NR 439.055(2)(2)When the department requires instrumentation to monitor the operation of a source or of air pollution control equipment, the following monitoring and recording frequencies shall, at minimum, be used:
NR 439.055(2)(a)(a) Temperature in the primary chamber and afterburner of an incinerator shall be monitored and recorded every 15 minutes.
NR 439.055(2)(b)(b) The following operational variables shall be measured and recorded once for every 8 hours of source operation or once per day, whichever yields the greater number of measurements:
NR 439.055(2)(b)1.1. Pressure drop across baghouses, mechanical collectors, wet scrubbers, absorption equipment or adsorption equipment.
NR 439.055(2)(b)2.2. Current and secondary current in electrostatic precipitators.
NR 439.055(2)(b)3.3. Voltage in electrostatic precipitators.
NR 439.055(2)(b)4.4. The sparking rate from electrostatic precipitators.
NR 439.055(2)(b)5.5. Flow of liquor in wet scrubbers used for particulate control.
NR 439.055(2)(b)6.6. pH of absorption scrubbing fluid.
NR 439.055(3)(3)When the department requires instrumentation to monitor the operation of air pollution control equipment, or to monitor source performance, the instrument shall measure operational variables with the following accuracy:
NR 439.055(3)(a)(a) The temperature monitoring device shall have an accuracy of 0.5% of the temperature being measured in degrees Fahrenheit or ± 5°F of the temperature being measured, or the equivalent in degrees Celsius (centigrade), whichever is greater.
NR 439.055(3)(b)(b) The pressure drop monitoring device shall be accurate to within 5% of the pressure drop being measured or within ±1 inch of water column, whichever is greater.
NR 439.055(3)(c)(c) The current, voltage, flow or pH monitoring device shall be accurate to within 5% of the specific variable being measured.
NR 439.055(4)(4)All instruments used for measuring source or air pollution control equipment operational variables shall be calibrated yearly or at a frequency based on good engineering practice as established by operational history, whichever is more frequent.
NR 439.055(5)(5)The department may require, in an operation permit or order, the measurement of a greater number of source or air pollution control operational variables, more frequent monitoring of operational variables, more accurate measurement of operational variables or more frequent calibration of monitoring equipment than those required under subs. (1) to (4) if the department determines that these requirements are necessary to ensure that the source does not exceed an applicable emission limit, or to ensure that the requirements of chs. NR 400 to 499 are met.
NR 439.055(6)(6)For any air pollution control equipment or monitoring instrumentation not specifically identified in subs. (1) and (2), the department may require, in an operation permit or order, and after consultation with the owner or operator of the facility, monitoring of air pollution control equipment operational variables and may specify the frequency of the monitoring and the type of monitoring instrumentation.
NR 439.055 HistoryHistory: Renum. from NR 154.06 (6), Register, September, 1986, No. 369, eff. 10-1-86; renum. from NR 439.06 and am. Register, September, 1987, No. 381, eff. 10-1-87; renum. from NR 439.08 and am., Register, May, 1992, No. 437, eff. 6-1-92; r. and recr. Register, December, 1993, No. 456, eff. 1-1-94; am. (1) (d) and (g) and (3) (a), Register, December, 1996, No. 492, eff. 1-1-97; CR 02-146: am. (6) Register October 2003 No. 574; CR 09-020: am. (2) (b) 2. Register January 2010 No. 649, eff. 2-1-10.
NR 439.06NR 439.06Methods and procedures for determining compliance with emission limitations (by air contaminant). When tests or a continuous monitoring system are required by the department, the owner or operator of a source shall use the reference methods listed in this section and in ss. NR 439.07 to 439.095 to determine compliance with emission limitations, unless an alternative or equivalent method is approved, or a specific method is required, in writing, by the department. Any alternative, equivalent or other specific method approved or required by the department for an ozone precursor shall be submitted to, and will not become effective for federal purposes until approved by, the administrator or designee as a source-specific revision to the department’s state implementation plan for ozone. The test methods shall include quality control and quality assurance procedures and the data reporting format which are specified and approved by the department for collection, analysis, processing and reporting of compliance monitoring data. Notwithstanding the compliance determination methods which the owner or operator of a source is authorized to use under this chapter, the department may use any relevant information or appropriate method to determine a source’s compliance with applicable emission limitations.
