(Subpart CCCC

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Subpart CCCC — Standards of Performance for Commercial and Industrial Solid Waste Incineration Units
Contents Introduction § 60.2000 What does this subpart do? § 60.2005 When does this subpart become effective? Applicability § 60.2010 Does this subpart apply to my incineration unit? § 60.2015 What is a new incineration unit? § 60.2020 What combustion units are exempt from this subpart? § 60.2030 Who implements and enforces this subpart? § 60.2035 How are these new source performance standards structured? § 60.2040 Do all eleven components of these new source performance standards apply at the same time? Preconstruction Siting Analysis § 60.2045 Who must prepare a siting analysis? § 60.2050 What is a siting analysis? Waste Management Plan § 60.2055 What is a waste management plan? § 60.2060 When must I submit my waste management plan? § 60.2065 What should I include in my waste management plan? Operator Training and Qualification § 60.2070 What are the operator training and qualification requirements? § 60.2 075 When must the operator training course be completed? § 60.2080 How do I obtain my operator qualification? § 60.2085 How do I maintain my operator qualification? § 60.2090 How do I renew my lapsed operator qualification? § 60.2095 What site

- specific documentation is required? § 60.2100 What if all the qualified operators are temporarily not accessible?(Subpart CCCC

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- 2013) Page 2 of 163 Emission Limitations and Operating Limits § 60.2105 What emission limitations must I meet and by when? § 60.2110 What operating limits must I meet and by when? § 60.2115 What if I do not use a wet scrubber, fabric filter, activated carbon injection, selective noncatalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations? § 60.2120 Affirmative defense for violation of emission standards during malfunction. Performance Testing § 60.2125 How do I conduct the initial and annual performa nce test? § 60.2130 How are the performance test data used? Initial Compliance Requirements § 60.2135 How do I demonstrate initial compliance with the emission l imitations and establish the operating limits? § 60.2140 By what date must I conduct the initial performance test? § 60.2141 By what date must I conduct the initial air pollution control device inspection? Continuous Compliance Requirements § 60.2145 How do I demonstrate continuous compliance with the emission limitations and the operating limits? § 60. 2150 By what date must I conduct the annual performance test? § 60.2151 By what date must I conduct the annual air pollution control device inspection? § 60.2155 May I conduct performance testing less often? § 60.2160 May I conduct a repeat performance test to establish new operating limits? Monitoring § 60.2165 What monitoring equipment must I in stall and what parameters must I monitor? § 60.2170 Is there a minimum amount of monitoring data I must obtain? Recordkeeping and Reporting § 60.2175 What record s must I keep? § 60.2180 Where and in what format must I keep my records? § 60.2185 What reports must I submit?(Subpart CCCC

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- 2013) Page 3 of 163 § 60.2190 What must I submit prior to commencing construction? § 60.2195 What information must I submit prior to initial startup? § 60.2200 What information must I submit following my initial performance test? § 60.2205 When must I submit my annual report? § 60.2210 What information must I include in my annual report? § 60.2215 What else must I report if I have a deviation from the operating limits or t he emission limitations? § 60.2220 What must I include in the deviation report? § 60.2225 What else must I report if I have a deviation from the requirement to have a qualified operator accessib le? § 60.2230 Are there any other notifications or reports that I must submit? § 60.2235 In what form can I submit my reports? § 60.2240 Can reporting dates be cha nged? Title V Operating Permits § 60.2242 Am I required to apply for and obtain a Title V operating permit for my unit? Air Curtain Incinerators § 60.2245 What is an air curtain incinerator? § 60.2250 What are the emission limitations for air curtain incinerators? § 60.2255 How must I monitor opacity for air curtain inc inerators? § 60.2260 What are the recordkeeping and reporting requirements for air curtain incinerators? Definitions § 60.2265 What definitions must I know? Table 1 to Subpart CCCC of Part 60

— Emission Limitations for CISWI Units for Which Construction is Commenced After November 30, 1999, But no Later Than June 4, 2010, or for Which Modification or Reconstruction is Commenced on or After June 1, 2001, But no Later Than August 7, 2013 Table 2 to Subpart CCCC of Part 60

— Operating Limits for Wet Scrubbers Table 3 to Subpart CCCC of Part 60

— Toxic Equivalency Factors(Subpart CCCC

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- 2013) Page 4 of 163 Table 4 to Subpart CCCC of Part 60

— Summary of Reporting Requirements a Table 5 to Subpart CCCC of Part 60

— Emission Limitations for Incinerators That Commenced Construction After June 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013 Table 6 to Subpart CCCC of Part 60

— Emission Limitations fo r Energy Recovery Units That Commenced Construction After June 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013 Table 7 to Subpart CCCC of Part 60

— Emission Limitations for Waste
- burning Kilns That Commenced Construction After June 4, 2010, or Reconstruction or Modification After August 7, 2013 Table 8 to Subpart CCCC of Part 60

— Emission Limitations for Small, Remote Incinerators That Commenced Construction After June 4, 2010, Or That Commenced Reconstruction or Modification After August 7, 2013 Introduction § 60.2000 What does this subpart do? This subpart establishes new source performance standards for commercial and industrial sol id waste incineration (CISWI) units. § 60.2005 When does this subpart become effective? This subpart takes effect on August 7, 2013. Some of the requirements in this subpart apply to planning the CISWI unit (i.e., the preconstruction requirements in § § 60. 2045 and 60.2050). Other requirements such as the emission limitations and operating limits apply after the CISWI unit begins operation. Applicability § 60.2010 Does this subpart apply to my incineration unit?(Subpart CCCC

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- 2013) Page 5 of 163 Yes, if your incineration unit meets all the

r equirements specified in paragraphs (a) through (c) of this section. (a) Your incineration unit is a new incineration unit as defined in § 60.2015. (b) Your incineration unit is a CISWI unit as defined in § 60.2265. (c) Your incineration unit is not exempt under § 60.2020. § 60.2015 What is a new incineration unit? (a) A new incineration unit is an incineration unit that meets any of the criteria specified in paragraph (a)(1) through (a)( 2 3 ) of this section. (1) A CIS WI unit that commenced construction after June 4, 2010. (2) A CISWI unit that commenced reconstruction or modification after August 7, 2013. (3) An i I ncinerator s and or air curtain incinerator s , as defined in this subpart, that commenced construction after November 30, 1999, but no later than June 4, 2010, or that commenced reconstruction or modification on or after June 1, 2001 , but no later than August 7, 2013, are is considered a new incineration unit s and remain s subject to the applicable requirements of this subpart until the units(Subpart CCCC

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- 2013) Page 6 of 163 the incinerator become s subject to the requirements of an approved s tate plan or f ederal plan that implements subpart DDDD of this part (Emission Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units)
. (b) This subpart does not affect your CISWI unit if you make physical or operational changes to your incineration unit primarily to comply with subpart DDDD of this part (Emission Guidelines and Compliance Times for Commercial and Ind ustrial Solid Waste Incineration Units). Such changes do not qualify as reconstruction or modification under this subpart. § 60.2020 What combustion units are exempt from this subpart? This subpart exempts the types of units described in paragraphs (a), (c ) through (i) and (n) of this section, but some units are required to provide notifications. Air curtain incinerators are exempt from the requirements in this subpart except for the provisions in § § 60.2242, 60.2250, and 60.2260. (a) Pathological waste inc ineration units. Incineration units burning 90 percent or more by weight (on a calendar quarter basis and excluding the weight of auxiliary fuel and combustion air) of pathological waste,(Subpart CCCC

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- level radioactive waste, and/or chemotherapeutic waste as define d in § 60.2265 are not subject to this subpart if you meet the two requirements specified in paragraphs (a)(1) and (2) of this section. (1) Notify the Administrator that the unit meets these criteria. (2) Keep records on a calendar quarter basis of the wei ght of pathological waste, low

- level radioactive waste, and/or chemotherapeutic waste burned, and the weight of all other fuels and wastes burned in the unit. (b) [Reserved] (c) Municipal waste combustion units. Incineration units that are subject to subpa rt Ea of this part (Standards of Performance for Municipal Waste Combustors); subpart Eb of this part (Standards of Performance for Large Municipal Waste Combustors); subpart Cb of this part (Emission Guidelines and Compliance Time for Large Municipal Comb ustors); subpart AAAA of this part (Standards of Performance for Small Municipal Waste Combustion Units); or subpart BBBB of this part (Emission Guidelines for Small Municipal Waste Combustion Units). (d) Medical waste incineration units. Incineration unit s regulated under subpart Ec of this part (Standards of Performance for Hospital/Medical/Infectious Waste(Subpart CCCC

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- 2013) Page 8 of 163 Incinerators for Which Construction is Commenced After June 20, 1996) or subpart Ce of this part (Emission Guidelines and Compliance Times for Hospita l/Medical/Infectious Waste Incinerators). (e) Small power production facilities. Units that meet the three requirements specified in paragraphs (e)(1) through ( 3 4 ) of this section. (1) The unit qualifies as a small power

- production facility under section 3 (17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C)). (2) The unit burns homogeneous waste (not including refuse

- derived fuel) to produce electricity. (3) You submit documentation to the Administrator notifying the EPA that the qualifying small power
pr oduction facility is combusting homogenous waste. (4) You maintain the records specified in § 60.2175(w). (f) Cogeneration facilities. Units that meet the three requirements specified in paragraphs (f)(1) through ( 3 4 ) of this section. (1) The unit qualifie s as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)).(Subpart CCCC

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- 2013) Page 9 of 163 (2) The unit burns homogeneous waste (not including refuse

- derived fuel) to produce electricity and steam or other forms of energy used for industrial, com mercial, heating, or cooling purposes. (3) You submit documentation to the Administrator notifying the Agency that the qualifying cogeneration facility is combusting homogenous waste. (4) You maintain the records specified in § 60.2175(x). (g) Hazardous wa ste combustion units. Units for which you are required to get a permit under section 3005 of the Solid Waste Disposal Act. (h) Materials recovery units. Units that combust waste for the primary purpose of recovering metals, such as primary and secondary sm elters. (i) Air curtain incinerators. Air curtain incinerators that burn only the materials listed in paragraphs (i)(1) through (3) of this section are only required to meet the requirements under § 60. 2242 and under “Air Curtain Incinerators” (§ § 60.2245 through 60.2260). (1) 100 percent wood waste. (2) 100 percent clean lumber. (3) 100 percent mixture of only wood waste, clean lumber, and/or yard waste.(Subpart CCCC

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- (l) [Reserved] (m) Sewage treatment plants. Incineration units regulated under subpart O of this part (Standards of Performance for Sewage Treatment Plants). (n) Sewage sludge incineration units. Incineration units combusting sewage sludge for the purpose of reducing the volume of the sewage sludge by removing combustible matter that are subject to subpart LLLL of this part (Standards of Performance for Sewage Sludge Incineration Units) or subpart MMMM of this part (Emission Guidelines for Sewage Sludge Incineration Units). (o) Other solid waste inc ineration units. Incineration units that are subject to subpart EEEE of this part (Standards of Performance for Other Solid Waste Incineration Units) or subpart FFFF of this part (Emission Guidelines and Compliance Times for Other Solid Waste Incineration Units). § 60.2030 Who implements and enforces this subpart? (a) This subpart can be implemented and enforced by the U.S. Environmental Protection Agency (EPA), or a delegated authority such as your State s tate , local, or tribal agency. If the EPA Administrator has delegated authority to your State s tate , local, or tribal agency, then that agency (as well as EPA) has the authority to implement(Subpart CCCC

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- 2013) Page 11 of 163 and enforce this subpart. You should contact your EPA Regional Office to find out if this subpart is delegated to
your State s tate , local, or tribal agency. (b) In delegating implementation and enforcement authority of this subpart to a State s tate , local, or tribal agency, the authorities contained in paragraph (c) of this

se ction are retained by the EPA Administrator and are not transferred to the State s tate , local, or tribal agency. (c) The authorities that will not be delegated to state, local, or tribal agencies are specified in paragraphs (c)(1) through (4) and (c)(6) thr ough (1 1 0 ) of this section. (1) Approval of alternatives to the emission limitations in table 1 of this subpart and operating limits established under § 60.2110. (2) Approval of major alternatives to test methods. (3) Approval of major alternatives to moni toring. (4) Approval of major alternatives to recordkeeping and reporting. (5) [Reserved] (6) The requirements in § 60.2115. (7) The requirements in § 60.2100(b)(2). (8) Approval of alternative opacity emission limits in § 60.2105 under § 60.11(e)(6) throu gh (e)(8).(Subpart CCCC

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- 2013) Page 12 of 163 (9) Performance test and data reduction waivers under § 60.2125(j), 60.8(b)(4) and (5). (10) Determination of whether a qualifying small power production facility or cogeneration facility under § 60.2020(e) or (f) is combusting homogenous waste. (11) Approval of an alternative to any electronic reporting to the EPA required by this subpart. § 60.2035 How are these new source performance standards structured? These new source performance standards contain the eleven major components listed in para graphs (a) through (k) of this section. (a) Preconstruction siting analysis. (b) Waste management plan. (c) Operator training and qualification. (d) Emission limitations and operating limits. (e) Performance testing. (f) Initial compliance requirements. (g ) Continuous compliance requirements. (h) Monitoring. (i) Recordkeeping and reporting. (j) Definitions. (k) Tables.(Subpart CCCC

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- 2013) Page 13 of 163 § 60.2040 Do all eleven components of these new source performance standards apply at the same time? No. You must meet the preconstruction siting analysis and waste management plan requirements before you commence construction of the CISWI unit. The operator training and qualification, emission limitations, operating limits, performance testing and compliance, monitoring, and most recordkeepi ng and reporting requirements are met after the CISWI unit begins operation. Preconstruction Siting Analysis § 60.2045 Who must prepare a siting analysis? (a) You must prepare a siting analysis if you plan to commence construction of an incinerator after D ecember 1, 2000. (b) You must prepare a siting analysis for CISWI units that commenced construction after June 4, 2010, or that commenced reconstruction or modification after August 7, 2013. (c) You must prepare a siting analysis if you are required to sub mit an initial application for a construction permit under 40 CFR part 51, subpart I, or 40 CFR part 52, as applicable, for the reconstruction or modification of your CISWI unit. § 60.2050 What is a siting analysis?(Subpart CCCC

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- 2013) Page 14 of 163 (a) The siting analysis must consider ai r pollution control alternatives that minimize, on a site

- specific basis, to the maximum extent practicable, potential risks to public health or the environment. In considering such alternatives, the analysis may consider costs, energy impacts, nonair envi ronmental impacts, or any other factors related to the practicability of the alternatives. (b) Analyses of your CISWI unit's impacts that are prepared to comply with State state , local, or other Federal
f ederal regulatory requirements may be used to satisfy the requirements of this section, provided they include the consideration of air pollution control alternatives specified in paragraph (a) of this section. (c) You must complete and submit the siting requirements of this section as required under § 60.219 0(c) prior to commencing construction. Waste Management Plan § 60.2055 What is a waste management plan? A waste management plan is a written plan that identifies both the feasibility and the methods used to reduce or separate certain components of solid wa ste from the waste stream in order to reduce or eliminate toxic emissions from incinerated waste. § 60.2060 When must I submit my waste management plan?(Subpart CCCC

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- 2013) Page 15 of 163 (a) You must submit a waste management plan prior to commencing construction. (b) For CISWI units that commence reconstruction or modification after August 7, 2013, you must submit a waste management plan prior to the commencement of modification or reconstruction. § 60.2065 What should I include in my waste management plan? A waste management plan must inc lude consideration of the reduction or separation of waste

- stream elements such as paper, cardboard, plastics, glass, batteries, or metals; or the use of recyclable materials. The plan must identify any additional waste management measures and implement th ose measures the source considers practical and feasible, considering the effectiveness of waste management measures already in place, the costs of additional measures, the emissions reductions expected to be achieved, and any other environmental or energy impacts they might have. Operator Training and Qualification § 60.2070 What are the operator training and qualification requirements? (a) No CISWI unit can be operated unless a fully trained and qualified CISWI unit operator is accessible, either at the f acility or can be at the facility within 1(Subpart CCCC

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- 2013) Page 16 of 163 hour. The trained and qualified CISWI unit operator may operate the CISWI unit directly or be the direct supervisor of one or more other plant personnel who operate the unit. If all qualified CISWI unit operators are temporarily not accessible, you must follow the procedures in § 60.2100. (b) Operator training and qualification must be obtained through a State s tate
- approved program or by completing the requirements included in paragraph (c) of this section. (c) Training must be obtained by completing an incinerator operator training course that includes, at a minimum, the three elements described in paragraphs (c)(1) through (3) of this section. (1) Training on the eleven subjects listed in paragraphs (c)(1)(i) t hrough (xi) of this section. (i) Environmental concerns, including types of emissions. (ii) Basic combustion principles, including products of combustion. (iii) Operation of the specific type of incinerator to be used by the operator, including proper star tup, waste charging, and shutdown procedures. (iv) Combustion controls and monitoring.(Subpart CCCC

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- 2013) Page 17 of 163 (v) Operation of air pollution control equipment and factors affecting performance (if applicable). (vi) Inspection and maintenance of the incinerator and air pollution control devices. (vii) Actions to prevent and correct malfunctions or to prevent conditions that may lead to malfunctions. (viii) Bottom and fly ash characteristics and handling procedures. (ix) Applicable Federal f ederal , State state , and local regulations, including Occupational Safety and Health Administration workplace standards. (x) Pollution prevention. (xi) Waste management practices. (2) An examination designed and administered by the instructor. (3) Written material covering the training course topic s that may serve as reference material following completion of the course. § 60.2075 When must the operator training course be completed? The operator training course must be completed by the later of the three dates specified in paragraphs (a) through (c) of this section. (a) Six months after your CISWI unit startup.(Subpart CCCC

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- 2013) Page 18 of 163 (b) December 3, 2001. (c) The date before an employee assumes responsibility for operating the CISWI unit or assumes responsibility for supervising the operation of the CISWI unit. § 60.2080 H ow do I obtain my operator qualification? (a) You must obtain operator qualification by completing a training course that satisfies the criteria under § 60.2070(b). (b) Qualification is valid from the date on which the training course is completed and the operator successfully passes the examination required under § 60.2070(c)(2). § 60.2085 How do I maintain my operator qualification? To maintain qualification, you must complete an annual review or refresher course covering, at a minimum, the five topics de scribed in paragraphs (a) through (e) of this section. (a) Update of regulations. (b) Incinerator operation, including startup and shutdown procedures, waste charging, and ash handling. (c) Inspection and maintenance. (d) Prevention and correction of malfunctions or conditions that may lead to malfunction. (e) Discussion of operating problems encountered by attendees.(Subpart CCCC

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- 2013) Page 19 of 163 § 60.2090 How do I renew my lapsed operator qualification? You must renew a lapsed operator qualification by one of the two methods spec ified in paragraphs (a) and (b) of this section. (a) For a lapse of less than 3 years, you must complete a standard annual refresher course described in § 60.2085. (b) For a lapse of 3 years or more, you must repeat the initial qualification requirements i n § 60.2080(a). § 60.2095 What site - specific documentation is required? (a) Documentation must be available at the facility and readily accessible for all CISWI unit operators that addresses the ten topics described in paragraphs (a)(1) through (10) of thi s section. You must maintain this information and the training records required by paragraph (c) of this section in a manner that they can be readily accessed and are suitable for inspection upon request. (1) Summary of the applicable standards under this subpart. (2) Procedures for receiving, handling, and charging
waste. (3) Incinerator startup, shutdown, and malfunction procedures.(Subpart CCCC

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- 2013) Page 20 of 163 (4) Procedures for maintaining proper combustion air supply levels. (5) Procedures for operating the incinerator and associa ted air pollution control systems within the standards established under this subpart. (6) Monitoring procedures for demonstrating compliance with the incinerator operating limits. (7) Reporting and recordkeeping procedures. (8) The waste management plan r equired under § § 60.2055 through 60.2065. (9) Procedures for handling ash. (10) A list of the wastes burned during the performance test. (b) You must establish a program for reviewing the information listed in paragraph (a) of this section with each incine rator operator. (1) The initial review of the information listed in paragraph (a) of this section must be conducted within 6 months after the effective date of this subpart or prior to an employee's assumption of responsibilities for operation of the CISWI unit, whichever date is later. (2) Subsequent annual reviews of the information listed in paragraph (a) of this section must be conducted not later than 12 months following the previous review.(Subpart CCCC

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- 2013) Page 21 of 163 (c) You must also maintain the information specified in parag raphs (c)(1) through (3) of this section. (1) Records showing the names of CISWI unit operators who have completed review of the information in § 60.2095(a) as required by § 60.2095(b), including the date of the initial review and all subsequent annual rev iews. (2) Records showing the names of the CISWI operators who have completed the operator training requirements under § 60.2070, met the criteria for qualification under § 60.2080, and maintained or renewed their qualification under § 60.2085 or § 60.2090 . Records must include documentation of training, the dates of the initial and refresher training, and the dates of their qualification and all subsequent renewals of such qualifications. (3) For each qualified operator, the phone and/or pager number at wh ich they can be reached during operating hours. § 60.2100 What if all the qualified operators are temporarily not accessible? If all qualified operators are temporarily not accessible (i.e., not at the facility and not able to be at the facility within 1 h our), you must meet one of the two criteria specified in paragraphs (a) and (b) of this(Subpart CCCC

