Subpart CCCC—Standards of Performance for Commercia l and

Industrial Solid Waste Incineration Units

Introduction

§60.2000 What does this subpart do?

This subpart establishes new source performance standards for commercial and industrial solid waste incineration (CISWI) units.

§60.2005 When does this subpart become effective?

This subpart takes effect on [THE DATE 6 MONTHS AFT ER PUBLICATION OF THE FINAL RULE IN THE FEDERAL REGIST ER]. Some of the requirements in this subpart apply to p lanning the CISWI unit and must be completed even before construction is initiated on the CISWI unit (i.e., the preconstruction requirements in §§60.2045 and 60.20 50). 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 incinerati on unit?

Yes, if your incineration unit meets all the requirements specified in paragraphs (a) through (c ) of this section.

(a) Your incineration unit is a new incineration u nit as defined in §60.2015.

(b) Your incineration unit is a CISWI unit as defi ned 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 uni t that meets any of the criteria specified in paragraph (a)(1) through (a) (2) of this section. Deleted: for Which Construction Is Commenced After November 30, 1999 or for Which Modification or Reconstruction Is Commenced on or After June 1, 2001

Deleted: This subpart takes effect on June 1, 2001.

Deleted: or
Deleted: either
Deleted: two(1) A commercial and industrial solid waste

incineration unit that c ommenced construction after [INSERT THE DATE OF PUBLICATION IN THE FEDERAL REGI STER].

(2) A commercial and industrial solid waste incineration unit that c ommenced reconstruction or modification after [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE].

(b) This subpart does not affect your incineration unit if you make physical or operational changes to your incineration unit primarily to comply with the emis sion guidelines in subpart DDDD of this part (Emission Guidelines and Compliance Times for Commercial and Industrial Solid Waste Incineration Units). Such c hanges do not qualify as reconstruction or modification un der this subpart.

§60.2020 What combustion units are exempt from th is subpart?

This subpart exempts the types of units described i n paragraphs (a), (c) through (i) and (m) of this sec tion, but some units are required to provide notification s. Air curtain incinerators are exempt from the requiremen ts in this subpart except for the provisions in §§60.2242 , 60.2250, and 60.2260.

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(a) Pathological waste incineration units. Incineration units burning 90 percent or more by we ight (on a calendar quarter basis and excluding the weight o f auxiliary fuel and combustion air) of pathological waste, low-level radioactive waste, and/or chemotherapeuti c waste as defined in §60.2265 are not subject to this subp art if you meet the two requirements specified in paragrap hs (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 th e weight of pathological waste, low-level radioactive waste, and/or chemotherapeutic waste burned, and the weigh t of all other fuels and wastes burned in the unit.

(b) [Reserved] Deleted: C
Deleted: November 30, 1999

Deleted: C
Deleted: on or
Deleted: June 1, 2001

Deleted:

Deleted: This subpart exempts fifteen types of units described in paragraphs (a) through (o) of this section

Deleted: Agricultural waste incineration 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 agricultural wastes as defined in §60.2265 are not subject to this subpart if you meet the two requirements specified in paragraphs (b)(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 weight of agricultural waste burned, and the weight of all other fuels and wastes burned in the unit.(c) Municipal waste combustion units . Incineration

units that are regulated under subpart Ea of this p art (Standards of Performance for Municipal Waste Combu stors); subpart Eb of this part (Standards of Performance f or Large Municipal Waste Combustors; subpart Cb of this part (Emission Guidelines and Compliance Time for Large Municipal Combustors; AAAA of this part (Standards of Performance for Small Municipal Waste Combustion Un its); or subpart BBBB of this part (Emission Guidelines for Small Municipal Waste Combustion Units). (d) Medical waste incineration units. Incineration units regulated under subpart Ec of this part (Standards of Performance f or Hospital/Medical/Infectious Waste Incinerators for Which Construction is Commenced After June 20, 1996) or s ubpart Ce of this part (Emission Guidelines and Compliance Times for Hospital/Medical/Infectious Waste Incinerators)

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(e) Small power production facilities. Units that meet the three requirements specified in paragraphs (e)(1) through (3) of this section.

(1) The unit qualifies as a small power-production facility under section 3(17)(C) of the Federal Powe r Act (16 U.S.C. 796(17)(C)).

(2) The unit burns homogeneous waste (not includin g refuse-derived fuel) to produce electricity.

(3) You notify the Administrator that the unit mee ts all of these criteria.

(f) Cogeneration facilities. Units that meet the three requirements specified in paragraphs (f)(1) t hrough (3) of this section.

(1) The unit qualifies as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)).

(2) The unit burns homogeneous waste (not includin g refuse-derived fuel) to produce electricity and ste am or other forms of energy used for industrial, commerci al, heating, or cooling purposes.

(3) You notify the Administrator that the unit mee ts all of these criteria. Deleted: meet either of the two criteria specified in paragraph (c)(1) or (2) of this section.
Deleted: for Which Construction is Commenced After September 20, 1994)
Deleted: that are Constructed on or Before September 20, 1994)
Deleted: subpart
Deleted: New Stationary Sources:
Deleted: Existing Stationary Sources:
Deleted: Municipal waste combustion units. ¶
Deleted: (2) Burn greater than 30 percent municipalsolid waste or refusederived fuel, as defined in subpart Ea, subpart Eb, subpart AAAA, and subpart BBBB of this part, and that have the capacity to burn less than 35 tons (32 megagrams) per day of municipal solid waste or refuse-derived fuel, if you meet the two requirements in paragraphs (c)(2)(i) and (ii) of this section.¶ (i) Notify the Administrator that the unit meets these criteria.¶ (ii) Keep records on a calendar quarter basis of the weight of municipal solid waste burned, and the weight of all other fuels and wastes burned in the unit.¶(g) Hazardous waste 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 o nly required to meet the requirements under “Air Curtai n 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.

(j) [Reserved] (k) [Reserved] (l) [Reserved] (m) Sewage treatment plants . Incineration units regulated under subpart O of this part (Standards of Performa nce for Sewage Treatment Plants).

(n) Sewage sludge incineration units . Incineration units combusting sewage sludge for the purpose of r educing the volume of the sewage sludge by removing combust ible matter. Sewage sludge incineration unit designs inc lude fluidized bed and multiple hearth.

§60.2025 [Removed]

§60.2030 Who implements and enforces this subpart ?

(a) This subpart can be implemented and enforced b y the U.S. Environmental Protection Agency (EPA), or a delegated authority such as your state, local, or t ribal agency. If the EPA Administrator has delegated aut hority to your state, local, or tribal agency, then that a gency (as well as EPA) has the authority to implement and enforce this subpart. You should contact your EPA Regional Office to find out if this subpart is delegated to your st ate, local, or tribal agency.

(b) In delegating implementation and enforcement authority of this subpart to a state, local, or tri bal agency, the authorities contained in paragraph (c) of this Deleted: that meet either of the two criteria specified in paragraph (g)(1) or (2) of this section.¶
Deleted: (1) Units for which you are required to get a permit under section 3005 of the Solid Waste Disposal Act.¶ (2) Units regulated under subpart EEE of 40 CFR part 63 (National Emission Standards for Hazardous Air Pollutants from Hazardous Waste Combustors).¶
Deleted: Cyclonic barrel burners. (See §60.2265)¶
Deleted: Rack, part, and drum reclamation units. (See §60.2265)¶
Deleted: Cement kilns. Kilns regulated under subpart LLL of part 63 of this chapter (National Emission Standards for Hazardous Air Pollutants from the Portland Cement Manufacturing Industry).¶
Deleted: sludge incinerators
Deleted: Chemical recovery units. 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. The seven types of units described in paragraphs (n)(1) through (7) of this section 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.¶ (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 burning only manufacturing byproduct
Deleted: What if my chemical recovery unit is not listed in §60.2020(n)?¶ (a) If your chemical recovery unit is not listed in §60.2020(n), you can petition the Administrator to add your unit to the ... [1]

... [2]section are retained by the EPA Administrator and a re not

transferred to the state, 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) through (9) of this section.

(1) Approval of alternatives to the emission limitations in table 1 of this subpart and operatin g limits established under §60.2110.

(2) Approval of major alternatives to test methods

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(3) Approval of major alternatives to monitoring.

(4) Approval of major alternatives to recordkeepin g and reporting.

(5) [Reserved]

(6) The requirements in §60.2115.

(7) The requirements in §60.2100(b)(2).

(8) Approval of alternative opacity emission limit s

in §60.2105 under §60.11(e)(6) through (e)(8).

(9) Performance test and data reduction waivers un der

§60.2125(j).

§60.2035 How are these new source performance sta ndards structured?

These new source performance standards contain the eleven major components listed in paragraphs (a) th rough (k) of this section.

(a) Preconstruction siting analysis.

(b) Waste management plan.

(c) Operator training and qualification. Deleted: The authorities that will not be delegated to State, local, or tribal agencies are specified in paragraphs (c)(1) through (7) of this section.

Deleted: The requirements in §60.2025.(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.

§60.2040 Do all eleven components of these new so urce performance standards apply at the same time?

No. You must meet the preconstruction siting analy sis and waste management plan requirements before you c ommence construction of the CISWI unit. The operator train ing and qualification, emission limitations, operating limi ts, performance testing and compliance, monitoring, and most recordkeeping and reporting requirements are met af ter 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 a n incinerator after December 1, 2000.

(b) You must prepare a siting analysis for CISWI units that commenced construction after [INSERT THE DATE OF PUBLICATION IN THE FEDERAL REGISTER] or that commen ced reconstruction or modification after [THE DATE 6 MO NTHS AFTER PUBLICATION OF THE FINAL RULE].

(c) You must prepare a siting analysis if you are required to submit 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. Deleted: CISWI unit

Deleted: if you are required to submit 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?

(a) The siting analysis must consider air pollutio n control alternatives that minimize, on a site-speci fic basis, to the maximum extent practicable, potential risks to public health or the environment. In considerin g such alternatives, the analysis may consider costs, ener gy impacts, nonair environmental 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, local, or other fede ral 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. 2190(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 use d to reduce or separate certain components of solid wast e from the waste stream in order to reduce or eliminate to xic emissions from incinerated waste.

§60.2060 When must I submit my waste management p lan?

You must submit a waste management plan prior to commencing construction.

§60.2065 What should I include in my waste manage ment plan?

A waste management plan must include consideration of the reduction or separation of waste-stream element s such as paper, cardboard, plastics, glass, batteries, or metals; or the use of recyclable materials. The plan must i dentify any additional waste management measures and implem ent those measures the source considers practical and f easible, considering the effectiveness of waste management m easures already in place, the costs of additional measures, theemissions reductions expected to be achieved, and a ny other

environmental or energy impacts they might have.

Operator Training and Qualification

§60.2070 What are the operator training and quali fication requirements?

(a) No CISWI unit can be operated unless a fully trained and qualified CISWI unit operator is access ible, either at the facility or can be at the facility wi thin 1 hour. The trained and qualified CISWI unit operato r may operate the CISWI unit directly or be the direct su pervisor of one or more other plant personnel who operate th e unit. If all qualified CISWI unit operators are temporari ly not accessible, you must follow the procedures in §60.2 100.

(b) Operator training and qualification must be obtained through a state-approved program or by com pleting 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) through (xi) of this section.

(i) Environmental concerns, including types of emissions.

(ii) Basic combustion principles, including produc ts of combustion.

(iii) Operation of the specific type of incinerato r to be used by the operator, including proper startu p, waste charging, and shutdown procedures.

(iv) Combustion controls and monitoring.

(v) Operation of air pollution control equipment a nd factors affecting performance (if applicable).

(vi) Inspection and maintenance of the incinerator and air pollution control devices.(vii) Actions to prevent malfunctions or to prevent

conditions that may lead to malfunctions.

(viii) Bottom and fly ash characteristics and handling procedures.

(ix) Applicable federal, state, and local regulations, including Occupational Safety and Heal th Administration workplace standards.

(x) Pollution prevention.

(xi) Waste management practices.

(2) An examination designed and administered by th e instructor.

(3) Written material covering the training course topics that may serve as reference material followi ng completion of the course.

§60.2075 When must the operator training course b e completed?

The operator training course must be completed by t he later of the three dates specified in paragraphs (a ) through (c) of this section.

(a) Six months after your CISWI unit startup.

(b) December 3, 2001.

(c) The date before an employee assumes responsibility for operating the CISWI unit or assu mes responsibility for supervising the operation of the CISWI unit.

§60.2080 How do I obtain my operator qualificatio n?

(a) You must obtain operator qualification by completing a training course that satisfies the cri teria under §60.2070(b).

(b) Qualification is valid from the date on which the training course is completed and the operator succe ssfully passes the examination required under §60.2070(c)(2 ). Deleted: Actions to correct malfunctions or conditions that may lead to malfunction.§60.2085 How do I maintain my operator qualificat ion?

To maintain qualification, you must complete an ann ual review or refresher course covering, at a minimum, the five topics described in paragraphs (a) through (e) of t his section.

(a) Update of regulations.

(b) Incinerator operation, including startup and shutdown procedures, waste charging, and ash handli ng.

(c) Inspection and maintenance.

(d) Prevention of malfunctions or conditions that may lead to malfunction.

(e) Discussion of operating problems encountered b y attendees.

§60.2090 How do I renew my lapsed operator qualif ication?

You must renew a lapsed operator qualification by o ne of the two methods specified 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 describ ed in §60.2085.

(b) For a lapse of 3 years or more, you must repea t the initial qualification requirements in §60.2080( a).

§60.2095 What site-specific documentation is requ ired?

(a) Documentation must be available at the facilit y and readily accessible for all CISWI unit operators that addresses the ten topics described in paragraphs (a )(1) through (10) of this section. You must maintain th is information and the training records required by pa ragraph (c) of this section in a manner that they can be re adily accessed and are suitable for inspection upon reque st.

(1) Summary of the applicable standards under this subpart. Deleted: Responses to malfunctions or conditions that may lead to malfunction.(2) Procedures for receiving, handling, and chargi ng

waste.

(3) Incinerator startup, shutdown, and malfunction procedures.

(4) Procedures for maintaining proper combustion a ir supply levels.

(5) Procedures for operating the incinerator and associated 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 required 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 incinerator operator.

(1) The initial review of the information listed i n paragraph (a) of this section must be conducted wit hin 6 months after the effective date of this subpart or prior to an employee's assumption of responsibilities for op eration of the CISWI unit, whichever date is later.

(2) Subsequent annual reviews of the information listed in paragraph (a) of this section must be con ducted not later than 12 months following the previous rev iew.

(c) You must also maintain the information specifi ed in paragraphs (c)(1) through (3) of this section.

(1) Records showing the names of CISWI unit operat ors who have completed review of the information in §60 .2095(a) as required by §60.2095(b), including the date of t he initial review and all subsequent annual reviews.(2) Records showing the names of the CISWI operato rs

who have completed the operator training requiremen ts under §60.2070, met the criteria for qualification under §60.2080, and maintained or renewed their qualifica tion 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 qualific ation and all subsequent renewals of such qualifications.

(3) For each qualified operator, the phone and/or pager number at which they can be reached during op erating 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 hour), you must meet one of t he two criteria specified in paragraphs (a) and (b) of thi s section, depending on the length of time that a qua lified operator is not accessible.

(a) When all qualified operators are not accessibl e for more than 8 hours, but less than 2 weeks, the C ISWI unit may be operated by other plant personnel famil iar 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 whe n 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 accessibl e for 2 weeks or more, you must take the two actions that are described in paragraphs (b)(1) and (2) of this sect ion.

(1) Notify the Administrator of this deviation in writing within 10 days. In the notice, state what c aused this deviation, what you are doing to ensure that a qualified operator is accessible, and when you anti cipate that a qualified operator will be accessible.

(2) Submit a status report to the Administrator ev ery 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 access ible and requesting approval from the Administrator to conti nueoperation of the CISWI unit. You must submit the f irst

status report 4 weeks after you notify the Administ rator of the deviation under paragraph (b)(1) of this sectio n. 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) a nd (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 op eration.

Emission Limitations and Operating Limits

§60.2105 What emission limitations must I meet an d by when?

(a) You must meet the emission limitations for eac h unit, including bypass stack or vent, specified in table 1 of this subpart or tables 5 through 9 of this subpa rt 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 that commenced construction after November 30, 1999 but no later than [INSERT THE DAT E OF PUBLICATION IN THE FEDERAL REGISTER] or that commen ced reconstruction or modification on or after June 1, 2001 but no later than [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE] must meet the more stringent emission l imit for the respective pollutant in table 1 of this subpart or table 6 of subpart DDDD.

(c) Units that do not use wet scrubbers must maintain opacity to less than or equal to the percent opacit y (1- hour block average) specified in table 1 of this su bpart or tables 5 through 9 of this subpart, as applicable.

§60.2110 What operating limits must I meet and by when?

(a) If you use a wet scrubber to comply with the emission limitations, you must establish operating limits Deleted: You must meet the emission limitations specified in table 1 of this subpart 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.¶

Deleted: ¶for four operating parameters (as specified in tabl e 2 of

this subpart) as described in paragraphs (a)(1) thr ough (4) of this section during the initial performance test

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(1) Maximum charge rate, calculated using one of t he 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 ra te measured during the most recent performance test demonstrating compliance with all applicable emissi on limitations.

(ii) For batch units, maximum charge rate is 110 percent of the daily charge rate measured during th e most recent performance test demonstrating compliance wi th all applicable emission limitations.

(2) Minimum pressure drop across the wet scrubber, which is calculated as 90 percent of the average pr essure drop across the wet scrubber measured during the mo st recent performance test demonstrating compliance wi th the particulate matter emission limitations; or minimum amperage to the wet scrubber, which is calculated a s 90 percent of the average amperage to the wet scrubber measured during the most recent performance test demonstrating compliance with the particulate matte r emission limitations.

(3) Minimum scrubber liquor flow rate, which is calculated as 90 percent of the average liquor flow rate at the inlet to the wet scrubber measured during the m ost recent performance test demonstrating compliance wi th all applicable emission limitations.

(4) Minimum scrubber liquor pH, which is calculate d as 90 percent of the average liquor pH at the inlet to the wet scrubber measured during the most recent perfor mance test demonstrating compliance with the HCl emission limitation.

(b) You must meet the operating limits established during the initial performance test 60 days after y our CISWI unit reaches the charge rate at which it will operate, but no later than 180 days after its initi al 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 alar m does not sound more than 5 percent of the operating time during a 6-month period. In calculating this operating tim e percentage, if inspection of the fabric filter demo nstrates that no corrective action is required, no alarm tim e is counted. If corrective action is required, each ala rm shall be counted as a minimum of 1 hour. If you take long er than 1 hour to initiate corrective action, the alarm tim e shall be counted as the actual amount of time taken by yo u to initiate corrective action.

(d) If you use an electrostatic precipitator to comply with the emission limitations, you must meas ure the voltage and amperage of the electrostatic precipita tor collection plates during the particulate matter per formance test. Calculate the average value of these paramet ers for each test run. The minimum test run averages estab lish your site-specific minimum voltage and amperage ope rating limits for the electrostatic precipitator.

(e) If you use activated carbon injection to compl y with the emission limitations, you must measure the mercury sorbent flow rate during the mercury performance te st. The minimum mercury sorbent flow rate test run averages establish your site-specific minimum mercury sorben t flow rate.

(f) If you use selective noncatalytic reduction to comply with the emission limitations, you must esta blish the maximum charge rate, the minimum secondary cham ber temperature (if applicable to your CISWI unit), and the minimum reagent flow rate as site-specific operatin g parameters during the initial nitrogen oxides perfo rmance test to determine compliance with the emissions lim its.

§60.2115 What if I do not use a wet scrubber , activated carbon injection, selective noncatalytic reduction, or an electrostatic precipitator to comply with the emission limitations?

(a) If you use an air pollution control device other than a wet scrubber, activated carbon injection, selective noncatalytic reduction, or an electrostatic precipi tator or limit emissions in some other manner to comply with the emission limitations under §60.2105, you must petit ion the Deleted: ¶EPA Administrator for specific operating limits to be

established during the initial performance test and continuously monitored thereafter. You must not co nduct the initial performance test until after the petiti on has been approved by the Administrator. Your petition must include the 5 items listed in paragraphs (1) through (5) of this section.

( 1 ) Identification of the specific parameters you propose to use as additional operating limits.

( 2 ) A discussion of the relationship between these parameters and emissions of regulated pollutants, identifying how emissions of regulated pollutants c hange with changes in these parameters, and how limits on these parameters will serve to limit emissions of regulat ed pollutants.

( 3 ) A discussion of how you will establish the upper and/or lower values for these parameters which will establish the operating limits on these parameters.

( 4 ) A discussion identifying the methods you will us e to measure and the instruments you will use to moni tor these parameters, as well as the relative accuracy and precision of these methods and instruments.

( 5 ) A discussion identifying the frequency and methods for recalibrating the instruments you will use for monitoring these parameters.

(b) For energy recovery units that do not use a wet scrubber, you must install, operate, certify, and m aintain a continuous opacity monitoring system according to the procedures in §60.2145 by the compliance date speci fied in §60.2105.

§ 60.2120 [Removed]

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Performance Testing

§60.2125 How do I conduct the initial and annual performance test? Deleted: five
Deleted: (a)
Deleted: (e)
Deleted: a

Deleted: b

Deleted: c

Deleted: d

Deleted: e

Deleted: What happens during periods of startup, shutdown, and malfunction?¶ (a) The emission limitations and operating limits apply at all times except during CISWI unit startups, shutdowns, or malfunctions
Deleted: (b) Each malfunction must last no longer than 3 hours.(a) All performance tests must consist of a minimu m

of three test runs conducted under conditions representative of normal operations.

(b) You must document that the waste burned during the performance test is representative 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 durin g the performance test.

(c) All performance tests must be conducted using the minimum run duration specified in table 1 of this s ubpart or tables 5 through 9 of this subpart

.
(d) Method 1 of appendix A of this part must be us ed to select the sampling location and number of trave rse points.

(e) Method 3A or 3B of appendix A of this part mus t be used for gas composition analysis, including mea surement of oxygen concentration. Method 3A or 3B of appendi x A of this part must be used simultaneously with each met hod.

(f) All pollutant concentrations, except for opaci ty, must be adjusted to 7 percent oxygen using Equation 1 of this section:

C adj = C meas (20.9–7)/(20.9-%O 2 ) (Eq. 1)

Where:

C adj = pollutant concentration adjusted to 7 percent oxy gen;

C meas = pollutant concentration measured on a dry basis;

(20.9–7) = 20.9 percent oxygen−7 percent oxygen (de fined oxygen correction basis);

20.9 = oxygen concentration in air, percent; and

%O 2 = oxygen concentration measured on a dry basis, per cent.

(g) You must determine dioxins/furans toxic equivalency by following the procedures in paragrap hs (g)(1) through (3) of this section.(1) Measure the concentration of each dioxin/furan

tetra-through octachlorinated-congener emitted usin g EPA Method 23.

(2) For each dioxin/furan (tetra-through octachlorinated) congener measured in accordance wi th paragraph (g)(1) of this section, multiply the cong ener concentration by its corresponding toxic equivalenc y factor specified in table 3 of this subpart.

(3) Sum the products calculated in accordance with paragraph (g)(2) of this section to obtain the tota l concentration of dioxins/furans emitted in terms of toxic equivalency.

(h) Method 22 of 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 throug h 9 of this subpart.

(i) Except as specified in paragraphs (i)(1),(i)(2 ), (i)(3), and (i)(4) of this section, within 60 days after achieving the maximum production rate at which the affected facility will be operated, but not later than 180 d ays after initial startup of such facility, or at such other times specified by this part, and at such other tim es as may be required by the Administrator under section 114 of the Clean Air Act, the owner or operator of such fa cility must conduct performance test(s) and furnish the Administrator a written report of the results of su ch performance test(s).

(1) If a force majeure is about to occur, occurs, or has occurred for which the affected owner or operat or intends to assert a claim of force majeure, the own er or operator must notify the Administrator, in writing as soon as practicable following the date the owner or oper ator first knew, or through due diligence should have kn own that the event may cause or caused a delay in testing be yond the regulatory deadline, but the notification must occu r before the performance test deadline unless the initial fo rce majeure or a subsequent force majeure event delays the notice, and in such cases, the notification must oc cur as soon as practicable.

(2) The owner or operator must provide to the Administrator a written description of the force ma jeureevent and a rationale for attributing the delay in testing

beyond the regulatory deadline to the force majeure ; describe the measures taken or to be taken to minim ize the delay; and identify a date by which the owner or op erator proposes to conduct the performance test. The perf ormance test must be conducted as soon as practicable after the force majeure occurs.

(3) The decision as to whether or not to grant an extension to the performance test deadline is solel y within the discretion of the Administrator. The Administr ator will notify the owner or operator in writing of app roval or disapproval of the request for an extension as soon as practicable.

(4) Until an extension of the performance test deadline has been approved by the Administrator und er paragraphs (i)(1), (2), and (3) of this section, th e owner or operator of the affected facility remains strict ly subject to the requirements of this part.

(j) Performance tests must be conducted and data reduced in accordance with the test methods and pro cedures contained in this subpart unless the Administrator does one of the following.

(1) Specifies or approves, in specific cases, the use of a reference method with minor changes in methodo logy.

(2) Approves the use of an equivalent method.

(3) Approves the use of an alternative method the results of which he has determined to be adequate f or indicating whether a specific source is in complian ce.

(4) Waives the requirement for performance tests because the owner or operator of a source has demon strated by other means to the Administrator’s satisfaction that the affected facility is in compliance with the standar d.

(5) Approves shorter sampling times and smaller sample volumes when necessitated by process variabl es or other factors. Nothing in this paragraph is constr ued to abrogate the Administrator’s authority to require t esting under section 114 of the Clean Air Act.(k) Performance tests must be conducted under such

conditions as the Administrator shall specify to th e plant operator based on representative performance of the affected facility. The owner or operator must make available to the Administrator such records as may be necessary to determine the conditions of the perfor mance tests.

(l) The owner or operator of an affected facility must provide the Administrator at least 30 days pri or notice of any performance test, except as specified under other subparts, to afford the Administrator the opp ortunity to have an observer present. If after 30 days noti ce for an initially scheduled performance test, there is a delay (due to operational problems, etc.) in conducting t he scheduled performance test, the owner or operator o f an affected facility must notify the Administrator (or delegated state or local agency) as soon as possibl e of any delay in the original test date, either by providin g at least 7 days prior notice of the rescheduled date o f the performance test, or by arranging a rescheduled dat e with the Administrator (or delegated state or local agen cy) by mutual agreement.

(m) The owner or operator of an affected facility must provide, or cause to be provided, performance testing facilities as follows:

(1) Sampling ports adequate for test methods applicable to such facility. This includes the fol lowing.

(i) Constructing the air pollution control system such that volumetric flow rates and pollutant emiss ion rates can be accurately determined by applicable te st methods and procedures.

(ii) Providing a stack or duct free of cyclonic fl ow during performance tests, as demonstrated by applic able test methods and procedures.

(2) Safe sampling platform(s).

(3) Safe access to sampling platform(s).

(4) Utilities for sampling and testing equipment.(n) Unless otherwise specified in this subpart, ea ch

performance test must consist of three separate run s using the applicable test method. Each run must be condu cted for the time and under the conditions specified in the applicable standard. For the purpose of determinin g compliance with an applicable standard, the arithme tic means of results of the three runs apply. In the e vent that a sample is accidentally lost or conditions oc cur in which one of the three runs must be discontinued be cause of forced shutdown, failure of an irreplaceable portio n of the sample train, extreme meteorological conditions, or other circumstances, beyond the owner or operator’s contr ol, compliance may, upon the Administrator’s approval, be determined using the arithmetic mean of the results of the two other runs.

§60.2130 How are the performance test data used?

You use results of performance tests to demonstrate compliance with the emission limitations in table 1 of this subpart or tables 5 through 9 of this subpart

.
Initial Compliance Requirements

§60.2135 How do I demonstrate initial compliance with the emission limitations and establish the operating li mits?

You must conduct an initial 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 9 of this subpart and to establish operating limits using the procedures in §60.2110 or §60.2115. The initial performance test must be conducted using the test methods listed in table 1 of this subpart or tables 5 through 9 of this subpart and the procedures in §60.2125. The use of the bypass stack during a performance test shall invalidate the performance test.

§60.2140 By what date must I conduct the initial performance test?

The initial performance test must be conducted with in 60 days after your CISWI unit reaches the charge ra te at which it will operate, but no later than 180 days a fter its initial startup. Deleted: 8

Deleted: ¶§60.2141 By what date must I conduct the initial a ir

pollution control device inspection?

(a) The initial air pollution control device inspection must be conducted within 60 days after installation of the control device and the associat ed CISWI unit reaches the charge rate at which it will opera te, but no later than 180 days after the device’s initial s tartup.

(b) Within 10 operating days following an air pollution control device inspection, all necessary repairs must be completed unless the owner or operator obta ins written approval from the state agency establishing a date whereby all necessary repairs of the designated fac ility must be completed.

Continuous Compliance Requirements

§60.2145 How do I demonstrate continuous complian ce with the emission limitations and the operating limits?

(a) You must conduct an annual performance test fo r particulate matter, hydrogen chloride, fugitive ash, and opacity for each CISWI unit as required under §60.2125 to determine compliance with the emission limitations. The annual performance test must be conducted using the test methods listed in table 1 of this subpart or tables 5 through 9 of this subpart and the procedures in §60.2125.

(b) You must continuously monitor the operating parameters specified in §60.2110 or established und er §60.2115. Operation above the established maximum or below the established minimum operating limits constitute s a deviation from the established operating limits. T hreehour rolling average values are used to determine compliance (except for baghouse leak detection syst em alarms) unless a different averaging period is esta blished under §60.2115. Operating limits are confirmed or reestablished during performance tests

.
(c) You must only burn the same types of waste use d to establish operating limits during the performanc e test.

(d) For energy recovery units, incinerators, burn- off ovens, and small remote units, you must perform ann ual visual emissions test for ash handling. Deleted: §60.8

Deleted: do not apply during performance tests

Deleted: ¶(e) For energy recovery units, you must conduct an

annual performance test for opacity (except where particulate matter continuous emission monitoring s ystem are used for compliance) and the pollutants (except for carbon monoxide) listed in table 1 of this subpart or tables 5 through 9 of this subpart.

(f) For energy recovery units, demonstrate continu ous compliance with the carbon monoxide emission limit using a carbon monoxide continuous emission monitoring syst em according to the following requirements:

(1) Determine continuous compliance with the carbo n monoxide emissions limit using a 24-hour block aver age, calculated as specified in section 12.4.1 of EPA Re ference Method 19 of appendix A–7 of this part.

(2) Operate the carbon monoxide continuous emissio n monitoring system in accordance with the requiremen ts of performance specification 4B of appendix B of this part and quality assurance procedure one of appendix F of th is part. (g) For energy recovery units with design capacitie s greater than 250 MMBtu/hr, demonstrate continuous compliance with the particulate matter emissions li mit using a particulate matter continuous emission moni toring system according to the procedures in §60.2165(n).

(h) For waste-burning kilns, you must conduct an annual performance test for particulate matter, hyd rogen chloride, fugitive ash, and opacity (as mentioned i n section 60.2145(a)), nitrogen oxides and sulfur dio xide as listed in table 7 of this subpart. You must determ ine compliance with the mercury emissions limit using a mercury continuous emission monitoring system according to the following requirements:

(1) Operate a continuous emission monitor in accordance with performance specification 12A of 40 CFR part 60, appendix B or a sorbent trap based integra ted monitor in accordance with performance specificatio n 12B of 40 CFR part 60, appendix B or appendix K of 40 CFR part 75. The duration of the performance test must be a cale ndar month. For each calendar month in which the waste- burning kiln operates, hourly mercury concentration data, a nd stack gas volumetric flow rate data must be obtained. Deleted: ¶

Deleted: ¶(2) Owners or operators using a mercury continuous

emission monitoring system must install, operate, calibrate, and maintain an instrument for continuou sly measuring and recording the exhaust gas flow rate t o the atmosphere according to the requirements of perform ance specification 12A of 40 CFR part 60, appendix B and quality assurance procedure 5 of 40 CFR part 60, appendix F , upon promulgation.

(3) The owner or operator of a waste-burning kiln must demonstrate initial compliance by operating a mercury continuous emission monitoring system while the raw mill of the in-line kiln/raw mill is under normal operating conditions and while the raw mill of the in-line ki ln/raw mill is not operating.

(i) 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 incl ude, 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 (j) of this sectio n. This requirement also applies to you if you petition the EPA Administrator for alternative monitoring parameters under §60.13(i).

(j) For each continuous monitoring system required in this section, you must develop and submit to the EP A Administrator for approval a site-specific monitori ng plan according to the requirements of this paragraph (j) that addresses paragraphs (j)(1)(i) through (vi) of this section.

(1) You must submit this site-specific monitoring plan at least 60 days before your initial performan ce evaluation of your continuous monitoring system.

(i) Installation of the continuous monitoring system sampling probe or other interface at a measurement location relative to each affected process unit such that th e measurement is representative of control of the exh aust Deleted:emissions ( e.g. , on or downstream of the last control

device).

(ii) Performance and equipment specifications for the sample interface, the pollutant concentration or pa rametric signal analyzer and the data collection and reducti on systems.

(iii) Performance evaluation procedures and acceptance criteria ( e .g., calibrations).

(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 reporting procedures in accordance with the general requirements of §60.7(b),(c), (c)(1), (c)(4), (d), (e), (f), and (g ).

(2) You must conduct a performance evaluation of each continuous monitoring system in accordance with you r sitespecific monitoring plan.

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

(k) If you have an operating limit that requires the use of a flow measurement device, you must meet the requirements in paragraphs (j) and (k)(1) through ( 4) of this section.

(1) Locate the flow sensor and other necessary equipment in a position that provides a representat ive flow.

(2) Use a flow sensor with a measurement sensitivity of 2 percent of the flow rate.

(3) Reduce swirling flow or abnormal velocity distributions due to upstream and downstream distur bances.

(4) Conduct a flow sensor calibration check at lea st semiannually.(l) If you have an operating limit that requires the

use of a pressure measurement device, you must meet the requirements in paragraphs (j) and (l)(1) through ( 6) of this section.

(1) Locate the pressure sensor(s) in a position that provides a representative measurement of the pressu re.

(2) Minimize or eliminate pulsating pressure, vibration, and internal and external corrosion.

(3) Use a gauge with a minimum tolerance of 1.27 centimeters of water or a transducer with a minimum tolerance of 1 percent of the pressure range.

(4) Check pressure tap pluggage daily.

(5) Using a manometer, check gauge calibration quarterly and transducer calibration monthly.

(6) Conduct calibration checks any time the sensor exceeds the manufacturer's specified maximum operat ing pressure range or install a new pressure sensor.

(m) If you have an operating limit that requires the use of a pH measurement device, you must meet the requirements in paragraphs (j) and (m)(1) through ( 3) of this section.

(1) Locate the pH sensor in a position that provides a representative measurement of scrubber effluent p H.

(2) Ensure the sample is properly mixed and representative of the fluid to be measured.

(3) Check the pH meter's calibration on at least two points every 8 hours of process operation.

(n) If you have an operating limit that requires the use of equipment to monitor voltage and secondary c urrent (or total power input) of an electrostatic precipit ator, you must use voltage and secondary current monitori ng equipment to measure voltage and secondary current to the electrostatic precipitator.

(o) If you have an operating limit that requires the use of equipment to monitor sorbent injection rate ( e .g.,weigh belt, weigh hopper, or hopper flow measuremen t

device), you must meet the requirements in paragrap hs (j) and (o)(1) through (3) of this section.

(1) Locate the device in a position(s) that provides a representative measurement of the total sorbent i njection rate.

(2) Install and calibrate the device in accordance with manufacturer's procedures and specifications.

(3) At least annually, calibrate the device in accordance with the manufacturer's procedures and specifications.

(p) 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 paragraphs (p)(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 and in accordance with the guidance provided in EPA–454/R–98–015, September 1997.

(3) The bag leak detection system must be certified by the manufacturer to be capable of detecting part iculate 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 l oadings.

(5) The bag leak detection system must be equipped with a device to continuously record the output sig nal from the sensor.

(6) The bag leak detection system must be equipped with an alarm system that will sound automatically when an increase in relative particulate matter emissions o ver a preset level is detected. The alarm must be located where it is easily heard by plant operating personnel.(7) For positive pressure fabric filter systems that

do not duct all compartments of cells to a common s tack, a bag leak detection system must be installed in each baghouse compartment or cell.

(8) Where multiple bag leak detectors are required, the system's instrumentation and alarm may be share d among detectors.

(q) For facilities using a continuous emission monitoring system to demonstrate compliance with th e sulfur dioxide emission limit, compliance with the sulfur dioxide emission limit may be demonstrated by using the con tinuous emission monitoring system specified in §60.2165 to measure sulfur dioxide and calculating a 24-hour daily geom etric average emission concentration using EPA Reference Method 19, sections 4.3 and 5.4, as applicable. The sulfu r dioxide continuous emission monitoring system must be operated according to performance specification 2 i n appendix B of this part and must follow the procedu res and methods specified in this paragraph (q). For sourc es that have actual inlet emissions less than 100 parts per million dry volume, the relative accuracy criterion for inl et sulfur dioxide continuous emission monitoring syste ms should be no greater than 20 percent of the mean va lue of the reference method test data in terms of the unit s of the emission standard, or 5 parts per million dry volum e absolute value of the mean difference between the r eference method and the continuous emission monitoring syste ms, whichever is greater.

(1) During each relative accuracy test run of the continuous emission monitoring system required by performance specification 2 in appendix B of this p art, sulfur dioxide and oxygen (or carbon dioxide) data must be collected concurrently (or within a 30- to 60-minut e period) by both the continuous emission monitors an d the test methods specified in paragraphs (q)(1)(i) and (q)(1)(ii) of this section.

(i) For sulfur dioxide, EPA Reference Method 6, 6A , or 6C, or as an alternative ANSI/ASME PTC–19.10–198 1 Flue and Exhaust Gas Analysis [Part 10, Instruments and Apparatus] (incorporated by reference, see §60.17), must be used.(ii) For oxygen (or carbon dioxide), EPA Reference

Method 3, 3A, or 3B, or as an alternative ANSI/ASME PTC– 19.10–1981 Flue and Eshaust Gas Analysis [Part 10, Instruments and Apparatus] (incorporated by referen ce, see §60.17) as applicable, must be used.

(2) The span value of the continuous emission monitoring system at the inlet to the sulfur dioxid e control device must be 125 percent of the maximum e stimated hourly potential sulfur dioxide emissions of the un it subject to this rule. The span value of the contin uous emission monitoring system at the outlet of the sul fur dioxide control device must be 50 percent of the ma ximum estimated hourly potential sulfur dioxide emissions of the unit subject to this rule.

(3) Quarterly accuracy determinations and daily calibration drift tests must be performed in accord ance with procedure 1 in appendix F of this part.

(4) When sulfur dioxide emissions data are not obtained because of continuous emission monitoring system breakdowns, repairs, calibration checks, and/or zer o and span adjustments, emissions data must be obtained b y using other monitoring systems as approved by EPA or EPA Reference Method 19 to provide, as necessary, valid emissions data for a minimum of 85 percent of the h ours per day, 90 percent of the hours per calendar quarter, and 95 percent of the hours per calendar year that the aff ected facility is operated and combusting solid waste (as that term is defined by the Administrator under RCRA in 40 CFR 240).

(r) For facilities using a continuous emission monitoring system to demonstrate continuous complia nce with the nitrogen oxides emission limit, compliance with the nitrogen oxides emission limit may be demonstrated by using the continuous emission monitoring system specified in §60.2165 to measure nitrogen oxides and calculating a 24- hour daily arithmetic average emission concentratio n using EPA Reference Method 19, section 4.1. The nitrogen oxides continuous emission monitoring system must be opera ted according to performance specification 2 in appendi x B of this part and must follow the procedures and method s specified in paragraphs (r)(1) through (r)(5) of th is section.(1) During each relative accuracy test run of the

continuous emission monitoring system required by performance specification 2 of appendix B of this p art, nitrogen oxides and oxygen (or carbon dioxide) data must be collected concurrently (or within a 30- to 60-minut e period) by both the continuous emission monitors an d the test methods specified in paragraphs (r)(1)(i) and (r)(1)(ii) of this section.

(i) For nitrogen oxides, EPA Reference Method 7, 7A, 7C, 7D, or 7E must be used.

(ii) For oxygen (or carbon dioxide), EPA Reference Method 3, 3A, or 3B, or as an alternative ANSI/ASME PTC–19– 10.1981 -Flue and Exhaust Gas Analysis [Part 10, Instruments and Apparatus] (incorporated by referen ce, see §60.17) as applicable, must be used.

(2) The span value of the continuous emission monitoring system must be 125 percent of the maximu m estimated hourly potential nitrogen oxide emissions of the unit.

(3) Quarterly accuracy determinations and daily calibration drift tests must be performed in accord ance with procedure 1 in appendix F of this part.

(4) When nitrogen oxides continuous emission monitoring system data are not obtained because of continuous emission monitoring system breakdowns, r epairs, calibration checks, and zero and span adjustments, emissions data must be obtained using other monitor ing systems as approved by EPA or EPA Reference Method 19 to provide, as necessary, valid emissions data for a m inimum of 85 percent of the hours per day, 90 percent of t he hours per calendar quarter, and 95 percent of the hours p er calendar year the unit is operated and combusting m unicipal solid waste.

(5) The owner or operator of an affected facility may request that compliance with the nitrogen oxides em ission limit be determined using carbon dioxide measuremen ts 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 leve ls must be established during the initial performance test according to the procedures and methods specified i nparagraphs (r)(5)(i) through (r)(5)(iv) of this sec tion.

This relationship may be re-established during perf ormance compliance tests.

(i) The fuel factor equation in Method 3B must be used to determine the relationship between oxygen a nd carbon dioxide at a sampling location. Method 3, 3A , or 3B, or as an alternative ANSI/ASME PTC–19.10–1981 -Flue and Exhaust Gas Analysis [Part 10, Instrument and Appar atus] (incorporated by reference, see §60.17) as applicab le, must be used to determine the oxygen concentration at th e 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 3 runs must be performed.

(s) For facilities using a continuous emission monitoring system to demonstrate continuous complia nce with any of the emission limits of this subpart, you mus t complete the following:

(1) Demonstrate compliance with the appropriate emission limit(s) using a 24-hour block average, ca lculated following the procedures in EPA Method 19 of append ix A-7 of this part.

(2) Operate all continuous emission monitoring systems in accordance with the applicable procedure s under appendices B and F of this part.

(t) Use of the bypass stack at any time is an emissions standards deviation for particulate matte r, HCl, Pb, Cd, and Hg.

§60.2150 By what date must I conduct the annual performance test?

You must conduct annual performance tests within 12 months following the initial performance test. Con duct subsequent annual performance tests within 12 month s following the previous one. Deleted: for particulate matter, hydrogen chloride, and opacity§60.2151 By what date must I conduct the annual ai r

pollution control device inspection?

On an annual basis (no more than 12 months followin g the previous annual air pollution control device inspection), you must complete the air pollution co ntrol device inspection as described in §60.2141.

§60.2155 May I conduct performance testing less o ften?

(a) You can test less often for particulate matter, hydrogen chloride, fugitive ash, or opacity provide d:

(1) You have test data for at least 3 consecutive
years.

(2) The test data results for particulate matter, hydrogen chloride, fugitive ash, or opacity is less than 75 percent of the emissions or opacity limit.

(3) There are no changes in the operation of the affected source or air pollution control equipment that could affect emissions. In this case, you do not ha ve to conduct a performance test for that pollutant for t he next 2 years. You must conduct a performance test during the third year and no more than 36 months following the previous performance test.

(b) If your CISWI unit continues to emit less than 75 percent of the emission limitation for particulate matter, hydrogen chloride, fugitive ash, or opacity, and there are no changes in the operation of the affected facilit y or air pollution control equipment that could increase emi ssions, you may choose to conduct performance tests for the se pollutants every third year, but each test must be within 36 months of the previous performance test.

(c) If a performance test shows emissions exceeded 75 percent or greater of the emission or opacity limit ation for particulate matter, hydrogen chloride, fugitive ash, or opacity, you must conduct annual performance tests for that pollutant until all performance tests over a 3-year period are within 75 percent of the applicable emission limitation.

§60.2160 May I conduct a repeat performance test to establish new operating limits? Deleted: ¶

Deleted: ¶

Deleted: You can test less often for a given pollutant if you have test data for at least 3 years, and all performance tests for the pollutant (particulate matter, hydrogen chloride, or opacity) over 3 consecutive years show that
yo u comply with the emission limitation. In this case, you do not have to conduct a performance test for that pollutant for the next 2 years. You must conduct a performance test during the 3rd year and no more than 36 months following the previous performance test.¶
Deleted: meet
Deleted: If a performance test shows a deviation from an emission limitation for particulate matter, hydrogen chloride, or opacity, you must conduct annual performance tests for that pollutant until all performance tests over a 3- year period show compliance. (c)
Deleted: a deviation from an
Deleted: ¶(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 performance test at any time.

(b) You must repeat the performance test if your f eed stream is different than the feed streams used duri ng any performance test used to demonstrate compliance.

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 in stall, calibrate (to manufacturers' specifications), maint ain, and operate devices (or establish methods) for monitori ng the value of the operating parameters used to determine compliance with the operating limits listed in tabl e 2 of this subpart. These devices (or methods) must measu re 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, cal ibrate, maintain, and continuously operate a bag leak detec tion system as specified in paragraphs (b)(1) through (8 ) of this section.

(1) You must install and operate a bag leak detect ion system for each exhaust stack of the fabric filter.

(2) Each bag leak detection system must be install ed, operated, calibrated, and maintained in a manner co nsistent with the manufacturer's written specifications and recommendations.

(3) The bag leak detection system must be certifie d by the manufacturer to be capable of detecting part iculate matter emissions at concentrations of 10 milligrams per actual cubic meter or less.

(4) The bag leak detection system sensor must prov ide output of relative or absolute particulate matter l oadings.(5) The bag leak detection system must be equipped

with a device to continuously record the output sig nal from the sensor.

(6) The bag leak detection system must be equipped with an alarm system that will sound automatically when an increase in relative particulate matter emissions o ver a preset level is detected. The alarm must be located where it is easily heard 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 m ust be installed downstream of the fabric filter.

(8) Where multiple detectors are required, the system's instrumentation and alarm may be shared am ong detectors.

(c) If you are using something other than a wet scrubber , activated carbon, selective non-catalytic reduction, or an electrostatic precipitator to comply with the emission limitations under §60.2105, you must i nstall, calibrate (to the manufacturers’ specifications), m aintain, and operate the equipment necessary to monitor comp liance 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 use selective noncatalytic reduction to comply with the emission limitations, you must comp lete 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 secon dary chamber temperature (if applicable to your CISWI un it) or the minimum reagent flow rate measured as 3-hour ro lling averages (calculated each hour as the average of th eprevious 3 operating hours) at all times. Operatin g

parameter limits do not apply during performance te sts.

(2) Operation of the affected facility above the maximum charge rate, below the minimum secondary ch amber temperature and below the minimum reagent flow rate simultaneously constitute a violation of the nitrog en oxides emissions limit.

(f) If you use an electrostatic precipitator to comply with the emission limits of this subpart, yo u must monitor the voltage and amperage of the electrostat ic precipitator collection plates and maintain the 3-h our block averages at or above the operating limits est ablished during the mercury or particulate matter performanc e test.

(g) To demonstrate continuous compliance with the hydrogen chloride emissions limit, a facility may substitute use of a hydrogen chloride continuous em ission monitoring system for conducting the hydrogen chlor ide annual performance test, monitoring the minimum hyd rogen chloride sorbent flow rate, and monitoring the mini mum scrubber liquor pH.

(h) To demonstrate continuous compliance with the particulate matter emissions limit, a facility may substitute use of a particulate matter continuous e mission monitoring system for conducting the particulate ma tter annual performance test and monitoring the minimum pressure drop across the wet scrubber, if applicable.

(i) To demonstrate continuous compliance with the dioxin/furan emissions limit, a facility may substi tute use of a continuous automated sampling system for the dioxin/furan annual performance test. You must rec ord the output of the system and analyze the sample accordi ng to EPA Method 23 of appendix A-7 of this part. This o ption to use a continuous automated sampling system takes ef fect on the date a final performance specification applicab le to dioxin/furan from continuous monitors is published in the FEDERAL REGISTER. The owner or operator who elects to continuously sample dioxin/furan emissions instead of sampling and testing using EPA Method 23 of appendi x A-7 must install, calibrate, maintain, and operate a co ntinuous automated sampling system and must comply with the requirements specified in §60.58b(p) and (q).(j) To demonstrate continuous compliance with the

mercury emissions limit, a facility may substitute use of a continuous automated sampling system for the mercur y annual performance test. You must record the output of th e system and analyze the sample at set intervals using any s uitable determinative technique that can meet appropriate performance criteria. This option to use a continu ous automated sampling system takes effect on the date a final performance specification applicable to mercury fro m monitors is published in the FEDERAL REGISTER. The owner or operator who elects to continuously sample mercu ry emissions instead of sampling and testing using EPA Reference Method 29 of appendix A-8 of this part, A STM D6784-02 (2008), Standard Test Method for Elemental , Oxidized, Particle Bound and Total Mercury in Flue Gas Generated from Coal-Fired Stationary Sources (Ontar io Hydro Method), or an approved alternative method for meas uring mercury emissions, must install, calibrate, maintai n, and operate a continuous automated sampling system and must comply with the requirements specified in §60.58b(p ) and (q).

(k) To demonstrate continuous compliance with the nitrogen oxides emissions limit, a facility may sub stitute use of a continuous emission monitoring system for the nitrogen oxides annual performance test to demonstr ate compliance with the nitrogen oxides emissions limit s.

(1) Install, calibrate, maintain, and operate a continuous emission monitoring system for measuring nitrogen oxides emissions discharged to the atmosph ere and record the output of the system. The requirements under performance specification 2 of appendix B of this p art, the quality assurance procedure one of appendix F of th is part and the procedures under §60.13 must be followed f or installation, evaluation, and operation of the cont inuous emission monitoring system.

(2) Following the date that the initial performanc e test for nitrogen oxides is completed or is require d to be completed under §60.2125, compliance with the emiss ion limit for nitrogen oxides required under §60.52b(d) must be determined based on the 24-hour daily arithmetic av erage of the hourly emission concentrations using continuous emission monitoring system outlet data. The 1-hour arithmetic averages must be expressed in parts per million by volume (dry basis) and used to calculate the 24- hourdaily arithmetic average concentrations. The 1-hou r

arithmetic averages must be calculated using the da ta points required under §60.13(e)(2).

(l) To demonstrate continuous compliance with the sulfur dioxide emissions limit, a facility may subs titute use of a continuous automated sampling system for t he sulfur dioxide annual performance test to demonstra te compliance with the sulfur dioxide emissions limits

.
(1) Install, calibrate, maintain, and operate a continuous emission monitoring system 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 p art, 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 continuous emission monitoring system.

(2) Following the date that the initial performanc e test for sulfur dioxide is completed or is required to be completed under §60.2125, compliance with the sulfu r dioxide emission limit may be determined based on t he 24- hour daily geometric average of the hourly arithmet ic average emission concentrations using continuous em ission monitoring system outlet data. The 1-hour arithmet ic averages must be expressed in parts per million cor rected to 7 percent oxygen (dry basis) and used to calcula te the 24-hour daily geometric average emission concentrat ions and daily geometric average emission percent reductions . The 1-hour arithmetic averages must be calculated using the data points required under §60.13(e)(2).

(m) For energy recovery units that do not use a we t scrubber, you must install, operate, certify, and m aintain 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. Ener gy recovery units that use a particulate matter contin uous emission monitoring system to demonstrate initial a nd continuing compliance according to the procedures i n §60.2165(n) are not required to install a continuou s opacity monitoring system and must perform the annu al performance tests for the opacity consistent with §60.2145(e).(1) Install, operate, and maintain each continuous

opacity monitoring system according to performance specification 1 of 40 CFR part 60, appendix B.

(2) Conduct a performance evaluation of each continuous opacity monitoring system according to t he requirements in §60.13 and according to PS-1 of 40 CFR part 60, appendix B.

(3) As specified in §60.13(e)(1), each continuous opacity monitoring system must complete a minimum o f one cycle of sampling and analyzing for each successive 10- second period and one cycle of data recording for e ach successive 6-minute period.

(4) Reduce the continuous opacity monitoring syste m 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 energy recovery units with design capaciti es greater than 250 MMBtu/hr, in place of particulate matter testing with EPA Method 5, an owner or operator mus t install, calibrate, maintain, and operate a continu ous emission monitoring system for monitoring particula te matter emissions discharged to the atmosphere and r ecord the output of the system. The owner or operator of an affected facility who continuously monitors particu late matter emissions instead of conducting performance testing using EPA Method 5 must install, calibrate, maintai n, and operate a continuous emission monitoring system and must comply with the requirements specified in paragraph s (n)(1) through (n)(14) of this section.

(1) Notify the Administrator 1 month before starti ng use of the system.

(2) Notify the Administrator 1 month before stoppi ng use of the system.

(3) The monitor must be installed, evaluated, and operated in accordance with the requirements of per formance specification 11 of appendix B of this part and qua lity assurance requirements of procedure two of appendix F of this part and §60.13.(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 unde r §60.2125 or within 180 days of notification to the Administrator of use of the continuous monitoring s ystem if the owner or operator was previously determining co mpliance by Method 5 performance tests, whichever is later.

(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 percen t oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility must be establishe d according to the procedures and methods specified i n §60.2145(r)(5)(i) through (r)(5)(iv).

(6) The owner or operator of an affected facility must conduct an initial performance test for partic ulate matter emissions as required under §60.2125. Compl iance with the particulate matter emission limit must be determined by using the continuous emission monitor ing system specified in paragraph (n) of this section t o measure particulate matter and calculating a 24-hou r block arithmetic average emission concentration using EPA Reference Method 19, section 4.1.

