Illinois’ deviation reporting requirements are included under Section 201.530(c), Illinois Administrative Code and are more stringent to the proposed changes to s. NR 439.03, Wis. Adm. Code. Unless specified in the applicable permit-by-rule subpart, a written report of any deviation is required to be submitted within 30 days after the date the deviation occurred.
Iowa’s deviation reporting requirements are included under 567 Iowa Administrative Code (IAC) 22.108(5) and 24.1 and are similar to the proposed changes to s. NR 439.03, Wis. Adm. Code. Iowa’s reporting timeline of excess emissions is more stringent, but the reporting of non-excess emission deviations is less stringent. The IAC requires a written report regarding excess emissions to be submitted within seven days, instead of Wisconsin’s proposed 10 days. Under IAC, excess emissions during periods of startup, shutdown, or cleaning of control equipment are not violations and are not to be reported as long as the startup, shutdown, or cleaning is accomplished expeditiously and in a manner consistent with good practice for minimizing emissions. EPA has proposed to find IAC 24.1(1) as substantially inadequate under section 110(k) of the CAA because it does not comply with EPA’s policy on excess emissions during periods of startup, shutdown, and malfunction (88 FR 11842). All other deviations are to be clearly identified in reports submitted at least every six months.
Michigan’s deviation reporting requirements are included under Section R. 336.1213(3)(c), Michigan Administrative Code and are similar to the proposed changes to s. NR 439.03, Wis. Adm. Code. Michigan includes provisions that only emissions that exceed the applicable standard for greater than a specified time period need to be reported as deviations within two business days with a written report submitted within 10 days after the deviation occurred. For deviations which are less than the specified time period or which do not exceed the emissions allowed under the permit, a facility is required to submit a report of those deviations at least once every six months.
Minnesota’s deviation reporting requirements are included under 7019.1000 Subpart 1 and 7007.0800 Subpart 6, Minn. Adm. Rules and are similar to the proposed changes to s. NR 439.03, Wis. Adm. Code. Minnesota requires deviations which could endanger human health be reported within two business days and all other deviations are to be reported in a semiannual monitoring report. Minnesota is more stringent on reporting breakdowns for more than one hour that cause any increase in emissions. Breakdown notifications are required within 24 hours of when the breakdown was discovered or reasonably should have been discovered. Minnesota requires semi-annual reporting of permit deviations which do not result in an emissions limit to be exceeded, which is similar to Wisconsin’s proposed rule.
Calibration – Proposed changes to s. NR 439.055(4), Wis. Adm. Code, replace the requirement that monitoring equipment be calibrated at least yearly with a requirement that equipment be calibrated at a frequency based on written manufacturer recommendations or as required by an applicable standard, whichever is more frequent. If no such recommendations or standards exist, the time between a calibration, replacement or validation may not exceed one year.
Illinois’ control device monitoring equipment calibration requirements are similar to the proposed changes in s. NR 439.055, Wis. Adm. Code. Monitoring equipment is required to be installed, calibrated, operated and maintained according to vendor specifications.
Iowa’s control equipment calibration requirements are similar to the proposed changes in s. NR 439.055, Wis. Adm. Code. Permits generally specify that monitoring equipment be operated in accordance with manufacturer recommendations. Iowa retains the authority to require more frequent calibrations.
Michigan requires air-cleaning devices to be calibrated under the authority of Mich. Admin. Code R. 336.1910. This section requires that these devices be installed, maintained, and operated in a satisfactory manner and in accordance with emissions limits and existing law. This requirement is similar to the proposed changes to s. NR 439.055(4), Wis. Adm. Code. Operation in a satisfactory manner is typically defined as operating according to manufacturer recommendations.
Minnesota’s control equipment calibration requirements are included under 7011.0075 Subpart 2.G., Minn. Adm. Rule and are similar to the proposed changes in s. NR 439.055, Wis. Adm. Code. All monitoring equipment for each piece of listed control equipment is required to be calibrated annually, or as required by the manufacturing specification.
Malfunction Prevention and Abatement Plan (MPAP) – Proposed changes to s. NR 439.11, Wis. Adm. Code, include defining thresholds when an MPAP is required, excludes smaller units from needing an MPAP, and clarifies plan content.
Throughout the Illinois Administrative Code, monitoring equipment is required to be installed, calibrated, operated and maintained according to vendor specifications. This requirement is similar to proposed s. NR 439.11(1r)(bm), Wis. Adm. Code, which allows a facility to consider and/or use a manufacturer recommendation to set the interval for routine inspection, maintenance, and calibration, replacement, or validation.