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- 2013) Page 22 of 163 section, depending on the length of time that a qualified operator is not accessible. (a) When all qualified operators are not accessible for more than 8 hours, but less than 2 weeks, the CISWI unit may be operated by other plant personnel familiar with the operation of the CISWI unit who have completed a review of the information specified in § 60.2095(a) within the past 12 months. However, you must record the period when all qualified operators were not accessible and include this deviation in the annual report as specified under § 60.2210. (b) When all qualified operators are not accessib le for 2 weeks or more, you must take the two actions that are described in paragraphs (b)(1) and (2) of this section. (1) Notify the Administrator of this deviation in writing within 10 days. In the notice, state what caused this deviation, what you are d oing to ensure that a qualified operator is accessible, and when you anticipate that a qualified operator will be accessible. (2) Submit a status report to the Administrator every 4 weeks outlining what you are doing to ensure that a qualified operator is accessible, stating when you anticipate that a qualified operator will be accessible and requesting approval from the Administrator to continue(Subpart CCCC

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- 2013) Page 23 of 163 operation of the CISWI unit. You must submit the first status report 4 weeks after you notify the Administrator of the deviation under paragraph (b)(1) of this section. If the Administrator notifies you that your request to continue operation of the CISWI unit is disapproved, the CISWI unit may continue operation for 90 days, then must cease operation. Operation of the unit may resume if you meet the two requirements in paragraphs (b)(2)(i) and (ii) of this section. (i) A qualified operator is accessible as required under § 60.2070(a). (ii) You notify the Administrator that a qualified operator is accessible and that you are resuming operation. Emission Limitations and Operating Limits § 60.2105 What emission limitations must I meet and by when? (a) You must meet the emission limitations for each CISWI unit, including bypass stack or vent, specified in table 1 of this subpart or tables 5 through 8 of this subpart by the applicable date in § 60.2140. You must be in compliance with the emission limitations of this subpart that apply to you at all times. (b) An incinerator or air curtain incinerator unit that commenced construction after November 30, 1999, but no(Subpart CCCC

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- 2013) Page 24 of 163 later than June 4, 2010, or that commenced reconstruction or modification on or after June 1, 2001 but no later than August 7, 2013, must continue to meet the more stringent emission limit s for the respective pollutant in table 1 of this subpart for units in the incinerator subcategory and § section 60.2250 of this subpart for air curtain incinerators until the units become subject to the requirements of an approved state plan or f ederal plan tha t implements subpart DDDD of this part (Emission Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units). or table 6 of subpart DDDD. § 60.2110 What operating limits must I meet and by when? (a) If you use a wet scrubb er(s) to comply with the emission limitations, you must establish operating limits for up to four operating parameters (as specified in table 2 of this subpart) as described in paragraphs (a)(1) through (4) of this section during the initial performance
te st. (1) Maximum charge rate, calculated using one of the two different procedures in paragraph (a)(1)(i) or (ii), as appropriate. (i) For continuous and intermittent units, maximum charge rate is 110 percent of the average charge rate measured during the m ost recent performance test(Subpart CCCC

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- 2013) Page 25 of 163 demonstrating compliance with all applicable emission limitations. (ii) For batch units, maximum charge rate is 110 percent of the daily charge rate measured during the most recent performance test demonstrating compliance with all applicable emission limitations. (2) Minimum pressure drop across the wet particulate matter scrubber, which is calculated as the lowest 1

- hour average pressure drop across the wet scrubber measured during the most recent performance test demonstrating compliance with the particulate matter emission limitations; or minimum amperage to the wet scrubber, which is calculated as the lowest 1

- hour average amperage to the wet scrubber measured during the most recent performance test demonstrating compliance w ith the particulate matter emission limitations. (3) Minimum scrubber liquid flow rate, which is calculated as the lowest 1

- hour average liquid flow rate at the inlet to the wet acid gas or particulate matter scrubber measured during the most recent perfor mance test demonstrating compliance with all applicable emission limitations. (4) Minimum scrubber liquor pH, which is calculated as the lowest 1

- hour average liquor pH at the inlet to the wet(Subpart CCCC

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- 2013) Page 26 of 163 acid gas scrubber measured during the most recent performance t est demonstrating compliance with the HCl emission limitation. (b) You must meet the operating limits established during the initial performance test 60 days after your CISWI unit reaches the charge rate at which it will operate, but no later than 180 days after its initial startup. (c) If you use a fabric filter to comply with the emission limitations, you must operate each fabric filter system such that the bag leak detection system alarm does not sound more than 5 percent of the operating time during a 6

- month period. In calculating this operating time percentage, if inspection of the fabric filter demonstrates that no corrective action is required, no alarm time is counted. If corrective action is required, each alarm shall be counted as a minimum of 1 h our. If you take longer than 1 hour to initiate corrective action, the alarm time shall be counted as the actual amount of time taken by you to initiate corrective action. (d) If you use an electrostatic precipitator to comply with the emission limitations , you must measure the (secondary) voltage and amperage of the electrostatic precipitator collection plates during the particulate(Subpart CCCC

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- 2013) Page 27 of 163 matter performance test. Calculate the average electric power value (secondary voltage × secondary current = secondary electr ic power) for each test run. The operating limit for the electrostatic precipitator is calculated as the lowest 1

- hour average secondary electric power measured during the most recent performance test demonstrating compliance with the particulate matter em ission limitations. (e) If you use activated carbon sorbent injection to comply with the emission limitations, you must measure the sorbent flow rate during the performance testing. The operating limit for the carbon sorbent injection is calculated as the lowest 1

- hour average sorbent flow rate measured during the most recent performance test demonstrating compliance with the mercury emission limitations. For energy recovery units, when your unit operates at lower loads, multiply your sorbent injection
rate by the load fraction, as defined in this subpart, to determine the required injection rate (e.g., for 50 percent load, multiply the injection rate operating limit by 0.5). (f) If you use selective noncatalytic reduction to comply with the emission limitat ions, you must measure the charge rate, the secondary chamber temperature (if applicable to your CISWI unit), and the reagent flow rate(Subpart CCCC

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- 2013) Page 28 of 163 during the nitrogen oxides performance testing. The operating limits for the selective noncatalytic reduction are calcul ated as the highest 1

- hour average charge rate, lower secondary chamber temperature, and lowest reagent flow rate measured during the most recent performance test demonstrating compliance with the nitrogen oxides emission limitations. (g) If you use a dry scrubber to comply with the emission limitations, you must measure the injection rate of each sorbent during the performance testing. The operating limit for the injection rate of each sorbent is calculated as the lowest 1

- hour average injection rate or

ea ch sorbent measured during the most recent performance test demonstrating compliance with the hydrogen chloride emission limitations. For energy recovery units, when your unit operates at lower loads, multiply your sorbent injection rate by the load fracti on, as defined in this subpart, to determine the required injection rate (e.g., for 50 percent load, multiply the injection rate operating limit by 0.5). (h) If you do not use a wet scrubber, electrostatic precipitator, or fabric filter to comply with the emission limitations, and if you do not determine compliance with your particulate matter emission limitation with a(Subpart CCCC

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- 2013) Page 29 of 163 particulate matter CEMS, you must maintain opacity to less than or equal to 10 percent opacity (1

- hour block average). (i) If you use a PM CPMS to demonstrate compliance, you must establish your PM CPMS operating limit and determine compliance with it according to paragraphs (i)(1) through (5) of this section. (1) Determine your operating limit as the average PM CPMS output value recorded during the performance test or at a PM CPMS output value corresponding to 75% of the emission limit if your PM performance test demonstrates compliance below 75% of the emission limit. You must verify an existing or establish a new operating limit after ea ch repeated performance test. You must repeat the performance test annually and reassess and adjust the site

- specific operating limit in accordance with the results of the performance test. ( i A ) Your PM CPMS must provide a 4

- 20 milliamp output
4

- 20 milliamp output, or digital equivalent, and the establishment of its relationship to manual reference method measurements must be determined in units of milliamps. ( ii B ) Your PM CPMS operating range must be capable of reading PM concentrations from zero to a level equivalent to at least two times your allowable emission limit. If(Subpart CCCC

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- 2013) Page 30 of 163 your PM CPMS is an auto

- ranging instrument capable of multiple scales, the primary range of the instrument must be capable of reading PM concentration from zero to a level equivale nt to two times your allowable emission limit. ( iii C ) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, record and average all milliamp or digital, output values from the PM CPMS for the periods corresponding to the compliance test runs (e.g., average all your PM CPMS output values for three corresponding 2

- hour Method 5I test runs). (2) If the average of your three PM performance test runs are below 75% of your PM emission limit, you must calculate an operating limit by establishing a relationship of PM CPMS signal to PM concentration using the PM CPMS instrument zero, the average PM CPMS output values corresponding to the three compliance test runs, and the average PM concentration f rom the Method 5 or performance test with the procedures in (i)(1)through (5) of this section. (i) Determine your instrument zero output with one of the following procedures:(Subpart CCCC

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- 2013) Page 31 of 163 (A) Zero point data for in

- situ instruments should be obtained by removing the in strument from the stack and monitoring ambient air on a test bench. (B) Zero point data for extractive instruments should be obtained by removing the extractive probe from the stack and drawing in clean ambient air. (C) The zero point can also can be estab lished obtained by performing manual reference method measurements when the flue gas is free of PM emissions or contains very low PM concentrations ( e.g., when your process is not operating, but the fans are operating or your source is combusting only natu ral gas) and plotting these with the compliance data to find the zero intercept. (D) If none of the steps in paragraphs (i)(2)(i) (A) through (i)(2)(i)(C) (iv) of this section are possible, you must use a zero output value provided by the manufacturer. (ii) Determine your PM CPMS instrument average in milliamps, or the digital equivalent, and the average of your corresponding three PM compliance test runs, using equation 1.

(Eq. 1)(Subpart CCCC

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- 2013) Page 32 of 163 Where:

X 1 = the PM CPMS output data points for the three

runs constituting the performance test, Y 1 = the PM concentration value for the three runs

constituting the performance test, and

n = the number of data points. (iii) With your instrument zero expressed in milliamps, or the digital equivalent, your three run av erage PM CPMS milliamp value, or its digital equivalent, and your three run average PM concentration from your three compliance tests, determine a relationship of lb/Mmbtu mg/dscm per milliamp or digital signal equivalent with equation 2.
(Eq. 2)
W here:

R = the relative mg/dscm per milliamp or digital

equivalent for your PM CPMS, Y 1 = the three run average mg/dscm PM

concentration, X 1 = the three run average milliamp or digital

signal output from you PM CPMS, and

z = the milliamp or digital signal e quivalent of

your instrument zero determined from (2)(i). (iv) Determine your source specific 30

- day rolling average operating limit using the mg/dscm per milliamp or digital value from Equation e quation 2 in equation 3, below. This sets your operating lim it at the PM CPMS output value corresponding to 75% of your emission limit.
(Eq. 3) Where:(Subpart CCCC

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- 2013) Page 33 of 163 O l = the operating limit for your PM CPMS on a 30

-

day rolling average, in milliamps or their digital signal equivalent
. L = your source emission limit expressed in

lb/Mmbtu mg/dscm , z = your instrument zero in milliamps or the

digital equivalent , determined from (2)( a i ), and R = the relative mg/dscm per milliamp or digital

signal output equivalent for your PM CPMS, from Equation e quation 3 2
. (3) If the average of your three PM compliance test runs is at or above 75% of your PM emission limit you must determine your operating limit by averaging the PM CPMS milliamp or digital signal output corresponding to your three PM performanc e test runs that demonstrate compliance with the emission limit using equation 4 and you must submit all compliance test and PM CPMS data according to the reporting requirements in paragraph (i)(5) of this section.
(Eq. 4) Where:

X 1 = the PM CPMS data points for all runs i,

n = the number of data points, and O h = your site specific operating limit, in

milliamps or digital signal equivalent
. (4) To determine continuous compliance, you must record the PM CPMS output data for all periods when the process i s operating and the PM CPMS is not out

- of

- control.(Subpart CCCC

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- 2013) Page 34 of 163 You must demonstrate continuous compliance by using all quality

- assured hourly average data collected by the PM CPMS for all operating hours to calculate the arithmetic average operating parameter in units of the operating limit (e.g., milliamps or digital signal bits , PM concentration, raw data signal) on a 30

- day rolling average basis. (5) For PM performance test reports used to set a PM CPMS operating limit, the electronic submission of the test report m ust also include the make and model of the PM CPMS instrument, serial number of the instrument, analytical principle of the instrument (e.g., beta attenuation), span of the instruments primary analytical range, milliamp or digital signal value equivalent t o the instrument zero output, technique by which this zero value was determined, and the average milliamp or digital ditigal signals corresponding to each PM compliance test run. § 60.2115 What if I do not use a wet scrubber, fabric filter, activated carbon injection, selective noncatalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations? If you use an air pollution control device other than a wet scrubber, activated carbon injection, selective noncatalytic reduction, fabric filter, an electrostatic precipitator, or a dry scrubber or limit emissions in some(Subpart CCCC

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- 2013) Page 35 of 163 other manner, including material balances, to comply with the emission limitations under § 60.2105, you must petition the EPA Administrator for specific operating limits to be established during the initial performance test and continuously monitored thereafter. You must submit the petition at least sixty days before the performance test is scheduled to begin. Your petition must include the five items list ed in paragraphs (a) through (e) of this section. (a) Identification of the specific parameters you propose to use as additional operating limits. (b) A discussion of the relationship between these parameters and emissions of regulated pollutants, identify ing how emissions of regulated pollutants change with changes in these parameters and how limits on these parameters will serve to limit emissions of regulated pollutants. (c) A discussion of how you will establish the upper and/or lower values for these p arameters which will establish the operating limits on these parameters. (d) A discussion identifying the methods you will use to measure and the instruments you will use to monitor these parameters, as well as the relative accuracy and precision of these methods and instruments.(Subpart CCCC

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- 2013) Page 36 of 163 (e) A discussion identifying the frequency and methods for recalibrating the instruments you will use for monitoring these parameters. § 60.2120 Affirmative defense for violation of emission standards during malfunction. In response to an action to enforce the standards set forth in paragraph § 60.2105 you may assert an affirmative defense to a claim for civil penalties for violations of such standards that are caused by malfunction, as defined at 40 CFR 60.2. Appropriate penalties may be assessed if you fail to meet your burden of proving all of the requirements in the affirmative defense. The affirmative defense shall not be available for claims for injunctive relief. (a) Assertion of affirmative defense. To establish the affirmative defense in any action to enforce such a standard, you must timely meet the reporting requirements in paragraph (b) of this section, and must prove by a preponderance of evidence that: (1) The violation: (i) Was caused by a sudden, infrequent, and unavoidable failure of air pollution control equipment, process equipment, or a process to operate in a normal or usual manner; and(Subpart CCCC

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- 2013) Page 37 of 163 (ii) Could not have been prevented through careful planning, proper design or better operation and maintenance practices; and (iii) Did not stem from any activity or event that could have been foreseen and avoided, or planned for; and (iv) Was not part of a recurring pattern indicative of inadequate design, operation, or maintenance; and (2) Repairs were made as expeditiously as possible when a violation occurred; and (3) The frequency, amount, and duration of the violation (including any bypass) were mini mized to the maximum extent practicable; and (4) If the violation resulted from a bypass of control equipment or a process, then the bypass was unavoidable to prevent loss of life, personal injury, or severe property damage; and (5) All possible steps were taken to minimize the impact of the violation on ambient air quality, the environment, and human health; and (6) All emissions monitoring and control systems were kept in operation if at all possible, consistent with safety and good air pollution control practices; and(Subpart CCCC

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- 2013) Page 38 of 163 (7) All of the actions in response to the violation were documented by properly signed, contemporaneous operating logs; and (8) At all times, the affected source was operated in a manner consistent with good practices for minimizing emission s; and (9) A written root cause analysis has been prepared, the purpose of which is to determine, correct, and eliminate the primary causes of the malfunction and the violation resulting from the malfunction event at issue. The analysis shall also specify, using best monitoring methods and engineering judgment, the amount of any emissions that were the result of the malfunction. (b) Report. The owner or operator seeking to assert an affirmative defense shall submit a written report to the Administrator with all necessary supporting documentation, that it has met the requirements set forth in paragraph (a) of this section. This affirmative defense report shall be included in the first periodic compliance, deviation report or excess emission report otherwise r equired after the initial occurrence of the violation of the relevant standard (which may be the end of any applicable averaging period). If such compliance, deviation report or excess emission report is due less than 45 days after the initial(Subpart CCCC

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occurrence o f the violation, the affirmative defense report may be included in the second compliance, deviation report or excess emission report due after the initial occurrence of the violation of the relevant standard. Performance Testing § 60.2125 How do I conduct the initial and annual performance test? (a) All performance tests must consist of a minimum of three test runs conducted under conditions representative of normal operations. (b) You must document that the waste burned during the performance test is repre sentative of the waste burned under normal operating conditions by maintaining a log of the quantity of waste burned (as required in § 60.2175(b)(1)) and the types of waste burned during the performance test. (c) All performance tests must be conducted usi ng the minimum run duration specified in table 1 of this subpart or tables 5 through 8 of this subpart. (d) Method 1 of appendix A of this part must be used to select the sampling location and number of traverse points. (e) Method 3A or 3B of appendix A of this part must be used for gas composition analysis, including measurement of(Subpart CCCC

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- 2013) Page 40 of 163 oxygen concentration. Method 3A or 3B of appendix A of this part must be used simultaneously with each method. (f) All pollutant concentrations, except for opacity, must be adju sted to 7 percent oxygen using e E quation 1 5 of this section:
C adj = C meas (20.9

- 7)/(20.9

- %O 2 ) ( Eq. 1 5 ) Where:

C adj = pollutant concentration adjusted to 7 percent

oxygen; C meas = pollutant concentration measured on a dry

basis; (20.9

- 7) = 20.9 percent oxygen−7 percent oxygen (defined

oxygen correction basis); 20.9 = oxygen concentration in air, percent; and %O 2 = oxygen concentration measured on a dry basis,

percent. (g) You must determine dioxins/furans toxic equivalency by following the procedures in paragraphs (g)(1) through (4) of this section. (1) Measure the concentration of each dioxin/furan
tetra
- through octa

- chlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, appendix A

- 7. (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet identification criteria 1 and 7. You must quantify the isomers per Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot or split to(Subpart CCCC

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- 2013) Page 41 of 163 reduce the number of isome rs not meeting identification criteria 1 or 7 of Section 5.3.2.5.) (3) For each dioxin/furan (tetra

- through octa

chlorinated) isomer measured in accordance with paragraph (g)(1) and (2) of this section, multiply the isomer concentration by its correspondin g toxic equivalency factor specified in table 3 of this subpart. (4) Sum the products calculated in accordance with paragraph (g)(3) of this section to obtain the total concentration of dioxins/furans emitted in terms of toxic equivalency. (h) Method 22 at 40 CFR part 60, appendix A

- 7 of this part must be used to determine compliance with the fugitive ash emission limit in table 1 of this subpart or tables 5 through 8 of this subpart. (i) If you have an applicable opacity operating limit, you must determine compliance with the opacity limit using Method 9 at 40 CFR part 60, appendix A

- 4 of this part, based on three 1

- hour blocks consisting of ten 6

- minute average opacity values, unless you are required to install a continuous opacity monitoring system, consi stent with § § 60.2145 and 60.2165.(Subpart CCCC

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- 2013) Page 42 of 163 (j) You must determine dioxins/furans total mass basis by following the procedures in paragraphs (j)(1) through (3) of this section. (1) Measure the concentration of each dioxin/furan
tetra
- through octa

- chlorinated isomer emitted using EPA Method 23 at 40 CFR part 60, appendix A

- 7. (2) Quantify isomers meeting identification criteria 2, 3, 4, and 5 in Section 5.3.2.5 of Method 23, regardless of whether the isomers meet identification criteria 1 and 7. You must quantify the isomers per Section 9.0 of Method 23. (Note: You may reanalyze the sample aliquot or split to reduce the number of isomers not meeting identification criteria 1 or 7 of Section 5.3.2.5.) (3) Sum the quantities measured in accordance with paragraphs (j)(1) and (2) of this section to obtain the total concentration of dioxins/furans emitted in terms of total mass basis. § 60.2130 How are the performance test data used? You use results of performance tests to demonstrate compliance with the emission limitation s in table 1 of this subpart or tables 5 through 8 of this subpart. Initial Compliance Requirements § 60.2135 How do I demonstrate initial compliance with the emission limitations and establish the operating limits?(Subpart CCCC