(7) Compliance with the particulate matter emissio n limit must be determined based on the 24-hour daily (block) average of the hourly arithmetic average emission concentrations using continuous emission monitoring system outlet data.

(8) At a minimum, valid continuous monitoring syst em 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 t o 7 percent oxygen (dry basis) and must be used to calc ulate the 24-hour daily arithmetic average emission concentrations. The 1-hour arithmetic averages mus t be calculated using the data points required under §60.13(e)(2).(10) All valid continuous emission monitoring syst em

data must be used in calculating average emission concentrations even if the minimum continuous emiss ion monitoring system data requirements of paragraph (n )(8) of this section are not met.

(11) The continuous emission monitoring system mus t be operated according to performance specification 11 in appendix B of this part.

(12) During each relative accuracy test run of the continuous emission monitoring system required by performance specification 11 in appendix B of this part, particulate matter and oxygen (or carbon dioxide) d ata must be collected concurrently (or within a 30- to 60-mi nute period) by both the continuous emission monitors an d the following test methods.

(i) For particulate matter, EPA Reference Method 5 must be used.

(ii) For oxygen (or carbon dioxide), EPA Reference Method 3, 3A, or 3B, as applicable must be used.

(13) Quarterly accuracy determinations and daily calibration drift tests must be performed in accord ance with procedure 2 in appendix F of this part.

(14) When particulate matter emissions data are no t obtained because of continuous emission monitoring system breakdowns, repairs, calibration checks, and zero a nd span adjustments, emissions data must be obtained by usi ng other monitoring systems as approved by the Administrator or EPA Reference Method 19 to provide, as necessary, valid emissions data for a minimum of 85 percent of the h ours per day, 90 percent of the hours per calendar quarter, and 95 percent of the hours per calendar year that the aff ected facility is operated and combusting waste.

(o) For energy recovery units, operate the carbon monoxide continuous emission monitoring system in accordance with the requirements of performance specification 4B of appendix B of this part and qua lity assurance procedure 1 of appendix F of this part.

(p) The owner/operator of an affected source with a bypass stack shall install, calibrate (to manufactu rers’specifications), maintain, and operate a device or method

for measuring the use of the bypass stack including date, time and duration.

§60.2170 Is there a minimum amount of monitoring data I must obtain?

(a) Y ou must conduct all monitoring at all times the CISWI unit is operating.

(b) You must use all the data collected during all periods in assessing compliance with the operating limits.

(c) For continuous emission monitoring systems for measuring sulfur dioxide emissions, valid continuou s monitoring system hourly averages must be obtained as specified in paragraphs (c)(1) and (c)(2) of this s ection for a minimum of 85 percent of the hours per day, 9 0 percent of the hours per calendar quarter, and 95 p ercent of the hours per calendar year that the affected fa cility is combusting waste. All valid continuous emission monitoring system data must be used in calculating average emission concentrations and percent reductions even if the minimum continuous emission monitoring system data requirements of this paragraph (c) are not met.

(1) At least 2 data points per hour must be used to calculate each 1-hour arithmetic average.

(2) Each sulfur dioxide 1-hour arithmetic average must be corrected to 7 percent oxygen on an hourly basis using the 1-hour arithmetic average of the oxygen ( or carbon dioxide) continuous emission monitoring syst em data.

(d) For continuous emission monitoring systems for measuring nitrogen oxides emissions, valid continuo us emission monitoring system hourly averages must be obtained as specified in paragraphs (d)(1) and (d)(2) of thi s section for a minimum of 85 percent of the hours pe r day, 90 percent of the hours per calendar quarter, and f or 95 percent of the hours per calendar year that the aff ected facility is combusting waste. All valid continuous emission monitoring system data must be used in calculating average emission concentrations and percent reductions even if the minimum continuous emission monitoring system data requirements of this paragraph (d) are not met. Deleted: Except for monitor malfunctions, associated repairs, and required quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments of the monitoring system), y
Deleted: other
Deleted: Do not use data recorded during monitor malfunctions, associated repairs, and required quality assurance or quality control activities for meeting the requirements of this subpart, including data averages and calculations.(1) At least 2 data points per hour must be used t o

calculate each 1-hour arithmetic average.

(2) Each nitrogen oxides 1-hour arithmetic average must be corrected to 7 percent oxygen on an hourly basis using the 1-hour arithmetic average of the oxygen ( or carbon dioxide) continuous emission monitoring syst em data.

(e) For continuous emission monitoring systems for measuring particulate matter emissions, valid conti nuous monitoring system hourly averages must be obtained as specified in paragraphs (e)(1) and (e)(2) for a min imum of 85 percent of the hours per day, 90 percent of the hours per calendar quarter, and 95 percent of the days pe r calendar year that the affected source is combustin g waste. All valid continuous emission monitoring system dat a must be used in calculating average emission concentrati ons and percent reductions even if the minimum continuous e mission monitoring system data requirements of this paragra ph (e) are not met.

(1) At least 2 data points per hour must be used to calculate each 1-hour arithmetic average.

(2) Each particulate matter one-hour arithmetic average must be corrected to 7 percent oxygen on an hourly basis using the one-hour arithmetic average of the oxygen (or carbon dioxide) continuous emission monitoring system data.

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 ( u ) 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, a nd hourly charge rates. Deleted:

Deleted: fourteen
Deleted: n(2) Liquor flow rate to the wet scrubber inlet eve ry

15 minutes of operation, as applicable.

(3) Pressure drop across the wet scrubber system every 15 minutes of operation or amperage to the we t scrubber every 15 minutes of operation, as applicab le.

(4) Liquor pH as introduced to the wet scrubber ev ery 15 minutes of operation, as applicable.

(5) For affected CISWI units that establish operat ing limits for controls other than wet scrubbers under §60.2110(d) through (f) or §60.2115, you must maintain data collected for all operating parameters used to dete rmine compliance with the operating limits.

(6) If a fabric filter is used to comply with the emission limitations, you must record the date, tim e, and duration of each alarm and the time corrective acti on 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 duri ng each 6-month period that the alarm sounds, calculated as specified in §60.2110(c).

(c) [Reserved]

(d) [Reserved]

(e) Identification of calendar dates and times for which data show a deviation from the operating limi ts in table 2 of this subpart or a deviation from other o perating limits established under §60.2110(d) through (f) or §60.2115 with a description of the deviations, reas ons for such deviations, and a description of corrective ac tions taken.

(f) The results of the initial, annual, and any subsequent performance tests conducted to determine compliance with the emission limits and/or to estab lish operating limits, as applicable. Retain a copy of the complete test report including calculations.

(g) All documentation produced as a result of the siting requirements of §§60.2045 and 60.2050. Deleted: Identification of calendar dates and times for which monitoring systems used to monitor operating limits were inoperative, inactive, malfunctioning, or out of control (except for downtime associated with zero and span and other routine calibration checks). Identify the operating parameters not measured, the duration, reasons for not obtaining the data, and a description of corrective actions taken.
Deleted: Identification of calendar dates, times, and durations of malfunctions, and a description of the malfunction and the corrective action taken.(h) Records showing the names of CISWI unit operat ors

who have completed review of the information in §60 .2095(a) as required by §60.2095(b), including the date of t he initial review and all subsequent annual reviews.

(i) Records showing the names of the CISWI operato rs who have completed the operator training requiremen ts under §60.2070, met the criteria for qualification under §60.2080, and maintained or renewed their qualifica tion 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 qualific ation 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 op erating hours.

(k) Records of calibration of any monitoring devic es as required under §60.2165.

(l) Equipment vendor specifications and related operation and maintenance requirements for the inci nerator, emission controls, and monitoring equipment.

(m) The information listed in §60.2095(a).

(n) On a daily basis, keep a log of the quantity o f waste burned and the types of waste burned (always required).

(o) Maintain records of the annual air pollution control device inspections that are required for ea ch CISWI unit subject to the emissions limits in table 1 of this subpart or tables 5 through 9 of this subpart, any required maintenance, and any repairs not completed within 1 0 days of an inspection or the timeframe established by th e state regulatory agency.

(p) For continuously monitored pollutants or parameters, you must document and keep a record of the following parameters measured using continuous moni toring systems.

(1) All 6-minute average 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.

(5) All one-hour average concentrations of particulate matter emissions.

(6) All one-hour average concentrations of mercury emissions.

(7) All one-hour average concentrations of hydroge n chloride emissions.

(q) Records indicating use of the bypass stack, including dates, times, and durations.

(r) If you choose to stack test less frequently th an annually, consistent with §60.2155(a) through (c), you must keep annual records that document that your emissio ns in the previous stack test(s) were less than 75 percen t of the applicable emission limit and document that there w as no change in source operations including fuel composit ion and operation of air pollution control equipment that w ould cause emissions of the relevant pollutant to increa se 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.

(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 emissions in accordance wit h §60.11(d), including corrective actions to restore malfunctioning process and air pollution control an d monitoring equipment to its normal or usual manner of operation.

§60.2180 Where and in what format must I keep my records?All records must be available onsite in either pape r

copy or computer-readable format that can be printe d upon request, unless an alternative format is approved b y the Administrator.

§60.2185 What reports must I submit?

See table 4 of this subpart for a summary of the reporting requirements.

§60.2190 What must I submit prior to commencing construction?

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 construct.

(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 initial 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 waste 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?

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 re ports must be signed by the facilities manager.

(a) The complete test report for the initial performance test results obtained under §60.2135, a s applicable.

(b) The values for the site-specific operating lim its established in §60.2110 or §60.2115.

(c) If you are using a fabric filter to comply wit h the emission limitations, documentation that a bag leak detection system has been installed and is being op erated, 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 submission of the information in §60.2200. You must submit subsequent reports no mo re than 12 months following the previous report. (If the un it 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 an nual report?

The annual report required under §60.2205 must incl ude the ten items listed in paragraphs (a) through (j) of this section. If you have a deviation from the operatin g limits or the emission limitations, you must also submit d eviation 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 t he 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 establishe d

pursuant to §60.2110 or §60.2115.

(e) If no deviation from any emission limitation o r operating limit that applies to you has been report ed, a statement that there was no deviation from the emis sion limitations or operating limits during the reportin g period.

(f) The highest recorded 3-hour average and the lowest recorded 3-hour 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.

(h) If a performance test was conducted during the reporting period, the results of that test.

(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 dur ing the reporting period.

(j) Documentation of periods when all qualified CI SWI unit operators were unavailable for more than 8 hou rs, but less than 2 weeks.

(k) If you had a malfunction during the reporting period, the compliance report must include the numb er, duration, and a brief description for each type of malfunction that occurred during the reporting peri od and that caused or may have caused any applicable emiss ion limitation to be exceeded. The report must also include a description of actions taken by an owner or operato r during a malfunction of an affected source to minimize emi ssions in accordance with §60.11(d), including actions tak en to correct a malfunction.

(l) For each deviation from an emission or operati ng limitation that occurs for a CISWI unit for which y ou are not using a CMS to comply with the emission or oper ating limitations in this subpart, the annual report must contain the following information. Deleted: , and that no monitoring system used to determine compliance with the operating limits was inoperative, inactive, malfunctioning or out of control(1) The total operating time of the CISWI unit at

which the deviation occurred during the reporting p eriod.

(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 continu ous monitoring system, including the continuous emissio n monitoring system, was out of control as specified in paragraph (o) of this section, the annual report mu st contain the following information for each deviatio n from an emission or operating limitation occurring for a CISWI unit for which you are using a continuous monitorin g system to comply with the emission and operating limitatio ns in this subpart.

(1) The date and time that each malfunction starte d and stopped.

(2) The date, time, and duration that each CMS was inoperative, except for zero (low-level) and high-l evel checks.

(3) The date, time, and duration that each continu ous monitoring system was out-of-control, including sta rt 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 deviati on during the reporting period, and the total duration as a percent of the total source operating time during t hat reporting period.

(6) A breakdown of the total duration of the deviations during the reporting period into those t hat 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 per iod, and the total duration of continuous monitoring system downtimeas a percent of the total operating time of the CIS WI unit

at which the continuous monitoring system downtime occurred during that reporting period.

(8) An identification of each parameter and pollut ant that was monitored at the CISWI unit.

(9) A brief description of the CISWI unit.

(10) A brief description of the continuous monitor ing system.

(11) The date of the latest continuous monitoring system certification or audit.

(12) A description of any changes in continuous monitoring system, processes, or controls since the last reporting period.

(n) If there were periods during which the continu ous monitoring system, including the continuous emissio n monitoring system, was not out of control as specif ied in paragraph (o) of this section, a statement that the re 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 contr ol if any of the following occur.

(1) The zero (low-level), mid-level (if applicable ), or high-level calibration drift exceeds two times t he applicable calibration drift specification in the applicable performance specification or in the rele vant standard.

(2) The continuous monitoring system fails a performance test audit (e.g., cylinder gas audit), relative accuracy audit, relative accuracy test audit, or li nearity test audit.

(3) The continuous opacity monitoring system calibration drift exceeds two times the limit in th e applicable performance specification in the relevan t standard.

§60.2215 What else must I report if I have a devi ation from the operating limits or the emission limitatio ns?(a) You must submit a deviation report if any

recorded 3-hour average parameter level is above th e maximum operating limit or below the minimum operat ing limit established under this subpart, if the bag le ak detection system alarm sounds for more than 5 perce nt of the operating time for the 6-month reporting period , or if a performance test was conducted that deviated from any emission limitation.

(b) The deviation report must be submitted by Augu st 1 of that year for data collected during the first half of the calendar year (January 1 to June 30), and by Fe bruary 1 of the following year for data you collected during the second half of the calendar year (July 1 to Decembe r 31).

§60.2220 What must I include in the deviation rep ort?

In each report required under §60.2215, for any pollutant or parameter that deviated from the emiss ion limitations or operating limits specified in this s ubpart, include the six items described in paragraphs (a) t hrough (f) of this section.

(a) The calendar dates and times your unit deviate d from the emission limitations or operating limit requirements.

(b) The averaged and recorded data for those dates

.
(c) Durations and causes of the following:

(1) E ach deviation from emission limitations or operating limits and your corrective actions.

(2) Bypass events and your corrective actions.

(d) A copy of the operating limit monitoring data during each deviation and any test report that docu ments the emission levels.

(e) [Removed]

(f) [Removed]

§60.2225 What else must I report if I have a devi ation from the requirement to have a qualified operator accessible? Deleted: ¶

Deleted: e

Deleted: The dates, times, number, duration, and causes for monitor downtime incidents (other than downtime associated with zero, span, and other routine calibration checks).
Deleted: Whether each deviation occurred during a period of startup, shutdown, or malfunction, or during another period.(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 qualifie d operator will be available.

(2) Submit a status report to the Administrator ev ery 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 Administrato r, under the provisions of §60.2100(b)(2), due to a fa ilure to provide an accessible qualified operator, you must notify the Administrator that you are resuming operation o nce a qualified operator is accessible.

§60.2230 Are there any other notifications or rep orts that I must submit?

Yes. You must submit notifications as provided by §60.7.

§60.2235 In what form can I submit my reports?

(a) Submit initial, annual, and deviation reports electronically or in paper format, postmarked on or before the submittal due dates.(b) After December 31, 2011, within 60 days after the

date of completing each performance evaluation cond ucted to demonstrate compliance with this subpart, the owner or operator of the affected facility must submit the t est data to EPA by entering the data electronically into EPA ’s WebFIRE database through EPA’s Central Data Exchang e. The owner or operator of an affected source shall enter the test data into EPA’s database using the Electronic Reporting Tool or other compatible electronic sprea dsheet. Only performance evaluation data collected using me thods compatible with ERT are subject to this requirement to be submitted electronically into EPA’s WebFIRE databas e.
§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 reportin g date.

Title V Operating Permits

§60.2242 Am I required to apply for and obtain a title V operating permit for my unit?

Yes. Each CISWI unit and air curtain incinerator affected by this subpart must operate pursuant to a permit issued under S ection 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 forcefu lly projecting a curtain of air across an open chamber or open pit in which combustion occurs. Incinerators of thi s type can be constructed above or below ground and with o r without refractory walls and floor. (Air curtain incinerators are not to be confused with convention al combustion devices with enclosed fireboxes and cont rolled air technology such as mass burn, modular, and flui dized bed combustors.)

(b) Air curtain incinerators that burn only the materials listed in paragraphs (b)(1) through (3) o f this section are only required to meet the requirements under “Air Curtain Incinerators” (§§60.2245 through 60.22 60). Deleted: ¶

Deleted: by the later of the two dates in paragraphs (a) and (b) of this section.
Deleted: s
Deleted: (a) Thirty-six months after December 1, 2000.¶ (b) The effective date of the title V permit program to which your unit is subject. If your unit is subject to title V as a result of some triggering requirement(s) other than this subpart (for example, being a major source), then your unit may be required to apply for and obtain a title V permit prior to the deadlines noted above. If more than one requirement triggers the requirement to apply for a title V permit, the 12-month timeframe for filing a title V application is triggered by the requirement which first causes the source to be subject to title V.¶(1) 100 percent wood waste.

(2) 100 percent clean lumber.

(3) 100 percent mixture of only wood waste, clean lumber, and/or yard waste.

§60.2250 What are the emission limitations for ai r curtain incinerators?

Within 60 days after your air curtain incinerator reaches the charge rate at which it will operate, b ut 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 th ree 1- hour blocks consisting of ten 6-minute average opac ity values), except as described in paragraph (b) of th is section.

(b) Maintain opacity to less than or equal to 35 percent opacity (as determined by the average of th ree 1- hour blocks consisting of ten 6-minute average opac ity values) during the startup period that is within th e first 30 minutes of operation.

§60.2255 How must I monitor opacity for air curta in 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 specifi ed in §60.8.

(c) After the initial test for opacity, conduct annual tests no more than 12 calendar months follow ing 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 describ ed in paragraphs (a)(1) through (3) of this section. Deleted: (a)

Deleted: 2
Deleted: (1)

Deleted: (1) The opacity limitation is 10 percent (6- minute average), except as described in paragraph (a)(2) of this section.¶ (2) The opacity limitation is 35 percent (6-minute average) during the startup period that is within the first 30 minutes of operation.¶ (b) Except during malfunctions, the requirements of this subpart apply at all times, and each malfunction must not exceed 3 hours.¶(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 ai r curtain incinerator.

(b) Keep records of results of all initial and ann ual opacity tests onsite in either paper copy or electr onic format, unless the Administrator approves another f ormat, for at least 5 years.

(c) Make all records available for submittal to th e Administrator or for an inspector's onsite review.( d) You must submit the results ( as determined by the average of three 1-hour blocks consisting of ten 6-minute average opacity values ) of the initial opacity tests no later than 60 days following the initial test. Submit annual o pacity test results within 12 months following the previou s report.

(e) Submit initial and annual opacity test reports as electronic or paper copy on or before the applicabl e 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 subpart are defi ned in the Clean Air Act and subpart A (General Provisi ons) of this part.

Administrator means the Administrator of the U.S. Environmental Protection Agency or his/her authoriz ed representative or Administrator of a State Air Poll ution Control Agency.

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 without refractory walls and flo or. (Air Deleted: ¶

Deleted: each

Deleted: ¶

Deleted: Agricultural waste means vegetative agricultural materials such as nut and grain hulls and chaff (e.g., almond, walnut, peanut, rice, and wheat), bagasse, orchard prunings, corn stalks, coffee bean hulls and grounds, and other vegetative waste materials generated as a result of agricultural operations.¶curtain incinerators are not to be confused with

conventional combustion devices with enclosed fireb oxes and controlled air technology such as mass burn, modula r, and fluidized bed combustors.)

Auxiliary fuel means natural gas, liquified petroleum gas, fuel oil, or diesel fuel.

Bag leak detection system means an instrument that is capable of monitoring particulate matter loadings i n the exhaust of a fabric filter (i.e., baghouse) in orde r to detect bag failures. A bag leak detection system in cludes, but is not limited to, an instrument that operates on triboelectric, light scattering, light transmittanc e, or other principle to monitor relative particulate mat ter loadings.

Burn-off oven means any rack reclamation unit, part reclamation unit, or drum reclamation unit.

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 December 31.

Chemotherapeutic waste means waste material resulting from the production or use of antineoplastic agents used for the purpose of stopping or reversing the growth of malignant cells.

Clean lumber means wood or wood products that have been cut or shaped and include wet, air-dried, and kilndried wood products. Clean lumber does not include wood products that have been painted, pigment-stained, o r pressure-treated by compounds such as chromate copp er 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 any solid waste as that term is defined in 40 CFR Part 241. Whilenot all CISWI units will include all of the followi ng

components, a CISWI unit includes, but is not limit ed to, the solid waste feed system, grate system, flue gas system, waste heat recovery equipment, if any, and bottom a sh system. The CISWI unit does not include air polluti on control equipment or the stack. The CISWI unit boun dary starts at the solid waste hopper (if applicable) an d extends through two areas: The combustion unit flue gas system, which ends immediately after the last combu stion chamber or after the waste heat recovery equipment, if any; and the combustion unit bottom ash system, which en ds 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 comb usted.

Cyclonic barrel burner means a combustion device for waste materials that is attached to a 55 gallon, op en-head drum. The device consists of a lid, which fits onto and encloses the drum, and a blower that forces combust ion air into the drum in a cyclonic manner to enhance the m ixing of waste material and air.

Deviation means any instance in which an affected source subject to this subpart, or an owner or oper ator of such a source:

(1) Fails to meet any requirement or obligation established by this subpart, including but not limi ted to any emission limitation, operating limit, or operat or qualification and accessibility requirements

.
(2) Fails to meet any term or condition that is adopted to implement an applicable requirement in t his subpart and that is included in the operating permi t for any affected source required to obtain such a permi t

.
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 incinerat ion unit without energy recovery. Formatted: Font color: Auto Deleted: ¶ means any combustion unit that combusts commercial or industrial waste (as defined in this subpart), that is a distinct operating unit of any commercial or industrial facility (including field erected, modular, and custom built incineration units operating with starved or excess air), and any air curtain incinerator that is a distinct operating unit of any commercial or industrial facility that does not comply with the opacity limits under this subpart applicable to air curtain incinerators burning commercial or industrial waste. While not all CISWI units will include all of the following components, a CISWI unit includes, but is not limited to, the commercial or industrial 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 commercial or industrial 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 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. A CISWI unit does not

Deleted: ; Deleted: ; or
Deleted: (3) Fails to meet any emission limitation, operating limit, or operator qualification and accessibility requirement in this subpart during startu p, shutdown, or malfunction, regardless or whether or not such failure is permitted by this subpart. ... [3]Drum reclamation unit means a unit that burns residues

out of drums (e.g., 55 gallon drums) so that the dr ums can be reused.

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 under RCRA in 40 CFR 240) for energy recovery. Energy recovery units include units that would be considered include boilers and process heaters i f they did not combust solid waste.

Fabric filter means an add-on air pollution control device used to capture particulate matter by filter ing gas streams through filter media, also known as a bagho use.

Incinerator

means any furnace used in the process of combusting solid waste (as that term is defined by the Administrator under RCRA in 40 CFR 240) for the pur pose of reducing the volume of the waste by removing combus tible matter. Incinerator designs include single chamber , twochamber, and cyclonic burn barrels.

Kiln means an oven or furnace, including any associated preheater or precalciner devices, used f or processing a substance by burning, firing or drying . Kilns include cement kilns, that produce clinker by heati ng limestone and other materials for subsequent produc tion of Portland cement and lime kilns, that produce quickl ime by calcination of limestone.

Low-level radioactive waste means waste material which contains radioactive nuclides emitting primarily be ta or gamma radiation, or both, in concentrations or quan tities that exceed applicable federal or state standards f or unrestricted release. Low-level radioactive waste i s not high-level radioactive waste, spent nuclear fuel, o r byproduct material as defined by the Atomic Energy Act of 1954 (42 U.S.C. 2014(e)(2)).

Minimum voltage or amperage means 90 percent of the lowest test-run average voltage or amperage to the electrostatic precipitator measured from the pressu re drop and liquid flow rate monitors during the most recen t Deleted: Malfunction means any sudden, infrequent, and not reasonably preventable failure of air pollution control 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.¶particulate matter or mercury performance test

demonstrating compliance with the applicable emissi on limits.

Modification or modified CISWI unit means a CISWI unit you have changed later than June 1, 2001 and that m eets one of two criteria:

(1) The cumulative cost of the changes over the li fe of the unit exceeds 50 percent of the original cost of building and installing the CISWI unit (not includi ng the cost of land) updated to current costs (current dol lars). To determine what systems are within the boundary o f the CISWI unit used to calculate these costs, see the definition of CISWI unit.

(2) Any physical change in the CISWI unit or chang e in the method of operating it that increases the am ount of any air pollutant emitted for which section 129 or section 111 of the Clean Air Act has established standards.

Opacity

means the degree to which emissions reduce the transmission of light and obscure the view of an ob ject in the background.

Part reclamation unit means a unit that burns coatings off parts (e.g., tools, equipment) so that the part s 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 tra nsport the waste material, and animal bedding (if applicab le).

Rack reclamation unit means a unit that burns the coatings off racks used to hold small items for app lication of a coating. The unit burns the coating overspray off the rack so the rack can be reused.

Raw mill means a ball and 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 fromthe 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 als o includes the air separator associated with the raw mill.

Reconstruction means rebuilding a CISWI unit and meeting two criteria:

(1) The reconstruction begins on or after June 1, 2001.

(2) The cumulative cost of the construction over t he life of the incineration unit exceeds 50 percent of the original cost of building and installing the CISWI unit (not including land) updated to current costs (curr ent 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 al l classes of refuse-derived fuel including two fuels:

(1) Low-density fluff refuse-derived fuel through densified refuse-derived fuel.

(2) Pelletized refuse-derived fuel.

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 th e Administrator under RCRA in 40 CFR 240) and has the capacity to combust 1 ton per day or less solid was te and is more than 50 miles driving distance to the neare st municipal solid waste landfill.

Solid waste incineration unit means a distinct operating unit of any facility which combusts any s olid waste material from commercial or industrial establ ishments or the general public (including single and multipl e residences, hotels and motels). Such term does not include incinerators or other units required to have a perm it under section 3005 of the Solid Waste Disposal Act. The t erm "solid waste incineration unit" does not include (A ) Formatted: No underline Deleted: Solid waste means any garbage, refuse, sludge from a waste treatment plant, water supply treatment plant, or air pollution control facility and other discarded material, including solid, liquid, semisolid, or contained gaseous material resulting from industrial, commercial, mining, agricultural operations, and from community activities, but does not include solid or dissolved material in domestic sewage, or solid or dissolved materials in irrigation return flows or industrial discharges which are point sources subject to permits under section 402 of the Federal Water Pollution Control Act, as amended (33 U.S.C. 1342), or source, special nuclear, or byproduct material as defined by the Atomic Energy Act of 1954, as amended (42 U.S.C. 2014).¶materials recovery facilities (including primary or

secondary smelters) which combust waste for the pri mary purpose of recovering metals, (B) qualifying small power production facilities, as defined in section 3(17)( C) of the Federal Power Act (16 U.S.C. 769(17)(C)), or qu alifying 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 units which burn tires o r used oil, but not including refuse-derived fuel) for the production of electric energy or in the case of qua lifying cogeneration facilities which burn homogeneous wast e for the production of electric energy and steam or form s of useful energy (such as heat) which are used for ind ustrial, commercial, heating or cooling purposes, or (C) air curtain incinerators provided that such incinerators only b urn wood wastes, yard wastes and clean lumber and that such air curtain incinerators comply with opacity limitation s to be established by the Administrator by rule.

