1

Subpart CCCC—Standards of Performance for Commercial and

Industrial Solid Waste Incineration Units for Which

Construction Is Commenced After November 30, 1999 or for

Which Modification or Reconstr u ction Is Commenced o n o r

After June 1, 2001

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 o n [TH E DATE 6 MONTHS AFTE R

PUBLICATION OF THE FINAL RULE IN THE FEDERAL REGISTER]

.

June 1, 2001. Some of the requirements in this subpart

apply to planning the CISWI unit and must be completed even

before construction is initiate d on the CISWI unit (i.e.

,

the preconstruction requirements in §§60.2045 and 60.2050).

Other requirements such a s th e emission limitations an d

operating limits apply afte r the CISWI unit begins

operation.

Applicability

§60.2010 Does this subpart apply to my incineration unit?

Yes, if your incineration unit meets all th e

requirements specified in para g raphs (a) through (c ) o f

this section.

(a) Your incineration uni t is a new incineration uni t

as defined in §60.2015.

(b) Your incineration unit is a CISWI unit as defined2

in §60.2265.

(c) Your incineration unit is not exempt under

§60.2020.

§60.2015 What is a new incineration unit?

(a) A new incineration unit is an incineration unit

that meets any either of the two criteria specified in

paragraph (a)(1) through or (a) (2) of this section.

(1) A CISWI unit that C c ommen c ed construction afte r

November 30, 1999 [THE DATE OF 60 DAYS AFTER PUBLICATION OF

THE FINAL RULE IN THE FEDERAL REGISTER].

(2) A CISWI unit that C c ommenced reconstruction or

modification on or after June 1, 2001 [THE DATE 6 MONTHS

AFTER PUBLICATION OF TH E FIN A L RULE IN TH E FEDERA L

REGISTER].

(b) This subpart does no t affect your CISW I

incineration unit if you make physical or operational

changes to your incineratio n uni t primarily to compl y wit h

the emission guidelines in subpart DDDD of this part

(Emission Guidelines and Compliance Times for Commercial

and Industrial Solid Waste Incineration Units). Such

changes do not qualify as reco n struction or modification

under this subpart.

§60.2020 What combustion units are exempt from this

subpart?

This subpart exempts the types o f units described i n

paragraphs (a), (c) through (i) and (nm ) of this section,

but some units are required to provide notifications.

Air curtain incinerators are ex e mpt from the requirements

in this subpart except for th e provisions in §§60.2242

,

60.2250, and 60.2260. fifteen types of units descr ibed i n3

paragraphs (a) through (o) of this section

.

(a) Pathological waste incineration units.

Incineration units burning 90 pe r cent or more by weigh t (o n

a calendar quarter basis and excluding the weight of

auxiliary fuel and combustion a i r) of pathological waste,

low-level radioactive waste, and/or chemotherapeutic waste

as defined in §60.2265 are not subject to this subpart if

you meet the two requirements specified in paragraphs

(a)(1) and (2) of this section.

(1) Notify th e Administrator that the unit mee ts

these criteria.

(2) Keep records on a calendar quarter basis of the

weight of pathological waste, low-level radioactive waste,

and/or chemotherapeutic waste bu r ned, and the weight of al l

other fuels and wastes burned in the unit.

(b) [Reserved]

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 i n pa r agraphs (b)(1) and (2 ) o f

this section.

(1) Notify the Administrator tha t the unit meets thes e

criteria.

(2) Keep records on a calendar quarter basis of th e

weight of agricultural waste bur n ed, and the weight o f al l

other fuels and wastes burned in the unit.

(c) Municipal waste combustio n units

. Incineration4

units that meet either o f the two criteria specified i n

paragraph (c)(1) or (2) of thi s section (1)A are regulated

under subject to subpart Ea of this part (Standards of

Performance for Municipal Wast e Combustors); subpart Eb o f

this part (Standards o f Perfor m ance for Large Municipa l

Waste Combustors );; for Which Construction is Commenced

After September 20, 1994) ; s u bpart Cb of thi s par t

(Emission Guidelines and Compliance Time for Large

Municipal Combustors );; tha t ar e Constructed on o r Befor e

September 20, 1994) ; subpar t s u bpart AAAA of thi s par t

(Standards of Performance for Ne w Stationary Sources: Smal l

Municipal Waste Combustion Units ) ; or subpart BBB B of th is

part (Emission Guidelines for Existing Stationary Sources:

Small Municipal Waste Combustion Units).

Municipal waste combustion units.

(2) Burn greater than 3 0 pe r cent municipal solid

waste or refuse

- derived fuel

, a s defined in subpart Ea

,

subpart Eb, subpart AAAA, an d s ubpart BBBB of this part

,

and that have the capacity to b urn less than 35 tons (32

megagrams) per day o f municipa l solid waste o r refuse

derived fuel, if you meet t he two requirements i n

paragraphs (c)(2)(i) and (ii) of this section.

(i) Notify the Administrator tha t the unit meets thes e

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.

(d) Medical waste incineration units. Incineration

units regulated under subpart E c of this part (Standards o f

Performance for Hospital/Medical/Infectious Waste

Incinerators for Which Construct i on is Commenced After Jun e

20, 1996) or subpart Ce of this part (Emission Guidelines5

and Compliance Times for Hospital/Medical/Infectious Waste

Incinerators).

(e) Small powe r production f a cilities. Units tha t

meet the three requirement s spe c ified 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 Power Act

(16 U.S.C. 796(17)(C)).

(2) The unit burns homogeneou s waste (not includin g

refuse-derived fuel) to produce electricity.

(3) You submit a request to no t ify the Administrato r

for a determination that the qualifying cogeneration

facility is combusting homogenous waste unit meets all o f

these criteria. as tha t term i s d efined in §60.2265

. Th e

request must include information sufficient to document

that the unit meets the criteria of the definition of a

small power production facility a nd that the waste materia l

the unit is proposed to burn is homogeneous.

(f) Cogeneration facilities. Units that meet th e

three requirements specified in paragraphs (f)(1) through

(3) of this section.

(1) The unit qualifies a s a cogeneration facility

under section 3(18)(B) of th e Fe d eral Power Act (16 U.S.C

.

796(18)(B)).

(2) The unit burns homogeneou s waste (not includin g

refuse-derived fuel) to produce electricity and steam o r

other forms of energy use d f o r industrial, commercial,

heating, or cooling purposes.

(3) You submit a request to no t ify the Administrato r6

for a determination that the qualifying cogeneration

facility is combusting homogeno u s waste as that term i s

defined in §60.2265 unit meets all of these criteria

. The

request must include information sufficient to document

that the unit meets the criteria of the definition of a

cogeneration facility and tha t t h e waste material th e uni t

is combusting is homogeneous.

(g) Hazardous waste combustion u nits

. Units for whic h

you are required t o get a permi t under section 300 5 of th e

Solid Waste Disposal Act. tha t meet either of th e tw o

criteria specified in paragrap h (g)(1) or (2) of thi s

section.

(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).

(h) Materials recovery units. Un i ts that combust wast e

for the primary purpose of r e covering metals, such a s

primary and secondary smelters.

(i) Air curtai n incinerat o rs. Air curtai n

incinerators that burn onl y the materials listed i n

paragraphs (i)(1) through (3 ) o f this section ar e onl y

required to meet the require m ents under “Air Curtai n

Incinerators” (§§60.2245 through 60.2260).

(1) 100 percent wood waste.

(2) 100 percent clean lumber.7

(3) 100 percent mixtur e of o n ly wood waste, clea n

lumber, and/or yard waste.

(j) [Reserved]

Cyclonic barrel burners. (See §60.2265)

(k) [Reserved]

Rack, part, and drum reclamation units. (See §60.2265)

(l) [Reserved]

Cement kilns. Kilns regulate d u nder subpart LLL o f

part 63 of this chapter (National Emission Standards for

Hazardous Air Pollutants from the Portland Cement

Manufacturing Industry).

(m) Sewage sludge incinerators treatment plants

.

Incineration units regulated un d er subpart O of this par t

(Standards of Performance for Sewage Treatment Plants).

(n) Sewage sludge incineration units

. Incineration

units combusting sewage sludg e f o r the purpose o f reducin g

the volume of the sewage slud g e by removing combustibl e

matter that are subject t o s u bpart LLLL of this par t

(Standards of Performance for Sewage Sludge Incineration

Units) or subpart MMMM of this part (Emission Guidelines

for Sewage Sludge Incineration Units). Chemical recovery

units. Combustion units burning materials to recover

chemical constituents or to produce chemical compounds

where there is an existing c o mmercial market for suc h

recovered chemical constituents or compounds. The seven

types of units described in par a graphs (n)(1) through (7 )

of this section are considered chemical recovery units.

(1) Units burning only pulping l iquors ( i.e., blac k

liquor) that are reclaim ed in a pulping liquor recover y8

process and reused in the pulping process.

(2) Units burning only spent s ulfuric acid used t o

produce virgin sulfuric acid.

(3) Units burning only woo d or c oal feedstock for th e

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 t o p r oduce purified carbon

monoxide that is used a s an int e rmediate in the productio n

of other chemical compounds.

(6) Units burning only hydrocar b on liquids or solids

to produce hydrogen, carbo n mo n oxide, synthesis gas, o r

other gases for use in other manufacturing processes.

(7) Units burning only photographic film to re cove r

silver.

(o) Laboratory Analysis Units. U n its that burn sample s

of materials for the purpose of chemical or physical

analysis.

§60.2025 Wha t if m y chemical r ecovery unit is no t liste d

in §60.2020(n)?

(a) If your chemical recovery unit is not listed in

§60.2020(n), you can petition th e Administrator to add you r

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.9

(2) A description of t h e composi t ion of the materials bein g

burned, highlighting the chemical constituents in these

materials that are recovered.

(3) A description (including a p r ocess flow diagram) of th e

process in which the materials a r e burned, highlighting th e

type, design

, and operation of the equipment used in this

process.

(4) A description (including a p r ocess flow diagram) of th e

chemical constituent recovery process, highlighting the

type, design, and operation of the equipment used in this

process.

(5) A description of the co m mercial markets for th e

recovered chemical constituents and their use.

(6) The composition o f the reco v ered chemical constituent s

and the composition o f these ch e mical constituents as th ey

are bought and sold in commercial markets.

(b) Until the Administrato r ap p roves your petition, th e

incineration unit is covered by this subpart.

(c) If a petition i s approved, t h e Administrator will amen d

§60.2020(n) to add the unit to the list of chemical

recovery units.

§60.2030 Who implements and enforces this subpart?

(a) This subpart can be implemented and enforced by

the U.S. Environmental Protec t ion Agency (EPA), or a

delegated authority such as your State, local, or tribal

agency. If the EPA Administrat o r has delegated authorit y

to your state, local, o r triba l agency, then that agenc y

(as well as EPA) has the authority to implement and enforce

this subpart. You shoul d contac t your EPA Regional Offic e10

to find out if this subpart is delegated to your state,

local, or tribal agency.

(b) In delegating implementation and enforcement

authority of this subpart to a state, local, or tribal

agency, the authorities containe d in paragraph (c ) of th is

section are retained by the EPA Administrator and are not

transferred to the state, local, or tribal agency.

(c) The authorities tha t wil l not be delegated to

state, local, or tribal agencies are specified i n

paragraphs (c)(1) through (4) and (c)(6) through (10) of

this section. State,

(1) Approval of alternativ e s to the emission

limitations in table 1 o f this s u bpart and operating limit s

established under §60.2110.

(2) Approval of major alternatives to test methods.

(3) Approval of major alternatives to monitoring.

(4) Approval of major alterna t ives to recordkeeping

and reporting.

(5) [Reserved] The requirem ents in §60.2025.

(6) The requirements in §60.2115.

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

(8) Approval of alternative o p acity emission limits

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

(9) Performance test and dat a r e duction waivers under

§60.2125(j), 60.8(b)(4) and (5).

(10) Determination of whether a q ualifying small powe r11

production facility or cogeneration facility under

§60.2020(e) or (f) is combustin g homogenous waste as tha t

term is defined in §60.2265.

§60.2035 How are these new source performance standards

structured?

These new source performance standards contain the

eleven major components listed in paragraphs (a) throug h

(k) of this section.

(a) Preconstruction siting analysis.

(b) Waste management plan.

(c) Operator training and qualification.

(d) Emission limitations and operating limits.

(e) Performance testing.

(f) Initial compliance requirements.

(g) Continuous compliance requirements.

(h) Monitoring.

(i) Recordkeeping and reporting.

(j) Definitions.

(k) Tables.

§60.2040 Do all eleven compo n ents of these ne w sourc e

performance standards apply at the same time?

No. You must meet th e preconstr u ction siting analysis12

and waste management pla n requi r ements before you commenc e

construction of the CISWI unit

. The operator training an d

qualification, emission limitations, operating limits,

performance testing and compliance, monitoring, and most

recordkeeping and reporting requ i rements are met afte r th e

CISWI unit begins operation.

Preconstruction Siting Analysis

§60.2045 Who must prepare a siting analysis?

(a) You must prepare a siting a n alysis if you plan t o

commence construction of a n CISWI unit incinerator afte r

December 1, 2000.

(b) You must prepare a siting analysis for CISWI

units that commenced construction after June 4, 2010, or

that commenced reconstruction or modification after [THE

DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE IN THE

FEDERAL REGISTER]. if you ar e req u ired to submit a n initia l

application for a construction p e rmit under 40 CFR par t 51

,

subpart I, or 40 CFR part 52, as applicable, for the

reconstruction or modification of your CISWI unit.

(c) You must complete an d submit the sitin g

requirements of this sectio n as required under §60.2190(c )

prior to commencing construction prepare a sitin g analysi s

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, f or the reconstruction o r

modification of your CISWI unit.

§60.2050 What is a siting analysis?

(a) The siting analysis must c onsider air pollutio n

control alternatives that minimize, on a site-specific

basis, to the maximum extent p r acticable, potential risks

to public health or the environment. In considering such

alternatives, the analysis may consider costs, energy13

impacts, nonair environmental im p acts, or any other factor s

related to the practicability of the alternatives.

(b) Analyses of you r CISWI un i t's impacts that ar e

prepared to comply wit h state

, local, or othe r Federa l

regulatory requirements may b e used to satisfy the

requirements of this section

, p rovided they include th e

consideration of air pollution control alternatives

specified in paragraph (a) of this section.

(c) You must complete an d submit the sitin g

requirements of this sectio n 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 tha t

identifies both the feasibilit y and the methods used t o

reduce or separate certain comp o nents of solid waste fro m

the waste stream in order to reduce or eliminate toxic

emissions from incinerated waste.

§60.2060 When must I submit my waste management plan?

You must submit a waste mana g ement plan prior t o

commencing construction.

§60.2065 What should I inclu d e in my wast e managemen t

plan?

A waste management pla n must in c lude consideration o f

the reduction or separation of waste-stream elements such

as paper, cardboard, plastics, g l ass, batteries, or metals ;

or the use of recyclabl e materia l s. The plan must identif y

any additional waste management measures and implement

those measures the source consid e rs practical and feasible

,14

considering the effectiveness of waste management measures

already in place, the costs o f additional measures, th e

emissions reductions expected to be achieved, and any othe r

environmental or energy impacts they might have.

Operator Training and Qualification

§60.2070 What are the operator training and qualification

requirements?

(a) No CISWI unit can be operated unless a fully

trained and qualified CISWI unit operator is accessible

,

either at the facility or can b e at the facility within 1

hour. The trained an d qualifi e d CISWI unit operator ma y

operate the CISWI unit directl y o r be the direct superviso r

of one or more other plant personnel who operate the unit.

If all qualified CISWI unit ope r ators are temporarily no t

accessible, you must follow the procedures in §60.2100.

(b) Operator training and qualification must be

obtained through a state-approve d program or b y completin g

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 element s des c ribed in paragraphs (c)(1 )

through (3) of this section.

(1) Training on the eleve n subjects listed i n

paragraphs (c)(1)(i) through (xi) of this section.

(i) Environmental concerns, including types of

emissions.

(ii) Basic combustion principles, including products

of combustion.

(iii) Operation of the specifi c type of incinerato r15

to be used by th e operator, incl u ding proper startup, wast e

charging, and shutdown procedures.

(iv) Combustion controls and monitoring.

(v) Operation o f air pollutio n control equipment an d

factors affecting performance (if applicable).

(vi) Inspection and maintenance of the incinerato r

and air pollution control devices.

(vii) Actions t o prevent an d c o rrect malfunctions or

to prevent conditions that may lead to malfunctions.

(viii) Bottom an d fly as h characteristics an d

handling procedures.

(ix) Applicable Federal, State, and local

regulations, including Occupational Safety and Health

Administration workplace standards.

(x) Pollution prevention.

(xi) Waste management practices.

(2) An examination designed an d administered by th e

instructor.

(3) Written materia l coverin g the training cours e

topics that may serve as reference material following

completion of the course.

§60.2075 When must the operator training course be

completed?

The operator training cours e mus t be completed b y th e

later of the three dates specified in paragraphs (a)

through (c) of this section.16

(a) Six months after your CISWI unit startup.

(b) December 3, 2001.

(c) The date before a n employee assume s

responsibility for operating t h e CISWI unit or assume s

responsibility for supervising t he operation of the CISWI

unit.

§60.2080 How do I obtain my operator qualification?

(a) You mus t obtain opera t or qualification b y

completing a training course that satisfies the criteri a

under §60.2070(b).

(b) Qualification is valid from the date on which the

training course is complete d an d the operator successfull y

passes the examination required under §60.2070(c)(2).

§60.2085 How do I maintain my operator qualification?

To maintain qualification, you m u st complete an annua l

review or refresher course cover i ng, at a minimum, th e fiv e

topics described in paragraph s (a) through (e) o f thi s

section.

(a) Update of regulations.

(b) Incinerator operation, including startup and

shutdown procedures, waste charging, and ash handling.

(c) Inspection and maintenance.

(d) Prevention and correctio n of malfunctions o r

conditions that may lead to malfunction. Responses to

malfunctions or conditions that may lead to malfunction.

(e) Discussion of operating p r oblems encountered by17

attendees.

§60.2090 How do I renew my lapsed operator qualification?

You must renew a lapsed operato r qualification by o ne

of the two methods specified in paragraphs (a) and (b) of

this section.

(a) For a lapse of less tha n 3 years, you mus t

complete a standard annual refresher course described i n

§60.2085.

(b) For a lapse o f 3 year s or more, you must repe at

the initial qualification requirements in §60.2080(a).

§60.2095 What site-specific documentation is required?

(a) Documentation must be avai l able at the facilit y

and readily accessible for all CISWI unit operators that

addresses the ten topic s descr i bed in paragraphs (a)(1 )

through (10) of this section

. You must maintain thi s

information and the trainin g re c ords required by paragrap h

(c) of this section in a manne r that they can be readily

accessed and are suitable for inspection upon request.

(1) Summary of the applicable standards under this

subpart.

(2) Procedures fo r receiving, h andling, and chargin g

waste.

(3) Incinerator startup, shutdown, and malfunction

procedures.

(4) Procedures fo r maintaining proper combustion ai r

supply levels.

(5) Procedures for operatin g the incinerator an d18

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 o f the waste s burned during th e

performance test.

(b) You must establis h a prog r am for reviewing th e

information listed in paragraph (a) of this section with

each incinerator operator.

(1) The initial review of the information listed in

paragraph (a) of this sectio n m ust be conducted within 6

months after the effective date of this subpart or prior to

an employee's assumption of responsibilities for operation

of the CISWI unit, whichever date is later.

(2) Subsequent annual review s of the informatio n

listed in paragraph (a) of this section must be conducted

not later than 12 months following the previous review.

(c) You mus t also maintai n the information specifie d

in paragraphs (c)(1) through (3) of this section.

(1) Records showing th e names o f CISWI unit operator s

who have completed review of th e information in §60.2095(a)

as required by §60.2095(b), i n cluding the date of th e

initial review and all subsequent annual reviews.19

(2) Records showing th e names o f the CISWI operator s

who have completed the operator t raining requirements unde r

§60.2070, met the criteria for qualification under

§60.2080, and maintained or renewed their qualification

under §60.2085 or §60.2090. Records must includ e

documentation of training, the dates of the initial an d

refresher training, and the dates of their qualificatio n

and all subsequent renewals of such qualifications.

(3) For each qualified opera t or, the phone and/o r

pager number at which the y can b e reached during operatin g

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 fac i lity and not able to b e a t

the facility within 1 hour), yo u must meet one of the tw o

criteria specified in paragraphs (a) and (b) of this

section, depending on the length of time that a qualified

operator is not accessible.

(a) When all qualified operato r s are not accessibl e

for more than 8 hours, but les s than 2 weeks

, the CISW I

unit may be operated b y other pl a nt personnel familiar wit h

the operation of the CISWI unit who have completed a review

of the information specified in § 60.2095(a) within the pas t

12 months. However, you must record the period when all

qualified operators were not accessible and include thi s

deviation in the annual report as specified under §60.2210.

(b) When all qualified operato r s are not accessibl e

for 2 weeks o r more, yo u must ta k e the two action s that a re

described in paragraphs (b)(1) and (2) of this section.

(1) Notify the Administrator of this deviation i n20

writing within 10 days. I n the notice, state what cause d

this deviation, what you are doing to ensure that a

qualified operator is accessibl e

, and when you anticipate

that a qualified operator will be accessible.

(2) Submit a statu s report to t h e Administrator ever y

4 weeks outlining what you are doing to ensure that a

qualified operator is accessible, stating when you

anticipate that a qualified oper a tor will be accessible an d

requesting approval from the Administrator to continue

operation of the CISWI unit. You must submit the first

status report 4 weeks afte r you n otify the Administrator o f

the deviation under paragraph (b)(1) of this section. If

the Administrator notifies yo u that your reques t t o

continue operation of the CISWI unit is disapproved, the

CISWI unit may continue operati o n for 90 days, the n mus t

cease operation. Operation of the unit may resume if you

meet the two requirement s in pa r agraphs (b)(2)(i) and (i i)

of this section.

(i) A qualified operator is accessible as required

under §60.2070(a).

(ii) You notify the Administrator that a qualified

operator is accessible and that you are resuming operation.

Emission Limitations and Operating Limits

§60.2105 What emission limita t ions must I mee t and b y

when?

You must meet the emission lim i tations 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.

(a) You must meet the emission limitations for each

CISWI unit, including bypass stack or vent, specified in

table 1 of this subpar t or ta b les 5 through 89 o f thi s21

subpart by the applicable date i n §60.2140

. You must b e i n

compliance with the emission limitations of this subpar t

that apply to you at all times.

(b) An incinerator unit that c ommenced construction

after November 30, 1999, but n o l ater than June 4, 2010, o r

that commenced reconstruction o r modification on or after

June 1, 2001 but no later than [INSERT THE DATE 6 MONTHS

AFTER PUBLICATION OF TH E FIN A L RULE IN TH E FEDERA L

REGISTER] must meet the more st r ingent emission limit fo r

the respective pollutant in table 1 of this subpart or

table 6 of subpart DDDD.

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

(a) If you use a wet scrubber ( s) to comply with th e

emission limitations, you must establish operating limits

for up to four operatin g paramet e rs (as specified in tabl e

2 of this subpart) as described in paragraphs (a)(1)

through (4) of thi s section dur i ng the initial performan ce

test.

(1) Maximum charge rate

, calcul a ted using one of th e

two different procedures in para g raph (a)(1)(i) or (ii), a s

appropriate.

(i) For continuous and interm i ttent units, maximum

charge rate is 110 percen t o f the average charge rat e

measured during the most recent performance test

demonstrating compliance with all applicable emission

limitations.

(ii) For batch units, maximum charge rate is 110

percent of the daily charge rate measured during the most

recent performance test demonstrating compliance with all

applicable emission limitations.

(2) Minimum pressur e drop acro s s the wet particula te22

matter scrubber, which is calcu l ated as the lowest 1-hou r

90 percent of the average pressure drop across the wet

scrubber measured during the mo s t recent performance test

demonstrating compliance with the particulate matter

emission limitations; or mini m um amperage to the we t

scrubber, which is calculated as the lowest 1-hour 9 0

p ercent of the average amper a ge to the wet scrubbe r

measured during the most recent performance test

demonstrating compliance with the particulate matter

emission limitations.

(3) Minimum scrubber liquor li q uid flow rate, whic h

is calculated as the lowes t 1 -hour 90 percent of th e

average liquor liquid flow rate at the inlet to the wet

acid gas or particulate matter s c rubber measured during th e

most recent performance test demonstrating compliance with

all applicable emission limitations.

(4) Minimum scrubber liquor pH

, which is calculate d

as the lowest 1-hour 90 percen t o f the average liquor pH a t

the inlet to the wet acid gas scrubber measured during the

most recent performance test demonstrating compliance with

the HCl emission limitation.

(b) You must meet the operating limits established

during the initial performanc e test 60 days afte r you r

CISWI unit reaches the charge rate at which it will

operate, but no later tha n 18 0 days after its initia l

startup.

(c) If yo u use a fabri c filt e r to comply wit h the

emission limitations, you must o perate each fabric filter

system such that the bag leak detection system alarm does

not sound more than 5 percent of the operating time during

a 6-month period. In calcula t ing this operating tim e

percentage, if inspection of the fabric filter demonstrate s23

that no corrective action i s r e quired, no alarm time i s

counted. If corrective action is required, each alarm shal l

be counted as a minimum of 1 hour. If you take longer than

1 hour to initiate correctiv e ac t ion, the alarm time shal l

be counted as th e actual amoun t of time take n by you t o

initiate corrective action.

(d) If you use an electrostati c p recipitator to comply

with the emission limitations

, you must measur e th e

(secondary) voltage and amperage of the electrostatic

precipitator collection plates during the particulate

matter performance test. Calculate the average electric

power value (secondary voltag e x secondary current =

secondary electric power) fo r ea c h test run. Th e operatin g

limit for the electrostatic pre c ipitator is calculated as

the lowest 1-hour average second a ry electric power measure d

during the most recent performance test demonstrating

compliance with the particulate matter emission

limitations.

(e) If you use activated carbo n sorbent injection t o

comply with the emissio n limitat i ons, you must measur e th e

sorbent flow rate during the performance testing. The

operating limit for th e car b on sorbent injection i s

calculated as the lowest 1-hour average sorbent flow rat e

measured during the most recent performance test

demonstrating compliance with the mercury emission

limitations.

(f) If you us e selective nonc a talytic reduction t o

comply with the emissio n limitat i ons, you must measur e th e

charge rate, the secondary chamber temperature (if

applicable to your CISWI unit), and the reagent flow rate

during the nitrogen oxides performance testing. The

operating limits for the selective noncatalytic reduction

are calculated as the lowest 1-hour average charge rate,24

secondary chamber temperature, and reagent flow rate

measured during the most recent performance test

demonstrating compliance with the nitrogen oxides emission

limitations.

(g) If you do no t use a wet s c rubber, electrostati c

precipitator, or fabric filte r t o comply with th e emissio n

limitations, and if you do not determine compliance with

your particulate matter emission limitation with a

particulate matter CEMS, yo u mus t maintain opacity t o les s

than or equal to 10 percent opacity (1-hour block average).

§60.2115 What if I do not use a wet scrubber

, fabric

filter, activated carbon injection, selective noncatalytic

reduction, or an electrostati c p recipitator to comply wit h

the emission limitations?

If you use an ai r pollution con t rol device other tha n

a wet scrubber, activated carbon injection, selective

noncatalytic reduction, fabric filter, or an electrostatic

precipitator or limit emissions in some other manner,

including material balances, to comply with the emissio n

limitations under §60.2105, you must petition the EPA

Administrator for specific operating limits to be

established during the initial performance test and

continuously monitored thereafter. You must not conduc t

the initial performance test un t il after the petition ha s

been approved by the Administr a tor. Your petition mus t

include the five items liste d in paragraphs (a) through (e )

of this section.

(a) Identification o f the sp e cific parameters yo u

propose to use as additional operating limits.

(b) A discussion of the relationship between these25

parameters and emissions of regulated pollutants,

identifying how emissions of regulated pollutants change

with changes in these parameters

, and how limits on these

parameters will serve to limit emissions of regulated

pollutants.

(c) A discussion of how you will establish the upper

and/or lower values fo r the s e parameters which wil l

establish the operating limits on these parameters.

(d) A discussion identifyin g th e methods you will us e

to measure and the instruments you will use to monitor

these parameters, as wel l as t he relative accuracy a nd

precision of these methods and instruments.

(e) A discussion identifyin g the frequency an d

methods for recalibrating th e in s truments you will us e fo r

monitoring these parameters.

§ 60.2120 Affirmative Defense for Exceedance of an Emissio n

Limit During Malfunction

. What happens during periods of

startup, shutdown, and malfunction?

(a) The emission limitations and operating limits

apply at all times except du r ing CISWI unit startups

,

shutdowns, or malfunctions

.

(b) Each malfunction must last no longer than 3 hours.

In response to an actio n to enf o rce the standards se t

forth in paragraph §60.2105

, yo u may assert a n affirmativ e

defense to a claim for civil penalties for exceedances of

such standards that are caused b y malfunction, as define d

at 40 CFR 60.2. Appropriate p enalties may be assessed

,

however, if you fai l to mee t you r burden of provin g all o f

the requirements in the affirmative defense. Th e

affirmative defense shall not b e available for claims fo r26

injunctive relief.

(a) To establish the affirmative defense in any actio n

to enforce such a limit

, yo u must timely meet th e

notification requirements in par a graph (b) of this section

,

and must prove by a preponderance of evidence that:

(1) The excess emissions:

(i) Were caused by a sudd e n, infrequent, and

unavoidable failure of air pollu t ion control and monitorin g

equipment, process equipment, or a process to operate i n a

normal or usual manner, and

(ii) Could not hav e been prev e nted through carefu l

planning, proper design or bette r operation and maintenanc e

practices; and

(iii) Did not stem from any activity or event that

could have been foreseen and avoided, or planned for; and

(iv) Were not part of a recurr i ng pattern indicativ e

of inadequate design, operation, or maintenance; and

(2) Repairs were made as expeditiously as possible

when the applicable emission limitations were being

exceeded. Off-shift and overtime labor were used, to the

extent practicable to make these repairs; and

(3) The frequency, amount and duration of the excess

emissions (including any bypas s ) were minimized to th e

maximum extent practicable during periods of such

emissions; and

(4) If the excess emissions resulted from a bypass of

control equipment or a proce s s, then the bypass wa s

unavoidable to prevent loss o f life, severe persona l

injury, or severe property damage; and27

(5) All possible steps we r e taken to minimize th e

impact of the excess emission s o n ambient air quality, th e

environment and human health; and

(6) All emissions and/or parameter monitoring and

systems, as well as contro l syst e ms, were kept in operatio n

if at all possible consistent with safety and good air

pollution control practices; and

(7) All of the action s i n response to the exces s

emissions were documented by properly signed,

contemporaneous operating logs; and

(8) At all times, th e facilit y was operated in a

manner consistent with good practices for minimizing

emissions; and

(9) A written root cause analys i s has been prepared

,

the purpose of whic h is t o determine, correct, a nd

eliminate the primary causes o f the malfunction and th e

excess emissions resulting from the malfunction event a t

issue. The analysis shall a lso specify, using bes t

monitoring methods and engineeri n g judgment, the amoun t o f

excess emissions that were the result of the malfunction.

(b) Notification. The owne r or operator of th e

facility experiencing an exceedance of its emission

limit(s) during a malfunction shall notify the

Administrator by telephone or facsimile (FAX) transmission

as soon as possible, but no later than two business days

after the initial occurrenc e o f the malfunction, i f i t

wishes to avail itself of an affirmative defense to civil

penalties for that malfunction

. The owne r or operat or

seeking to assert a n affirmativ e defense shall als o submi t

a written report to the Administrator within 45 days of the

initial occurrence of the exce e dance of the standard i n

§60.2105 to demonstrate, with all necessary supporting28

documentation, that it has met t he requirements set fort h

in paragraph (a) of this section. The owner or operator

may seek an extension of this deadline for up to 30

additional days by submittin g a written request t o th e

Administrator before the expira t ion of the 45 day period

.

Until a request for an extension has been approved by the

Administrator, the owner o r op e rator is subject t o th e

requirement to submit such rep o rt within 45 days o f th e

initial occurrence of the exceedance.

Performance Testing

§60.2125 How do I conduct the initial and annual

performance test?

(a) All performance tests must consist of a minimum

of three test runs conducted under conditions

representative of normal operations.

(b) You must documen t that th e waste burned durin g

the performance test i s represen t ative of the wast e burne d

under normal operating conditio n s by maintaining a log o f

the quantity of wast e b u rned (as required i n

§60.2175(b)(1)) and the types of waste burned during the

performance test.

(c) All performance test s must b e conducted using th e

minimum run duration specified in table 1 of this subpart

or tables 5 through 8 of this subpart

.

(d) Method 1 of appendix A of this part must be used

to select the samplin g locatio n and number o f travers e

points.

(e) Method 3 A or 3 B of appendi x A of thi s part mu st29

be used for gas composition anal y sis, including measuremen t

of oxygen concentration. Method 3A or 3B of appendix A of

this part must be used simultaneously with each method.

(f) All pollutant concentration s

, except for opacity

,

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 oxygen;

C

meas = pollutant concentration measured on a dry basis;

(20.9–7)

= 20.9 percent oxygen

− 7 percent oxygen (define d

oxygen correction basis);

20.9 = oxygen concentration in air, percent; and

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

(g) You must determine dioxins/furans toxic

equivalency by following the procedures in paragraphs

(g)(1) through (3) of this section.

(1) Measure the concentration of each dioxin/furan

tetra- through octa

- chlorinated

- congener isomer emitte d

using EPA Method 23 at 40 CFR part 60, appendix A-7

.

(2) For each dioxin/furan (tetra-through

octachlorinated octa-chlorinated ) congener isomer measured in

accordance with paragraph (g)(1 ) of this section

, multipl y

the congener isomer concentration by its corresponding toxic

equivalency factor specified in table 3 of this subpart.

(3) Sum the products calculated in accordance with30

paragraph (g)(2) of this section to obtain the total

concentration of dioxins/furans emitted in terms of toxic

equivalency.

(h) Method 2 2 at 4 0 CFR par t 60

, appendix A-7 o f thi s

part must be used t o determine c o mpliance with the fugitiv e

ash emission limit in table 1 o f this subpart or tables 5

through 9 8 of this subpart.

(i) If you have an applica b le opacity operatin g

limit, you must determine compli a nce with the opacity limi t

using Method 9 at 40 CFR part 6 0,of appendix A-4 of this

part, based on three 1-hou r bl o cks consisting of ten 6-

minute average opacity values, u nless you are required t o

install a continuous opacity monitoring system, consistent

with §60.2145 and §60.2165.

§60.2130 How are the performance test data used?

You use results of performance tests to demonstrate

compliance with the emission lim i tations in table 1 o f thi s

subpart or tables 5 through 8 of this subpart

.

Initial Compliance Requirements

§60.2135 How do I demonstrate i nitial compliance with th e

emission limitations and establish the operating limits?

You must conduct a n initial performance test, as

required under §60. 8 2125 and §60.2105 to determine

compliance with the emission lim i tations in table 1 o f thi s

subpart or tables 5 throug h 89 of this subpart, t o

establish compliance with any opacity operating limit i n

§60.2110, and t o establish o p erating limits using t he

procedures in §60.2110 o r § 60.2115. The initia l

performance test must be conduc t ed using the test method s31

listed in table 1 of thi s subpar t or tables 5 through 89 o f

this subpart and the procedures in §60.2125. The use of

the bypass stack during a perfor m ance test shall invalidat e

the performance test. You mu s t conduct a performanc e

evaluation of each continuous m o nitoring system within 60

days of installation of the monitoring system.

§60.2140 By what date mus t I conduct the initial

performance test?

(a) The initial performanc e te s t must be conducte d

within 60 days after you r CISW I unit reaches the charg e

rate at which it will operate, b ut no later than 180 day s

after its initial startup.

(b) If you commence or recommen c e combusting a soli d

waste at an existing combustion unit at any commercial or

industrial facility, and you conducted a test consisten t

with the provisions of this subpart while combusting the

solid waste within the 6 months preceding th e

reintroduction of that solid waste in the combustio n

chamber, you do no t need t o rete s t until 6 month s from th e

date you reintroduce that solid waste.

(c) If you commence combusting or recommence

combusting a solid waste a t an e xisting combustion unit a t

any commercial or industria l f a cility and you hav e no t

conducted a performance test con s istent with the provision s

of this subpart whil e combusti n g the given soli d wast e

within the 6 months preceding the reintroduction of that

solid waste in the combustion chamber, you must conduct a

performance test within 6 0 days commencing or recommencin g

solid waste combustion.

§60.2141 By what date must I conduct the initial air

pollution control device inspection?

(a) The initial air pollution control device

inspection must be conducted within 60 days afte r32

installation of the control devi c e and the associated CISW I

unit reaches the charge rate at which it will operate, but

no later than 180 days after the device’s initial startup.

(b) Within 10 operating day s following an air

pollution control device inspection, all necessary repairs

must be completed unles s the o wner or operator obtai ns

written approval from th e state agency establishing a da te

whereby all necessary repairs of the designated facilit y

must be completed.

Continuous Compliance Requirements

§60.2145 How do I demonstrate continuous compliance with

the emission limitations and the operating limits?

(a) Compliance with standards.

(1) The emission standards and o p erating requirement s

set forth in this subpart apply at all times.

(2) If you cease combusting solid waste, you may opt

to remain subject to the provisions of this subpart.

Consistent with the definitio n of CISWI unit, you ar e

subject to the requirements of this subpart at least 6

months following the last date o f solid waste combustion

. Solid waste combustion is ceased when solid waste is not in

the combustion chamber (i.e., the solid waste feed to the

combustor has been cut off for a period of time not less

than the solid waste residence time).

(3) If you cease combustin g solid w a ste, you must be

in compliance with any newly applicable standards on the

effective date of th e waste-to-f u el switch. Th e effectiv e

date of the waste-to-fuel switch is a date selected by you,

that must be at least 6 months from the date that yo u

ceased combusting solid waste, consistent with

§60.2145(a)(2). Your source mus t remain in compliance wit h

this subpart until th e effectiv e date of th e waste-to-fue l

switch.

(4) If you own or operate an existing commercial or

industrial combustion unit that combusted a fuel or nonwaste material, and you commenc e or recommence combustion33

of solid waste, you are subject to the provisions of this

subpart as of the firs t day yo u introduce or reintroduc e

solid waste to the combustion chamber, and this date

constitutes the effective date o f the fuel-to-waste switch

.

You must complete all initial co m pliance demonstrations fo r

any section 112 standards tha t are applicable to you r

facility before you commence or recommence combustion o f

solid waste. You must provide 30 days prior notice of the

effective date of th e wast e -to-fuel switch. Th e

notification must identify:

(i) The name of the owner or operator of the CISWI

unit, the location of the sou r ce, the emissions unit(s )

that will cease burning solid waste, and the date of the

notice;

(ii) The currently applicable subcategory under this

subpart, and any 40 CF R part 6 3 subpart and subcategor y

that will be applicable after you cease combusting solid

waste;

(iii) The fuel(s), non-waste material(s) and solid

waste(s) the CISWI unit is cu r rently combusting and ha s

combusted over the past 6 months, and the fuel(s) or nonwaste materials the unit will commence combusting;

(iv) The date on whic h you b e came subject to th e

currently applicable emission limits;

(v) The date upo n which yo u w ill cease combustin g

solid waste, and the dat e (if d ifferent) that you inten d

for any new requirements to become applicable (i.e., the

effective date of the waste-to-fuel switch), consistent

with (2) and (3)) above.

(5) All air pollutio n control e q uipment necessary fo r

compliance with any newly applic a ble emissions limits whic h

apply as a result o f the ces s ation or commencement o r

recommencement of combusting sol i d waste must b e installe d

and operational as of the effective date of the waste-tofuel, or fuel-to-waste switch.

(6) All monitoring systems necessary for compliance

with any newly applicable monitoring requirements which

apply as a result o f the ces s ation or commencement o r

recommencement of combusting sol i d waste must b e installe d34

and operational as of the effective date of the waste-tofuel, or fuel-to-waste switch. All calibration and drif t

checks must be performed as of the effective date of the

waste-to-fuel, or fuel-to-waste switch. Relative accuracy

tests must be performed a s of th e performance test deadlin e

for PM CEMS. Relative accuracy testing for other CEMS need

not be repeated if that testing was previously performed

consistent with Clean Air Ac t section 112 monitorin g

requirements or monitoring requirements under this subpart.

( a b ) You must conduc t an annua l performance test fo r

the pollutants listed in table 1 of this subpart or tables

5 through 8 of this subpart partic ulate matter, hydrogen

chloride, fugitive ash, and opac i ty for each CISWI uni t a s

required under §60.8 §60.2125

. to determine complianc e

with the emission limitations

. T he annual performance tes t

must be conducted using the test methods listed in table 1

of this subpart or tables 5 thr o ugh 8 of this subpart an d

the procedures in §60.2125. An n ual performance tests ar e

not required if yo u use CE M S or continuous opaci ty

monitoring systems to determine compliance.

( b c ) You must continuousl y m onitor the operating

parameters specified in §60.2110 or established under

§60.2115 and as specified in § 60.2170

. Use 3-hour bloc k

average values to determine comp l iance (except for baghous e

leak detection system alarms ) u n less a different averagin g

period is established under §60

. 2115. Operation above the

established maximum

, or below t h e established minimum

, or

outside the allowable range of operating limits specified

in paragraph (a) of this section constitutes a deviation

from the your established operating limits established

under this subpart, except during performance tests

conducted to determine complia n ce with the emissio n an d

operating limits or to establ i sh new operating limits

. Three

- hour rolling average val u es are used t o determin e

compliance (except for baghouse leak detection system

alarms) unless a differen t aver a ging period is establishe d

under §60.2115. Operating li m its do not apply durin g

performance tests are confirmed or reestablished during

performance tests

.

( c d ) You mus t only bur n only t h e same types o f waste

and fuels used t o establish sub c ategory applicability (fo r

energy recovery units) and op e rating limits during th e35

performance test.

(e) For energy recovery units, i n cinerators, and smal l

remote units, you must perform a n annual visual emission s

test for ash handling.

(f) For energy recovery units

, you must conduct a n

annual performance test for opacity (except where

particulate matter CEMS or continuous opacity monitoring

systems are used are used ) an d the pollutants listed i n

table 6 of this subpart.

(g) You may elect to demonstrate continuous complianc e

with the carbon monoxid e emiss i on limit using a carbo n

monoxide CEMS according to the following requirements:

(1) You must measur e emissions a ccording to §60.13 to

calculate 1-hour arithmetic averages, corrected to 7

percent oxygen. CEMS data durin g startup and shutdown, a s

defined in this subpart, ar e n o t corrected to 7 percen t

oxygen, and are measured a t stac k oxygen content. You mus t

demonstrate initial compliance with the carbon monoxide

emissions limit using a 30-da y r o lling average of these 1-

hour arithmetic average emission concentrations, including

CEMS data during startup an d s h utdown as defined in thi s

subpart, calculated using Equati o n 19-19 in sectio n 12.4. 1

of EPA Reference Metho d 19 a t 4 0 CFR part 60

, appendix A– 7

of this part.

(2) Operate the carbo n monoxid e CEMS in accordanc e

with the requirements of performance specification 4A o f

appendix B of this part and quality assurance procedure 1

of appendix F of this part.

(h) For waste-burning kilns, demonstrate continuous

compliance with the particulate matter emissions limit

using a particulate matter CEMS a ccording to the procedure s

in §60.2165(n). Energy recover y units with design hea t

input capacities greater than o r equal to 250 MMBtu/hr ma y

elect to demonstrate continuous compliance with the

particulate matter emissions limit using a particulate36

matter CEMS according to th e procedures in §60.2165(n)

instead of the particulate matter continuous parameter

monitoring system (CPMS) specified in §60.2145.

(i) For energy recovery units w i th design heat inpu t

capacities greater than or equa l to 10 MMBtu/hour and les s

than 250 MMBtu/hr, you must ins t all, operate, certify an d

maintain a continuous opacity monitoring system (COMS)

according to the procedures in §60.2165.

(j) For waste-burning kilns, you must conduct an

annual performance test for cadmium, lead, dioxins/furans

and hydrogen chloride as listed in table 7 of this subpart.

You must determine complianc e w i th hydrogen chloride usin g

a hydrogen chloride CEMS if you do not use an acid gas wet

scrubber. You must determine compliance with nitrogen

oxides, sulfur dioxide, carbon monoxide, and particulate

matter using CEMS. You must det e rmine compliance with th e

mercury emissions limit using a mercury CEMS according t o

the following requirements:

(1) Operate a CEMS system in accordance with

performance specification 12A of 40 CFR part 60, appendi x B

or a sorbent trap based integrated monitor in accordance

with performance specification 12B of 40 CFR part 60

,37

appendix B. The duration of the performance test must be a

calendar month. For each calenda r month in which th e wasteburning kiln operates, hourly mercury concentration data,

and stack gas volumetric flow rate data must be obtained.

(2) Owners or operator s using a mercury CEMS mu st

install, operate, calibrate, and maintain an instrument fo r

continuously measuring and recording the mercury mass

emissions rate to the atmosphere according to th e

requirements of performance spec i fications 6 and 12 A of 40

CFR part 60, appendix B

, and qu a lity assurance procedure 6

of 40 CFR part 60, appendix F.

(3) The owner or operato r of a w a ste-burning kiln mus t

demonstrate initial compliance b y operating a mercur y CEM S

while the raw mill o f the i n-line kiln/raw mill i s

operating under normal condition s and while the ra w mill o f

the in-line kiln/raw mill is not operating.

(k) If you use an air pollution control device to meet

the emission limitations i n thi s subpart, you mus t conduc t

an initial and annual inspect i on of the air pollutio n

control device. The inspectio n m ust include, at a minimum

, the following:

(1) Inspect air pollution contro l device(s) for prope r

operation.

(2) Develop a site-specific monitoring plan according

to the requirements in paragraph (l) of this section. This

requirement also applies to yo u if you petition th e EP A

Administrator for alternative monitoring parameters under

§60.13(i).38

(l) For each continuou s monitor i ng system required i n

this section, you must develo p and submit to th e EP A

Administrator for approval a site-specific monitoring plan

according to the requirements of this paragraph (l) that

addresses paragraphs (l)(1)(i) through (vi) of this

section.

(1) You must submit this site-sp e cific monitoring pla n

at least 60 days before you r ini t ial performance evaluation

of your continuous monitoring system.

(i) Installation of the continuous monitoring system

sampling probe or other interfac e at a measurement locatio n

relative to each affected process unit such that the

measurement is representative o f control of th e exhaus t

emissions (e.g., on or downst r eam of the last contro l

device).

(ii) Performance and equipment specifications for the

sample interface, the pollutant concentration or parametric

signal analyzer and the data collection and reduction

systems.

(iii) Performance evaluation procedures and acceptance

criteria (e.g., 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 conduc t a performa n ce evaluation of ea ch

continuous monitoring system i n accordance with your sitespecific monitoring plan.

(3) You must operate and maintain the continuous

monitoring system in continuou s operation according to th e

site-specific monitoring plan.

(m) If you have an operating limit that requires the

use of a flow monitorin g sy s tem, you must meet th e39

requirements in paragraphs (l) and (m)(1) through (4) of

this section.

(1) Install the flow sensor and other necessar y

equipment in a position tha t provides a representative

flow.

(2) Use a flow sensor with a m e asurement sensitivity

of no greater than 2 percent of the expected process flow

rate.

(3) Minimize the effect s of swi r ling flow or abnorm al

velocity distributions due to upstream and downstream

disturbances.

(4) Conduct a flow monitoring system performance

evaluation in accordance with y o ur monitoring plan at th e

time of each performance test but no less frequently than

annually.

(n) If you have an operating limit that requires the

use of a pressure monitoring system, you must meet the

requirements in paragraphs (l) and (n)(1) through (6) of

this section.

(1) Install the pressur e sensor( s ) in a positio n tha t

provides a representative measurement of the pressure

(e.g., PM scrubber pressure drop).

(2) Minimize or eliminate pulsating pressure,

vibration, and internal and external corrosion.

(3) Use a pressure senso r with a minimum tolerance o f

1.27 centimeters of water o r a minimum tolerance of 1

percent of the pressur e monitor i ng system operating range

, whichever is less.

(4) Perform checks at leas t once each process

operating day to ensure pressure measurements are not

obstructed (e.g., check for pressure tap pluggage daily).

(5) Conduct a performance evalu a tion of the pressure

monitoring system in accordance with your monitoring plan

at the time of each performance test but no less frequently

than annually.

(6) If at any time the measured pressure exceeds the40

manufacturer's specified maximum operating pressure range,

conduct a performance evaluation of the pressure monitorin g

system in accordance wit h your m onitoring plan and confi rm

that the pressure monitoring sy s tem continues to meet th e

performance requirements in your monitoring plan.

Alternatively, install and verify the operation of a new

pressure sensor.

(o) If you have an operating limit that requires a pH

monitoring system, you must m eet the requirements i n

paragraphs (l) and (o)(1) through (4) of this section.

(1) Install the pH senso r in a p osition that provides

a representative measurement of scrubber effluent pH.

(2) Ensure the sampl e is properly mixed an d

representative of the fluid to be measured.

(3) Conduct a performanc e e v aluation of the p H

monitoring system in accordance with your monitoring plan

at least once each process operating day.

(4) Conduct a performance evalua t ion (including a twopoint calibration with on e of the two buffer solutio ns

having a pH withi n 1 o f the p H o f the operating limit ) o f

the pH monitoring system in acco r dance with your monitorin g

plan at the time of each performance test but no less

frequently than quarterly.

(p) If you have a n operating l imit that requires a

secondary electric power monitoring system for an

electrostatic precipitator, you must meet the requirements

in paragraphs (l) and (p)(1) through (2) of this section.

(1) Install sensors to measur e (secondary) voltage

and current to the precipitator collection plates.

(2) Conduct a performance evalu a tion of the electric

power monitoring system i n acco r dance with your monitorin g

plan at the time of each performance test but no less

frequently than annually.

(q) If you have an operating limit that requires the

use of a monitoring system t o measure sorbent injection

rate (e.g., weigh belt, weigh hopper, or hopper flow

measurement device), you must meet the requirements i n

paragraphs (l) and (q)(1) and (2) of this section.41

(1) Install the syste m in a pos i tion(s) that provide s

a representative measurement of t he total sorbent injectio n

rate.

(2) Conduct a performance evaluation of the sorben t

injection rate monitoring system in accordance with you r

monitoring plan at the time of each performance test but no

less frequently than annually.

(r) If you elect to use a fabric filter bag leak

detection system to comply with the requirements of this

subpart, you must install, calibrate, maintain, and

continuously operate a ba g l eak detection system a s

specified in paragraphs(l) and ( r)(1) through (5) of thi s

section.

(1) Install a bag leak detection sensor(s) in a

position(s) that will b e represe n tative of the relativ e o r

absolute particulate matter loadings for each exhaust

stack, roof vent, o r compartme n t (e.g., for a positiv e

pressure fabric filter) of the fabric filter.

(2) Use a bag leak detection system certified by the

manufacturer to be capabl e of d e tecting particulate matte r

emissions at concentrations o f 10 milligrams per actua l

cubic meter or less.

(3) Conduct a performance evalu a tion of the bag lea k

detection system in accordance with your monitoring pla n

and consistent with th e guidanc e provided in EPA–454/R–98–

015 (incorporated by reference, see §60.17).

(4) Use a bag lea k detection s y stem equipped with a

device to continuously record the output signal from the

sensor.

(5) Use a bag lea k detection s y stem equipped with a

system that will sound an alarm when an increase in

relative particulate matter emi s sions over a preset level

is detected. The alarm must be located where it is

observed readily by plant operating personnel.

(s) For facilities usin g a CEMS to demonstrat e

compliance with the sulfur dioxide emission limit,

compliance with the sulfur dioxide emission limit may be

demonstrated by using the CEM S specified in §60.2165 t o42

measure sulfur dioxide an d cal c ulating a 30-day rollin g

average emission concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 at 40 CFR part

60, Appendix A-7 of this part. The sulfur dioxide CEMS

must be operated according to p erformance specification 2

in appendix B of this part and must follow the procedures

and methods specified in this paragraph (s). For sources

that have actual inlet emission s less than 100 part s pe r

million dry volume, th e relati v e accuracy criterion fo r

inlet sulfur dioxide CEMS should be no greater than 20

percent of the mean value of the reference method test data

in terms of th e units o f the em i ssion standard, or 5 part s

per million dry volume abso l ute value of the mea n

difference between the reference method and the CEMS,

whichever is greater.

(1) During each relative accurac y test run of th e CEMS

required by performance specification 2 in appendix B of

this part, collect sulfur diox i de and oxygen (or carbo n

dioxide) data concurrently (or within a 30- to 60-minute

period) with both the continuous emissions monitors and th e

test methods specified in paragraphs (s)(1)(i) and

(s)(1)(ii) of this section.

(i) For sulfur dioxide, EP A Refe r ence Method 6 or 6C

,

or as an alternative ANSI/ASME P T C 19.10–1981 (incorporate d

by reference, see §60.17) must be used.

(ii) For oxygen (o r carbon di o xide), EPA Referenc e

Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10–

1981 (incorporated by reference, see §60.17), must be used.

(2) The span valu e of the CEM S at the inle t to th e

sulfur dioxide control device m u st be 125 percent o f th e

maximum estimated hourly potential sulfur dioxide emissions

of the unit subject to this rule. The span value of the

CEMS at the outlet o f the sul f ur dioxide control devic e

must be 50 percen t of th e maximum estimated hourl y

potential sulfur dioxide emissi o ns of the unit subject t o

this rule.

(3) Conduct accuracy determinations quarterly and

calibration drift tests dail y i n accordance with procedur e

1 in appendix F of this part.

(t) For facilities usin g a CEMS to demonstrat e

continuous compliance with the nitrogen oxides emission43

limit, compliance with the nitr o gen oxides emission limit

may be demonstrated by usin g the CEMS specified in §60.216 5

to measure nitrogen oxides and c a lculating a 30-day rollin g

average emission concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 at 40 CFR part

60, appendix A-7 of this part. The nitrogen oxides CEMS

must be operated according to p erformance specification 2

in appendix B of this part and must follow the procedures

and methods specified in paragr a phs (t)(1) through (t)(5)

of this section.

(1) During each relative accurac y test run of th e CEMS

required by performance specification 2 of appendix B of

this part, collect nitrogen oxides and oxygen (or carbon

dioxide) data concurrently (or within a 30- to 60-minute

period) with both the CEMS and the test methods specified

in paragraphs (t)(1)(i) and (t)(1)(ii) of this section.

(i) For nitrogen oxides, EP A Ref e rence Method 7 or 7 E

at 40 CFR part 60, appendix A-4 must be used.

(ii) For oxygen (o r carbon di o xide), EPA Referenc e

Method 3A or 3B at 40 CFR part 6 0, appendix A-3, or as an

alternative ANSI/ASME PTC 19–10.1981 (incorporated by

reference, see §60.17), as applicable, must be used.

(2) The span value of th e continuous emission

monitoring system must be 125 percent of the maximum

estimated hourly potential nitro g en oxide emissions o f th e

unit.

(3) Conduct accuracy determinations quarterly and

calibration drift tests dail y i n accordance with procedur e

1 in appendix F of this part.

(4) The owner or operato r of a n affected facility may

request that compliance with th e nitrogen oxides emission

limit be determined using carbon dioxide measurements

corrected to an equivalent of 7 percent oxygen. If carbon

dioxide is selected for use i n diluent corrections, th e

relationship between oxygen an d carbon dioxide levels mus t

be established during the initial performance test

according to the procedures a nd methods specified i n

paragraphs (t)(4)(i) through (t)(4)(iv) of this section.

This relationship may be re-established during performance

compliance tests.44

(i) The fuel factor equation in Method 3B must be used

to determine the relationshi p b etween oxygen and carbo n

dioxide at a sampling location. Method 3A or 3B, or as an

alternative ANSI/ASME PTC 19.10–1981 (incorporated by

reference, see §60.17), a s app l icable, must be use d t o

determine the oxygen concentrati o n at the sam e location as

the carbon dioxide monitor.

(ii) Samples must be taken for at least 30 minutes in

each hour.

(iii) Each sample must represent a 1-hour average.

(iv) A minimum of three runs must be performed.

(u) For facilities usin g a CEMS to demonstrat e

continuous compliance with any of the emission limits of

this subpart, you must complete the following:

(1) Demonstrate compliance with the appropriate

emission limit(s) using a 30-day rolling average,

calculated using Equation 19-19 in section 12.4.1 of EPA

Reference Method 19 at 40 CF R pa r t 60, appendix A-7 of thi s

part.

(2) Operate all CEMS in accordan c e with the applicabl e

procedures under appendices B and F of this part.

(v) Use of the bypass stack at any time is an

emissions standards deviation for particulate matter, HCl,

Pb, Cd, Hg, NOx, SO2, and dioxin/furans.

(w) For energy recovery unit s wi t h a design heat inpu t

capacity of 100 MMBt u per hou r o r greater that d o not us e a

carbon monoxide CEMS, you mu s t install, operate, an d

maintain a oxygen analyzer system as defined in §60.2265

according to the procedures in paragraphs (w)(1) through

(4) of this section.

(1) The oxygen analyzer system must be installed by

the initial performance test date specified in §60.2675.

(2) You must operate the oxygen trim system with the

oxygen level set at th e minimu m percent oxygen by volum e45

that is established as the o p erating limit for oxyge n

according to paragraph (w)(3) of this section.

(3) You must maintain the oxygen level such that it is

not below the lowest hourly av e rage oxygen concentration

measured during the most recent CO performance test.

(4) You must calculate and re c ord a 30-day rollin g

average oxygen concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 of Appendix A-7

of this part.

(x) For energy recovery units w i th design heat inpu t

capacities greater than or equ a l to 250 MMBtu/hour, yo u

must install, certify, maintai n

, and operate a PM CP MS

monitoring emissions discharged to the atmosphere and

record the output of th e system as specified in paragraph s

(x)(1) through (5) of this section. For other energy

recovery units, you may elect to use PM CPMS operated in

accordance with this section in lieu of using other CMS for

monitoring PM compliance (e.g.

, bag leak detectors

, ES P

secondary power, PM scrubber pressure)

(1) Install, certify, operate, and maintain your P M

CPMS according to the procedur e s in your approved sitespecific monitoring plan developed in accordance with

§60.2145(l) and (x)(1)(i) through (iii) of this section.

(i) The operating principle o f the PM CPMS must b e

based on in-stack or extract i ve light scatter, ligh t

scintillation, or beta attenuation of the exhaust gas or

representative exhaust gas sample. The reportable

measurement output from the P M CPMS may be expressed a s

milliamps, stack concentration, or other raw data signal.

(ii) The PM CPMS must have a cycle time (i.e., period

required to complete sampling, measurement, and reporting

for each measurement) no longer than 60 minutes.46

(iii) The PM CPMS mus t be cap a ble of detecting an d

responding to particulate matter concentrations of no

greater than 0.5 mg/actual cubic meter.

(3) Collect PM CPMS hourl y avera g e output data for al l

energy recovery unit operating h ours. Express the PM CPM S

output as millamps, PM concent r ation, or other raw dat a

signal value.

(4) Calculate the arithmetic 30- d ay rolling average o f

all of the hourly average PM CPMS output collected during

all energy recovery unit ope r ating hours data (e.g.

,

milliamps, PM concentration, raw data signal).

§60.2150 By what date must I conduct the annua l

performance test?

You must conduct annual perform a nce tests between 11

and 13 months of the previou s for particulate matter

, hydrogen chloride, and opacity w ithin 12 months following

the initial performance test. Conduct subsequent annual

performance tests within 12 mon t hs following the previous

one.

§60.2151 By what date must I conduct the annual air

pollution control device inspection?

On an annual basis (no more than 12 months following

the previous annual air pollution control device

inspection), you must complete the air pollution contro l

device inspection as described in §60.2141.

§60.2155 May I conduct performance testing less often?

(a) You must conduct annual performance tests

according to the schedule speci f ied in §60.2150, with th e47

following exceptions:

(1) You may conduct a repeat performance test at any

time to establish new value s f o r the operating limits t o

apply from that point forward, as specified in §60.2160.

The Administrator may reques t a repeat performance test at

any time.

(2) You must repeat the perfo r mance test within 6 0

days of a process change, as defined in §60.2265.

(3) If the initia l or an y subse q uent performance tes t

for any pollutant in table 1 or tables 5 through 8 of this

subpart, as applicable, demonstrates that the emission

level for the pollutant i s no greater than the emissio n

level specified in paragrap h ( a )(3)(i) or (a)(3)(ii) o f

this section, as applicable, an d you are not require d t o

conduct a performance test fo r t h e pollutant in response t o

a request by the Administrato r i n paragraph (a)(1) of thi s

section or a process chang e i n paragraph (a)(2) of thi s

section, you may elect to ski p conducting a performanc e

test for the pollutant fo r th e next 2 years. You mus t

conduct a performance test fo r the pollutant during th e

third year and no more than 37 months following the

previous performance test for t h e pollutant. For cadmiu m

and lead, both cadmium and lead must be emitted at emission

levels no greater tha n their r espective emission levels

specified in paragraph (a)(3)(i) of this section for yo u t o

qualify for less frequent testing under this paragraph.

(i) For particulate matter, hydrogen chloride,

mercury, nitrogen oxides, sulfur dioxide, cadmium, lead an d

dioxins/furans, the emission le v el equal to 75 percent o f

the applicable emission limit in table 1 or table s 5

through 8 of this subpart, as applicable, to this subpart.

(ii) For fugitive emissions, visible emissions (of

combustion ash from the as h conv e ying system) for 2 percen t48

of the time during eac h of th e three 1-hour observatio n

periods.

(4) If you are conducting less frequent testing for a

pollutant as provided in paragr a ph (a)(3) of this sectio n

and a subsequent performanc e test for th e pollutan t

indicates that your CISWI unit does not meet the emission

level specified in paragrap h ( a )(3)(i) or (a)(3)(ii) o f

this section, as applicable, you must conduct annua l

performance tests for the po l lutant according to th e

schedule specified in paragraph (a) of this section unti l

you qualify for less frequen t te s ting for the pollutant a s

specified in paragraph (a)(3) of this section.

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

you comply with the emissio n lim i tation. In this case, yo u

do not have to conduc t a p e rformance test for tha t

pollutant for the next 2 ye a rs. You must conduct a

performance test duri ng the 3rd year and no more than 36

months following the previous performance test.

(b) [Reserved] If your CISWI unit continues to meet th e

emission limitation for particulate matter, hydrogen

chloride, or opacity, you may ch o ose to conduct performanc e

test s for these pollutants ever y third year, but each tes t

must be within 36 months of the previous performance test.

(c) If a performance test shows a deviation from an

emission limitation for particulate matter, hydrogen

chloride, or opacity, you must condu ct annual performance

tests for that pollutant unti l a l l performance tests over a

3

- year period show compliance.

§60.2160 May I conduct a repeat performance test to49

establish new operating limits?

(a) Yes. You may conduct a repeat performance test at

any time to establish ne w value s for the operating limits

.

The Administrator may reques t a repeat performance test at

any time.

(b) You must repeat the performance test if your feed

stream is different than the feed streams used during any

performance test used to demonstrate compliance.

Monitoring

§60.2165 What monitoring equipment must I install and

what parameters must I monitor?

(a) If you are using a wet sc r ubber to comply with

the emission limitation under § 6 0.2105, you must install,

calibrate (to manufacturers' specifications), maintain, and

operate devices (or establish m e thods) for monitoring the

value of the operatin g para m eters used to determin e

compliance with the operating limits listed in table 2 of

this subpart. These devices (or methods) must measure an d

record the values for these o p erating parameters at th e

frequencies indicated in table 2 of this subpart a t al l

times except as specified in §60.2170(a).

(b) If yo u use a fabri c filt e r to comply wit h the

requirements of this subpart

, y o u must install, calibrate

,

maintain, and continuously ope r ate a bag lea k detectio n

system as specified in paragra p hs (b)(1) through (8) o f

this section.

(1) You must install and operate a bag leak detection

system for each exhaust stack of the fabric filter.

(2) Each bag lea k detection sys t em must be installed

,50

operated, calibrated, and mainta i ned in a manner consisten t

with the manufacturer's written specifications and

recommendations.

(3) The bag leak detection system must be certified

by the manufacturer t o be capab l e of detecting particula te

matter emissions at concentrat i ons of 10 milligram s pe r

actual cubic meter or less.

(4) The bag lea k detection syst e m sensor must provid e

output of relative or absolute particulate matter loadings.

(5) The bag lea k detection sy s tem must be equippe d

with a device to continuousl y re c ord the output signal fro m

the sensor.

(6) The bag lea k detection sy s tem must be equippe d

with an alarm system tha t will a l ert sound automatically a n

operator when an increase in r e lative particulate matter

emissions over a preset level is detected. The alarm must

be located where it i s observ e d easily heard by plan t

operating personnel.

(7) For positive pressure fabric filter systems, a

bag leak detection system mu s t be installed in eac h

baghouse compartment or cell. For negative pressure o r

induced air fabric filters, the bag leak detector must be

installed downstream of the fabric filter.

(8) Where multiple detector s are required, th e

system's instrumentation and a l arm may be shared amon g

detectors.

(c) If you are using something other than a wet

scrubber

, activated carbon

, selective non-catalyti c

reduction, or an electrostati c p recipitator to comply wit h

the emission limitations unde r § 60.2105, you must install

,51

calibrate (to the manufacturers’ specifications), maintain,

and operate the equipment neces s ary to monitor compliance

with the site-specific operating limits established using

the procedures in §60.2115.

(d) If you use activated carbon injection to comply

with the emission limitations i n this subpart, you mus t

measure the minimum mercur y so r bent flow rate onc e pe r

hour.

(e) If you use selective noncatalytic reduction to

comply with the emission limitat i ons, you must complete th e

following:

(1) Following the date o n which the initia l

performance test is complete d or is require d to be

completed under §60.2125, whichever date comes first,

ensure that the affected facility does not operate above

the maximum charge rate, or b e low the minimum secondar y

chamber temperature (if applica b le to your CISWI unit) o r

the minimum reagent flo w rate measured as 3-hour blo ck

averages at all times.

(2) Operation o f the affecte d facility above t he

maximum charge rate, below the minimum secondary chamber

temperature and below th e m i nimum reagent flow rat e

simultaneously constitute a violation of the nitrogen

oxides emissions limit.

(f) If you use an electros t atic precipitator t o

comply with the emission limits of this subpart, you must

monitor the secondary power to the electrostatic52

precipitator collection plates and maintain the 3-hour

block averages at or above th e o p erating limits established

during the mercury or particulate matter performance test.

(g) For waste-burning kilns not equipped with a wet

scrubber, in place of hydrogen chloride testing with EPA

Method 321 at 40 CFR part 63, appendix A, an owner o r

operator must install, calibrat e

, maintain, and operate a

CEMS for monitoring hydrogen chloride emissions discharged

to the atmosphere an d record th e output of the system

. T o

demonstrate continuous compliance with the hydrogen

chloride emissions limit for uni t s other than waste-burnin g

kilns not equipped with a wet scrubber, a facility may

substitute use of a hydrogen ch l oride CEMS for conductin g

the hydrogen chloride annual performance test, monitoring

the minimum hydrogen chlorid e sorbent flow rate, an d

monitoring the minimum scrubber liquor pH.

(h) To demonstrat e continuou s compliance with th e

particulate matter emissions limit, a facility may

substitute use of a particulate matter CEMS for conducti ng

the PM annual performance test a nd monitoring the minimu m

pressure drop across the wet scrubber, if applicable.

(i) To demonstrat e continuou s compliance with th e

dioxin/furan emissions limit, a f acility may substitute us e

of a continuous automated sampling system for th e

dioxin/furan annual performance t est. You mus t record t he

output of the system an d analy z e the sample according t o

EPA Method 23 a t 40 CF R part 60

, appendix A-7 of thi s part

.

This option to use a continuou s automated sampling syste m

takes effect on th e date a fina l performance specificatio n53

applicable 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 at 40

CFR part 60, appendix A-7 must install, calibrate,

maintain, and operate a continuous automated sampling

system and must comply with th e requirements specified i n

§60.58b(p) and (q).

(j) To demonstrat e continuou s compliance with th e

mercury emissions limit, a facil i ty may substitute use o f a

continuous automated sampling sy s tem for the mercury annua l

performance test. You must record the output of the system

and analyze the sample a t set i n tervals using any suitabl e

determinative technique that can meet performance

specification 12B. The owne r o r operator who elects t o

continuously sample mercury emissions instead of sampling

and testing using EP A Reference M ethod 29 or 30 B at 4 0 CF R

part 60, appendix A-8 of t h is part, ASTM D6784-0 2

(Reapproved 2008) (incorporated by reference, see §60.17),

or an approved alternativ e met h od for measuring mercur y

emissions, must install, calibra t e, maintain, and operate a

continuous automated sampling s y stem and must comply with

performance specification 12A and quality assurance

procedure 5, as well as the requirements specified i n

§60.58b(p) and (q).

(k) To demonstrat e continuou s compliance with th e

nitrogen oxides emissions limit

, a facility ma y substitut e

use of a CEMS fo r the nitrogen oxides annual performanc e

test to demonstrate complianc e with the nitrogen oxide s

emissions limits.54

(1) Install, calibrate

, maintai n

, and operate a CEMS

for measuring nitrogen oxides e m issions discharged to the

atmosphere and record the out p ut of the system. Th e

requirements under performance specification 2 of appendix

B of this part, the quality assurance procedure one of

appendix F of this part and the procedures under §60.13

must be followed for installation, evaluation, and

operation of the CEMS.

(2) Following the date that t h e initial performanc e

test for nitrogen oxides is completed or is required to be

completed under §60.2125, compliance with the emission

limit for nitrogen oxides requir e d under §60.52b(d) must b e

determined based on the 30-da y rolling average of th e

hourly emission concentrations u s ing CEMS outlet data. Th e

1-hour arithmetic averages must be expressed in parts pe r

million by volume (dry basis) and used to calculate the 30-

day rolling average concentratio n s. The 1-hou r arithmeti c

averages must be calculate d usin g the data point s require d

under §60.13(e)(2).

(l) To demonstrat e continuou s compliance with th e

sulfur dioxide emissions limit, a facility may substitute

use of a continuous automate d sampling system for th e

sulfur dioxide annual performance test to demonstrate

compliance with the sulfur dioxide emissions limits.

(1) Install, calibrate

, maintai n

, and operate a CEMS

for measuring sulfur dioxide emissions discharged to th e

atmosphere and record the out p ut of the system. Th e

requirements under performance specification 2 of appendix55

B of this part, the quality assurance requirements o f

procedure one of appendix F o f this part and procedure s

under §60.13 must be followed fo r installation, evaluation

,

and operation of the CEMS.

(2) Following the date that t h e initial performanc e

test for sulfur dioxide is completed or is required to be

completed under §60.2125, compliance with the sulfur

dioxide emission limit may be determined based on the 30-

day rolling average of the h ourly arithmetic averag e

emission concentrations using CE M S outlet data. The 1-hou r

arithmetic averages must b e expr e ssed in parts pe r millio n

corrected to 7 percent oxyge n (dry basis) and used t o

calculate the 30-day rolling average emission

concentrations and daily geometric average emission percent

reductions. The 1-hou r ari t hmetic averages must b e

calculated using the data points required under

§60.13(e)(2).

(m) For energy recover y units o v er 10 MMBtu/hr desig n

heat input that do not use a wet scrubber, fabric filter

with bag leak detection system, o r particulate matter CEMS

,

you must install, operate, c ertify, and maintain a

continuous opacity monitoring system according to the

procedures in paragraphs (m)(1) t hrough (5) of this sectio n

by the compliance date specif i ed in §60.2105. Energ y

recovery units that use a CEMS to demonstrate initial and

continuing compliance according to the procedures in

§60.2165(n) are not required to install a continuou s

opacity monitoring system and must perform the annual

performance tests for the opacity consistent with

§60.2145(f).56

(1) Install, operate, and mai n tain each continuous

opacity monitoring system according to performance

specification 1 of 40 CFR part 60, appendix B.

(2) Conduct a performanc e evaluation of each

continuous opacity monitoring system according to the

requirements in §60.13 and according to PS-1 of 40 CFR part

60, appendix B.

(3) As specifie d in §60.13(e ) (1), each continuou s

opacity monitoring system must complete a minimum of one

cycle of sampling and analyzin g for each successive 10-

second period and one cycle of data recording for each

successive 6-minute period.

(4) Reduce the continuous opa c ity monitoring system

data as specified in §60.13(h)(1).

(5) Determine and record all the 6-minute averages

(and 1-hour block averages as applicable) collected.

(n) For energ y recovery unit s w ith design capacitie s

greater than 250 MMBtu/hr, in p l ace of particulate matte r

testing with EPA Metho d 5 a t 40 CFR part 60, appendi x A-3

,

an owner or operato r may instal l

, calibrate, maintain, a nd

operate a CEMS fo r monitoring p a rticulate matter emission s

discharged to the atmosphere and record the output of the

system. For waste-burning kil n s, a CEMS for monitorin g

particulate matter emissions i s required. The owner o r

operator of an affecte d facilit y who continuously monitor s

particulate matter emissions instead of conducting57

performance testing using EPA Method 5 at 40 CFR part 60,

appendix A-3 must install, calib r ate, maintain, and operat e

a CEMS and must comply with the requirements specified in

paragraphs (n)(1) through (n)(14) of this section.

(1) Notify th e Administrator 1 month before startin g

use of the system.

(2) Notify th e Administrator 1 month before stoppin g

use of the system.

(3) The monitor must b e inst a lled, evaluated, and

operated in accordance with the r equirements of performanc e

specification 11 of appendix B of this part and qualit y

assurance requirements of procedure two of appendix F of

this part and §60.13

. Us e M e thod 5 or Metho d 5I o f

Appendix A of this part for the PM CEMS correlation

testing.

(4) The initial performanc e evaluation must b e

completed no later than 180 days after the date of initial

startup of the affected faci l ity, as specified unde r

§60.2125 or within 18 0 day s of notification t o th e

Administrator of use of the cont i nuous monitoring system i f

the owner or operator was previo u sly determining complianc e

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 betwee n oxygen and carbon dioxid e58

levels for the affected faci l ity must be establishe d

according to the procedures a nd methods specified i n

§60.2145(s)(5)(i) through (s)(5)(iv).

(6) The owner o r operator o f an affected facility

must conduct an initial performance test for particulat e

matter emissions as required under §60.2125. Complianc e

with the particulate matter emission limit must be

determined by using the CEM S spe c ified in paragraph (n) o f

this section to measur e particu l ate matter and calculatin g

a 30-day rolling average emission concentration using

Equation 19-19 in section 12.4. 1 of EPA Reference Method 1 9

at 40 CFR part 60, appendix A-7.

(7) Compliance with the parti c ulate matter emission

limit must be determined based on the 30-day rolling

average calculated using Equati o n 19-19 in section 12.4.1

of EPA Reference Metho d 19 a t 4 0 CFR part 60, appendix A- 7

from the 1-hour arithmetic average CEMS outlet data.

(8) At a minimum, vali d contin u ous monitoring syste m

hourly averages must b e ob t ained as specified i n

§60.2170(e).

(9) The 1-hou r arithmetic av e rages required unde r

paragraph (n)(7) of this sect i on must be expressed i n

milligrams per dry standar d cu b ic meter corrected t o 7

percent oxygen (dry basis) an d must be used to calculat e

the 30-day rolling average emiss i on concentrations. The 1-

hour arithmetic averages mus t b e calculated using th e dat a

points required under §60.13(e)(2).59

(10) All valid CEMS data must be used in calculating

average emission concentrations even if the minimum CEMS

data requirements of paragraph ( n)(8) of this section ar e

not met.

(11) The CEMS must be o p erated according t o

performance specification 11 in appendix B of this part.

(12) During each relativ e acc u racy test run of th e

CEMS required by performance spe c ification 11 in appendix B

of this part, particulat e matt e r and oxygen (o r carbo n

dioxide) data must be collected concurrently (or within a

30- to 60-minute period) by bot h the continuous emissions

monitors and the following test methods.

(i) For particulate matter, EPA Reference Method 5

must be used.

(ii) For oxygen (or carbon dioxide), EPA Reference

Method 3A or 3B, as applicable, must be used.

(13) Quarterly accuracy determinations and daily

calibration drift tests mus t b e performed in accordanc e

with procedure 2 in appendix F of this part.

(14) When particulate matter e m issions data are no t

obtained because of CEMS breakdowns, repairs, calibration

checks, and zero an d span adjus t ments, emissions data mu st

be obtained by using other moni t oring systems as approve d

by the Administrator or EPA Reference Method 19 at 40 CFR

part 60, appendix A-7 to pro v ide, as necessary, vali d

emissions data for a minimum o f 8 5 percent of the hours pe r60

day, 90 percent of the hours per calendar quarter, and 95

percent of the hours pe r calen d ar year that the affecte d

facility is operated and combusting waste.

(o) To demonstrat e continuou s compliance with th e

carbon monoxide emissions limit

, you must use a continuou s

automated sampling system.

(1) Install, calibrate

, maintai n

, and operate a CEMS

for measuring carbon monoxide e m issions discharged to the

atmosphere and record the out p ut of the system. Th e

requirements under performance specification 4B of appendix

B of this part, th e quality assurance procedure 1 o f

appendix F of this par t and t h e procedures under §60.1 3

must be followed for installation, evaluation, and

operation of the CEMS.

(2) Following the date that t h e initial performanc e

test for carbon monoxide is completed or is required to be

completed under §60.2140, compliance with the carbon

monoxide emission limit may b e d e termined based on the 30-

day rolling average of the h ourly arithmetic averag e

emission concentrations, including CEMS data during startup

and shutdown as defined i n this subpart, using CEMS outle t

data. Except for CEMS dat a durin g startup and shutdown, a s

defined in this subpart

, the 1 -hour arithmetic average s

must be expressed in part s pe r million corrected to 7

percent oxygen (dry basis) an d u s ed to calculate the 30-da y

rolling average emission concentrations. CEMS data during

startup and shutdown, as defined in this subpart, are not

corrected to 7 percent oxygen

, and are measured at stac k

oxygen content. The 1-hour ar i thmetic averages must b e

calculated using the data points required under61

§60.13(e)(2).

(p) The owner/operator of an affected source with a

bypass stack shall install, calibrate (to manufacturers’

specifications), maintain, and o perate a device or method

for measuring the use of the bypass stack including date,

time and duration.

(q) For energy recovery unit s wi t h a design heat inpu t

capacity of 100 MMBt u per hou r o r greater that d o not us e a

carbon monoxide CEMS, you mu s t install, operate, an d

maintain a oxygen analyzer system as defined in §60.2265

according to the procedures in paragraphs (q)(1) through

(4) of this section.

(1) The oxygen analyzer system must be installed by

the initial performance test date specified in §60.2675.

(2) You must operate the oxygen trim system with the

oxygen level set at th e minimu m percent oxygen by volum e

that is established as the o p erating limit for oxyge n

according to paragraph (q)(3) of this section.

(3) You must maintain the oxygen level such that it is

not below the lowest hourly av e rage oxygen concentration

measured during the most recent CO performance test.

(4) You must calculate and re c ord a 30-day rollin g

average oxygen concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 of Appendix A-7

of this part.

(r) For energy recovery units w i th design heat inpu t

capacities greater than or equ a l to 250 MMBtu/hour, yo u

must install, certify, maintai n

, and operate a PM CP MS

monitoring emissions discharged to the atmosphere and

record the output of th e system as specified in paragraph s62

(r)(1) through (5) of this sect i on. If you elect to use a

particulate matter CEMS as specified in paragraph (n) of

this section, you are no t requ i red to use a P M CPMS t o

monitor particulate matter emissions. For other energy

recovery units, you may elect to use PM CPMS operated in

accordance with this section in lieu of using other CMS for

monitoring PM compliance (e.g.

, bag leak detectors

, ES P

secondary power, PM scrubber pressure)

(1) Install, certify, operate, and maintain your P M

CPMS according to the procedur e s in your approved sitespecific monitoring plan developed in accordance with

§60.2145(l) and (r)(1)(i) through (iii) of this section.

(i) The operating principle o f the PM CPMS must b e

based on in-stack or extract i ve light scatter, ligh t

scintillation, or beta attenuation of the exhaust gas or

representative exhaust gas sample. The reportable

measurement output from the P M CPMS may be expressed a s

milliamps, stack concentration, or other raw data signal.

(ii) The PM CPMS must have a cycle time (i.e., period

required to complete sampling, measurement, and reporting

for each measurement) no longer than 60 minutes.

(iii) The PM CPMS mus t be cap a ble of detecting an d

responding to particulate matter concentrations of no

greater than 0.5 mg/actual cubic meter.

(3) Collect PM CPMS hourl y avera g e output data for al l

energy recovery unit operating h ours. Express the PM CPM S

output as millamps, PM concent r ation, or other raw dat a

signal value.

(4) Calculate the arithmetic 30- d ay rolling average o f

all of the hourly average PM CPMS output collected during

all energy recovery unit ope r ating hours data (e.g.

,

milliamps, PM concentration, raw data signal).63

§60.2170 Is there a minimum a m ount of monitoring data I

must obtain?

For each continuous monitoring system required or

optionally allowed under §60.2165, you must collect dat a

according to this section:

(a) You must operate the monitor i ng system and collec t

data at all required intervals at all times compliance is

required except for periods of monitoring system

malfunctions or out-of-control periods, repairs associated

with monitoring system malfunctions or out-of-control

periods (as specified i n 60.22 1 0(o) of this part)

, an d

required monitoring system quality assurance or quality

control activities (including, as applicable, calibration

checks and required zero and span adjustments). A

monitoring system malfunction is any sudden, infrequent,

not reasonably preventable failu r e of the monitoring syste m

to provide valid data

. Monitorin g system failures tha t ar e

caused in part by poor maintenance or careless operation

are not malfunctions. You are re q uired to effect monitorin g

system repairs in response to monitoring system

malfunctions or out-of-control periods and to return th e

monitoring system to operation as expeditiously as

practicable.

(b) You may not use data recorded during monitoring

system malfunctions or out-of-control periods, repairs

associated with monitoring system malfunctions or out-ofcontrol periods, or required monitoring system quality

assurance or control activitie s in calculations use d t o64

report emissions or operating le v els. You must use al l th e

data collected during all other periods in assessing the

operation of the control devi c e and associated contro l

system.

(c) Except for periods of monitoring system

malfunctions or out-of-control periods, repairs associated

with monitoring system malfunctions or out-of-control

periods, and required monitoring system quality assurance

or quality control activities including, as applicable,

calibration checks and require d zero and span adjustments

,

failure to collect required data is a deviation of the

monitoring requirements.

(a) Except for monitor malfunctions, associated

repairs, and required qualit y a s surance or quality contro l

activities (including, as applicable, calibration checks

and required zero and span adjustments of the monitoring

system), you must conduct all monitoring at all times the

CISWI unit is operating.

(b) Do not use data rec o rded during monito r

malfunctions, associated repairs, and required quality

assurance or quality contro l a c tivities for meeting th e

requirements of this subpart, i n cluding data av erages and

calculations. You must use all the data collected during

all ` other periods in assessing compliance with the

operating limits.

Recordkeeping and Reporting

§60.2175 What records must I keep?

You must maintain the fourteen items (as applicable)

as specified in paragraphs (a)

, (b), and (e) through ( n u )

of this section for a period of at least 5 years:65

(a) Calendar date of each record.

(b) Records of the data de s cribed in paragraph s

(b)(1) through (6) of this section:

(1) The CISWI uni t charge date s

, times, weights, an d

hourly charge rates.

(2) Liquor flow rate to the wet scrubber inlet every

15 minutes of operation, as applicable.

(3) Pressure dro p across th e wet scrubber syst em

every 15 minutes of operatio n or amperage to th e we t

scrubber every 15 minutes of operation, as applicable.

(4) Liquor pH as introduced to the wet scrubber every

15 minutes of operation, as applicable.

(5) For affected CISWI unit s th a t establish operating

limits for controls other t h an wet scrubbers under

§60.2110(d) through (f) or §60.2 1 15, you must maintain dat a

collected for all operating parameters used to determin e

compliance with the operating limits.

(6) If a fabric filter i s us e d to comply wit h the

emission limitations, you must r ecord the date, time, an d

duration of each alarm and the time corrective action was

initiated and completed, and a brief description of th e

cause of the alarm an d the co r rective action taken. Yo u

must also record the percen t of operating time during eac h

6-month period that th e ala r m sounds, calculated a s

specified in §60.2110(c).

(c) [Reserved]

(d) [Reserved]

(c) Identification of calendar dates and times for66

which monitoring systems used t o monitor operating limits

were inoperative, inactive, malfunctioning, or out of

c ontrol (except for downtim e ass o ciated with zero an d spa n

and other routine calibration checks). Identify the

operating parameters not measured, the duration, reasons

for not obtaining the data

, and a description of correctiv e

actions taken.

(d) Identific ation of calend a r dates, times, an d

durations of malfunctions, an d a description o f th e

malfunction and the corrective action taken.

(e) Identification of calendar dates and times for

which data show a deviatio n fr o m the operating limits i n

table 2 of this subpart or a deviation from other operating

limits established under §60.2110(d) through (f) or

§60.2115 with a descriptio n of t he deviations, reasons f or

such deviations, and a description of corrective action s

taken.

(f) The results o f the init i al, annual, and an y

subsequent performance tests conducted to determine

compliance with the emissio n l i mits and/or to establis h

operating limits, as applicable. Retain a copy of the

complete test report including calculations.

(g) All documentation produce d as a result o f th e

siting requirements of §§60.2045 and 60.2050.

(h) Records showing th e names o f CISWI unit operator s

who have completed review of th e information in §60.2095(a)

as required by §60.2095(b), i n cluding the date of th e

initial review and all subsequent annual reviews.

(i) Records showing th e names o f the CISWI operator s

who have completed the operator t raining requirements unde r

§60.2070, met the criteria for qualification under67

§60.2080, and maintained or renewed their qualification

under §60.2085 or §60.2090. Records must includ e

documentation of training, the dates of the initial an d

refresher training, and the dates of their qualificatio n

and all subsequent renewals of such qualifications.

(j) For each qualified opera t or, the phone and/o r

pager number at which the y can b e reached during operatin g

hours.

(k) Records o f calibration o f a ny monitoring device s

as required under §60.2165.

(l) Equipment vendor specifications and related

operation and maintenance requirements for the incinerator,

emission controls, and monitoring equipment.

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

(n) On a daily basis

, keep a l o g of the quantit y o f

waste burned and th e types of waste burned (alwa ys

required).

(o) Maintain records of the annual air pollution

control device inspections that a re required for each CISW I

unit subject to the emissions limits in table 1 of this

subpart or tables 5 through 8 of this subpart, any required

maintenance, and any repairs no t completed within 10 day s

of an inspection or th e timefram e established by the stat e

regulatory agency.

(p) For continuously monitored pollutants or

parameters, you must document and keep a record of the

following parameters measured using continuous monitoring

systems.

(1) All 6-minute average levels of opacity.68

(2) All 1-hour average concentrations of sulfur

dioxide emissions.

(3) All 1-hour average concentrations of nitrogen

oxides emissions.

(4) All 1-hour average concentrations of carbon

monoxide emissions. You must in d icate which data are CEM S

data during startup and shutdown.

(5) All 1-hour average concentrations of particulate

matter emissions.

(6) All 1-hour average concentrations of mercury

emissions.

(7) All 1-hour average concentrations of hydrogen

chloride emissions.

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

(9) All 1-hour average PM CPM S r e adings or particulate

matter continuous emissions monitor outputs.

(q) Records indicating use o f the bypass stack

,

including dates, times, and durations.

(r) If you choose to stack test less frequently than

annually, consistent with §60.21 5 5(a) through (c), you mus t

keep annual records that document that your emissions in

the previous stack test(s) were less than 75 percent of the

applicable emission limit and document that there was no

change in source operation s inc l uding fuel composition an d

operation of air pollutio n con t rol equipment that woul d

cause emissions of the relevant pollutant to increase

within the past year.

