(3) An owner or operator may choose to test only those periods of the batch emission episode during which the emission rate for the entire batch emission episode can be determined or during which the organic HAP emissions are greater than the average emission rate of the batch emission episode. The owner or operator choosing either of these options shall develop an emission profile illustrating the emission rate (kilogram per unit time) over the entire batch emission episode, based on either process knowledge or test data, to demonstrate that test periods are representative. Examples of information that could constitute process knowledge include calculations based on material balances and process stoichiometry. Previous test results may be used to develop the emission profile provided the results are still relevant to the current batch process vent conditions. The emission profile shall be included in the site-specific test plan required by §63.1417(h)(2).
    (4) When choosing sampling sites using the methods specified in §63.1414(a)(1), inlet sampling sites shall be located as specified in paragraphs (e)(1)(ii)(A)(4)(i) and (ii) of this section. Outlet sampling sites shall be located at the outlet of the control device prior to release to the atmosphere.
    (i) The control device inlet sampling site shall be located at the exit from the batch unit operation after any condensers operating as process condensers and before any control device.
    (ii) If a batch process vent is introduced with the combustion air or as a secondary fuel into a boiler or process heater with a design capacity less than 44 megawatts, selection of the location of the inlet sampling sites shall ensure the measurement of total organic HAP concentrations in all batch process vents and primary and secondary fuels introduced into the boiler or process heater.
    (B) Testing only the most challenging batch emission episode. Under this paragraph, an owner or operator groups together several batch emission episodes and conducts a single performance test for the batch emission episode that is the most challenging, in terms of achieving emission reductions, for the control device or control technology; thereby demonstrating that the achieved emission reduction for the tested batch emission episode is the minimum control device or control technology performance expected for each batch emission episode in the group. The owner or operator shall use the control device efficiency determined from the performance test for all the other batch emission episodes in that group for purposes of paragraph (e)(2)(iii) of this section. Performance tests shall be conducted using the testing procedures specified in §63.1414(a) and (b) and the following procedures:
    (1) The procedures specified in paragraphs (e)(2)(ii)(A)(2) through (4) of this section.
    (2) Develop an emission profile illustrating the emission rate (kilogram/unit time) for each period of emissions to be addressed by the performance test. The emission profile shall be based on either process knowledge or test data. Examples of information that could constitute process knowledge include calculations based on material balances and process stoichiometry. Previous test results may be used to develop the emission profile provided the results are still relevant to the current batch process vent conditions. The emission profile shall be included in the site-specific test plan required by §63.1417(h)(2).
    (3) Provide rationale for why the control device efficiency for all the other batch emission episodes in the group will be greater than or equal to the control device efficiency achieved during the tested period of the most challenging batch emission episode in the group, as specified in the Notification of Compliance Status Report required by §63.1417(e).
    (iii) Batch cycle percent reduction. The percent reduction for the batch cycle for an individual reactor batch process vent and the overall percent reduction for the collection of non-reactor batch process vents within the affected source shall be determined using Equation 1 of this section and the control device efficiencies specified in paragraphs (e)(1)(iii)(A) through (C) of this section. All information used to calculate the batch cycle percent reduction for an individual reactor batch process vent, including a definition of the batch cycle identifying all batch emission episodes, shall be recorded as specified in §63.1416 (d)(1)(ii). All information used to calculate the overall percent reduction for the collection of non-reactor batch process vents within the affected source, including a list of all batch emission episodes from the collection of non-reactor batch process vents within the affected source, shall be recorded as specified in §63.1416 (d)(1)(ii). This information shall include identification of those batch emission episodes, or portions thereof, selected for control. This information shall include estimates of uncontrolled organic HAP emissions for those batch emission episodes, or portions thereof, that are not selected for control, determined as specified in paragraph (e)(2)(iii)(D) or (E) of this section.

Where:
PR = Percent reduction.
Eunc = Mass rate of total organic HAP for uncontrolled batch emission episode i, kg/hr.
Einlet,  con = Mass rate of total organic HAP for controlled batch emission episode i at the inlet to the control device, kg/hr.
R = Control efficiency of control device as specified in paragraphs (e)(1)(iii)(A) through (e)(1)(iii)(C) of this section. The value of R may vary between batch emission episodes.
n = Number of uncontrolled batch emission episodes, controlled batch emission episodes, and control devices. The value of n is not necessarily the same for these three items.
    (A) When conducting a performance test, the control efficiency of the control device shall be determined following the procedures in §63.1414(b)(4).
    (B) For combustion control devices listed in paragraphs (a)(2)(i)(A) and (B) of this section and for flares, the control efficiency in Equation 1 of this section shall be 98 percent.
    (C) If a performance test is not required, the control efficiency shall be based on the design evaluation specified in paragraph (e)(1)(i) of this section.
    (D) For batch process vents estimated through engineering assessment, as described in §63.1414(f)(6), to emit less than 10 tons per year of uncontrolled organic HAP emissions, the owner or operator may use in Equation 1 of this section the emissions determined using engineering assessment or may determine organic HAP emissions using any of the procedures specified in §63.1414(d).
    (E) For batch process vents estimated through engineering assessment, as described in §63.1414(d)(6), to emit 10 tons per year or greater of uncontrolled organic HAP emissions, organic HAP emissions shall be estimated following the procedures specified in §63.1414(d).
    (F) Owners or operators designating a condenser, sometimes operated as a process condenser, as a control device shall conduct inprocess recycling and follow the recordkeeping requirements specified in §63.1416(d)(1)(vi).
    (iv) Initial compliance with percent reduction standards. Initial compliance with the percent reduction standards specified in §63.1406(a)(1)(ii) and (2)(ii) and §63.1407(a)(2)(ii) and (3)(ii) is achieved when the owner or operator demonstrates, following the procedures in paragraphs (e)(1)(i) through (iii) of this section, that the required percent reduction is achieved.
    (v) Continuous compliance with percent reduction standards. Continuous compliance with the percent reduction standards specified in §63.1406(a)(1)(ii) and (2)(ii) and §63.1407(a)(2)(ii) and (3)(ii) shall be demonstrated following the continuous monitoring procedures specified in §63.1415.
    (2) Compliance with mass emission limit standards. Each owner or operator shall determine initial and continuous compliance with the mass emission limits specified in §63.1406 (a)(1)(iii) and (a)(2)(iii), according to the following procedures, as appropriate:
    (i) If production at an affected source is exclusively non-solvent-based amino/phenolic resin or is exclusively solvent-based amino/phenolic resin, or an owner or operator chooses to meet the non-solvent-based emission limit, the owner or operator shall demonstrate initial and continuous compliance as follows:
    (A) Initial compliance. Initial compliance shall be based on the average of the first 6 monthly average emission rate data points. The 6-month average shall be compared to the mass emission limit specified in §63.1406 (a)(1)(iii) and (a)(2)(iii), as appropriate.
    (B) Continuous compliance. For the first year of compliance, continuous compliance shall be based on a cumulative average monthly emission rate calculated each month based on the available monthly emission rate data points (e.g., 7 data points after 7 months of operation, 8 data points after 8 months of operation) beginning the first month after initial compliance is demonstrated. The first continuous compliance cumulative average monthly emission rate shall be calculated using the first 7 monthly average emission rate data points. After the first year of compliance, a 12-month rolling average monthly emission rate shall be calculated each month based on the previous 12 monthly emission rate data points. Continuous compliance shall be determined by comparing the cumulative average monthly emission rate or the 12-month rolling average monthly emission rate to the mass emission limit specified in §63.1406 (a)(1)(iii) and (a)(2)(iii), as appropriate.
    (C) Procedures to determine the monthly emission rate. The monthly emission rate, kilograms of organic HAP per megagram of product, shall be determined at the end of each month using Equation 2 of this section:

Where:
ER = Emission rate of organic HAP from reactor batch process vents, kg of HAP/Mg product.
Ei = Emission rate of organic HAP from reactor batch process vent i as determined using the procedures specified in paragraph (e)(2)(i)(C)(1) of this section, kg/month.
RPm = Amount of resin produced in one month as determined using the procedures specified in paragraph (e)(2)(i)(C)(4) of this section, Mg/month.
n = Number of batch process vents.
    (1) The monthly emission rate of organic HAP, in kilograms per month, from an individual batch process vent (Ei) shall be determined using Equation 3 of this section. Once organic HAP emissions for a batch cycle (Ecyclei) have been estimated, as specified in either paragraph (e)(2)(i)(C)(2) or (3) of this section, the owner or operator may use the estimated organic HAP emissions (Ecyclei) to determine Ei using Equation 3 of this section until the estimated organic HAP emissions (Ecyclei) are no longer representative due to a process change or other reasons known to the owner or operator. If organic HAP emissions for a batch cycle (Ecyclei) are determined to no longer be representative, the owner or operator shall redetermine organic HAP emissions for the batch cycle (Ecyclei) following the procedures in paragraph (e)(2)(i)(C)(2) or (3) of this section, as appropriate.

Where:
Ei = Monthly emissions from a batch process vent, kg/month.
Ni = Number of type i batch cycles performed monthly, cycles/month.
Ecyclei = Emissions from the batch process vent associated with a single type i batch cycle, as determined using the procedures specified in either paragraph (e)(2)(i)(C)(2) or (3) of this section, kg/batch cycle.
n = Number of different types of batch cycles that cause the emission of organic HAP from the batch process vent.
    (2) For reactor batch process vents estimated through engineering assessment, as described in §63.1414(d)(6), to emit less than 10 tons per year of uncontrolled organic HAP emissions, the owner or operator may use the emissions determined using engineering assessment in Equation 3 of this section or may determine organic HAP emissions using any of the procedures specified in §63.1414(d). For reactor batch process vents estimated through engineering assessment, as described in §63.1414(d)(6), to emit 10 tons per year or greater of uncontrolled organic HAP emissions, uncontrolled organic HAP emissions from the batch emission episodes making up the batch cycle shall be estimated following the procedures specified in §63.1414(d).
    (3) For reactor batch process vents vented to a control device or control technology, controlled organic HAP emissions shall be determined as follows:
    (i) Uncontrolled organic HAP emissions shall be determined following the procedures in paragraph (e)(2)(i)(C)(2) of this section.
    (ii) Control device or control technology efficiency shall be determined using the procedures in paragraph (e)(1)(i) of this section for small control devices or the procedures in paragraph (e)(1)(ii) of this section for large control devices.
    (iii) Controlled organic HAP emissions shall be determined by applying the control device or control technology efficiency, determined in paragraph (e)(2)(i)(C)(3)(ii) of this section, to the uncontrolled organic HAP emissions, determined in paragraph (e)(2)(i)(C)(3)(i) of this section.
    (4) The rate of resin produced, RPM (Mg/month), shall be determined based on production records certified by the owner or operator to represent actual production for the month. A sample of the records selected by the owner or operator for this purpose shall be provided to the Administrator in the Precompliance Report as required by §63.1417(d).
    (ii) If production at an affected source reflects a mix of solvent-based and non-solvent-based resin and the owner or operator does not choose to meet the non-solvent-based emission limit specified in §63.1406 (a)(1)(iii) or (a)(2)(iii), as applicable, the owner or operator shall demonstrate initial and continuous compliance as follows:
    (A) Procedures for determining a site-specific emission limit. A site-specific emission limit shall be determined using Equation 4 of this section.