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 the first charge to th e unit.

Waste-burning kiln means a cement kiln that is heated, in whole or in part, by combusting solid waste (as that term is defined by the Administrator under RCRA in 40 CFR 240).

Wet scrubber means an add-on air pollution control device that utilizes an aqueous or alkaline scrubbi ng liquor to collect particulate matter (including non vaporous 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 d oes not include:

(1) Grass, grass clippings, bushes, shrubs, and clippings from bushes and shrubs from residential, commercial/retail, institutional, or industrial sou rces as part of maintaining yards or other private or publi c lands.(2) Construction, renovation, or demolition wastes

.
(3) Clean lumber.

Table 1 to Subpart CCCC of Part 60—Emission Limitat ions for CISWI Units for Which Construction Is Commenced Aft er November 30, 1999, but no later than [INSERT THE DA TE OF PUBLICATION IN THE FEDERAL REGISTER] or for Which Modification or Reconstruction Is Commenced on or A fter June 1, 2001, but no later than [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE].

For the air pollutant You must meet

this emission 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, 10A, or 10B of appendix A of this part).
Dioxins/furans (toxic equivalency basis) 0.41

nanograms per dry standard cubic meter 3-run

average (1 hour minimum sample time per run) Performance test

(Method 23 of appendix A of this part).

Hydrogen chloride 62 parts per

million by dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 26A of appendix A of this part).

Lead 0.04

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).

Mercury 0.47

milligrams per dry 3-run

average (1 hour minimum Performance test

(Method 29 of appendix A ofstandard cubic meter sample time

per run) this part).

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 (1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A of this part.

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.
Table 2 to Subpart CCCC of Part 60—Operating Limits for Wet Scrubbers

And monitoring using these minimum frequencies For these operating parameters You must

establish these operating limits 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 Minimum

pressure Continuous Every 15 minutes 3-hour

rolling athe wet

scrubber or amperage to wet scrubber drop or

amperage

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 Equivalenc y Factors

Dioxin/furan congener Toxic equivalency factor
2,3,7,8-tetrachlorinated dibenzo-pdioxin 1

1,2,3,7,8-pentachlorinated dibenzo-pdioxin 0.5

1,2,3,4,7,8-hexachlorinated dibenzo-pdioxin 0.1

1,2,3,7,8,9-hexachlorinated dibenzo-pdioxin 0.1

1,2,3,6,7,8-hexachlorinated dibenzo-pdioxin 0.1

1,2,3,4,6,7,8-heptachlorinated dibenzop-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 0.11,2,3,7,8,9-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 Repor ting Requirements a

Report Due date Contents Reference

Preconstruction report Prior to

commencing construction • Statement of

intent to construct • Anticipated date of commencement of construction

• Documentation for siting requirements • Waste management plan • Anticipated date of initial startup §60.2190

Startup notification Prior to

initial startup • Type of

waste to be burned • Maximum design waste burning capacity §60.2195• Anticipated maximum charge rate • If applicable, the petitionfor sitespecific operating limits

Initial test report No later than

60 days following the initial performance test • Complete

test report for the initial performance test • The valuesfor the sitespecific 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 limits

• Highest recorded 3- hour average and the lowest 3-hour
average, as applicable, §§60.2205 and

60.2210

Deleted: • If no deviations or malfunctions were reported, a statement that no deviations occurred during the reporting periodfor each operating parameter recorded for the calendar year being reported • If a performance test was conducted during the reporting period, the results of the test • If a performance test was not conducted during the reporting period, a statement that the requirements of §60.2155(a) or (b) were met

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

Emission limitation or operating limit deviation report By August 1 of

that year for data collected during the first half of • Dates and

times of deviation • Averaged and recorded data §60.2215 and

60.2220 Deleted: • Information for deviations or malfunctions recorded under §60.2175(b)(6) and (c) through (e)the calendar year. By February 1 of the following year for data collected during the second half of the calendar
year for those

dates • Duration and causes of each deviation and the corrective actions taken • Copy of operating limit monitoring data and any test reports • Dates, times, and causes for monitor downtime incidents

Qualified operator deviation notification Within 10 days

of deviation • Statement of

cause of deviation • Description of efforts 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 §60.2225(a)(2) Deleted: • Whether each deviation occurred during a period of startup, shutdown, or malfunctionoperation

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 se ctions of the rule for the complete requirements.

Table 5 to Subpart CCCC of Part 60—Emission Limitat ions for Incinerators That Commenced Construction After [INSERT THE DATE OF PUBLICATION IN THE FEDERAL REGISTER] Or Tha t Commenced Reconstruction or Modification After [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE]

For the air pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.00066

milligrams per dry standard cubic meter 3- run average

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Carbon monoxide 1.4 parts

per million dry volume 24 hour block

average Carbon monoxide

continuous emission monitoring system (performance specification 4A of this part, using a RA of 0.5 ppm instead of 5 ppm as specified in 13.2. For the cylinder gas audit, +/- 15% or 0.5 ppm, whichever is greater.)
Dioxins/furans 0.0093 3- run average Performance test Deleted: nFor the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

(total mass basis) nanograms

per dry standard cubic meter (collect a

minimum volume of 4 dry standard cubic meters) (Method 23 of

appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 0.00073

nanograms per dry standard cubic meter 3- run average

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

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 0.074 parts

per million dry volume 3- run average

(collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 26A of appendix A-8 of this part).

Lead 0.0013

milligrams per dry standard cubic meter 3-run averag e

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.
Mercury 0.00013

milligrams per dry standard cubic meter 3- run average

(collect enough volume to meet a detection limit data quality objective of 0.03 ug/dscm) Performance test

(Method 30B of appendix A-8 of this part)

Opacity 1 percent Three 1-hour blocks consisting of ten 6-minute
average opacity values Performance test

(Method 9 of appendix A-4 of this part). Formatted: Not Highlight

Formatted: Not HighlightFor the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Oxides of nitrogen 19 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part). Use a span gas with a concentration of 100 ppm or less.

Particulate matter (filterable) 0.0077

milligrams per dry standard cubic meter 3- run average

(collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 5 or 29 of appendix A-3 or appendix A-8 of this part).

Sulfur dioxide 1.5 parts

per million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a maximum allowable drift of 0.2 ppm and a span gas with a concentration of 5 ppm or less.
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 of appendix A-7 of this part).

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.

Table 6 to Subpart CCCC of Part 60—Emission Limitat ions for Energy Recovery Units That Commenced Construction A fter [INSERT THE DATE OF PUBLICATION IN THE FEDERAL REGI STER] Or That Commenced Reconstruction or Modification After [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE] Deleted:For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.00012

milligrams per dry standard cubic meter 3- run average

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Carbon monoxide 3 parts per

million dry volume 24 hour block

average Carbon Monoxide

continuous emission monitoring system (Performance Specification 4A of this part, using a RA of 0.5 ppm instead of 5 ppm as specified in 13.2. For the cylinder gas audit, +/- 15% or 0.5 ppm, whichever is greater.
Dioxins/furans (total mass basis) 0.034

nanograms per dry standard cubic meter 3- run average

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

(Method 23 of appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 0.0027

nanograms per dry standard cubic meter 3- run average

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

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 0.17 parts

per million dry volume 3- run average

(collect a minimum volume of 2 dry standard cubic meters Performance test

(Method 26A of appendix A-8 of this part).
Deleted:For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Lead 0.0012

milligrams per dry standard cubic meter 3- run average

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.
Mercury 0.00013

milligrams per dry standard cubic meter 3- run average

(collect enough volume to meet a detection limit data quality objective of 0.03 ug/dscm) Performance test

(Method 30B of appendix A-8 of this part.

Opacity 1 percent 6-minute
averages; 1-hour block average for units that operate dry control systems Continuous opacity

monitoring (performance

s pecification 1 of appendix B of this part), unless equipped with a wet scrubber.

Oxides of nitrogen 75 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part).

Particulate matter (filterable) 4.4

milligrams per dry standard cubic meter 3- run average

(collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 5 or 29 of appendix A-3 or appendix A-8 of this part) if the unit has a design capacity less than or equal to 250 MMBtu/hr; or PM CEMS (performance specification 11 of appendix B of Formatted: Not Highlight

Formatted: Not HighlightFor the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method
this part) if the unit has a design capacity greater than 250 MMBtu/hr.

Sulfur dioxide 4.1 parts

per million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a span gas with a concentration of 20 ppm or less.
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 of appendix A-7 of this part).

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.

Table 7 to Subpart CCCC of Part 60—Emission Limitat ions for Waste-burning Kilns That Commenced Construction After [INSERT THE DATE OF PUBLICATION IN THE FEDERAL REGI STER] Reconstruction or Modification After [THE DATE 6 MO NTHS AFTER PUBLICATION OF THE FINAL RULE]

For the air pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.00030

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 4 Performance test

(Method 29 of appendix A-8 of this part). Use ICPMS for theFor the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

d ry standard cubic meters) analytical finish.

Carbon monoxide 36 parts per

million dry volume 24 hour

block
average Carbon monoxide

continuous emission monitoring system (performance specification 4A of this part, using an RA of 1 ppm instead of 5 ppm as specified in 13.2. For the cylinder gas audit, +/- 15% or 0.5 ppm, whichever is greater).
Dioxins/furans (total mass basis) 0.00035

nanograms per dry standard cubic meter 3-run

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

(Method 23 of appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 0.000028

nanograms per dry standard cubic meter 3-run

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

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 1.5 parts

per million dry volume 3-run

average (collect a minimum volume of 1 dry standard Performance test

(Method 26A of appendix A-8 of this part). Deleted:For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method
cubic meter)

Lead 0.00078

milligrams per dry standard cubic meter 3-run

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Mercury 0.024

milligrams per dry standard cubic meter 24 hour

block
average Mercury CEMS

(performance specification 12A of appendix B of this part or mercury sorbent trap method specified in appendix K of part 75).
Opacity 1 percent Three 1- hour blocks consisting of ten 6- minute
average opacity values Performance test

(Method 9 of appendix A-4 of this part).

Oxides of nitrogen 140 parts

per million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part).

Particulate matter (filterable) 1.8

milligrams per dry standard cubic meter 3-run

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

(Method 5 or 29 of appendix A-3 or appendix A-8 of this part).For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

meters)

Sulfur dioxide 3.6 parts

per million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a span gas with a concentration of 20 ppm or less.
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 of appendix A-7 of this part).

a All emission limitations (except for opacity) are measured at 7 percent oxygen, dry basis at standard conditions.

Table 8 to Subpart CCCC of Part 60—Emission Limitat ions for Burn-off Ovens That Commenced Construction After [INSERT THE DATE OF PUBLICATION IN THE FEDERAL REGISTER] Or That Commenced Reconstruction or Modification After [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL FULE]

For the air pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.0032

milligrams per dry standard cubic meter 3- run average

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish. Deleted:For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Carbon monoxide 74 parts per

million dry volume 24 hour block

average Carbon monoxide

continuous emission monitoring system (performance specification 4A of this part, using a RA of 2 ppm instead of 5 ppm as specified in 13.2. For the cylinder gas audit, +/- 15% or 0.5 ppm, whichever is greater).
Dioxins/furans (total mass basis) 0.011

nanograms per dry standard cubic meter 3- run average

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

(Method 23 of appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 0.00086

nanograms per dry standard cubic meter 3- run average

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

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 17.6 parts

per million dry volume 3- run average

(collect a minimum volume of 1 dry standard cubic meters) Performance test

(Method 26A of appendix A-8 of this part).

Lead 0.029

milligrams per dry standard cubic meter 3- run average

(collect a minimum volume of 1 dry standard cubic meters) Performance test

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish. Deleted: s

Deleted: sFor the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method
Mercury 0.0033

milligrams per dry standard cubic meter 3- run average

(collect enough volume to meet a detection limit data quality objective of 0.3 ug/dscm) Performance test

(Method 30B of appendix A-8 of this part).

Opacity 2 percent Three 1-hour blocks consisting of ten 6-minute
average opacity values Performance test

(Method 9 of appendix A-4 of this part).

Oxides of nitrogen 16 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part). Use a span gas with a concentration of 100 ppm or less.

Particulate matter (filterable) 28

milligrams per dry standard cubic meter 3- run average

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

(Method 5 or 29 of appendix A-3 and A-8 of this part).

Sulfur dioxide 1.5 parts

per million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a maximum allowable drift of 0.2 ppm and a span gas with concentration of 5 ppm or less.
Fugitive ash Visible Three 1-hour Visible emission Deleted:For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

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

periods test (Method 22 of

appendix A-7 of this part).

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.

Table 9 to Subpart CCCC of Part 60—Emission Limitat ions for Small, Remote Incinerators That Commenced Construct ion After [INSERT THE DATE OF PUBLICATION IN THE FEDERA L REGISTER] Or That Commenced Reconstruction or Modif ication After (THE DATE 6 MONTHS AFTER PUBLICATION OF THE F INAL RULE]

For the air pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.057

milligrams per dry standard cubic meter 3-run

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Carbon monoxide 4.0 parts

per million dry volume 24 hour

block
average Carbon monoxide

continuous emission monitoring system (performance specification 4A of this part, using a RA of 0.5 ppm instead of 5 ppm as specifiedFor the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

in 13.2. For the cylinder gas audit, +/- 15% or 0.5 ppm, whichever is greater.)
Dioxins/furans (total mass basis) 1200

nanograms per dry standard cubic meter 3-run

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

(Method 23 of appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 94 nanograms

per dry standard cubic meter 3-run

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

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 150 parts

per million by dry volume 3-run

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

(Method 26 or 26A of appendix A-8 of this part).

Lead 1.4

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 1 dry standard cubic) Performance test

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Mercury 0.0013

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 1 dry standard Performance test

(Method 29 of appendix A-8 of this part).For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method
cubic meter)
Opacity 13 percent Three 1- hour blocks consisting of ten 6- minute
average opacity values Performance test

(Method 9 of appendix A-4 of this part).

Oxides of nitrogen 210 parts

per million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part).

Particulate matter (filterable) 240

milligrams per dry standard cubic meter 3-run

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

(Method 5 or 29 of appendix A-3 or appendix A-8 of this part).

Sulfur dioxide 43 parts per

million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a span gas with a concentration of 200 ppm or less.
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 of appendix A-7 of this part).

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns. Deleted:Subpart DDDD—Emissions Guidelines and Compliance Ti mes for

Commercial and Industrial Solid Waste Incineration Units

Introduction

§60.2500 What is the purpose of this subpart?

This subpart establishes emission guidelines and compliance schedules for the control of emissions f rom commercial and industrial solid waste incineration (CISWI) units. The pollutants addressed by these emission guidelines are listed in table 2 of this subpart and tables 6 through 10 of this subpart . These emission guidelines are developed in accordance with sections 111(d) an d 129 of the Clean Air Act and subpart B of this part.

§60.2505 Am I affected by this subpart?

(a) If you are the Administrator of an air quality program in a state or United States protectorate wi th one or more existing CISWI units that meets the criteria in paragraphs (b) through (d) of this section , you must submit a state plan to U.S. Environmental Protection Agenc y (EPA) that implements the emission guidelines contained i n this subpart.

(b) You must submit the state plan to EPA by Decem ber 3, 2001 , for incinerators that commenced construction on o r before November 30, 1999, and that were not modifie d or reconstructed after June 1, 2001.

(c) You must submit a state plan to EPA that meets the requirements of this subpart and contains the m ore stringent emission limit for the respective polluta nt in table 6 of this subpart or table 1 of subpart CCCC of this part to EPA by [THE DATE 1 YEAR AFTER PUBLICATION O F THE FINAL RULE IN THE Federal Register] for incinerator s that commenced construction after November 30, 1999, but no later than [INSERT THE DATE OF PUBLICATION IN THE F ederal Register] or commenced modification or reconstructi on after June 1, 2001, but no later than [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE IN THE FEDERAL REGIST ER]

.

(d) You must submit a state plan to EPA that meets the requirements of this subpart and contains the e mission limits in tables 7 through 10 of this subpart by [T HE DATE 1 YEAR AFTER PUBLICATION OF THE FINAL RULE IN THE F ederal Formatted: Underline
Formatted: Underline
Formatted: Underline
Formatted: Underline

Formatted: Underline Deleted: ¶
Deleted: that Commenced Construction On or Before November 30, 1999

Deleted: commenced construction on or before November 30, 1999Register] for CISWI units other than incinerators t hat

commenced construction on or before [INSERT THE DAT E OF PUBLICATION OF THE PROPOSED RULE IN THE Federal Reg ister].

§60.2510 Is a state plan required for all states?

No. You are not required to submit a state plan if there are no existing CISWI units in your state, an d you submit a negative declaration letter in place of th e state plan.

§60.2515 What must I include in my state plan?

(a) You must include the nine items described in paragraphs (a)(1) through (9) of this section in yo ur state plan.

(1) Inventory of affected CISWI units, including those that have ceased operation but have not been dismantled.

(2) Inventory of emissions from affected CISWI uni ts in your state.

(3) Compliance schedules for each affected CISWI unit.

(4) Emission limitations, operator training and qualification requirements, a waste management plan , and operating limits for affected CISWI units that are at least as protective as the emission guidelines contained in this subpart.

(5) Performance testing, recordkeeping, and report ing requirements.

(6) Certification that the hearing on the state pl an was held, a list of witnesses and their organizatio nal affiliations, if any, appearing at the hearing, and a brief written summary of each presentation or written sub mission.

(7) Provision for state progress reports to EPA.

(8) Identification of enforceable state mechanisms that you selected for implementing the emission gui delines of this subpart. Formatted: Underline
Formatted: Underline
Formatted: Underline(9) Demonstration of your state's legal authority to

carry out the sections 111(d) and 129 state plan.

(b) Your state plan may deviate from the format an d content of the emission guidelines contained in thi s subpart. However, if your state plan does deviate in content, you must demonstrate that your state plan is at least as protective as the emission guidelines cont ained in this subpart. Your state plan must address regulat ory applicability, increments of progress for retrofit, operator training and qualification, a waste manage ment plan, emission limitations, performance testing, op erating limits, monitoring, recordkeeping and reporting, an d air curtain incinerator requirements.

(c) You must follow the requirements of subpart B of this part (Adoption and Submittal of State Plans fo r Designated Facilities) in your state plan.

§60.2520 Is there an approval process for my stat e plan?

Yes. The EPA will review your state plan according to §60.27. §60.2525 What if my state plan is not approvable?

(a) If you do not submit an approvable state plan (or a negative declaration letter) by December 2, 2002, EPA will develop a federal plan according to §60.27 to implement the emission guidelines contained in this subpart. Owners and operators of CISWI units not c overed by an approved state plan must comply with the fede ral plan. The federal plan is an interim action and wi ll be automatically withdrawn when your state plan is app roved.

(b) If you do not submit an approvable state plan (or a negative declaration letter) to EPA that meets th e requirements of this subpart and contains the emiss ion limits in tables 6 through 10 of this subpart for C ISWI units that commenced construction after November 30 , 1999, but on or before by [THE DATE OF PUBLICATION OF THE FINAL RULE IN THE Federal Register] by [THE DATE 1 YEAR A FTER THE DATE OF PUBLICATION OF THE FINAL RULE IN THE Federa l Register], then EPA will develop a federal plan acc ording to §60.27 to implement the emission guidelines cont ained in this subpart. Owners and operators of CISWI units n ot covered by an approved state plan must comply with the federal plan. The federal plan is an interim action and Formatted: Underline
Formatted: Underline
Formatted: Underline
Formatted: Underline Deleted: ¶ ¶will be automatically withdrawn when your state pla n is

approved.

§60.2530 Is there an approval process for a negat ive declaration letter?

No. The EPA has no formal review process for negat ive declaration letters. Once your negative declaration letter has been received, EPA will place a copy in the pub lic docket and publish a notice in the FEDERAL REGISTER

. If, at a later date, an existing CISWI unit is found in your state, the federal plan implementing the emission guidelines contained in this subpart would automati cally apply to that CISWI unit until your state plan is a pproved.

§60.2535 What compliance schedule must I include in my state plan?

(a) For CISWI units in the incinerator subcategory that commenced construction on or before November 3 0, 1999,
y our state plan must include compliance schedules th at require CISWI units to achieve final compliance as expeditiously as practicable after approval of the state plan but not later than the earlier of the two date s specified in paragraphs (a)(1) and (2) of this sect ion.

(1) December 1, 2005.

(2) Three years after the effective date of state plan approval.

(b) For CISWI units in the incinerator subcategory that commenced construction after November 30, 1999 , but on or before [INSERT THE DATE OF PUBLICATION IN THE FE DERAL REGISTER], and for CISWI units in the energy recove ry units, waste-burning kilns, burn-off ovens, and sma ll remote incinerators subcategories that commenced construction before [INSERT THE DATE OF PUBLICATION IN THE FEDERAL REGISTER], your state plan must include com pliance schedules that require CISWI units to achieve final compliance as expeditiously as practicable after ap proval of the state plan but not later than the earlier of the two dates specified in paragraphs (b)(1) and (b)(2) of this section.

(1) [THE DATE 5 YEARS AFTER PUBLICATION OF THE FIN AL RULE IN THE FEDERAL REGISTER]. Deleted: ¶ ¶

Deleted: Y(2) 3 years after the effective date of state plan

approval.

(c) For compliance schedules more than 1 year following the effective date of state plan approval , state plans must include dates for enforceable increments of progress as specified in §60.2580.

§60.2540 Are there any state plan requirements fo r this subpart that apply instead of the requirements spec ified in subpart B?

Yes. Subpart B establishes general requirements fo r developing and processing section 111(d) plans. Th is subpart applies instead of the requirements in subp art B of this part for paragraphs (a) and (b) of this sectio n:

(a) State plans developed to implement this subpar t must be as protective as the emission guidelines co ntained in this subpart. State plans must require all CISW I units to comply by the dates specified in §60.2535. This applies instead of the option for case-by-case less stringe nt emission standards and longer compliance schedules in §60.24(f).

(b) State plans developed to implement this subpar t are required to include two increments of progress for the affected CISWI units. These two minimum increments are the final control plan submittal date and final complia nce date in §60.21(h)(1) and (5). This applies instead of t he requirement of §60.24(e)(1) that would require a st ate plan to include all five increments of progress for all CISWI units.

§60.2541 In lieu of a state plan submittal, are th ere other acceptable option(s) for a state to meet its section 111(d)/129(b)(2) obligations?

Yes, a state may meet its Clean Air Act Section 111(d)/129 obligations by submitting an acceptable written request for delegation of the federal plan that mee ts the requirements of this section. This is the only oth er option for a state to meet its Clean Air Act sectio n 111(d)/129 obligations.

(a) An acceptable federal plan delegation request must include the following: Deleted: December 1, 2005 or 3 years after the effective date of state plan approval, whichever is sooner(1) A demonstration of adequate resources and lega l

authority to administer and enforce the federal pla n.

(2) The items under §60.2515(a)(1), (2), and (7).

(3) Certification that the hearing on the state delegation request, similar to the hearing for a st ate plan submittal, was held, a list of witnesses and their organizational affiliations, if any, appearing at t he hearing, and a brief written summary of each presen tation or written submission.

(4) A commitment to enter into a Memorandum of Agreement with the Regional Administrator that sets forth the terms, conditions, and effective date of the de legation and that serves as the mechanism for the transfer o f authority. Additional guidance and information is given in EPA’s Delegation Manual, Item 7-139, Implementation and Enforcement of 111(d)(2) and 111(d)/(2)/129(b)(3) f ederal plans.

(b) A state with an already approved CISWI Clean A ir Act Section 111(d)/129 state plan is not precluded from receiving EPA approval of a delegation request for the revised federal plan, providing the requirements of paragraph (a) of this section are met, and at the t ime of the delegation request, the state also requests wit hdrawal of EPA’s previous state plan approval.

(c) A state’s Section 111(d)/129 obligations are separate from its obligations under title V of the Clean Air Act.

§60.2542 What authorities will not be delegated to state, local, or Tribal agencies?

The authorities listed under §60.2030(c) will not b e delegated to state, local, or Tribal agencies.

§60.2545 Does this subpart directly affect CISWI unit owners and operators in my state?

(a) No. This subpart does not directly affect CIS WI unit owners and operators in your state. However, CISWI unit owners and operators must comply with the stat e plan you develop to implement the emission guidelines co ntainedin this subpart. States may choose to incorporate the

model rule text directly in their state plan.

(b) If you do not submit an approvable plan to implement and enforce the guidelines contained in t his subpart by December 2, 2002, the EPA will implement and enforce a federal plan, as provided in §60.2525, to ensure that each unit within your state reaches compliance with all the provisions of this subpart by December 1, 2 005.

(c) If you do not submit an approvable plan to implement and enforce the guidelines contained in t his subpart by [THE DATE 1 YEAR AFTER PUBLICATION OF TH E FINAL RULE IN THE Federal Register] for CISWI units that commenced construction after November 30, 1999, but on or before [THE DATE OF PUBLICATION OF THE FINAL RULE I N THE Federal Register], the EPA will implement and enfor ce a federal plan, as provided in §60.2525, to ensure th at each unit within your state that commenced construction after November 30, 1999, but on or before by [THE DATE OF PUBLICATION OF THE FINAL RULE IN THE Federal Regist er], reaches compliance with all the provisions of this subpart by [THE DATE 5 YEARS AFTER PUBLICATION OF THE FINAL RULE IN THE FEDERAL REGISTER].

Applicability of State Plans

§60.2550 What CISWI units must I address in my st ate plan?

(a) Your state plan must address incineration unit s that meet all three criteria described in paragraph s (a)(1) through (3) of this section.

(1) Incineration units in your state that commence d construction on or before November 30, 1999.

(2) Incineration units that meet the definition of a CISWI unit as defined in §60.2875.

(3) Incineration units not exempt under §60.2555.

(b) If the owner or operator of a CISWI unit makes changes that meet the definition of modification or reconstruction on or after June 1, 2001, the CISWI unit becomes subject to subpart CCCC of this part and th e state plan no longer applies to that unit. Formatted: Underline
Formatted: Underline

Formatted: Underline
Formatted: Underline

Formatted: Underline
Formatted: Underline
Formatted: Underline(c) If the owner or operator of a CISWI unit makes

physical or operational changes to an existing CISW I unit primarily to comply with your state plan, subpart C CCC of this part does not apply to that unit. Such change s do not qualify as modifications or reconstructions under s ubpart CCCC of this part.

§60.2555 What combustion units are exempt from my state plan?

This subpart exempts the types of units described in paragraphs (a) , (c) through (i) and (m) of this section , but some units are required to provide notification s. Air curtain incinerators are exempt from the requiremen ts in this subpart except for the provisions in §§60.2805 , 60.2860, and 60.2870

.
(a) Pathological waste incineration units. Incineration units burning 90 percent or more by we ight (on a calendar quarter basis and excluding the weight o f auxiliary fuel and combustion air) of pathological waste, low-level radioactive waste, and/or chemotherapeuti c waste as defined in §60.2875 are not subject to this subp art if you meet the two requirements specified in paragrap hs (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 th e weight of pathological waste, low-level radioactive waste, and/or chemotherapeutic waste burned, and the weigh t of all other fuels and wastes burned in the unit.

