NR 440.215(9)(g)11.11. Quarterly accuracy determinations and daily calibration drift tests shall be performed in accordance with procedure 1 of Appendix F of 40 CFR part 60, incorporated by reference in s. NR 440.17. NR 440.215(9)(g)12.12. When nitrogen oxides emissions data are not obtained because of CEMS breakdowns, repairs, calibration checks and zero and span adjustments, emission data calculations to determine compliance shall be made using other monitoring systems as approved by the department or Method 19 to provide, as necessary, valid emission data for a minimum of 75% of the hours per day for 75% of the days per month the unit is operated and combusting MSW. NR 440.215(9)(h)(h) The following procedures shall be used for determining compliance with the operating standards under sub. (7): NR 440.215(9)(h)1.1. Compliance with the carbon monoxide emission limits in sub. (7) (a) shall be determined using a 4-hour block arithmetic average for all types of affected facilities except mass burn rotary waterwall MWCs, RDF stokers and spreader stoker and RDF mixed fuel-fired combustors. NR 440.215(9)(h)2.2. For affected mass burn rotary waterwall MWCs, RDF stokers and spreader stoker and RDF mixed fuel-fired combustors, compliance with the carbon monoxide emission limits in sub. (7) (a) shall be determined using a 24-hour daily arithmetic average. NR 440.215(9)(h)3.3. The owner or operator of an affected facility shall install, calibrate, maintain and operate a CEMS for measuring carbon monoxide at the combustor outlet and record the output of the system. NR 440.215(9)(h)4.4. The 4-hour and 24-hour daily arithmetic averages in subds. 1. and 2. shall be calculated from 1-hour arithmetic averages expressed in parts per million by volume dry basis. The 1-hour arithmetic averages shall be calculated using the data points generated by the CEMS. At least 2 data points shall be used to calculate each 1-hour arithmetic average. NR 440.215(9)(h)5.5. An owner or operator may request that compliance with the carbon monoxide emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7% oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility shall be established during the initial compliance test. NR 440.215(9)(h)6.6. The following procedures shall be used to determine compliance with load level requirements under sub. (7) (b): NR 440.215(9)(h)6.a.a. The owner or operator of an affected facility with steam generation capability shall install, calibrate, maintain and operate a steam flow meter or a feedwater flow meter, measure steam or feedwater flow in kilograms per hour or pounds per hour on a continuous basis, and record the output of the monitor. Steam or feedwater flow shall be calculated in 4-hour block arithmetic averages. NR 440.215(9)(h)6.b.b. The method contained in ASME Power Test Codes: Test Code for Steam Generating Units, PTC 4.1 (1964) section 4, incorporated by reference in s. NR 440.17 (2) (h) 2., shall be used for calculating the steam or feedwater flow required under subd. 6. a. The recommendations of Instruments and Apparatus: Measurement of Quantity of Materials, ASME Interim Supplement 19.5 (1971) chapter 4, incorporated by reference in s. NR 440.17 (2) (h) 3., shall be followed for design, construction, installation, calibration and use of nozzles and orifices except as specified in subd. 6. c. NR 440.215(9)(h)6.c.c. Measurement devices such as flow nozzles and orifices are not required to be recalibrated after they are installed. NR 440.215(9)(h)6.d.d. All signal conversion elements associated with steam or feedwater flow measurements shall be calibrated according to the manufacturer’s instructions before each dioxin or furan compliance and performance test, and at least once per year. NR 440.215(9)(h)7.7. To determine compliance with the maximum particulate matter control device temperature requirements under sub. (7) (c), the owner or operator of an affected facility shall install, calibrate, maintain and operate a device for measuring temperature of the flue gas stream at the inlet to the final particulate matter control device on a continuous basis and record the output of the device. Temperature shall be calculated in 4-hour block arithmetic averages. NR 440.215(9)(h)8.8. Maximum demonstrated MWC unit load shall be determined during the initial compliance test for dioxins/furans and each subsequent performance test during which compliance with the dioxin/furan emission limit under sub. (4) is achieved. Maximum demonstrated MWC unit load shall be the maximum 4- hour arithmetic average load achieved during the most recent test during which compliance with the dioxin/furan limit was achieved. NR 440.215(9)(h)9.9. The maximum demonstrated particulate matter control device temperature shall be determined during the initial compliance test for dioxins/furans and each subsequent performance test during which compliance with the dioxin/furan emission limit under sub. (4) is achieved. Maximum demonstrated particulate matter control device temperature shall be the maximum 4-hour arithmetic average temperature achieved at the final particulate matter control device inlet during the most recent test during which compliance with the dioxin/furan limit was achieved. NR 440.215(9)(h)10.10. At a minimum, valid CEMS data for carbon monoxide, steam or feedwater flow and particulate matter control device inlet temperature shall be obtained 75% of the hours per day for 75% of the days per month the affected facility is operated and combusting MSW. NR 440.215(9)(h)11.11. All valid data shall be used in calculating the parameters specified under this paragraph even if the minimum data requirements of subd. 10. are not met. NR 440.215(9)(h)12.12. Quarterly accuracy determinations and daily calibration drift tests for carbon monoxide CEMS shall be performed in accordance with procedure 1 of Appendix F of 40 CFR part 60, incorporated by reference in s. NR 440.17. NR 440.215(9)(j)(j) The following procedures shall be used for calculating MWC unit capacity as defined under sub. (2): NR 440.215(9)(j)1.1. For MWC units capable of combusting MSW continuously for a 24-hour period, MWC unit capacity in megagrams per day or tons per day of MSW combusted shall be calculated based on 24 hours of operation at the maximum design charging rate. The design heating values under subd. 4. shall be used in calculating the design charging rate. NR 440.215(9)(j)2.2. For batch MWC units, MWC unit capacity in megagrams per day or tons per day of MSW combusted shall be calculated as the maximum design amount of MSW that can be charged per batch multiplied by the maximum number of batches that could be processed in a 24-hour period. The maximum number of batches that could be processed in a 24-hour period is calculated as 24 hours divided by the design number of hours required to process one batch of MSW, and may include fractional batches. The design heating values under subd. 4. shall be used in calculating the MWC unit capacity in megagrams per day or tons per day of MSW. NR 440.215 NoteNote: For example, if one batch requires 16 hours then 24/16 or 1.5 batches could be combusted in a 24-hour period.
NR 440.215(9)(j)4.4. MWC unit capacity shall be calculated using a design heating value of 10,500 kilojoules per kilogram (4,500 Btu per pound) for all MSW. NR 440.215(10)(10) Reporting and recordkeeping requirements. The owner or operator of an affected facility located at an MWC plant with a capacity greater than 225 megagrams per day (250 tons per day) shall provide notification of intent to construct and of planned initial startup date and the type or types of fuels planned for combustion in the affected facility. The MWC unit capacity and MWC plant capacity and supporting capacity calculations shall be provided at the time of the notification of construction. NR 440.215(10c)(10c) Daily records. The owner or operator of an affected facility located within a small or large MWC plant and subject to the standards under sub. (3), (4), (5), (6) or (7) shall maintain records of the following information for each affected facility for a period of at least 2 years: