting documentation demonstrating conformance with guidance and specifications for bag leak detection systems in Section 229.166(d)(1); and

 

4)         A copy of the waste management plan required under Subpart K of this Part.

 

c)         All owners or operators of HMIWIs shall submit the information specified under this subsection (c) to the Agency, as follows:

 

1)         By September 15, 2001, and by September 15 of each year thereafter, for an HMIWI subject to the emissions limits under Section 229.125(a) or 229.126(a) of this Part;

 

2)         By January 1, 2014, and by January 1 of each year thereafter, except as provided for in Section 229.115(b)(3) or Section 229.116(c)(4), as applicable, for an HMIWI subject to the emissions limits under Section 229.125(c) or (e) or Section 229.126(c) of this Part; and

 

3)         The annual report required under subsection (c)(1) or (2 ) of this Section shall include the following information:

 

A)        Before January 1, 2014, the values for site-specific operating parameters established pursuant to Section 229.142(a)(4), (5) or (6) of this Part, as applicable;

 

B)        On and after January 1, 2014, except as provided for in Section 229.115(b)(3) or Section 229.116(c)(4), as applicable, the values for site-specific operating parameters established pursuant to Section 229.142(b)(3), (4) or (5) of this Part, as applicable;

 

C)        The highest maximum operating parameter and the lowest minimum operating parameter, as applicable, for each operating parameter, recorded for the calendar year being reported pursuant to Section 229.142(a)(4), (5) or (6), or Section 229.142(b)(3), (4) or (5) of this Part, as applicable;

 

D)        The highest maximum operating parameter and the lowest minimum operating parameter, as applicable, for each operating parameter recorded pursuant to Section 229.142(a)(4), (5) or (6) or Section 229.142(b)(3), (4) or (5) of this Part, as applicable, for the calendar year preceding the year being reported, in order to provide the Agency with a summary of the performance of the affected facility over a 2-year period;

 

E)        Any information recorded pursuant to Section 229.182(a)(3) through (5) of this Subpart for the calendar year being reported and for the calendar year preceding the year being reported;

 

F)         If no exceedences or malfunctions were recorded under Section 229.182(a)(3) through (a)(5) of this Subpart for the calendar year being reported, a statement that no exceedences occurred during the reporting period; and

 

G)        Any use of the bypass stack, the duration of use, the reason for malfunction, and the corrective actions taken.

 

d)         Once an HMIWI is issued a CAAPP permit, the owner or operator of the HMIWI shall submit the reports required under subsection (c) of this Section semiannually. The semiannual reports must be submitted within 60 days following the end of the reporting period.  The first semiannual reporting period ends on June 30 of each year and the second semiannual reporting period ends on December 31 of each year.

 

e)         The owner or operator of each rural HMIWI subject to the emissions limits under Section 229.126(b) of this Part, shall submit an annual report containing all information listed in subsections (b) and (c) of this Section by no later than 60 days following the year in which the data was collected.  Subsequent reports shall be sent no later than 12 calendar months following the previous report.  Once the unit is subject to permitting requirements under the CAAPP, the owner or operator shall submit these reports semiannually in accordance with the schedule specified in subsection (d) of this Section.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)





 




Section 229.APPENDIX A   Toxic Equivalency (TEQ) Factors

 

The following TEQ factors shall be used to determine compliance with the dioxin/furans standards under either Section 229.125(b) or Section 229.126(b) of this Part.

 