(b) [Reserved]

(c) Municipal waste combustion units. Incineration units that are regulated under subpart Ea of this part (Standards of Performance for Municipal Waste Combu stors ) ; subpart Eb of this part (Standards of Performance f or Large Municipal Waste Combustors ) ; subpart Cb of this part (Emission Guidelines and Compliance Time for Large Municipal Combustors ) ; 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). Deleted: ¶
Deleted: fifteen
Deleted: o
Deleted:

. Deleted: Agricultural waste incineration 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 agricultural wastes as defined in §60.2875 are not subject to this subpart if you meet the two requirements specified in paragraphs (b)(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 weight of agricultural waste burned, and the weight of all other fuels and wastes burned in the unit.
Deleted: meet either of the two criteria specified in paragraphs (c)(1) or (2) of this section (1)
Deleted: for Which Construction is Commenced After September 20, 1994
Deleted: that are Constructed on or Before September 20, 1994
Deleted: New Stationary Sources
Deleted: Existing Stationary Sources:
Deleted: ¶
Deleted: (2) Burn greater than 30 percent municipalsolid waste or refusederived fuel, as defined in subpart Ea, subpart Eb, subpart AAAA, and subpart BBBB of this part, and that have the capacity to burn less than 35 tons (32 megagrams) per day of municipal solid waste or refuse-derived fuel, if you meet the two requirements in paragraphs (c)(2)(i) and (ii) of this section.¶ (i) Notify the Administrator that the unit meets these criteria.¶ (ii) Keep records on a calendar quarter basis of ... [4](d) Medical waste incineration units. Incineration

units regulated under subpart Ec of this part (Stan dards of Performance for Hospital/Medical/Infectious Waste Incinerators for Which Construction is Commenced Af ter June 20, 1996) or subpart Ca of this part (Emission Guid elines and Compliance Times for Hospital/Medical/Infectiou s Waste Incinerators).

(e) Small power production facilities. Units that meet the three requirements specified in paragraphs (e)(1) through (3) of this section.

(1) The unit qualifies as a small power-production facility under section 3(17)(C) of the Federal Powe r Act (16 U.S.C. 796(17)(C)).

(2) The unit burns homogeneous waste (not includin g refuse-derived fuel) to produce electricity.

(3) You notify the Administrator that the unit mee ts all of these criteria.

(f) Cogeneration facilities. Units that meet the three requirements specified in paragraphs (f)(1) t hrough (3) of this section.

(1) The unit qualifies as a cogeneration facility under section 3(18)(B) of the Federal Power Act (16 U.S.C. 796(18)(B)).

(2) The unit burns homogeneous waste (not includin g refuse-derived fuel) to produce electricity and ste am or other forms of energy used for industrial, commerci al, heating, or cooling purposes.

(3) You notify the Administrator that the unit mee ts all of these criteria.

(g) Hazardous waste 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 o nly Deleted: ¶

Deleted: that meet either of the two criteria specified in paragraph (g)(1) or (2) of this section
Deleted: ¶
Deleted: (1) Units for which you are required to get a permit under section 3005 of the Solid Waste Disposal Act.¶ (2) Units regulated under subpart EEE of 40 CFR part 63 (National Emission Standards for Hazardous Air Pollutants from Hazardous Waste Combustors).¶required to meet the requirements under “Air Curtai n

Incinerators” (§§60.2810 through 60.2870).

(1) 100 percent wood waste.

(2) 100 percent clean lumber.

(3) 100 percent mixture of only wood waste, clean lumber, and/or yard waste.

(j) [Reserved] (k) [Reserved]

(l) [Reserved]

(m) Sewage treatment plants

. Incineration units regulated under subpart O of this part (Standards o f Performance for Sewage Treatment Plants)(n) Sewage sludge incineration units . Incineration units combusting sewage sludge for the purpose of reducing the volume of th e sewage sludge by removing combustible matter. Sewage sludg e incineration unit designs include fluidized bed and multiple hearth.

§60.2558 [Removed] Use of Model Rule

§60.2560 What is the “model rule” in this subpart ?

(a) The model rule is the portion of these emissio n guidelines (§§60.2575 through 60.2875) that address es the regulatory requirements applicable to CISWI units. The model rule provides these requirements in regulatio n format. You must develop a state plan that is at l east as protective as the model rule. You may use the mode l rule language as part of your state plan. Alternative l anguage may be used in your state plan if you demonstrate t hat the alternative language is at least as protective as t he model rule contained in this subpart.

(b) In the model rule of §§60.2575 to 60.2875, “yo u” means the owner or operator of a CISWI unit.

§60.2565 How does the model rule relate to the re quired elements of my state plan?

Use the model rule to satisfy the state plan requirements specified in §60.2515(a)(4) and (5). Formatted: Space Before: Auto, After: Auto

Formatted: Font: Not Bold
Formatted: Font: 12 pt, Not Bold Deleted: Cyclonic barrel burners. (See §60.2875)¶ ¶
Deleted: Rack, part, and drum reclamation units. (See §60.2875)
Deleted: Cement kilns. Kilns regulated under subpart LLL of part 63 of this chapter (National Emiss ion Standards for Hazardous Air Pollutants from the Portland Cement Manufacturing Industry).

Deleted: sludge incinerators
Deleted: ¶
Deleted: Chemical recovery units. 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. The seven types of units described in paragraphs (n)(1) through (7) of this section 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.¶ (2) U nits 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 burning only manufacturing byproduct streams/residues 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

Deleted: What if a chemical recovery unit is not listed in §60.2555(n)?¶ (a) If a chemical recovery unit is not listed in
Deleted: ¶ ... [6] ... [5]§60.2570 What are the principal components of the model

rule?

The model rule contains the eleven major components listed in paragraphs (a) through (k) of this sectio n.

(a) Increments of progress toward compliance.

(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.

Model Rule—Increments of Progress

§60.2575 What are my requirements for meeting inc rements of progress and achieving final compliance?

If you plan to achieve compliance more than 1 year following the effective date of state plan approval , you must meet the two increments of progress specified in paragraphs (a) and (b) of this section.

(a) Submit a final control plan.

(b) Achieve final compliance.

§60.2580 When must I complete each increment of p rogress?

Table 1 of this subpart specifies compliance dates for each of the increments of progress.§60.2585 What must I include in the notifications of

achievement of increments of progress?

Your notification of achievement of increments of progress must include the three items specified in paragraphs (a) through (c) of this section.

(a) Notification that the increment of progress ha s been achieved.

(b) Any items required to be submitted with each increment of progress.

(c) Signature of the owner or operator of the CISW I unit.

§60.2590 When must I submit the notifications of achievement of increments of progress?

Notifications for achieving increments of progress must be postmarked no later than 10 business days a fter the compliance date for the increment.

§60.2595 What if I do not meet an increment of pr ogress?

If you fail to meet an increment of progress, you m ust submit a notification to the Administrator postmark ed within 10 business days after the date for that inc rement of progress in table 1 of this subpart. You must i nform the Administrator that you did not meet the increme nt, and you must continue to submit reports each subsequent calendar month until the increment of progress is m et.

§60.2600 How do I comply with the increment of pr ogress for submittal of a control plan?

For your control plan increment of progress, you mu st satisfy the two requirements specified in paragraph s (a) and (b) of this section.

(a) Submit the final control plan that includes th e five items described in paragraphs (a)(1) through ( 5) of this section.

(1) A description of the devices for air pollution control and process changes that you will use to co mply Deleted:with the emission limitations and other requirement s of

this subpart.

(2) The type(s) of waste to be burned.

(3) The maximum design waste burning capacity.

(4) The anticipated maximum charge rate.

(5) If applicable, the petition for site-specific operating limits under §60.2680.

(b) Maintain an onsite copy of the final control plan.

§60.2605 How do I comply with the increment of pr ogress for achieving final compliance?

For the final compliance increment of progress, you must complete all process changes and retrofit cons truction of control devices, as specified in the final contr ol plan, so that, if the affected CISWI unit is brought onli ne, all necessary process changes and air pollution control devices would operate as designed.

§60.2610 What must I do if I close my CISWI unit and then restart it?

(a) If you close your CISWI unit but will restart it prior to the final compliance date in your state pl an, you must meet the increments of progress specified in § 60.2575.

(b) If you close your CISWI unit but will restart it after your final compliance date, you must complete emission control retrofits and meet the emission limitations and operating limits on the date your u nit restarts operation.

§60.2615 What must I do if I plan to permanently close my CISWI unit and not restart it?

If you plan to close your CISWI unit rather than comply with the state plan, submit a closure notifi cation, including the date of closure, to the Administrator by the date your final control plan is due.

Model Rule—Waste Management Plan§60.2620 What is a waste management plan?

A waste management plan is a written plan that identifies both the feasibility and the methods use d to reduce or separate certain components of solid wast e from the waste stream in order to reduce or eliminate to xic emissions from incinerated waste.

§60.2625 When must I submit my waste management p lan?

You must submit a waste management plan no later th an the date specified in table 1 of this subpart for s ubmittal of the final control plan.

§60.2630 What should I include in my waste manage ment plan?

A waste management plan must include consideration of the reduction or separation of waste-stream element s 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 the s ource must implement those measures considered practical and feasible, based on the effectiveness of waste manag ement measures already in place, the costs of additional measures, the emissions reductions expected to be a chieved, and any other environmental or energy impacts they might have.

Model Rule—Operator Training and Qualification

§60.2635 What are the operator training and quali fication requirements?

(a) No CISWI unit can be operated unless a fully trained and qualified CISWI unit operator is access ible, either at the facility or can be at the facility wi thin 1 hour. The trained and qualified CISWI unit operato r may operate the CISWI unit directly or be the direct su pervisor of one or more other plant personnel who operate th e unit. If all qualified CISWI unit operators are temporari ly not accessible, you must follow the procedures in §60.2 665.

(b) Operator training and qualification must be obtained through a state-approved program or by com pleting 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) through (xi) of this section.

(i) Environmental concerns, including types of emissions.

(ii) Basic combustion principles, including produc ts of combustion.

(iii) Operation of the specific type of incinerato r to be used by the operator, including proper startu p, waste charging, and shutdown procedures.

(iv) Combustion controls and monitoring.

(v) Operation of air pollution control equipment a nd factors affecting performance (if applicable).

(vi) Inspection and maintenance of the incinerator and air pollution control devices.

(vii) Actions to prevent malfunctions or to prevent conditions that may lead to malfunction.

(viii) Bottom and fly ash characteristics and handling procedures.

(ix) Applicable federal, state, and local regulations, including Occupational Safety and Heal th Administration workplace standards.

(x) Pollution prevention.

(xi) Waste management practices.

(2) An examination designed and administered by th e instructor.

(3) Written material covering the training course topics that can serve as reference material followi ng completion of the course. Deleted: correct§60.2640 When must the operator training course b e

completed?

The operator training course must be completed by t he later of the three dates specified in paragraphs (a ) through (c) of this section.

(a) The final compliance date (Increment 2).

(b) Six months after CISWI unit startup.

(c) Six months after an employee assumes responsibility for operating the CISWI unit or assu mes responsibility for supervising the operation of the CISWI unit.

§60.2645 How do I obtain my operator qualificatio n?

(a) You must obtain operator qualification by completing a training course that satisfies the cri teria under §60.2635(b).

(b) Qualification is valid from the date on which the training course is completed and the operator succe ssfully passes the examination required under §60.2635(c)(2 ).

§60.2650 How do I maintain my operator qualificat ion?

To maintain qualification, you must complete an ann ual review or refresher course covering, at a minimum, the five topics described in paragraphs (a) through (e) of t his section.

(a) Update of regulations.

(b) Incinerator operation, including startup and shutdown procedures, waste charging, and ash handli ng.

(c) Inspection and maintenance.

(d) Prevention of malfunctions or conditions that may lead to malfunction.

(e) Discussion of operating problems encountered b y attendees.

§60.2655 How do I renew my lapsed operator qualif ication? Deleted: Respons es toYou must renew a lapsed operator qualification by o ne

of the two methods specified 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 describ ed in §60.2650.

(b) For a lapse of 3 years or more, you must repea t the initial qualification requirements in §60.2645( a).

§60.2660 What site-specific documentation is requ ired?

(a) Documentation must be available at the facilit y and readily accessible for all CISWI unit operators that addresses the ten topics described in paragraphs (a )(1) through (10) of this section. You must maintain th is information and the training records required by pa ragraph (c) of this section in a manner that they can be re adily accessed and are suitable for inspection upon reque st.

(1) Summary of the applicable standards under this subpart.

(2) Procedures for receiving, handling, and chargi ng waste.

(3) Incinerator startup, shutdown, and malfunction procedures.

(4) Procedures for maintaining proper combustion a ir supply levels.

(5) Procedures for operating the incinerator and associated 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 required under §§60.2620 through 60.2630.

(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 incinerator operator.

(1) The initial review of the information listed i n paragraph (a) of this section must be conducted by the later of the three dates specified in paragraphs (b )(1)(i) through (iii) of this section.

(i) The final compliance date (Increment 2).

(ii) Six months after CISWI unit startup.

(iii) Six months after being assigned to operate t he CISWI unit.

(2) Subsequent annual reviews of the information listed in paragraph (a) of this section must be con ducted no later than 12 months following the previous revi ew.

(c) You must also maintain the information specifi ed in paragraphs (c)(1) through (3) of this section.

(1) Records showing the names of CISWI unit operat ors who have completed review of the information in §60 .2660(a) as required by §60.2660(b), including the date of t he initial review and all subsequent annual reviews.

(2) Records showing the names of the CISWI operato rs who have completed the operator training requiremen ts under §60.2635, met the criteria for qualification under §60.2645, and maintained or renewed their qualifica tion under §60.2650 or §60.2655. Records must include documentation of training, the dates of the initial refresher training, and the dates of their qualific ation and all subsequent renewals of such qualifications.

(3) For each qualified operator, the phone and/or pager number at which they can be reached during op erating hours.

§60.2665 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 hour), you must meet one of t he two criteria specified in paragraphs (a) and (b) of thi s section, depending on the length of time that a qua lified operator is not accessible.

(a) When all qualified operators are not accessibl e for more than 8 hours, but less than 2 weeks, the C ISWI unit may be operated by other plant personnel famil iar with the operation of the CISWI unit who have completed a review of the information specified in §60.2660(a) within the past 12 months. However, you must record the period whe n all qualified operators were not accessible and include this deviation in the annual report as specified under § 60.2770.

(b) When all qualified operators are not accessibl e for 2 weeks or more, you must take the two actions that are described in paragraphs (b)(1) and (2) of this sect ion.

(1) Notify the Administrator of this deviation in writing within 10 days. In the notice, state what caused this deviation, what you are doing to ensure that a qualified operator is accessible, and when you anti cipate that a qualified operator will be accessible.

(2) Submit a status report to the Administrator ev ery 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 access ible and requesting approval from the Administrator to conti nue operation of the CISWI unit. You must submit the f irst status report 4 weeks after you notify the Administ rator of the deviation under paragraph (b)(1) of this sectio n. 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) a nd (ii) of this section.

(i) A qualified operator is accessible as required under §60.2635(a).

(ii) You notify the Administrator that a qualified operator is accessible and that you are resuming op eration.Model Rule—Emission Limitations and Operating Limit s

§60.2670 What emission limitations must I meet an d by when?

(a) You must meet the emission limitations for eac h unit, including bypass stack or vent, specified in table 2 of this subpart or tables 6 through 10 of this subp art by the final compliance date under the approved state plan, federal plan, or delegation, as applicable. Th e emission limitations apply at all times the unit is operatin g including and not limited to startup, shutdown, or malfunction.

(b) Units that do not use wet scrubbers must maint ain opacity to less than or equal to the percent opacit y (1- hour block average) specified in table 2 of this su bpart or tables 6 through 10 of this subpart, as applicable.

§60.2675 What operating limits must I meet and by when?

(a) If you use a wet scrubber to comply with the emission limitations, you must establish operating limits for four operating parameters (as specified in tabl e 3 of this subpart) as described in paragraphs (a)(1) thr ough (4) of this section during the initial performance test

.
(1) Maximum charge rate, calculated using one of t he 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 ra te measured during the most recent performance test demonstrating compliance with all applicable emissi on limitations.

(ii) For batch units, maximum charge rate is 110 percent of the daily charge rate measured during th e most recent performance test demonstrating compliance wi th all applicable emission limitations.

(2) Minimum pressure drop across the wet scrubber, which is calculated as 90 percent of the average pr essure drop across the wet scrubber measured during the mo st recent performance test demonstrating compliance wi th the particulate matter emission limitations; or minimum Deleted: You must meet the emission limitations specified in table 2 of this subpart on the date the initial performance test is required or completed (whichever is earlier).¶amperage to the wet scrubber, which is calculated a s 90

percent of the average amperage to the wet scrubber measured during the most recent performance test demonstrating compliance with the particulate matte r emission limitations.

(3) Minimum scrubber liquor flow rate, which is calculated as 90 percent of the average liquor flow rate at the inlet to the wet scrubber measured during the m ost recent performance test demonstrating compliance wi th all applicable emission limitations.

(4) Minimum scrubber liquor pH, which is calculate d as 90 percent of the average liquor pH at the inlet to the wet scrubber measured during the most recent perfor mance test demonstrating compliance with the HCl emission limitation.

(b) You must meet the operating limits established during the initial performance test on the date the initial performance test is required or completed (whicheve r is earlier).

(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 alar m does not sound more than 5 percent of the operating time during a 6-month period. In calculating this operating tim e percentage, if inspection of the fabric filter demo nstrates that no corrective action is required, no alarm tim e is counted. If corrective action is required, each al arm shall be counted as a minimum of 1 hour. If you ta ke longer than 1 hour to initiate corrective action, t he 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 meas ure the voltage and amperage of the electrostatic precipita tor collection plates during the particulate matter per formance test. Calculate the average value of these paramet ers for each test run. The minimum test run averages estab lish your site-specific minimum voltage and amperage ope rating limits for the electrostatic precipitator.

(e) If you use activated carbon injection to compl y with the emission limitations, you must measure the mercurysorbent flow rate during the mercury performance te st. The

minimum mercury sorbent flow rate test run averages establish your site-specific minimum mercury sorben t flow rate.

(f) If you use selective noncatalytic reduction to comply with the emission limitations, you must esta blish the maximum charge rate, the minimum secondary cham ber temperature (if applicable to your CISWI unit) and the minimum reagent flow rate as site-specific operatin g parameters during the initial nitrogen oxides perfo rmance test to determine compliance with the emissions lim its.

§60.2680 What if I do not use a wet scrubber , activated carbon injection, selective noncatalytic reduction, or an electrostatic precipitator to comply with the emission limitations?

(a) If you use an air pollution control device other than a wet scrubber, activated carbon injection, selective noncatalytic reduction, or an electrostatic precipi tator or limit emissions in some other manner to comply with the emission limitations under §60.2670, you must petit ion the Administrator for specific operating limits to be established during the initial performance test and continuously monitored thereafter. You must not co nduct the initial performance test until after the petiti on has been approved by the Administrator. Your petition must include the five items listed in paragraphs (a) (1) through (a)(5) of this section.

( 1 ) Identification of the specific parameters you propose to use as additional operating limits.

( 2 ) A discussion of the relationship between these parameters and emissions of regulated pollutants, identifying how emissions of regulated pollutants c hange with changes in these parameters, and how limits on these parameters will serve to limit emissions of regulat ed pollutants.

( 3 ) A discussion of how you will establish the upper and/or lower values for these parameters which will establish the operating limits on these parameters.

( 4 ) A discussion identifying the methods you will us e to measure and the instruments you will use to moni tor Deleted: (e)

Deleted: a

Deleted: b

Deleted: c

Deleted: dthese parameters, as well as the relative accuracy and

precision of these methods and instruments.

( 5 ) A discussion identifying the frequency and methods for recalibrating the instruments you will use for monitoring these parameters.

(b) For energy recovery units that do not use a wet scrubber, you must install, operate, certify, and m aintain a continuous opacity monitoring system according to the procedures in §60.2710 by the compliance date speci fied in §60.2670.

§60.2685 [Removed] Model Rule—Performance Testing

§60.2690 How do I conduct the initial and annual performance test?

(a) All performance tests must consist of a minimu m of three test runs conducted under conditions representative of normal operations.

(b) You must document that the waste burned during the performance test is representative of the waste burned under normal operating conditions by maintaining a log of the quantity of waste burned (as required in §60.2740(b)(1)) and the types of waste burned durin g the performance test.

(c) All performance tests must be conducted using the minimum run duration specified in table s 2 and 6 through 10 of this subpart.

(d) Method 1 of appendix A of this part must be us ed to select the sampling location and number of trave rse points.

(e) Method 3A or 3B of appendix A of this part mus t be used for gas composition analysis, including mea surement of oxygen concentration. Method 3A or 3B of append ix A of this part must be used simultaneously with each met hod.

(f) All pollutant concentrations, except for opaci ty, must be adjusted to 7 percent oxygen using Equation 1 of this section:

C adj = C meas (20.9−7)/(20.9−%O 2 ) (Eq. 1) Deleted: e

Deleted: What happens during periods of startup, shutdown, and malfunction?¶ ( a) The emission limitations and operating limits apply at all times except during CISWI unit startups, shutdowns, or malfunctions.¶ (b) Each malfunction must last no longer than 3 hours. ¶Where:

C adj = pollutant concentration adjusted to 7 percent oxy gen;

C meas = pollutant concentration measured on a dry basis;

(20.9−7) = 20.9 percent oxygen−7 percent oxygen (de fined oxygen correction basis);

20.9 = oxygen concentration in air, percent; and

%O 2 = oxygen concentration measured on a dry basis, per cent.

(g) You must determine dioxins/furans toxic equivalency by following the procedures in paragrap hs (g)(1) through (3) of this section.

(1) Measure the concentration of each dioxin/furan tetra- through octa-congener emitted using EPA Meth od 23.

(2) For each dioxin/furan congener measured in accordance with paragraph (g)(1) of this section, m ultiply the congener concentration by its corresponding tox ic equivalency factor specified in table 4 of this sub part.

(3) Sum the products calculated in accordance with paragraph (g)(2) of this section to obtain the tota l concentration of dioxins/furans emitted in terms of toxic equivalency.

(h) Method 22 of appendix A-7 of this part must be used to determine compliance with the fugitive ash emission limit in table 2 of this subpart or tables 6 throug h 10 of this subpart.

(i) Except as specified in paragraphs (i)(1),(i)(2 ), (i)(3), and (i)(4) of this section, within 60 days after achieving the maximum production rate at which the affected facility will be operated, but not later than 180 d ays after initial startup of such facility, or at such other times specified by this part, and at such other tim es as may be required by the Administrator under section 114 of the Clean Air Act, the owner or operator of such fa cility must conduct performance test(s) and furnish the Administrator a written report of the results of su ch performance test(s).(1) If a force majeure is about to occur, occurs, or

has occurred for which the affected owner or operat or intends to assert a claim of force majeure, the own er or operator must notify the Administrator, in writing as soon as practicable following the date the owner or oper ator first knew, or through due diligence should have kn own that the event may cause or caused a delay in testing be yond the regulatory deadline, but the notification must occu r before the performance test deadline unless the initial fo rce majeure or a subsequent force majeure event delays the notice, and in such cases, the notification must oc cur as soon as practicable.

(2) The owner or operator must provide to the Administrator a written description of the force ma jeure event and a rationale for attributing the delay in testing beyond the regulatory deadline to the force majeure ; describe the measures taken or to be taken to minim ize the delay; and identify a date by which the owner or op erator proposes to conduct the performance test. The perf ormance test must be conducted as soon as practicable after the force majeure occurs.

(3) The decision as to whether or not to grant an extension to the performance test deadline is solel y within the discretion of the Administrator. The Administr ator will notify the owner or operator in writing of app roval or disapproval of the request for an extension as soon as practicable.

(4) Until an extension of the performance test deadline has been approved by the Administrator und er paragraphs (i)(1), (2), and (3) of this section, th e owner or operator of the affected facility remains strict ly subject to the requirements of this part.

(j) Performance tests must be conducted and data reduced in accordance with the test methods and pro cedures contained in this subpart unless the Administrator does one of the following.

(1) Specifies or approves, in specific cases, the use of a reference method with minor changes in methodo logy.

(2) Approves the use of an equivalent method.(3) Approves the use of an alternative method the

results of which he has determined to be adequate f or indicating whether a specific source is in complian ce.

(4) Waives the requirement for performance tests because the owner or operator of a source has demon strated by other means to the Administrator’s satisfaction that the affected facility is in compliance with the standar d.

(5) Approves shorter sampling times and smaller sample volumes when necessitated by process variabl es or other factors. Nothing in this paragraph is constr ued to abrogate the Administrator’s authority to require t esting under section 114 of the Clean Air Act.

(k) Performance tests must be conducted under such conditions as the Administrator shall specify to th e plant operator based on representative performance of the affected facility. The owner or operator must make available to the Administrator such records as may be necessary to determine the conditions of the perfor mance tests.

(l) The owner or operator of an affected facility must provide the Administrator at least 30 days pri or notice of any performance test, except as specified under other subparts, to afford the Administrator the opp ortunity to have an observer present. If after 30 days noti ce for an initially scheduled performance test, there is a delay (due to operational problems, etc.) in conducting t he scheduled performance test, the owner or operator o f an affected facility must notify the Administrator (or delegated state or local agency) as soon as possibl e of any delay in the original test date, either by providin g at least 7 days prior notice of the rescheduled date o f the performance test, or by arranging a rescheduled dat e with the Administrator (or delegated state or local agen cy) by mutual agreement.

(m) The owner or operator of an affected facility must provide, or cause to be provided, performance testing facilities as follows:

(1) Sampling ports adequate for test methods applicable to such facility. This includes the fol lowing.(i) Constructing the air pollution control system

such that volumetric flow rates and pollutant emiss ion rates can be accurately determined by applicable te st methods and procedures.

(ii) Providing a stack or duct free of cyclonic fl ow during performance tests, as demonstrated by applic able test methods and procedures.

(2) Safe sampling platform(s).

(3) Safe access to sampling platform(s).

(4) Utilities for sampling and testing equipment.

(n) Unless otherwise specified in this subpart, ea ch performance test must consist of three separate run s using the applicable test method. Each run must be condu cted for the time and under the conditions specified in the applicable standard. For the purpose of determinin g compliance with an applicable standard, the arithme tic means of results of the three runs apply. In the e vent that a sample is accidentally lost or conditions oc cur in which one of the three runs must be discontinued be cause of forced shutdown, failure of an irreplaceable portio n of the sample train, extreme meteorological conditions, or other circumstances, beyond the owner or operator’s contr ol, compliance may, upon the Administrator’s approval, be determined using the arithmetic mean of the results of the two other runs.

§60.2695 How are the performance test data used?

You use results of performance tests to demonstrate compliance with the emission limitations in table 2 of this subpart or tables 6 through 10 of this subpart.

Model Rule—Initial Compliance Requirements

§60.2700 How do I demonstrate initial compliance with the amended emission limitations and establish the operating limits?