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- 2013) Page 43 of 163 You must conduct a performance test, as required under § § 60.2125 and 60.2105 to determine compliance with the emission limitations in table 1 of this subpart or tables 5 through 8 of this subpart, to establish compliance with any opacity operating limit in § 60.2110, to establish the kiln

- speci fic emission limit in § 60.21 45(y), as applicable, and to establish operating limits using the procedures in § § 60.2110 or 60.2115. The performance test must be conducted using the test methods listed in table 1 of this subpart or tables 5 through 8 of this subpart and the procedures in § 60.2125. The use of the bypass stack during a performance test shall invalidat e the performance test. You must conduct a performance evaluation of each continuous monitoring system within 60 days of installation of the monitoring system. § 60.2140 By what date must I conduct the initial performance test? (a) The initial performance test must be conducted within 60 days after your CISWI unit reaches the charge rate at which it will operate, but no later than 180 days after its initial startup. (b) If you commence or recommence combusting a solid waste at an existing combustion unit at any commercial or industrial facility, and you conducted a test consistent(Subpart CCCC

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- 2013) Page 44 of 163 with the provisions of this subpart while combusting the solid waste within the 6 months preceding the reintroduction of that solid waste in the combustion chamber, you do not need to retest until 6 months from the date you reintroduce that solid waste. (c) If you commence combusting or recommence combusting a solid waste at an existing combustion unit at any commercial or industrial facility and you have not conducted a performance test consistent with the provisions of this subpart while combusting the solid waste within the 6 months preceding the reintroduction of that solid waste in the combustion chamber, you must conduct a performance test within 60 days commencing or recommenc ing from the date you reintroduce that solid waste combustion
. § 60.2141 By what date must I conduct the initial air pollution control device inspection? (a) The initial air pollution control device inspection must be conducted within 60 days after install ation of the control device and the associated CISWI unit reaches the charge rate at which it will operate, but no later than 180 days after the device's initial startup. (b) Within 10 operating days following an air pollution control device inspection, al l necessary repairs must be completed unless the owner or operator obtains(Subpart CCCC

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- 2013) Page 45 of 163 written approval from the state agency establishing a date whereby all necessary repairs of the designated facility must be completed. Continuous Compliance Requirements § 60.2145 How do I demonstrate continuous compliance with the emission limitations and the operating limits? (a) Compliance with standards. (1) The emission standards and operating requirements set forth in this subpart apply at all times. (2) If you cease combustin g solid waste, you may opt to remain subject to the provisions of this subpart. Consistent with the definition of CISWI unit, you are subject to the requirements of this subpart at least 6 months following the last date of solid waste combustion. Solid was te combustion is ceased when solid waste is not in the combustion chamber ( i.e., the solid waste feed to the combustor has been cut off for a period of time not less than the solid waste residence time). (3) If you cease combusting solid waste, you must be in compliance with any newly applicable standards on the effective date of the waste

- to
- fuel switch. The effective date of the waste

- to
- fuel switch is a date selected by you, that must be at least 6 months from the date that you ceased combusting solid wa ste, consistent with §(Subpart CCCC

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- 2013) Page 46 of 163 60.2145(a)(2). Your source must remain in compliance with this subpart until the effective date of the waste

- to
- fuel switch. (4) If you own or operate an existing commercial or industrial combustion unit that combusted a fuel or non

waste material, and you commence or recommence combustion of solid waste, you are subject to the provisions of this subpart as of the first day you introduce or reintroduce solid waste to the combustion chamber, and this date constitutes the effective date of the fuel

- to
- waste switch. You must complete all initial compliance demonstrations for any section 112 standards that are applicable to your facility before you commence or recommence combustion of solid waste. You must provide 30 days prior notice of t he effective date of the waste

- to
- fuel switch. The notification must identify: (i) The name of the owner or operator of the CISWI unit, the location of the source, the emissions unit(s) that will cease burning solid waste, and the date of the notice; (ii) The currently applicable subcategory under this subpart, and any 40 CFR part 63 subpart and subcategory that will be applicable after you cease combusting solid waste;(Subpart CCCC

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- 2013) Page 47 of 163 (iii) The fuel(s), non

- waste material(s) and solid waste(s) the CISWI unit is currently combusting and has combusted over the past 6 months, and the fuel(s) or non

waste materials the unit will commence combusting; (iv) The date on which you became subject to the currently applicable emission limits; (v) The date upon which you will cease com busting solid waste, and the date (if different) that you intend for any new requirements to become applicable ( i.e., the effective date of the waste

- to
- fuel switch), consistent with paragraphs (a)(2) and (3)of this section. (5) All air pollution control e quipment necessary for compliance with any newly applicable emissions limits which apply as a result of the cessation or commencement or recommencement of combusting solid waste must be installed and operational as of the effective date of the waste

- to
fue l, or fuel

- to
- waste switch. (6) All monitoring systems necessary for compliance with any newly applicable monitoring requirements which apply as a result of the cessation or commencement or recommencement of combusting solid waste must be installed and ope rational as of the effective date of the waste

- to
fuel, or fuel

- to
- waste switch. All calibration and drift checks must be performed as of the effective date of the(Subpart CCCC

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- 2013) Page 4 8 of 163 waste
- to
- fuel, or fuel

- to
- waste switch. Relative accuracy tests must be performed as of the performance test deadline for PM CEMS (if PM CEMS are elected to demonstrate continuous compliance with the particulate matter emission limits). Relative accuracy testing for other CEMS need not be repeated if that testing was previously performed consiste nt with Clean Air Act section 112 monitoring requirements or monitoring requirements under this subpart. (b) You must conduct an annual performance test for the pollutants listed in table 1 of this subpart or tables 5 through 8 of this subpart and opacity for each CISWI unit as required under § 60.2125. The annual performance test must be conducted using the test methods listed in table 1 of this subpart or tables 5 through 8 of this subpart and the procedures in § 60.2125. Annual performance tests are
not required if you use CEMS or continuous opacity monitoring systems to determine compliance. (c) You must continuously monitor the operating parameters specified in § 60.2110 or established under § 60.2115 and as specified in § 60.2170. Use 3

- hour block

aver age values to determine compliance (except for baghouse leak detection system alarms) unless a different averaging period is established under § 60.2115 or, for energy recovery units, where the averaging time for each operating(Subpart CCCC

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- 2013) Page 49 of 163 parameter is a 30

- day rollin g, calculated each hour as the average of the previous 720 operating hours. Operation above the established maximum, below the established minimum, or outside the allowable range of operating limits specified in paragraph (a) of this section constitutes a deviation from your operating limits established under this subpart, except during performance tests conducted to determine compliance with the emission and operating limits or to establish new operating limits. Operating limits are confirmed or reestablis hed during performance tests. (d) You must burn only the same types of waste and fuels used to establish subcategory applicability (for energy recovery units) and operating limits during the performance test. (e) For energy recovery units, incinerators, an d small remote units, you must perform an annual visual emissions test for ash handling. (f) For energy recovery units, you must conduct an annual performance test for opacity (except where particulate matter CEMS or continuous opacity monitoring systems a re used are used) and the pollutants listed in table 6 of this subpart.(Subpart CCCC

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- 2013) Page 50 of 163 (g) You may elect to demonstrate continuous compliance with the carbon monoxide emission limit using a carbon monoxide CEMS according to the following requirements: (1) You must measur e emissions according to § 60.13 to calculate 1

- hour arithmetic averages, corrected to 7 percent oxygen. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. You must demonstrate initial compliance with the carbon monoxide emissions limit using a 30

- day rolling average of these 1

- hour arithmetic average emission concentrations, including CEMS data during startup and shutdown as defined in this subpart, calculated using e E quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A

- 7 of this part. (2) Operate the carbon monoxide CEMS in accordance with the requirements of performance specification 4A of appendix B of this part and quality assurance procedure 1 of appendix F of this part. (h) Coal and liquid/gas energy recovery units with average annual heat input rates greater than or equal to 250 MMBtu/hr may elect to demonstrate continuous compliance with the particulate matter emissions limit using a particulate matter CEMS according to the procedures in §(Subpart CCCC

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- 2013) Page 51 of 163 60.2165(n) instead of the particulate matter continuous parameter monitoring system (CPMS) specified in § 60.2145. Coal and liquid/gas energy recovery units with annual average heat in put rates less than 250 MMBtu/hr, incinerators, and small remote incinerators may also elect to demonstrate compliance using a particulate matter CEMS according to the procedures in § 60.2165(n) instead of particulate matter testing with EPA Method 5 at 40 CFR part 60, appendix A

- 3 and, if applicable, the continuous opacity monitoring requirements in paragraph (i) of this section. (i) For energy recovery units with annual average heat input rates greater than or equal to 10 MMBtu/hour and less than 250 MMBt u/hr, you must install, operate, certify and maintain a continuous opacity monitoring system (COMS) according to the procedures in § 60.2165. (j) For waste

- burning kilns, you must conduct an annual performance test for cadmium, lead, dioxins/furans and hyd rogen chloride as listed in table 7 of this subpart. You must determine compliance with hydrogen chloride using a hydrogen chloride CEMS if you do not use an acid gas wet scrubber or dry scrubber. You must determine compliance with nitrogen oxides, sulfur dioxide, and carbon monoxide using CEMS. You must determine compliance with particulate matter using CPMS. You must determine compliance with the(Subpart CCCC

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- 2013) Page 52 of 163 mercury emissions limit using a mercury CEMS according to the following requirements: (1) Operate a CEMS syste m in accordance with performance specification 12A of 40 CFR part 60, appendix B or a sorbent trap based integrated monitor in accordance with performance specification 12B of 40 CFR part 60, appendix B. The duration of the performance test must be a calen dar month. For each calendar month in which the waste

burning kiln operates, hourly mercury concentration data, and stack gas volumetric flow rate data must be obtained. You must demonstrate compliance with the mercury emissions limit using a 30

- day rollin g average of these 1

- hour mercury concentrations, including CEMS data during startup and shutdown as defined in this subpart, calculated using Equation e quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A

- 7 of this part
. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. (2) Owners or operators using a mercury CEMS must install, operate, calibrate, and maintain an instrument for continuously measuring and recording the mercury mass emissions rate to the atmosphere according to the requirements of performance specifications 6 and 12A of 40(Subpart CCCC

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- 2013) Page 53 of 163 CFR part 60, appendix B, and quality assurance procedure 6 of 40 CFR part 60, appendix F. (3) The owner or operator of a waste

- burning kiln must demonstrate initial compliance by operating a mercury CEMS while the raw mill of the in

- line kiln/raw mill is operating under normal conditions and including at least one period when the raw mill is o ff. (k) If you use an air pollution control device to meet the emission limitations in this subpart, you must conduct an initial and annual inspection of the air pollution control device. The inspection must include, at a minimum, the following: (1) Inspect air pollution control device(s) for proper operation. (2) Develop a site

- specific monitoring plan according to the requirements in paragraph (l) of this section. This requirement also applies to you if you petition the EPA Administrator for alterna tive monitoring parameters under § 60.13(i). (l) For each continuous monitoring system required in this section, you must develop and submit to the EPA Administrator for approval a site

- specific monitoring plan according to the requirements of this paragra ph (l) that(Subpart CCCC

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- 2013) Page 54 of 163 addresses paragraphs (l)(1)(i) through (vi) of this section. (1) You must submit this site

- specific monitoring plan at least 60 days before your initial performance evaluation of your continuous monitoring system. (i) Installation of the contin uous monitoring system sampling probe or other interface at a measurement location relative to each affected process unit such that the measurement is representative of control of the exhaust emissions ( e.g., on or downstream of the last control device). (ii) Performance and equipment specifications for the sample interface, the pollutant concentration or parametric signal analyzer and the data collection and reduction systems. (iii) Performance evaluation procedures and acceptance criteria ( e.g., calibrat ions). (iv) Ongoing operation and maintenance procedures in accordance with the general requirements of § 60.11(d). (v) Ongoing data quality assurance procedures in accordance with the general requirements of § 60.13. (vi) Ongoing recordkeeping and reporti ng procedures in accordance with the general requirements of § 60.7(b), (c), (c)(1), (c)(4), (d), (e), (f), and (g).(Subpart CCCC

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- 2013) Page 55 of 163 (2) You must conduct a performance evaluation of each continuous monitoring system in accordance with your site

specific monitoring plan. ( 3) You must operate and maintain the continuous monitoring system in continuous operation according to the site

- specific monitoring plan. (m) If you have an operating limit that requires the use of a flow monitoring system, you must meet the requirements i n paragraphs (l) and (m)(1) through (4) of this section. (1) Install the flow sensor and other necessary equipment in a position that provides a representative flow. (2) Use a flow sensor with a measurement sensitivity at full scale of no greater than 2 pe rcent. (3) Minimize the effects of swirling flow or abnormal velocity distributions due to upstream and downstream disturbances. (4) Conduct a flow monitoring system performance evaluation in accordance with your monitoring plan at the time of each perform ance test but no less frequently than annually. (n) If you have an operating limit that requires the use of a pressure monitoring system, you must meet the(Subpart CCCC

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- 2013) Page 56 of 163 requirements in paragraphs (l) and (n)(1) through (6) of this section. (1) Install the pressure sens or(s) in a position that provides a representative measurement of the pressure ( e.g., PM scrubber pressure drop). (2) Minimize or eliminate pulsating pressure, vibration, and internal and external corrosion. (3) Use a pressure sensor with a minimum toleran ce of 1.27 centimeters of water or a minimum tolerance of 1 percent of the pressure monitoring system operating range, whichever is less. (4) Perform checks at the frequency outlined in your site

- specific monitoring plan to ensure pressure
measurements are not obstructed (e.g., check for pressure tap pluggage plugging daily). (5) Conduct a performance evaluation of the pressure monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually
. (6) If at any time the measured pressure exceeds the manufacturer's specified maximum operating pressure range, conduct a performance evaluation of the pressure monitoring system in accordance with your monitoring plan and confirm that the pressure monit oring system continues to meet the(Subpart CCCC

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- 2013) Page 57 of 163 performance requirements in your monitoring plan. Alternatively, install and verify the operation of a new
pressure sensor. (o) If you have an operating limit that requires a pH monitoring system, you must meet the requir ements in paragraphs (l) and (o)(1) through (4) of this section. (1) Install the pH sensor in a position that provides a representative measurement of scrubber effluent pH. (2) Ensure the sample is properly mixed and representative of the fluid to be measu red. (3) Conduct a performance evaluation of the pH monitoring system in accordance with your monitoring plan at least once each process operating day. (4) Conduct a performance evaluation (including a two

point calibration with one of the two buffer solut ions having a pH within 1 of the pH of the operating limit) of the pH monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than quarterly. (p) If you have an operating limit that requires a secondary electric power monitoring system for an electrostatic precipitator, you must meet the requirements in paragraphs (l) and (p)(1) through (2) of this section.(Subpart CCCC

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- 2013) Page 58 of 163 (1) Install sensors to measure (secondary) voltage and current to the precipitator collec tion plates. (2) Conduct a performance evaluation of the electric power monitoring system in accordance with your monitoring plan at the time of each performance test but no less frequently than annually. (q) If you have an operating limit that requires th e use of a monitoring system to measure sorbent injection
rate ( e.g., weigh belt, weigh hopper, or hopper flow measurement device), you must meet the requirements in paragraphs (l) and (q)(1) and (2) of this section. (1) Install the system in a position(s) that provides a representative measurement of the total sorbent injection
rate. (2) Conduct a performance evaluation of the sorbent injection rate monitoring system in accordance with your monitoring plan at the time of each performance test but no less f requently than annually. (r) If you elect to use a fabric filter bag leak detection system to comply with the requirements of this subpart, you must install, calibrate, maintain, and continuously operate a bag leak detection system as specified in paragrap hs (l) and (r)(1) through (5) of this section.(Subpart CCCC

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- 2013) Page 59 of 163 (1) Install a bag leak detection sensor(s) in a position(s) that will be representative of the relative or absolute particulate matter loadings for each exhaust stack, roof vent, or compartment ( e.g., for a po sitive pressure fabric filter) of the fabric filter. (2) Use a bag leak detection system certified by the manufacturer to be capable of detecting particulate matter emissions at concentrations of 10 milligrams per actual cubic meter or less. (3) Conduct a performance evaluation of the bag leak detection system in accordance with your monitoring plan and consistent with the guidance provided in EPA

- 454/R

- 98

- 015 (incorporated by reference, see § 60.17). (4) Use a bag leak detection system equipped with a devi ce to continuously record the output signal from the

sensor. (5) Use a bag leak detection system equipped with a system that will sound an alarm when an increase in relative particulate matter emissions over a preset level is detected. The alarm must be lo cated where it is observed readily by plant operating personnel. (s) For facilities using a CEMS to demonstrate compliance with the sulfur dioxide emission limit, compliance with the sulfur dioxide emission limit may be(Subpart CCCC

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- 2013) Page 60 of 163 demonstrated by using the CEMS speci fied in § 60.2165 to measure sulfur dioxide. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. You must calculate a 30

- day rolling average of the 1

- hour arith metic average emission concentrations, including CEMS data during startup and shutdown as defined in this subpart, calculated using Equation e quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, Appendix A

- 7 of this part. The sulfu r dioxide CEMS must be operated according to performance specification 2 in appendix B of this part and must follow the procedures and methods specified in this paragraph (s). For sources that have actual inlet emissions less than 100 parts per million dry volume, the relative accuracy criterion for inlet sulfur dioxide CEMS should be no greater than 20 percent of the mean value of the reference method test data in terms of the units of the emission standard, or 5 parts per million dry volume absolute value of the mean difference between the reference method and the CEMS, whichever is greater. (1) During each relative accuracy test run of the CEMS required by performance specification 2 in appendix B of this part, collect sulfur dioxide and oxygen (or carbon(Subpart CCCC

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- 2013) Page 61 of 163 dioxide) data concurrently (or within a 30

- to 60

- minute period) with both the CEMS and the test methods specified in paragraphs (s)(1)(i) and (ii) of this section. (i) For sulfur dioxide, EPA Reference Method 6 or 6C, or as an alternative ANSI/ASME PTC 1 9.10

- 1981 (incorporated by reference, see § 60.17) must be used. (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10

- 1981 (incorporated by reference, see § 60.17), must be used. (2) The span value of the CEMS at the inlet to the sulfur dioxide control device must be 125 percent of the maximum estimated hourly potential sulfur dioxide emissions of the unit subject to this rule. The span value of the CEMS at the outlet of the sulfur dioxide control devi ce must be 50 percent of the maximum estimated hourly potential sulfur dioxide emissions of the unit subject to this rule. (3) Conduct accuracy determinations quarterly and calibration drift tests daily in accordance with procedure 1 in appendix F of this part. (t) For facilities using a CEMS to demonstrate continuous compliance with the nitrogen oxides emission limit, compliance with the nitrogen oxides emission limit(Subpart CCCC

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- 2013) Page 62 of 163 may be demonstrated by using the CEMS specified in § 60.2165 to measure nitrogen oxides. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. You must calculate a 30

- day rolling average of the 1

- hour arithmetic average emission concentrations, includ ing CEMS data during startup and shutdown as defined in this subpart, using Equation e quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A

- 7 of this part. The nitrogen oxides CEMS must be operated according to performanc e specification 2 in appendix B of this part and must follow the procedures and methods specified in paragraphs (t)(1) through (5) of this section. (1) During each relative accuracy test run of the CEMS required by performance specification 2 of appendix B of this part, collect nitrogen oxides and oxygen (or carbon dioxide) data concurrently (or within a 30

- to 60

- minute period) with both the CEMS and the test methods specified in paragraphs (t)(1)(i) and (ii) of this section. (i) For nitrogen oxides, EPA R eference Method 7 or 7E at 40 CFR part 60, appendix A

- 4 must be used. (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B at 40 CFR part 60, appendix A

- 3, or as an(Subpart CCCC

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- 2013) Page 63 of 163 alternative ANSI/ASME PTC 19

- 10.1981 (incorporated by reference, see § 60.17) , as applicable, must be used. (2) The span value of the continuous emission monitoring system must be 125 percent of the maximum estimated hourly potential nitrogen oxide emissions of the unit. (3) Conduct accuracy determinations quarterly and calibration drift tests daily in accordance with procedure 1 in appendix F of this part. (4) The owner or operator of an affected facility may request that compliance with the nitrogen oxides emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7 percent oxygen. If carbon dioxide is selected for use in diluent corrections, the relationship between oxygen and carbon dioxide levels must be established during the initial performance test according to the procedures and methods spec ified in paragraphs (t)(4)(i) through (t)(4)(iv) of this section. This relationship may be re

- established during performance compliance tests. (i) The fuel factor equation in Method 3B must be used to determine the relationship between oxygen and carbon di oxide at a sampling location. Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10

- 1981 (incorporated by(Subpart CCCC

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- 2013) Page 64 of 163 reference, see § 60.17), as applicable, must be used to determine the oxygen concentration at the same location as the carbon dioxide monitor. (ii ) Samples must be taken for at least 30 minutes in each hour. (iii) Each sample must represent a 1