NR 439.06(1)(1)Nonfugitive particulate emissions. The owner or operator of a source shall use Method 5, 5A, 5B, 5D, 5E, 5F, 5G, 5H, 5I, or 17 in 40 CFR part 60, Appendix A, incorporated by reference in s. NR 484.04 (13), and when required, Method 202 in 40 CFR part 51, Appendix M, incorporated by reference in s. NR 484.04 (9), to determine compliance with a nonfugitive particulate emission limitation.
NR 439.06(1m)(1m)Nonfugitive PM10 particulate emissions. The owner or operator of a source shall use Method 201 or 201A in 40 CFR part 51, Appendix M, incorporated by reference in s. NR 484.04 (9), to determine compliance with a nonfugitive PM10 particulate emission limitation.
NR 439.06(2)(2)Sulfur dioxide emissions. The owner or operator of a source shall use one or more of the following methods to determine compliance with a sulfur dioxide emission limitation:
NR 439.06(2)(a)(a) Perform compliance emission testing following Method 6, 6A, 6B, 6C, or 8 in 40 CFR part 60, Appendix A, incorporated by reference in s. NR 484.04 (13).
NR 439.06(2)(b)(b) Install, calibrate, maintain and operate a continuous emission monitor that meets the applicable performance specifications in 40 CFR part 60, Appendix B or, for affected units, the performance specifications in 40 CFR part 75, Appendices A to I, incorporated by reference in s. NR 484.04 (21) and (27). The owner or operator of the source shall submit a quality control and quality assurance plan for approval by the department. The monitor shall follow the plan, as approved by the department.
NR 439.06(2)(c)(c) Perform periodic fuel sampling and analysis of fossil and nonfossil fuels using the methods and procedures specified in s. NR 439.08.
NR 439.06(3)(3)Organic compound emissions. The owner or operator of a source shall use the test methods and procedures listed in this subsection to determine compliance with an organic compound emission limitation. If a test method inadvertently measures compounds which are listed in s. NR 400.02 (162) as having negligible photochemical reactivity, the owner or operator may exclude these compounds when determining compliance with a VOC emission limit if the amount of these compounds is accurately quantified and the exclusion is approved by the department. As a precondition to excluding these compounds as VOC or at any subsequent time, the department may require an owner or operator to provide monitoring or testing methods and results demonstrating, to the satisfaction of the department, the amount of negligibly reactive compounds in the source’s emissions. Unless a source achieves compliance through an averaging method specifically authorized by the department, organic compound emission limitations in chs. NR 419 to 424 shall be achieved on an instantaneous basis.
NR 439.06(3)(a)(a) Method 18, 25, 25A, or 25B in 40 CFR part 60, Appendix A, incorporated by reference in s. NR 484.04 (13), shall be used to determine organic compound emission concentrations or emission rates.
NR 439.06(3)(am)(am) Method 204, 204A, 204B, 204C, 204D, 204E, or 204F in 40 CFR part 51, Appendix M, or the data quality objective method or lower confidence limit method in 40 CFR part 63, Subpart KK, Appendix A, incorporated by reference in s. NR 484.04 (9) and (24), shall be used to determine the capture efficiency of a control system for volatile organic compound emissions. The reporting and recordkeeping recommendations within a test method shall be followed unless alternative reporting or recordkeeping provisions have been approved in writing by the department. When determining the overall emission reduction efficiency of a volatile organic compound control system, simultaneous measurements of both the capture efficiency of the system and the pollutant reduction efficiency of the control device may be required.
NR 439.06(3)(b)(b) Method 24 or 24A in 40 CFR part 60, Appendix A, incorporated by reference in s. NR 484.04 (13), shall be used to determine the organic solvent content, the volume of solids, the weight of solids, the water content and the density of surface coatings, inks, and cleaning materials.
NR 439.06(3)(c)(c) Method 21 in 40 CFR part 60, Appendix A, incorporated by reference in s. NR 484.04 (13), shall be used to detect organic compound emission leaks except as provided in par. (i) 2. or 3.