(a) You must conduct an initial performance test, as required under §§60.2690 and 60.2670, to determine compliance with the emission limitations in table 2 of this subpart and tables 6 through 10 of this subpart and to Deleted: ¶

Deleted: §60.8,establish operating limits using the procedures in §60.2675

or §60.2680. The initial performance test must be conducted using the test methods listed in table 2 of this subpart and tables 6 through 10 of this subpart and the procedures in §60.2690. The use of the bypass stack during a performance test shall invalidate the performance test.

(b) You may use the results from a performance tes t conducted within the two previous years that demons trated compliance with the emission limits in table 2 of t his subpart or tables 5 through 9 of this subpart. How ever, you must continue to meet the operating limits esta blished during the most recent performance test that demons trated compliance with the emission limits in table 2 of t his subpart or tables 5 through 9 of this subpart. The test must use the test methods in table 2 of this subpar t or tables 5 through 9 of this subpart.

§60.2705 By what date must I conduct the initial performance test?

The initial performance test must be conducted no later than 180 days after your final compliance dat e. Your final compliance date is specified in table 1 of th is subpart.

§60.2706 By what date must I conduct the initial a ir pollution control device inspection?

(a) The initial air pollution control device inspection must be conducted within 60 days after installation of the control device and the associat ed CISWI unit reaches the charge rate at which it will opera te, but no later than 180 days after the final compliance d ate for meeting the amended emission limitations.

(b) Within 10 operating days following an air pollution control device inspection, all necessary repairs must be completed unless the owner or operator obta ins written approval from the state agency establishing a date whereby all necessary repairs of the designated fac ility must be completed.

Model Rule—Continuous Compliance Requirements

§60.2710 How do I demonstrate continuous complian ce with the emission limitations and the operating limits?(a) You must conduct an annual performance test fo r

particulate matter, hydrogen chloride, fugitive ash, and opacity for each CISWI unit as required under §60.2690 to determine compliance with the emission limitations. The annual performance test must be conducted using the test methods listed in table 2 of this subpart or tables 6 through 10 of this subpart and the procedures in §60.2690.

(b) You must continuously monitor the operating parameters specified in §60.2675 or established und er §60.2680. Operation above the established maximum o r below the established minimum operating limits constitute s a deviation from the established operating limits. T hreehour rolling average values are used to determine compliance (except for baghouse leak detection syst em alarms) unless a different averaging period is esta blished under §60.2680. Operating limits are confirmed or established during performance tests.

(c) You must only burn the same types of waste use d to establish operating limits during the performanc e test.

(d) For energy recovery units, incinerators, burn- off ovens, and small remote units, you must perform ann ual visual emissions test for ash handling.

(e) For energy recovery units, you must conduct an annual performance test for opacity (except where particulate matter continuous emissions monitoring systems are used for compliance) and the pollutants (except for carbon monoxide) listed in table 2 of this subpart and tables 6 through 10 of this subpart.

(f) For energy recovery units, demonstrate continu ous compliance with the carbon monoxide emission limit using a carbon monoxide continuous emission monitoring syst em according to the following requirements:

(1) Determine continuous compliance with the carbo n monoxide emissions limit using a 24-hour block aver age, calculated as specified in section 12.4.1 of EPA Re ference Method 19 of appendix A–7 of this part.

(2) Operate the carbon monoxide continuous emissio n monitoring system in accordance with the applicable requirements of performance specification 4B of app endix B Deleted: §60.8

Deleted: do not applyand the quality assurance procedures of appendix F of this

part.

(g) For energy recovery units with design capaciti es greater than 250 MMBtu/hr, demonstrate continuous compliance with the particulate matter emissions li mit using a particulate matter continuous emission moni toring system according to the procedures in §60.2730(n).

(h) For waste-burning kilns, you must conduct an annual performance test for particulate matter, hyd rogen chloride, fugitive ash, and opacity as listed in ta ble 8 of this subpart. You must determine compliance with t he mercury emissions limit using a mercury continuous emission monitoring system according to the following requir ements:

(1) Operate a continuous emission monitor in accordance with performance specification 12A of 40 CFR part 60, appendix B or a sorbent trap based integra ted monitor in accordance with performance specificatio n 12B of 40 CFR part 60, appendix B of Appendix K of 40 CFR part 75. The duration of the performance test must be a cale ndar month. For each calendar month in which the cement kiln operates, hourly mercury concentration data, and st ack gas volumetric flow rate data must be obtained.

(2) Owners or operators using a mercury continuous emission monitoring system must install, operate, calibrate, and maintain an instrument for continuou sly measuring and recording the exhaust gas flow rate t o the atmosphere according to the requirements of perform ance specification 12A of 40 CFR part 60, appendix B and quality assurance procedure 5 of 40 CFR part 60, appendix F , upon promulgation.(3) The owner or operator of a cement kiln must demonstrate initial compliance by operating a mercury continuous emission monitor while the raw mill of t he inline kiln/raw mill is under normal operating condit ions and while the raw mill of the in-line kiln/raw mill is not operating.

(i) 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 incl ude, at a minimum, the following: Deleted: ¶(1) Inspect air pollution control device(s) for

proper operation.

(2) Develop a site-specific monitoring plan according to the requirements in paragraph (j) of this sectio n. This requirement also applies to you if you petition the EPA Administrator for alternative monitoring parameters under §60.13(i).

(j) For each continuous monitoring system required in this section, you must develop and submit to the EP A Administrator for approval a site-specific monitori ng plan according to the requirements of this paragraph (j) that addresses paragraphs (j)(1)(i) through (vi) of this section.

(1) You must submit this site-specific monitoring plan at least 60 days before your initial performance ev aluation of your continuous monitoring system.

(i) Installation of the continuous monitoring system sampling probe or other interface at a measurement location relative to each affected process unit such that th e measurement is representative of control of the exh aust emissions (e.g., on or downstream of the last contr ol device).

(ii) Performance and equipment specifications for the sample interface, the pollutant concentration or pa rametric signal analyzer and the data collection and reducti on systems.

(iii) Performance evaluation procedures and accept ance criteria (e.g., calibrations).

(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 reporting procedure s in accordance with the general requirements of §60.7(b ), (c), (c)(1), (c)(4), (d), (e), (f) and (g).(2) You must conduct a performance evaluation of e ach

continuous monitoring system in accordance with you r sitespecific monitoring plan.

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

(k) If you have an operating limit that requires t he use of a flow measurement device, you must meet the requirements in paragraphs (j) and (k)(1) through ( 4) of this section.

(1) Locate the flow sensor and other necessary equipment in a position that provides a representat ive flow.

(2) Use a flow sensor with a measurement sensitivity of 2 percent of the flow rate.

(3) Reduce swirling flow or abnormal velocity distributions due to upstream and downstream distur bances.

(4) Conduct a flow sensor calibration check at lea st semiannually.

(l) If you have an operating limit that requires the use of a pressure measurement device, you must meet the requirements in paragraphs (j) and (l)(1) through ( 6) of this section.

(1) Locate the pressure sensor(s) in a position th at provides a representative measurement of the pressu re.

(2) Minimize or eliminate pulsating pressure, vibration and internal and external corrosion.

(3) Use a gauge with a minimum tolerance of 1.27 centimeters of water or a transducer with a minimum tolerance of 1 percent of the pressure range.

(4) Check pressure tap pluggage daily.

(5) Using a manometer, check gauge calibration quarterly and transducer calibration monthly.(6) Conduct calibration checks any time the sensor

exceeds the manufacturer's specified maximum operat ing pressure range or install a new pressure sensor.

(m) If you have an operating limit that requires t he use of a pH measurement device, you must meet the requirements in paragraphs (j) and (m)(1) through ( 3) of this section.

(1) Locate 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 measured.

(3) Check the pH meter's calibration on at least two points every 8 hours of process operation.

(n) If you have an operating limit that requires t he use of equipment to monitor voltage and secondary c urrent (or total power input) of an electrostatic precipit ator, you must use voltage and secondary current monitoring e quipment to measure voltage and secondary current to the electrostatic precipitator.

(o) If you have an operating limit that requires t he use of equipment to monitor sorbent injection rate ( e.g. , weigh belt, weigh hopper, or hopper flow measuremen t device), you must meet the requirements in paragrap hs (j) and (o)(1) through (3) of this section.

(1) Locate the device in a position(s) that provid es a representative measurement of the total sorbent inj ection rate.

(2) Install and calibrate the device in accordance with manufacturer's procedures and specifications.

(3) At least annually, calibrate the device in accordance with the manufacturer's procedures and specifications.

(p) 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 paragraphs (p)(1) through (8) of this section. Formatted: Font: Italic(1) You must install and operate a bag leak detect ion

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 con sistent with the manufacturer's written specifications and recommendations and in accordance with the guidance provided in EPA–454/R–98–015, September 1997.

(3) The bag leak detection system must be certifie d by the manufacturer to be capable of detecting particu late matter emissions at concentrations of 10 milligrams per actual cubic meter or less.

(4) The bag leak detection system sensor must prov ide output of relative or absolute particulate matter l oadings.

(5) The bag leak detection system must be equipped with a device to continuously record the output sig nal from the sensor.

(6) The bag leak detection system must be equippe d with an alarm system that will sound automatically when an increase in relative particulate matter emissions o ver a preset level is detected. The alarm must be located where it is easily heard by plant operating personnel.

(7) For positive pressure fabric filter systems th at do not duct all compartments of cells to a common s tack, a bag leak detection system must be installed in each baghouse compartment or cell.

(8) Where multiple bag leak detectors are required, the system’s instrumentation and alarm may be share d among detectors.

(q) For facilities using a continuous emission monitoring system to demonstrate compliance with th e sulfur dioxide emission limit, compliance with the sulfur dioxide emission limit may be demonstrated by using the con tinuous emission monitoring system specified in §60.2165 to measure sulfur dioxide and calculating a 24-hour daily geom etric average emission concentration using EPA Reference Method 19, sections 4.3 and 5.4, as applicable. The sulfu r dioxide continuous emission monitoring system must be opera ted according to performance specification 2 in appendi x B ofthis part and must follow the procedures and method s

specified in this paragraph (q). For sources that have actual inlet emissions less than 100 parts per mill ion dry volume, the relative accuracy criterion for inlet s ulfur dioxide continuous emission monitoring systems shou ld be no greater than 20 percent of the mean value of the re ference method test data in terms of the units of the emiss ion standard, or 5 parts per million dry volume absolut e value of the mean difference between the reference method and the continuous emission monitoring systems, whichever i s greater.

(1) During each relative accuracy test run of the continuous emission monitoring system required by performance specification 2 in appendix B of this p art, sulfur dioxide and oxygen (or carbon dioxide) data must be collected concurrently (or within a 30- to 60-minut e period) by both the continuous emission monitors and the te st methods specified in paragraphs (q)(1)(i) and (q)(1 )(ii) of this section.

(i) For sulfur dioxide, EPA Reference Method 6, 6A , or 6C, or as an alternative ANSI/ASME PTC–19.10–1981 — Flue and Exhaust Gas Analysis [Part 10, Instruments and Appa ratus] (incorporated by reference, see §60.17] must be use d.

(ii) For oxygen (or carbon dioxide), EPA Method 3, 3A, or 3B, or as an alternative ANSI/ASME PTC–19–10–198 1 Flue and Exhaust Gas Analysis [Part 10, Instruments and Apparatus] (incorporated by reference, see §60.17]a s applicable, must be used.

(2) The span value of the continuous emission monitoring system at the inlet to the sulfur dioxid e control device must be 125 percent of the maximum estimated hourly potential sulfur dioxide emissions of the unit subj ect to this rule. The span value of the continuous emissi on monitoring system at the outlet of the sulfur dioxi de control device must be 50 percent of the maximum es timated hourly potential sulfur dioxide emissions of the un it subject to this rule.

(3) Quarterly accuracy determinations and daily calibration drift tests must be performed in accord ance with procedure 1 in appendix F of this part.(4) When sulfur dioxide emissions data are not

obtained because of continuous emission monitoring system breakdowns, repairs, calibration checks and/or zero and span adjustments, emissions data must be obtained by usi ng other monitoring systems as approved by EPA or EPA Refere nce Method 19 to provide, as necessary, valid emissions data for a minimum of 85 percent of the hours per day, 90 pe rcent of the hours per calendar quarter, and 95 percent of t he hours per calendar year that the affected facility is ope rated and combusting solid waste (as that term is defined by the Administrator under RCRA in 40 CFR 240).

(r) For facilities using a continuous emission monitoring system to demonstrate continuous complia nce with the nitrogen oxides emission limit, compliance with the nitrogen oxides emission limit may be demonstrated by using the continuous emission monitoring system specified in §60.2165 to measure nitrogen oxides and calculating a 24- hour daily arithmetic average emission concentratio n using EPA Reference Method 19, section 4.1. The nitrogen oxides continuous emission monitoring system must be opera ted according to performance specification 2 in appendi x B of this part and must follow the procedures and method s specified in paragraphs (r)(1) through (r)(5) of th is section.

(1) During each relative accuracy test run of the continuous emission monitoring system required by performance specification 2 of appendix B of this p art, nitrogen oxides and oxygen (or carbon dioxide) data must be collected concurrently (or within a 30- to 60-minut e period) by both the continuous emission monitors and the te st methods specified in paragraphs (r)(1)(i) and (r)(1 )(ii) of this section.

(i) For nitrogen oxides, EPA Reference Method 7, 7 A, 7C, 7D, or 7E must be used.

(ii) For oxygen (or carbon dioxide), EPA Reference Method 3, 3A, or 3B, or as an alternative ANSI/ASME PTC– 19.10–1981 Flue and Exhaust Gas Analysis [Part 10, Instruments and Apparatus] (incorporated by referen ce, see §60.17], as applicable, must be used.

(2) The span value of the continuous emission monitoring system must be 125 percent of the maximu m estimated hourly potential nitrogen oxide emissions of unit.(3) Quarterly accuracy determinations and daily

calibration drift tests must be performed in accord ance with procedure 1 in appendix F of this part.

(4) When nitrogen oxides continuous emissions monitoring data are not obtained because of continu ous emission monitoring system breakdowns, repairs, cal ibration checks and zero and span adjustments, emissions dat a must be obtained using other monitoring systems as approved by EPA or EPA Reference Method 19 to provide, as necessary , valid emissions data for a minimum of 85 percent of the h ours per day, 90 percent of the hours per calendar quarter, and 95 percent of the hours per calendar year the unit is operated and combusting solid waste.

(5) The owner or operator of an affected facility may request that compliance with the nitrogen oxides em ission limit be determined using carbon dioxide measuremen ts 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 leve ls must be established during the initial performance test according to the procedures and methods specified in paragrap hs (r)(5)(i) through (r)(5)(iv) of this section. This relationship may be reestablished during performanc e compliance tests.

(i) The fuel factor equation in Method 3B must be used to determine the relationship between oxygen and ca rbon dioxide at a sampling location. Method 3, 3A, or 3B, or as an alternative ANSI/ASME PTC–19.10–1981 Flue and Ex haust Gas Analysis [Part 10, Instruments and Apparatus] (inco rporated by reference, see §60.17], as applicable, must be u sed to determine the oxygen concentration at the same loca tion 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 3 runs must be performed.

(s) For facilities using a continuous emission monitoring system to demonstrate continuous complia nce withany of the emission limits of this subpart, you mus t

complete the following:

(1) Demonstrate compliance with the appropriate emission limit(s) using a 24-hour block average, ca lculated following the procedures in EPA Method 19 of append ix A-7 of this part.

(2) Operate all continuous emission monitoring sys tem in accordance with the applicable procedures under appendices B and F of this part.

(t) Use of the bypass stack at any time is an emissions standards deviation for particulate matte r, HCl, Pb, Cd and Hg.

§60.2715 By what date must I conduct the annual performance test?

You must conduct annual performance tests within 12 months following the initial performance test. Con duct subsequent annual performance tests within 12 month s following the previous one.

§60.2716 By what date must I conduct the annual ai r pollution control device inspection?

On an annual basis (no more than 12 months followin g the previous annual air pollution control device inspection), you must complete the air pollution co ntrol device inspection as described in §60.2706.

§60.2720 May I conduct performance testing less o ften?

(a) You can test less often for particulate matter, hydrogen chloride, fugitive ash, or opacity, provid ed:

(1) You have test data for at least 3 consecutive
years.

(2) The test data results for particulate matter, hydrogen chloride, fugitive ash, or opacity is less than 75 percent of the emissions or opacity limit.

(3) There are no changes in the operation of the affected source or air pollution control equipment that could affect emissions. In this case, you do not h ave to Deleted: ¶
Deleted: for particulate matter, hydrogen chloride, and opacity

Deleted: ¶

Deleted: ¶
Deleted: a given pollutant if you have test data for at least 3 years, and all performance tests for the pollutant (particulate matter, hydrogen chloride, or opacity) over 3 consecutive years show that you comply with the emission limitation. In this case, you do not have to conduct a performance test for that pollutant for the next 2 years. You must conduct a performance test during the third year and no more than 36 months following the previous performance test.conduct a performance test for that pollutant for t he next

2 years. You must conduct a performance test durin g the third year and no more than 36 months following the previous performance test.

(b) If your CISWI unit continues to emit less than 75 percent of the emission limitation for particulate matter, hydrogen chloride, fugitive ash, or opacity and there are no changes in the operation of the affected facilit y or air pollution control equipment that could increase emi ssions, you may choose to conduct performance tests for the se pollutants every third year, but each test must be within 36 months of the previous performance test.

(c) If a performance test shows emissions exceeded 75 percent or greater of the emission or opacity limit ation for particulate matter, hydrogen chloride, fugitive ash, or opacity, you must conduct annual performance tests for that pollutant until all performance tests over a 3-year period are within 75 percent of the applicable emission limitation

. §60.2725 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 performance test at any time.

(b) You must repeat the performance test if your f eed stream is different than the feed streams used duri ng any performance test used to demonstrate compliance.

Model Rule—Monitoring

§60.2730 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 §60.2670, you must in stall, calibrate (to manufacturers' specifications), maint ain, and operate devices (or establish methods) for monitori ng the value of the operating parameters used to determine compliance with the operating limits listed in tabl e 3 of this subpart. These devices (or methods) must meas ure and record the values for these operating parameters at the Deleted: to meet the emission limitation
Deleted:

Deleted: a deviation from an emission limitation

Deleted: show compliancefrequencies indicated in table 3 of this subpart at all

times except as specified in §60.2735(a).

(b) If you use a fabric filter to comply with the requirements of this subpart, you must install, cal ibrate, maintain, and continuously operate a bag leak detec tion system as specified in paragraphs (b)(1) through (8 ) of this section.

(1) You must install and operate a bag leak detect ion system for each exhaust stack of the fabric filter.

(2) Each bag leak detection system must be install ed, operated, calibrated, and maintained in a manner co nsistent with the manufacturer's written specifications and recommendations.

(3) The bag leak detection system must be certifie d by the manufacturer to be capable of detecting part iculate matter emissions at concentrations of 10 milligrams per actual cubic meter or less.

(4) The bag leak detection system sensor must prov ide output of relative or absolute particulate matter l oadings.

(5) The bag leak detection system must be equipped with a device to continuously record the output sig nal from the sensor.

(6) The bag leak detection system must be equipped with an alarm system that will sound automatically when an increase in relative particulate matter emissions o ver a preset level is detected. The alarm must be locate d where it is easily heard 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 pressur e or induced air fabric filters, the bag leak detector m ust be installed downstream of the fabric filter.

(8) Where multiple detectors are required, the system ’ s instrumentation and alarm may be shared among detectors.

(c) If you are using something other than a wet scrubber , activated carbon, selective non-catalyticreduction, or an electrostatic precipitator to comply with

the emission limitations under §60.2670, you must i nstall, calibrate (to the manufacturer ’ s specifications), maintain, and operate the equipment necessary to monitor comp liance with the site-specific operating limits established using the procedures in §60.2680.

(d) If you use activated carbon injection to compl y with the emission limitations in this subpart, you must measure the minimum mercury sorbent flow rate once per hour.

(e) If you use selective non-catalytic reduction t o comply with the emission limitations, you must comp lete the following:

(1) Following the date on which the initial performance test is completed or is required to be completed under §60.2690 whichever date comes first , ensure that the affected facility does not operate above t he maximum charge rate, or below the minimum secondary chamber temperature (if applicable to your CISWI unit) or t he minimum reagent flow rate measured as 3-hour rollin g averages (calculated each hour as the average of th e previous 3 operating hours) at all times. Operatin g parameter limits are confirmed or reestablished dur ing performance tests.

(2) Operation of the affected facility above the maximum charge rate, below the minimum secondary ch amber temperature, and below the minimum reagent flow rat e simultaneously constitute a violation of the nitrog en oxides emissions limit.

(f) If you use an electrostatic precipitator to comply with the emission limits of this subpart, yo u must monitor the voltage and amperage of the electrostat ic precipitator collection plates and maintain the 3-h our block averages at or above the operating limits est ablished during the mercury or particulate matter performanc e test.

(g) To demonstrate continuous compliance with the hydrogen chloride emissions limit, a facility may substitute use of a hydrogen chloride continuous em ission monitoring system for conducting the hydrogen chlor ide annual performance test, monitoring the minimum hyd rogenchloride sorbent flow rate, and monitoring the mini mum

scrubber liquor pH.

(h) To demonstrate continuous compliance with the particulate matter emissions limit, a facility may substitute use of a particulate matter continuous e mission monitoring system for conducting the particulate ma tter annual performance test and monitoring the minimum pressure drop across the wet scrubber, if applicable.

(i) To demonstrate continuous compliance with the dioxin/furan emissions limit, a facility may substi tute use of a continuous automated sampling system for the dioxin/furan annual performance test. You must rec ord the output of the system and analyze the sample accordi ng to EPA Reference Method 23 of appendix A-7 of this par t. This option to use a continuous automated sampling syste m takes effect on the date a final performance specificatio n applicable to dioxin/furan from continuous monitors is published in the Federal Register. The owner or op erator who elects to continuously sample dioxin/furan emis sions instead of sampling and testing using EPA Reference Method 23 of appendix A-7 must install, calibrate, maintai n, and operate a continuous automated sampling system and must comply with the requirements specified in §60.58b(p ) and (q).

(j) To demonstrate continuous compliance with the mercury emissions limit, a facility may substitute use of a continuous automated sampling system for the mercur y annual performance test. You must record the output of th e system and analyze the sample at set intervals using any s uitable determinative technique that can meet appropriate performance criteria. This option to use a continu ous automated sampling system takes effect on the date a final performance specification applicable to mercury fro m monitors is published in the Federal Register. The owner or operator who elects to continuously sample mercu ry emissions instead of sampling and testing using EPA Method 29 of appendix A-8 of this part, ASTM D6784-02 (200 8), Standard Test Method for Elemental, Oxidized, Parti cle Bound and Total Mercury in Flue Gas Generated from CoalFired Stationary Sources (Ontario Hydro Method), or an approved alternative method for measuring mercury emissions, must install, calibrate, maintain, and o perate a continuous automated sampling system and must compl y with the requirements specified in §60.58b(p) and (q).(k) To demonstrate continuous compliance with the

nitrogen oxides emissions limit, a facility may sub stitute use of a continuous emission monitoring system for the nitrogen oxides annual performance test to demonstr ate compliance with the nitrogen oxides emissions limit s.

(1) Install, calibrate, maintain, and operate a continuous emission monitoring system for measuring nitrogen oxides emissions discharged to the atmosph ere and record the output of the system. The requirements under performance specification 2 of appendix B of this p art, the quality assurance procedure 1 of appendix F of this part and the procedures under §60.13 must be followed fo r installation, evaluation, and operation of the cont inuous emission monitoring system.

(2) Following the date that the initial performanc e test for nitrogen oxides is completed or is require d to be completed under §60.2690, compliance with the emission limit for nitrogen oxides required under §60.52b(d) must be determined based on the 24-hour daily arithmetic av erage of the hourly emission concentrations using continuous emission monitoring system outlet data. The 1-hour arithmetic averages must be expressed in parts per million by volume (dry basis) and used to calculate the 24- hour daily arithmetic average concentrations. The 1-hou r arithmetic averages must be calculated using the da ta points required under §60.13(e)(2).

(l) To demonstrate continuous compliance with the sulfur dioxide emissions limit, a facility may subs titute use of a continuous automated sampling system for t he sulfur dioxide annual performance test to demonstra te compliance with the sulfur dioxide emissions limits

.
(1) Install, calibrate, maintain, and operate a continuous emission monitoring system 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 p art, the quality assurance procedure 1 of appendix F of this part and the procedures under §60.13 must be followed fo r installation, evaluation, and operation of the cont inuous emission monitoring system.

(2) Following the date that the initial performanc e test for sulfur dioxide is completed or is required to becompleted under §60.2690, compliance with the sulfur

dioxide emission limit may be determined based on t he 24- hour daily geometric average of the hourly arithmet ic average emission concentrations using continuous em ission monitoring system outlet data. The 1-hour arithmet ic averages must be expressed in parts per million cor rected to 7 percent oxygen (dry basis) and used to calcula te the 24-hour daily geometric average emission concentrat ions and daily geometric average emission percent reductions . The 1-hour arithmetic averages must be calculated using the data points required under §60.13(e)(2).

(m) For energy recovery units that do not use a we t scrubber, you must install, operate, certify, and m aintain a continuous opacity monitoring system according to the procedures in paragraphs (m)(1) through (5) of this section by the compliance date specified in §60.22670. Energy recovery units that use a particulate matter contin uous emission monitoring system to demonstrate initial a nd continuing compliance according to the procedures i n §60.2730(n) are not required to install a continuou s opacity monitoring system and must perform the annu al performance tests for opacity consistent with §60.2 710(e).

(1) Install, operate, and maintain each continuous opacity monitoring system according to performance specification 1 of 40 CFR part 60, appendix B.

(2) Conduct a performance evaluation of each continuous opacity monitoring system according to t he requirements in §60.13 and according to PS-1 of 40 CFR part 60, appendix B.

(3) As specified in §60.13(e)(1), each continuous opacity monitoring system must complete a minimum o f one cycle of sampling and analyzing for each successive 10- second period and one cycle of data recording for e ach successive 6-minute period.

(4) Reduce the continuous opacity monitoring syste m 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 energy recovery units with design capaciti es greater than 250 MMBtu/hr, in place of particulate mattertesting with EPA Method 5, an owner or operator may elect

to install, calibrate, maintain, and operate a cont inuous emission monitoring system for monitoring particula te matter emissions discharged to the atmosphere and r ecord the output of the system. The owner or operator of an affected facility who continuously monitors particu late matter emissions instead of conducting performance testing using EPA Method 5 must install, calibrate, maintai n, and operate a continuous emission monitoring system and must comply with the requirements specified in paragraph s (n)(1) through (n)(14) of this section.

(1) Notify the Administrator 1 month before starti ng use of the system.

(2) Notify the Administrator 1 month before stoppi ng use of the system.

(3) The monitor must be installed, evaluated, and operated in accordance with the requirements of per formance specification 11 of appendix B of this part and qua lity assurance requirements of procedure 2 of appendix F of this part and §60.13.

(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 unde r §60.2690 or within 180 days of notification to the Administrator of use of the continuous monitoring s ystem if the owner or operator was previously determining co mpliance by Method 5 performance tests, whichever is later.