- hour average. (iv) A minimum of three runs must be performed. (u) For facilities using a CEMS to demonstrate continuous compliance with any of the emission limits of this subpart, you must complete the following: (1) Demonstrate compliance with the appropriate emission limit(s) using a 30

- day rolling average of 1

- hour arithmetic average emission concentrations, including CEMS data during startup and shutdown as defined in this subpart, calculated using Equation e quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A

- 7 of this part. CEMS data during startup and shutdown, as defined in the subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. (2) Operate all CEMS in accordance with the applicable procedures under appendices B and F of this part. (v) Use of the bypass stack at any time is an emissions standards deviation for particulate matter, HCl, Pb, Cd, Hg, NO X , SO 2 , and dioxin/furans.(Subpart CCCC

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- 2013) Page 65 of 163 (w) For energy recovery units with a design heat input capacity of 100 MMBtu per hour or greater that do not use a carbon monoxide CEMS, you must install, operate, and maintain a oxygen analyzer system as defined in § 60.2265 according to the procedures in paragraphs (w)(1) through (4) of this section. (1) The oxygen analyzer system must be installed by the initial performance test date specified in § 60. 2675 2 140
. (2) You must operate the oxygen trim system within compliance with paragraph (w)(3) of this se ction at all times. (3) You must maintain the oxygen level such that the 30

- day rolling average that is established as the operating limit for oxygen is not below the lowest hourly average oxygen concentration measured during the most recent CO performance test. (4) You must calculate and record a 30

- day rolling average oxygen concentration using Equation e quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 of Appendix A

7 of this part. (x) For energy recovery units with annual average heat input rat es greater than or equal to 250 MMBtu/hour and
waste
- burning kilns, you must install, calibrate, maintain,(Subpart CCCC

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- 2013) Page 66 of 163 and operate a PM CPMS and record the output of the system as specified in paragraphs (x)(1) through (x) (8) of this section. For other energy recovery units, you may elect to use PM CPMS operated in accordance with this section. PM CPMS are suitable in lieu of using other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure). (1) Install, calibrate, opera te, and maintain your PM CPMS according to the procedures in your approved site

specific monitoring plan developed in accordance with § 60.2145 paragraphs (l) and (x)(1)(i) through (x)(1) (iii) of this section. (i) The operating principle of the PM CPMS must be based on in

- stack or extractive light scatter, light scintillation, beta attenuation, or mass accumulation detection of the exhaust gas or representative sample. The reportable measurement output from the PM CPMS must be expressed as milliamps. (ii) The PM CPMS must have a cycle time (i.e., period required to complete sampling, measurement, and reporting for each measurement) no longer than 60 minutes. (iii) The PM CPMS must be capable of detecting and responding to particulate matter concentration incre ments s of no greater than 0.5 mg/actual cubic meter.(Subpart CCCC

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- 2013) Page 67 of 163 (2) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, you must adjust the site

- specific operating limit in accordance with the r esults of the performance test according to the procedures specified in § 60.2110. (3) Collect PM CPMS hourly average output data for all energy recovery unit or waste

- burning kiln operating hours. Express the PM CPMS output as milliamps. (4) Calculate the arithmetic 30

- day rolling average of all of the hourly average PM CPMS output collected during all energy recovery unit or waste

- burning kiln operating hours data (milliamps or their digital equivalent ). (5) You must collect data using the PM CPMS at all times the energy recovery unit or waste

- burning kiln is operating and at the intervals specified in paragraph (x)(1)(ii) of this section, except for periods of monitoring system malfunctions, repairs associated with monitoring system malfunctions, required monitoring system quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments), and any scheduled maintenance as defined in your site

- specific monitoring plan.(Subpart CCCC

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- 2013) Page 68 of 163 (6) You must use all t he data collected during all energy recovery unit or waste

- burning kiln operating hours in assessing the compliance with your operating limit except: (i) Any data collected during monitoring system malfunctions, repairs associated with monitoring system

ma lfunctions, or required monitoring system quality assurance or quality control activities conducted during monitoring system malfunctions are not used in calculations (report any such periods in your annual deviation report); (ii) Any data collected during periods when the monitoring system is out of control as specified in your site

- specific monitoring plan, repairs associated with periods when the monitoring system is out of control, or required monitoring system quality assurance or quality control activ ities conducted during out

- of

- control periods are not used in calculations (report emissions or operating levels and report any such periods in your annual deviation report); (iii) Any PM CPMS data recorded during periods of CEMS data during startup and sh utdown, as defined in this subpart. (7) You must record and make available upon request results of PM CPMS system performance audits, as well as(Subpart CCCC

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- 2013) Page 69 of 163 the dates and duration of periods from when the PM CPMS is out of control until completion of the corrective ac tions necessary to return the PM CPMS to operation consistent with your site

- specific monitoring plan. (8) For any deviation of the 30

- day rolling average PM CPMS average value from the established operating parameter limit, you must: (i) Within 48 hours o f the deviation, visually inspect the air pollution control device; (ii) If inspection of the air pollution control device identifies the cause of the deviation, take corrective action as soon as possible and return the PM CPMS measurement to within the es tablished value; and (iii) Within 30 days of the deviation or at the time of the annual compliance test, whichever comes first, conduct a PM emissions compliance test to determine compliance with the PM emissions limit and to verify. Within 45 days of the deviation, you must re

- establish the CPMS operating limit. You are not required to conduct additional testing for any deviations that occur between the time of the original deviation and the PM emissions compliance test required under this paragraph. (iv) PM CPMS deviations leading to more than four required performance tests in a 12

- month process operating(Subpart CCCC

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- 2013) Page 70 of 163 period (rolling monthly) constitute a violation of this subpart. (y) When there is an alkali bypass and/or an in

- line coal mill that exhaust emission s through a separate stack (s) , the combined emissions are subject to the emission limit s applicable to waste

- burning kilns
. To determine the kiln

- specific emission limit for demonstrating compliance , you must : (1) C alculate a kiln

- specific emission limit us ing

e quation 6 : C ks = ((Emission limit x (Q ab +Q cm +Q ks ))

– (Q ab x C ab )

– (Q cm x C cm ))/Q ks (Eq. 6 ) Where:
C ks = Kiln stack concentration (ppmvd, mg/dscm, ng/dscm, depending on pollutant. Each corrected to 7% O 2 .) Q ab = Alkali bypass flow rate (volume/hr)
C ab = Alkali bypass concentration (ppmvd, mg/dscm, ng/dscm, depending on pollutant. Each corrected to 7% O 2 .) Q cm = In
- line c oal mill flow rate (volume/hr)
C cm = In
- line c oal mill concentration (ppmvd, mg/dscm, ng/dscm, depending on pollutant. Each corrected to 7% O 2 .) Q ks = Kiln stack flow rate (volume/hr) (2) Particulate matter concentration must be measured downstream of the in

- line coal mill. All other p ollutant(Subpart CCCC

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c oncentration s must be measur ed either upstream or downstream of the in

- line coal mill. § 60.2150 By what date must I conduct the annual performance test? You must conduct annual performance tests between 11 and 13 months of the previous performance test. § 60.2151 By what date must I conduct the annual air pollution control device inspection? On an annual basis (no more than 12 months following the previous annual air pollution control device inspection), you must complete the air pollution control device inspection as described in § 60.2141. § 60.2155 May I conduct performance testing less often? (a) You must conduct annual performance tests according to the schedule specified in § 60.2150, with the following exceptions: (1) You may conduct a repeat performance test at any time to e stablish new values for the operating limits to apply from that point forward, as specified in § 60.2160. The Administrator may request a repeat performance test at any time. (2) You must repeat the performance test within 60 days of a process change, as d efined in § 60.2265.(Subpart CCCC

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- 2013) Page 72 of 163 (3) If the initial or any subsequent performance test for any pollutant in table 1 or tables 5 through 8 of this subpart, as applicable, demonstrates that the emission level for the pollutant is no greater than the emission level speci fied in paragraph (a)(3)(i) or (a)(3)(ii) of this section, as applicable, and you are not required to conduct a performance test for the pollutant in response to a request by the Administrator in paragraph (a)(1) of this section or a process change in para graph (a)(2) of this section, you may elect to skip conducting a performance test for the pollutant for the next 2 years. You must conduct a performance test for the pollutant during the third year and no more than 37 months following the previous performa nce test for the pollutant. For cadmium and lead, both cadmium and lead must be emitted at emission levels no greater than their respective emission levels specified in paragraph (a)(3)(i) of this section for you to qualify for less frequent testing under this paragraph. (i) For particulate matter, hydrogen chloride, mercury, nitrogen oxides, sulfur dioxide, cadmium, lead and dioxins/furans, the emission level equal to 75 percent of the applicable emission limit in table 1 or tables 5 through 8 of this subp art, as applicable, to this subpart.(Subpart CCCC

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- 2013) Page 73 of 163 (ii) For fugitive emissions, visible emissions (of combustion ash from the ash conveying system) for 2 percent of the time during each of the three 1

- hour observations periods. (4) If you are conducting less frequent te sting for a pollutant as provided in paragraph (a)(3) of this section and a subsequent performance test for the pollutant indicates that your CISWI unit does not meet the emission level specified in paragraph (a)(3)(i) or (a)(3)(ii) of this section, as app licable, you must conduct annual performance tests for the pollutant according to the schedule specified in paragraph (a) of this section until you qualify for less frequent testing for the pollutant as specified in paragraph (a)(3) of this section. (b) [R eserved] § 60.2160 May I conduct a repeat performance test to establish new operating limits? (a) Yes. You may conduct a repeat performance test at any time to establish new values for the operating limits. The Administrator may request a repeat performanc e test at any time. (b) You must repeat the performance test if your feed stream is different than the feed streams used during any performance test used to demonstrate compliance.(Subpart CCCC

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- 2013) Page 74 of 163 Monitoring § 60.2165 What monitoring equipment must I install and what parameters must I monitor? (a) If you are using a wet scrubber to comply with the emission limitation under § 60.2105, you must install, calibrate (to manufacturers' specifications), maintain, and operate devices (or establish methods) for monitoring the

v alue of the operating parameters used to determine compliance with the operating limits listed in table 2 of this subpart. These devices (or methods) must measure and record the values for these operating parameters at the frequencies indicated in table 2 of this subpart at all times except as specified in § 60.2170(a). (b) If you use a fabric filter to comply with the requirements of this subpart, you must install, calibrate, maintain, and continuously operate a bag leak detection system as specified in pa ragraphs (b)(1) through (8) of this section. (1) You must install and operate a bag leak detection system for each exhaust stack of the fabric filter. (2) Each bag leak detection system must be installed, operated, calibrated, and maintained in a manner co nsistent with the manufacturer's written specifications and recommendations.(Subpart CCCC

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- 2013) Page 75 of 163 (3) The bag leak detection system must be certified by the manufacturer to be capable of detecting particulate matter emissions at concentrations of 10 milligrams per actual cubic meter or less. (4) The bag leak detection system sensor must provide output of relative or absolute particulate matter loadings. (5) The bag leak detection system must be equipped with a device to continuously record the output signal from the sensor. (6) The bag leak detection system must be equipped with an alarm system that will alert automatically an operator when an increase in relative particulate matter emissions over a preset level is detected. The alarm must be located where it is observed easily by plant operating personnel. (7) For positive pressure fabric filter systems, a bag leak detection system must be installed in each baghouse compartment or cell. For negative pressure or induced air fabric filters, the bag leak detector must be installed downstream of the fabric filter. (8) Where multiple detectors are required, the system's instrumentation and alarm may be shared among detectors.(Subpart CCCC

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- 2013) Page 76 of 163 (c) If you are using something other than a wet scrubber, activated carbon, selective non

- catalytic reduction, an electrostatic precipitator, or a dry scrubber to comply with the emission limitations under § 60.2105, you must install, calibrate (to the manufacturers' specifications), maintain, and operate the equipment necessary to monitor compliance with the site

- specific operating limits established using the procedures in § 60.2115. (d) If you use activated carbon injection to comply with the emission limitations in this subpart, you must measure the minimum mercury sorbent flow rate once per hour. (e) If you us e selective noncatalytic reduction to comply with the emission limitations, you must complete the following: (1) Following the date on which the initial performance test is completed or is required to be completed under § 60.2125, whichever date comes firs t, ensure that the affected facility does not operate above the maximum charge rate, or below the minimum secondary chamber temperature (if applicable to your CISWI unit) or the minimum reagent flow rate measured as 3

- hour block averages at all times.(Subpart CCCC

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- 2013) Page 77 of 163 (2) Operation of the affected facility above the maximum charge rate, below the minimum secondary chamber temperature and below the minimum reagent flow rate simultaneously constitute a violation of the nitrogen oxides emissions limit. (f) If you use an electr ostatic precipitator to comply with the emission limits of this subpart, you must monitor the secondary power to the electrostatic precipitator collection plates and maintain the 3

- hour block averages at or above the operating limits established during the mercury or particulate matter performance test. (g) For waste

- burning kilns not equipped with a wet scrubber or dry scrubber, in place of hydrogen chloride testing with EPA Method 321 at 40 CFR part 63, appendix A, an owner or operator must install, calib rate, maintain, and operate a CEMS for monitoring hydrogen chloride emissions discharged to the atmosphere and record the output of the system. To demonstrate continuous compliance with the hydrogen chloride emissions limit for units other than
waste
- burni ng kilns not equipped with a wet scrubber or dry scrubber, a facility may substitute use of a hydrogen chloride CEMS for conducting the hydrogen chloride annual performance test, monitoring the minimum hydrogen chloride(Subpart CCCC

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- 2013) Page 78 of 163 sorbent flow rate, monitoring the mi nimum scrubber liquor pH, and monitoring minimum injection rate. (h) To demonstrate continuous compliance with the particulate matter emissions limit, a facility may substitute use of a particulate matter CEMS for conducting the PM annual performance test and using other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure). (i) To demonstrate continuous compliance with the dioxin/furan emissions limit, a facility may substitute use of a continuous automated sampling system for the dioxin/furan annual performance test. You must record the output of the system and analyze the sample according to EPA Method 23 at 40 CFR part 60, appendix A

- 7 of this part. This option to use a continuous automated sampling system takes effect on the date a final performance specification applicable to dioxin/furan from continuous monitors is published in the F EDERAL R EGISTER . The owner or operator who elects to continuously sample dioxin/furan emissions instead of sampling and tes ting using EPA Method 23 at 40 CFR part 60, appendix A

- 7 must install, calibrate, maintain, and operate a continuous automated sampling system and must comply with the requirements specified in § 60.58b(p) and (q). A facility may substitute continuous(Subpart CCCC

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- 2013) Page 79 of 163 diox in/furan monitoring for the minimum sorbent flow rate, if activated carbon sorbent injection is used solely for compliance with the dioxin/furan emission limit. (j) To demonstrate continuous compliance with the mercury emissions limit, a facility may subst itute use of a continuous automated sampling system for the mercury annual performance test. You must record the output of the system and analyze the sample at set intervals using any suitable determinative technique that can meet performance specification 12B. The owner or operator who elects to continuously sample mercury emissions instead of sampling and testing using EPA Reference Method 29 or 30B at 40 CFR part 60, appendix A

- 8 of this part, ASTM D6784

- 02 (Reapproved 2008) (incorporated by reference, s ee § 60.17), or an approved alternative method for measuring mercury emissions, must install, calibrate, maintain, and operate a continuous automated sampling system and must comply with performance specification 12A and quality assurance procedure 5, as w ell as the requirements specified in § 60.58b(p) and (q). A facility may substitute continuous mercury monitoring for the minimum sorbent flow rate, if activated carbon sorbent injection is used solely for compliance with the mercury emission limit.(Subpart CCCC

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- 2013) Page 80 of 163 (k) To demonstrate continuous compliance with the nitrogen oxides emissions limit, a facility may substitute use of a CEMS for the nitrogen oxides annual performance test to demonstrate compliance with the nitrogen oxides emissions limits and monitoring the char ge rate, secondary chamber temperature, and reagent flow for selective noncatalytic reduction, if applicable. (1) Install, calibrate, maintain, and operate a CEMS for measuring nitrogen oxides emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 2 of appendix B of this part, the quality assurance procedure one of appendix F of this part and the procedures under § 60.13 must be followed for installation, evaluation, and operation of the CEMS. (2) Following the date that the initial performance test for nitrogen oxides is completed or is required to be completed under § 60.2125, compliance with the emission limit for nitrogen oxides required under § 60.52b(d) must be determined based on th e 30

- day rolling average of the hourly emission concentrations using CEMS outlet data. The
1

- hour arithmetic averages must be expressed in parts per million by volume corrected to 7 percent oxygen (dry basis) and used to calculate the 30

- day rolling averag e(Subpart CCCC

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- 2013) Page 81 of 163 concentrations. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. The 1

- hour arithmetic averages must be calculated using the data points required under § 6 0.13(e)(2). (l) To demonstrate continuous compliance with the sulfur dioxide emissions limit, a facility may substitute use of a continuous automated sampling system for the sulfur dioxide annual performance test to demonstrate compliance with the sulfur d ioxide emissions limits. (1) Install, calibrate, maintain, and operate a CEMS for measuring sulfur dioxide emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 2 of appendix B of this part, the quality assurance requirements of procedure one of appendix F of this part and procedures under § 60.13 must be followed for installation, evaluation, and operation of the CEMS. (2) Following the date that the initial performance test for sulfur dioxide is completed or is required to be completed under § 60.2125, compliance with the sulfur dioxide emission limit may be determined based on the 30

- day rolling average of the hourly arithmetic average emission concentrations using CEMS outlet data. Th e 1

- hour(Subpart CCCC

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- 2013) Page 82 of 163 arithmetic averages must be expressed in parts per million corrected to 7 percent oxygen (dry basis) and used to calculate the 30

- day rolling average emission concentrations. CEMS data during startup and shutdown, as defined in this subpart, are n ot corrected to 7 percent oxygen, and are measured at stack oxygen content. The 1

- hour arithmetic averages must be calculated using the data points required under § 60.13(e)(2). (m) For energy recovery units over 10 MMBtu/hr but less than 250 MMBtu/hr annual average heat input rates that do not use a wet scrubber, fabric filter with bag leak detection system, or particulate matter CEMS, you must install, operate, certify, and main tain a continuous opacity monitoring system according to the procedures in paragraphs (m)(1) through (5) of this section by the compliance date specified in § 60.2105. Energy recovery units that use a CEMS to demonstrate initial and continuing compliance a ccording to the procedures in § 60.2165(n) are not required to install a continuous opacity monitoring system and must perform the annual performance tests for the opacity consistent with § 60.2145(f). (1) Install, operate, and maintain each continuous
opa city monitoring system according to performance specification 1 of 40 CFR part 60, appendix B.(Subpart CCCC

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- 2013) Page 83 of 163 (2) Conduct a performance evaluation of each continuous opacity monitoring system according to the requirements in § 60.13 and according to PS

- 1 of 40 CFR part 6 0, appendix B. (3) As specified in § 60.13(e)(1), each continuous opacity monitoring system must complete a minimum of one cycle of sampling and analyzing for each successive 10

- second period and one cycle of data recording for each successive 6

- minute per iod. (4) Reduce the continuous opacity monitoring system data as specified in § 60.13(h)(1). (5) Determine and record all the 6

- minute averages (and 1

- hour block averages as applicable) collected. (n) For coal and liquid/gas energy recovery units, incinera tors, and small remote incinerators, an owner or operator may elect to install, calibrate, maintain, and operate a CEMS for monitoring particulate matter emissions discharged to the atmosphere and record the output of the system. The owner or operator of a n affected facility who continuously monitors particulate matter emissions instead of conducting performance testing using EPA Method 5 at 40 CFR part 60, appendix A

- 3 or, as applicable, monitor with a particulate matter CPMS according to paragraph (r) of this section, must install, calibrate, maintain, and operate a(Subpart CCCC

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- 2013) Page 84 of 163 CEMS and must comply with the requirements specified in paragraphs (n)(1) through (13) of this section. (1) Notify the Administrator 1 month before starting use of the system. (2) Notify the Ad ministrator 1 month before stopping use of the system. (3) The monitor must be installed, evaluated, and operated in accordance with the requirements of performance specification 11 of appendix B of this part and quality assurance requirements of procedure two of appendix F of this part and § 60.13. Use Method 5 or Method 5I of Appendix A of this part for the PM CEMS correlation testing. (4) The initial performance evaluation must be completed no later than 180 days after the date of initial startup of the affected facility, as specified under § 60.2125 or within 180 days of notification to the Administrator of use of the continuous monitoring system if the owner or operator was previously determining compliance by Method 5 performance tests, whichever is la ter. (5) The owner or operator of an affected facility may request that compliance with the particulate matter emission limit be determined using carbon dioxide measurements corrected to an equivalent of 7 percent(Subpart CCCC