Dioxin/Furan Congener	Toxic Equivalency Factor
2,3,7,8-tetrachlorinated dibenzo-p-dioxin	1.0
1,2,3,7,8-pentachlorinated dibenzo-p-dioxin	0.5
1,2,3,4,7,8-hexachlorinated dibenzo-p-dioxin	0.1
1,2,3,7,8,9-hexachlorinated dibenzo-p-dioxin	0.1
1,2,3,6,7,8-hexachlorinated dibenzo-p-dioxin	0.1
1,2,3,4,6,7,8-heptachlorinated dibenzo-p-dioxin	0.01
octachlorinated dibenzo-p-dioxin	0.001
2,3,7,8-tetrachlorinated dibenzofuran	0.1
2,3,4,7,8-pentachlorinated dibenzofuran	0.5
1,2,3,7,8-pentachlorinated dibenzofuran	0.05
1,2,3,4,7,8-hexachlorinated dibenzofuran	0.1
1,2,3,6,7,8-hexachlorinated dibenzofuran	0.1
1,2,3,7,8,9-hexachlorinated dibenzofuran	0.1
2,3,4,6,7,8-hexachlorinated dibenzofuran	0.1
1,2,3,4,6,7,8-heptachlorinated dibenzofuran	0.01
1,2,3,4,7,8,9-heptachlorinated dibenzofuran	0.01
octachlorinated dibenzofuran	0.001

 

 

Section 229.APPENDIX B   Operating Parameters to be Monitored and Minimum Measurement and Recording Frequencies

 

An "X" in any box in this matrix means that measurement of that parameter is required.

 

MINIMUM FREQUENCY				CONTROL SYSTEM
Operating Parameters	Data Measurement	Data Recording	Dry Scrubber Followed by Fabric Filter		Wet Scrubber	Dry Scrubber Followed by Fabric Filter and Wet Scrubber	Selective Noncatalytic Reduction System
Maximum Charge Rate1	Continuous	Once per hour	X		X	X	X
Maximum Fabric Filter Inlet Temperature	Continuous	Once per minute	X			X
Maximum Flue Gas Temperature	Continuous	Once per minute	X		X
Minimum Secondary Chamber Temperature	Continuous	Once per minute	X		X	X	X
Minimum Dioxin/Furan Sorbent Flow Rate	Hourly	Once per hour	X			X
Minimum HCl Sorbent Flow Rate	Hourly	Once per hour	X			X
Minimum Reagent Flow Rate	Hourly	Once per hour					X
Minimum Hg Sorbent Flow Rate	Hourly	Once per hour	X			X
Minimum Pressure Drop Across the Wet Scrubber or Minimum Horsepower or Amperage to Wet Scrubber	Continuous	Once per minute			X	X
Minimum Scrubber Liquor Flow Rate	Continuous	Once per hour			X	X
Minimum Scrubber Liquor pH	Continuous	Once per hour			X	X

¹For batch HMIWIs, record the charge per batch.

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)

 

Section 229.APPENDIX C   Reference Test Methods and Procedures for Performance Tests

 

The following test methods and procedures shall be used as specified in Section 229.140(e) of this Part, when conducting any performance test for the purpose of demonstrating compliance with the emissions limits established under this Part.

 

a)         All performance tests shall consist of a minimum of 3 test runs conducted under representative operating conditions. The minimum sample time of 1 hour per test run shall be used unless otherwise indicated. In order to demonstrate compliance with the emissions limits set forth in Subpart E of this Part, the arithmetic average of all 3 performance test runs shall be used.

 

b)         Method 1, at 40 CFR 60, incorporated by reference at Section 229.104(d) of this Part, shall be used to select the sampling location and number of traverse points.

 

c)         Method 2, at 40 CFR 60, shall be used to determine average gas density, as well as to measure gas velocity.

 

d)         Method 3, 3A, or 3B, at 40 CFR 60, shall be used for gas composition analysis, including measurement of oxygen concentration. Method 3, 3A or 3B, at 40 CFR 60, shall be used simultaneously with each of the other reference methods. As an alternative to Method 3B, ASME PTC-19-10-1981-Part 10 may be used.

           

e)         The pollutant concentrations shall be adjusted to 7 percent oxygen using the following equation:

 

C_adj = C_meas (20.9-7)/(20.9-%O₂)

 

Where:

 

Cadj	=	pollutant concentration adjusted to 7 percent oxygen;
Cmeas	=	pollutant concentration measured on a dry basis
(20.9-7)	=	20.9 percent oxygen - 7 percent oxygen (defined oxygen corrective basis);
20.9	=	oxygen concentration in air, percent; and
%O2	=	oxygen concentration measured on a dry basis, percent.