Where:
SSEL = Site specific emission limit, kg of organic HAP/Mg of product.
MGs = Megagrams of solvent-based resin product produced, megagrams.
MGns = Megagrams of non-solvent-based resin product produced, megagrams.
ELs = Emission limit for solvent-based resin product, kg organic HAP/Mg solvent-based resin product.
ELns = Emission limit for non-solvent-based resin product, kg organic HAP/Mg non-solvent-based resin product.
    (B) Initial compliance. For purposes of determining initial compliance, the site-specific emission limit shall be based on production for the first 6 months beginning January 20, 2000 or the first 6 months after initial start-up, whichever is later. Using the site-specific emission limit, initial compliance shall be demonstrated using the procedures in paragraph (e)(2)(i)(A) of this section, as appropriate.
    (C) Continuous compliance. For purposes of determining continuous compliance for the period of operation starting at the beginning of the 7th month and ending after the 12th month, the site-specific emission limit shall be determined each month based on production for the cumulative period. For purposes of determining continuous compliance after the first year of production, the site-specific emission limit shall be determined each month based on production for a 12-month rolling period. Using the site-specific emission limit, continuous compliance shall be demonstrated using the procedures in paragraph (e)(2)(i)(B) of this section, as appropriate.
    (3) Compliance by venting to a flare. Initial compliance with the standards specified in §63.1406(a)(1)(i) and (a)(2)(i) and §63.1407(a)(2)(i) and (a)(3)(i) shall be demonstrated following the procedures specified in paragraph (g) of this section. Continuous compliance with these standards shall be demonstrated following the continuous monitoring procedures specified in §63.1415.
    (4) Compliance with alternative standard. Initial and continuous compliance with the alternative standard specified in §§63.1406(b) and 63.1407(b)(1) shall be demonstrated following the procedures in paragraph (f) of this section.
    (f) Compliance with alternative standard. Initial and continuous compliance with the alternative standards in §§63.1404(b), 63.1405(b)(c), 63.1406(b), 63.1407(b)(1), and 63.1408(b)(1) are demonstrated when the daily average outlet organic HAP concentration is 20 ppmv or less when using a combustion control device or 50 ppmv or less when using a non-combustion control device. To demonstrate initial and continuous compliance, the owner or operator shall follow the test method specified in §63.1414(a)(6) and shall be in compliance with the monitoring provisions in §63.1415(e) no later than the initial compliance date and on each day thereafter.
    (g) Flare compliance demonstrations. Notwithstanding any other provision of this subpart, if an owner or operator of an affected source uses a flare to comply with any of the requirements of this subpart, the owner or operator shall comply with paragraphs (g)(1) through (3) of this section. When using a flare to comply, the owner or operator is not required to conduct a performance test to determine percent emission reduction or outlet organic HAP concentration. If a compliance demonstration has been conducted previously for a flare, using the techniques specified in paragraphs (g)(1) through (3) of this section, that compliance demonstration may be used to satisfy the requirements of this paragraph if either no deliberate process changes have been made since the compliance demonstration, or the results of the compliance demonstration reliably demonstrate compliance despite process changes.
    (1) Conduct a visible emission test using the techniques specified in §63.11(b)(4).
    (2) Determine the net heating value of the gas being combusted using the techniques specified in §63.11(b)(6).
    (3) Determine the exit velocity using the techniques specified in either §63.11(b)(7)(i) (and §63.11(b)(7)(iii), where applicable) or §63.11(b)(8), as appropriate.
    (h) Continuous process vent compliance at existing sources. (1) Each owner or operator complying with the mass emission limit specified in §63.1405(a)(3)(b)(2)(i) shall determine initial compliance as specified in paragraph (h)(1)(i) of this section and continuous compliance as specified in paragraph (h)(1)(ii) of this section.
      (i) Initial compliance. Initial compliance shall be determined by comparing the results of the performance test or design evaluation as specified in paragraph (a)(1) of this section based on the average of the first 6 monthly average emission rate data points. The 6-month average shall be compared to the mass emission limit specified in §63.1405(a)(3)(b)(2)(i).
      (ii) Continuous compliance. For the first year of compliance, cContinuous compliance shall be based on the daily a cumulative average monthly emission rate calculated for each operating day.each month based on the available monthly emission rate data points (e.g., 7 data points after 7 months of operation, 8 data points after 8 months of operation) beginning the first month after initial compliance is demonstrated. The first continuous compliance cumulative average dailymonthly emission rate shall be calculated using the first 24-hour period or otherwise-specified operating day after the compliance date.7 monthly average emission rate data points. After the first year of compliance, a 12-month rolling average monthly emission rate shall be calculated each month based on the previous 12 monthly emission rate data points. Continuous compliance shall be determined by comparing the cumulative daily average monthly   emission rate or the 12-month rolling average monthly emission rate to the mass emission limit specified in §63.1405(a)(3)(b)(2)(i).
      (2) As required by paragraph (c)(6)(ii) of this section, each owner or operator complying with the emission rate limits specified in §63.1405(b)(2)(ii) and (iii), as applicable, by means other than those specified in paragraph (c)(6)(i) of this section shall determine initial compliance as specified in paragraph (h)(2)(i) of this section and continuous compliance as specified in paragraph (h)(2)(ii) of this section.
      (i) Initial compliance. Initial compliance shall be determined by comparing the results of the performance test or design evaluation as specified in paragraph (a)(1) of this section to the emission rate limits specified in §63.1405(b)(2)(ii) and (iii), as applicable.
      (ii) Continuous compliance. Continuous compliance shall be based on the hourly average emission rate calculated for each operating day. The first continuous compliance average hourly emission rate shall be calculated using the first 24-hour period or otherwise-specified operating day after the compliance date. Continuous compliance shall be determined by comparing the average hourly emission rate to the emission rate limit specified in §63.1405(b)(2)(ii) or (iii), as applicable.
      (2)(3) Procedures to determine continuous compliance with the mass emission limit specified in §63.1405(b)(2)(i).the monthly emission rate. (i) The daily monthly emission rate, kilograms of organic HAP per megagram of product, shall be determined for each operating dayat the end of each month using Equation 5 of this section:

    Where:
    ER = Emission rate of organic HAP from continuous process vent, kg of HAP/Mg product.
    Ei = Emission rate of organic HAP from continuous process vent i as determined using the procedures specified in paragraph (h)(23)(ii) of this section, kg/daymonth.
    RPm = Amount of resin produced in one month as determined using the procedures specified in paragraph (h)(23)(iii) of this section, Mg/daymonth.
      (ii) The dailymonthly emission rate of organic HAP, in kilograms per daymonth, from an individual continuous process vent (Ei) shall be determined. Once organic HAP emissions have been estimated, as specified in paragraph (h)(23)(ii)(A) of this section for uncontrolled continuous process vents or paragraphs (h)(2)(ii)(A) and (B) of this section for continuous process vents vented to a control device or control technology, the owner or operator may use the estimated organic HAP emissions (Ei) until the estimated organic HAP emissions are no longer representative due to a process change or other reason known to the owner or operator. If organic HAP emissions (Ei) are determined to no longer be representative, the owner or operator shall redetermine organic HAP emissions for the continuous process vent following the procedures in paragraph (h)(23)(ii)(A) of this section for uncontrolled continuous process vents or paragraphs (h)(23)(ii)(A) and (B) of this section for continuous process vents vented to a control device or control technology.
      (A) For continuous process vents estimated through engineering assessment, as described in §63.1414(d)(10), to emit less than 10 tons per year of uncontrolled organic HAP emissions, the owner or operator may use the emissions determined using engineering assessment in Equation 5 of this section or may determine organic HAP emissions using the procedures specified in paragraph (a)(1)(i) of this section. For continuous process vents estimated through engineering assessment, as described in §63.1414(d)(10), to emit 10 tons per year or greater of uncontrolled organic HAP emissions, uncontrolled organic HAP emissions shall be estimated following the procedures specified in paragraph (a)(1)(i) of this section.
      (B) For continuous process vents vented to a control device or control technology, controlled organic HAP emissions shall be determined as follows:
      (1) Uncontrolled organic HAP emissions shall be determined following the procedures in paragraph (h)(2)(ii)(A) of this section.
      (2) Control device or control technology efficiency shall be determined using the procedures in paragraph (a)(1)(i) of this section for large control devices or the procedures in paragraph (a)(1)(ii) of this section for small control devices.
      (3) Controlled organic HAP emissions shall be determined by applying the control device or control technology efficiency, determined in paragraph (h)(2)(ii)(B)(2) of this section, to the uncontrolled organic HAP emissions, determined in paragraph (h)(2)(ii)(B)(1) of this section.
      (iii) The rate of resin produced, RPM (Mg/daymonth), shall be determined based on production records certified by the owner or operator to represent actual production for the daymonth. A sample of the records selected by the owner or operator for this purpose shall be provided to the Administrator in the Precompliance Report as required by §63.1417(d).
      (4) Procedures to determine continuous compliance with the emission rate limit specified in §63.1405(b)(2)(ii) or (iii).
      (i) The hourly emission rate, kilograms of organic HAP per hour, shall be determined for each hour during the operating day using Equation 6 of this section:
      EH=K2j=1nCjMjQS (Eq.6)
      Where:
      EH = 	Hourly emission rate of organic HAP in the sample, kilograms per hour.
      K2 = 	Constant, 2.494 x 10[−6] (parts per million)[−1] (gram-mole per standard cubic meter) (kilogram/gram) (minutes/hour), where standard temperature for (gram-mole per standard cubic meter) is 20 °C.
      n = 	Number of components in the sample.
      CJ = 	Organic HAP concentration on a dry basis of organic compound j in parts per million as determined by the methods specified in paragraph (h)(4)(ii) of this section.
      Mj = 	Molecular weight of organic compound j, gram/gram-mole.
      QS = 	Continuous process vent flow rate, dry standard cubic meter per minute, at a temperature of 20 °C, as determined by the methods specified in paragraph (h)(4)(ii) of this section.
       (ii) The average hourly emission rate, kilograms of organic HAP per hour, shall be determined for each operating day using Equation 7 of this section:
      AE=i=1nEHn
(Eq.7)

      Where:
      AE = Average hourly emission rate per operating day, kilograms per hour.
      n = 	Number of hours in the operating day.
      (ii) Continuous process vent flow rate and organic HAP concentration shall be determined using the procedures specified in §63.1414(a), or by using the engineering assessment procedures in paragraph (h)(4)(iii) of this section.
       (iii) Engineering assessment. For the purposes of determining continuous compliance with the emission rate limit specified in §63.1405(b)(2)(ii) or (iii) using Equations 6 and 7, engineering assessments may be used to determine continuous process vent flow rate and organic HAP concentration. An engineering assessment includes, but is not limited to, the following examples:
      (A) Previous test results, provided the tests are representative of current operating practices.
      (B) Bench-scale or pilot-scale test data representative of the process under representative operating conditions.
      (C) Maximum volumetric flow rate or organic HAP concentration specified or implied within a permit limit applicable to the continuous process vent.
      (D) Design analysis based on accepted chemical engineering principles, measurable process parameters, or physical or chemical laws or properties. Examples of analytical methods include, but are not limited to, the following:
      (1) Estimation of maximum organic HAP concentrations based on process stoichiometry material balances or saturation conditions; and
      (2) Estimation of maximum volumetric flow rate based on physical equipment design such as pump or blower capacities.
    (i) Deviations. Paragraphs (i)(1) through (4) of this section describe deviations from the emission limits, the operating limits, the work practice standards, and the emission standard, respectively. Paragraph (i)(5) of this section describes situations that are not deviations. Paragraph (i)(6) of this section describes periods that are excluded from compliance determinations.
    (1) Deviations from the emission limit. The following are deviations from the emission limit:
    (i) Exceedance of the condenser outlet gas temperature limit (i.e., having an average value higher than the established maximum level) monitored according to the provisions of §63.1415(b)(3);
    (ii) Exceedance of the outlet concentration (i.e., having an average value higher than the established maximum level) monitored according to the provisions of §63.1415(b)(8);
    (iii) Exceedance of the mass emission limit (i.e., having an average value higher than the specified limit) monitored according to the provisions of paragraph (e)(2) of this section for batch process vents and according to the provisions of paragraph (h)(1) of this section for continuous process vents; and
    (iv) Exceedance of the organic HAP outlet concentration limit (i.e., having an average value higher than the specified limit) monitored according to the provisions of §63.1415(e); and
    (v) Exceedance of the emission rate limit (i.e., having an average value higher than the specified limit) determined according to the provisions of paragraph (h)(2) of this section.
    (2) Deviations from the operating limit. Exceedance of the parameters monitored according to §63.1415(b)(1), (b)(2), and (b)(4) through (7) are considered deviations from the operating limit. An exceedance of the monitored parameter has occurred if:
    (i) The parameter, averaged over the operating day or block, is below a minimum value established during the initial compliance demonstration; or (ii) The parameter, averaged over the operating day or block, is above the maximum value established during the initial compliance demonstration.
    (3) Deviations from the work practice standard. If all flames at the pilot light of a flare are absent, there has been a deviation from the work practice standard.
    (4) Deviation from the emission standard. If monitoring data are insufficient, as described in paragraphs (i)(4)(i) through (iii) of this section, there has been a deviation from the emission standard.
    (i) The period of control device or control technology operation is 4 hours or greater in an operating day, and monitoring data are insufficient to constitute a valid hour of data, as defined in paragraph (i)(4)(iii) of this section, for at least 75 percent of the operating hours;
    (ii) The period of control device or control technology operation is less than 4 hours in an operating day, and more than one of the hours during the period of operation does not constitute a valid hour of data due to insufficient monitoring data; and
    (iii) Monitoring data are insufficient to constitute a valid hour of data, as used in paragraphs (i)(4)(i) and (ii) of this section, if measured values are unavailable for any of the 15-minute periods within the hour. For data compression systems approved under §63.1417(k)(3), monitoring data are insufficient to calculate a valid hour of data if there are less than four data measurements made during the hour.
    (5) Situations that are not deviations. If any of the situations listed in paragraphs (i)(5)(i) or (ii) of this section occur, such situations shall not be considered to be deviations.
    (i) Monitoring data cannot be collected during monitoring device calibration check or monitoring device malfunction; or
    (ii) Monitoring data are not collected during periods of nonoperation of the affected source or portion thereof (resulting in cessation of the emissions to which the monitoring applies).
    (6) Periods not considered to be part of the period of control or recovery device operation. The periods listed in paragraphs (i)(6)(i) and (ii) of this section are not considered to be part of the period of control or recovery device operation for purposes of determining averages or periods of control device or control technology operation.
    (i) Monitoring system breakdowns, repairs, calibration checks, and zero (low-level) and high-level adjustments; or
    (ii) Periods of nonoperation of the affected source (or portion thereof), resulting in cessation of the emissions to which the monitoring applies.
§63.1414   Test methods and emission estimation equations.
    (a) Test methods. When required to conduct a performance test, the owner or operator shall use the test methods specified in paragraphs (a)(1) through (6) of this section, except where another section of this subpart requires either the use of a specific test method or the use of requirements in another subpart containing specific test method requirements.
    (1) Method 1 or 1A, 40 CFR part 60, appendix A, shall be used for selection of the sampling sites if the flow measuring device is a pitot tube, except that references to particulate matter in Method 1A do not apply for the purposes of this subpart. No traverse is necessary when Method 2A or 2D, 40 CFR part 60, appendix A is used to determine gas stream volumetric flow rate.
    (2) Method 2, 2A, 2C, or 2D, 40 CFR part 60, appendix A, is used for velocity and volumetric flow rates.
    (3) Method 3, 40 CFR part 60, appendix A, is used for gas analysis.
    (4) Method 4, 40 CFR part 60, appendix A, is used for stack gas moisture.
    (5) The following methods shall be used to determine the organic HAP concentration.
    (i) Method 316 or Method 320, 40 CFR part 60, appendix A, shall be used to determine the concentration of formaldehyde.
    (ii) Method 18, 40 CFR part 60, appendix A, shall be used to determine the concentration of all organic HAP other than formaldehyde.
    (iii) Method 308, 40 CFR part 60, appendix A, may be used as an alternative to Method 18 to determine the concentration of methanol.
    (6) When complying with the alternative standard, as specified in §63.1413(f), the owner or operator shall use a Fourier Transform Infrared Spectroscopy (FTIR) instrument following Method PS-15, 40 CFR part 60, appendix B.
    (b) Batch process vent performance testing procedures -- (1) Average batch vent flow rate determination. The average batch vent flow rate for a batch emission episode shall be calculated using Equation 1 of this section:

Where:
AFRepisode = Average batch vent flow rate for the batch emission episode, scmm.
FRi = Volumetric flow rate for individual measurement i, taken every 15 minutes using the procedures in paragraph (a)(2) of this section, scmm.
n = Number of flow rate measurements taken during the batch emission episode.
    (2) Average batch vent concentration determination using an integrated sample. If an integrated sample is taken over the entire batch emission episode to determine the average batch vent concentration of total organic HAP, organic HAP emissions shall be calculated using Equation 2 of this section:

Where:
Eepisode = Emissions, kg/episode.
K = Constant, 2.494 x 10[−6] (ppmv)[−1] (gm-mole/scm) (kg/gm) (min/hr), where standard temperature is 20 °C.
Cj = Average batch vent concentration of sample organic HAP component j of the gas stream, dry basis, ppmv.
Mj = Molecular weight of sample organic HAP component j of the gas stream, gm/gm-mole.
AFR = Average batch vent flow rate of gas stream, dry basis, scmm.
Th = Hours/episode.
n = Number of organic HAP in stream.
    (3) Average batch vent concentration determination using grab samples. If grab samples are taken to determine the average batch vent concentration of total organic HAP, organic HAP emissions shall be calculated as follows:
    (i) For each measurement point, the emission rate shall be calculated using Equation 3 of this section:

Where:
Epoint = Emission rate for individual measurement point, kg/hr.
K = Constant, 2.494 x 10[−6] (ppmv)[−1] (gm-mole/scm) (kg/gm) (min/hr), where standard temperature is 20 °C.
Cj = Concentration of sample organic HAP component j of the gas stream, dry basis, ppmv.
Mj = Molecular weight of sample organic HAP component j of the gas stream, gm/gm-mole.
FR = Flow rate of gas stream for the measurement point, dry basis, scmm.
n = Number of organic HAP in stream.
    (ii) The organic HAP emissions per batch emission episode shall be calculated using Equation 4 of this section:

Where:
Eepisode = Emissions, kg/episode.
DUR = Duration of the batch emission episode, hr/episode.
Ei = Emissions for measurement point i, kg/hr.
n = Number of measurements.
    (4) Control device efficiency determination for a batch emission episode. The control efficiency for the control device shall be calculated using Equation 5 of this section:

Where:
R = Control efficiency of control device, percent.
Einlet = Mass rate of total organic HAP for batch emission episode i at the inlet to the control device as calculated under paragraph (b)(2) or (b)(3) of this section, kg/episode.
Eoutlet = Mass rate of total organic HAP for batch emission episode i at the outlet of the control device, as calculated under paragraph (b)(2) or (b)(3) of this section, kg/episode.
n = Number of batch emission episodes in the batch cycle selected to be controlled.
    (c) Percent oxygen correction for combustion control devices. If the control device is a combustion device, total organic HAP concentrations shall be corrected to 3 percent oxygen when supplemental combustion air is used to combust the emissions. The integrated sampling and analysis procedures of Method 3B, 40 CFR part 60, appendix A, shall be used to determine the actual oxygen concentration (%020). The samples shall be taken during the same time that the total organic HAP samples are taken. The concentration corrected to 3 percent oxygen (Cc) shall be computed using Equation 6 of this section:

Where:
Cc = Concentration of total organic HAP corrected to 3 percent oxygen, dry basis, ppmv.
Cm = Total concentration of TOC in vented gas stream, average of samples, dry basis, ppmv.
%02d = Concentration of oxygen measured in vented gas stream, dry basis, percent by volume.
    (d) Uncontrolled organic HAP emissions. Uncontrolled organic HAP emissions for individual reactor batch process vents or individual non-reactor batch process vents shall be determined using the procedures specified in paragraphs (d)(1) through (8) of this section. To estimate organic HAP emissions from a batch emissions episode, owners or operators may use either the emissions estimation equations in paragraphs (d)(1) through (4) of this section, or direct measurement as specified in paragraph (d)(5) of this section. Engineering assessment may be used to estimate organic HAP emissions from a batch emission episode only under the conditions described in paragraph (d)(6) of this section. In using the emissions estimation equations in paragraphs (d)(1) through (4) of this section, individual component vapor pressure and molecular weight may be obtained from standard references. Methods to determine individual HAP partial pressures in multicomponent systems are described in paragraph (d)(9) of this section. Other variables in the emissions estimation equations may be obtained through direct measurement, as defined in paragraph (d)(5) of this section; through engineering assessment, as defined in paragraph (d)(6)(ii) of this section; by process knowledge; or by any other appropriate means. Assumptions used in determining these variables shall be documented as specified in §63.1417. Once organic HAP emissions for the batch emission episode have been determined using either the emissions estimation equations, direct measurement, or engineering assessment, organic HAP emissions from a single batch cycle shall be calculated in accordance with paragraph (d)(7) of this section, and annual organic HAP emissions from the batch process vent shall be calculated in accordance with paragraph (d)(8) of this section.
    (1) Emissions from purging of empty vessels. Organic HAP emissions from the purging of an empty vessel shall be calculated using Equation 7 of this section. Equation 7 of this section does not take into account evaporation of any residual liquid in the vessel:

Where:
Eepisode = Emissions, kg/episode.
Vves = Volume of vessel, m[3].
P = Total organic HAP partial pressure, kPa.
MWwavg = Weighted average molecular weight of organic HAP in vapor, determined in accordance with paragraph (d)(4)(i)(D) of this section, kg/kmol.
R = Ideal gas constant, 8.314 m[3]·kPa/kmol·K.
T = Temperature of vessel vapor space, K.
m = Number of volumes of purge gas used.
    (2) Emissions from purging of filled vessels. Organic HAP emissions from the purging of a filled vessel shall be calculated using Equation 8 of this section:

Where:
Eepisode = Emissions, kg/episode.
y = Saturated mole fraction of all organic HAP in vapor phase.
Vdr = Volumetric gas displacement rate, m[3]/min.
P = Pressure in vessel vapor space, kPa.
MWwavg = Weighted average molecular weight of organic HAP in vapor, determined in accordance with paragraph (d)(4)(i)(D) of this section, kg/kmol.
R = Ideal gas constant, 8.314 m[3]·kPa/kmol·K.
T = Temperature of vessel vapor space, K.
Pi = Vapor pressure of individual organic HAP i, kPa.
xi = Mole fraction of organic HAP i in the liquid.
n = Number of organic HAP in stream.
Tm = Minutes/episode.
    (3) Emissions from vapor displacement. Organic HAP emissions from vapor displacement due to transfer of material into or out of a vessel shall be calculated using Equation 9 of this section:

Where:
Eepisode = Emissions, kg/episode.
y = Saturated mole fraction of all organic HAP in vapor phase.
V = Volume of gas displaced from the vessel, m[3].
P = Pressure in vessel vapor space, kPa.
MWwavg = Weighted average molecular weight of organic HAP in vapor, determined in accordance with paragraph (d)(4)(i)(D) of this section, kg/kmol.
R = Ideal gas constant, 8.314 m[3]·kPa/kmol·K.
T = Temperature of vessel vapor space, K.
    (4) Emissions from heating of vessels. Organic HAP emissions caused by the heating of a vessel shall be calculated using the procedures in either paragraph (d)(4)(i),(ii), or (iii) of this section, as appropriate.
    (i) If the final temperature to which the vessel contents is heated is lower than 50 K below the boiling point of the HAP in the vessel, then organic HAP emissions shall be calculated using the equations in paragraphs (d)(4)(i)(A) through (D) of this section.
    (A) Organic HAP emissions caused by heating of a vessel shall be calculated using Equation 10 of this section. The assumptions made for this calculation are atmospheric pressure of 760 millimeters of mercury (mm Hg) and the displaced gas is always saturated with volatile organic compounds (VOC) vapor in equilibrium with the liquid mixture:

Where:
Eepisode = Emissions, kg/episode.
(Pi)T1, (Pi)T2 = Partial pressure (kPa) of each organic HAP i in the vessel headspace at initial (T1) and final (T2) temperature.
n = Number of organic HAP in stream.
Δη = Number of kilogram-moles (kg-moles) of gas displaced, determined in accordance with paragraph (d)(4)(i)(B) of this section.
101.325 = Constant, kPa.
(MWWAVG,  T1), (MWWAVG,  T2) = Weighted average molecular weight of total organic HAP in the displaced gas stream, determined in accordance with paragraph (d)(4)(i)(D) of this section, kg/kmol.
    (B) The moles of gas displaced, Δ, is calculated using Equation 11 of this section:

Where:
Δη = Number of kg-moles of gas displaced.
Vfs = Volume of free space in the vessel, m[3].
R = Ideal gas constant, 8.314 m[3]·kPa/kmol·K.
Pa1 = Initial noncondensible gas partial pressure in the vessel, kPa.
Pa2 = Final noncondensible gas partial pressure in the vessel, kPa.
T1 = Initial temperature of vessel, K.
T2 = Final temperature of vessel, K.
    (C) The initial and final pressure of the noncondensible gas in the vessel shall be calculated using Equation 12 of this section:

Where:
Pa = Initial or final partial pressure of noncondensible gas in the vessel headspace, kPa.
101.325 = Constant, kPa.
(Pi)T = Partial pressure of each organic HAP i in the vessel headspace, kPa, at the initial or final temperature (T1 or T2).
n = Number of organic HAP in stream.
    (D) The weighted average molecular weight of organic HAP in the displaced gas, MWwavg, shall be calculated using Equation 13 of this section:

Where:
C = Organic HAP component
n = Number of organic HAP components in stream.
    (ii) If the vessel contents are heated to a temperature greater than 50 K below the boiling point, then organic HAP emissions from the heating of a vessel shall be calculated as the sum of the organic HAP emissions calculated in accordance with paragraphs (d)(4)(ii)(A) and (B) of this section.
    (A) For the interval from the initial temperature to the temperature 50 K below the boiling point, organic HAP emissions shall be calculated using Equation 10 of this section, where T2 is the temperature 50 K below the boiling point.
    (B) For the interval from the temperature 50 K below the boiling point to the final temperature, organic HAP emissions shall be calculated as the summation of emissions for each 5 K increment, where the emissions for each increment shall be calculated using Equation 10 of this section.
    (1) If the final temperature of the heatup is at or lower than 5 K below the boiling point, the final temperature for the last increment shall be the final temperature for the heatup, even if the last increment is less than 5 K.
    (2) If the final temperature of the heatup is higher than 5 K below the boiling point, the final temperature for the last increment shall be the temperature 5 K below the boiling point, even if the last increment is less than 5 K.
    (3) If the vessel contents are heated to the boiling point and the vessel is not operating with a condenser, the final temperature for the final increment shall be the temperature 5 K below the boiling point, even if the last increment is less than 5 K.
    (iii) If the vessel is operating with a condenser, and the vessel contents are heated to the boiling point, the process condenser, as defined in §63.1402, is considered part of the process. Organic HAP emissions shall be calculated as the sum of emissions calculated using Equation 10 of this section, which calculates organic HAP emissions due to heating the vessel contents to the temperature of the gas exiting the condenser, and emissions calculated using Equation 9 of this section, which calculates emissions due to the displacement of the remaining saturated noncondensible gas in the vessel. The final temperature in Equation 10 of this section shall be set equal to the exit gas temperature of the condenser. Equation 9 of this section shall be used as written below in Equation 14 of this section, using free space volume, and T is set equal to the condenser exit gas temperature:

Where:
Eepisode = Emissions, kg/episode.
y = Saturated mole fraction of all organic HAP in vapor phase.
Vfs = Volume of the free space in the vessel, m[3].
P = Pressure in vessel vapor space, kPa.
MWwavg = Weighted average molecular weight of organic HAP in vapor, determined in accordance with paragraph (d)(4)(i)(D) of this section, kg/kmol.
R = Ideal gas constant, 8.314 m[3]·kPa/kmol·K.
T = Temperature of condenser exit stream, K.
    (5) Emissions determined by direct measurement. The owner or operator may estimate annual organic HAP emissions for a batch emission episode by direct measurement. The test methods and procedures specified in paragraphs (a) and (b) of this section shall be used for direct measurement. If direct measurement is used, the owner or operator shall perform a test for the duration of a representative batch emission episode. Alternatively, the owner or operator may perform a test during only those periods of the batch emission episode for which the emission rate for the entire episode can be determined or for which the emissions are greater than the average emission rate of the batch emission episode. The owner or operator choosing either of these options shall develop an emission profile illustrating the emission rate (kilogram per unit time) over the entire batch emission episode, based on either process knowledge or test data, to demonstrate that test periods are representative. Examples of information that could constitute process knowledge include calculations based on material balances and process stoichiometry. Previous test results may be used to develop the emission profile provided the results are still relevant to the current batch process vent conditions. The emission profile shall be included in the site-specific test plan required by §63.1417(h)(2).
    (6) Emissions determined by engineering assessment. To use engineering assessment to estimate organic HAP emissions from a batch emission episode, owners or operators shall comply with paragraphs (d)(6)(i) through (iii) of this section.
    (i) If the criteria specified in paragraphs (d)(6)(i)(A), (B), and (C) of this section are met for a specific batch emission episode, the owner or operator may use engineering assessment to estimate organic HAP emissions from that batch emission episode.
    (A) Previous test data, where the measurement of organic HAP emissions was an outcome of the test, that show a greater than 20 percent discrepancy between the test value and the value estimated using the applicable equations in paragraphs (d)(1) through (4) of this section. Paragraphs (d)(6)(i)(A)(1) and (2) of this section describe test data that will be acceptable under this paragraph.
    (1) Test data for the batch emission episode obtained during production of the product for which the demonstration is being made.
    (2) Test data obtained for a batch emission episode from another process train where the test data were obtained during production of the product for which the demonstration is being made. Test data from another process train may be used only if the owner or operator can demonstrate that the data are representative of the batch emission episode for which the demonstration is being made, taking into account the nature, size, operating conditions, production rate, and sequence of process steps (e.g., reaction, distillation, etc.) of the equipment in the other process train.
    (B) Previous test data for the batch emission episode with the highest organic HAP emissions on a mass basis where the measurement of organic HAP emissions was an outcome of the test, where data were obtained during the production of the product for which the demonstration is being made, and where the data show a greater than 20 percent discrepancy between the test value and the value estimated using the applicable equations in paragraphs (d)(1) through (4) of this section. If the criteria in this paragraph are met, then engineering assessment may be used for all batch emission episodes associated with that batch cycle for the batch unit operation.
    (C) The owner or operator has requested and been granted approval to use engineering assessment to estimate organic HAP emissions from a batch emissions episode. The request to use engineering assessment to estimate organic HAP emissions from a batch emissions episode shall contain sufficient information and data to demonstrate to the Administrator that engineering assessment is an accurate means of estimating organic HAP emissions for that particular batch emissions episode. The request to use engineering assessment to estimate organic HAP emissions for a batch emissions episode shall be submitted in the Precompliance Report, as required by §63.1417(d).
    (ii) Engineering assessment includes, but is not limited to, the following:
    (A) Previous test results, provided the tests are representative of current operating practices;
    (B) Bench-scale or pilot-scale test data obtained under conditions representative of current process operating conditions;
    (C) Flow rate or organic HAP emission rate specified or implied within a permit limit applicable to the batch process vent; and
    (D) Design analysis based on accepted chemical engineering principles, measurable process parameters, or physical or chemical laws or properties. Examples of analytical methods include, but are not limited to:
    (1) Use of material balances;
    (2) Estimation of flow rate based on physical equipment design such as pump or blower capacities;
    (3) Estimation of organic HAP concentrations based on saturation conditions; and
    (4) Estimation of organic HAP concentrations based on grab samples of the liquid or vapor.
    (iii) Data or other information used to demonstrate that the criteria in paragraph (d)(6)(i) of this section have been met shall be reported as specified in paragraphs (d)(6)(iii)(A) and (B) of this section.
    (A) Data or other information used to demonstrate that the criteria in paragraphs (d)(6)(i)(A) and (B) of this section have been met shall be reported in the Notification of Compliance Status, as required by §63.1417(e)(9).
    (B) The request for approval to use engineering assessment to estimate organic HAP emissions from a batch emissions episode as allowed under paragraph (d)(6)(i)(C) of this section, and sufficient data or other information for demonstrating to the Administrator that engineering assessment is an accurate means of estimating organic HAP emissions for that particular batch emissions episode shall be submitted with the Precompliance Report, as required by §63.1417(d).
    (7) Emissions for a single batch cycle. For each batch process vent, the organic HAP emissions associated with a single batch cycle shall be calculated using Equation 15 of this section:

Where:
Ecycle = Emissions for an individual batch cycle, kg/batch cycle.
Eepisodei = Emissions from batch emission episode i, kg/episode.
n = Number of batch emission episodes for the batch cycle.
    (8) Annual emissions from a batch process vent. Annual organic HAP emissions from a batch process vent shall be calculated using Equation 16 of this section:

Where:
AE = Annual emissions from a batch process vent, kg/yr.
Ni = Number of type i batch cycles performed annually, cycles/year.
Ecyclei = Emissions from the batch process vent associated with a single type i batch cycle, as determined in paragraph (d)(7) of this section, kg/batch cycle.
n = Number of different types of batch cycles that cause the emission of organic HAP from the batch process vent.
    (9) Partial pressures in multicomponent systems. Individual HAP partial pressures in multicomponent systems shall be determined using the appropriate method specified in paragraphs (d)(9)(i) through (iii) of this section.
    (i) If the components are miscible, use Raoult's law to calculate the partial pressures;
    (ii) If the solution is a dilute aqueous mixture, use Henry's law constants to calculate partial pressures;
    (iii) If Raoult's law or Henry's law is not appropriate or available, the owner or operator may use any of the options in paragraph (d)(9)(iii)(A), (B), or (C) of this section.
    (A) Experimentally obtained activity coefficients, Henry's law constants, or solubility data;
    (B) Models, such as group-contribution models, to predict activity coefficients; or
    (C) Assume the components of the system behave independently and use the summation of all vapor pressures from the HAPs as the total HAP partial pressure.
    (10) For continuous process vent emissions determined by engineering assessment, the engineering assessment includes, but is not limited to, the examples provided in §63.1412(k)(3).
§63.1415   Monitoring requirements.
    (a) General requirements. Each owner or operator of an emission point located at an affected source that uses a control device to comply with the requirements of this subpart and has one or more parameter monitoring level requirement specified under this subpart, shall install the monitoring equipment specified in paragraph (b) of this section in order to demonstrate continued compliance with the provisions of this subpart. All monitoring equipment shall be installed, calibrated, maintained, and operated according to manufacturer's specifications or other written procedures that provide adequate assurance that the equipment would reasonably be expected to monitor accurately.
    (1) This monitoring equipment shall be in operation at all times when organic HAP emissions that are required to be controlled as part of complying with the emission limits specified in §§63.1404, 63.1405, 63.1406, 63.1407, and 63.1408 are vented to the control device.
    (2) For control devices controlling less than 1 ton per year of uncontrolled organic HAP emissions, monitoring shall consist of a daily verification that the control device is operating properly. If the control device is used to control batch process vents alone or in combination with other emission points, the verification may be on a per batch cycle basis. This verification shall include, but not be limited to, a daily or per batch demonstration that the control device is working as designed. The procedure for this demonstration shall be submitted for review and approval as part of the Precompliance Report, as required by §63.1417(d)(10).
    (3) Nothing in this section shall be construed to allow a monitoring parameter excursion caused by an activity that violates other applicable provisions of subpart A, F, or G of this part.
    (b) Monitoring equipment. The monitoring equipment specified in paragraphs (b)(1) through (8) of this section shall be installed as specified in paragraph (a) of this section. The parameters to be monitored are specified in Table 3 of this subpart.
    (1) Where a scrubber is used, the following monitoring equipment is required.
    (i) A pH monitoring device equipped with a continuous recorder to monitor the pH of the scrubber effluent.
    (ii) A flow measurement device equipped with a continuous recorder shall be located at the scrubber influent for liquid flow. Gas stream flow shall be determined using one of the following procedures:
    (A) The owner or operator may determine gas stream flow using the design blower capacity with appropriate adjustments for pressure drop.
    (B) If the scrubber is subject to regulations in 40 CFR parts 264 through 266 that required a determination of the liquid to gas (L/G) ratio prior to the applicable compliance date for this subpart, the owner or operator may determine gas stream flow by the method that had been utilized to comply with those regulations. A determination that was conducted prior to the compliance date for this subpart may be utilized to comply with this subpart if it is still representative.
    (C) The owner or operator may prepare and implement a gas stream flow determination plan that documents an appropriate method which will be used to determine the gas stream flow. The plan shall require determination of gas stream flow by a method which will at least provide a value for either a representative or the highest gas stream flow anticipated in the scrubber during representative operating conditions other than malfunctions. The plan shall include a description of the methodology to be followed and an explanation of how the selected methodology will reliably determine the gas stream flow, and a description of the records that will be maintained to document the determination of gas stream flow. The owner or operator shall maintain the plan as specified in §63.1416(a).
    (2) Where an absorber is used, a scrubbing liquid temperature monitoring device and a specific gravity monitoring device are required, each equipped with a continuous recorder.
    (3) Where a condenser is used, a condenser exit temperature (product side) monitoring device equipped with a continuous recorder is required.
    (4) Where a carbon adsorber is used, an integrating regeneration steam flow or nitrogen flow, or pressure monitoring device having an accuracy of +-10 percent of the flow rate, level, or pressure, or better, capable of recording the total regeneration steam flow or nitrogen flow, or pressure (gauge or absolute) for each regeneration cycle; and a carbon bed temperature monitoring device, capable of recording the carbon bed temperature after each regeneration and within 15 minutes of completing any cooling cycle are required.
    (5) Where an incinerator is used, a temperature monitoring device equipped with a continuous recorder is required.
    (i) Where an incinerator other than a catalytic incinerator is used, the temperature monitoring device shall be installed in the firebox or in the ductwork immediately downstream of the firebox in a position before any substantial heat exchange occurs.
    (ii) Where a catalytic incinerator is used, temperature monitoring devices shall be installed in the gas stream immediately before and after the catalyst bed.
    (6) Where a flare is used, a device (including but not limited to a thermocouple, ultra-violet beam sensor, or infrared sensor) capable of continuously detecting the presence of a pilot flame is required.
    (7) Where a boiler or process heater of less than 44 megawatts design heat input capacity is used, a temperature monitoring device in the firebox equipped with a continuous recorder is required. Any boiler or process heater in which all vent streams are introduced with the primary fuel or are used as the primary fuel is exempt from this requirement.
    (8) As an alternate to paragraphs (b)(1) through (7) of this section, the owner or operator may install an organic monitoring device equipped with a continuous recorder. Said organic monitoring device shall meet the requirements of Performance Specification 8 or 9 of 40 CFR part 60, appendix B, and shall be installed, calibrated, and maintained according to §63.6.
    (c) Alternative monitoring parameters. An owner or operator may request approval to monitor parameters other than those specified in Table 3 of this subpart. The request shall be submitted according to the procedures specified in §63.1417(j). Approval shall be requested if the owner or operator:
    (1) Uses a control device or control technology other than those included in paragraph (b) of this section; or
    (2) Uses one of the control devices included in paragraph (b) of this section, but seeks to monitor a parameter other than those specified in Table 3 of this subpart.
    (d) Monitoring of bypass lines. Owners or operators using a vent system that contains bypass lines that could divert emissions away from a control device or control technology used to comply with the provisions of this subpart shall comply with either paragraph (d)(1) or (2) of this section. Equipment such as low leg drains, high point bleeds, analyzer vents, open-ended valves or lines, and pressure relief valves needed for safety purposes are not subject to this paragraph.
    (1) Properly install, maintain, and operate a flow indicator that takes a reading at least once every 15 minutes. Records shall be generated as specified in §63.1416(d)(3). The flow indicator shall be installed at the entrance to any bypass line that could divert emissions away from the control device or control technology and to the atmosphere; or
    (2) Secure the bypass line damper or valve in the non-diverting position with a car-seal or a lock-and-key type configuration. A visual inspection of the seal or closure mechanism shall be performed at least once every month to ensure that the damper or valve is maintained in the non-diverting position and emissions are not diverted through the bypass line. Records shall be generated as specified in §63.1416(d)(3).
    (e) Monitoring for the alternative standards. For control devices that are used to comply with the provisions of §§63.1404(b), 63.1405(b)(c), 63.1406(b), 63.1407(b), or 63.1408(b) the owner or operator shall conduct continuous monitoring of the outlet organic HAP concentration whenever emissions are vented to the control device. Continuous monitoring of outlet organic HAP concentration shall be accomplished using an FTIR instrument following Method PS-15 of 40 CFR part 60, appendix B. The owner or operator shall calculate a daily average outlet organic HAP concentration.
§63.1416   Recordkeeping requirements.
    (a) Data retention. Unless otherwise specified in this subpart, each owner or operator of an affected source shall keep copies of all applicable records and reports required by this subpart for at least 5 years, as specified in paragraph (a)(1) of this section, with the exception listed in paragraph (a)(2) of this section.
    (1) All applicable records shall be maintained in such a manner that they can be readily accessed. The most recent 6 months of records shall be retained on site or shall be accessible from a central location by computer or other means that provides access within 2 hours after a request. The remaining 4 and one-half years of records may be retained offsite. Records may be maintained in hard copy or computer-readable form including, but not limited to, on paper, microfilm, computer, floppy disk, CD-ROM, optical disc, magnetic tape, or microfiche.
    (2) If an owner or operator submits copies of reports to the appropriate EPA Regional Office, the owner or operator is not required to maintain copies of reports. If the EPA Regional Office has waived the requirement of §63.10(a)(4)(ii) for submittal of copies of reports, the owner or operator is not required to maintain copies of those reports.
    (b) Malfunction records. Records shall be kept as specified in paragraphs (b)(1) through (3) of this section.
    (1) In the event that an affected unit fails to meet an applicable standard, record the number of failures. For each failure record the date, time, and duration of each failure.
    (2) For each failure to meet an applicable standard, record and retain a list of the affected sources or equipment, an estimate of the quantity of each regulated pollutant emitted over any emission limit, and a description of the method used to estimate the emissions.
    (3) Record actions taken to minimize emissions in accordance with §63.1420(h)(4), and any corrective actions taken to return the affected unit to its normal or usual manner of operation.
    (c) Monitoring records. Owners or operators required to comply with §63.1415 and, therefore, required to keep continuous records shall keep records as specified in paragraphs (c)(1) through (6) of this section.
    (1) The owner or operator shall record either each measured data value or average values for 1 hour or shorter periods calculated from all measured data values during each period. If values are measured more frequently than once per minute, a single value for each minute may be used to calculate the hourly (or shorter period) average instead of all measured values. Owners or operators of batch process vents shall record each measured data value; if values are measured more frequently than once per minute, a single value for each minute may be recorded instead of all measured values.
    (2) Daily average, batch cycle daily average, or block average values of each continuously monitored parameter shall be calculated for each operating day as specified in paragraphs (c)(2)(i) and (ii) of this section, except as specified in paragraphs (c)(3) and (4) of this section. The option of conducting parameter monitoring for batch process vents on a batch cycle daily average basis or a block average basis is described in paragraph (d)(2) of this section.
    (i) The daily average value, batch cycle daily average, or block average shall be calculated as the average of all parameter values recorded during the operating day, or batch cycle, as appropriate, except as specified in paragraph (c)(4) of this section. For batch process vents, only parameter values recorded during those batch emission episodes, or portions thereof, in the batch cycle that the owner or operator has selected to control in order to comply shall be used to calculate the average. The calculated average shall cover a 24-hour period if operation is continuous, or the number of hours of operation per operating day if operation is not continuous for daily average values or batch cycle daily average values. The calculated average shall cover the entire period of the batch cycle for block average values. As specified in §63.1413(a)(4)(i)(C)(3), the owner or operator shall provide the information needed to calculate batch cycle daily averages for operating days that include partial batch cycles.
    (ii) The operating day shall be the period the owner or operator specifies in the operating permit or the Notification of Compliance Status for purposes of determining daily average values or batch cycle daily average values of monitored parameters. The block shall be the entire period of the batch cycle, as specified by the owner or operator in the operating permit or the Notification of Compliance Status for purposes of determining block average values of monitored parameters.
    (3) If all recorded values for a monitored parameter during an operating day or block are above the minimum level or below the maximum level established in the Notification of Compliance Status or operating permit, the owner or operator may record that all values were above the minimum level or below the maximum level rather than calculating and recording a daily average, or block average, for that operating day. For these operating days or blocks, the records required in paragraph (c)(1) of this section shall also be retained for 5 years.
    (4) Monitoring data recorded during periods identified in paragraphs (c)(4)(i) and (ii) of this section shall not be included in any average computed under this subpart. Records shall be kept of the times and durations of all such periods and any other periods during process or control device or recovery device or control technology operation when monitors are not operating:
    (i) Monitoring system breakdowns, repairs, calibration checks, and zero (low-level) and high-level adjustments; and
    (ii) Periods of non-operation of the affected source (or portion thereof) resulting in cessation of the emissions to which the monitoring applies.
    (5) The owner or operator who has received approval to monitor different parameters, under §63.1417(j) as allowed under §63.1415(e), than those specified for storage vessels, continuous process vents, or batch process vents shall retain for a period of 5 years each record specified in their approved Alternative Monitoring Parameters request.
    (6) The owner or operator who has received approval to use alternative continuous monitoring and recordkeeping provisions as specified in §63.1417(k) shall retain for a period of 5 years each record specified in their approved Alternative Continuous Monitoring request.
    (d) Batch process vent records -- (1) Compliance demonstration records. Each owner or operator of a batch process vent complying with §63.1406 or §63.1407 shall keep the following records, as applicable, readily accessible.
    (i) If a batch process vent is seeking to demonstrate compliance with the alternative standard specified in §63.1406(b) or §63.1407(b), results of the initial compliance demonstration specified in §63.1413(f).
    (ii) If a batch process vent is seeking to demonstrate compliance with the percent reduction requirements of §63.1406(a)(1)(ii) or §63.1407(a)(2)(ii), records documenting the batch cycle percent reduction or overall percent reduction, as appropriate, as specified in §63.1413(e)(1)(iii).
    (iii) When using a flare to comply with §63.1406(a)(1)(i) or §63.1407(a)(2)(i):
    (A) The flare design (i.e., steam-assisted, air-assisted or non-assisted);
    (B) All visible emission readings, heat content determinations, flow rate measurements, and exit velocity determinations made during the compliance determination required by §63.1413(g); and
    (C) Periods when all pilot flames were absent during the compliance determination required by §63.1413(g).
    (iv) The following information when using a control device or control technology, other than a flare, to achieve compliance with the percent reduction requirement of §63.1406(a)(1)(ii) or §63.1407(a)(2)(ii):