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- 2013) Page 85 of 163 oxygen. The relationship between oxygen an d carbon dioxide levels for the affected facility must be established according to the procedures and methods specified in § 60.2145(s)(5)(i) through (s)(5)(iv). (6) The owner or operator of an affected facility must conduct an initial performance test for particulate matter emissions as required under § 60.2125. Compliance with the particulate matter emission limit, if PM CEMS are elected for demonstrating compliance, must be determined by using the CEMS specified in this paragraph (n) to measure particula te matter. You must calculate a 30

- day rolling average of 1

- hour arithmetic average emission concentrations, including CEMS data during startup and shutdown, as defined in this subpart, using e E quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A

- 7. (7) Compliance with the particulate matter emission limit must be determined based on the 30

- day rolling average calculated using Equation e quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 at 40 CFR part 60, appendix A
- 7 from the 1

- hour arithmetic average CEMS outlet data.(Subpart CCCC

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- 2013) Page 86 of 163 (8) At a minimum, valid continuous monitoring system hourly averages must be obtained as specified in § 60.2170(e). (9) The 1

- hour arithmetic averages required under paragraph (n)(7) of this section must be expressed in milligrams per dry standard cubic meter corrected to 7 percent oxygen (dry basis) and must be used to calculate the 30

- day rolling average emission concentrations. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. The 1

- hour arithmetic averages must be calculated using the data points required under § 60.13(e)(2). (10) All valid CEMS data must be used in calculating average emission concen trations even if the minimum CEMS data requirements of paragraph (n)(8) of this section are
not met. (11) The CEMS must be operated according to performance specification 11 in appendix B of this part. (12) During each relative accuracy test run of the
CEM S required by performance specification 11 in appendix B of this part, particulate matter and oxygen (or carbon dioxide) data must be collected concurrently (or within a(Subpart CCCC

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- 2013) Page 87 of 163 30

- to 60

- minute period) by both the CEMS and the following test methods. (i) For part iculate matter, EPA Reference Method 5 must be used. (ii) For oxygen (or carbon dioxide), EPA Reference Method 3A or 3B, as applicable, must be used. (13) Quarterly accuracy determinations and daily calibration drift tests must be performed in accordance

w ith procedure 2 in appendix F of this part. (o) To demonstrate continuous compliance with the carbon monoxide emissions limit, you must may substitute

use of a continuous automated sampling system for the carbon monoxide annual performance test
. (1) Install, calibrate, maintain, and operate a CEMS for measuring carbon monoxide emissions discharged to the atmosphere and record the output of the system. The requirements under performance specification 4B of appendix B of this part, the quality assur ance procedure 1 of appendix F of this part and the procedures under § 60.13 must be followed for installation, evaluation, and operation of the CEMS. (2) Following the date that the initial performance test for carbon monoxide is completed or is required to be completed under § 60.2140, compliance with the carbon(Subpart CCCC

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- 2013) Page 88 of 163 monoxide emission limit may be determined based on the 30

- day rolling average of the hourly arithmetic average emission concentrations, including CEMS data during startup and shutdown as defined i n this subpart, using CEMS outlet data. Except for CEMS data during startup and shutdown, as defined in this subpart, the 1

- hour arithmetic averages must be expressed in parts per million corrected to 7 percent oxygen (dry basis) and used to calculate the 30

- day rolling average emission concentrations. CEMS data during startup and shutdown, as defined in this subpart, are not corrected to 7 percent oxygen, and are measured at stack oxygen content. The 1

- hour arithmetic averages must be calculated using the data points required under § 60.13(e)(2). (p) The owner/operator of an affected source with a bypass stack shall install, calibrate (to manufacturers' specifications), maintain, and operate a device or method for measuring the use of the bypass stack inclu ding date, time and duration. (q) For energy recovery units with a design heat input capacity of 100 MMBtu per hour or greater that do not use a carbon monoxide CEMS, you must install, operate, and maintain a oxygen analyzer system as defined in § 60.2265(Subpart CCCC

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- 2013) Page 89 of 163 according to the procedures in paragraphs (q)(1) through (q) (4) of this section. (1) The oxygen analyzer system must be installed by the initial performance test date specified in § 60. 2675 2 140
. (2) You must operate the oxygen trim system within compliance with paragraph (q)(3) of this section at all times. (3) You must maintain the oxygen level such that the 30

- day rolling average that is established as the operating limit for oxygen according to paragraph (q)(4) or o f this section is not below the lowest hourly average oxygen concentration measured during the most recent CO performance test. (4) You must calculate and record a 30

- day rolling average oxygen concentration using Equation e quation 19

- 19 in section 12.4.1 of EPA Reference Method 19 of Appendix A
7 of this part. (r) For energy recovery units with annual average heat input rates greater than or equal to 250 MMBtu/hour and
waste
- burning kilns, you must install, calibrate, maintain, and operate a PM CPMS and record the output of the system as specif ied in paragraphs (r)(1) through (8) of this section. If you elect to use a particulate matter CEMS as(Subpart CCCC

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- 2013) Page 90 of 163 specified in paragraph (n) of this section, you are not required to use a PM CPMS to monitor particulate matter emissions. For other energy recovery unit s, you may elect to use PM CPMS operated in accordance with this section. PM CPMS are suitable in lieu of using other CMS for monitoring PM compliance (e.g., bag leak detectors, ESP secondary power, PM scrubber pressure). (1) Install, calibrate, operate, a nd maintain your PM CPMS according to the procedures in your approved site

specific monitoring plan developed in accordance with § 60.2145(l) and (r)(1)(i) through (iii) of this section. (i) The operating principle of the PM CPMS must be based on in

- stack or extractive light scatter, light scintillation, beta attenuation, or mass accumulation detection of PM in the exhaust gas or representative sample. The reportable measurement output from the PM CPMS must be expressed as milliamps or a digital signal equi valent
. (ii) The PM CPMS must have a cycle time (i.e., period required to complete sampling, measurement, and reporting for each measurement) no longer than 60 minutes. (iii) The PM CPMS must be capable of detecting and responding to particulate matter concentration increments s(Subpart CCCC

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- 2013) Page 91 of 163 of no greater than as low as no greater than 0.5 mg/actual cubic meter. (2) During the initial performance test or any such subsequent performance test that demonstrates compliance with the PM limit, you must adjust the site

- specif ic operating limit in accordance with the results of the performance test according to the procedures specified in § 60.2110. (3) Collect PM CPMS hourly average output data for all energy recovery unit or waste

- burning kiln operating hours. Express the PM CPMS output as milliamps or the digital signal equivalent
. (4) Calculate the arithmetic 30

- day rolling average of all of the hourly average PM CPMS output collected during all energy recovery unit or waste

- burning kiln operating hours data (milliamps or di gital bits ). (5) You must collect data using the PM CPMS at all times the energy recovery unit or waste

- burning kiln is operating and at the intervals specified in paragraph (r)(1)(ii) of this section, except for periods of monitoring system malfunctions, repairs associated with monitoring system malfunctions, required monitoring system quality assurance or quality control activities (including, as applicable, calibration checks and required zero and(Subpart CCCC

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- 2013) Page 92 of 163 span adjustments), and any scheduled maintenance as defin ed in your site

- specific monitoring plan. (6) You must use all the data collected during all energy recovery unit or waste

- burning kiln operating hours in assessing the compliance with your operating limit except: (i) Any data collected during monitoring s ystem malfunctions, repairs associated with monitoring system malfunctions, or required monitoring system quality assurance or quality control activities conducted during monitoring system malfunctions are not used in calculations (report any such periods in your annual deviation report); (ii) Any data collected during periods when the monitoring system is out of control as specified in your site

- specific monitoring plan, repairs associated with periods when the monitoring system is out of control, or requi red monitoring system quality assurance or quality control activities conducted during out

- of

- control periods are not used in calculations (report emissions or operating levels and report any such periods in your annual deviation report); (iii) Any PM CPMS data recorded during periods of CEMS data during startup and shutdown, as defined in this subpart.(Subpart CCCC

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- 2013) Page 93 of 163 (7) You must record and make available upon request results of PM CPMS system performance audits, as well as the dates and duration of periods from when the PM CPMS is out of control until completion of the corrective actions necessary to return the PM CPMS to operation consistent with your site

- specific monitoring plan. (8) For any deviation of the 30

- day rolling average PM CPMS average value from the establ ished operating parameter limit, you must: (i) Within 48 hours of the deviation, visually inspect the air pollution control device; (ii) If inspection of the air pollution control device identifies the cause of the deviation, take corrective action as soon as possible and return the PM CPMS measurement to within the established value; and (iii) Within 30 days of the deviation or at the time of the annual compliance test, whichever comes first, conduct a PM emissions compliance test to determine compliance w ith the PM emissions limit and to verify the
op eration of the control device(s) . Within 45 days of the deviation, you must re

- establish the CPMS operating limit. You are not required to conduct additional testing for any deviations that occur between the t ime of the original(Subpart CCCC

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- 2013) Page 94 of 163 deviation and the PM emissions compliance test required under this paragraph. (iv) PM CPMS deviations leading to more than four required performance tests in a 12

- month process operating period (rolling monthly) constitute a violation o f this subpart. (s) If you use a dry scrubber to comply with the emission limits of this subpart, you must monitor the injection rate of each sorbent and maintain the 3

- hour block averages at or above the operating limits established during the hydrogen ch loride performance test. § 60.2170 Is there a minimum amount of monitoring data I must obtain? For each continuous monitoring system required or optionally allowed under § 60.2165, you must collect data according to this section: (a) You must operate the m onitoring system and collect data at all required intervals at all times compliance is required except for periods of monitoring system malfunctions or out

- of

- control periods, repairs associated with monitoring system malfunctions or out

- of

- control periods (as specified in 60.2210(o) of this part), and required monitoring system quality assurance or quality control activities (including, as applicable, calibration(Subpart CCCC

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- 2013) Page 95 of 163 checks and required zero and span adjustments). A monitoring system malfunction is any sudden, infrequent, not reasonably preventable failure of the monitoring system to provide valid data. Monitoring system failures that are caused in part by poor maintenance or careless operation are not malfunctions. You are required to effect monitoring system repairs in response to monitoring system malfunctions or out

- of

- control periods and to return the monitoring system to operation as expeditiously as practicable. (b) You may not use data recorded during monitoring system malfunctions or out

- of

- control peri ods, repairs associated with monitoring system malfunctions or out

- of

control periods, or required monitoring system quality assurance or control activities in calculations used to report emissions or operating levels. You must use all the data collected d uring all other periods , including data normalized for above scale readings, in assessing the operation of the control device and associated control system. (c) Except for periods of monitoring system malfunctions or out

- of

- control periods, repairs associa ted with monitoring system malfunctions or out

- of

- control periods, and required monitoring system quality assurance(Subpart CCCC

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- 2013) Page 96 of 163 or quality control activities including, as applicable, calibration checks and required zero and span adjustments, failure to collect requir ed data is a deviation of the monitoring requirements. Recordkeeping and Reporting § 60.2175 What records must I keep? You must maintain the items (as applicable) as specified in paragraphs (a), (b), and (e) through (x) of this section for a period of at least 5 years: (a) Calendar date of each record. (b) Records of the data described in paragraphs (b)(1) through (6) of this section: (1) The CISWI unit charge dates, times, weights, and hourly charge rates. (2) Liquor flow rate to the wet scrubber inlet ev ery 15 minutes of operation, as applicable. (3) Pressure drop across the wet scrubber system every 15 minutes of operation or amperage to the wet scrubber every 15 minutes of operation, as applicable. (4) Liquor pH as introduced to the wet scrubber every
1 5 minutes of operation, as applicable. (5) For affected CISWI units that establish operating limits for controls other than wet scrubbers under § 60.2110(d) through (g) or § 60.2115, you must maintain data(Subpart CCCC

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- 2013) Page 97 of 163 collected for all operating parameters used to det ermine compliance with the operating limits. For energy recovery units using activated carbon injection or a dry scrubber, you must also maintain records of the load fraction and corresponding sorbent injection rate records. (6) If a fabric filter is used to comply with the emission limitations, you must record the date, time, and duration of each alarm and the time corrective action was initiated and completed, and a brief description of the cause of the alarm and the corrective action taken. You must also record the percent of operating time during each 6

- month period that the alarm sounds, calculated as specified in § 60.2110(c). (c)

— (d) [Reserved] (e) Identification of calendar dates and times for which data show a deviation from the operating limits in table 2 of this subpart or a deviation from other operating limits established under § 60.2110(d) through (g) or § 60.2115 with a description of the deviations, reasons for such deviations, and a description of corrective actions taken. (f) The results of the initial, annual, and any subsequent performance tests conducted to determine compliance with the emission limits and/or to establish(Subpart CCCC

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- 2013) Page 98 of 163 operating limits, as applicable. Retain a copy of the complete test report including calculations. (g) All documentatio n produced as a result of the siting requirements of § § 60.2045 and 60.2050. (h) Records showing the names of CISWI unit operators who have completed review of the information in § 60.2095(a) as required by § 60.2095(b), including the date of the initial r eview and all subsequent annual reviews. (i) Records showing the names of the CISWI operators who have completed the operator training requirements under § 60.2070, met the criteria for qualification under § 60.2080, and maintained or renewed their qualifi cation under § 60.2085 or § 60.2090. Records must include documentation of training, the dates of the initial and refresher training, and the dates of their qualification and all subsequent renewals of such qualifications. (j) For each qualified operator, the phone and/or pager number at which they can be reached during operating hours. (k) Records of calibration of any monitoring devices as required under § 60.2165. (l) Equipment vendor specifications and related operation and maintenance requirements for the incinerator, emission controls, and monitoring equipment.(Subpart CCCC

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- 2013) Page 99 of 163 (m) The information listed in § 60.2095(a). (n) On a daily basis, keep a log of the quantity of waste burned and the types of waste burned (always required). (o) Maintain records of the annual a ir pollution control device inspections that are required for each CISWI unit subject to the emissions limits in table 1 of this subpart or tables 5 through 8 of this subpart, any required maintenance, and any repairs not completed within 10 days of an ins pection or the timeframe established by the state regulatory agency. (p) For continuously monitored pollutants or parameters, you must document and keep a record of the following parameters measured using continuous monitoring systems. (1) All 6

- minute ave rage levels of opacity. (2) All 1

- hour average concentrations of sulfur dioxide emissions. (3) All 1

- hour average concentrations of nitrogen oxides emissions. (4) All 1

- hour average concentrations of carbon monoxide emissions. You must indicate which data are CEMS data during startup and shutdown.(Subpart CCCC

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- 2013) Page 100 of 163 (5) All 1

- hour average concentrations of particulate matter emissions. (6) All 1

- hour average concentrations of mercury emissions. (7) All 1

- hour average concentrations of hydrogen chloride emissions. (8) All 1

- hour average percent oxygen concentrations. (9) All 1

- hour average PM CPMS readings or particulate matter CEMS outputs. (q) Records indicating use of the bypass stack, including dates, times, and durations. (r) If you choose to stack test less frequently than annually, consistent with § 60.2155(a) through (c), you must keep annual records that document that your emissions in the previous stack test(s) were less than 75 percent of the applicable emission limit and document that there was no change in sourc e operations including fuel composition and operation of air pollution control equipment that would cause emissions of the relevant pollutant to increase within the past year. (s) Records of the occurrence and duration of each malfunction of operation ( i.e ., process equipment) or the air pollution control and monitoring equipment.(Subpart CCCC

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- 2013) Page 101 of 163 (t) Records of all required maintenance performed on the air pollution control and monitoring equipment. (u) Records of actions taken during periods of malfunction to minimize emi ssions in accordance with § 60.11(d), including corrective actions to restore malfunctioning process and air pollution control and monitoring equipment to its normal or usual manner of operation. (v) For operating units that combust non

- hazardous secondary materials that have been determined not to be solid waste pursuant to § 241.3(b)(1) of this chapter, you must keep a record which documents how the secondary material meets each of the legitimacy criteria under § 241.3(d)(1). If you combust a fuel that ha s been processed from a discarded non

- hazardous secondary material pursuant
to § 241.3(b)(4) of this chapter, you must keep records as to how the operations that produced the fuel satisfies the definition of processing in § 241.2 and each of the legitimacy criteria of § 241.3(d)(1) of this chapter. If the fuel received a non

- waste determination pursuant to the petition process submitted under § 241.3(c) of this chapter, you must keep a record that documents how the fuel satisfies the requirements of the pet ition process. For operating units that combust non

- hazardous secondary(Subpart CCCC

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- 2013) Page 102 of 163 materials as fuel per § 241.4, you must keep records documenting that the material is a listed non

- waste under § 241.4(a). (w) Records of the criteria used to establish that the unit q ualifies as a small power production facility under section 3(17)(C) of the Federal Power Act (16 U.S.C. 796(17)(C)) and that the waste material the unit is proposed to burn is homogeneous. (x) Records of the criteria used to establish that the unit qualif ies as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)) and that the waste material the unit is proposed to burn is homogeneous. § 60.2180 Where and in what format must I keep my records? All records must be av ailable onsite in either paper copy or computer
- readable format that can be printed upon request, unless an alternative format is approved by the Administrator. § 60.2185 What reports must I submit? See table 4 of this subpart for a summary of the reportin g requirements. § 60.2190 What must I submit prior to commencing construction?(Subpart CCCC

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- 2013) Page 103 of 163 You must submit a notification prior to commencing construction that includes the five items listed in paragraphs (a) through (e) of this section. (a) A statement of intent to c onstruct. (b) The anticipated date of commencement of construction. (c) All documentation produced as a result of the siting requirements of § 60.2050. (d) The waste management plan as specified in § § 60.2055 through 60.2065. (e) Anticipated date of initia l startup. § 60.2195 What information must I submit prior to initial startup? You must submit the information specified in paragraphs (a) through (e) of this section prior to initial startup. (a) The type(s) of waste to be burned. (b) The maximum design wa ste burning capacity. (c) The anticipated maximum charge rate. (d) If applicable, the petition for site

- specific operating limits under § 60.2115. (e) The anticipated date of initial startup. § 60.2200 What information must I submit following my initial performance test?(Subpart CCCC

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- 2013) Page 104 of 163 You must submit the information specified in paragraphs (a) through (c) of this section no later than 60 days following the initial performance test. All reports must be signed by the facilities manager. (a) The complete test report for t he initial performance test results obtained under § 60.2135, as applicable. (b) The values for the site

- specific operating limits established in § 60.2110 or § 60.2115. (c) If you are using a fabric filter to comply with the emission limitations, document ation that a bag leak detection system has been installed and is being operated, calibrated, and maintained as required by § 60.2165(b). § 60.2205 When must I submit my annual report? You must submit an annual report no later than 12 months following the s ubmission of the information in § 60.2200. You must submit subsequent reports no more than 12 months following the previous report. (If the unit is subject to permitting requirements under title V of the Clean Air Act, you may be required by the permit to submit these reports more frequently.) § 60.2210 What information must I include in my annual report?(Subpart CCCC

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- 2013) Page 105 of 163 The annual report required under § 60.2205 must include the ten items listed in paragraphs (a) through (j) of this section. If you have a deviation from t he operating limits or the emission limitations, you must also submit deviation reports as specified in § § 60.2215, 60.2220, and 60.2225. (a) Company name and address. (b) Statement by a responsible official, with that official's name, title, and signature , certifying the accuracy of the content of the report. (c) Date of report and beginning and ending dates of the reporting period. (d) The values for the operating limits established pursuant to § 60.2110 or § 60.2115. (e) If no deviation from any emission limitation or operating limit that applies to you has been reported, a statement that there was no deviation from the emission limitations or operating limits during the reporting period. (f) The highest recorded 3

- hour average and the lowest recorded 3

- h our average, as applicable, for each operating parameter recorded for the calendar year being reported. (g) Information recorded under § 60.2175(b)(6) and (c) through (e) for the calendar year being reported.(Subpart CCCC

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- 2013) Page 106 of 163 (h) If a performance test was conducted during the reporting period, the results of that test. For each performance test conducted during the reporting period, if any performance test is conducted, the process unit(s) tested, the pollutant(s) tested and the date that such performance test was conducted. Submit, following the procedure specified in § 60. 2235(b)(i), the performance test report no later than the date that you submit the annual report. (i) If you met the requirements of § 60.2155(a) or (b), and did not conduct a performance test during the reporting period, you must state that you met the requirements of § 60.2155(a) or (b), and, therefore, you were not required to conduct a performance test during the reporting period. (j) Documentation of periods when all qualified CISWI unit operators wer e unavailable for more than 8 hours, but less than 2 weeks. (k) If you had a malfunction during the reporting period, the compliance report must include the number, duration, and a brief description for each type of malfunction that occurred during the rep orting period and that caused or may have caused any applicable emission limitation to be exceeded. The report must also include a(Subpart CCCC

