Ill. Admin. Code tit. 35, § 217.158
a) Notwithstanding any other emissions averaging plan provisions under this Part, an owner or operator of a source with certain emission units subject to Subpart E, F, G, H, I, or M of this Part, or subject to Subpart Q of this Part that are located in either one of the areas set forth under Section 217.150(a)(1)(A)(i) or (ii) or Section 217.150(a)(2)(A)(i) or (ii), may demonstrate compliance with the applicable Subpart through an emissions averaging plan. An emissions averaging plan can only address emission units that are located at one source and each unit may only be covered by one emissions averaging plan. The emission units at the source are affected units and are subject to the requirements of this Section.
1) The following units may be included in an emissions averaging plan:
2) The following types of units may not be included in an emissions averaging plan:
b) Before July 1, 2025, an owner or operator must submit an emissions averaging plan to the Agency by January 1, 2015. The plan must include, but is not limited to, the following:
c) On and after July 1, 2025, an owner or operator must submit an emissions averaging plan to the Agency at least 30 days before beginning the use of that plan to demonstrate compliance. The plan must include, but is not limited to, the following:
e) Notwithstanding subsection (d) of this Section:
f) An owner or operator must:
g) Until July 1, 2025, the total mass of actual NOx emissions from the units listed in the emissions averaging plan must be equal to or less than the total mass of allowable NOx emissions for those units for both the ozone season and calendar year. The following equation must be used to determine compliance:

Where:
![]() | = | ![]() |
![]() | = | ![]() |
![]() | = | Total sum of the actual NOx mass emissions from units included in the averaging plan for each fuel used (tons per ozone season and year). |
![]() | = | Total sum of the allowable NOx mass emissions from units included in the averaging plan for each fuel used (tons per ozone season and year). |
![]() | = | Total mass of actual NOx emissions in tons for a unit as determined in subsection (f)(1) of this Section. |
| i | = | Subscript denoting an individual unit. |
| j | = | Subscript denoting the fuel type used. |
| k | = | Number of different fuel types. |
| n | = | Number of different units in the averaging plan. |
![]() | = | Total mass of allowable NOx emissions in tons for a unit as determined in subsection (g)(2) of this Section. |
For each unit in the averaging plan, and each fuel used by the unit, determine actual and allowable NOx emissions using the following equations:
1) Actual emissions must be determined as follows:
When emission limits are prescribed in lb/mmBtu,

When emission limits are prescribed in lb/ton of processed product,

2) Allowable emissions must be determined as follows:
h) On and after July 1, 2025, the total mass of actual NOx emissions from the units listed in the emissions averaging plan must be equal to or less than the total mass of allowable NOx emissions for those units on a 30-day rolling average basis. The following equation must be used to determine compliance:

Where:
![]() | = | ![]() |
| Where Nact is the total sum of the actual NOx mass emissions from units included in the averaging plan for each fuel used (tons per 30-day rolling average basis). | ||
![]() | = | ![]() |
| Where Nall is the total sum of the allowable NOx mass emissions from units included in the averaging plan for each fuel used (tons per 30-day rolling average basis). | ||
![]() | = | Total mass of actual NOx emissions in tons for a unit as determined in subsection (h)(1) of this Section. |
| i | = | Subscript denoting an individual unit. |
| j | = | Subscript denoting the fuel type used. |
| k | = | Number of different fuel types. |
| n | = | Number of different units in the averaging plan. |
![]() | = | Total mass of allowable NOx emissions in tons for a unit as determined in subsection (h)(2) of this Section. |
For each unit in the averaging plan, and each fuel used by the unit, determine actual and allowable NOx emissions using the following equations:
When emission limits are prescribed in lb/mmBtu,

When emission limits are prescribed in lb/ton of processed product,

Where:
![]() | = | Total mass of actual NOx emissions in tons for a unit. | |
![]() | = | Total mass of allowable NOx emissions in tons for a unit. | |
![]() | = | Actual NOx emission rate (lbs/mmBtu or lbs/ton of product) as determined by a performance test, a CEMS, or an alternative method approved by the Agency. | |
![]() | = | Allowable NOx emission rate (lbs/mmBtu or lbs/ton of product) as provided in Section 217.164, 217.184, 217.204, 217.224, 217.244, or 217.344, as applicable. For an affected industrial boiler subject to Subpart E of this Part, or process heater subject to Subpart F of this Part, with a rated heat input capacity less than or equal to 100 mmBtu/hr demonstrating compliance through an emissions averaging plan, the allowable NOx emission rate is to be determined from a performance test after the boiler or heater has undergone combustion tuning. For all other units in an emissions averaging plan, an uncontrolled NOx emission rate from USEPA's AP-42, as incorporated by reference in Section 217.104, or an uncontrolled NOx emission rate as determined by an alternative method approved by the Agency, will be used. | |
| H | = | Heat input (mmBtu/ozone season or mmBtu/year) calculated from fuel flow meter and the heating value of the fuel used. | |
| P | = | weight in tons of processed product. | |
1) Actual emissions must be determined as follows:
When emissions limitations are prescribed in lb/mmBtu,