(s) Records of the occurrence and duration of eac h

malfunction of operation (i.e., process equipment) or the

air pollution control and monitoring equipment.

(t) Records of all required ma i ntenance performed on

the air pollution control and monitoring equipment.69

(u) Records of action s take n during periods o f

malfunction to minimize emissions in accordance with

§60.11(d), including corrective actions to restore

malfunctioning process and air pollution control and

monitoring equipment to its n o rmal or usual manner o f

operation.

(v) For operating units that combust non-hazardous

secondary materials that have b een determined not to b e

solid waste pursuant to §241.3( b )(1) of this chapter, yo u

must keep a record which documents how the secondary

material meets each o f the le g itimacy criteria. If y ou

combust a fuel that ha s been p rocessed from a discarde d

non-hazardous secondary material pursuant to §241.3(b)(4)

of this chapter, you must keep records as to how the

operations that produced th e fu e l satisfies the definitio n

of processing in §241.2 o f t h is chapter. If the fue l

received a non-waste determinati o n pursuant to the petitio n

process submitted under §241.3(c ) of this chapter, you mus t

keep a record that document s h o w the fuel satisfies th e

requirements of the petition process.

§60.2180 Where and in what format must I keep my records?

All records must be available o n site in either pape r

copy or computer-readable forma t that can be printed upo n

request, unless an alternative format is approved by the

Administrator.

§60.2185 What reports must I submit?

See table 4 of this subpart for a summary of the

reporting requirements.70

§60.2190 What must I submit prior to commencing

construction?

You must submit a notificatio n prior to commencin g

construction that includes th e five items liste d i n

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 produce d as a result o f th e

siting requirements of §60.2050.

(d) The waste management p l an as specified i n

§§60.2055 through 60.2065.

(e) Anticipated date of initial startup.

§60.2195 What information must I submit prior t o initia l

startup?

You must submit the information specified in

paragraphs (a) through (e) o f th i s section prior to initia l

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 petit i on for site-specifi c

operating limits under §60.2115.

(e) The anticipated date of initial startup.

§60.2200 What information must I submit following my71

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 report s

must be signed by the facilities manager.

(a) The complet e test rep o rt for the initi al

performance test results obtained under §60.2135, as

applicable.

(b) The values for th e site-spe c ific operating limits

established in §60.2110 or §60.2115.

(c) If you are using a fabric filter to comply wit h

the emission limitations, docu m entation that a ba g lea k

detection system has bee n instal l ed and is bein g operated

,

calibrated, and maintained as required by §60.2165(b).

§ 60.2205 When must I submit my annual report?

You must submit an annual report no later than 12

months following the submission of the information in

§60.2200. You must submi t subse q uent reports no more tha n

12 months following the previou s report. (If the uni t i s

subject to permitting requireme n ts under title V of th e

Clean Air Act, yo u may b e requir e d by the permi t to submi t

these reports more frequently.)

§60.2210 What information mus t I include i n my annual

report?

The annual report required under §60.2205 must includ e

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 deviatio n

reports as specified in §§60.2215, 60.2220, and 60.2225.72

(a) Company name and address.

(b) Statement by a responsible official, with that

official's name, title, and signature, certifying the

accuracy of the content of the report.

(c) Date of report and beginning and ending dates of

the reporting period.

(d) The values for the operat i ng limits establishe d

pursuant to §60.2110 or §60.2115.

(e) If no deviation from any emission limitation or

operating limit that applies t o you has been reported

, a

statement that there was no d e viation from the emissio n

limitations or operating limits during the reporting

period

, and that no monitorin g system used to determin e

compliance with the operating limits was inoperative,

inactive, malfunctioning or out of control

.

(f) The highest recorded 3- h our average and th e

lowest recorded 3-hour average

, as applicable, fo r eac h

operating parameter recorded for the calendar year bein g

reported.

(g) Information recorded under § 60.2175(b)(6) and (c )

through (e) for the calendar year being reported.

(h) If a performanc e test was conducted during th e

reporting period, the results of that test.

(i) If you me t the requireme n ts of §60.2155(a) o r

(b), and did not conduct a performance test during the

reporting period, you must s tate that you met th e

requirements of §60.2155(a) o r (b), and, therefore, yo u

were not required to conduc t a p erformance test during th e

reporting period.73

(j) Documentation of periods wh e n all qualified CISW I

unit operators were unavailable f or more than 8 hours

, bu t

less than 2 weeks.

(k) If you ha d a malfunctio n during the reporting

period, the compliance report must include the number

,

duration, and a brie f descri p tion for each typ e o f

malfunction that occurred durin g the reporting period and

that caused or ma y have cause d any applicable emissi on

limitation to be exceeded. The report must also include a

description of actions taken b y a n owner or operator durin g

a malfunction of an affected so u rce to minimize emission s

in accordance with §60.11(d), including actions taken t o

correct a malfunction.

(l) For each deviatio n from a n emission or operating

limitation that occurs for a CISWI unit for which you are

not using a continuous monitorin g system to comply wit h th e

emission or operating limitati o ns in this subpart, th e

annual report must contain the following information.

(1) The total operating time of the CISWI unit at

which the deviation occurred during the reporting period.

(2) Information on th e number, d uration, and cause o f

deviations (including unknown cause, if applicable), as

applicable, and the corrective action taken.

(m) If there wer e periods durin g which the continuou s

monitoring system, including th e CEMS, was out of contro l

as specified in paragraph (o) of this section, the annual

report must contain the follo w ing information for eac h74

deviation from an emission or operating limitation

occurring for a CISWI unit for which you are using a

continuous monitoring system to comply with the emissio n

and operating limitations 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-level

checks.

(3) The date, time

, and duratio n that each continuou s

monitoring system was out-of-control, including start and

end dates and hour s and descrip t ions of corrective actio ns

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, an d the total duration a s a

percent of the tota l source o p erating time during th at

reporting period.

(6) A breakdown o f the to t al duration of th e

deviations during the reportin g p eriod into those tha t ar e

due to control equipmen t proble m s, process problems, othe r

known causes, and other unknown causes.

(7) A summary o f the tota l d u ration of continuous75

monitoring system downtime durin g the reporting period, an d

the total duration of continuous monitoring system downtim e

as a percent o f the tota l operat i ng time of th e CISWI uni t

at which the continuous monitori n g system downtime occurre d

during that reporting period.

(8) An identification of eac h p a rameter and pollutant

that was monitored at the CISWI unit.

(9) A brief description of the CISWI unit.

(10) A brief description o f the continuous monitoring

system.

(11) The date of th e latest continuous monitoring

system certification or audit.

(12) A description of any c hanges in continuou s

monitoring system, processes, or controls since the las t

reporting period.

(n) If there wer e periods durin g which the continuou s

monitoring system, including t h e CEMS, was not out o f

control as specified in paragra p h (o) of this section

, a

statement that there wer e not periods during which t he

continuous monitoring system wa s out of control durin g th e

reporting period.

(o) A continuous monitorin g sys t em is out of contro l

in accordance with the procedure in 40 CFR part 60,

appendix F of this part, as if any of the following occur.76

(1) The zer o (low-level), mid- l evel (if applicable)

,

or high-level calibration drift exceeds two times the

applicable calibration drift specification in the

applicable performance specification or in the relevant

standard.

(2) The continuous monitor i ng system fails a

performance test audit (e.g., cy l inder gas audit), relativ e

accuracy audit, relative accurac y test audit, o r linearit y

test audit.

(3) The continuous opacity monitoring system

calibration drift exceeds two times the limit in the

applicable performance specification in the relevant

standard.

§60.2215 What else must I rep o rt if I have a deviatio n

from the operating limits or the emission limitations?

(a) You must submit a deviation report if any

recorded 3-hour average param e ter level is above th e

maximum operating limit or be l ow the minimum operatin g

limit established under this s ubpart, if the bag lea k

detection system alarm sounds f o r more than 5 percen t o f

the operating time for th e 6-mon t h reporting period, or i f

a performance test was conduct e d that deviated from an y

emission limitation.

(b) The deviation repor t must b e submitted by Augus t

1 of that yea r for dat a collecte d during the firs t half o f

the calendar year (January 1 t o J une 30), and by February 1

of the following year fo r dat a you collected during th e

second half of the calendar year (July 1 to December 31).77

§60.2220 What must I include in the deviation report?

In each report required unde r §60.2215, for an y

pollutant or parameter that d e viated from the emissio n

limitations or operating limit s specified in this subpart

,

include the six items described in paragraphs (a) throug h

(f) of this section.

(a) The calendar dates and times your unit deviated

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) Each each deviation from e m ission limitations or

operating limits and your corrective actions.

(2) Bypass events and your corrective actions.

(d) A copy o f the operatin g l imit monitoring data

during each deviation and any test report that documents

the emission levels.

(e) [Removed]

(f) [Removed]

(e) The dates, times, number, duration, and caus es

for monitor downtime incidents (other than downtime

associated with zero, span, an d other routine calibration

checks).

(f) Whether each deviation occ u rred during a perio d

of startup, shutdown, o r malfu n ction, or during anothe r

period.

§60.2225 What else must I rep o rt if I have a deviatio n78

from the requirement to have a qualified operato r

accessible?

(a) If all qualifie d operators a re not accessible fo r

2 weeks or more, you must take the two actions in

paragraphs (a)(1) and (2) of this section.

(1) Submit a notificatio n of t h e deviation within 1 0

days that includes th e three it e ms in paragraphs (a)(1)( i)

through (iii) of this section.

(i) A statement of what caused the deviation.

(ii) A description of what you are doing to ensure

that a qualified operator is accessible.

(iii) The date when you anticipate that a qualified

operator will be available.

(2) Submit a statu s report to t h e Administrator ever y

4 weeks that includes the t h ree items in paragraph s

(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 whe n you antici p ate that a qualifie d

operator will be accessible.

(iii) Request approval fro m the Administrator to

continue operation of the CISWI unit.

(b) If your unit was shut down by the Administrator,

under the provisions of §60.2100 ( b)(2), due to a failur e t o

provide an accessible qualified operator, you must notify

the Administrator that you are resuming operation once a

qualified operator is accessible.79

§60.2230 Are there any other notifications or reports

that I must submit?

(a) Yes. You mus t submit notifi c ations as provided b y

§60.7.

(b) If you ceas e combusting so l id waste but continu e

to operate, you must provide 30 days prior notice of the

effective date of the waste-to-f u el switch, consistent wit h

60.2145(a). The notification must identify:

(1) The name of the owner or operator of the CISWI

unit, the location of the sou r ce, the emissions unit(s )

that will cease burning solid waste, and the date of the

notice;

(2) The currently applicable subcategory under this

subpart, and any 40 CF R part 6 3 subpart and subcategor y

that will be applicable after you cease combusting solid

waste;

(3) The fuel(s), non-wast e m aterial(s) and solid

waste(s) the CISWI unit is cu r rently combusting and ha s

combusted over the past 6 months, and the fuel(s) or nonwaste materials the unit will commence combusting;

(4) The date on whic h you b e came subject to th e

currently applicable emission limits;

(5) The date upo n which yo u w ill cease combustin g

solid waste, and the dat e (if d ifferent) that you inten d80

for any new requirements to become applicable (i.e., the

effective date of the waste-to-fuel switch), consistent

with paragraphs (2) and (3)) of this section.

§60.2235 In what form can I submit my reports?

(a) Submit initial, annual

, and deviation reports

electronically or in pape r forma t

, postmarked on o r befor e

the submittal due dates.

(b) As of January 1, 2012, an d within 60 days afte r

the date of completing eac h perf o rmance test, as defined i n

§63.2, conducted to demonstrate compliance with this

subpart, you must submit relative accuracy test audit

(i.e., reference method) data a n d performance test (i.e.,

compliance test) data, except opacity data, electronically

to EPA’s Central Data Excha n ge (CDX) by using th e

Electronic Reporting Tool (ERT) (see

http://www.epa.gov/ttn/chief/ert/ert tool.html/) or other

compatible electronic spreadsheet. Only data collected

using test methods compatible wi t h ERT are subject t o thi s

requirement to be submitted electronically into EPA’s

WebFIRE database.

§60.2240 Can reporting dates be changed?

If the Administrator agrees, you may change th e

semiannual or annual reportin g dates. See §60.19(c) fo r

procedures to seek approval to change your reporting date.

Title V Operating Permits

§60.2242 Am I required to apply for and obtain a Tt itle V

operating permit for my unit?

Yes. Each CISW I unit an d ai r curtain incinerato r81

subject to standards under t h is subpart must operat e

pursuant to a permit issue d unde r section 129(e) and T t itl e

V of the Clean Air Act

. by th e later of the two dates i n

paragraphs (a) and (b) of this section.

(a) Thirty

- six mon ths after December 1, 2000.

(b) The effective date of the title V permit program

to which your unit is subject. I f your unit is subject t o

title V as a resul t of some trig g ering requirement(s) othe r

than this subpart (for example

, b eing a major source), th e n

your unit may b e required t o app l y for and obtai n a titl e V

permit prior to the deadlines noted above. If more than one

requirement triggers the require m ent to apply for a title V

permit, the 12

- month timefram e for filing a title V

application is trigge red b y th e requirement which firs t

causes the source to be subject to title V.

Air Curtain Incinerators

§60.2245 What is an air curtain incinerator?

(a) An air curtain incinerato r o perates by forcefully

projecting a curtain of air across an open chamber or open

pit in which combustion occurs. Incinerators of this typ e

can be constructed above o r b elow ground and with o r

without refractory walls and floor. (Air curtai n

incinerators are not to be confused with conventional

combustion devices with enclosed fireboxes and controlled

air technology such as mass burn, modular, and fluidized

bed combustors.)

(b) Air curtain incinerator s that burn only th e

materials listed in paragraphs ( b)(1) through (3) of thi s

section are only required to meet the requirements under

“Air Curtain Incinerators” (§§60.2245 through 60.2260).82

(1) 100 percent wood waste.

(2) 100 percent clean lumber.

(3) 100 percent mixtur e of o n ly wood waste, clea n

lumber, and/or yard waste.

§60.2250 What are the emission limitations for air

curtain incinerators?

(a) Within 60 day s after you r a i r curtain incinerato r

reaches the charge rate at which it will operate, but no

later than 180 days afte r its initial startup, you mus t

meet the two limitations specifi e d in paragraphs (a) (1) an d

( b 2 ) of this section.

(a) Maintain opacity to less than or equal to 10

percent opacity (as determined by the average of three 1-

hour blocks consisting of te n 6-minute average opacit y

values), except as described i n paragraph (b) of thi s

section.

(b) Maintain opacity to less than or equal to 35

percent opacity (as determined by the average of three 1-

hour blocks consisting of te n 6-minute average opacit y

values) during the startup perio d that is within th e firs t

30 minutes of operation.

(1) The opacity limitati o n is 10 percent (6

- minut e

average), except as described i n paragraph (a)(2) of thi s

section.

(2) The opacity limitatio n is 35 percent (6

- minut e

average) during the startup peri o d that is within th e firs t

30 minutes of operation.

(b) Except during malfunct ions, the requirements of

this subpart apply at al l times

, and each malfunction mus t

not exceed 3 hours.

§60.2255 How must I monitor opacity for air curtain83

incinerators?

(a) Use Method 9 of appendi x A of this part t o

determine compliance with the opacity limitation.

(b) Conduct an initia l test fo r opacity as specifie d

in §60.8.

(c) After the initial test for opacity, conduc t

annual tests no more tha n 12 ca l endar months following th e

date of your previous test.

§60.2260 What are the recordkeeping and reporting

requirements for air curtain incinerators?

(a) Prior t o commencing cons t ruction on your a ir

curtain incinerator, submit the three items described i n

paragraphs (a)(1) through (3) of this section.

(1) Notification of you r inten t to construct the ai r

curtain incinerators.

(2) Your planned initial startup date.

(3) Types of materials you pla n to burn in your ai r

curtain incinerator.

(b) Keep records of results of all initial and annual

opacity tests onsite in eithe r paper copy or electroni c

format, unless the Administrator approves another format,

for at least 5 years.

(c) Make all records available for submittal to the

Administrator or for an inspector's onsite review

.

(d) You must submit th e results ( as determined by th e

average of three 1-hour block s consisting of ten each 6-

minute average opacity values ) o f the initial opacity test s84

no later than 60 day s followin g the initial test. Submi t

annual opacity test result s with i n 12 months followin g th e

previous report.

(e) Submit initial an d annual o p acity test reports a s

electronic or paper copy on or before the applicable

submittal date.

(f) Keep a copy of the initial and annual reports

onsite for a period of 5 years.

Definitions

§60.2265 What definitions must I know?

Terms used but not define d in th i s subpart are define d

in the Clean Air Act and subpart A (General Provisions) of

this part.

Administrator means the Administrator of the U.S.

Environmental Protection Agency or his/her authorized

representative or Administrator of a State Air Pollutio n

Control Agency.

Affirmative defense means, i n the context of a n

enforcement proceeding, a respo n se or defense put forward

by a defendant, regarding whi c h the defendant has th e

burden of proof, and th e merits of which are independentl y

and objectively evaluated in a judicial or administrative

proceeding.

Agricultural waste means ve g etative agricultura l

materials such as nut and grain hulls and chaff (e.g.,

almond, walnut, peanut, rice

, a n d wheat), bagasse, orchar d

prunings, corn stalks, coffee b e an hulls and grounds, an d

other vegetative waste material s generated as a result o f85

agricultural operations.

Air curtain incinerator means an incinerator that

operates by forcefully projecti n g a curtain of air acros s

an open chamber o r pit i n which combustion occurs

.

Incinerators of this type ca n be constructed above or belo w

ground and with or withou t refra c tory walls and floor. (Ai r

curtain incinerators are no t to be confuse d wit h

conventional combustion devices with enclosed fireboxes and

controlled air technology such a s mass burn, modular, an d

fluidized bed combustors.)

Annual heat input means the heat input for the 12

months preceding the compliance demonstration.

Auxiliary fuel means natural gas, liquified petroleum

gas, fuel oil, or diesel fuel.

Average annual heat input rate m e ans annual heat inpu t

divided by the hours of operation for the 12 months

preceding the compliance demonstration.

Bag leak detection syste m means an instrument that is

capable of monitoring particulate matter loadings in th e

exhaust of a fabric filte r (i. e

., baghouse) in order t o

detect bag failures. A bag lea k detection system includes

,

but is not limited to

, an in s trument that operates o n

triboelectric, light scattering, light transmittance, or

other principle to monitor relative particulate matter

loadings.

Burn-off oven means any rack r e clamation unit, part

reclamation unit, or drum reclam a tion unit. A burn-off ove n

is not an incinerator, waste

- burning kiln, an energ y

recovery unit or a small, rem o te incinerator under thi s86

subpart.

Bypass stack means a device used for discharging

combustion gases to avoi d se v ere damage to th e ai r

pollution control device or other equipment.

Calendar quarter means three consecutive months (non

overlapping) beginning on: January 1, April 1, July 1, or

October 1.

Calendar year means 365 consecu t ive days starting on

January 1 and ending on December 31.

CEMS data during startu p and s hutdown means carbo n

monoxide CEMS data collected du r ing the first 4 hour s o f

operation of energy recovery uni t startup from a col d start

and the hour of operatio n follow i ng the cessation of wast e

material being fed to th e ener g y recovery unit during a

unit shutdown.

Chemical recovery unit means combustion units burning

materials to recover chemical constituents or to produc e

chemical compounds where there is an existing commercia l

market for such recovered chemical constituents or

compounds. The followin g se v en types of unit s ar e

considered chemical recovery units:

(1) Units burning only pulping liquors (i.e., black

liquor) that are reclaimed in a pulping liquor recover y

process and reused in the pulping process.

(2) Units burning only spent sulfuric acid used t o

produce virgin sulfuric acid.

(3) Units burning only wood or coa l f eedstock for the

production of charcoal.87

(4) Units burning only manufacturing byproduct

streams/residue containing catalyst metals which are

reclaimed and reused as catalysts or used to produce

commercial grade catalysts.

(5) Units burning only coke to produce purified

carbon monoxide that is used as an intermediate in the

production of other chemical compounds.

(6) Units burning only hydrocarbon liquids or solids

to produce hydrogen, carbo n mo n oxide, synthesis gas, o r

other gases for use in other manufacturing processes.

(7) Units burning only photographic film to recover

silver.

Chemotherapeutic waste means waste material resulting

from the production or use of antineoplastic agents used

for the purpose of stopping or reversing the growth of

malignant cells.

Clean lumber means wood or wo o d products that hav e

been cut or shaped an d include wet, air-dried, and kilndried wood products. Clean lum b er does not include woo d

products that have been painted, pigment-stained, or

pressure-treated by compounds such as chromate copper

arsenate, pentachlorophenol, and creosote.

Commercial and industrial solid waste incineration

(CISWI) unit means any combu s tion unit that combust s

commercial or industrial was t e (as defined in this

subpart), that is a distinc t operating unit o f an y

commercial or industrial facility (including field erected,

modular, and custom built incine r ation units operating wit h

starved or excess air), and a n y air curtain incinerato r

that is a distinct operating unit of any commercial or

industrial facility that does n o t comply with the opacit y

limits under this subpar t a p plicable to air cur tai n88

incinerators burning commercial or industrial waste. that

combusts, or has combusted in the preceding 6 months, any

solid waste as that term i s defi n ed in 40 CFR part 241

. I f

the operating unit burns materi a ls other than traditional

fuels as defined in §241. 2 tha t have been discarded, an d

you do not keep an d produc e records as required b y

§60.2175(v), the material i s a solid waste an d th e

operating unit is a CISWI unit

. While not al l CISWI unit s

will include all of th e followin g components, a CISWI uni t

includes, but is no t limite d to, the commercia l o r

industrial the solid wast e feed system, grate system, flu e

gas system, waste hea t recover y equipment, if any

, an d

bottom ash system. The CISWI unit does not include air

pollution control equipment or the stack. The CISWI unit

boundary starts at the commercia l or industrial solid wast e

hopper (if applicable) and exte n ds through two areas: Th e

combustion unit flue ga s syste m

, which ends immediatel y

after the last combustion chamber or after the waste heat

recovery equipment, if any ; and the combustion unit bott om

ash system, which ends at the truck loading station or

similar equipment that transfers the ash to final disposal

.