 

f)         Method 5, 26A, or 29, at 40 CFR 60, shall be used to measure PM emissions.  As an alternative, a PM CEMS may be used in determining compliance with PM emissions using a 12-hour rolling average, calculated each hour as the average of the previous 12 operating hours.

           

g)         Method 7 or 7E, at 40 CFR 60, shall be used to measure NO_x emissions.

 

h)         Method 6 or 6C, at 40 CFR 60, shall be used to measure SO₂ emissions.

 

i)          Method 9, at 40 CFR 60, shall be used to measure stack opacity. As an alternative, the use of a bag leak detection system or a PM CEMS to demonstrate compliance with the PM standards is considered demonstrative of compliance with the opacity requirements.

 

j)          Method 10 or 10B, at 40 CFR 60, shall be used to measure CO emissions. As an alternative, a CO CEMS may be used to measure CO emissions.

 

k)         Method 22, at 40 CFR 60, shall be used to measure fugitive ash emissions.

 

l)          Method 23, at 40 CFR 60, shall be used to measure total dioxin/furan emissions.  As an alternative, the facility may elect to sample total dioxins/furans by installing, calibrating, maintaining, and operating a continuous automated sampling system for monitoring dioxin/furan emissions.  The minimum sample time for Method 23 sampling shall be 4 hours per test run.  If the affected facility has selected the TEQ for dioxin/furans (set out in Appendix A of this Part), as provided under Section 229.125 or 229.126 of this Part, whichever is applicable, the following procedures shall be used to determine compliance:

 

1)         Measure the concentration of each dioxin/furan tetra-through-octa-congener emitted using Method 23;

 

2)         For each dioxin/furan congener measured in accordance with subsection (i)(1) of this Section, multiply the congener concentration by its corresponding TEQ factor specified in Appendix A of this Part; and

 

3)         Sum the products calculated in accordance with subsection (i)(2) of this Section to obtain the total concentration of dioxin/furans emitted in terms of TEQ.

 

m)        Method 26 or 26A, at 40 CFR 60, shall be used to measure HCl emissions.  As an alternative, an HCl CEMS may be used to measure HCl emissions.  Before January 1, 2014, if the affected facility has selected the percentage reduction standard for HCl as provided under Section 229.125(a) or 229.126(a) of this Part, whichever is applicable, the percentage reduction in HCl emissions (%R_HCl) is computed using the following formula:

 

(%R_HCl) = ((E_i-E_o)/E_i) x 100

 

Where:

 

%RHCl	=	percentage reduction of HCI emissions achieved;
Ei	=	HCI emissions concentration measured at the control device inlet, corrected to 7 percent oxygen (dry basis); and
Eo	=	metal emissions concentration (Pb, Cd, or Hg) measured at the control device outlet, corrected to 7 percent oxygen (dry basis).

 

n)         Method 29, at 40 CFR 60, shall be used to measure Pb, Cd, and Hg emissions.  As an alternative, ASTM D6784-02 may be used to measure Hg emissions; a multi-metals CEMS or Hg CEMS may be used to measure Pb, Cd, and Hg emissions; or the facility may elect to sample Hg by installing, calibrating, maintaining, and operating a continuous automated sampling system for monitoring Hg emissions.  Before January 1, 2014, if the affected facility has selected the percentage reduction standards for metals as provided in Section 229.125(a) or 229.126(a) of this Part, whichever is applicable, the percentage reduction in emissions (%R_metal) is computed using the following formula:

 

(%R_metal) = ((E_i-E_o)/E_i) x 100

 

Where:

 

%RMETAL	=	percentage reduction of metal emissions (Pb, Cd, or Hg) achieved;
Ei	=	metal emissions concentration (Pb, Cd, or Hg) measured at the control device inlet, corrected to 7 percent oxygen (dry basis); and
EO	=	metal emissions concentration (Pb, Cd, or Hg) measured at the control device outlet, corrected to 7 percent oxygen (dry basis).

 

(Source:  Amended at 35 Ill. Reg. 16615, effective September 30, 2011)