    (A) For an incinerator, non-combustion control device, or other control technology, the percent reduction of organic HAP achieved for emissions vented to the control device or control technology, as determined using the procedures specified in §63.1413(e)(1);
    (B) For a boiler or process heater, a description of the location at which the vent stream is introduced into the boiler or process heater; and
    (C) For a boiler or process heater with a design heat input capacity of less than 44 megawatts and where the vent stream is not introduced with the primary fuel or used as the primary fuel, the percent reduction of organic HAP achieved for emissions vented to the control device, as determined using the procedures specified in §63.1413(e)(1).
    (v) If a batch process vent is seeking to demonstrate compliance with the mass emission limits specified in §63.1406(a)(1)(iii) or (a)(2)(iii) or specified in §63.1407(b)(2), the following information:
    (A) Results of the initial compliance demonstration specified in §63.1413(e)(2).
    (B) The organic HAP emissions from the batch process vent associated with each single type of batch cycle (Ecyclei) determined as specified in §63.1413(e)(2).
    (C) The site-specific emission limit required by §63.1413(e)(2), as appropriate.
    (vi) If an owner or operator designates a condenser sometimes operated as a process condenser as a control device, comply with either paragraph (d)(1)(vi)(A) or (B) of this section.
    (A) Retain information, data, analyses to document inprocess recycling of the material recovered when the condenser is operating as a control device.
    (B) When requested by the Administrator, demonstrate that material recovered by the condenser operating as a control device is reused in a manner meeting the definition of inprocess recycling.
    (2) Establishment of parameter monitoring level records. For each parameter monitored according to §63.1415(b) and Table 3 of this subpart, or for alternate parameters and/or parameters for alternate control devices or control technologies monitored according to §63.1417(j) as allowed under §63.1415(e), maintain documentation showing the establishment of the level that indicates proper operation of the control device or control technology as required by §63.1415(c) for parameters specified in §63.1415(b) and as required by §63.1417(j) for alternate parameters. An owner or operator may choose to monitor operating parameters for batch process vents on a batch cycle daily average basis or on a block average basis. The batch cycle daily average is based on parameter monitoring accomplished during the operating day (i.e., a 24-hour basis). The block average is based on the parameter monitoring accomplished during a single batch cycle. As defined in §63.1402, the block shall be the period of time equal to a single batch cycle. Monitored parameter documentation shall include the following:
    (i) Parameter monitoring data used to establish the level.
    (ii) Identification that the parameter monitoring level is associated with a batch cycle daily average or a block average.
    (iii) A definition of the batch cycle or block, as appropriate.
    (3) Controlled batch process vent continuous compliance records. Continuous compliance records shall be kept as follows:
    (i) Each owner or operator of a batch process vent that uses a control device or control technology to comply with the percent reduction requirements of §63.1406(a)(1)(ii) or §63.1407(a)(2)(ii) shall keep the following records, as applicable, readily accessible:
    (A) Continuous records of the equipment operating parameters specified to be monitored under §63.1415(b) as applicable, and listed in Table 3 of this subpart, or specified by the Administrator in accordance with §63.1417(f) as allowed under §63.1415(e). Said records shall be kept as specified under paragraph (c) of this section, except as follows:
    (1) For carbon adsorbers, the records specified in Table 3 of this subpart shall be maintained in place of continuous records.
    (2) For flares, the records specified in Table 4 of this subpart shall be maintained in place of continuous records.
    (B) Records of the batch cycle daily average value or block average value of each continuously monitored parameter, as specified in paragraph (c) of this section.
    (ii) Each owner or operator of a batch process vent that uses a control device or control technology to comply with §63.1406 or §63.1407 shall keep the following records, as applicable, readily accessible:
    (A) Hourly records of whether the flow indicator for bypass lines specified in §63.1415(d) was operating and whether a diversion was detected at any time during the hour. Also, records of the time and duration periods when the vent is diverted from the control device or control technology or the flow indicator specified in §63.1415(d) is not operating.
    (B) Where a seal or closure mechanism is used to comply with §63.1415(d), hourly records of whether a diversion was detected at any time are not required. The owner or operator shall record whether the monthly visual inspection of the seals or closure mechanisms has been done and shall record the occurrence of all periods when the seal mechanism is broken, the bypass line damper or valve position has changed, or the key for a lock-and-key type configuration has been checked out, and records of any car-seal that has broken.
    (C) Records specifying the times and duration of periods of monitoring system breakdowns, repairs, calibration checks, and zero (low-level) and high-level adjustments. In addition, records specifying any other periods of process or control device operation or control technology operation when monitors are not operating.
    (iii) Each owner or operator of a batch process vent seeking to demonstrate compliance with the alternative standard, as specified in §63.1406(b) or §63.1407(b), shall keep the records of continuous emissions monitoring described in §63.1416(c).
    (iv) Each owner or operator of a batch process vent seeking to demonstrate compliance with the mass emission limits, specified in §63.1406(a)(1)(iii) or (a)(2)(iii), shall keep the following records, as applicable, readily accessible.
    (A) The cumulative average monthly emission rate or the 12-month rolling average monthly emission rate, as appropriate.
    (B) If there is a deviation from the mass emission limit, as specified in §63.1413(i), the individual monthly emission rate data points making up the cumulative average monthly emission rate or the 12-month rolling average monthly emission rate, as appropriate.
    (C) If it becomes necessary to redetermine (Ecyclei) for a reactor batch process vent, as specified in §63.1413(e)(2), the new value(s) for (Ecyclei).
    (D) If an owner or operator is demonstrating compliance using the procedures in §63.1413(e)(2), the monthly value of the site-specific emission limit developed under §63.1413(e)(2).
    (e) Aggregate batch vent stream records -- (1) Compliance demonstration records. Each owner or operator of an aggregate batch vent stream complying with §63.1408(a)(1) or (2) shall keep the following records, as applicable, readily accessible:
    (i) If an aggregate batch vent stream is in compliance with the percent reduction requirements of §63.1408(a)(1)(ii) or (a)(2)(ii), owners or operators shall comply with the recordkeeping requirements for continuous process vents specified in 40 CFR part 63, subpart SS.
    (ii) If an aggregate batch vent stream is in compliance with the alternative standard specified in §63.1408(b), results of the initial compliance demonstration specified in §63.1413(f).
    (iii) When using a flare to comply with §63.1408(a)(1)(i) or (a)(2)(i):
    (A) The flare design (i.e., steam-assisted, air-assisted or non-assisted).
    (B) All visible emission readings, heat content determinations, flow rate measurements, and exit velocity determinations made during the compliance determination required by §63.1413(g).
    (C) Periods when all pilot flames were absent during the compliance determination required by §63.1413(g).
    (iv) If an aggregate batch vent stream is seeking to comply with the mass emission limits specified in §63.1408(b)(2), results of the initial compliance demonstration specified in §63.1413(e)(2). In addition, for each batch process vent, the emissions associated with each single type of batch cycle (Ecyclei), determined as specified in §63.1413(e)(2), shall be recorded.
    (2) Establishment of parameter monitoring level records. For each parameter monitored according to §63.1415(b) and Table 3 of this subpart, or for alternate parameters and/or parameters for alternate control devices monitored according to §63.1417(j) as allowed under §63.1415(e), maintain documentation showing the establishment of the level that indicates proper operation of the control device as required by §63.1415(c) for parameters specified in §63.1415(b) and as required by §63.1417(j) for alternate parameters. Monitored parameter documentation shall include the parameter monitoring data used to establish the level.
    (3) Controlled aggregate batch vent streams continuous compliance records. The following continuous compliance records shall be kept, as applicable:
    (i) Each owner or operator of an aggregate batch vent stream that uses a control device to comply with the percent reduction requirement of §63.1408(a)(1)(ii) or (a)(2)(ii) shall keep the following records, as applicable, readily accessible:
    (A) Continuous records of the equipment operating parameters specified to be monitored under §63.1415(b) as applicable, and listed in Table 3 of this subpart, or specified by the Administrator in accordance with §63.1417(j) as allowed under §63.1415(e). Records shall be kept as specified under paragraph (c) of this section, except as follows:
    (1) For carbon adsorbers, the records specified in Table 3 of this subpart shall be maintained in place of continuous records.
    (2) For flares, the records specified in Table 3 of this subpart shall be maintained in place of continuous records.
    (B) Records of the daily average value of each continuously monitored parameter, as specified in paragraph (c) of this section.
    (ii) Each owner or operator of an aggregate batch vent stream that uses a control device to comply with paragraph §63.1408(a)(1) or (2) of this section shall keep the following records, as applicable, readily accessible:
    (A) Hourly records of whether the flow indicator for bypass lines specified in §63.1415(d) was operating and whether a diversion was detected at any time during the hour. Also, records of the times and durations of periods when the vent is diverted from the control device or the flow indicator specified in §63.1415(d) is not operating.
    (B) Where a seal or closure mechanism is used to comply with §63.1415(d), hourly records of whether a diversion was detected at any time are not required. The owner or operator shall record whether the monthly visual inspection of the seals or closure mechanisms has been done, and shall record the occurrence of all periods when the seal mechanism is broken, the bypass line damper or valve position has changed, or the key for a lock-and-key type configuration has been checked out, and records of any car-seal that has broken.
    (C) Records specifying the times and duration of periods of monitoring system breakdowns, repairs, calibration checks, and zero (low-level) and high-level adjustments. In addition, records specifying any other periods of process or control device operation when monitors are not operating.
    (iii) Each owner or operator of an aggregate batch vent stream seeking to demonstrate compliance with the alternative standard, as specified in §63.1408(b), shall keep the records of continuous emissions monitoring described in §63.1416(c).
    (iv) Each owner or operator of an aggregate batch vent stream seeking to demonstrate compliance with the mass emission limits, specified in §63.1408(b)(2), shall keep the following records, as applicable, readily accessible:
    (A) The rolling average monthly emission rate or the 12-month rolling average monthly emission rate, as appropriate.
    (B) If there is a deviation from the emission limit, as specified in §63.1413(i)(1), the individual monthly emission rate data points making up the rolling average monthly emission rate or the 12-month rolling average monthly emission rate, as appropriate.
    (C) If it becomes necessary to redetermine (Ecyclei) for a reactor batch process vent, as specified in §63.1413(e)(2), the new value(s) for (Ecyclei).
    (f) Continuous process vent records -- (1) TRE index value records. Each owner or operator of a continuous process vent at a new affected source shall maintain records of measurements, engineering assessments, and calculations performed according to the procedures of §63.1412(j) to determine the TRE index value. Documentation of engineering assessments, described in §63.1412(k), shall include all data, assumptions, and procedures used for the engineering assessments.
    (2) Volumetric flow rate records. Each owner or operator of a continuous process vent shall record the volumetric flow rate as measured using the sampling site and volumetric flow rate determination procedures (if applicable) specified in §63.1412(b) and (f) or determined through engineering assessment as specified in §63.1412(k).
    (3) Organic HAP concentration records. Each owner or operator shall record the organic HAP concentration as measured using the sampling site and organic HAP concentration determination procedures (if applicable) specified in §63.1412(b)and (e), or determined through engineering assessment as specified in §63.1412(k).
    (4) Process change records. Each owner or operator of a continuous process vent shall keep up-to-date, readily accessible records of any process changes that change the control applicability for a continuous process vent. Records are to include any recalculation or measurement of the flow rate, organic HAP concentration, and TRE index value.
    (5) If a continuous process vent is seeking to demonstrate compliance with the mass emission limit specified in §63.1405(a)(3)(b)(2)(i), keep records specified in paragraphs (f)(5)(i) through and (iii) of this section.
    (i) The results of the initial compliance demonstration specified in §63.1413(h)(1)(i).
    (ii) Identification of the period of time that represents an operating day.
       (iii) The daily monthly organic HAP emissions from the continuous process vent determined as specified in §63.1413(h)(2)(3).
      (6) If a continuous process vent is seeking to demonstrate compliance with the emission rate limits specified in §63.1405(b)(2)(ii) or (iii) , keep records specified in paragraphs (f)(6)(i) through (iii) of this section.
      (i) The results of the initial compliance demonstration specified in §63.1413(h)(2)(i).
      (ii) Identification of the period of time that represents an operating day.
      (iii) The average hourly organic HAP emissions from the continuous process vent determined as specified in §63.1413(h)(4).
 	(67) When using a flare to comply with §63.1405(a)(1) or (b)(1), keep the records specified in paragraphs (f)(6)(i) through (f)(7)(iii) of this section.
    (i) The flare design (i.e., steam-assisted, air-assisted or non-assisted);
    (ii) All visible emission readings, heat content determinations, flow rate measurements, and exit velocity determinations made during the compliance determination required by §63.1413(g); and
    (iii) Periods when all pilot flames were absent during the compliance determination required by §63.1413(g).
    (g) Other records or documentation. (1) For continuous monitoring systems used to comply with this subpart, owners or operators shall keep records documenting the completion of calibration checks and records documenting the maintenance of continuous monitoring systems that are specified in the manufacturer's instructions or that are specified in other written procedures that provide adequate assurance that the equipment would reasonably be expected to monitor accurately.
    (2) The owner or operator of an affected source granted a waiver under §63.10(f) shall maintain any information demonstrating whether an affected source is meeting the requirements for a waiver of recordkeeping or reporting requirements.
    (3) Owners or operators using the exemption from the equipment leak provisions provided by §63.1400(f) shall comply with either paragraph (g)(3)(i) or (ii) of this section.
    (i) The owner or operator shall retain information, data, and analysis used to document the basis for using the exemption provided by §63.1400(f). Such information, data, and analysis shall be retained for the 12-month period preceding December 14, 1998 and for each 12-month period the affected source is in operation and using the exemption provided by §63.1400(f). The beginning of each 12-month period shall be the anniversary of December 14, 1998.
    (ii) When requested by the Administrator, the owner or operator shall demonstrate that actual annual production is equal to or less than 800 megagrams per year of amino/phenolic resin for the 12-month period preceding December 14, 1998, and for each 12-month period the affected source has been in operation and using the exemption provided by §63.1400(f). The beginning of each 12-month period shall be the anniversary of December 14, 1998.
    (4) The owner or operator of a heat exchange system located at an affected source shall retain the following records:
    (i) Monitoring data required by §63.1409 indicating a leak and the date when the leak was detected, and if demonstrated not to be a leak, the basis for that determination.
    (ii) Records of any leaks detected by procedures subject to §63.1409(c)(2) and the date the leak was detected.
    (iii) The dates of efforts to repair leaks.
    (iv) The method or procedure used to confirm repair of a leak and the date repair was confirmed.
    (5) For pressure relief devices in organic HAP service, keep records of the information specified in paragraphs (g)(5)(i) through (v) of this section, as applicable.
    (i) A list of identification numbers for pressure relief devices that vent to a fuel gas system, process, drain system, or closed-vent system and control device, under the provisions in §63.1411(d).