Iowa’s MPAP requirements are included in 567 IAC 24.2(445B). Maintenance plans are required for equipment or control equipment where the Iowa director determines that a continued pattern of excess emissions indicative of inadequate operation and maintenance is occurring. Iowa’s plan is required when determined by the director, while Wisconsin’s MPAP requirements are based on the emissions of the specific process. The content of the MPAP is similar to the proposed changes in s. NR 439.11, Wis. Adm. Code. Wisconsin’s proposed rule provides more clarity for what emissions units need an MPAP than Iowa’s rules, but Iowa would likely have less equipment subject to the MPAP requirements.
Michigan’s MPAP requirements are included under Section R. 336.1911, Michigan Administrative Code. The content of the MPAP is similar to the proposed changes in s. NR 439.11, Wis. Adm. Code. However, Michigan’s plan is required whenever requested by the department, while Wisconsin’s MPAP requirements are based on the emissions of the specific process. Wisconsin’s proposed rule provides more clarity for what emissions units need an MPAP than Michigan’s rules, and Michigan has the option to be more or less stringent than Wisconsin on when a plan is required.
Under 7011.075 Subpart 2, Minn. Adm. Code, Minnesota’s maintenance requirements for control equipment are included. The requirements include training, inspection timelines, and repair records for maintaining each piece of listed control equipment. These maintenance requirements are similar to and slightly more stringent than the proposed changes to s. NR 439.11, Wis. Adm. Code.
9. Summary of Factual Data and Analytical Methodologies Used and How Any Related Findings Support the Regulatory Approach Chosen:
The department is proposing updates to test methods referenced under ch. NR 439, Wis. Adm. Code. The American Society of Testing and Materials (ASTM) is an international standards organization that develops and publishes voluntary consensus technical standards for a wide variety of materials, products, systems and services. ASTM technical standards are the written procedures that provide consistent application, specification and results. ASTM technical standards are created or periodically updated. This rule package incorporates the current state of the ASTM technical standards. EPA reference methods are the technical written procedures to characterize and measure air contaminants. EPA reference methods are periodically created and updated. This rule package incorporates the current state of EPA reference methods.
This proposed rulemaking revises provisions related to monitoring methodology to ensure requirements related to instrument calibration, validation, and replacement reflect current technology, business operations, and maintenance strategies.
10. Analysis and Supporting Documents Used to Determine the Effect on Small Business or in Preparation of an Economic Impact Report:
The proposed changes will apply to all businesses, including small businesses, which emit or cause emissions of air contaminants (“emissions sources”) subject to ch. NR 439, Wis. Adm. Code. The department estimates the total costs of the rule to be unaffected by or possibly reduced because the proposed rule revisions will not impose new compliance costs on any business. The proposed changes are intended to clarify, reduce, and make more efficient reporting, monitoring, and recordkeeping requirements.
11. Effect on Small Business (initial regulatory flexibility analysis):
No business is expected to incur additional costs in order to comply with the revised rule. Some small businesses may have reduced costs due to proposed rule changes that reduce frequency and redundancy of reporting.
12. Agency Contact Person: Maria Hill; Maria.Hill@wisconsin.gov; (608) 216-3179
13. Place where comments are to be submitted and deadline for submission:
Written comments may be submitted at the public hearings, by regular mail, or email to:
Olivia Salmon – AM/7
Bureau of Air Management
Wisconsin Department of Natural Resources
PO Box 7921
Madison, WI 53703
Comments may be submitted to the department contact person listed above or to DNRAdministrativeRulesComments@wisconsin.gov until the deadline given in the upcoming notice of public hearing. The notice of public hearing and deadline for submitting comments will be published in the Wisconsin Administrative Register and on the department’s website, at https://dnr.wisconsin.gov/calendar. Comments may also be submitted through the Wisconsin Administrative Rules Website at https://docs.legis.wisconsin.gov/code/chr/active.