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- 2013) Page 107 of 163 description of actions taken by an owner or operator during a malfunction of an affected source to minimize emissions in acco rdance with § 60.11(d), including actions taken to correct a malfunction. (l) For each deviation from an emission or operating limitation that occurs for a CISWI unit for which you are not using a continuous monitoring system to comply with the emission or operating limitations in this subpart, the annual report must contain the following information. (1) The total operating time of the CISWI unit at which the deviation occurred during the reporting period. (2) Information on the number, duration, and cause of deviations (including unknown cause, if applicable), as applicable, and the corrective action taken. (m) If there were periods during which the continuous monitoring system, including the CEMS, was out of control as specified in paragraph (o) of this s ection, the annual report must contain the following information for each deviation from an emission or operating limitation occurring for a CISWI unit for which you are using a continuous monitoring system to comply with the emission and operating limitat ions in this subpart. (1) The date and time that each malfunction started and stopped.(Subpart CCCC

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- 2013) Page 108 of 163 (2) The date, time, and duration that each CMS was inoperative, except for zero (low

- level) and high

- level checks. (3) The date, time, and duration that each continuous monitoring system was out

- of

- control, including start and end dates and hours and descriptions of corrective actions taken. (4) The date and time that each deviation started and stopped, and whether each deviation occurred during a period of malfunction or during another period. (5) A summary of the total duration of the deviation during the reporting period, and the total duration as a percent of the total source operating time during that reporting period. (6) A breakdown of the total duration of the devi ations during the reporting period into those that are due to control equipment problems, process problems, other known causes, and other unknown causes. (7) A summary of the total duration of continuous monitoring system downtime during the reporting peri od, and the total duration of continuous monitoring system downtime as a percent of the total operating time of the CISWI unit at which the continuous monitoring system downtime occurred during that reporting period.(Subpart CCCC

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- 2013) Page 109 of 163 (8) An identification of each parameter and pollutant that was monitored at the CISWI unit. (9) A brief description of the CISWI unit. (10) A brief description of the continuous monitoring system. (11) The date of the latest continuous monitoring system certification or audit. (12) A descriptio n of any changes in continuous monitoring system, processes, or controls since the last reporting period. (n) If there were periods during which the continuous monitoring system, including the CEMS, was not out of control as specified in paragraph (o) of t his section, a statement that there were not periods during which the continuous monitoring system was out of control during the reporting period. (o) A continuous monitoring system is out of control in accordance with the procedure in 40 CFR part 60,
appe ndix F of this part, as if any of the following occur. (1) The zero (low

- level), mid

- level (if applicable), or high

- level calibration drift exceeds two times the applicable calibration drift specification in the applicable performance specification or in t he relevant standard.(Subpart CCCC

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- 2013) Page 110 of 163 (2) The continuous monitoring system fails a performance test audit ( e.g., cylinder gas audit), relative accuracy audit, relative accuracy test audit, or linearity test audit. (3) The continuous opacity monitoring system calibration d rift exceeds two times the limit in the applicable performance specification in the relevant standard. § 60.2215 What else must I report if I have a deviation from the operating limits or the emission limitations? (a) You must submit a deviation report if any recorded 3

- hour average parameter level is above the maximum operating limit or below the minimum operating limit established under this subpart, if the bag leak detection system alarm sounds for more than 5 percent of the operating time for the 6

- mont h reporting period, or if a performance test was conducted that deviated from any emission limitation. (b) The deviation report must be submitted by August 1 of that year for data collected during the first half of the calendar year (January 1 to June 30), and by February 1 of the following year for data you collected during the second half of the calendar year (July 1 to December 31). § 60.2220 What must I include in the deviation report?(Subpart CCCC

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- 2013) Page 111 of 163 In each report required under § 60.2215, for any pollutant or parameter that deviated from the emission limitations or operating limits specified in this subpart, include the six items described in paragraphs (a) through (f) of this section. (a) The calendar dates and times your unit deviated from the emission limita tions or operating limit requirements. (b) The averaged and recorded data for those dates. (c) Durations and causes of the following: (1) Each deviation from emission limitations or operating limits and your corrective actions. (2) Bypass events and your c orrective actions. (d) A copy of the operating limit monitoring data during each deviation and for any test report that documents the emission levels the process unit(s) tested, the pollutant(s) tested and the date that the performance test was conducted. Submit, following the procedure specified in § 60. 2235(b)(i), the performance test report no later than the date that you submit the deviation report . § 60.2225 What else must I report if I have a deviation from the requirement to have a qualified operator accessible?(Subpart CCCC

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- 2013) Page 112 of 163 (a) If all qualified operators are not accessible for 2 weeks or more, you must take the two actions in paragraphs (a)(1) and (2) of this section. (1) Submit a notification of the deviation within 10 days that includes the three items in paragraphs (a)(1)(i) through (iii) of this section. (i) A statement of what caused the deviation. (ii) A description of what you are doing to ensure that a qualified operator is accessible. (iii) The date when you anticipate that a qualified operator will be available. (2) Submit a status report to the Administrator every 4 weeks that includes the three items in paragraphs (a)(2)(i) through (iii) of this section. (i) A description of what you are doing to ensure that a qualified operator is accessible. (ii) The date when you anticipate that a qualified operator will be accessible. (iii) Request approval from the Administrator to continue operation of the CISWI unit. (b) If your unit was shut down by the Administrator, under the provisions of § 60.2100(b)(2), due to a failure to provide an accessible qualified operator, you must(Subpart CCCC

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- 2013) Page 113 of 163 notify the Administrator that you are resuming operation once a qualified operator is accessible. § 60.2230 Are there any other notifications or reports that I must submit? (a) Yes. Yo u must submit notifications as provided by § 60.7. (b) If you cease combusting solid waste but continue to operate, you must provide 30 days prior notice of the effective date of the waste

- to
- fuel switch, consistent with 60.2145(a). The notification must i dentify: (1) The name of the owner or operator of the CISWI unit, the location of the source, the emissions unit(s) that will cease burning solid waste, and the date of the notice; (2) The currently applicable subcategory under this subpart, and any 40 CFR part 63 subpart and subcategory that will be applicable after you cease combusting solid waste; (3) The fuel(s), non

- waste material(s) and solid waste(s) the CISWI unit is currently combusting and has combusted over the past 6 months, and the fuel(s) or n on waste materials the unit will commence combusting; (4) The date on which you became subject to the currently applicable emission limits;(Subpart CCCC

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- 2013) Page 114 of 163 (5) The date upon which you will cease combusting solid waste, and the date (if different) that you intend for any n ew requirements to become applicable ( i.e., the effective date of the waste

- to
- fuel switch), consistent with paragraphs (b)(2) and (3)of this section. § 60.2235 In what form can I submit my reports? (a) (a) Submit initial, annual and deviation reports elec tronically on or before the submittal due dates. Submit the reports to the EPA via the Compliance and Emissions Data Reporting Interface (CEDRI). (CEDRI can be accessed through the EPA’s Central Data Exchange (CDX) ( http://cdx.epa.gov/epa_home.asp ).) Use the appropriate electronic report in CEDRI for this subpart . Instead of using the electronic report in CEDRI for this subpart, you may submit an alternate electronic file format consistent with the extensible markup language (XML) schema listed on the CEDRI website ( http://www.epa.gov/ttn/chief/cedri/index.html ) , once the XML schema is available . If the reporting form specific to this subpart is not available in CEDRI at the time that the report is due, submit the report to the Administrator at the appropriate address listed in §60.4. Begin submitting reports via CEDRI no later than 9 0 days after the form becomes available in CEDRI. The reports must be submitted(Subpart CCCC

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- 2013) Page 115 of 163 by the deadlines specified in this subpart, regardless of the method in which the report is submitted. (b) Submit results of each performance test and CEMS performance evaluati on required by this subpart as follows. (1) Within 60 days after the date of completing each performance test (see §60.8), submit the results of the performance test following the procedure specified in either paragraph (b)(1)(i) or (b)(1)(ii) of this sect ion. (i) For data collected using test methods supported by the EPA’s Electronic Reporting Tool (ERT) as listed on the EPA’s ERT website ( http://www.epa.gov/ttn/chief/ert/index.html ) at the time

o f the test, submit the results of the performance test to the EPA via the CEDRI. (CEDRI can be accessed through the EPA’s CDX.) Performance test data must be submitted in a file format generated through the use of the EPA’s ERT
. Instead of submitting perfo rmance test data in a file format generated through the use of the EPA’s ERT, you may submit an alternate electronic file format consistent with the XML schema listed on the EPA’s ERT website , once the XML schema is available . If you claim that some of the performance test information being submitted is confidential business information (CBI), submit a complete file generated through the use of the EPA’s ERT ( or an(Subpart CCCC

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- 2013) Page 116 of 163 alternate electronic file consistent with the XML schema liste d on the EPA’s ERT website once the XML schema is available) , including information claimed to be CBI, on a compact disc, flash drive, or other commonly used electronic storage media to the EPA. The electronic media must be clearly marked as CBI and mailed to U.S. EPA/OAPQS/CORE CBI Office, Attention: Group Leader, Measurement Policy Group , MD C404

- 02, 4930 Old Page Road , Durham, NC 27703. The same ERT or alternate file with the CBI omitted must be submitted to the EPA via the EPA’s CDX as described earlier in this paragraph. (ii) For data collected using test methods that are not supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the test, submit the results of the performance test to the Administrator at the appropriate address l isted in §60.4. (2) Within 60 days after the date of completing each CEMS performance evaluation, submit the results of the performance evaluation following the procedure specified in either paragraph (b)(2)(i) or (b)(2)(ii) of this section. (i) For perfo rmance evaluations of continuous monitoring systems measuring relative accuracy test audit (RATA) pollutants that are supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the test,(Subpart CCCC

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- 2013) Page 117 of 163 submit the results of the performance evaluation to the EPA via the CEDRI. (CEDRI can be accessed through the EPA’s CDX.) Performance evaluation data must be submitted in a file format generated through the use of the EPA’s ERT
. Instead of submitting performance evaluation data in a file format generated t hrough the use of the EPA’s ERT, you may submit an alternate electronic file format consistent with the XML schema listed on the EPA’s ERT website , once the XML schema is available . If you claim that some of the performance evaluation information being sub mitted is CBI, submit a complete file generated through the use of the EPA’s ERT ( or an alternate electronic file consistent with the XML schema listed on the EPA’s ERT website once the XML schema is available) , including information claimed to be CBI, on a compact disc, flash drive, or other commonly used electronic storage media to the EPA. The electronic media must be clearly marked as CBI and mailed to U.S. EPA/OAPQS/CORE CBI Office, c/o OAQPS Document Control Officer (Room C404

- 02), U.S. Environmental Protection Agency, Research Triangle Park, North Carolina 27711, Attention: WebFIRE Administrator. The same ERT or alternate file with the CBI omitted must be submitted to the EPA via the EPA’s CDX as described earlier in this paragraph.(Subpart CCCC

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- 2013) Page 118 of 163 (ii) For any performance evaluations of continuous monitoring systems measuring RATA pollutants that are not supported by the EPA’s ERT as listed on the EPA’s ERT website at the time of the test, submit the results of the performance evaluation to the Administrator at the appropriate address listed in §60.4. (c) All information required in this subpart to be submitted to the EPA must also be submitted in paper format to the appropriate s tate, l ocal or t ribal a gency whenever authority has been delegated to such agency (the delegated authority) unless the delegated authority specifies another format. Information submitted in paper format must be postmarked no later than the date that the report is required to be submitted to the EPA’s CDX electronically. Any information required to be submitted electronically to the EPA’s CDX may, at the discretion of the delegated authority , satisfy the requirements of this paragraph. Submit initial, annual, and deviation reports electronically or in paper format, postmarked on or befor e the submittal due dates. (b) Submit results of performance tests and CEMS performance evaluation tests as follows. (1) Within 60 days after the date of completing each performance test as required by this subpart, you must(Subpart CCCC

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- 2013) Page 119 of 163 submit the results of the perfo rmance tests required by this subpart to EPA's WebFIRE database by using the Compliance and Emissions Data Reporting Interface (CEDRI) that is accessed through EPA 's Central Data Exchange (CDX)( http:// www.epa.gov/cdx ). Performance test data must be submit ted in the file format generated through use of EPA's Electronic Reporting Tool (ERT) (see http://www.epa.gov/ttn/chief/ert/index.html ). Only data collected using test methods on the ERT Web site are subject to this requirement for submitting reports elec tronically to WebFIRE. Owners or operators who claim that some of the information being submitted for performance tests is confidential business information (CBI) must submit a complete ERT file including information claimed to be CBI on a compact disk, fl ash drive, or other commonly used electronic storage media to EPA. The electronic media must be clearly marked as CBI and mailed to U.S. EPA/OAPQS/CORE CBI Office, Attention: WebFIRE Administrator, MD C404

- 02, 4930 Old Page Rd., Durham, NC 27703. The same ERT file with the CBI omitted must be submitted to EPA via CDX as described earlier in this paragraph. At the discretion of the delegated authority, you must also submit these reports, including the confidential business information, to the delegated(Subpart CCCC

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- 2013) Page 120 of 163 autho rity in the format specified by the delegated authority. For any performance test conducted using test methods that are not listed on the ERT Web site, the owner or operator shall submit the results of the performance test in paper submissions to the Admin istrator. (2) Within 60 days after the date of completing each CEMS performance evaluation test, as defined in this subpart and required by this subpart, you must submit the relative accuracy test audit (RATA) data electronically into EPA's Central Data Ex change by using CEDRI as mentioned in paragraph (b)(1) of this section. Only RATA pollutants that can be documented with the ERT (as listed on the ERT Web site) are subject to this requirement. For any performance evaluations with no corresponding RATA pol lutants listed on the ERT Web site, the owner or operator shall submit the results of the performance evaluation in paper submissions to the Administrator. § 60.2240 Can reporting dates be changed? If the Administrator agrees, you may change the semiannual or annual reporting dates. See § 60.19(c) for procedures to seek approval to change your reporting date. Title V Operating Permits § 60.2242 Am I required to apply for and obtain a Title V operatin g permit for my unit?(Subpart CCCC

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- 2013) Page 121 of 163 Yes. Each CISWI unit and air curtain incinerator subject to standards under this subpart must operate pursuant to a permit issued under Section 129(e) and Title V of the Clean Air Act. Air Curtain Incinerators § 60.2245 What is an air curtain incinerator? (a) An air curtain incinerator operates by forcefully projecting a curtain of air across an open chamber or open pit in which combustion occurs. Incinerators of this type can be constructed above or below ground and with or without re fractory walls and floor. (Air curtain incinerators are not to be confused with conventional combustion devices with enclosed fireboxes and controlled air technology such as mass burn, modular, and fluidized bed combustors.) (b) Air curtain incinerators th at burn only the materials listed in paragraphs (b)(1) through (3) of this section are only required to meet the requirements under § 60.2242 and under “Air Curtain Incinerators” (§ § 60.2245 through 60.2260). (1) 100 percent wood waste. (2) 100 percent cle an lumber. (3) 100 percent mixture of only wood waste, clean lumber, and/or yard waste.(Subpart CCCC

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- 2013) Page 122 of 163 § 60.2250 What are the emission limitations for air curtain incinerators? Within 60 days after your air curtain incinerator reaches the charge rate at which it will ope rate, but no later than 180 days after its initial startup, you must meet the two limitations specified in paragraphs (a) and (b) of this section. (a) Maintain opacity to less than or equal to 10 percent opacity (as determined by the average of three 1

- hou r blocks consisting of ten 6

- minute average opacity values), except as described in paragraph (b) of this section. (b) Maintain opacity to less than or equal to 35 percent opacity (as determined by the average of three 1

- hour blocks consisting of ten 6

- min ute average opacity values) during the startup period that is within the first 30 minutes of operation. § 60.2255 How must I monitor opacity for air curtain incinerators? (a) Use Method 9 of appendix A of this part to determine compliance with the opacity limitation. (b) Conduct an initial test for opacity as specified in § 60.8.(Subpart CCCC

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- 2013) Page 123 of 163 (c) After the initial test for opacity, conduct annual tests no more than 12 calendar months following the date of your previous test. § 60.2260 What are the recordkeeping and reporting requirements for air curtain incinerators? (a) Prior to commencing construction on your air curtain incinerator, submit the three items described in paragraphs (a)(1) through (3) of this section. (1) Notification of your intent to construct the a ir curtain incinerators. (2) Your planned initial startup date. (3) Types of materials you plan to burn in your air curtain incinerator. (b) Keep records of results of all initial and annual opacity tests onsite in either paper copy or electronic format, u nless the Administrator approves another format, for at least 5 years. (c) Make all records available for submittal to the Administrator or for an inspector's onsite review. (d) You must submit the results (as determined by the average of three 1

- hour bloc ks consisting of ten 6

- minute average opacity values) of the initial opacity tests no later than 60 days following the initial test. Submit(Subpart CCCC

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- 2013) Page 124 of 163 annual opacity test results within 12 months following the previous report. (e) Submit initial and annual opacity te st reports as electronic or paper copy on or before the applicable submittal date. (f) Keep a copy of the initial and annual reports onsite for a period of 5 years. Definitions § 60.2265 What definitions must I know? Terms used but not defined in this subp art are defined in the Clean Air Act and subpart A (General Provisions) of this part. Administrator means the Administrator of the U.S. Environmental Protection Agency or his/her authorized representative or Administrator of a State Air Pollution Control A gency. 30

- day rolling average means the arithmetic mean of the previous 720 hours of valid operating data. Valid data excludes periods when this unit is not operating. The 720 hours should be consecutive, but not necessarily continuous if operations are in termittent. Affirmative defense means, in the context of an enforcement proceeding, a response or defense put forward by a defendant, regarding which the defendant has the(Subpart CCCC

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- 2013) Page 125 of 163 burden of proof, and the merits of which are independently and objectively evaluated in a judicial or administrativ e proceeding. Air curtain incinerator means an incinerator that operates by forcefully projecting a curtain of air across an open chamber or pit in which combustion occurs. Incinerators of this type can be constructed above or below ground and with or with out refractory walls and floor. (Air curtain incinerators are not to be confused with conventional combustion devices with enclosed fireboxes and controlled air technology such as mass burn, modular, and fluidized bed combustors.) Annual heat input means t he heat input for the 12 months preceding the compliance demonstration. Auxiliary fuel means natural gas, liquified petroleum gas, fuel oil, or diesel fuel. Average annual heat input rate means annual heat input divided by the hours of operation for the 12 months preceding the compliance demonstration. Bag leak detection system means an instrument that is capable of monitoring particulate matter loadings in the exhaust of a fabric filter (i.e., baghouse) in order to detect bag failures. A bag leak detection system includes, but is not limited to, an instrument that operates on(Subpart CCCC

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- 2013) Page 126 of 163 triboelectric, light scattering, light transmittance, or other principle to monitor relative particulate matter loadings.
Burn
- off oven means any rack reclamation unit, part reclamatio n unit, or drum reclamation unit. A burn

- off oven is not an incinerator, waste

- burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Bypass stack means a device used for discharging combustion gases to avoid severe damage to the air pollution control device or other equipment. Calendar quarter means three consecutive months (nonoverlapping) beginning on: January 1, April 1, July 1, or October 1. Calendar year means 365 consecutive days starting on January 1 and ending on D ecember 31. CEMS data during startup and shutdown means the following: (1) For incinerators, small remote incinerators, and energy recovery units: CEMS data collected during the first hours of a CISWI unit startup from a cold start until waste is fed to th e unit and the hours of operation following the cessation of waste material being fed to the CISWI unit during a unit shutdown. For each startup event, the length(Subpart CCCC

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- 2013) Page 127 of 163 of time that CEMS data may be claimed as being CEMS data during startup must be 48 operating hours or less. For each shutdown event, the length of time that CEMS data may be claimed as being CEMS data during shutdown must be 24 operating hours or less. (2) For waste

- burning kilns: CEMS data collected during the periods of kiln operation that do not include normal operations. Startup begins when the kiln's induced fan is turned on and continues until continuous feed is introduced into the kiln, at which time the kiln is in normal operating mode. Shutdown begins when feed to the kiln is halted. Che mical recovery unit means combustion units burning materials to recover chemical constituents or to produce chemical compounds where there is an existing commercial market for such recovered chemical constituents or compounds. A chemical recovery unit is n ot an incinerator,
a waste
- burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. The following seven types of units are considered chemical recovery units: (1) Units burning only pulping liquors (i.e., black liquor) that are reclaimed in a pulping liquor recovery process and reused in the pulping process.(Subpart CCCC

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- 2013) Page 128 of 163 (2) Units burning only spent sulfuric acid used to produce virgin sulfuric acid. (3) Units burning only wood or coal feedstock for the production of charcoal. (4) Units b urning only manufacturing byproduct streams/residue containing catalyst metals that are reclaimed and reused as catalysts or used to produce commercial grade catalysts. (5) Units burning only coke to produce purified carbon monoxide that is used as an inte rmediate in the production of other chemical compounds. (6) Units burning only hydrocarbon liquids or solids to produce hydrogen, carbon monoxide, synthesis gas, or other gases for use in other manufacturing processes. (7) Units burning only photographic f ilm to recover silver. Chemical recovery unit means combustion units burning materials to recover chemical constituents or to produce chemical compounds where there is an existing commercial market for such recovered chemical constituents or compounds. Th e following seven types of units are considered chemical recovery units:(Subpart CCCC