When emissions limitations are prescribed in lb/ton of processed product,

Alternatively, for units equipped with CEMS that monitor stack flow in accordance with 40 CFR 60 or 75, or alternate methodology that has been approved by the Agency or USEPA and included in a federally enforceable permit, actual emission rate for a given unit can be determined as follows:

Where:
![]() | = | NOx emission rate (lb/hr) as determined by a performance test, a CEMS, a PEMS, or an alternative method approved by the Agency. |
![]() | = | 1.194 x 10-7 (1.194 x 10-7 converts to (lb/dscf)/ppm) |
![]() | = | Hourly average NOx concentration during unit operation in ppm on a dry basis for a given unit. |
![]() | = | Hourly average volumetric flow rate during unit operation in scf/hr on a dry basis for a given unit. |
2) Allowable emissions must be determined as follows:
j) The owner or operator of an emission unit located at a petroleum refinery who is demonstrating compliance with an applicable Subpart through an emissions averaging plan under this Section may exclude from the calculation demonstrating compliance (i.e. 30-day rolling average under Section 217.152) those time periods when an emission unit included in the emissions averaging plan is shut down for a maintenance turnaround, provided that the requirements in subsection (j)(1) through (j)(5) are met:
5) the owner or operator notifies the Agency in writing within 30 days of the end of the maintenance turnaround of the actual start and end dates for the maintenance turnaround and, for each day of the maintenance turnaround, the daily emissions of the combined emission units in the emissions averaging plan.
The owner or operator must resume compliance with the 30-day rolling average on the calendar day immediately following the end of the maintenance turnaround and incorporating the operating days preceding the maintenance turnaround. For purposes of this subsection, "maintenance turnaround" means the shutdown of any emission unit or control equipment that is scheduled at least 30 days in advance of the shutdown and the purpose of such shutdown is to (1) perform general equipment cleaning and repairs due to normal equipment wear and tear; (2) perform required equipment tests and internal inspections; (3) install any unit or equipment modifications/additions, or make provisions for a future modification or addition; and/or (4) perform normal end-of-run catalyst changeouts or refurbishments.
l) The owner or operator of an emission unit located at a petroleum refinery who is demonstrating compliance with an applicable Subpart through an emissions averaging plan under this Section may exclude from the calculation demonstrating compliance (i.e. 30-day rolling average under Section 217.152) those time periods when NOx pollution control equipment that controls one or more emission units included in the emissions averaging plan is shut down for a maintenance turnaround, provided that the requirements in subsection (l)(1) through (l)(5) are met:
5) the owner or operator notifies the Agency in writing within 30 days of the end of the maintenance turnaround of the actual start and end dates for the maintenance turnaround and, for each day of the maintenance turnaround, the daily emissions of the combined emission units in the emissions averaging plan.
The owner or operator must resume compliance with the 30-day rolling average on the calendar day immediately following the end of the maintenance turnaround and incorporating the operating days preceding the maintenance turnaround. For purposes of this subsection, "maintenance turnaround" means the shutdown of any emission unit or control equipment that is scheduled at least 30 days in advance of the shutdown and the purpose of such shutdown is to (1) perform general equipment cleaning and repairs due to normal equipment wear and tear; (2) perform required equipment tests and internal inspections; (3) install any unit or equipment modifications/additions, or make provisions for a future modification or addition; and/or (4) perform normal end-of-run catalyst changeouts or refurbishments.
m) Notwithstanding subsection (h), for the owner or operator of a petroleum refinery located in Channahon or Wood River, the equation used to determine compliance before January 1, 2028, is as follows:

Where Nact and Nall are defined as under subsection (h).
When emissions limitations are prescribed in lb/mmBtu,

When emissions limitations are prescribed in lb/ton of processed product,

Where:
![]() | = | Total mass of actual NOx emissions in tons for a unit. |
![]() | = | Total mass of allowable NOx emissions in tons for a unit. |
![]() | = | Actual NOx emission rate (lbs/mmBtu or lbs/ton of product) as determined by a performance test, a CEMS, a PEMS, or an alternative method approved by the Agency. |
![]() | = | Allowable NOx emission rate (lbs/mmBtu or lbs/ton of product) as provided in Section 217.164, 217.184, 217.204, 217.224, 217.244, or 217.344, as applicable. |
| H | = | Heat input (mmBtu/30-day rolling average basis) calculated from fuel flow meter and the heating value of the fuel used. |
| P | = | weight in tons of processed product. |
(Source: Amended at 49 Ill. Reg. 6355, effective April 23, 2025)