(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 percen t oxygen. The relationship between oxygen and carbon dioxide levels for the affected facility must be establishe d according to the procedures and methods specified i n §60.2145(r)(5)(i) through (r)(5)(iv).

(6) The owner or operator of an affected facility must conduct an initial performance test for partic ulate matter emissions as required under §60.2690. Compl iance with the particulate matter emission limit must be determined by using the continuous emission monitor ing system specified in paragraph (n) of this section t omeasure particulate matter and calculating a 24-hou r block

arithmetic average emission concentration using EPA Reference Method 19, section 4.1.

(7) Compliance with the particulate matter emissio n limit must be determined based on the 24-hour daily (block) average of the hourly arithmetic average emission concentrations using continuous emission monitoring system outlet data.

(8) At a minimum, valid continuous emission monitoring system hourly averages must be obtained as specified in §60.2735(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 t o 7 percent oxygen (or carbon dioxide)(dry basis) and m ust be used to calculate the 24-hour daily arithmetic aver age emission concentrations. The 1-hour arithmetic ave rages must be calculated using the data points required u nder §60.13(e)(2).

(10) All valid continuous emission monitoring syst em data must be used in calculating average emission concentrations even if the minimum continuous emiss ion monitoring system data requirements of paragraph (n )(8) of this section are not met.

(11) The continuous emission monitoring system mus t be operated according to performance specification 11 in appendix B of this part.

(12) During each relative accuracy test run of the continuous emission monitoring system required by performance specification 11 in appendix B of this part, particulate matter and oxygen (or carbon dioxide) d ata must be collected concurrently (or within a 30- to 60-mi nute period) by both the continuous emissions monitors a nd the test methods.

(i) For particulate matter, EPA Reference Method 5 must be used.

(ii) For oxygen (or carbon dioxide), EPA Reference Method 3, 3A, or 3B, as applicable must be used.(13) Quarterly accuracy determinations and daily

calibration drift tests must be performed in accord ance with procedure 2 in appendix F of this part.

(14) When particulate matter emissions data are no t obtained because of continuous emission monitoring system breakdowns, repairs, calibration checks, and zero a nd span adjustments, emissions data must be obtained by usi ng other monitoring systems as approved by the Administrator or EPA Reference Method 19 to provide, as necessary, valid emissions data for a minimum of 85 percent of the h ours per day, 90 percent of the hours per calendar quarter, and 95 percent of the hours per calendar year that the aff ected facility is operated and combusted waste.

(o) For energy recovery units, you must install, operate, certify and maintain a continuous emission monitoring system for carbon monoxide, according to the requirements of performance specification 4B of app endix B of this part and quality assurance procedure 1 of a ppendix F of this part.

(p) The owner/operator of an affected source with a bypass stack shall install, calibrate (to manufactu rer’s specifications), maintain and operate a device or m ethod for measuring the use of the bypass stack including date, time and duration.

§60.2735 Is there a minimum amount of monitoring data I must obtain?

(a) Y ou must conduct all monitoring at all times the CIS WI unit is operating.

(b) You must use all the data collected during all periods in assessing compliance with the operating limits.

(c) For continuous emission monitoring systems for measuring sulfur dioxide emissions, valid continuou s monitoring system hourly averages must be obtained as specified in paragraphs (c)(1) and (c)(2) of this s ection for a minimum of 85 percent of the hours per day, 9 0 percent of the hours per calendar quarter, and 95 p ercent of the hours per calendar year that the affected fa cility is combusting waste. All valid continuous emission monitoring system data must be used in calculating average emission concentrations and percent reductions even if the Formatted: Space Before: 0 pt, After: 0 pt

Formatted: Indent: First line: 0.5"

Formatted: Font: Courier New, Not Bold Deleted: ¶

Deleted: ¶

Deleted: Except for monitoring malfunctions, associated repairs, and required quality assurance or quality control activities (including, as applicable, calibration checks and required zero and span adjustments of the monitoring system),
Deleted: y Deleted: Do not use data recorded during monitoring malfunctions, associated repairs, and required quality assurance or quality control activities for meeting the requirements of this subpart, i ncluding data averages and calculations.
Deleted: otherminimum continuous emission monitoring system data

requirements of this paragraph (c) are not met.

(1) At least 2 data points per hour must be used t o calculate each 1-hour arithmetic average.

(2) Each sulfur dioxide 1-hour arithmetic average must be corrected to 7 percent oxygen on an hourly basis using the 1-hour arithmetic average of the oxygen ( or carbon dioxide) continuous emission monitoring syst em data.

(d) For continuous emission monitoring systems for measuring nitrogen oxides emissions, valid continuo us emission monitoring system hourly averages must be obtained as specified in as specified in paragraphs (d)(1) a nd (d)(2) of this section for a minimum of 85 percent of the hours per day, 90 percent of the hours per calendar quarter, and for 95 percent of the hours per calend ar year that the affected facility is combusting waste. Al l valid continuous emission monitoring system data must be used in calculating average emission concentrations and per cent reductions even if the minimum continuous emission monitoring system data requirements of this paragra ph (d) are not met.

(1) At least 2 data points per hour must be used t o calculate each 1-hour arithmetic average.

(2) Each nitrogen oxides 1-hour arithmetic average must be corrected to 7 percent oxygen on an hourly basis using the 1-hour arithmetic average of the oxygen ( or carbon dioxide) continuous emission monitoring syst em data.

(e) For continuous emission monitoring systems for measuring particulate matter emissions, valid conti nuous monitoring system hourly averages must be obtained as specified in paragraphs (e)(1) and (e)(2) for a min imum of 85 percent of the hours per day, 90 percent of the hours per calendar quarter, and 95 percent of the hours p er calendar year that the affected source is combustin g waste. All valid continuous emission monitoring system dat a must be used in calculating average emission concentrati ons and percent reductions even if the minimum continuous e mission monitoring system data requirements of this paragra ph (c) are not met.(1) At least 2 data points per hour must be used to

calculate each one-hour arithmetic average.

(2) Each particulate matter one-hour arithmetic ave rage must be corrected to 7 percent oxygen on an hourly basis using the one-hour arithmetic average of the oxygen (or carbon dioxide) continuous emission monitoring system data. Model Rule—Recordkeeping and Reporting

§60.2740 What records must I keep?

You must maintain the items (as applicable) as specified in paragraphs (a) , (b), and (e) through ( t ) 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, an d hourly charge rates.

(2) Liquor flow rate to the wet scrubber inlet ever y 15 minutes of operation, as applicable.

(3) Pressure drop across the wet scrubber system ev ery 15 minutes of operation or amperage to the wet scru bber every 15 minutes of operation, as applicable.

(4) Liquor pH as introduced to the wet scrubber eve ry 15 minutes of operation, as applicable.

(5) For affected CISWI units that establish operati ng limits for controls other than wet scrubbers under §60.2675(d) through (f) or §60.2680, you must maintain data collected for all operating parameters used to determine compliance with the operating limits.

(6) If a fabric filter is used to comply with the emission limitations, you must record the date, tim e, and duration of each alarm and the time corrective acti on 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 duri ng each 6-month period that the alarm sounds, calculated as specified in §60.2675(c).

(c) [Reserved] Formatted: Space Before: 0 pt, After: 0 pt
Deleted: ¶ ¶

Deleted: 13
Deleted: m

Deleted: Identification of calendar dates and times for which monitoring systems used to monitor operating limits were inoperative, inactive, malfunctioning, or out of control (except for downtime associated with zero and span and other routine calibration checks). Identify the operating parameters not measured, the duration, reasons for not obtaining the data, and a description of corrective actions taken.(d) [Reserved]

(e) Identification of calendar dates and times for which data show a deviation from the operating limi ts in table 3 of this subpart or a deviation from other o perating limits established under §60.2675(d) through (f) or §60.2680 with a description of the deviations, reas ons for such deviations, and a description of corrective ac tions taken.

(f) The results of the initial, annual, and any subsequent performance tests conducted to determine compliance with the emission limits and/or to estab lish operating limits, as applicable. Retain a copy of t he complete test report including calculations.

(g) Records showing the names of CISWI unit operato rs who have completed review of the information in §60 .2660(a) as required by §60.2660(b), including the date of t he initial review and all subsequent annual reviews.

(h) Records showing the names of the CISWI operator s who have completed the operator training requiremen ts under §60.2635, met the criteria for qualification under §60.2645, and maintained or renewed their qualifica tion under §60.2650 or §60.2655. Records must include documentation of training, the dates of the initial and refresher training, and the dates of their qualific ation and all subsequent renewals of such qualifications.

(i) For each qualified operator, the phone and/or pager number at which they can be reached during op erating hours.

(j) Records of calibration of any monitoring device s as required under §60.2730.

(k) Equipment vendor specifications and related operation and maintenance requirements for the inci nerator, emission controls, and monitoring equipment.

(l) The information listed in §60.2660(a).

(m) On a daily basis, keep a log of the quantity of waste burned and the types of waste burned (always required). Deleted: Identification of calendar dates, times, and durations of malfunctions, and a description of the malfunction and the corrective action taken.(n) Maintain records of the annual air pollution

control device inspections that are required for ea ch CISWI unit subject to the emissions limits in table 2 of this subpart or tables 6 through 10 of this subpart, any required maintenance, and any repairs not completed within 10 days of an inspection or the timeframe establish ed by the state regulatory agency.

(o) For continuously monitored pollutants or parameters, you must document and keep a record of the following parameters measured using continuous moni toring systems.

(1) All 6-minute average 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.

(5) All one-hour average concentrations of particulate matter emissions.

(6) All one-hour average concentrations of mercury emissions.

(7) All one-hour average concentrations of hydroge n chloride emissions.

(p) Records indicating use of the bypass stack, including dates, times and durations.

(q) If you choose to stack test less frequently th an annually, consistent with §60.2720(a) through (c), you must keep annual records that document that your emissio ns in the previous stack test(s) were less than 75 percen t of the applicable emission limit and document that there w as no change in source operations including fuel composit ion and operation of air pollution control equipment that w ould cause emissions of the relevant pollutant to increa se within the past year.(r) Records of the occurrence and duration of each

malfunction of operation (i.e., process equipment) or the air pollution control and monitoring equipment.

(s) Records of all required maintenance performed on the air pollution control and monitoring equipment.

(t) Records of actions taken during periods of malfunction to minimize emissions in accordance wit h §60.11(d), including corrective actions to restore malfunctioning process and air pollution control an d monitoring equipment to its normal or usual manner of operation.

§60.2745 Where and in what format must I keep my records?

All records must be available onsite in either pape r copy or computer-readable format that can be printe d upon request, unless an alternative format is approved b y the Administrator.

§60.2750 What reports must I submit?

See table 5 of this subpart for a summary of the reporting requirements.

§60.2755 When must I submit my waste management p lan?

You must submit the waste management plan no later than the date specified in table 1 of this subpart for submittal of the final control plan.

§60.2760 What information must I submit following my initial performance test?

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 re ports must be signed by the facilities manager.

(a) The complete test report for the initial performance test results obtained under §60.2700, a s applicable.

(b) The values for the site-specific operating lim its established in §60.2675 or §60.2680.(c) If you are using a fabric filter to comply wit h

the emission limitations, documentation that a bag leak detection system has been installed and is being op erated, calibrated, and maintained as required by §60.2730( b).

§60.2765 When must I submit my annual report?

You must submit an annual report no later than 12 months following the submission of the information in §60.2760. You must submit subsequent reports no mor e than 12 months following the previous report. (If the un it 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.)

§60.2770 What information must I include in my an nual report?

The annual report required under §60.2765 must incl ude the ten items listed in paragraphs (a) through (j) of this section. If you have a deviation from the operating limits or the emission limitations, you must also submit d eviation reports as specified in §§60.2775, 60.2780, and 60. 2785.

(a) Company name and address.

(b) Statement by a responsible official, with that official's name, title, and signature, certifying t he 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 establishe d pursuant to §60.2675 or §60.2680.

(e) If no deviation from any emission limitation o r operating limit that applies to you has been report ed, a statement that there was no deviation from the emis sion limitations or operating limits during the reportin g period

.
(f) The highest recorded 3-hour average and the lowest recorded 3-hour average, as applicable, for each operating parameter recorded for the calendar year being reported. Deleted: , and that no monitoring system used to determine compliance with the operating limits was inoperative, inactive, malfunctioning or out of control.(g) Information recorded under §60.2740(b)(6) and (c)

through (e) for the calendar year being reported.

(h) If a performance test was conducted during the reporting period, the results of that test.

(i) If you met the requirements of §60.2720(a) or (b), and did not conduct a performance test during the reporting period, you must state that you met the requirements of §60.2720(a) or (b), and, therefore, you were not required to conduct a performance test dur ing the reporting period.

(j) Documentation of periods when all qualified CI SWI unit operators were unavailable for more than 8 hou rs, but less than 2 weeks.

(k) If you had a malfunction during the reporting period, the compliance report must include the numb er, duration, and a brief description for each type of malfunction that occurred during the reporting peri od and that caused or may have caused any applicable emiss ion limitation to be exceeded. The report must also in clude a description of actions taken by an owner or operato r during a malfunction of an affected source to minimize emi ssions in accordance with §60.11(d), including actions tak en to correct a malfunction.

(l) For each deviation from an emission or operating limitation that occurs for a CISWI unit for which y ou are not using a CMS to comply with the emission or oper ating 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 p eriod.

(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 continuous emissio n monitoring system, was out of control as specified in paragraph (o) of this section, the annual report mu st contain the following information for each deviatio n from an emission or operating limitation occurring for a CISWIunit for which you are using a continuous monitorin g system

to comply with the emission and operating limitatio ns in this subpart.

(1) The date and time that each malfunction started and stopped.

(2) The date, time, and duration that each CMS was inoperative, except for zero (low-level) and high-l evel checks.

(3) The date, time, and duration that each continuous monitoring system was out-of-control, including sta rt 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 t hat reporting period.

(6) A breakdown of the total duration of the deviations during the reporting period into those t hat 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 per iod, and the total duration of continuous monitoring system downtime as a percent of the total operating time of the CIS WI unit at which the continuous monitoring system downtime occurred during that reporting period.

(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 description 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 continuous emissio n monitoring system, was not out of control as specif ied in paragraph (o) of this section, a statement that the re 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 if any of the following occur.

(1) The zero (low-level), mid-level (if applicable), or high-level calibration drift exceeds two times t he applicable calibration drift specification in the applicable performance specification or in the rele vant standard.

(2) The continuous monitoring system fails a performance test audit (e.g., cylinder gas audit), relative accuracy audit, relative accuracy test audit, or li nearity test audit.

(3) The continuous opacity monitoring system calibration drift exceeds two times the limit in th e applicable performance specification in the relevan t standard.

§60.2775 What else must I report if I have a devi ation from the operating limits or the emission limitatio ns?

(a) You must submit a deviation report if any recorded 3-hour average parameter level is above th e maximum operating limit or below the minimum operat ing limit established under this subpart, if the bag le ak detection system alarm sounds for more than 5 perce nt of the operating time for the 6-month reporting period , or if a performance test was conducted that deviated from any emission limitation.

(b) The deviation report must be submitted by Augu st 1 of that year for data collected during the first half of the calendar year (January 1 to June 30), and by Fe bruary 1of the following year for data you collected during the

second half of the calendar year (July 1 to Decembe r 31).

§60.2780 What must I include in the deviation rep ort?

In each report required under §60.2775, for any pollutant or parameter that deviated from the emiss ion limitations or operating limits specified in this s ubpart, include the six items described in paragraphs (a) t hrough (f) of this section.

(a) The calendar dates and times your unit deviate d from the emission limitations or operating limit requirements.

(b) The averaged and recorded data for those dates

.
(c) Duration and causes of the following:

(1) E ach deviation from emission limitations or operating limits and your corrective actions.

(2) Bypass events and your corrective actions.

(d) A copy of the operating limit monitoring data during each deviation and any test report that docu ments the emission levels. (e) [Removed] (f) [Removed]

§60.2785 What else must I report if I have a devi ation from the requirement to have a qualified operator accessible?

(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. Formatted: Font: Bold Deleted: ¶

Deleted: e
Deleted: the

Deleted: ¶
Deleted: The dates, times, number, duration, and causes for monitoring downtime incidents (other than downtime associated with zero, span, and other routine calibration checks). ¶ ¶
Deleted: Whether each deviation occurred during a period of startup, shutdown, or malfunction, or during another period.¶(iii) The date when you anticipate that a qualifie d

operator will be available.

(2) Submit a status report to the Administrator eve ry 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 Administrato r, under the provisions of §60.2665(b)(2), due to a fa ilure to provide an accessible qualified operator, you must notify the Administrator that you are resuming operation o nce a qualified operator is accessible.

§60.2790 Are there any other notifications or rep orts that I must submit?

Yes. You must submit notifications as provided by §60.7. §60.2795 In what form can I submit my reports?

(a) Submit initial, annual and deviation reports electronically or in paper format, postmarked on or before the submittal due dates.

(b) After December 31, 2011, within 60 days after t he date of completing each performance evaluation cond ucted to demonstrate compliance with this subpart, the owner or operator of the affected facility must submit the t est data to EPA by entering the data electronically into EPA ’s WebFIRE database through EPA’s Central Data Exchang e. The owner or operator of an affected source shall enter the test data into EPA’s database using the Electronic Reporting Tool or other compatible electronic sprea dsheet. Only performance evaluation data collected using me thods compatible with ERT are subject to this requirement to be submitted electronically into EPA’s WebFIRE databas e.
§60.2800 Can reporting dates be changed? Deleted: ¶
Deleted:
,

Deleted: ¶ ¶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 reportin g date.

Model Rule—Title V Operating Permits

§60.2805 Am I required to apply for and obtain a title V operating permit for my unit?

Yes. Each CISWI unit and air curtain incinerator affected by this subpart must operate pursuant to a permit issued under section 129(e) and title V of the Clea n Air Act

.

Model Rule—Air Curtain Incinerators

§60.2810 What is an air curtain incinerator?

(a) An air curtain incinerator operates by forcefu lly projecting a curtain of air across an open chamber or open pit in which combustion occurs. Incinerators of th is type can be constructed above or below ground and with o r without refractory walls and floor. (Air curtain incinerators are not to be confused with convention al combustion devices with enclosed fireboxes and cont rolled air technology such as mass burn, modular, and flui dized bed combustors.)

(b) Air curtain incinerators that burn only the materials listed in paragraphs (b)(1) through (3) o f this section are only required to meet the requirements under “Air Curtain Incinerators” (§§60.2810 through 60.28 70).

(1) 100 percent wood waste.

(2) 100 percent clean lumber.

(3) 100 percent mixture of only wood waste, clean lumber, and/or yard waste.

§60.2815 What are my requirements for meeting inc rements of progress and achieving final compliance? Deleted: ¶

Deleted: by the later of the two dates in paragraphs (a) and (b) of this section.
Deleted: (a) Thirty-six months after December 1, 2000.¶ (b) The effective date of the title V permit program to which your unit is subject. If your unit is subject to title V as a result of some triggering requirement(s) other than this subpart (for example, being a major source), then your unit may be required to apply for and obta in a title V permit prior to the deadlines noted above. If more than one requirement triggers the requirement to apply for a title V permit, the 12-month timeframe for filing a title V application is triggered by the requirement which first causes the source to be subject to title V.If you plan to achieve compliance more than 1 year

following the effective date of state plan approval , you must meet the two increments of progress specified in paragraphs (a) and (b) of this section.

(a) Submit a final control plan.

(b) Achieve final compliance.

§60.2820 When must I complete each increment of p rogress?

Table 1 of this subpart specifies compliance dates for each of the increments of progress.

§60.2825 What must I include in the notifications of achievement of increments of progress?

Your notification of achievement of increments of progress must include the three items described in paragraphs (a) through (c) of this section.

(a) Notification that the increment of progress ha s been achieved.

(b) Any items required to be submitted with each increment of progress (see §60.2840).

(c) Signature of the owner or operator of the incinerator.

§60.2830 When must I submit the notifications of achievement of increments of progress?

Notifications for achieving increments of progress must be postmarked no later than 10 business days a fter the compliance date for the increment.

§60.2835 What if I do not meet an increment of pr ogress?

If you fail to meet an increment of progress, you m ust submit a notification to the Administrator postmark ed within 10 business days after the date for that inc rement of progress in table 1 of this subpart. You must in form the Administrator that you did not meet the increment, and you must continue to submit reports each subsequent cal endar month until the increment of progress is met.§60.2840 How do I comply with the increment of pr ogress

for submittal of a control plan?

For your control plan increment of progress, you mu st satisfy the two requirements specified in paragraph s (a) and (b) of this section.

(a) Submit the final control plan, including a description of any devices for air pollution contro l and any process changes that you will use to comply wit h the emission limitations and other requirements of this subpart.

(b) Maintain an onsite copy of the final control plan.

§60.2845 How do I comply with the increment of pr ogress for achieving final compliance?

For the final compliance increment of progress, you must complete all process changes and retrofit cons truction of control devices, as specified in the final contr ol plan, so that, if the affected incinerator is brought onl ine, all necessary process changes and air pollution control devices would operate as designed.

§60.2850 What must I do if I close my air curtain incinerator and then restart it?

(a) If you close your incinerator but will reopen it prior to the final compliance date in your state pl an, you must meet the increments of progress specified in § 60.2815.

(b) If you close your incinerator but will restart it after your final compliance date, you must complete emission control retrofits and meet the emission limitations on the date your incinerator restarts operation.

§60.2855 What must I do if I plan to permanently close my air curtain incinerator and not restart it?

If you plan to close your incinerator rather than comply with the state plan, submit a closure notifi cation, including the date of closure, to the Administrator by the date your final control plan is due.§60.2860 What are the emission limitations for ai r

curtain incinerators?

After the date the initial stack test is required o r completed (whichever is earlier), you must meet the limitations 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 th ree 1- hour blocks consisting of ten 6-minute average opac ity values), except as described in paragraph (b) of th is section.

(b) Maintain opacity to less than or equal to 35 percent opacity (as determined by the average of th ree 1- hour blocks consisting of ten 6-minute average opac ity values) during the startup period that is within th e first 30 minutes of operation.

§60.2865 How must I monitor opacity for air curta in 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 specifi ed in §60.8 no later than 180 days after your final co mpliance date.

(c) After the initial test for opacity, conduct annual tests no more than 12 calendar months follow ing the date of your previous test.

§60.2870 What are the recordkeeping and reporting requirements for air curtain incinerators?

(a) Keep records of results of all initial and ann ual opacity tests onsite in either paper copy or electr onic format, unless the Administrator approves another f ormat, for at least 5 years.

(b) Make all records available for submittal to th e Administrator or for an inspector's onsite review. Deleted: (a)

Deleted: (1)
Deleted: 2

Deleted: ¶ (1) The opacity limitation is 10 percent (6-minute average), except as described in paragraph (a)(2) of this section.¶ (2) The opacity limitation is 35 percent (6-minute average) during the startup period that is within the first 30 minutes of operation.¶ (b) Except during malfunctions, the requirements of this subpart apply at all times, and each malfunction must not exceed 3 hours.¶

Deleted: ¶(c) Submit an initial report no later than 60 days

following the initial opacity test that includes th e information specified in paragraphs (c) (1) and (2) of this section.

(1) The types of materials you plan to combust in y our air curtain incinerator.

(2) The results ( as determined by the average of three 1-hour blocks consisting of the 6-minute average opacity values ) of the initial opacity tests.

(d) Submit annual opacity test results within 12 months following the previous report.

(e) Submit initial and annual opacity test reports as electronic or paper copy on or before the applicabl e submittal date and keep a copy onsite for a period of 5 years. Model Rule—Definitions

§60.2875 What definitions must I know?

Terms used but not defined in this subpart are defi ned in the Clean Air Act and subparts A and B of this p art.

Administrator means the Administrator of the U.S. Environmental Protection Agency or his/her authoriz ed representative or Administrator of a State Air Poll ution Control Agency.

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 without refractory walls and flo or. (Air curtain incinerators are not to be confused with conventional combustion devices with enclosed fireb oxes and controlled air technology such as mass burn, modula r, and fluidized bed combustors.)

Auxiliary fuel means natural gas, liquified petroleum gas, fuel oil, or diesel fuel.

Bag leak detection system means an instrument that is capable of monitoring particulate matter loadings i n the exhaust of a fabric filter (i.e., baghouse) in orde r to Formatted: Indent: First line: 0", Space Before: 0 pt, After: 0 pt

Formatted: Space Before: 0 pt, After: 0 pt Deleted: each

Deleted: ¶ ¶

Deleted: ¶ Agricultural waste means vegetative agricultural materials such as nut and grain hulls and chaff (e.g., almond, walnut, peanut, rice, and wheat), bagasse, orchard prunings, corn stalks, coffee bean hulls and grounds, and other vegetative waste materials generated as a result of agricultural operations.¶detect bag failures. A bag leak detection system in cludes,

but is not limited to, an instrument that operates on triboelectric, light scattering, light transmittanc e, or other principle to monitor relative particulate mat ter loadings.

Burn-off oven means any rack reclamation unit, part reclamation unit, or drum reclamation unit

.
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 December 31. Chemotherapeutic waste means waste material resulting from the production or use of antineoplastic agents used for the purpose of st opping or reversing the growth of malignant cells.

Clean lumber means wood or wood products that have been cut or shaped and include wet, air-dried, and kilndried wood products. Clean lumber does not include wood products that have been painted, pigment-stained, o r pressure-treated by compounds such as chromate copp er 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 any solid waste as that term is defined in 40 CFR Part 241. While not all CISWI units will include all of the followi ng components, a CISWI unit includes, but is not limit ed to, the solid waste feed system, grate system, flue gas system, waste heat recovery equipment, if any, and bottom a sh system. The CISWI unit does not include air polluti on control equipment or the stack. The CISWI unit boun dary starts at the solid waste hopper (if applicable) an d extends through two areas: The combustion unit flue gas system, which ends immediately after the last combu stion chamber or after the waste heat recovery equipment, if any; and the combustion unit bottom ash system, which en ds at the truck loading station or similar equipment that transfers the ash to final disposal. The CISWI unit Formatted: Font: (Default) Courier New, No underline
Formatted: Font: (Default) Courier New Deleted: ¶ ¶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.

Cyclonic barrel burner means a combustion device for waste materials that is attached to a 55 gallon, op en-head drum. The device consists of a lid, which fits onto and encloses the drum, and a blower that forces combust ion air into the drum in a cyclonic manner to enhance the m ixing of waste material and air.

Deviation means any instance in which an affected source subject to this subpart, or an owner or oper ator of such a source:

(1) Fails to meet any requirement or obligation established by this subpart, including but not limi ted to any emission limitation, operating limit, or operat or qualification and accessibility requirements

.
(2) Fails to meet any term or condition that is adopted to implement an applicable requirement in t his subpart and that is included in the operating permi t for any affected source required to obtain such a permi t

.
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 incinerat ion unit without energy recovery.

Drum reclamation unit means a unit that burns residues out of drums (e.g., 55 gallon drums) so that the dr ums can be reused.