    (ii) A list of identification numbers for pressure relief devices subject to the provisions in §63.1411(a).
    (iii) A list of identification numbers for pressure relief devices equipped with rupture disks, under the provisions in §63.1411(b)(2).
    (iv) The dates and results of the monitoring following a pressure release for each pressure relief device subject to the provisions in §63.1411(a) and (b). The results shall include:
    (A) The background level measured during each compliance test.
    (B) The maximum instrument reading measured at each piece of equipment during each compliance test.
    (v) For pressure relief devices in organic HAP service subject to §63.1411(c), keep records of each pressure release to the atmosphere, including the following information:
    (A) The source, nature, and cause of the pressure release.
    (B) The date, time, and duration of the pressure release.
    (C) An estimate of the quantity of total HAP emitted during the pressure release and the calculations used for determining this quantity.
    (D) The actions taken to prevent this pressure release.
    (E) The measures adopted to prevent future such pressure releases.
     (h) Reduced recordkeeping program. For any parameter with respect to any item of equipment, the owner or operator may implement the recordkeeping requirements specified in paragraph (h)(1) or (2) of this section as alternatives to the provisions specified in this subpart for storage vessels, continuous process vents, batch process vents, or aggregate batch vent streams. The owner or operator shall retain for a period of 5 years each record required by paragraph (h)(1) or (2) of this section.
    (1) The owner or operator may retain only the daily average, batch cycle daily average, or block average value, and is not required to retain more frequent values, for a parameter with respect to an item of equipment, if the requirements of paragraphs (h)(1)(i) through (vi) of this section are met. An owner or operator electing to comply with the requirements of paragraph (h)(1) of this section shall notify the Administrator in the Notification of Compliance Status Report required under §63.1417(e) or, if the Notification of Compliance Status has already been submitted, in the Periodic Report immediately preceding implementation of the requirements of this paragraph as specified in §63.1417(f)(10).
    (i) The monitoring system is capable of detecting unrealistic or impossible data during periods of operation (e.g., a temperature reading of −200 °C on a boiler) and will alert the operator by alarm or other means. The owner or operator shall record the occurrence. All instances of the alarm or other alert in an operating day or block constitute a single occurrence.
    (ii) The monitoring system generates, updated at least hourly throughout each operating day, a running average of the parameter values that have been obtained during that operating day or block, and the capability to observe this running average is readily available on-site to the Administrator during the operating day. The owner or operator shall record the occurrence of any period meeting the criteria in paragraphs (h)(1)(ii)(A) and (B) of this section. All instances in an operating day or block constitute a single occurrence:
    (A) The running average is above the maximum or below the minimum established limits; and
    (B) The running average is based on at least six 1-hour average values.
    (iii) The monitoring system is capable of detecting unchanging data during periods of operation, except in circumstances where the presence of unchanging data is the expected operating condition based on past experience (e.g., pH in some scrubbers) and will alert the operator by alarm or other means. The owner or operator shall record the occurrence. All instances of the alarm or other alert in an operating day or block constitute a single occurrence.
    (iv) The monitoring system will alert the owner or operator by an alarm or other means if the running average parameter value calculated under paragraph (h)(1)(ii) of this section reaches a set point that is appropriately related to the established limit for the parameter that is being monitored.
    (v) The owner or operator shall verify the proper functioning of the monitoring system, including its ability to comply with the requirements of paragraphs (h)(1)(i) through (iv) of this section, at the times specified in paragraphs (h)(1)(v)(A) through (C). The owner or operator shall document that the required verifications occurred.
    (A) Upon initial installation.
    (B) Annually after initial installation.
    (C) After any change to the programming or equipment constituting the monitoring system which might reasonably be expected to alter the monitoring system's ability to comply with the requirements of this section.
    (vi) The owner or operator shall retain the records identified in paragraphs (h)(1)(vi)(A) through (D) of this section.
    (A) Identification of each parameter for each item of equipment for which the owner or operator has elected to comply with the requirements of paragraph (h)(1) of this section.
    (B) A description of the applicable monitoring system(s) and how compliance will be achieved with each requirement of paragraphs (h)(1)(i) through (v) of this section. The description shall identify the location and format (e.g., on-line storage, log entries) for each required record. If the description changes, the owner or operator shall retain, as provided in paragraph (a) of this section, except as provided in paragraph (h)(1)(vi)(D) of this section, both the current and the most recent superseded description.
    (C) A description and the date of any change to the monitoring system that would reasonably be expected to impair its ability to comply with the requirements of paragraph (h) of this section.
    (D) Owners and operators subject to paragraph (h)(1)(vi)(B) of this section shall retain the current description of the monitoring system as long as the description is current. The current description shall, at all times, be retained on-site or be accessible from a central location by computer or other means that provides access within 2 hours after a request. The owner or operator shall retain all superseded descriptions for at least 5 years after the date of their creation. Superseded descriptions shall be retained on-site (or accessible from a central location by computer or other means that provides access within 2 hours after a request) for at least 6 months after their creation. Thereafter, superseded descriptions may be stored off-site.
    (2) If an owner or operator has elected to implement the requirements of paragraph (h)(1) of this section for a parameter with respect to an item of equipment and a period of 6 consecutive months has passed without any deviation as defined in paragraph (h)(2)(iv) of this section, the owner or operator is no longer required to record the daily average, batch cycle daily average, or block average value for any operating day when the daily average, batch cycle daily average, or block average value is less than the maximum or greater than the minimum established limit. With approval by the Administrator, monitoring data generated prior to the compliance date of this subpart shall be credited toward the period of 6 consecutive months if the parameter limit and the monitoring accomplished during the period prior to the compliance date were required and/or approved by the Administrator.
    (i) If the owner or operator elects not to retain the daily average, batch cycle daily average, or block average values, the owner or operator shall notify the Administrator in the next Periodic Report as specified in §63.1417(f)(11). The notification shall identify the parameter and unit of equipment.
    (ii) If, on any operating day or during any block after the owner or operator has ceased recording the daily average, batch cycle daily average, or block average values as provided in paragraph (h)(2) of this section, there is a deviation as defined in paragraph (h)(2)(iv) of this section, the owner or operator shall immediately resume retaining the daily average, batch cycle daily average, or block average value for each operating day and shall notify the Administrator in the next Periodic Report. The owner or operator shall continue to retain each daily average, batch cycle daily average, or block average value until another period of 6 consecutive months has passed without a deviation as defined in paragraph (h)(2)(iv) of this section.
    (iii) The owner or operator shall retain the records specified in paragraphs (h)(1)(i) through (iv) of this section for the duration specified in paragraph (h) of this section. For any calendar week, if compliance with paragraphs (h)(1)(i) through (iv) of this section does not result in retention of a record of at least one occurrence or measured parameter value, the owner or operator shall record and retain at least one value during a period of operation.
    (iv) For purposes of paragraph (h)(2) of this section, a deviation means that the daily average, batch cycle daily average, or block average value of monitoring data for a parameter is greater than the maximum, or less than the minimum established value.
§63.1417   Reporting requirements.
    (a) Reporting and notification. In addition to the reports and notifications required by subpart A of this part as specified in Table 1 of this subpart, the owner or operator of an affected source shall prepare and submit the reports listed in paragraphs (d) through (i) of this section as applicable. All reports required by this subpart and the schedule for their submittal are listed in Table 5 of this subpart.
    (b) General. Owners and operators are required to meet the reporting requirements of this subpart unless they can demonstrate that failure to submit information required to be included in a specified report was due to the circumstances described in paragraphs (b)(1) through (3) of this section. Examples of circumstances where this paragraph may apply include information related to newly-added equipment or emission points, changes in the process, changes in equipment required or utilized for compliance with the requirements of this subpart, or changes in methods or equipment for monitoring, recordkeeping, or reporting.
    (1) The information was not known in time for inclusion in the report specified by this subpart.
    (2) The owner or operator has been diligent in obtaining the information.
    (3) The owner or operator submits a report according to the provisions of paragraphs (b)(3)(i) through (iii) of this section, as appropriate.
    (i) If this subpart expressly provides for supplements to the report in which the information is required, the owner or operator shall submit the information as a supplement to that report. The information shall be submitted no later than 60 days after it is obtained, unless otherwise specified in this subpart.
    (ii) If this subpart does not expressly provide for supplements, but the owner or operator must submit a request for revision of an operating permit pursuant to 40 CFR part 70 or part 71 due to circumstances to which the information pertains, the owner or operator shall submit the information with the request for revision to the operating permit.
    (iii) In any case not addressed by paragraph (b)(3)(i) or paragraph (b)(3)(ii) of this section, the owner or operator shall submit the information with the first Periodic Report, as required by this subpart, which has a submission deadline at least 60 days after the information is obtained.
    (c) Submittals. All reports required under this subpart shall be sent to the Administrator at the appropriate address listed in §63.13. If acceptable to both the Administrator and the owner or operator of an affected source, reports may be submitted on electronic media.
    (d) Precompliance Report. Owners or operators of affected sources requesting an extension for compliance; requesting approval to use alternative monitoring parameters, alternative continuous monitoring and recordkeeping, or alternative controls; requesting approval to use engineering assessment to estimate organic HAP emissions from a batch emissions episode as described in §63.1414(d)(6)(i)(C); wishing to establish parameter monitoring levels according to the procedures contained in §63.1413(a)(4)(ii); establishing parameter monitoring levels based on a design evaluation as specified in §63.1413(a)(3); or following the procedures in §63.1413(e)(2); or following the procedures in §63.1413(h)(2)(3), shall submit a Precompliance Report according to the schedule described in paragraph (d)(1) of this section. The Precompliance Report shall contain the information specified in paragraphs (d)(2) through (11) of this section, as appropriate.
    (1) The Precompliance Report shall be submitted to the Administrator no later than 12 months prior to the compliance date. Unless the Administrator objects to a request submitted in the Precompliance Report within 45 days after its receipt, the request shall be deemed approved. For new affected sources, the Precompliance Report shall be submitted to the Administrator with the application for approval of construction or reconstruction required by §63.5(d), as specified on Table 1 of this subpart. Supplements to the Precompliance Report may be submitted as specified in paragraph (d)(11) of this section.
    (2) A request for an extension for compliance, as specified in §63.1401(d), may be submitted in the Precompliance Report. The request for a compliance extension will include the data outlined in §63.6(i)(6)(i)(A), (B), and (D), as required in §63.1401(d)(1).
    (3) The alternative monitoring parameter information required in paragraph (j) of this section shall be submitted in the Precompliance Report if, for any emission point, the owner or operator of an affected source seeks to comply through the use of a control technique other than those for which monitoring parameters are specified in this subpart or seeks to comply by monitoring a different parameter than those specified in this subpart.
    (4) If the affected source seeks to comply using alternative continuous monitoring and recordkeeping as specified in paragraph (k) of this section, the owner or operator shall submit the information requested in paragraph (d)(4)(i) or (ii) of this section in the Precompliance Report:
    (i) The owner or operator shall submit notification of the intent to use the provisions specified in paragraph (k) of this section; or
    (ii) The owner or operator shall submit a request for approval to use alternative continuous monitoring and recordkeeping provisions as specified in paragraph (k) of this section.
    (5) The owner or operator shall report the intent to use alternative controls to comply with the provisions of this subpart in the Precompliance Report. The Administrator may deem the alternative controls to be equivalent to the controls required by the standard under the procedures outlined in §63.6(g).
    (6) If a request for approval to use engineering assessment to estimate organic HAP emissions from a batch emissions episode, as specified in §63.1414(d)(6)(i)(C), is being made, the information required by §63.1414(d)(6)(iii)(B) shall be submitted in the Precompliance Report.
    (7) If an owner or operator elects to establish parameter monitoring levels according to the procedures contained in §63.1413(a)(4)(ii), or will be establishing parameter monitoring levels based on a design evaluation as specified in §63.1413(a)(3), the following information shall be submitted in the Precompliance Report:
    (i) Identification of which procedures (i.e., §63.1413(a)(1)(i) or (ii)) are to be used; and
    (ii) A description of how the parameter monitoring level is to be established. If the procedures in §63.1413(a)(4)(ii) are to be used, a description of how performance test data will be used shall be included.
    (8) If an owner or operator is complying with the mass emission limit specified in §63.1405(a)(3)(b)(2)(i), the sample of production records specified in §63.1413(h)(2)(3) shall be submitted in the Precompliance Report.
    (9) If an owner or operator is complying with the mass emission limit specified in §63.1406(a)(1)(iii) or (a)(2)(iii), §63.1407(b)(2), or §63.1408(b)(2), the sample of production records specified in §63.1413(e)(2) shall be submitted in the Precompliance Report.
    (10) The procedure for a control device controlling less than 1 ton per year of uncontrolled organic HAP emissions shall be submitted, as specified in §63.1415(a)(2). Such a procedure shall meet the requirements specified in §63.1415(a)(2).
    (11) Supplements to the Precompliance Report may be submitted as specified in paragraph (d)(11)(i) or (ii) of this section. Unless the Administrator objects to a request submitted in a supplement to the Precompliance Report within 45 days after its receipt, the request shall be deemed approved.
    (i) Supplements to the Precompliance Report may be submitted to clarify or modify information previously submitted.
    (ii) Supplements to the Precompliance Report may be submitted to request approval to use alternative monitoring parameters, as specified in paragraph (j) of this section; to use alternative continuous monitoring and recordkeeping, as specified in paragraph (k) of this section; to use alternative controls, as specified in paragraph (d)(5) of this section; to use engineering assessment to estimate organic HAP emissions from a batch emissions episode, as specified in paragraph (d)(6) of this section; or to establish parameter monitoring levels according to the procedures contained in §63.1413(a)(4)(ii) or (a)(3), as specified in paragraph (d)(7) of this section.