The CISWI unit include s all as h handling systems connecte d

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, n o r does it include an y

combustion turbine or reciprocating internal combustion

engine.

Commercial or industrial waste m eans solid waste (as

defined in this subpart) th a t is combusted at an y

commercial or industrial facility using controlled flame

combustion in an enclosed, dist i nct operating unit: Whose

design does not provide fo r ener g y recovery (as defined i n

this subpart); or operated wi t hout energy recovery (a s

defined in this subpart). Commercial or industrial wast e

also means solid waste (as d efined in this subpart )

combusted in an air curtai n inci n erator that is a distinc t

operating unit of any commercial or industrial facility.89

Contained gaseous material mean s gases that are in a

container when that container is combusted.

Continuous monitoring system (CMS) means the total

equipment, required under the emission monitoring sections

in applicable subparts, used to sample and condition (if

applicable), to analyze, an d to provide a permanent reco rd

of emissions or process parameters. A particulate matte r

continuous parameter monitoring s ystem (PM CPMS) i s a ty pe

of CMS.

Cyclonic barrel burner means a combustion device for

waste materials that is attache d to a 55 gallon, open-hea d

drum. The device consists of a lid, which fits onto and

encloses the drum, and a blower that forces combustion ai r

into the drum in a cycloni c mann e r to enhance the mixing o f

waste material and air. A cycl o nic burn barrel is not a n

incinerator, waste-burning kiln, an energy recovery unit o r

a small, remote incinerator under this subpart.

Deviation means any instance i n which an affecte d

source subject to this subpart, or an owner or operator of

such a source:

(1) Fails to meet any requ i rement or obligatio n

established by this subpart, in c luding but not limited t o

any emission limitation, operating limit, or operator

qualification and accessibility requirements

. ;

(2) Fails to meet any term or condition that is

adopted to implement an appli c able requirement in thi s

subpart and that is include d i n the operating permit fo r

any affected source required to obtain such a permit ; or

.90

(3 ) Fails to meet any emission limitation, operating

limit, or operator qualification and accessibility

requirement in this subpart during startup, shutdown, o r

malfunction, regardless or whet h er or not such failure i s

permitted by this subpart.

Dioxins/furans means tetra- through

octachlorinated octa-chlorinated dibenzo-p-dioxins and

dibenzofurans.

Discard means, for purposes o f t h is subpart and 40 CF R

part 60, subpart DDDD, only

, bur n ed in an incineration uni t

without energy recovery.

Drum reclamation unit means a un i t that burns residue s

out of drums (e.g.

, 55 gallo n dr u ms) so that th e drums ca n

be reused.

Energy recovery means the process of recovering

thermal energy from combustio n f o r useful purposes suc h a s

steam generation or process heating.

Energy recovery unit means a combustion unit

combusting solid waste (as that term is defined by the

Administrator under the Resource Conservation and Recovery

Act in 40 CFR 241) for energy recovery. Energy recovery

units include units that would be considered boilers and

process heaters if they did not combust solid waste.

Energy recovery unit designed to burn biomass

(Biomass) means an energy recovery unit that burns solid

waste, biomass, and non-coa l sol i d materials but les s tha n

10 percent coal, on a heat input basis on an annual

average, either alone o r in com b ination with liquid wast e,

liquid fuel or gaseous fuels.

Energy recovery unit designed to burn coal (Coal)91

means an energy recovery unit that burns solid waste and at

least 10 percent coal on a hea t input basis on an annual

average, either alone o r in com b ination with liquid wast e,

liquid fuel or gaseous fuels.

Energy recovery unit designe d t o burn liquid waste

materials and gas (Liquid/gas) means an energy recover y

unit that burns a liquid waste with liquid or gaseous fuels

not combined with any solid fuel or waste materials.

E nergy recovery unit designe d t o burn solid material s

(Solids) includes energy recovery units designed to bur n

coal and energy recovery units designed to burn biomass.

Fabric filter means an add-on a ir pollution control

device used to captur e particula t e matter by filterin g ga s

streams through filter media, also known as a baghouse.

Foundry sand thermal reclamatio n unit means a typ e o f

part reclamation unit that rem o ves coatings that are o n

foundry sand. A foundry sand thermal reclamation unit is

not an incinerator, waste-burnin g kiln, an energ y recover y

unit or a small, remote incinerator under this subpart.

Homogeneous wastes are stable, consistent in

formulation, have known fue l p r operties, have a define d

origin, have predictable chemical and physical attributes,

and result in consistent combustion characteristics and

have a consistent emissions profile.

Incinerator means any furnace u s ed in the process o f

combusting solid waste (as that term is defined by the

Administrator under 40 CFR 241 ) f or the purpose of reducin g

the volume of the waste b y re m oving combustible matter.

Incinerator designs include single chamber and, twochamber.

Kiln means an oven or fur n ace, including any

associated preheater or precalciner devices, used for

processing a substance by burnin g

, firing or drying. Kiln s

include cement kilns that pr o duce clinker by heatin g92

limestone and other material s f o r subsequent production o f

Portland Cc ement

.

Laboratory analysis unit means u n its that burn sample s

of materials for the purpose of chemical or physical

analysis. A laboratory analysis u nit is not an incinerator

, waste-burning kiln, an energy r ecovery unit or a small

, remote incinerator under this subpart.

Low-level radioactive waste means waste material which

contains radioactive nuclides emitting primarily beta or

gamma radiation, or both, in c o ncentrations or quantities

that exceed applicable Federal or State standards for

unrestricted release. Low-level radioactive waste is not

high-level radioactive waste, spent nuclear fuel, or

byproduct material as defined by the Atomic Energy Act of

1954 (42 U.S.C. 2014(e)(2)).

Malfunction means any sudden, infrequent, and not

reasonably preventable failure of air pollution control

equipment, process equipment, or a process to operate i n a

normal or usual manner. Failure s that are caused, in part

,

by poor maintenance or careless operation are no t

malfunctions

.

Minimum voltage or amperage means 90 percent of the

lowest test-run average volt a ge or amperage to the

electrostatic precipitator measured during the most recent

particulate matter or mercury performance test

demonstrating compliance with the applicable emission

limits.

Modification or modified CISWI u n it means a CISWI uni t

that has been yo u have change d l a ter than June 1

, 2001 an d

that meets one of two criteria:

(1) The cumulative cost of the changes over the life

of the unit exceeds 50 percent of the original cost of

building and installing the CIS W I unit (not including th e93

cost of land) updated to curren t costs (current dollars)

.

To determine what systems ar e w ithin the boundary of th e

CISWI unit used to calculat e these costs, see th e

definition of CISWI unit.

(2) Any physical change in the CISWI unit or change

in the method of operating it that increases the amount of

any air pollutant emitted fo r wh i ch section 129 or sectio n

111 of the Clean Air Act has established standards.

Opacity means the degree to whic h emissions reduce th e

transmission of light and obscure the view of an object in

the background.

Operating day means a 24-hour period between 12:0 0

midnight and the following midni g ht during which any amoun t

of solid waste is combusted at any time in the CISWI unit.

Oxygen analyzer system means all equipment required t o

determine the oxygen content of a gas stream and used to

monitor oxygen in the boiler flue gas or firebox. This

definition includes oxygen trim systems. The source owner

or operator is responsible to in s tall, calibrate, maintain

,

and operate the oxygen analyzer system in accordance wit h

the manufacturer’s recommendations.

Oxygen trim system means a syste m of monitors that i s

used to maintain excess air at the desired level in a

combustion device. A typical sys t em consists of a flu e ga s

oxygen and/or carbon monoxide monitor that automatically

provides a feedback signa l to the combustion ai r

controller.

Part reclamation unit means a un i t that burns coating s

off parts (e.g., tools, equipment) so that the parts can be

reconditioned and reused.

Particulate matter means total particulate matter

emitted from CISWI units as measured by Method 5 or Method94

29 of appendix A of this part.

Pathological waste means waste material consisting of

only human or animal remains

, anatomical parts, and/o r

tissue, the bags/containers use d to collect and transport

the waste material, and animal bedding (if applicable).

Performance evaluation means the conduct of relative

accuracy testing, calibration error testing, and other

measurements used in validating the continuous monitoring

system data.

Performance test means the collection of data

resulting from the executio n o f a test metho d (usuall y

three emission test runs) used to demonstrate compliance

with a relevant emission stan d ard as specified in th e

performance test section of the relevant standard.

Process change means a significant permit revision,

but only with respec t to thos e p ollutant-specific emission

units for which the proposed per m it revision is applicable

,

including but not limited to a change in the air pollution

control devices used to compl y w i th the emission limits fo r

the affected CISWI unit (e.g., change in the sorbent used

for activated carbon injection).

Rack reclamation unit mean s a unit that burns t he

coatings off racks used t o hold s mall items for applicatio n

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 ma y be added or remove d fro m

the feed during the grinding ope r ation. If the raw mil l i s

used to remove moisture from feed materials, it is also, by

definition, a raw material dr y er. The raw mil l als o

includes the air separator associated with the raw mill.95

Reconstruction means rebuilding a CISWI unit and

meeting two criteria:

(1) The reconstruction begin s on or after June 1

,

2001.

(2) The cumulative cos t of th e construction over the

life of the incineration uni t e xceeds 50 percent of th e

original cost of building and installing the CISWI uni t

(not including land) updated t o current costs (curren t

dollars). To determine wha t systems are within th e

boundary of the CISWI unit used to calculate these costs,

see the definition of CISWI unit.

Refuse-derived fuel means a type of municipal soli d

waste produced by processin g mu n icipal solid waste throug h

shredding and size classification. This includes all

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 o f tim e after all waste ha s

been combusted in the primary chamber.

Small, remote incinerator means an incinerator that

combusts solid waste (as tha t term is defined b y th e

Administrator in 40 CFR 241) an d combusts 3 tons per day o r

less solid waste and is more than 25 miles driving distance

to the nearest municipal solid waste landfill.

Solid waste means any garbage, r efuse, sludge from a

waste treatment plant, water sup p ly treatment plant, or ai r

pollution control facility and other discarded material,

including solid, liquid, semisolid, or contained gaseous

material resulting from industrial, comme rcial, mining,96

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 unde r section 402 of the Federa l

Water Pollution Control Act, as amended (33 U.S.C. 1342)

,

or source, special nuclear, o r byproduct material a s

defined by the Atomic Energy Act of 1954, as amended (42

U.S.C. 2014).

Soil treatment unit means a uni t that thermally treats

petroleum –contaminated soils fo r the sole purpos e of si te

remediation. A soil treatemen t u nit may be direct-fired o r

indirect fired. A soil tre a tment unit is not a n

incinerator, waste-burning kiln, an energy recovery unit o r

a small, remote incinerator under this subpart.

Solid waste incineration unit means a distinct

operating unit of any facilit y which combusts any soli d

waste (as that term is defined by the Administrator in 40

CFR part 241) material from commercial or industria l

establishments or the genera l p u blic (including single an d

multiple residences, hotels and m otels). Such term does no t

include incinerators or othe r u nits required to hav e a

permit under section 3005 o f th e Solid Waste Disposal Act

.

The term "solid wast e incinerati o n unit" does no t include :

(A) materials recovery facilities (including primary or

secondary smelters) which comb u st waste for th e primar y

purpose of recovering metals; (B) qualifying small powe r

production facilities, as defined in section 3(17)(C) o f

the Federal Power Act (16 U.S.C

. 769(17)(C)), or qualifying

cogeneration facilities, as defi n ed in section 3(18)(B ) o f

the Federal Power Act (16 U.S.C. 796(18)(B)), which burn

homogeneous waste (such as units which burn tires or used

oil, but not includin g refu s e-derived fuel) for th e

production of electric energy o r in the case of qualifyin g

cogeneration facilities which burn homogeneous waste for

the production of electric ene r gy and steam or form s o f

useful energy (such as heat ) whi c h are used for industrial

, commercial, heating or cooling p u rposes; or (C) air curtai n

incinerators provided that such i ncinerators only burn woo d97

wastes, yard wastes, and clea n lumber and that such ai r

curtain incinerators comply wit h opacity limitations t o b e

established by the Administrator by rule.

Space heater means a usually p o rtable appliance for

heating a relatively small area. These units are not

subject to the incinerator, was t e-burning kiln, or small,

remote subcategories.

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 the unit.

Waste-burning kiln means a kil n that is heated, i n

whole or in part, by combusting solid waste (as that term

is defined by the Administrator in 40 CFR part 241). A

waste-burning kiln does not incl u de a kiln that i s feedin g

non-hazardous secondary ingredients exclusively into the

cold end of the kiln.

Wet scrubber means an add-on air pollution control

device that uses utilizes an aqueous or alkaline scrubbing

liquor to collect particulate matter (including nonvaporous

metals and condensed organics) and/or to absorb and

neutralize acid gases.

Wood waste means untreated wood and untreated wood

products, including tree stumps (whole or chipped), trees,

tree limbs (whole or chipped), bark, sawdust, chips,

scraps, slabs, millings, and shavings. Wood waste does not

include:

(1) Grass, grass clippings, bushes, shrubs, and

clippings from bushes and shrubs from residential,

commercial/retail, institutional, or industrial sources as98

part of maintaining yards or other private or public lands.

(2) Construction, renovation, or demolition wastes.

(3) Clean lumber.

Table 1 to Subpart CCCC of Part 60—Emission Limitations for

CISWI Units for Which Construction Is Commenced After

November 30, 1999, but no later than June 4, 2010, or for

Which Modification or Reconstruction Is Commenced on or

After June 1, 2001, but no later than [THE DATE 6 MONTHS

AFTER PUBLICATION OF THE FINAL RULE IN THE FEDERAL

REGISTER].

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

(collect a

minimum volume of

1 dry standard

cubic meter per

run) ( 1 hour

minimum sample

time per run) Performance

test (Method

29 at 40 CFR

part 60, of

appendix A -8

of this

part ).

Carbon monoxide 157 parts

per million

by dry

volume 3-run average (1

hour minimum

sample time per

run) Performance

test (Method

10 at 40 CFR

part 60,

appendix A4).

Performance

test (Method99

10, 10A, or

10B of

appendix A of

this part).

Dioxin s / F f uran s

(toxic

equivalency

basis) 0.41

nanograms

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

2 dry standard

cubic meters per

run) (1 hour

minimum sample

time per run) Performance

test (Method

23 of

appendix A -7

of this

part).

Hydrogen

chloride 62 parts

per million

by dry

volume 3-run average

(For Method 26,

collect a minimum

volume of 120

liters per run.

For Method 26A,

collect a minimum

volume of 1 dry

standard cubic

meter per run) ( 1

hour minimum

sample time per

run) Performance

test (Method

26 or 26A at

40 CFR part

60, of

appendix A -8

of this

part ).

Lead 0.04

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

1 dry standard

cubic meter per

run) (1 hour

minimum sample

time per run) Performance

test (Method

29 at 40 CFR

part 60, of

appendix A -8

of this

part ).100

Mercury 0.47

milligrams

per dry

standard

cubic meter 3-run average

(For Method 29

and ASTM D6784-

02(Reapproved

2008) b , collect a

minimum volume of

1 dry standard

cubic meter per

run. For Method

30B, collect a

minimum sample as

specified in

Method 30B at 40

CFR part 60,

appendix A) ( 1

hour minimum

sample time per

run) Performance

test (Method

29 or 30B at

40 CFR part

60, of

appendix A -8

of this part )

or ASTM

D6784-02

(Reapproved

2008 ) b

.

Opacity 10 percent Three 1-hour

blocks consisting

of ten 6-minute

averages opacity

values 6

- minute

averages Performance

test (Method

9 at 40 CFR

part 60, of

appendix A -4

of this

part ).

Oxides of

nitrogen Nitrogen

Oxides 388 parts

per million

by dry

volume 3-run average

( for Method 7E, 1

hour minimum

sample time per

run) Performance

test (Method

7 , 7A, 7C,

7D, or 7E at

40 CFR part

60, of

appendix A -4

of this

part ).101

Particulate

matter 70

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

1 dry standard

cubic meter per

run) (1 hour

minimum sample

time per run) Performance

test (Method

5 or 29 at 40

CFR part

60, of

appendix A -3

or A-8 of

this part ).

Sulfur d D ioxide 20 parts

per million

by dry

volume 3-run average

(For Method 6,

collect a minimum

volume of 200

liters per run.

For Method 6C,

collect sample

for a minimum

duration of 1

hour per run) ( 1

hour minimum

sample time per

run) Performance

test (Method

6 or 6 C c at

40 CFR part

60, of

appendix A -4

of this

part )

.

a All emissio n limitations ( except for opacity) a re

measured at 7 percent oxygen

, dry basis at standar d

conditions.

b Incorporated by reference, see §60.17.

Table 2 to Subpart CCCC of Part 60—Operating Limits for Wet

Scrubbers

For these

operating You must

establish And monitoring using these minimum

frequencies102

parameters 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 3 to Subpart CCCC of Par t 60—Toxic Equivalenc y

Factors

Dioxin/furan congener Toxic equivalency

factor

2,3,7,8-tetrachlorinated dibenzo-pdioxin 1103

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 0.1

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 0.001104

Table 4 to Subpart CCC C of Pa r t 60—Summary of Reportin g

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

• Anticipated

maximum charge

rate

• If

applicable, the

petition for

site-specific

operating

limits §60.2195105

Initial test

report No later than

60 days

following the

initial

performance

test • Complete test

report for the

initial

performance

test

• The values

for 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

• If no

deviations or

malfunctions

were reported,

a statement

that no

deviations

occurred during §§60.2205 and

60.2210106

the reporting

period

• Highest

recorded 3- hour

average and the

lowest 3-hour

average, as

applicable, for

each operating

parameter

recorded for

the calendar

year being

reported

• Information

for deviations

or malfunctions

recorded under

§60.2175(b)(6)

and (c) through

(e) • If a

performance

test was

conducted

during the

reporting

period, the

results of the

test

• If a

performance

test was not

conducted

during the

reporting107

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

• If you are

conducting

performance

tests once

every 3 years

consistent with

§60.2155(a),

the date of the

last 2

performance

tests, a

comparison of

the emission

level you

achieved in the

last 2

performance

tests to the 75

percent

emission limit108

threshold

required in

§60.2155(a) and

a statement as

to whether

there have been

any operational

changes since

the last

performance

test that could

increase

emissions.

Emission

limitation or

operating limit

deviation

report By August 1

of that year

for data

collected

during the

first half of

the calendar

year. By

February 1 of

the following

year for data

collected

during the

second half

of the

calendar year • Dates and

times of

deviation

• Averaged and

recorded data

for those dates

• Duration and

causes of each

deviation and

the corrective

actions taken

• Copy of

operating limit

monitoring data

and any test

reports

• Dates, times,

and causes for

monitor

downtime

incidents §60.2215 and

60.2220109

• Whether each

deviation

occurred during

a period of

startup,

shutdown, or

malfunction

Qualified

operator

deviation

notification Within 10

days of

deviation • Statement o f

cause of

deviation

• Description

of efforts t o

have an

accessible

qualified

operator

• The date a

qualified

operator will

be accessible §60.2225(a)(1)

Qualified

operator

deviation

status report Every 4 week s

following

deviation • Description

of efforts t o

have an

accessible

qualified

operator

• The date a

qualified

operator will

be accessible

• Request fo r

approval to

continue

operation §60.2225(a)(2)110

Qualified

operator

deviation

notification of

resumed

operation Prior to

resuming

operation • Notification

that you ar e

resuming

operation §60.2225(b)

a This table is only a summary

, s ee the referenced sections

of the rule for the complete requirements.

Table 5 to Subpart CCCC of Part 60—Emission Limitations for

Incinerators That Commenced Construction After June 4,

2010, Or That Commenced Reconstruction or Modification

After [THE DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL

RULE IN THE FEDERAL REGISTER]

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And determining

compliance using

this method

Cadmium 0.0023

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 4 dry

standard cubic

meters per run) Performance test

(Method 29 at 40

CFR part 60,

appendix A-8 of

this part).

Use ICPMS for

the analytical

finish.

Carbon

monoxide 12 parts per

million by

dry volume 3- run average (1

hour minimum

sample time per

run) Performance test

(Method 10 at 40

CFR part 60,

appendix A-4).

Dioxin/furan

(Total Mass

Basis) 0.58

nanograms per

dry standard 3-run average

(collect a

minimum volume Performance test

(Method 23 at 40

CFR part 60,111

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And determining

compliance using

this method

cubic meter of 4 dry

standard cubic

meters per run) appendix A-7).

Dioxin/furan

(toxic

equivalency

basis) 0.13

nanograms per

dry standard

cubic meter 3-run average

(collect a

minimum volume

of 4 dry

standard cubic

meters per run) Performance test

(Method 23 at 40

CFR part 60,

appendix A-7).

Hydrogen

chloride 0.091 parts

per million

by dry volume 3-run average

(For Method 26,

collect a

minimum volume

of 360 liters

per run. For

Method 26A,

collect a

minimum volume

of 3 dry

standard cubic

meters per run) Performance test

(Method 26 or

26A at 40 CFR

part 60,

appendix A-8).

Lead 0.0019

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 4 dry

standard cubic

meters per run) Performance test

(Method 29 of

appendix A-8 at

40 CFR part 60 ).

Use ICPMS for

the analytical

finish.

Mercury 0.00084

milligrams 3-run average

(collect enough Performance test

(Method 29 or112

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And determining

compliance using

this method

per dry

standard

cubic meter volume to meet a

detection limit

data quality

objective of

0.03 ug/dry

standard cubic

meter) 30B at 40 CFR

part 60,

appendix A-8) or

ASTM D6784-

02(Reapproved

2008) b

.

Nitrogen

Oxides 23 parts per

million dry

volume 3-run average

(for Method 7E,

1 hour minimum

sample time per

run) Performance test

(Method 7 or 7E

at 40 CFR part

60, appendix A4).

Particulate

matter

(filterable) 18 milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 2 dry

standard cubic

meters per run) Performance test

(Method 5 or 29

at 40 CFR part

60, appendix A- 3

or appendix A-8

at 40 CFR part

60).

Sulfur

dioxide 11 parts per

million dry

volume 3- run average (1

hour minimum

sample time per

run) Performance test

(Method 6 or 6C

at 40 CFR part

60, appendix A4.