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- 2013) Page 129 of 163 (1) Units burning only pulping liquors ( i.e., black liquor) that are reclaimed in a pulping liquor recovery process and reused in the pulping process. (2) Units burning only spent sul furic acid used to produce virgin sulfuric acid. (3) Units burning only wood or coal feedstock for the production of charcoal. (4) Units burning only manufacturing byproduct streams/residue containing catalyst metals which are reclaimed and reused as catalysts or used to produce commercial grade catalysts. (5) Units burning only coke to produce purified carbon monoxide that is used as an intermediate in the production of other chemical compounds. (6) Units burning only hydrocarbon liquids or solids
to produce hydrogen, carbon monoxide, synthesis gas, or other gases for use in other manufacturing processes. (7) Units burning only photographic film to recover silver. Chemotherapeutic waste means waste material resulting from the production or use of antin eoplastic agents used for the purpose of stopping or reversing the growth of malignant cells.(Subpart CCCC

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- 2013) Page 130 of 163 Clean lumber means wood or wood products that have been cut or shaped and include wet, air

- dried, and kiln

dried wood products. Clean lumber does not include wood products that have been painted, pigment

- stained, or
pressure - treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote. Commercial and industrial solid waste incineration (CISWI) unit means any distinct operating unit of any commercial or industrial facility that combusts, or has combusted in the preceding 6 months, any solid waste as that term is defined in 40 CFR part 241. If the operating unit burns materials other than traditional fuels as defined in § 241.2 that have been discarded, and you do not keep and produce records as required by § 60.2175(v), the operating unit is a CISWI unit. While not all CISWI units will include all of the following components, a CISWI unit includes, but is not limited to, the solid waste feed system, grate system, flue gas system, waste heat recovery equipment, if any, and bottom ash system. The CISWI unit does not include air pollution control equipment or the stack. The CISWI unit boundary starts at the solid waste hopper (if applicable) and extends through two areas: The combustion unit flue gas system, which ends immediately after the last combustion chamber or after the waste heat(Subpart CCCC

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- 2013) Page 131 of 163 recovery equipment, if any; and the combustion unit bottom ash system, which ends at the truck loading station or similar equipment that transfers the ash to final disposal. The CISWI unit includes all ash handling systems connected to the bottom ash handling system. Contained gaseous material means gases that are in a container when that container is combusted.
Co ntinuous emission monitoring system (CEMS) means the total equipment that may be required to meet the data acquisition and availability requirements of this subpart, used to sample, condition (if applicable), analyze, and provide a record of emissions.
Con tinuous monitoring system (CMS) means the total equipment, required under the emission monitoring sections in applicable subparts, used to sample and condition (if applicable), to analyze, and to provide a permanent record of emissions or process parameter s. A particulate matter continuous parameter monitoring system (PM CPMS) is a type of CMS. Cyclonic burn barrel means a combustion device for waste materials that is attached to a 55 gallon, open

- head drum. The device consists of a lid, which fits onto and encloses the drum, and a blower that forces combustion air into the drum in a cyclonic manner to enhance the mixing of(Subpart CCCC

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- 2013) Page 132 of 163 waste material and air. A cyclonic burn barrel is not an incinerator, a waste

- burning kiln, an energy recovery unit or a small, remote i ncinerator under this subpart. Deviation means any instance in which an affected source subject to this subpart, or an owner or operator of such a source: (1) Fails to meet any requirement or obligation established by this subpart, including but not limite d to any emission limitation, operating limit, or operator qualification and accessibility requirements. (2) Fails to meet any term or condition that is adopted to implement an applicable requirement in this subpart and that is included in the operating pe rmit for any affected source required to obtain such a permit. Dioxins/furans means tetra
- through octa

- chlorinated dibenzo

- p - dioxins and dibenzofurans. Dioxins/furans means tetra
- through octachlorinated dibenzo

- p - dioxins and dibenzofurans. Discard means, for purposes of this subpart and 40 CFR part 60, subpart DDDD, only, burned in an incineration unit without energy recovery. Drum reclamation unit means a unit that burns residues out of drums (e.g., 55 gallon drums) so that the drums can be reused
.(Subpart CCCC

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- 2013) Page 133 of 163 Dry scrubber means an add

- on air pollution control system that injects dry alkaline sorbent (dry injection) or sprays an alkaline sorbent (spray dryer) to react with and neutralize acid gas in the exhaust stream forming a dry powder material. Sorbent inj ection systems in fluidized bed boilers and process heaters are included in this definition. A dry scrubber is a dry control system. Energy recovery means the process of recovering thermal energy from combustion for useful purposes such as steam generation or process heating. Energy recovery unit means a combustion unit combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241) for energy recovery. Energy recovery units include units that would be considered boilers and process heaters if they did not combust solid waste. Energy recovery unit designed to burn biomass (Biomass) means an energy recovery unit that burns solid waste, biomass, and non

- coal solid materials but less than 10 percent coal, on a heat input basis on an ann ual average, either alone or in combination with liquid waste, liquid fuel or gaseous fuels. Energy recovery unit designed to burn coal (Coal) means an energy recovery unit that burns solid waste and at(Subpart CCCC

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- 2013) Page 134 of 163 least 10 percent coal on a heat input basis on an ann ual average, either alone or in combination with liquid waste, liquid fuel or gaseous fuels. Energy recovery unit designed to burn liquid waste materials and gas (Liquid/gas) means an energy recovery unit that burns a liquid waste with liquid or gaseous fu els not combined with any solid fuel or waste materials. Energy recovery unit designed to burn solid materials (Solids) includes energy recovery units designed to burn coal and energy recovery units designed to burn biomass. Fabric filter means an add

- on a ir pollution control device used to capture particulate matter by filtering gas streams through filter media, also known as a baghouse. Foundry sand thermal reclamation unit means a type of part reclamation unit that removes coatings that are on foundry sa nd. A foundry sand thermal reclamation unit is not an incinerator, a waste

- burning kiln, an energy recovery unit or a small, remote incinerator under this subpart. Incinerator means any furnace used in the process of combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241) for the purpose of reducing the volume of the waste by removing combustible(Subpart CCCC

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- 2013) Page 135 of 163 matter. Incinerator designs include single chamber and two

chamber.
In
- line coal mill means those coal mills using kiln exhaust gases in their process. Coal mills with a heat source other than the kiln or coal mills using exhaust gases from the clinker cooler alone are not an in

- line coal mill.
In
- line kiln/ raw mill means a system in a Po rtland Cement production process where a dry kiln system is integrated with the raw mill so that all or a portion of the kiln exhaust gases are used to perform the drying operation of the raw mill, with no auxiliary heat source used. In this system the kil n is capable of operating without the raw mill operating, but the raw mill cannot operate without the kiln gases, and consequently, the raw mill does not generate a separate exhaust gas stream. Kiln means an oven or furnace, including any associated preh eater or precalciner devices, in

- line raw mills, in

- line coal mills or alkali bypasses used for processing a substance by burning, firing or drying. Kilns include cement kilns that produce clinker by heating limestone and other materials for subsequent pro duction of Portland Cement. Because the alkali bypass, in

- line raw mill and in

- line coal mill are considered an integral part(Subpart CCCC

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- 2013) Page 136 of 163 of the kiln, the kiln emissions limits also appl y to the exhaust of the alkali bypass, in

- line raw mill and in

- line coal mill. Lab oratory analysis unit means units that burn samples of materials for the purpose of chemical or physical analysis. A laboratory analysis unit is not an incinerator,
waste
- burning kiln, an energy recovery unit or a small, remote incinerator under this subpa rt. Load fraction means the actual heat input of an energy recovery unit divided by heat input during the performance test that established the minimum sorbent injection rate or minimum activated carbon injection rate, expressed as a fraction (e.g., for 50 percent load the load fraction is 0.5).
Low
- level radioactive waste means waste material which contains radioactive nuclides emitting primarily beta or gamma radiation, or both, in concentrations or quantities that exceed applicable Federal f ederal or Sta te s tate standards for unrestricted release. Low

- level radioactive waste is not high

- level radioactive waste, spent nuclear fuel, or byproduct material as defined by the Atomic Energy Act of 1954 (42 U.S.C. 2014(e)(2)). Malfunction means any sudden, infreq uent, and not reasonably preventable failure of air pollution control(Subpart CCCC

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- 2013) Page 137 of 163 equipment, process equipment, or a process to operate in a normal or usual manner. Failures that are caused, in part, by poor maintenance or careless operation are not malfunctions. Minimum voltage or amperage means 90 percent of the lowest test

- run average voltage or amperage to the electrostatic precipitator measured during the most recent particulate matter or mercury performance test demonstrating compliance with the applicable em ission limits. Modification or modified CISWI unit means a CISWI unit that has been changed later than August 7, 2013 and that meets one of two criteria: (1) The cumulative cost of the changes over the life of the unit exceeds 50 percent of the original co st of building and installing the CISWI unit (not including the cost of land) updated to current costs (current dollars). To determine what systems are within the boundary of the CISWI unit used to calculate these costs, see the definition of CISWI unit. ( 2) Any physical change in the CISWI unit or change in the method of operating it that increases the amount of any air pollutant emitted for which section 129 or section 111 of the Clean Air Act has established standards.(Subpart CCCC

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- 2013) Page 138 of 163 Municipal solid waste or municipal

- type solid waste means household, commercial/retail, or institutional waste. Household waste includes material discarded by residential dwellings, hotels, motels, and other similar permanent or temporary housing. Commercial/retail waste includes material d iscarded by stores, offices, restaurants, warehouses, nonmanufacturing activities at industrial facilities, and other similar establishments or facilities. Institutional waste includes materials discarded by schools, by hospitals (nonmedical), by nonmanufa cturing activities at prisons and government facilities, and other similar establishments or facilities. Household, commercial/retail, and institutional waste does include yard waste and refuse

- derived fuel. Household, commercial/retail, and institutional waste does not include used oil; sewage sludge; wood pallets; construction, renovation, and demolition wastes (which include railroad ties and telephone poles); clean wood; industrial process or manufacturing wastes; medical waste; or motor vehicles (inclu ding motor vehicle parts or vehicle fluff). Opacity means the degree to which emissions reduce the transmission of light and obscure the view of an object in the background.(Subpart CCCC

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- 2013) Page 139 of 163 Operating day means a 24

- hour period between 12:00 midnight and the following midn ight during which any amount of solid waste is combusted at any time in the CISWI unit. Oxygen analyzer system means all equipment required to determine the oxygen content of a gas stream and used to monitor oxygen in the boiler or process heater flue gas, boiler or process heater, firebox, or other appropriate location. This definition includes oxygen trim systems and certified oxygen CEMS. The source owner or operator is responsible to install, calibrate, maintain, and operate the oxygen analyzer system i n accordance with the manufacturer's recommendations. Oxygen trim system means a system of monitors that is used to maintain excess air at the desired level in a combustion device over its operating range . A typical system consists of a flue gas oxygen and /or carbon monoxide monitor that automatically provides a feedback signal to the combustion air controller or draft controller
. Modification or modified CISWI unit means a CISWI unit you have changed later than June 1, 2001 and that meets one of two criteria: (1) The cumulative cost of the changes over the life of the unit exceeds 50 percent of the original cost of building and installing the CISWI unit (not includi ng the(Subpart CCCC

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- 2013) Page 140 of 163 cost of land) updated to current costs (current dollars). To determine what systems are within the boundary of the CISWI unit used to calculate these costs, see the definition of CISWI unit. (2) Any physical change in the CISWI unit or change in the method of operating it that increases the amount of any air pollutant emitted for which section 129 or section 111 of the Clean Air Act has established standards. Part reclamation unit means a unit that burns coatings off parts (e.g., tools, equipment) so that the parts can be reconditioned and reused. Particulate matter means total particulate matter emitted from CISWI units as measured by Method 5 or Method 29 of appendix A of this part. Pathological waste means waste material consisting of only human or animal remains, anatomical parts, and/or tissue, the bags/containers used to collect and transport the waste material, and animal bedding (if applicable). Oxygen analyzer system means all equipment required to determine the oxygen content of a gas stream and used to monitor oxygen in the boiler or process heater flue gas, boiler or process heater, firebox, or other appropriate location. This definition includes oxygen trim systems and certified oxygen CEMS. The source owner or operator is(Subpart CCCC

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- 2013) Page 141 of 163 responsible to in stall, calibrate, maintain, and operate the oxygen analyzer system in accordance with the manufacturer's recommendations. Oxygen trim system means a system of monitors that is used to maintain excess air at the desired level in a combustion device. A typic al system consists of a flue gas oxygen and/or carbon monoxide monitor that automatically provides a feedback signal to the combustion air controller. Performance evaluation means the conduct of relative accuracy testing, calibration error testing, and oth er measurements used in validating the continuous monitoring system data. Performance test means the collection of data resulting from the execution of a test method (usually three emission test runs) used to demonstrate compliance with a relevant emission standard as specified in the performance test section of the relevant standard. Process change means any of the following physical or operational changes: (1) A physical change (maintenance activities excluded) to the CISWI unit which may increase the emission rate of any air pollutant to which a standard applies;(Subpart CCCC

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- 2013) Page 1 42 of 163 (2) An operational change to the CISWI unit where a new type of non

- hazardous secondary material is being combusted; (3) A physical change (maintenance activities excluded) to the air pollutio n control devices used to comply with the emission limits for the CISWI unit (e.g., replacing an electrostatic precipitator with a fabric filter); (4) An operational change to the air pollution control devices used to comply with the emission limits for th e affected CISWI unit (e.g., change in the sorbent injection rate used for activated carbon injection). Rack reclamation unit means a unit that burns the coatings off racks used to hold small items for application of a coating. The unit burns the coating o verspray off the rack so the rack can be reused. Raw mill means a ball or tube mill, vertical roller mill or other size reduction equipment, that is not part of an in

- line kiln/raw mill, used to grind feed to the appropriate size. Moisture may be added or removed from the feed during the grinding operation. If the raw mill is used to remove moisture from feed materials, it is also, by definition, a raw material dryer. The raw mill also includes the air separator associated with the raw mill.(Subpart CCCC

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- 2013) Page 143 of 163 Reconstruction means rebuilding a CISWI unit and meeting two criteria: (1) The reconstruction begins on or after June 1 August 7 , 2001 20 13
. (2) The cumulative cost of the construction over the life of the incineration unit exceeds 50 percent of the original cost of buildi ng and installing the CISWI unit (not including land) updated to current costs (current dollars). To determine what systems are within the boundary of the CISWI unit used to calculate these costs, see the definition of CISWI unit. Refuse

- derived fuel means a type of municipal solid waste produced by processing municipal solid waste through shredding and size classification. This includes all classes of refuse

- derived fuel including two fuels: (1) Low

- density fluff refuse

- derived fuel through densified refus e - derived fuel. (2) Pelletized refuse

- derived fuel. Responsible official means one of the following: (1) For a corporation: A president, secretary, treasurer, or vice

- president of the corporation in charge of a principal business function, or any other per son who performs similar policy or decision

- making functions for the corporation, or a duly authorized representative of(Subpart CCCC

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- 2013) Page 144 of 163 such person if the representative is responsible for the overall operation of one or more manufacturing, production, or operating facil ities applying for or subject to a permit and either: (i) The facilities employ more than 250 persons or have gross annual sales or expenditures exceeding $25 million (in second quarter 1980 dollars); or (ii) The delegation of authority to such representat ives is approved in advance by the permitting authority; (2) For a partnership or sole proprietorship: A general partner or the proprietor, respectively; (3) For a municipality, State s tate , Federal f ederal , or other public agency: Either a principal executi ve officer or ranking elected official. For the purposes of this part, a principal executive officer of a Federal f ederal agency includes the chief executive officer having responsibility for the overall operations of a principal geographic unit of the age ncy (e.g., a Regional Administrator of EPA); or (4) For affected facilities: (i) The designated representative in so far as actions, standards, requirements, or prohibitions under Title IV of the Clean Air Act or the regulations promulgated thereunder are concerned; or(Subpart CCCC

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- 2013) Page 145 of 163 (ii) The designated representative for any other purposes under part 60. Shutdown means the period of time after all waste has been combusted in the primary chamber. Small, remote incinerator means an incinerator that combusts solid waste (as that term is defined by the Administrator in 40 CFR part 241) and combusts 3 tons per day or less solid waste and is more than 25 miles driving distance to the nearest municipal solid waste landfill. Soil treatment unit means a unit that thermally treats petroleum

- contaminated soils for the sole purpose of site remediation. A soil treatment unit may be direct

- fired or indirect fired. A soil treatment unit is not an incinerator, a waste

- burning kiln, an energy recovery unit or a small, remote incinerator un der this subpart. Solid waste means the term solid waste as defined in 40 CFR 241.2. Solid waste incineration unit means a distinct operating unit of any facility which combusts any solid waste (as that term is defined by the Administrator in 40 CFR part 2 41) material from commercial or industrial establishments or the general public (including single and multiple residences, hotels and motels). Such term does not include incinerators or other units required to have a(Subpart CCCC

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- 2013) Page 146 of 163 permit under section 3005 of the Solid Waste Disposal Act. The term “solid waste incineration unit” does not include: (1) Materials recovery facilities (including primary or secondary smelters) which combust waste for the primary purpose of recovering metals; (2) Qualifying small power producti on facilities, as defined in section 3(17)(C) of the Federal Power Act (16 U.S.C. 769(17)(C)), or qualifying cogeneration facilities, as defined in section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)), which burn homogeneous waste (such as unit s which burn tires or used oil, but not including refuse

- derived fuel) for the production of electric energy or in the case of qualifying cogeneration facilities which burn homogeneous waste for the production of electric energy and steam or forms of usefu l energy (such as heat) which are used for industrial, commercial, heating or cooling purposes; or (3) Air curtain incinerators provided that such incinerators only burn wood wastes, yard wastes, and clean lumber and that such air curtain incinerators comp ly with opacity limitations to be established by the Administrator by rule. Space heater means a unit that meets the requirements of 40 CFR 279.23. A space heater is not an incinerator, a(Subpart CCCC

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- burning kiln, an energy recovery unit or a small, remote incin erator under this subpart. Standard conditions, when referring to units of measure, means a temperature of 68 °F (20 °C) and a pressure of 1 atmosphere (101.3 kilopascals). Startup period means the period of time between the activation of the system and th e first charge to the unit.
Waste
- burning kiln means a kiln that is heated, in whole or in part, by combusting solid waste (as that term is defined by the Administrator in 40 CFR part 241). Secondary materials used in Portland cement kilns shall not be dee med to be combusted unless they are introduced into the flame zone in the hot end of the kiln or mixed with the precalciner fuel. Wet scrubber means an add

- on air pollution control device that uses an aqueous or alkaline scrubbing liquor to collect particu late matter (including nonvaporous metals and condensed organics) and/or to absorb and neutralize acid gases. Wood waste means untreated wood and untreated wood products, including tree stumps (whole or chipped), trees, tree limbs (whole or chipped), bark, sawdust, chips, scraps, slabs, millings, and shavings. Wood waste does not include:(Subpart CCCC

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- 2013) Page 148 of 163 (1) Grass, grass clippings, bushes, shrubs, and clippings from bushes and shrubs from residential, commercial/retail, institutional, or industrial sources as part of maint aining yards or other private or public lands. (2) Construction, renovation, or demolition wastes. (3) Clean lumber. Table 1 to Subpart CCCC of Part 60

— Emission Limitations for CISWI Units Incinerators for Which Construction is Commenced After November 30, 1999, But no Later Than June 4, 2010, or for Which Modification or Reconstruction is Commenced on or After June 1, 2001, But no Later Than August 7, 2013

For the air pollutant You must meet

this emiss ion limitation a Using this averaging

time And determining compliance using this method Cadmium 0.004

milligrams per dry standard cubic meter 3

- run average (1 hour

minimum sample time per run) Performance test (Method 29 of appendix A of this part). Carbon monoxide 157 parts per

million by dry volume 3

- run average (1 hour

minimum sample time per run) Performance test (Method 10 at 40 CFR part 60, appendix A

- 4). Dioxin/Furan (toxic equivalency basis) 0.41 nanograms

per dry standard cubic meter 3

- run average (collect

a minimum volume of 4 dry standard cubic meters per run) Performance test (Method 23 of appendix A

- 7 of this part). Hydrogen chloride 62 parts per

million by dry volume 3

- run average (For

Method 26, collect a minimum volume of 120 liters per run. For Method 26A, collect a minimum volume of 1 dry standard cubic meter per run) Performance test (Method 26 or 26A at 40 CFR part 60, appendix A

8).