    (e) Notification of Compliance Status. For existing and new affected sources, a Notification of Compliance Status shall be submitted within 150 days after the compliance dates specified in §63.1401. For equipment leaks, the Notification of Compliance Status shall contain the information specified in 40 CFR part 63, subpart UU. For storage vessels, continuous process vents, batch process vents, and aggregate batch vent streams, the Notification of Compliance Status shall contain the information listed in paragraphs (e)(1) through (9) of this section. For pressure relief devices subject to the requirements of §63.1411(c), the owner or operator shall also submit the information listed in paragraph (e)(10) of this section in a supplement to the Notification of Compliance Status within 150 days after the first applicable compliance date for pressure relief device monitoring.
    (1) The results of any emission point applicability determinations, performance tests, design evaluations, inspections, continuous monitoring system performance evaluations, any other information used to demonstrate compliance, and any other information, as appropriate, required to be included in the Notification of Compliance Status under 40 CFR part 63, subpart WW SS and subpart SS WW, as referred to in §63.1404 for storage vessels; under 40 CFR part 63, subpart SS, as referred to in §63.1405 for continuous process vents; under §63.1416(f)(1) through (3), (5)(i) and (ii), and (6)(i) and (ii) for continuous process vents; under §63.1416(d)(1) for batch process vents; and under §63.1416(e)(1) for aggregate batch vent streams. In addition, each owner or operator shall comply with paragraphs (e)(1)(i) and (ii) of this section.
    (i) For performance tests, applicability determinations, and estimates of organic HAP emissions that are based on measurements, the Notification of Compliance Status shall include one complete test report, as described in paragraph (e)(1)(ii) of this section, for each test method used for a particular kind of emission point. For additional tests performed for the same kind of emission point using the same method, the results and any other required information shall be submitted, but a complete test report is not required.
    (ii) A complete test report shall include a brief process description, sampling site description, description of sampling and analysis procedures and any modifications to standard procedures, quality assurance procedures, record of operating conditions during the test, record of preparation of standards, record of calibrations, raw data sheets for field sampling, raw data sheets for field and laboratory analyses, documentation of calculations, and any other information required by the test method.
    (2) For each monitored parameter for which a maximum or minimum level is required to be established, the Notification of Compliance Status shall contain the information specified in paragraphs (e)(2)(i) through (iv) of this section, unless this information has been established and provided in the operating permit.
    (i) The required information shall include the specific maximum or minimum level of the monitored parameter(s) for each emission point.
    (ii) The required information shall include the rationale for the specific maximum or minimum level for each parameter for each emission point, including any data and calculations used to develop the level and a description of why the level indicates proper operation of the control device or control technology.
    (iii) The required information shall include a definition of the affected source's operating day, as specified in §63.1416(c)(2)(ii), for purposes of determining daily average values or batch cycle daily average values of monitored parameters. The required information shall include a definition of the affected source's block(s), as specified in §63.1416(c)(2)(ii), for purposes of determining block average values of monitored parameters.
    (iv) For batch process vents, the required information shall include a definition of each batch cycle that requires the control of one or more batch emission episodes during the cycle, as specified in §§63.1413(e)(1)(iii) and 63.1416(c)(2)(ii).
    (3) When the determination of applicability for process units, as made following the procedures in §63.1400(g), indicates that a process unit is an APPU, an identification of the APPU and a statement indicating that the APPU is an APPU that produces more than one intended product at the same time, as specified in §63.1400(g)(1), or is a flexible operations process unit as specified in §63.1400(g)(2) through (4).
    (4) [Reserved]
    (5) The results for each predominant use determination for storage vessels belonging to an affected source subject to this subpart that is made under §63.1400(h)(6).
    (6) Notification that the owner or operator has elected to comply with §63.1416(h), Reduced Recordkeeping Program.
    (7) Notification that an affected source is exempt from the equipment leak provisions of §63.1410 according to the provisions of §63.1400(f), and the affected source's actual annual production of amino/phenolic resins for the 12-month period preceding December 14, 1998.
    (8) An owner or operator with a combustion device, recovery device, or recapture device affected by the situation described in §63.1400(i)(5) shall identify which rule shall be complied with for monitoring, recordkeeping, and reporting requirements, as allowed under §63.1400(i)(5).
    (9) Data or other information used to demonstrate that an owner or operator may use engineering assessment to estimate emissions for a batch emission episode, as specified in §63.1413(d)(6)(iii)(A).
    (10) For pressure relief devices in organic HAP service, a description of the device or monitoring system to be implemented, including the pressure relief devices and process parameters to be monitored (if applicable), and a description of the alarms or other methods by which operators will be notified of a pressure release.
    (f) Periodic Reports. Except as specified in paragraph (f)(12) of this section, a report containing the information in paragraph (f)(2) of this section or containing the information in paragraphs (f)(3) through (11) and (13) through (15) of this section, as appropriate, shall be submitted semiannually no later than 60 days after the end of each 180 day period. In addition, for equipment leaks subject to §63.1410, the owner or operator shall submit the information specified in 40 CFR part 63, subpart UU, and for heat exchange systems subject to §63.1409, the owner or operator shall submit the information specified in §63.1409. Section 63.1415 shall govern the use of monitoring data to determine compliance for emissions points required to apply controls by the provisions of this subpart.
    (1) Except as specified in paragraph (f)(12) of this section, a report containing the information in paragraph (f)(2) of this section or containing the information in paragraphs (f)(3) through (11) and (13) through (15) of this section, as appropriate, shall be submitted semiannually no later than 60 days after the end of each 180 day period. The first report shall be submitted no later than 240 days after the date the Notification of Compliance Status is due and shall cover the 6-month period beginning on the date the Notification of Compliance Status is due. Subsequent reports shall cover each preceding 6-month period.
    (2) If none of the compliance exceptions specified in paragraphs (f)(3) through (11) and (13) through (15) of this section occurred during the 6-month period, the Periodic Report required by paragraph (f)(1) of this section shall be a statement that the affected source was in compliance for the preceding 6-month period and no activities specified in paragraphs (f)(3) through (11) and (13) through (15) of this section occurred during the preceding 6-month period.
    (3) For an owner or operator of an affected source complying with the provisions of §§63.1404 through 63.1409 for any emission point, Periodic Reports shall include:
    (i) All information specified in 40 CFR part 63, subpart WW and subpart SS for storage vessels; 40 CFR part 63, subpart SS for continuous process vents required to comply with subpart SS; §63.1416(d)(3)(ii) for batch process vents; and §63.1416(e) for aggregate batch vent stream.
    (ii) The daily average values, batch cycle daily average values, or block average values of monitored parameters for deviations, as specified in §63.1413(i), of operating parameters. In addition, the periods and duration of periods when monitoring data were not collected shall be specified.
    (4) Notification if one or more emission point(s) or one or more APPU is added to an affected source. The owner or operator shall submit the following information:
    (i) A description of the addition to the affected source;
    (ii) Notification of applicability status (i.e., does the emission point require control) of the additional emission point, if appropriate, or notification of all emission points in the added APPU.
    (5) If there is a deviation from the mass emission limit specified in §63.1405(a)(3), §63.1406(a)(1)(iii) or (a)(2)(iii), §63.1407(b)(2), or §63.1408(b)(2), the following information, as appropriate, shall be included:
    (i) The cumulative average monthly emission rate or the 12-month rolling average monthly emission rate, as appropriate.
    (ii) The individual monthly emission rate data points making up the cumulative average monthly emission rate or the 12-month rolling average monthly emission rate, as appropriate.
    (iii) If an owner or operator is demonstrating compliance using the procedures in §63.1413(e)(2)(ii), the monthly value of the site-specific emission limit.
    (6) If any performance tests are reported in a Periodic Report, the following information shall be included:
    (i) One complete test report shall be submitted for each test method used for a particular kind of emission point tested. A complete test report shall contain the information specified in paragraph (e)(1)(ii) of this section.
    (ii) For additional tests performed for the same kind of emission point using the same method, results and any other information required shall be submitted, but a complete test report is not required.
    (7) The Periodic Report shall include the results for each change made to a primary product determination for amino/phenolic resins made under §63.1400(g).
    (8) The Periodic Report shall include the results for each change made to a predominant use determination for a storage vessel belonging to an affected source subject to this subpart that is made under §63.1400(h)(6).
    (9) If an owner or operator invokes the delay of repair provisions for a heat exchange system, the following information shall be submitted, as appropriate. If the leak remains unrepaired, the information shall also be submitted in each subsequent periodic report until repair of the leak is reported.
    (i) The presence of the leak and the date that the leak was detected.
    (ii) Whether or not the leak has been repaired. If the leak is repaired, the date the leak was successfully repaired. If the leak remains unrepaired, the expected date of repair.
    (iii) The reason(s) for delay of repair. If delay of repair is invoked due to the reasons described in §63.1409(e)(2), documentation of emissions estimates shall be included.
    (10) Notification that the owner or operator has elected to comply with §63.1416(h), Reduced Recordkeeping Program.
    (11) Notification that the owner or operator has elected to not retain the daily average, batch cycle daily average, or block average values, as appropriate, as specified in §63.1416(h)(2)(i).
    (12) The owner or operator of an affected source shall submit quarterly reports for particular emission points as specified in paragraphs (f)(12)(i) through (iv) of this section.
    (i) The owner or operator of an affected source shall submit quarterly reports for a period of 1 year for an emission point if the Administrator requests the owner or operator to submit quarterly reports for the emission point.
    (ii) The quarterly reports shall include all information specified in paragraphs (f)(3) through (11) and (13) through (15) of this section applicable to the emission point for which quarterly reporting is required under paragraph (f)(12)(i) of this section. Information applicable to other emission points within the affected source shall be submitted in the semiannual reports required under paragraph (f)(1) of this section.
    (iii) Quarterly reports shall be submitted no later than 60 days after the end of each quarter.
    (iv) After quarterly reports have been submitted for an emission point for 1 year, the owner or operator may return to semiannual reporting for the emission point unless the Administrator requests the owner or operator to continue to submit quarterly reports.
    (13) For pressure relief devices, Periodic Reports must include the information specified in paragraphs (f)(13)(i) through (iii) of this section.
    (i) For pressure relief devices in organic HAP service subject to §63.1411, report confirmation that all monitoring to show compliance was conducted within the reporting period.
    (ii) For pressure relief devices in organic HAP gas or vapor service subject to §63.1411(b), report any instrument reading of 500 ppm above background or greater, more than 5 days after the relief device returns to organic HAP gas or vapor service after a pressure release.
    (iii) For pressure relief devices in organic HAP service subject to §63.1411(c), report each pressure release to the atmosphere, including the following information:
    (A) The source, nature, and cause of the pressure release.
    (B) The date, time, and duration of the pressure release.
    (C) An estimate of the quantity of total HAP emitted during the pressure release and the method used for determining this quantity.
    (D) The actions taken to prevent this pressure release.
    (E) The measures adopted to prevent future such pressure releases.
     (14) If there is a deviation from the mass emission limit specified in §63.1405(b)(2)(i) , the report shall include the daily average emission rate calculated for each operating day for which a deviation occurred.
    (15) If there is a deviation from the mass emission limit specified in §63.1405(b)(2)(ii) or (iii), the report shall include the daily average emission rate calculated for each operating day for which a deviation occurred.
    (g) Reports of Malfunctions. If a source fails to meet an applicable standard, report such events in the Periodic Report. Report the number of failures to meet an applicable standard. For each instance, report the date, time and duration of each failure. For each failure the report must include a list of the affected sources or equipment, an estimate of the quantity of each regulated pollutant emitted over any emission limit, and a description of the method used to estimate the emissions.
    (h) Other reports. Other reports shall be submitted as specified in paragraphs (h)(1) through (8) of this section.
    (1) For storage vessels, the notifications of inspections required by 40 CFR part 63, subpart WW shall be submitted.
    (2) A site-specific test plan shall be submitted no later than 90 days before the planned date for a performance test. Unless the Administrator requests changes to the site-specific test plan within 45 days after its receipt, the site-specific test plan shall be deemed approved. The test plan shall include a description of the planned test and rationale for why the planned performance test will provide adequate and representative results for demonstrating the performance of the control device. If required by §63.1413(e)(1) or §63.1414(d)(5), the test plan shall include an emission profile and rationale for why the selected test period is representative.
    (3) The owner or operator shall notify the Administrator of the intention to conduct a performance test at least 30 days before the performance test is scheduled in order to allow the Administrator the opportunity to have an observer present during the test. If after 30 days notice for an initially scheduled performance test, there is delay (due to operational problems, etc.) in conducting the scheduled performance test, the owner or operator of an affected source shall notify the Administrator as soon as possible of any delay in the original test date, either by providing at least 7 days prior notice of the rescheduled date of the performance test, or by arranging a rescheduled date with the Administrator by mutual agreement.
    (4) When the conditions of §63.1400(g)(7) or the conditions of §63.1400(g)(8) are met, notification of changes to the primary product for an APPU or process unit shall be submitted. When a notification is made in response to a change in the primary product under §63.1400(g)(7), rationale for why it is anticipated that no amino/phenolic resins will be produced in the process unit in the future shall be included.
    (5) Owners or operators of APPU or emission points (other than equipment leak components subject to §63.1410) that are added to the affected source under the provisions of §63.1400(d)(2) or (3) or under the provisions of §63.5(b)(6) shall submit reports as specified in paragraphs (h)(5)(i) through (ii) of this section.
    (i) Reports shall include:
    (A) A description of the process change or addition, as appropriate;
    (B) The planned start-up date and the appropriate compliance date; and
    (C) Identification of the emission points (except equipment leak components subject to §63.1410) specified in paragraphs (h)(5)(i)(C)(1) through (3) of this section, as applicable.
    (1) All the emission points in an added APPU.
    (2) All the emission points in an affected source that becomes a new affected source.
    (3) All the added or created emission points resulting from a process change.
    (ii) If the owner or operator wishes to request approval to use alternative monitoring parameters, alternative continuous monitoring or recordkeeping, alternative controls, engineering assessment to estimate organic HAP emissions from a batch emissions episode, or wishes to establish parameter monitoring levels according to the procedures contained in §63.1413(a)(1)(ii) or (ii), a Precompliance Report shall be submitted no later than 180 days prior to the appropriate compliance date.
    (6) The information specified in paragraphs (h)(6)(i) and (ii) of this section shall be submitted when a small control device becomes a large control device, as specified in §63.1413(a)(1)(ii).