Fugitive ash Visible

emissions for

no more than

5 percent of

the hourly

observation Three 1-hour

observation

periods Visible emission

test (Method 22

at 40 CFR part

60, appendix A7).113

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And determining

compliance using

this method

period

a All emission limitations are measured at 7 percent

oxygen, dry basis at standard conditions. For

dioxins/furans, you must meet either the Total Mass Limit

or the toxic equivalency basis limit.

b Incorporated by reference, see §60.17.

c If you ar e conducting st a ck tests to demonstra te

compliance and your performance tests for this pollutan t

for at least 2 consecutive years show that your emissions

are at or below this limit, you can skip testing according

to §60.2155 if all of the other provision of §60.2155 are

met. For all other pollutants that do not contain a

footnote “c”, your performance t e sts for this pollutant fo r

at least 2 consecutive year s mus t show that your emission s

are at or 75 percent of this limit in order to qualify for

skip testing.

Table 6 to Subpart CCCC of Part 60—Emission Limitations for

Energy Recovery Units That Commenced Construction After

June 4, 2010, Or That Commenced Reconstruction or

Modification After [THE DATE 6 MONTHS AFTER PUBLICATION OF

THE FINAL RULE IN THE FEDERAL REGISTER]

For the air

pollutant You must meet this

emission

limitation a Using this

averaging

time And

determining

compliance

using this

method Liquid/Gas Solids114

For the air

pollutant You must meet this

emission

limitation a Using this

averaging

time And

determining

compliance

Cadmium 0.023

milligrams

per dry

standard

cubic meter Biomass -

0.00014

milligrams

per dry

standard

cubic meter 3-run

average

(collect a

minimum

volume of 4

dry

standard

cubic

meters per

run) Performance

test (Method

29 at 40 CFR

part 60,

appendix A- 8).

Use ICPMS for

the analytical

finish. Coal –

0.058

milligrams

per dry

standard

cubic meter

Carbon

monoxide 36 parts

per million

dry volume Biomass –

160 parts

per million

dry volume 3-run

average (1

hour

minimum

sample time

per run) Performance

test (Method

10 at 40 CFR

part 60,

appendix A- 4). Coal – 46

parts per

million dry

volume

Dioxins/furans

(Total Mass

Basis) No Total

Mass Basis

limit, must

meet the

toxic

equivalency

basis limit Biomass -

0.52

nanograms

per dry

standard

cubic

meter c 3-run

average

(collect a

minimum

volume of 4

dry

standard Performance

test (Method

23 at 40 CFR

part 60,

appendix A-7).115

For the air

pollutant You must meet this

emission

limitation a Using this

averaging

time And

determining

compliance

below Coal – 0.51

nanograms

per dry

standard

cubic

meter c cubic

meters)

Dioxins/furans

(toxic

equivalency

basis) 0.093

nanograms

per dry

standard

cubic

meter c Biomass -

0.076

nanograms

per dry

standard

cubic

meter c 3-run

average

(collect a

minimum

volume of 4

dry

standard

cubic

meters per

run) Performance

test (Method

23 of appendix

A-7 of this

part).

Coal -

0.075

nanograms

per dry

standard

cubic

meter c

Hydrogen

chloride 14 parts

per million

dry volume 0.50 parts

per million

dry volume 3-run

average

(For Method

26, collect

a minimum

volume of

360 liters

per run.

For Method

26A, Performance

test (Method

26 or 26A at

40 CFR part

60, appendix

A-8).116

For the air

pollutant You must meet this

emission

limitation a Using this

averaging

time And

determining

compliance

collect a

minimum

volume of 3

dry

standard

cubic

meters per

run)

Lead 0.096

milligrams

per dry

standard

cubic meter Biomass -

0.0019

milligrams

per dry

standard

cubic meter 3-run

average

(collect a

minimum

volume of 4

dry

standard

cubic

meters per

run) Performance

test (Method

29 at 40 CFR

part 60,

appendix A- 8).

Use ICPMS for

the analytical

finish. Coal -

0.0031

milligrams

per dry

standard

cubic meter

Mercury 0.00091

milligrams

per dry

standard

cubic

meter c 0.0020

milligrams

per dry

standard

cubic meter 3-run

average

(collect

enough

volume to

meet an instack

detection

limit data

quality Performance

test (Method

29 or 30B at

40 CFR part

60, appendix

A-8) or ASTM

D6784-02

(Reapproved

2008)b.117

For the air

pollutant You must meet this

emission

limitation a Using this

averaging

time And

determining

compliance

objective

of 0.03

ug/dscm)

Oxides of

nitrogen 76 parts

per million

dry volume Biomass –

290 parts

per million

dry volume 3-run

average

( for Method

7E, 1 hour

minimum

sample time

per run) Performance

test (Method 7

or 7E at 40

CFR part 60,

appendix A- 4). Coal – 340

parts per

million dry

volume

Particulate

matter

(filterable) 110

milligrams

per dry

standard

cubic meter Biomass -

5.1

milligrams

per dry

standard

cubic meter 3-run

average

(collect a

minimum

volume of 1

dry

standard

cubic meter

per run) Performance

test (Method 5

or 29 at 40

CFR part 60,

appendix A-3

or appendix A8) if the unit

has a design

capacity less

than 250

MMBtu/hr; or

PM CEMS118

For the air

pollutant You must meet this

emission

limitation a Using this

averaging

time And

determining

compliance

Coal - 86

milligrams

per dry

standard

cubic meter (performance

specification

11 of appendix

B and

procedure 2 of

appendix F of

this part) if

the unit has a

design

capacity equal

to or greater

than 250

MMBtu/hr. Use

Method 5 or 5I

of Appendix A

of this part

and collect a

minimum sample

volume of 1

dscm per test

run for the PM

CEMS

correlation

testing.

Sulfur dioxide 720 parts

per million

dry volume Biomass –

7.3 parts

per million

dry volume 3-run

average

( for Method

6, collect

a minimum

of 60

liters, for Performance

test (Method 6

or 6C at 40

CFR part 60,

appendix A-4.

Use a span gas

with a Coal – 650

parts per

million dry119

For the air

pollutant You must meet this

emission

limitation a Using this

averaging

time And

determining

compliance

volume Method 6C,

1 hour

minimum

sample time

per run) concentration

of 20 ppm or

less for a

biomass-fed

boiler.

Fugitive ash Visible

emissions

for no more

than 5

percent of

the hourly

observation

period Visible

emissions

for no more

than 5

percent of

the hourly

observation

period Three 1-

hour

observation

periods Visible

emission test

(Method 22 at

40 CFR part

60, appendix

A-7).

a All emission limitations are measured at 7 percent

oxygen, dry basis at standard conditions. For

dioxins/furans, you must meet either the Total Mass Basis

limit or the toxic equivalency basis limit.

b Incorporated by reference, see §60.17.

c If you ar e conducting st a ck tests to demonstra te

compliance and your performance tests for this pollutan t

for at least 2 consecutive years show that your emissions

are at or below this limit, you can skip testing according

to §60.2155 if all of the other provision of §60.2155 are

met. For all other pollutants that do not contain a

footnote “c”, your performance t e sts for this pollutant fo r

at least 2 consecutive year s mus t show that your emission s

are at or 75 percent of this limit in order to qualify for120

skip testing.

Table 7 to Subpart CCC C of Part 6 0—Emission Limitations fo r

Waste-burning Kilns That Commenced Construction After June

4, 2010, or Reconstructio n or M o dification After [THE DA TE

6 MONTHS AFTER PUBLICATION OF THE FINAL RULE IN THE FEDERAL

REGISTER]

For the air

pollutant You must meet

this emission

limitation a Using this

averaging

time And determining

compliance using

this method

Cadmium 0.00082

milligrams per

dry standard

cubic meter 3-run

average

(collect a

minimum

volume of 4

dry

standard

cubic

meters per

run) Performance test

(Method 29 at 40

CFR part 60,

appendix A- 8). Use

ICPMS for the

analytical finish.

Carbon

monoxide 90 (long

kilns) / 32 0

(preheater /

precalciner)

parts per

million dry

volume 3-run

average (1

hour

minimum

sample time

per run) Performance test

(Method 10 at 40

CFR part 60,

appendix A-4).

Dioxins/furans

(total mass 0.51 nanograms

per dry 3-run

average Performance test

(Method 23 at 40121

For the air

pollutant You must meet

this emission

limitation a Using this

averaging

time And determining

compliance using

this method

basis) standard cubic

meter b (collect a

minimum

volume of 4

dry

standard

cubic

meters per

run) CFR part 60,

appendix A-7).

Dioxins/furans

(toxic

equivalency

basis) 0.075

nanograms per

dry standard

cubic meter b 3-run

average

(collect a

minimum

volume of 4

dry

standard

cubic

meters) Performance test

(Method 23 at 40

CFR part 60,

appendix A-7).

Hydrogen

chloride 3.0 parts per

million dry

volume b 3-run

average (1

hour

minimum

sample time

per run) or

30-day

rolling

average if

HCl CEMS

are used Performance test

(Method 321 at 40

CFR part 63,

appendix A) or HCl

CEMS if a wet

scrubber is not

used.

Lead 0.0043

milligrams per 3-run

average Performance test

(Method 29 at 40122

For the air

pollutant You must meet

this emission

limitation a Using this

averaging

time And determining

compliance using

this method

dry standard

cubic meter (collect a

minimum

volume of 4

dry

standard

cubic

meters) CFR part 60,

appendix A- 8). Use

ICPMS for the

analytical finish.

Mercury 0.0037

milligrams per

dry standard

cubic meter 30-day

rolling

average Mercury CEMS or

sorbent trap

monitoring system

(performance

specification 12A

or 12B,

respectively, of

appendix B of this

part.)

Oxides of

nitrogen 200 parts per

million dry

volume 30-day

rolling

average NOx Continuous

Emissions

Monitoring System

(performance

specification 2 of

appendix B and

procedure 1 of

appendix F of this

part). Use a span

value of 400 ppm.

Particulate

matter

(filterable) 8.9 milligrams

per dry

standard cubic

meter 30-day

rolling

average PM Continuous

Emissions

Monitoring System

(performance123

For the air

pollutant You must meet

this emission

limitation a Using this

averaging

time And determining

compliance using

this method

specification 11

of appendix B and

procedure 2 of

appendix F of this

part)

Sulfur dioxide 130 parts per

million dry

volume 30-day

rolling

average Sulfur dioxide

Continuous

Emissions

Monitoring System

(performance

specification 2 of

appendix B and

procedure 1 of

appendix F of this

part). Use a span

value of 260 ppm.

a All emission limitations are measured at 7 percent

oxygen, dry basis at standard conditions. For

dioxins/furans, you must meet either the total mass basis

limit or the toxic equivalency basis limit.

b If you ar e conducting st a ck tests to demonstra te

compliance and your performance tests for this pollutan t

for at least 2 consecutive years show that your emissions

are at or below this limit, you can skip testing according

to §60.2155 if all of the other provision of §60.2155 are

met. For all other pollutants that do not contain a

footnote “b”, your performance t e sts for this pollutant fo r

at least 2 consecutive year s mus t show that your emission s

are at or 75 percent of this limit in order to qualify for

skip testing.124

Table 8 to Subpart CCC C of Part 6 0—Emission Limitations fo r

Small, Remote Incinerators That Commenced Construction

After June 4, 2010, Or Tha t C o mmenced Reconstruction or

Modification After (THE DAT E 6 M ONTHS AFTER PUBLICATION OF

THE FINAL RULE IN THE FEDERAL REGISTER]

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And

determining

compliance

using this

method

Cadmium 0.61

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

1 dry standard

cubic meter per

run) Performance

test (Method

29 at 40 CFR

part 60,

appendix A8).

Carbon

monoxide 12 parts per

million dry

volume 3-run average (1

hour minimum

sample time per

run) Performance

test (Method

10 at 40 CFR

part 60,

appendix A4).

Dioxins/furans

(total mass

basis) 1,200

nanograms per

dry standard

cubic meter 3-run average

(collect a

minimum volume of

1 dry standard

cubic meter per

run) Performance

test (Method

23 at 40 CFR

part 60,

appendix A7).

Dioxins/furans 31 nanograms 3-run average Performance125

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And

determining

compliance

using this

method

(toxic

equivalency

basis) per dry

standard

cubic meter (collect a

minimum volume of

1 dry standard

cubic meter per

run) test (Method

23 at 40 CFR

part 60,

appendix A7).

Hydrogen

chloride 200 parts per

million by

dry volume 3-run average

(For Method 26,

collect a minimum

volume of 60

liters per run.

For Method 26A,

collect a minimum

volume of 1 dry

standard cubic

meter per run) Performance

test (Method

26 or 26A at

40 CFR part

60, appendix

A-8).

Lead 0.26

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

1 dry standard

cubic) Performance

test (Method

29 at 40 CFR

part

60,appendix

A-8). Use

ICPMS for the

analytical

finish.

Mercury 0.0035

milligrams

per dry

standard 3-run average

(For Method 29

and ASTM D6784- 02

(Reapproved Performance

test (Method

29 or 30B at

40 CFR part126

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And

determining

compliance

using this

method

cubic meter 2008) b

, collect a

minimum volume of

2 dry standard

cubic meters per

run. For Method

30B, collect a

minimum volume as

specified in

Method 30B at 40

CFR part 60,

appendix A) 60, appendix

A-8) or ASTM

D6784-02

(Reapproved

2008) b

.

Oxides of

nitrogen 78 parts per

million dry

volume 3-run average

(for Method 7E, 1

hour minimum

sample time per

run) Performance

test (Method

7 or 7E at 40

CFR part 60,

appendix A4).

Particulate

matter

(filterable) 230

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 at 40

CFR part 60,

appendix A-3

or appendix

A-8).

Sulfur dioxide 1.2 parts per

million dry

volume 3-run average (1

hour minimum

sample time per

run) Performance

test (Method

6 or 6c at 40

CFR part 60,127

For the air

pollutant You must meet

this emission

limitation a Using this

averaging time And

determining

compliance

using this

method

appendix A-4.

Fugitive ash Visible

emissions for

no more than

5 percent of

the hourly

observation

period Three 1-hour

observation

periods Visible

emission test

(Method 22 at

40 CFR part

60, appendix

A-7).

a All emission limitations (except for opacity) are

measured at 7 percent oxygen, dry basis at standard

conditions. For dioxins/furans, you must meet either the

total mass basis limit or the toxic equivalency basis

limit.

b Incorporated by reference, see §60.17.

Subpart DDDD—Emissions Guidelines and Compliance Times for

Commercial and Industrial Solid Waste Incineration Units

that Commenced Construction On or Before November 30, 1999

Introduction

§60.2500 What is the purpose of this subpart?

This subpart establishes emission guidelines and

compliance schedules for the c ontrol of emissions fro m

commercial and industrial solid waste incineration (CISWI)

units. The pollutants addr e ssed by these emission

guidelines are listed in table 2 of this subpart and tables128

6 through 9 of this subpart

. These emission guidelines are

developed in accordance with sec t ions 111(d) and 129 o f th e

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 stat e or Unit e d States protectorate wit h

one or more existing CISWI units that commenced

construction on or before Nov e mber 30, 1999 meets th e

criteria in paragraphs (b) throu g h (d) of this section

, yo u

must submit a s S tat e plan t o U. S

. Environmental Protectio n

Agency (EPA) that implements the emission guidelines

contained in this subpart.

(b) You must submit the s S tate plan to EPA by

December 3, 2001 for incinerator units that commenced

construction on or before November 30, 1999 and that were

not modified or reconstructed after June 1, 2001.

(c) You must submit a state plan that meets th e

requirements of this subpar t and contains the more

stringent emission limit for the respective pollutant i n

table 6 of this subpart or table 1 of subpart CCCC of this

part to EPA by [THE DATE 1 YEA R AFTER PUBLICATION OF THE

FINAL RULE IN THE FEDERAL REGIS T ER] for incinerators tha t

commenced construction after N o vember 30, 1999, but n o

later than June 4, 2010, or commenced modification o r

reconstruction after June 1, 20 0 1 but no later tha n [TH E

DATE 6 MONTHS AFTER PUBLICATION OF THE FINAL RULE IN THE

FEDERAL REGISTER].

(d) You must submit a state p l an to EPA that meets

the requirements of thi s subpar t and contains th e emissio n

limits in tables 7 through 9 of t his subpart by [INSERT TH E

DATE 1 YEAR AFTER PUBLICATION OF THE FINAL RULE IN THE

FEDERAL REGISTER] for CISWI units other than incinerato r129

units that commenced construct i on on or befor e June 4,

2010.

§60.2510 Is a State plan required for all states?

No. You are not required to s u bmit a State plan if

there are no existing CISWI units in your state, and you

submit a negative declaration le t ter in place of th e Stat e

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) o f this section in your Stat e

plan.

(1) Inventory of affecte d C I SWI units, including

those that have cease d opera t ion but have no t bee n

dismantled.

(2) Inventory o f emissions fro m affected CISWI uni ts

in your state.

(3) Compliance schedules fo r each affected CISW I

unit.

(4) Emission limitations, operator training and

qualification requirements, a waste management plan, and

operating limits for affected CI S WI units that are a t leas t

as protective as th e emission g u idelines contained in th is

subpart.

(5) Performance testing, recordkeeping, and reporting

requirements.

(6) Certification that th e hear i ng on the State pla n

was held, a lis t of witnesse s and their organization al

affiliations, if any, appearing a t the hearing, and a brie f130

written summary of each presentation or written submission.

(7) Provision for State progress reports to EPA.

(8) Identification of enforceable State mechanisms

that you selected fo r implement i ng the emission guideline s

of this subpart.

(9) Demonstration o f your Stat e 's legal authority to

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

(b) Your State plan may deviate from the format and

content of the emission guid e lines contained in thi s

subpart. However, if you r St a te plan does deviate i n

content, you must demonstrate t h at your State plan i s a t

least as protective as the emiss i on guidelines contained i n

this subpart. You r State pla n must address regulato ry

applicability, increments of progress for retrofit,

operator training and qualification, a waste management

plan, emission limitations, performance testing, operating

limits, monitoring, recordkeeping and reporting, and air

curtain incinerator requirements.

(c) You must follow the requirements of subpart B of

this part (Adoption and Submittal of State Plans for

Designated Facilities) in your State plan.

§60.2520 Is there an approval process for my State plan?

Yes. The EPA will revie w your S s t ate plan according t o

§60.27.

§60.2525 What if my State plan is not approvable?

(a) If you do not submit an approvable s S tate plan

(or a negative declaration lette r ) by December 2, 2002

, EP A131

will develop a f F ederal pla n according to §60.27 t o

implement the emission guidelines contained in this

subpart. Owners and operators of CISWI units not covered

by an approved s S tate pla n mus t comply with the f F edera l

plan. The f F ederal plan is an i nterim action and will b e

automatically withdrawn when your S s tate plan is approved.

(b) If you do not submit an approvable state plan (or

a negative declaration letter) to EPA that meets the

requirements of this subpart a nd contains the emissio n

limits in tables 6 through 9 of this subpart for CISWI

units that commenced construct i on on or befor e June 4,

2010, then EPA will develo p a federal plan according t o

§60.27 to implement the emission guidelines contained i n

this subpart. Owners and oper a tors of CISWI units no t

covered by an approved state plan must comply with the

federal plan. The federal pla n is an interim action an d

will be automatically withdraw n when your state plan i s

approved.

§60.2530 Is there an approva l process for a negative

declaration letter?

No. The EPA has no formal review process for negative

declaration letters. Once your negative declaration letter

has been received, EPA will place a copy in the public

docket and publish a notice in the FEDERAL REGISTER

. If,

at a later date, an existing C I SWI unit is found in your

state, the F f ederal plan implementing the emission

guidelines contained in this subpart would automatically

apply to that CISWI uni t un t il your s S tate plan i s

approved.

§60.2535 What compliance schedule must I include in m y

State plan?

(a) For CISWI units in the incinerator subcategory

that commenced construction on o r before November 30, 1999

,132

Y y our State plan mus t include compliance schedules tha t

require CISWI units to achi e ve final compliance as

expeditiously as practicable af t er approval of the s S tate

plan but not later than the earlier of the two dates

specified in paragraphs (a)(1) and (2) of this section.

(1) December 1, 2005.

(2) Three years afte r the eff e ctive date of s S tat e

plan approval.

(b) For CISWI units in the incinerator subcategory

that commenced construction afte r November 30, 1999, but o n

or before June 4, 2010, and for CISWI units in the energ y

recovery units and waste-burning kilns subcategories that

commenced construction before Ju n e 4, 2010, your state pla n

must include compliance schedule s that require CISW I unit s

to achieve final compliance as e x peditiously as practicabl e

after approval of the state plan but not later than the

earlier of the two date s specifi e d in paragraphs (b)(1) an d

(b)(2) of this section.

(1) [INSERT THE DAT E 5 YEARS AFTER PUBLICATION O F

THE FINAL RULE IN THE FEDERAL REGISTER].

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

approval.

(c) For CISWI units in the small remote incinerator

subcategory that commenced construction after November 30,

1999, but on or before June 4, 2 010, your state plan mus t133

include compliance schedules that require small remote

incinerator CISWI units to ac h ieve final compliance a s

expeditiously as practicable after approval of the stat e

plan but not later than the earlier of the two dates

specified in paragraphs (b)(1) and (b)(2) of this section.

(1) March 21, 2016.

(2) 3 years after th e effectiv e date of state pla n

approval.

(d) (b) For complianc e schedul e s more than 1 yea r

following the effective date of s S tate plan approval,

s S tate plans must includ e dates for enforceable increment s

of progress as specified in §60.2580.

§60.2540 Are there any sS tat e plan requirements for thi s

subpart that apply instead of th e requirements specified i n

subpart B?

Yes. Subpart B establishes ge n eral requirements for

developing and processing section 111(d) plans. This

subpart applies instead of th e r e quirements in subpart B o f

this part for paragraphs (a) and (b) of this section:

(a) State plans developed to i mplement this subpar t

must be as protectiv e as th e em i ssion guidelines containe d

in this subpart. State plans must require all CISWI units

to comply by December 1, 2005 or 3 years after the

effective date of stat e plan ap p roval, whichever is soon er

the dates specified in §60.2535. This applies instead of

the option for case-by-case less stringent emission

standards and longer compliance schedules in §60.24(f).