Lead 0.04 milligrams

per dry standard cubic meter 3

- run average (1 hour

minimum sample time per r un) Performance test (Method 29 of appendix A of this part). Mercury 0.47 milligrams

per dry standard cubic meter 3

- run average (1 hour

minimum sample time per run) Performance test (Method 29 of appendix A of this part).(Subpart CCCC

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For the air pollutant You must meet

this emiss ion limitation a Using this averaging

time And determining compliance using this method Nitrogen Oxides 388 parts per

million by dry volume 3

- run average (for

Method 7E, 1 hour minimum sample time per run) Performance test (Method 7 or 7E at 40 CFR part 60, appendix A

4). Opacity 10 percent 6

- minute averages Performance test (Method 9 of appendix A of this part). Oxides of nitrogen 388 parts per

million by dry volume 3

- run average (1 hour

minimum sample time per run) Performance test (Method 7, 7A, 7C, 7D, or 7E of appendix A of this part). Particulate matter 70 milligrams

per dry standard cubic meter 3

- run average (1 hour

minimum sample time per run) Performance test (Method 5 or 29 of appendix A of this part). Sulfur Dioxide 20 parts per

million by dry volume 3

- run average (For

Method 6, collect a minimum volume of 20 liters per run. For Method 6C, collect sample for a minimum duration of 1 hour per run) Performance test (Method 6 or 6C at 40 CFR part 60, appendix A

4).

a All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard conditions. Table 2 to Subpart CCCC of Part 60

— Operating Limits for Wet Scrubbers

For these operating parameters You must establish these operating limits And monitoring using these minimum

frequencies
Data measurement Data

recording Averaging time Charge rate Maximum charge rate Continuous Every hour Daily (batch units)

3

- hour rolling (continuous and intermittent units) a Pressure drop across the wet scrubber or amperage to wet scrubber Minimum pressure drop or amperage Continuous Every 15 minutes 3

- hour rolling a(Subpart CCCC

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For these operating parameters You must establish these operating limits And monitoring using these minimum

frequencies
Data measurement Data

recording Averaging time Scrubber liquor flow rate Minimum flow rate Continuous Every 15 minutes 3

- hour rolling a Scrubber liquor pH Minimum pH Continuous Every 15 minutes 3

- hour rolling a

a Calculated each hour as the average of the previous 3 operating hours.

. Table 3 to Subpart CCCC of Part 60

— Toxic Equivalency Factors Dioxin/furan congener Toxic equivalency factor 2,3,7,8

- tetrachlorinated dibenzo

- p - dioxin 1 1,2,3,7,8

- pentachlorinated dibenzo

- p - dioxin 0.5 1,2,3,4,7,8

- hexachlorinated dibenzo

- p - dioxin 0.1 1,2,3,7,8,9

- hexachlorinated dibenzo

- p - dioxin 0.1 1,2,3,6,7,8

- hexachlorinated dibenzo

- p - dioxin 0.1 1,2,3,4,6,7,8

- heptachlorinated dibenzo

- p - dioxin 0.01 octachlorinated dibenzo

- p - dioxin 0.001 2,3,7,8

- tetrachlorinated dibenzofuran 0.1 2,3,4,7,8

- pentachlorinated dibenzofuran 0.5 1,2,3,7,8

- pentachlorinated dibenzofuran 0.05 1,2,3,4,7,8

- hexachlorinated dibenzofuran 0.1 1,2,3,6,7,8

- hexachlorinated dibenzofuran 0.1 1,2,3,7,8,9

- hexachlorinated dibenzofuran 0.1 2,3,4,6,7,8

- hexachlorinated dibenzofuran 0.1 1,2,3,4,6,7,8

- heptachlorinated dibenzofuran 0.01 1,2,3,4,7,8,9

- heptachlorinated dibenzofuran 0.01 octachlorinated dibenzofuran 0.001 Table 4 to Subpart CCCC of Part 60

— Summary of Reporting Requirements a Report Due date Contents Reference Preconstruction report Prior to

commencing construction  Statement of intent to construct § 60.2190(Subpart CCCC

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Report Due date Contents Reference

 Anticipated date of commencement of construction

 Documentation for siting requirements

 Waste management plan

 Anticipated date of initial startup Startup notification Prior to initial

startup  Type of waste to be burned

 Maximum design waste burning capacity

 Anticipated maximum charge rate

 If applicable, the petition for site

specific operating limits § 60.2195

Initial test report No later than

60 days follo wing the initial performance test  Complete test report for the initial performance test

 The values for the site

- specific operating limits

 Installation of bag leak detection system for fabric filter § 60.2200

Annual report No later than

12 months following the submission of the initial test report. Subsequent reports are to be submitted no more than 12 months following the previous report  Name and address

 Statement and signature by responsible official

 Date of report

 Values for the operating limit s

 Highest recorded 3

- hour average and the lowest 3

- hour average, as applicable, for each operating parameter recorded for the calendar year being reported § § 60.2205 and 60.2210.(Subpart CCCC

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Report Due date Contents Reference

 For each performance test conducted during the reporting period, I i f a ny performance test was i s cond ucted , during the reporting period, the results of the test the process unit(s) tested, the pollutant(s) tested, and the date that such performance test was conducted.

 If a performance test was not conducted during the reporting period, a statement that the requirements of § 60.2155(a) were met

 Documentation of periods when all qualified CISWI unit operators were unavailable for more than 8 hours but less than 2 weeks

 If you are conducting performance tests once every 3 years consistent with § 60.2155(a), the date of the last 2 performance tests, a comparison of the emission level you achieved in the last 2 performance tests to the 75 percent emission limit threshold requ ired in § 60.2155(a) and a statement as to whether there have been any(Subpart CCCC

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Report Due date Contents Reference operational changes since the last performance test that could increase emissions Emission limitation or operating limit deviation report By August 1 of

that year for data collected during the first half of the calendar year. By February 1 of the following year for data collected during the second half of the calendar year  Dates and times of deviation

 Averaged and recorded data for those dates

 Duration and causes of each deviation and the corrective actions taken

 Copy of operating limit monitoring data and , if any performance test was conducted that documents emission levels, the process unit(s) tested, the pollutant(s) tested, and t he date that such performance text was conducted reports

 Dates, times and causes for monitor downtime incidents § 60.2215 and 60.2220.

Qualified operator deviation notification Within 10 days of

deviation  Statement of cause of deviation

 Description of eff orts to have an accessible qualified operator

 The date a qualified operator will be accessible § 60.2225(a)(1)

Qualified operator deviation status report Every 4 weeks

following deviation  Description of efforts to have an accessible qualified operator

 The date a qualified operator will be accessible

 Request for approval to continue operation § 60.2225(a)(2)(Subpart CCCC

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Report Due date Contents Reference Qualified operator deviation notification of resumed operation Prior to resuming

operation  Notification that you are resuming operation § 60.2225(b)

a This table is only a summary, see the referenced sections of the rule for the complete requirements.

Table 5 to Subpart CCCC of Part 60

— Emission Limitations for Incinerators That Commenced Construction After June 4, 2010, or That Commenced Reconstruction or Modification After August 7, 2013

For the air pollutant You must meet

this emission limitation a Using this averaging time And determining compliance using this method Cadmium 0.0023

milligrams per dry standard cubic meter 3

- run average (collect a minimum volume of 4 dry standard cubic meter per run) Performance test (Method 29 at 40 CFR part 60, appendix A

- 8 of this part). Use ICPMS for the analytical finish. Carbon monoxide 17 parts per

million by dry volume 3

- run average (1 hour minimum sample time per run) Performance test (Method 10 at 40 CFR part 60, appendix A

- 4). Dioxin/furan (Total Mass Basis) 0.58 nanograms

per dry standard cubic meter c 3

- run average (collect a minimum volume of 4 dry standard cubic meters per run) Perfor mance test (Method 23 at 40 CFR part 60, appendix A

- 7). Dioxin/furan (toxic equivalency basis) 0.13 nanograms

per dry standard cubic meter 3

- run average (collect a minimum volume of 4 dry standard cubic meter per run) Performance test (Method 23 at 40 CFR part 60, appendix A

- 7). Fugitive ash Visible

emissions for no more than 5 percent of the hourly observation period Three 1

- hour observation periods Visible emission test (Method 22 at 40 CFR part 60, appendix A

- 7).(Subpart CCCC

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For the air pollutant You must meet

this emission limitation a Using this averaging time And determining compliance using this method Hydrogen chloride 0.091 parts per

million by dry volume 3

- run average (For Method 26, collect a minimum volume of 360 liters per run. For Method 26A, collect a minimum volume of 3 dry standard cubic meters per run) Performance test (Method 26 or 26A at 40 CFR part 60, appendix A

- 8).

Lead 0.015 milligrams

per dry standard cubic meter c 3

- run average (collect a minimum volume of 4 dry standard cubic meters per run) Performance test (Method 29 of appendix A

- 8 at 40 CFR part 60). Use ICPMS for the analytical finish. Mercury 0.00084

milligrams per dry standard cubic meter c 3

- run average (collect enough volume to meet a detection limit data quality objective of 0.03 ug/dry standard cubic meter) Performance test (Method 29 or 30B at 40 CFR part 60, appendix A

- 8) or ASTM D6784

- 02 (Reapproved 2008). b Nitrogen Oxides 23 parts per

million dry volume 3

- run average (for Method 7E, 1 hour minimum sample time per run) Performance test (Method 7 or 7E at 40 CFR part 60, appendix A

- 4). Particulate matter (filterable) 18 milligrams

per dry standard cu bic meter 3

- run average (collect a minimum volume of 2 dry standard cubic meters per run) Performance test (Method 5 or 29 at 40 CFR part 60, appendix A

- 3 or appendix A

- 8 at 40 CFR part 60). Sulfur dioxide 11 parts per

million dry volume 3

- run average (1 hour minimum sample time per run) Performance test (Method 6 or 6C at 40 CFR part 60, appendix A

- 4).

a All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the Total Mass Limit or the toxic equivalency basis limit.
b Incorporated by reference, see § 60.17. Table 6 to Subpart CCCC of Part 60

— Emission Limitations for Energy Recovery Units That Commenced Construction After(Subpart CCCC

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For the air pollutant You must meet this

emission limitation a Using this averaging time And determining

compliance using this method Liquid/gas Solids Cadmium 0.023

milligrams per dry standard cubic meter Biomass

—

0.0014 milligrams per dry standard cubic meter. c Coal

— 0.0095 milligrams per dry standard cubic meter 3

- run average

(collect a minimum volume of 4 dry standard cubic meters per run) Performance test

(Method 29 at 40 CFR part 60, appendix A

8). Use ICPMS for the a nalytical finish.

Carbon monoxide 35 parts per

million dry volume Biomass

—

240 parts per million dry volume Coal

— 95 parts per million dry volume 3

- run average

(1 hour minimum sample time per run) Performance test

(Method 10 at 40 CFR part 60, appendix A
4).

Dioxin/furans (Total Mass Basis) No Total

Mass Basis limit, must meet the toxic equivalency basis limit below Biomass

—

0.52 nanograms per dry standard cubic meter. c Coal

— 5.1 nanograms per dry standard cubic meter. c 3

- run average

(collect a minimum volume of 4 dry standard cubic meters) Performance test

(Method 23 at 40 CFR part 60, appendix A

7).

Dioxins/furan s (toxic equivalency basis) 0.093

nanograms per dry standard cubic meter. c Biomass

—

0.076 nanograms per dry standard cubic meter. c 3

- run average

(collect a minimum volume of 4 dry standard cubic meters per run) Performance test

(Method 23 of appendix A

- 7 of this part).(Subpart CCCC

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For the air pollutant You must meet this

emission limitation a Using this averaging time And determining

compliance using this method Liquid/gas Solids

Coal

— 0.075 nanograms per dry standard cubic meter. c Fugitive ash Visible

emissions for no more than 5 percent of th e hourly observation period Three 1

-

hour observatio n periods Visible

emission test (Method 22 at 40 CFR part 60, appendix A
- 7). Fugitive ash

Hydrogen chloride 14 parts per

million dry volume Biomass

—

0.20 parts per million dry volume Coal

— 13 parts per million dry volume 3

- run average

(For Method 26, collect a minimum volume of 360 liters per run. For Method 26A, collect a minimum volume of 3 dry standard cubic meters per run) Performance test

(Method 26 or 26A at 40 CFR part 60, appendix A

- 8).

Lead 0.0 96

milligrams per dry standard cubic meter Biomass

—

0.014 milligrams per dry standard cubic meter. c Coal

— 0.14 milligrams per dry standard cubic meter. 3

- run average

(collect a minimum volume of 4 dry standard cubic meters per run) Performance test

(Method 29 at 40 CFR part 60, appendix A

8). Use ICPMS for the analytical finish.

Mercury 0.00056

milligrams per dry standard cubic meter. c Biomass

—

0.0022 milligrams per dry standard cubic meter Coal

— 0.016 3

- run average

(collect enough volume to meet an in

- stack detection limit data quality Performance test

(Method 29 or 30B at 40 CFR part 60, appendix A

- 8) or ASTM D6784

- 02 (Reapproved 2008)b.(Subpart CCCC

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For the air pollutant You must meet this

emission limitation a Using this averaging time And determining

compliance using this method Liquid/gas Solids

milligrams per dry standard cubic meter objective of

0.03 ug/dscm)

Oxides of nitrogen 76 parts per

million dry volume Biomass

—

290 parts per million dry volume Coal

— 340 parts per million dry volume 3

- run average

(for Method 7E, 1 hour minimum sample time per run) Performance test

(Method 7 or 7E at 40 CFR part 60, appendix A

- 4).

Particulate matter (filterable) 110

milligrams per dry standard cubic meter Biomass

—

5.1 milligrams per dry standard cubic meter Coal

— 160 milligrams per dry standard cubic meter 3

- run average

(collect a minimum volume of 1 dry standard cubic meter per run) Performance test

(Method 5 or 29 at 40 CFR part 60, appendix A

- 3 or appendix A

- 8) if the unit has an annual average heat input rate less than 250 MMBtu/hr; or PM CPMS (as specified in § 60.2145(x)) if the unit has an annual average heat input rate equal to or greater than 250 MMBtu/hr. Sulfur dioxide 720 parts

per million dry volume Biomass

—

7.3 parts per million dry volume Coal

— 650 parts per million dry volume 3

- run average

(for Method 6, collect a minimum of 60 liters, for Method 6C,1 hour minimum sample time per run) Performance test

(Method 6 or 6C at 40 CFR part 60, appendix A

- 4).

a All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the Total Mass Basis limit or the toxi c equivalency basis limit.
b Incorporated by reference, see § 60.17. Table 7 to Subpart CCCC of Part 60

— Emission Limitations for Waste
- burning Kilns That Commenced Construction After June(Subpart CCCC

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For the air pollutant You must meet this

emission limitation a Using this averaging time And determining compliance using this method Cadmium 0.0014 milligrams

per dry standard cubic meter. b 3

- run average (collect a minimum volume of 4 dry standard cubic meter s per run) Performance test (Method 29 at 40 CFR part 60, appendix A

8). Use ICPMS for the analytical finish.

Carbon monoxide 90 (long kilns)/190

(preheater/precalcin er) parts per million dry volume 3

- run average (1 hour minimum sample time per run) Performance test (Method 10 at 40 CFR part 60, appendix A

4). Dioxins/fura ns (total mass basis) 0.51 nanograms per

dry standard cubic meter. b 3

- run average (collect a minimum volume of 4 dry standard cubic meters per run) Performance test (Method 23 at 40 CFR part 60, appendix A

7).

Dioxins/fura ns (toxic equivalency basis) 0.075 nanograms per

dry standard cubic meter. b 3

- run average (collect a minimum volume of 4 dry standard cubic meters) Performance test (Method 23 at 40 CFR part 60, appendix A

7).
Hyd rogen chloride 3.0 parts per

million dry volume. b 3

- run average (1 hour minimum sample time per run) or 30

- day rolling average if HCl CEMS are used Performance test (Method 321 at 40 CFR part 63, appendix A) or HCl CEMS if a wet scrubber or dry scrubber is not used.

Lead 0.014 milligrams per

dry standard cubic meter. b 3

- run average (collect a minimum volume of 4 dry standard cubic meters) Performance test (Method 29 at 40 CFR part 60, appendix A

8). Use ICPMS for the analytical finish. Mercury 0.0037 mill igrams

per dry standard cubic meter 30

- day rolling average Mercury CEMS or sorbent trap monitoring system (performance specification 12A or 12B, respectively, of appendix B of this part.) Oxides of nitrogen 200 parts per

million dry volume 30

- day rolling average NOx CEMS (performance specification 2 of appendix B and procedure 1 of(Subpart CCCC

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For the air pollutant You must meet this

emission limitation a Using this averaging time And determining compliance using this method appendix F of this part). Particulate matter (filterable) 2.2 milligrams per

dry standard cubic meter 30

- day rolling average PM CPMS (as specified in § 60.2145(x)).

Sulfur dioxide 28 parts per million

dry volume 30

- day rolling average Sulfur dioxide CEMS (performance specification 2 of appendix B and procedure 1 of appendix F of this part).

a All emission limitations are measured at 7 percent oxygen, dry basis at standard c onditions. For dioxins/furans, you must meet either the Total Mass Basis limit or the toxic equivalency basis limit.
b If you are conducting stack tests to demonstrate compliance and your performance tests for this pollutant for at least 2 consecutive years show that your emissions are at or below this limit, you can skip testing according to § 60.2155 if all of the other provisions of § 60.2155 are met. For all other pollutants that do not contain a footnote “b”, your performance tests for this pollutant for at least 2 consecutive years must show that your emissions are at or below 75 percent of this limit in order to qual ify for skip testing. Table 8 to Subpart CCCC of Part 60

— Emission Limitations for Small, Remote Incinerators That Commenced Construction After June 4, 2010, Or That Commenced Reconstruction or Modification After August 7, 2013

For the air pollutant You must meet

this emission limitation a Using this averaging

time And determining compliance using this method Cadmium 0.67 milligrams

per dry standard cubic meter 3

- run average (collect

a minimum volume of 1 dry standard cubic meters per run) Performance te st (Method 29 at 40 CFR part 60, appendix A

- 8). Carbon monoxide 13 parts per

million dry volume 3

- run average (1 hour

minimum sample time per run) Performance test (Method 10 at 40 CFR part 60, appendix A

- 4). Dioxins/furans (total mass basis) 1,800 nanograms

per dry standard cubic meter. b 3

- run average (collect

a minimum volume of 1 dry standard cubic meters per run) Performance test (Method 23 at 40 CFR part 60, appendix A

- 7). Dioxins/furans (toxic 31 nanograms

per dry 3

- run average (collect

a minimum volume of 1 Performance test (Method 23 at 40(Subpart CCCC

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For the air pollutant You must meet

this emission limitation a Using this averaging

time And determining compliance using this method equivalency basis) standard cubic

meter. b dry standard cubic

meters) CFR part 60, appendix A

- 7). Fugitive ash Visible

emissions for no more than 5 percent of the hourly observation period Three 1

- hour

observation periods Visible emissions test (Method 22 at 40 CFR part 60, appendix A

- 7).

Hydrogen chloride 200 parts per

million by dry volume 3

- run average (For

Method 26, collect a minimum volume of 60 liters per run. For Method 26A, collect a minimum vo lume of 1 dry standard cubic meter per run) Performance test (Method 26 or 26A at 40 CFR part 60, appendix A

- 8).

Lead 2.0 milligrams

per dry standard cubic meter 3

- run average (collect

a minimum volume of 1 dry standard cubic meters) Performance test (Method 29 at 40 CFR part 60, appendix A

- 8). Use ICPMS for the analytical finish. Mercury 0.0035

milligrams per dry standard cubic meter 3

- run average (For

Method 29 and ASTM D6784

- 02 (Reapproved 2008) b , collect a minimum volume of 2 dry standard cubic m eters per run. For Method 30B, collect a minimum volume as specified in Method 30B at 40 CFR part 60, appendix A) Performance test (Method 29 or 30B at 40 CFR part 60, appendix A

- 8) or ASTM D6784

- 02 (Reapproved 2008). b

Oxides of nitrogen 170 parts per

million dry volume 3

- run average (for

Method 7E, 1 hour minimum sample time per run) Performance test (Method 7 or 7E at 40 CFR part 60, appendix A

4). Particulate matter (filterable) 270 milligrams

per dry standard cubic meter 3

- run average (collect

a mi nimum volume of 1 dry standard cubic meters) Performance test (Method 5 or 29 at 40 CFR part 60, appendix A

- 3 or appendix A

8).(Subpart CCCC

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For the air pollutant You must meet

this emission limitation a Using this averaging

time And determining compliance using this method Sulfur dioxide 1.2 parts per

million dry volume 3

- run average (1 hour

minimum sample time per run) Performance test (Method 6 o r 6c at 40 CFR part 60, appendix A

4).

a All emission limitations are measured at 7 percent oxygen, dry basis at standard conditions. For dioxins/furans, you must meet either the Total Mass Basis limit or the toxic equivalency basis limit.
b Incorporated by reference, see § 60.17.(Subpart CCCC

- eCFR version 9

- 13

- 2013) Page 163 of 163