Section 326 IAC 8-19-5 - Compliance testing requirementsAuthority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11
Affected: IC 13-15; IC 13-17
Sec. 5.
(a) Upon the commissioner's request, the owner or operator of a batch process train or unit operation within a batch process train shall conduct testing to demonstrate compliance with section 3 this rule. The owner or operator shall, at its own expense, conduct the tests in accordance with the applicable test methods and procedures specified in subsections (d), (e), and (f).(b) Notwithstanding subsection (a), flares and process boilers used to comply with the control requirements of section 3 of this rule shall be exempt from compliance testing requirements.(c) When a flare is used to comply with the control requirements of section 3 of this rule, the flare shall comply with the requirements of 40 CFR 60.18 *.(d) The owner or operator of a batch process train or unit operation within a batch process train that is exempt from the control requirements of section 3 of this rule due to: (1) an average flow rate that is equal to or above the calculated applicability flow rate; or(2) a VOC concentration of less than or equal to five hundred (500) ppmv (unit operation); shall demonstrate, upon the commissioner's request, the absence of oversized gas moving equipment in any manifold. Gas moving equipment shall be considered oversized if it exceeds the maximum requirements of the exhaust flow rate by more than thirty percent (30%).(e) For the purpose of demonstrating compliance with the control requirements in section 3 of this rule, the batch process train or unit operation shall be run at representative operating conditions and flow rates during any compliance test.(f) The following methods in 40 CFR 60, Appendix A* shall be used to demonstrate compliance with the reduction efficiency requirement set forth in section 3 of this rule: (1) U.S. EPA Method 1 or 1A, as appropriate, for selection of the sampling sites if the flow measuring device is not a rotameter. The control device inlet sampling site for determination of vent stream VOC composition reduction efficiency shall be prior to the control device and after the control device.(2) U.S. EPA Method 2, 2A, 2B, 2C, or 2D, as appropriate, for determination of gas stream volumetric flow rate flow measurements, which shall be taken continuously. No traverse is necessary when the flow measuring device is an ultrasonic probe.(3) U.S. EPA Method 25A or U.S. EPA Method 18, if applicable, to determine the concentration of VOC in the control device inlet and outlet as follows:(A) The sampling time for each run shall be as follows:(i) For batch cycles less than eight (8) hours in length, readings shall be taken continuously over the entire length of the batch cycle with a maximum of fifteen (15) minute intervals between measurements if using U.S. EPA Method 25A. If using U.S. EPA Method 18, readings shall be taken continuously with a maximum of fifteen (15) minute intervals between measurements throughout the batch cycle unless it becomes necessary to change the impinger train, in which case a thirty (30) minute interval shall not be exceeded.(ii) For batch cycles of eight (8) hours and greater in length, the owner or operator may either test in accordance with the test procedures defined in item (i) or the owner or operator may elect to perform tests, pursuant to either U.S. EPA Method 25A or U.S. EPA Method 18, only during those portions of each emission event that define the emission profile of each emission event occurring within the batch cycle. For each emission event of less than four (4) hours in duration, the owner or operator shall test continuously over the entire emission event as set forth in item (i). For each emission event of greater than four (4) hours in duration, the owner or operator shall elect either to perform a minimum of three (3) one (1) hour test runs during the emission event or shall test continuously over the entire emission event within each unit operation in the batch process train. To demonstrate that the portion of the emission event to be tested defines the emission profile for the emission event, the owner or operator electing to rely on this option shall develop an emission profile for the entire emission event. The emission profile shall be based upon either process knowledge or test data collected. Examples of information that could constitute process knowledge include, but are not limited to, calculations based on material balances and process stoichiometry. Previous test results may be used provided the results are still relevant to the current process vent stream conditions.(B) The mass emission rate from the process vent or inlet to the control device shall be determined by combining concentration and flow rate measurements taken simultaneously at sampling sites selected in accordance with subdivision (1) throughout the batch cycle.(C) The mass emission rate from the control device outlet shall be obtained by combining concentration and flow rate measurements taken simultaneously at sampling sites selected in accordance with subdivision (1) throughout the batch cycle.(D) The efficiency of the control device shall be determined by integrating the mass emission rates obtained in clauses (B) and (C) over the time of the batch cycle and dividing the difference in inlet and outlet mass flow totals by the inlet mass flow total.(g) The owner or operator of a batch process train or unit operation may propose an alternative test method or procedures to demonstrate compliance with the control requirements set forth in section 3 of this rule. The method or procedures shall be:(1) approved by the commissioner and U.S. EPA in writing; and(2) included as federally enforceable permit conditions.(h) In the absence of a request by the commissioner to conduct compliance testing in accordance with provisions of this rule, the owner or operator may demonstrate compliance by the use of engineering estimates or process stoichiometry.(i) During the compliance test conducted to demonstrate compliance with the control requirements of section 3 of this rule, the owner or operator shall establish the operating limits (operating parameter values) for the monitoring devices required under section 6 of this rule. *These documents are incorporated by reference. Copies may be obtained from the Government Printing Office, 732 North Capitol Street NW, Washington, D.C. or are available for review and copying at the Indiana Department of Environmental Manageme nt, Office of Air Quality, Indiana Government Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.
Air Pollution Control Board; 326 IAC 8-19-5; filed Nov 3, 2009, 3:32 p.m.: 20091202-IR-326090222FRA; errata filed Nov 19, 2009, 10:03 a.m.: 20091216-IR-326090222ACA