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 Adminitrator under RCRA in 40 CFR 240) for energy r ecovery. Energy recovery units include units that would be Deleted: means any combustion unit that combusts commercial or industrial waste (as defined in this subpart), that is a distinct operating unit of any commercial or industrial facility (including field erected, modular, and custom built incineration units operating with starved or excess air), and any air curtain incinerator that is a distinct operating unit of any commercial or industrial facility that does not comply with the opacity limits under this subpart applicable to air curtain incinerators burning commercial or industrial waste. While not all CISWI units will include all of the following components, a CISWI unit includes, but is not limited to, the commercial or industrial 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 commercial or industrial 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 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.
Deleted: ¶ ¶
Deleted: ;
Deleted: ; or
Deleted: (3) Fails to meet any emission limitation, operating limit, or operator qualification and accessibility requirement in this subpart during startup, shutdown, or malfunction, regardless or whether or not such failure is permitted by this subpart.¶ ... [7]considered boilers and process heaters if they did not

combust solid waste.

Fabric filter means an add-on air pollution control device used to capture particulate matter by filter ing gas streams through filter media, also known as a bagho use.

Incinerator

means any furnace used in the process of combusting solid waste (as the term is defined by t he Administrator under RCRA in 40 CFR 240) for the pur pose of reducing the volume of the waste by removing combus tible matter. Incinerator designs include single chamber , twochamber and cyclonic burn barrels.

Kiln means an oven or furnace, including any associated preheater or precalciner devices, used f or processing a substance by burning, firing, or dryin g. Kilns include cement kilns, that produce clinker by heating limestone and other materials for subsequent produc tion of Portland cement and lime kilns, that produce quickl ime by calcination of limestone.

Low-level radioactive waste means waste material which contains radioactive nuclides emitting primarily be ta or gamma radiation, or both, in concentrations or quan tities that exceed applicable federal or state standards f or unrestricted release. Low-level radioactive waste i s not high-level radioactive waste, spent nuclear fuel, o r byproduct material as defined by the Atomic Energy Ac t of 1954 (42 U.S.C. 2014(e)(2)).

Minimum voltage or amperage means 90 percent of the lowest test-run average voltage or amperage to the electrostatic precipitator measured from the pressu re drop and liquid flow rate monitors during the most recen t particulate matter or mercury performance test demonstrating compliance with the applicable emissi on limits.

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 li fe of the unit exceeds 50 percent of the original cost of building and installing the CISWI unit (not includi ng the cost of land) updated to current costs (current dol lars). Formatted: Font: (Default) Courier New

Formatted: Indent: First line: 0" Deleted:

Deleted: Malfunction means any sudden, infrequent, and not reasonably preventable failure of air pollution control 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.¶

Deleted: ¶To determine what systems are within the boundary o f the

CISWI unit used to calculate these costs, see the definition of CISWI unit.

(2) Any physical change in the CISWI unit or chang e in the method of operating it that increases the am ount of any air pollutant emitted for which section 129 or section 111 of the Clean Air Act has established standards.

Opacity

means the degree to which emissions reduce the transmission of light and obscure the view of an ob ject in the background.

Part reclamation unit means a unit that burns coatings off parts (e.g., tools, equipment) so that the part s 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 tra nsport the waste material, and animal bedding (if applicab le).

Rack reclamation unit means a unit that burns the coatings off racks used to hold small items for app lication of a coating. The unit burns the coating overspray off the rack so the rack can be reused.

Raw mill means a ball and 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.

Reconstruction means rebuilding a CISWI unit and meeting two criteria:

(1) The reconstruction begins on or after June 1, 2001.(2) The cumulative cost of the construction over t he

life of the incineration unit exceeds 50 percent of the original cost of building and installing the CISWI unit (not including land) updated to current costs (curr ent dollars). To determine what systems are within the boundary of the CISWI unit used to calculate these costs, se e 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 al l classes of refuse-derived fuel including two fuels:

(1) Low-density fluff refuse-derived fuel through densified refuse-derived fuel.

(2) Pelletized refuse-derived fuel.

Small, remote incinerator means an incinerator that combusts solid waste (as that term is defined by th e Administrator under RCRA) in 40 CFR 240 and has the capacity to combust 1 ton per day or less solid was te and is more than 50 miles driving distance to the neare st municipal solid waste landfill.

Shutdown means the period of time after all waste has been combusted in the primary chamber.

Solid waste incineration unit means a distinct operating unit of any facility which combusts any s olid waste material from commercial or industrial establ ishments or the general public (including single and multipl e residences, hotels and motels). Such term does not include incinerators or other units required to have a perm it under section 3005 of the Solid Waste Disposal Act. The t erm "solid waste incineration unit" does not include (A ) materials recovery facilities (including primary or secondary smelters) which combust waste for the pri mary purpose of recovering metals, (B) qualifying small power production facilities, as defined in section 3(17)( C) of the Federal Power Act (16 U.S.C. 769(17)(C)), or qu alifying 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 units which burn tires o r used oil, but not including refuse-derived fuel) for the production of electric energy or in the case of qua lifying cogeneration facilities which burn homogeneous wast e for Formatted: No underline Deleted: Solid waste means any garbage, refuse, sludge from a waste treatment plant, water supply treatment plant, or air pollution control facility and other discarded material, including solid, liquid, semisolid, or contained gaseous material resulting from industrial, commercial, mining, agricultural operations, and from community activities, but does not include solid or dissolved material in domestic sewage, or solid or dissolved materials in irrigation return flows or industrial discharges which are point sources subject to
per mits under section 402 of the Federal Water Pollution Control Act, as amended (33 U.S.C. 1342), or source, special nuclear, or byproduct material as defined by the Atomic Energy Act of 1954, as amended (42 U.S.C. 2014).¶the production of electric energy and steam or form s of

useful energy (such as heat) which are used for ind ustrial, commercial, heating or cooling purposes, or (C) air curtain incinerators provided that such incinerators only b urn wood wastes, yard wastes and clean lumber and that such air curtain incinerators comply with opacity limitation s to be established by the Administrator by rule.

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 the first charge to th e unit.

Waste-burning kiln means a kiln that is heated, in whole or in part, by combusting solid waste (as the term is defined by the Administrator under RCRA in 40 CFR 2 40).

Wet scrubber means an add-on air pollution control device that utilizes an aqueous or alkaline scrubbi ng liquor to collect particulate matter (including non vaporous 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 d oes not include:

(1) Grass, grass clippings, bushes, shrubs, and clippings from bushes and shrubs from residential, commercial/retail, institutional, or industrial sou rces as part of maintaining yards or other private or publi c lands.

(2) Construction, renovation, or demolition wastes

.
(3) Clean lumber.

Table 1 to Subpart DDDD of Part 60—Model Rule— Increments of Progress and Compliance Schedules Comply with these increments

of progress By these dates a

Increment 1—Submit final control plan (Dates to be specified in state plan) Formatted: Space Before: 0 pt, After: 0 ptIncrement 2—Final compliance (Dates to be specified in state plan) b

a Site-specific schedules can be used at the discreti on of the state.
b The date can be no later than 3 years after the eff ective date of state plan approval or December 1, 2005 , for CISWI units that commenced construction on or before Nove mber 30, 1999. The date can be no later than 3 years after the effective date of approval of a revised state plan or [THE DATE 5 YEARS AFTER PUBLICATION OF THE FINAL RULE IN THE FEDERAL REGISTER] for CISWI units that commenced construction on or before [INSERT THE DATE OF PUBLI CATION IN THE FEDERAL REGISTER]

.

Table 2 to Subpart DDDD of Part 60—Model Rule—Emiss ion Limitations That Apply Before. [Date to be specified in state plan] b

.

For the air pollutant You must meet

this emission 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 t est

(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, 10A, or 10B, of appendix A of this part)
Dioxins/furans (toxic equivalency basis) 0.41
nanograms per dry standard cubic meter 3-run

average (1 hour minimum sample time per run) Performance test

(Method 23 of appendix A of this part)

Hydrogen chloride 62 parts per

million by dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 26A of appendix A of this part)

Lead 0.04 3-run Performance test Deleted:

.milligrams per dry standard cubic meter average (1

hour minimum sample time per run) (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)

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

(Methods 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 (1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A of this part)

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns. b The date specified in the state plan can be no late r than 3 years after the effective date of approval of a r evised state plan or [THE DATE 5 YEARS AFTER PUBLICATION O F THE FINAL RULE IN THE FEDERAL REGISTER].

Table 3 to Subpart DDDD of Part 60—Model Rule— Operating Limits for Wet Scrubbers

For these operating You must

establish And monitor using these minimum frequenciesparameters these operating limits 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

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 4 to Subpart DDDD of Part 60—Model Rule—Toxic Equivalency Factors

Dioxin/furan congener Toxic equivalency factor
2,3,7,8-tetrachlorinated dibenzo-pdioxin 1

1,2,3,7,8-pentachlorinated dibenzo-pdioxin 0.5

1,2,3,4,7,8-hexachlorinated dibenzo-pdioxin 0.1

1,2,3,7,8,9-hexachlorinated dibenzo-pdioxin 0.1

1,2,3,6,7,8-hexachlorinated dibenzo-pdioxin 0.1

1,2,3,4,6,7,8-heptachlorinated 0.01dibenzo-p-dioxin

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 5 to Subpart DDDD of Part 60—Model Rule—Summa ry of Reporting Requirements a
Report Due date Contents Reference

Waste Management Plan No later than

the date specified in table 1 for submittal of the final control plan • Waste

management plan §60.2755.

Initial Test Report No later than

60 days following the initial performance • Complete test

report for the initial performance test • The values for §60.2760. Deleted: ¶test the sitespecific operating limits • Installation of bag leak detection systems for fabric filters
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 limits

• Highest recorded 3-hour average and the lowest 3-hour
average, as applicable, for each operating parameter recorded for the calendar year being reported

• If a performance test was conducted during the reporting period, the results of the test • If a performance test was not conducted during the reporting period, a statement that the requirements §§60.2765 and

60.2770.

Deleted: • If no deviations or malfunctions were reported, a statement that no deviations occurred during the reporting period

Deleted: • Information for deviations or malfunctions recorded under §60.2740(b)(6) and (c) through (e)of §60. 2720 (a) or (b) were met • Documentation of periods when all qualified CISWI unit operators were unavailable for more than 8 hours but less than 2 weeks

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 any test reports • Dates, times, and causes for monitor downtime incidents §§60.2775 and

60.2780.

Qualified Operator Deviation Notification Within 10 days

of deviation • Statement of

cause of deviation • Description of efforts to have an accessible qualified operator • The date a qualified operator will be accessible §60.2785(a)(1). Deleted: 2155

Deleted: for

Deleted: • Whether each deviation occurred during a period of startup, shutdown, or malfunction¶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 §60.2785(a)(2).

Qualified Operator Deviation Notification of Resumed Operation Prior to

resuming operation • Notification

that you are resuming operation §60.2785(b)

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

Table 6 to Subpart DDDD of Part 60—Model Rule—Emiss ion Limitations That Apply To Incinerators On and After [Date

to be specified in state plan] a

For the air pollutant You must

meet this emission
limitation b Using this

averaging time And determining

compliance using this method

Cadmium 0.0013

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Carbon monoxide 2.2 parts

per million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 10 of appendix A-4 of this part). Use a maximum allowable drift of 0.2 ppm and a span gas Formatted: Space Before: 0 pt, After: 0 pt

Formatted: Space Before: 0 pt, After: 0 pt

Deleted:

Deleted:For the air

pollutant You must

meet this emission
limitation b Using this

averaging time And determining

compliance using this method

with a CO concentration of 10 ppm or less. The span gas must contain approximately the same concentration of CO 2 expected from the source.
Dioxins/furans (total mass basis) 0.031

nanograms per dry standard cubic meter 3-run

average (collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 23 of appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 0.0025

nanograms per dry standard cubic meter 3-run

average (collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 29 parts per

million dry volume 3-run

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

(Method 26A of appendix A-8 of this part).

Lead 0.0026

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish. Deleted:

Deleted:

Deleted:For the air

pollutant You must

meet this emission
limitation b Using this

averaging time And determining

compliance using this method
Mercury 0.0028

milligrams per dry standard cubic meter 3-run

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

(Method 29 or 30B of appendix A-8 of this part).

Opacity 1 percent Three 1- hour blocks consisting of ten 6- minute
average opacity values Performance test

(Method 9 of appendix A-4 of this part).

Oxides of nitrogen 34 parts per

million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part).

Particulate matter filterable 13

milligrams per dry standard cubic meter 3-run

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

(Method 5 or 29 of appendix A-3 or appendix A-8 of this part).

Sulfur dioxide 2.5 parts

per million dry volume 3-run

average (1 hour min imum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a maximum allowable drift of 0.2 ppm and a span gas with concentration of 5 ppm or less.
Fugitive ash Visible

emissions for no more Three 1- hour

observation periods Visible emission

test (Method 22 of appendix A-7 of Deleted: s

Deleted:For the air

pollutant You must

meet this emission
limitation b Using this

averaging time And determining

compliance using this method

than 5 percent of the hourly observation period this part).

a The date specified in the state plan can be no late r than 3 years after the effective date of approval of a r evised state plan or [THE DATE 5 YEARS AFTER PUBLICATION O F THE FINAL RULE IN THE FEDERAL REGISTER].
b All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.

Table 7 to Subpart DDDD of Part 60—Model Rule—Emiss ion Limitations That Apply To Energy Recovery Units Aft er [DATE OF PUBLICATION OF THE FINAL RULE IN THE FEDERAL REG ISTER]

For the air pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.00041

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Carbon monoxide 150 parts

per million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 10 of appendix A-4 of this part).

Dioxins/furans (total mass basis) 0.75

nanograms per dry standard cubic meter 3-run

average (collect a minimum volume of 1 dry standard Performance test

(Method 23 of appendix A-7 of this part). Deleted: ¶

Deleted:For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method
cubic meter)
Dioxins/furans (toxic equivalency basis) 0.059

nanograms per dry standard cubic meter 3-run

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

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 1.5 parts

per million dry volume 3-run

average (collect a minimum volume of 1 dry standard cubic meters) Performance test

(Method 26A of appendix A-8 of this part).

Lead 0.002

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Mercury 0.00096

milligrams per dry standard cubic meter 3-run

average (collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 29 of appendix A of this part).

Opacity 1 percent 6-minute
averages; 1- hour block average for units that operate dry control Continuous opacity

monitoring (performance

s pecification 1 of appendix B of this part), unless equipped with a Deleted:

Deleted:

Deleted:

Deleted:

Deleted:For the air

pollutant You must

meet this emission
limitation a Using this

averaging time And determining

compliance using this method
systems wet scrubber.

Oxides of nitrogen 130 parts

per million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part).

Particulate matter filterable 9.2

milligrams per dry standard cubic meter 3-run

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

(Method 5 or 29 of appendix A-3 or appendix A-8 of this part) if the unit has a design capacit y less than or equal to 250 MMBtu/hr; or PM CEMS (performance specification 11 of appendix B of this part) if the unit has a design capacity greater than 250 MMBtu/hr.

Sulfur dioxide 4.1 parts

per million dry volume 3-run

average (1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a span gas with a concentration of 20 ppm or less.
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 of appendix A-7 of this part). Deleted:a All emission limitations (except for opacity) are m easured

at 7 percent oxygen, dry basis at standard conditio ns.

Table 8 to Subpart DDDD of Part 60—Model Rule—Emiss ion Limitations That Apply to Waste-burning Kilns After [DATE OF PUBLICATION OF THE FINAL RULE IN THE FEDERAL REG ISTER]

For the air pollutant You must meet

this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.0003

milligrams per dry standard cubic meter 3- run average

(collect a minimum volume of 2 dry standard cubic meters) Performance test

(Method 29 of appendix A-8 of this part).

Carbon monoxide 710 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 10 of appendix A-4 of this part).

Dioxins/furans (total mass basis) 2.1 nanograms

per dry standard cubic meter 3- run average

(collect a minimum volume of 1 dry standard cubic meters) Performance test

(Method 23 of appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 0.17

nanograms per dry standard cubic meter 3- run average

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

(Method 23 of appendix A-7 of this part).

Hydrogen chloride 1.5 parts per

million dry volume 3- run average

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

(Method 26A of appendix A-8 of this part).

Lead 0.0027

milligrams per dry standard 3- run average

(collect a minimum volume of 2 Performance test

(Method 29 of appendix A-8 of this part). Deleted: ¶For the air

pollutant You must meet

this emission
limitation a Using this

averaging time And determining

compliance using this method

cubic meter dry standard

cubic meters)
Mercury 0.024

milligrams per dry standard cubic meter 3- run average

(collect a minimum volume of 1 dry standard cubic meters) Mercury CEMS

(performance

s pecification 12A of appendix B of this part or mercury sorbent trap method specified in appendix K of part 75).
Opacity 4 percent Three 1-hour blocks consisting of ten 6-minute
average opacity values Performance test

(Method 9 of appendix A-4 of this part).

Oxides of nitrogen 1100 parts

per million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part).

Particulate matter filterable 60 milligrams

per dry standard cubic meter 3-run aver age

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

(Method 5 or 29 of appendix A-3 of this part).

Sulfur dioxide 410 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part.

Fugitive ash Visible

emissions for no more than 5 percent of Three 1-hour

observation periods Visible emission

test (Method 22 of appendix A-7 of this part). Deleted: ¶
Deleted:For the air

pollutant You must meet

this emission
limitation a Using this

averaging time And determining

compliance using this method
the hourly observation period

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.

Table 9 to Subpart DDDD of Part 60—Model Rule—Emiss ion Limitations That Apply to Burn-off Ovens After [DAT E OF PUBLICATION OF THE FINAL RULE IN THE FEDERAL REGIST ER]

For the air pollutant You must meet

this emission
limitation a Using this

averaging time And determining

compliance using this method

Cadmium 0.0045

milligrams per dry standard cubic meter 3- run average

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.

Carbon monoxide 80 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 10, 10A, or 10B of appendix A-4 of this part).
Dioxins/furans (total mass basis) 310 nanograms

per dry standard cubic meter 3- run average

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

(Method 23 of appendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 25 nanograms

per dry standard cubic meter 3- run average

(collect a minimum volume of 1 dry standard Performance test

(Method 23 of appendix A-7 of this part). Formatted: Indent: First line: 0"For the air

pollutant You must meet

this emission
limitation a Using this

averaging time And determining

compliance using this method
cubic meter)
Hydrogen chloride 130 parts per

million dry volume 3- run average

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

(Method 26A of appendix A-8 of this part).

Lead 0.041

milligrams per dry standard cubic meter 3- run average

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

(Method 29 of appendix A-8 of this part). Use ICPMS for the analytical finish.
Mercury 0.014

milligrams per dry standard cubic meter 3- run average

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

(Method 29 of appendix A-8 of this part.

Opacity 2 percent Three 1-hour blocks consisting of ten 6-minute
average opacity values Performance test

(Method 9 of appendix A-4 of this part).

Oxides of nitrogen 120 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 7E of appendix A-4 of this part).

Particulate matter filterable 33 milligrams

per dry standard cubic meter 3- run average

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

(Method 5 or 29 of appendix A-3 or appendix A-8 of this part).For the air

pollutant You must meet

this emission
limitation a Using this

averaging time And determining

compliance using this method

Sulfur dioxide 11 parts per

million dry volume 3- run average

(1 hour minimum sample time per run) Performance test

(Method 6 or 6c of appendix A-4 of this part. Use a span gas with a concentration of 50 ppm or less.
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 of appendix A-7 of this part).

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.

Table 10 to Subpart DDDD of Part 60—Model Rule—Emis sion Limitations That Apply to Small, Remote Incinerator s After [DATE OF PUBLICATION OF THE FINAL RULE IN THE FEDER AL REGISTER]

For the air pollutant You must meet

this emission
limitation a Using this

averaging time And

determining compliance using this method

Cadmium 0.26

milligrams per dry standard cubic meter 3-run average

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

test (Method 29 of a ppendix A-8 of this part).

Carbon monoxide 78 parts per

million dry volume 3-run average

(1 hour minimum sample time per run) Performance

test (Method 10 of a ppendix A-4 of this part).
Dioxins/furans 1600 nanograms 3-run average PerformanceFor the air

pollutant You must meet

this emission
limitation a Using this

averaging time And

determining compliance using this method
(total mass basis) per dry

standard cubic meter (collect a

minimum volume of 1 dry standard cubic meter) test (Method

23 of a ppendix A-7 of this part).

Dioxins/furans (toxic equivalency basis) 130 nanograms

per dry standard cubic meter 3-run average

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

test (Method 23 of a ppendix A-7 of this part).

Hydrogen chloride 150 parts per

million dry volume 3-run average

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

test (Method 26A of appendix A-8 of this part).

Lead 1.4 milligrams

per dry standard cubic meter 3-run average

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

test (Method 29 of a ppendix A-8 of this part).

Mercury 0.0029

milligrams per dry standard cubic meter 3-run average

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

test (Method 29 of appendix A-8 of this part).

Opacity 13 percent Three 1-hour blocks consisting of ten 6-minute
average opacity values Performance

test (Method 9of appendix A4 of this part).

Oxides of nitrogen 210 parts per

million dry 3-run average

(1 hour Performance

test (MethodFor the air

pollutant You must meet

this emission
limitation a Using this

averaging time And

determining compliance using this method

volume minimum sample

time per run) 7E of a ppendix

A-4 of this part).

Particulate matter filterable 240 milligrams

per dry standard cubic meter 3-run average

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

test (Method 5 or 29 of appendix A-3or appendix A8 of this part).

Sulfur dioxide 44 parts per

million dry volume 3-run average

(1 hour minimum sample time per run) Performance

test (Method 6 or 6c of appendix A-4 of this part.
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 of appendix A-7 of this part).

a All emission limitations (except for opacity) are m easured at 7 percent oxygen, dry basis at standard conditio ns.Page 4: [1] Deleted Author



### Chemical recovery units. 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. The seven types of units described in paragraphs (n)(1) through (7) of this section 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.

(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 burning only manufacturing byproduct streams/residues 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.

(o) Laboratory Analysis Units. Units that burn samples of materials for the purpose of chemical or physical analysis.

Page 4: [2] Deleted Author


### What if my chemical recovery unit is not listed in §60.2020(n)?

### (a) If your chemical recovery unit is not listed in

§60.2020(n), you can petition the Administrator to add your unit to the list. The petition must contain the six items in paragraphs (a)(1) through (6) of this section.

(1) A description of the source of the materials being burned.

(2) A description of the composition of the materials being burned, highlighting the chemical constituents in these materials that are recovered.

(3) A description (including a process flow diagram) of the process in which the materials are burned, highlighting the type, design, and operation of the equipment used in this
process.

(4) A description (including a process flow diagram) of the chemical constituent recovery process, highlighting the type, design, and operation of the equipment used in this
process.

(5) A description of the commercial markets for the recovered chemical constituents and their use.

(6) The composition of the recovered chemical constituents and the composition of these chemical constituents as they are bought and sold in commercial markets.

(b) Until the Administrator approves your petition, the incineration unit is covered by this subpart.

(c) If a petition is approved, the Administrator will amend §60.2020(n) to add the unit to the list of chemical recovery units.

Page 57: [3] Deleted Author



### means any combustion unit that combusts commercial or industrial waste (as defined in this subpart), that is a distinct operating unit of any commercial or industrial facility (including field erected, modular, and custom built incineration units operating with starved or excess air), and any air curtain incinerator that is a distinct operating unit of any commercial or industrial facility that does not comply with the opacity limits under this

### subpart applicable to air curtain incinerators burning

commercial or industrial waste. While not all CISWI units will include all of the following components, a CISWI unit includes, but is not limited to, the commercial or industrial 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 commercial or industrial 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 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. A CISWI unit does not include any of the fifteen types of units described in §60.2555 of this subpart, nor does it include any combustion turbine or reciprocating internal combustion engine. Commercial or industrial waste means solid waste (as defined in this subpart) that is combusted at any commercial or industrial facility using controlled flame combustion in an enclosed, distinct operating unit: Whose design does not provide for energy recovery (as defined in this subpart); or operated without energy recovery (as defined in this subpart). Commercial or industrial waste also means solid waste (as defined in this subpart) combusted in an air curtain incinerator that is a distinct operating unit of any commercial or industrial facility.

Page 90: [4] Deleted Author



### (2) Burn greater than 30 percent municipal solid waste or refuse-derived fuel, as defined in subpart Ea, subpart Eb, subpart AAAA, and subpart BBBB of this part, and that have the capacity to burn less than 35 tons (32 megagrams) per day of municipal solid waste or refuse-derived fuel, if you meet the two requirements in paragraphs (c)(2)(i) and (ii) of this section.

(i) Notify the Administrator that the unit meets these criteria.

(ii) Keep records on a calendar quarter basis of the weight of municipal solid waste burned, and the weight of all other fuels and wastes burned in the unit.Page 92: [5] Deleted Author



### Chemical recovery units. 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. The seven types of units described in paragraphs (n)(1) through (7) of this section 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.

(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 burning only manufacturing byproduct streams/residues 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.

(o) Laboratory Analysis Units. Units that burn samples of materials for the purpose of chemical or physical analysis.

Page 92: [6] Deleted Author


### What if a chemical recovery unit is not listed in §60.2555(n)?

### (a) If a chemical recovery unit is not listed in

§60.2555(n), the owner or operator of the unit can petition the Administrator to add the unit to the list. The petition must contain the six items in paragraphs (a)(1) through (6) of this section.

(1) A description of the source of the materials being burned.

(2) A description of the composition of the materials being burned, highlighting the chemical constituents in these materials that are recovered.

(3) A description (including a process flow diagram) of the process in which the materials are burned, highlighting the type, design, and operation of the equipment used in this
process.

(4) A description (including a process flow diagram) of the chemical constituent recovery process, highlighting the type, design, and operation of the equipment used in this
process.

(5) A description of the commercial markets for the recovered chemical constituents and their use.

(6) The composition of the recovered chemical constituents and the composition of these chemical constituents as they are bought and sold in commercial markets.

(b) Until the Administrator approves your petition, the incineration unit is covered by this subpart.

(c) If a petition is approved, the Administrator wi ll amend §60.2555(n) to add the unit to the list of chemical recovery un its.
Page 147: [7] Deleted Author



### means any combustion unit that combusts commercial or industrial waste (as defined in this subpart), that is a distinct operating unit of any commercial or industrial facility (including field erected, modular, and custom built incineration units operating with starved or excess air), and any air curtain incinerator that is a distinct operating unit of any commercial or industrial facility that does not comply with the opacity limits under this subpart applicable to air curtain incinerators burning commercial or industrial waste. While not all CISWI units

### will include all of the following components, a CISWI unit

includes, but is not limited to, the commercial or industrial 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 commercial or industrial 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 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. A CISWI unit does not include any of the fifteen types of units described in §60.2555 of this subpart, nor does it include any combustion turbine or reciprocating internal combustion engine.

Commercial or industrial waste means solid waste (as defined in this subpart) that is combusted at any commercial or industrial facility using controlled flame combustion in an enclosed, distinct operating unit: Whose design does not provide for energy recovery (as defined in this subpart); or operated without energy recovery (as defined in this subpart). Commercial or industrial waste also means solid waste (as defined in this subpart) combusted in an air curtain incinerator that is a distinct operating unit of any commercial or industrial facility.