The consent of the Attorney General will be requested for the incorporation by reference of the following methods into ch. NR 484, Wis. Adm. Code:
“Determination of PM10 Emissions” (40 CFR 51 Appendix M, Method 201)
“Determination of PM10 and PM2.5 Emissions from Stationary Sources” (40 CFR 51 Appendix M, Method 201A)
“Dry Impinger Method for Determining Condensable Particulate Emissions from Stationary Sources” (40 CFR part 51 Appendix M, Method 202)
“Determination of Carbon Dioxide, Methane, Nitrogen, and Oxygen form Stationary Sources” (40 CFR part 60 Appendix A, Method 3C)
“Determination of Metals from Stationary Sources” (40 CFR part 60 Appendix A, Method 29)
“Measurement of Vapor Phase Organic and Inorganic Emissions by Extractive Fourier Transform Infrared (FTIR) Spectroscopy” (40 CFR part 60 Appendix A, Method 320)
“Standard Test Method for Total Moisture in Coal” (ASTM D3302/D3302M-22a)
“Standard Test Method for Determination of Gaseous Compounds by Extractive Direct Interface Fourier Transform Infrared (FTIR) Spectroscopy” (ASTM D6348-12(2020))
[see PDF for formatting]
RULE TEXT
Section 1   NR 400.02 (79) is amended to read:
NR 400.02 (79)“Heat input" means the total gross calorific value per unit of time of all fuels being burned, where gross calorific value of a fuel is measured by ASTM Method D240-02D240-19, D1826-94 (2017), or D5865-04D5865/D5865M-19, incorporated by reference in s. NR 484.10 (4)(26), and (55g). WhereWhen the test method gives a higher and a lower heating value, heat input is calculated in Btu per hour using the higher heating value of the fuel.
Section 2   NR 419.08 (5) and (6) (b) are amended to read:
NR 419.08 (5) Emission control system monitoring. The owner or operator of any facility which uses a wet scrubber to control organic gas emissions from the catalysis of urethane cold box binders shall continuously measure and record the pH of the scrubber liquid and monitor in addition to meeting the monitoring requirements of s. NR 439.055 (1) (e) and measure and record pressure drop across the scrubber and demister in inches of water and scrubber liquor flow in gallons per minute once for every 8 hours of source operation or once per day, whichever yields the greater number of measurements.
(6) (b) Records of operation variables which are required to be measured under sub. (5) and s. NR 439.055 (1) (e).
Section 3   NR 439.01 (1) is amended to read:
NR 439.01 (1) Applicability. This chapter applies to all air contaminant sources and to their owners and operators. For sources subject to an emission standard under chs. NR 460 to 469 or under 40 CFR part 63, the requirements of ch. NR 460 40 CFR parts 60 to 63, the applicable requirements of 40 CFR parts 60 to 63 apply in addition to the requirements of this chapter. In the case of anya conflict between applicable provisions under chs. NR 460 to 46940 CFR parts 60 to 63 and provisions of this chapter, the provisions under chs. NR 460 to 46940 CFR parts 60 to 63 shall apply, this chapter not withstanding.
Section 4   NR 439.02 (1) is renumbered (1s) and as renumbered is amended to read:
NR 439.02 (1s) “Audit samples sample” means a glass vials vial, a gas cylinders cylinder, or other materials which contain material that contains a known concentration of a pollutant that may be used for the purpose of quality assurance of certain laboratory analyses required for the determination of compliance.
Section 5   NR 439.02 (1m) is created to read:
NR 439.02 (1m) (a) “Adsorption” means the transfer of a gaseous pollutant from the gas stream by transferring pollutants to a solid surface, typically carbon.
(b) "Adsorption device includes a fixed regenerable bed, a disposable or rechargeable canister, a moving bed adsorber, and a fluid bed adsorber.
Section 6   NR 439.02 (2) is amended to read:
NR 439.02 (2) “Baghouse” means a control device in which dust−laden gases are forced through a fabric bag and particulates are retained by direct interception, inertial impaction, diffusion, electrostatic attraction, or gravitational settling.
Section 7   NR 439.02 (2m) is created to read:
NR 439.02 (2m) “Calibration” means the comparison of a standard or instrument with a known accurate standard or instrument to detect and quantify inaccuracies and to report or eliminate those inaccuracies by adjustment.
Section 8   NR 439.02 (4) is amended to read:
NR 439.02 (4)Condensible Condensable particulate matter” means any material, except uncombined water, that may not be collected in the front half of the particulate matter emission sampling train but which that exists as a solid or liquid at standard conditions.
Section 7g.   NR 439.02 (5) is renumbered NR 439.02 (5) (a).
Section 7r.   NR 439.02 (5) (b) is created to read:
NR 439.02 (5) (b) “Continuous monitoring system” includes a continuous emission monitoring system, a predictive emission monitoring system, a continuous opacity monitoring system, and a continuous parameter monitoring system.
Section 9   NR 439.02 (5m), (6e), (6m) and (6s) are created to read:
NR 439.02 (5m) “Deviation” means any instance in which a source is not in conformance with a permit requirement or applicable regulation, including exceedances and excursions.
(6e) “Exceedance” means a condition that is detected by monitoring, testing, or other documentation that provides data in terms of a limitation or standard and that indicates that emissions or opacity are greater than the applicable limitation or standard, or less than the applicable standard in the case of a percent reduction requirement, consistent with any averaging period specified for averaging the results of the monitoring or testing, or specified in the applicable limitation or standard.
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