(b) State plans developed to i mplement this subpar t134

are required to include tw o incr e ments of progress for th e

affected CISWI units. Thes e two minimum increments are th e

final control plan submittal dat e and final compliance dat e

in §60.21(h)(1) and (5). Thi s applies instead of th e

requirement of §60.24(e)(1) that would require a State pla n

to include all five increment s of progress for all CISW I

units.

§60.2541 In lieu of a state plan submittal, are there

other acceptable option(s) for a state to meet it s Clea n

Air Act section 111(d)/129(b)(2) obligations?

Yes, a state may mee t its C l ean Air Act sectio n

111(d)/129 obligations by submitting an acceptable written

request for delegation of the federal plan that meets the

requirements of this section. Th i s is the only othe r optio n

for a state to meet its Clean Air Act section 111(d)/129

obligations.

(a) An acceptable federal plan d e legation request mus t

include the following:

(1) A demonstration of adequate resources and lega l

authority to administer and enforce the federal plan.

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

(3) Certification that the h e aring on the stat e

delegation request, similar to t h e hearing for a stat e pla n

submittal, was held, a lis t of witnesses an d thei r

organizational affiliations, if any, appearing at the

hearing, and a brief written su m mary of each presentatio n

or written submission.135

(4) A commitment to enter i n to a Memorandum o f

Agreement with the Regional Administrator who sets fort h

the terms, conditions, and effec t ive date of the delegatio n

and that serves as th e mecha n ism for the transfer o f

authority. Additional guidance a n d information is give n i n

EPA’s Delegation Manual, Item 7-139, Implementation and

Enforcement of 111(d)(2) and 111(d)/(2)/129(b)(3) federal

plans.

(b) A state with an already approved CISWI Clean Air

Act section 111(d)/129 state p l an is not precluded fro m

receiving EPA approval o f a d e legation request for t he

revised federal plan, providing the requirements of

paragraph (a) of this section a r e met, and at the time o f

the delegation request, th e sta t e also requests withdrawa l

of EPA’s previous state plan approval.

(c) A state’s Clea n Air Ac t section 111(d)/12 9

obligations are separate from it s obligations under Title V

of the Clean Air Act.

§60.2542 What authorities wil l n ot be delegated to state

, local, or tribal agencies?

The authorities listed under §6 0 .2030(c) will not be

delegated to state, local, or tribal agencies.

§60.2545 Does this subpart directly affect CISWI unit

owners and operators in my state?136

(a) No. This subpart does not directly affect CISWI

unit owners and operators i n y o ur state. However, CISW I

unit owners and operators must comply with the State plan

you develop to implemen t the em i ssion guidelines containe d

in this subpart. States may choose to incorporate the

model rule text directly in their s S tate plan.

(b) If you do not submit an approvable plan to

implement and enforce the gui d elines contained in thi s

subpart for CISWI unit s that co m menced construction befor e

November 30, 1999 by December 2, 2002, the EPA will

implement and enforce a Federal plan, as provided in

§60.2525, to ensure that eac h un i t within your State stat e

reaches compliance with al l the provisions of this subpa rt

by December 1, 2005.

(c) If you do not submit an approvable plan to

implement and enforce the gui d elines contained in thi s

subpart by [INSERT THE DATE 1 YEAR AFTER PUBLICATION OF THE

FINAL RULE IN THE FEDERAL REGISTER] on or before June 4,

2010, EPA will implement an d e n force a federal plan, a s

provided in §60.2525, to ensur e t hat each unit within you r

state that commenced construct i on on or befor e June 4,

2010, reaches compliance with all the provisions of this

subpart by [INSERT THE DAT E 5 Y EARS AFTER PUBLICATION O F

THE FINAL RULE IN THE FEDERAL REGISTER].

Applicability of State Plans

§60.2550 What CISWI units mus t I address in my S s tat e

plan?

(a) Your s S tat e plan mus t addr e ss incineration unit s

that meet all three criteria des c ribed in paragraphs (a)(1 )

through (3) of this section.

(1) Incineration units in you r State that commence d137

construction on or before June 4, 2010 November 30, 1999

.

(2) Incineration units tha t mee t 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 o f a CISWI unit makes

changes that meet th e defin i tion of modification o r

reconstruction on or after Jun e 1, 2001, the CISW I uni t

becomes subject to subpart CCCC of this part and the State

plan no longer applies to that unit.

(c) If the owner or operator o f a CISWI unit makes

physical or operational changes to an existing CISWI uni t

primarily to comply with your State plan, subpart CCCC of

this part does no t apply t o that unit. Such change s do n ot

qualify as modifications or reconstructions under subpart

CCCC of this part.

§60.2555 What combustion units are exempt from my Stat e

plan?

This subpart exempts fifteen the types of unit s

described in paragraphs (a)

, (c) through (i), (m) and ( o n )

of this section

, but som e unit s are required to provid e

notifications. Air curtain incinerators are exempt fro m

the requirements in thi s subpar t except for th e provision s

in §§60.2805, 60.2860, and 60.2870

.

(a) Pathological waste incineration units

.

Incineration units burning 90 pe r cent or more by weigh t (o n

a calendar quarter basis and excluding the weight of

auxiliary fuel and combustion a i r) of pathological waste,

low-level radioactive waste, and/or chemotherapeutic waste

as defined in §60.2875 are not subject to this subpart if138

you meet the two requirements specified in paragraphs

(a)(1) and (2) of this section.

(1) Notify th e Administrator that the unit mee ts

these criteria.

(2) Keep records on a calendar quarter basis of the

weight of pathological waste, low-level radioactive waste,

and/or chemotherapeutic waste bu r ned, and the weight of al l

other fuels and wastes burned in the unit.

(b) [Reserved]

(b) Agricultural waste incineration units.

Incineration units burning 90 pe r cent or more by weigh t (o n

a calendar quarter basis and exc luding the weight of

auxiliary fuel and combustion a i r) 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 thes e

criteria.

(2) Keep records on a calendar quarter basis of th e

weight of agricultural waste bur n ed, and the weight o f al l

other fuels and wastes burned in the unit.

(c) Municipal waste combustion units

. Incineration

units that meet ei ther o f the two criteria specified i n

paragraphs (c)(1) or (2) of thi s section (1) are regulate d

under subject to subpart Ea o f this part (Standards o f

Performance for Municipal Wast e Combustors); subpart Eb o f

this part (Standards o f Perfor m ance for Large Municipa l

Waste Combustors for Which Construction is Commenced After

September 20, 1994 ); subpar t C b of this par t (Emissio n

Guidelines and Compliance Time for Large Municipal139

Combustors that are Constructed o n or Before September 20,

1994 ); subpart AAAA o f this par t (Standards of Performan ce

for New Stationary Sources ; Small Municipal Waste

Combustion Units); or subpart B B BB of this part (Emissio n

Guidelines for Existing Stationary Sources: Small Municipal

Waste Combustion Units).

(2) Burn greater than 30 per cen t municipal solid waste

or refuse

- derived fuel, as defi n ed in subpart Ea, subpar t

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 soli d waste or refuse

- derived fue l, i f

you meet the two requirements i n paragraphs (c)(2)(i) an d

(ii) of this section.

(i) Notify the Administrator tha t the unit meets thes e

criteria.

(ii) Keep records on a calendar quarter basis of the

weight of municipal solid waste burned, and the weig ht of

all other fuels and wastes burned in the unit.

(d) Medical waste incineration units. Incineration

units regulated under subpart E c of this part (Standards o f

Performance for Hospital/Medical/Infectious Waste

Incinerators for Which Construct i on is Commenced After Jun e

20, 1996) or subpart Ca of this part (Emission Guidelines

and Compliance Times for Hospital/Medical/Infectious Waste

Incinerators).

(e) Small powe r production f a cilities. Units tha t

meet the three requirement s spe c ified in paragraphs (e)(1 )

through (3) of this section.

(1) The unit qualifies as a small power-production140

facility under section 3(17)(C) of the Federal Power Act

(16 U.S.C. 796(17)(C)).

(2) The unit burns homogeneou s waste (not includin g

refuse-derived fuel) to produce electricity.

(3) You notify submi t a reques t to the Administrato r

for a determination that the qualifying cogeneration

facility is combusting homogeno u s waste as that term i s

defined in §60.2875. unit meets a l l of these criteria. Th e

request must include information sufficient to document

that the unit meets the criteria of the definition of a

small power production facility a nd that the waste materia l

the unit is proposed to burn is homogeneous.

(f) Cogeneration facilities. Units that meet th e

three requirements specified in paragraphs (f)(1) through

(3) of this section.

(1) The unit qualifies a s a cogeneration facility

under section 3(18)(B) of th e Fe d eral Power Act (16 U.S.C

.

796(18)(B)).

(2) The unit burns homogeneou s waste (not includin g

refuse-derived fuel) to produce electricity and steam o r

other forms of energy use d f o r industrial, commercial,

heating, or cooling purposes.

(3) You m ust notif y submi t a request to th e

Administrator for a determination that the qualifying

cogeneration facility is combusting homogenous waste as

that term is defined §60.2875 unit meets all of these

criteria

. The reques t must inc l ude information sufficien t

to document that the unit meets the criteria of the

definition of a cogeneration facility and that the waste

material the unit is proposed to burn is homogeneous.141

(g) Hazardous waste combustion u nits

. Units that mee t

either of the two criteri a speci f ied in paragraph (g)(1) o r

(2) of this section for which y ou are required t o get a

permit under section 3005 of the Solid Waste Disposal Act.

(1) Units for which you are required to get a permit

under section 3 005 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).

(h) Materials recovery units. Un i ts that combust wast e

for the primary purpose of r e covering metals, such a s

primary and secondary smelters.

(i) Air curtai n incinerat o rs. Air curtai n

incinerators that burn onl y the materials listed i n

paragraphs (i)(1) through (3 ) o f this section ar e onl y

required to meet the require m ents under “Air Curtai n

Incinerators” (§§60.2810 through 60.2870).

(1) 100 percent wood waste.

(2) 100 percent clean lumber.

(3) 100 percent mixtur e of o n ly wood waste, clea n

lumber, and/or yard waste.

(j) [Reserved] Cyclonic barrel burners. (See §60.2875)

(k) [Reserved] Rack, part, and d r um reclamation units

.

(See §60.2875)142

(l) [Reserved] Cement kilns. K ilns regulated under

subpart LLL of part 63 of this chapter (National Emission

Standards for Hazardous Air Pollutants from the Portlan d

Cement Manufacturing Industry).

(m) Sewage sludge incinerat o rs treatment plants

.

Incineration units regulated un d er subpart O of this par t

(Standards of Performance for Sewage Treatment Plants).

(n) Sewage sludge incineration units. Incineration

units combusting sewage sludg e f o r the purpose o f reducin g

the volume of the sewage slud g e by removing combustibl e

matter that are subject t o s u bpart LLLL of this par t

(Standards of Performance for Sewage Sludge Incineration

Units) or subpart MMMM of this part (Emission Guidelines

for Sewage Sludge Incineration Units).

Chemical recovery units. Combustion u n its burning materials t o

recover chemical constituents o r to p r oduce chemical compounds whe re

there is an existing commercia l mark e t for such recovered chemica l

constituents or compounds. The seve n types of units described i n

paragraphs (n)(1) through (7) o f this section are considered chemica l

recovery units.

(1) Units burning onl y pulping liquor s ( i.e., black liquor ) tha t

are reclaimed in a pulping liq uor recovery process and reused in th e

pulping process.

(2) Units burning onl y spent sulfuri c a c id used to produc e virgi n

sulfuric acid.

(3) Units burning only wood or coal feedstock for the production

of charcoal.

(4) Units burning onl y manufacturing b ypr oduct streams/residue s

containing catalyst metals whic h are r e claimed and reused a s catalyst s

or used to produce commercial grade catalysts.143

(5) Units burning only cok e to produc e purified carbon monoxid e

that is used as a n intermediate in t h e production of other chemic al

compounds.

(6) Units burning only hydrocarbo n liq u ids or solids to produc e

hydrogen, carbon monoxide, synthesi s g as, or other gase s for us e i n

other manufacturing processes.

(7) Units burning only photographic film to recover silver.

(o) Laboratory Analysis Units. Units that burn samples o f

materials for the purpose of chemical or physical analysis.

§60. 2558 What if a chemica l r e covery unit is not liste d

in §60.2555(n)?

(a) If a chemical recovery unit i s not l isted in §60.2555(n), th e

owner or operator of the unit can petition the Administrator to add th e

unit to the list. The petition must contain the six items in paragraph s

(a)(1) through (6) of this section.

(1) A description of the source of the materials being burned.

(2) A descrip tion o f the compositio n of the material s bein g

burned, highlighting the chemical cons t ituents in these materials tha t

are recovered.

(3) A description (includin g a proce s s flow diagram) o f th e

process in which th e materials are b urned, highlighting the typ e,

design, and operation of the equipment used in this process.

(4) A description (includin g a proce s s flow diagram) o f th e

chemical constituent recovery process, highlighting the type, design

,

and operation of the equipment used in this process.

(5) A des cription of the commercial m arkets for the recovered

chemical constituents and their use.144

(6) The composition o f the recovere d chemical constituents an d

the composition of thes e chemical cons t ituents as they ar e bought a nd

sold in commercial markets.

(b) U ntil the Administrator appro v es your petition, th e

incineration unit is covered by this subpart.

(c) If a petitio n is approved, th e Administrator will amen d

§60.2555(n) to add the unit to the list of chemical recovery units.

Use of Model Rule

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

(a) The model rule is the portion of these emission

guidelines (§§60.2575 through 60.2875) that addresses the

regulatory requirements applica b le to CISWI units

. Th e

model rule provides these requirements in regulation

format. You must develop a State plan that is at least as

protective as the model rule. Y ou may use the model rul e

language as part of you r State p lan. Alternative languag e

may be used i n your Stat e plan i f you demonstrate tha t th e

alternative language is at leas t as protective as the mode l

rule contained in this subpart.

(b) In the model rule of §§60.2575 to 60.2875, “you”

means the owner or operator of a CISWI unit.

§60.2565 How does the model r u le relate to the require d

elements of my State plan?

Use the model rule to sati s fy the State pla n

requirements specified in §60.2515(a)(4) and (5).

§60.2570 What are the princip a l components of the model

rule?

The model rule contains the el e ven major components145

listed in paragraphs (a) through (k) of this section.

(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 increments

of progress and achieving final compliance?

If you plan to achiev e complia n ce more than 1 yea r

following the effective date of State plan approval, you

must meet the two increments of progress specified i n

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 progress?146

Table 1 of this subpart specifie s compliance dates fo r

each of the increments of progress.

§60.2585 What must I includ e in the notifications o f

achievement of increments of progress?

Your notification of achievement of increments of

progress must include the t h ree items specified in

paragraphs (a) through (c) of this section.

(a) Notification that the incr e ment 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 CISWI

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 after the

compliance date for the increment.

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

If you fail to meet an increment of progress, you must

submit a notification to the Administrator postmarked

within 10 business days after the date for that increment

of progress in table 1 of this subpart. You must inform

the Administrator that you di d n o t meet the increment, an d

you must continue t o submi t reports each subsequen t

calendar month until the increment of progress is met.

§60.2600 How do I comply with the increment of progres s

for submittal of a control plan?147

For your control pla n increment of progress, you mu st

satisfy the two requirements specified in paragraphs (a )

and (b) of this section.

(a) Submit the final control plan that includes the

five items described in paragraphs (a)(1) through (5) of

this section.

(1) A description o f the devi c es for air pollution

control and process changes th a t you will use t o compl y

with the emission limitation s a nd other requirements o f

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 petit i on for site-specifi c

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 progres s

for achieving final compliance?

For the final compliance increment of progress, yo u

must complete all process change s and retrofit constructio n

of control devices, as specifie d in the final control plan

,

so that, if the affected CISWI unit is brought online, all

necessary process changes and ai r pollution control device s

would operate as designed.

§60.2610 What must I do if I c l ose my CISWI unit and the n

restart it?148

(a) If yo u close you r CISWI un i t but will restar t i t

prior to the final compliance date in your State plan, you

must meet the increments of progress specified in §60.2575.

(b) If yo u close you r CISWI un i t but will restar t i t

after your final complianc e date, you must complet e

emission control retrofits and meet the emission

limitations and operating limi t s on the dat e your un it

restarts operation.

§60.2615 What must I do if I plan to permanently close my CISWI uni t

and not restart it?

If you plan to clos e your CI S WI unit rather tha n

comply with the Stat e plan, sub m it a closure notificatio n,

including the date of closure

, t o the Administrator by th e

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 tha t

identifies both the feasibilit y and the methods used t o

reduce or separate certain comp o nents of solid waste fro m

the waste stream in order to reduce or eliminate toxic

emissions from incinerated waste.

§60.2625 When must I submit my waste management plan?

You must submit a wast e manageme n t plan no later tha n

the date specified in table 1 of this subpart for submittal

of the final control plan.

§60.2630 What should I inclu d e in my wast e managemen t

plan?

A waste management pla n must in c lude consideration o f149

the reduction or separation of waste-stream elements such

as paper, cardboard, plastics, g l ass, batteries, or metals ;

or the use of recyclable materials. The plan must identify

any additional waste management measures, and the sourc e

must implement those measures considered practical and

feasible, based on the effectiveness of waste managemen t

measures already in place, t he costs of additional

measures, the emissions reductio n s expected to be achieved

,

and any other environmental or energy impacts they might

have.

Model Rule—Operator Training and Qualification

§60.2635 What are the operator training and qualification

requirements?

(a) No CISWI unit can be operated unless a fully

trained and qualified CISWI unit operator is accessible

,

either at the facility or can b e at the facility within 1

hour. The trained an d qualifi e d CISWI unit operator ma y

operate the CISWI unit directl y o r be the direct superviso r

of one or more other plant personnel who operate the unit.

If all qualified CISWI unit ope r ators are temporarily no t

accessible, you must follow the procedures in §60.2665.

(b) Operator training and qualification must be

obtained through a state-approve d program or b y completin g

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 element s des c ribed in paragraphs (c)(1 )

through (3) of this section.

(1) Training on the eleve n subjects listed i n

paragraphs (c)(1)(i) through (xi) of this section.150

(i) Environmental concerns, including types of

emissions.

(ii) Basic combustion principles, including products

of combustion.

(iii) Operation of the specifi c type of incinerato r

to be used by th e operator, incl u ding proper startup, wast e

charging, and shutdown procedures.

(iv) Combustion controls and monitoring.

(v) Operation o f air pollutio n control equipment an d

factors affecting performance (if applicable).

(vi) Inspection and maintenance of the incinerato r

and air pollution control devices.

(vii) Actions to prevent and c o rrect malfunctions or

to prevent conditions that may lead to malfunction s

.

(viii) Bottom an d fly as h characteristics an d

handling procedures.

(ix) Applicable Federal, State, and local

regulations, including Occupational Safety and Health

Administration workplace standards.

(x) Pollution prevention.

(xi) Waste management practices.

(2) An examination designed an d administered by th e

instructor.

(3) Written materia l coverin g the training cours e

topics that can serve as reference material following

completion of the course.151

§60.2640 When must the operator training course be

completed?

The operator training cours e mus t be completed b y th e

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 t h e CISWI unit or assume s

responsibility for supervising t he operation of the CISWI

unit.

§60.2645 How do I obtain my operator qualification?

(a) You mus t obtain opera t or qualification b y

completing a training course that satisfies the criteri a

under §60.2635(b).

(b) Qualification is valid from the date on which the

training course is complete d an d the operator successfull y

passes the examination required under §60.2635(c)(2).

§60.2650 How do I maintain my operator qualification?

To maintain qualification, you m u st complete an annua l

review or refresher course cover i ng, at a minimum, th e fiv e

topics described in paragraph s (a) through (e) o f thi s

section.

(a) Update of regulations.

(b) Incinerator operation, including startup and

shutdown procedures, waste charging, and ash handling.152

(c) Inspection and maintenance.

(d) Prevention and correction of Responses to

malfunctions or conditions that may lead to malfunction.

(e) Discussion of operating p r oblems encountered by

attendees.

§60.2655 How do I renew my lapsed operator qualification?

You must renew a lapsed operato r qualification by o ne

of the two methods specified in paragraphs (a) and (b) of

this section.

(a) For a lapse of less tha n 3 years, you mus t

complete a standard annual refresher course described i n

§60.2650.

(b) For a lapse o f 3 year s or more, you must repe at

the initial qualification requirements in §60.2645(a).

§60.2660 What site-specific documentation is required?

(a) Documentation must be avai l able at the facilit y

and readily accessible for all CISWI unit operators that

addresses the ten topic s descr i bed in paragraphs (a)(1 )

through (10) of this section

. You must maintain thi s

information and the trainin g re c ords required by paragrap h

(c) of this section in a manne r that they can be readily

accessed and are suitable for inspection upon request.

(1) Summary of the applicable standards under this

subpart.

(2) Procedures fo r receiving, h andling, and chargin g

waste.

(3) Incinerator startup, shutdown, and malfunction153

procedures.

(4) Procedures fo r maintaining proper combustion ai r

supply levels.

(5) Procedures for operatin g the incinerator an d

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 o f the waste s burned during th e

performance test.

(b) You must establis h a prog r am for reviewing th e

information listed in paragraph (a) of this section with

each incinerator operator.

(1) The initial review of the information listed in

paragraph (a) of this section must be conducted by the

later of the thre e dates specif i ed 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 afte r being a s signed to operate th e

CISWI unit.154

(2) Subsequent annual review s of the informatio n

listed in paragraph (a) of this section must be conducted

no later than 12 months following the previous review.

(c) You mus t also maintai n the information specifie d

in paragraphs (c)(1) through (3) of this section.

(1) Records showing th e names o f CISWI unit operator s

who have completed review of th e information in §60.2660(a)

as required by §60.2660(b), i n cluding the date of th e

initial review and all subsequent annual reviews.

(2) Records showing th e names o f the CISWI operator s

who have completed the operator t raining requirements unde r

§60.2635, met the criteria for qualification under

§60.2645, and maintained or renewed their qualification

under §60.2650 or §60.2655. Records must include

documentation of training, th e dates of th e initia l

refresher training, and the dates of their qualificatio n

and all subsequent renewals of such qualifications.

(3) For each qualified opera t or, the phone and/o r

pager number at which the y can b e reached during operatin g

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 fac i lity and not able to b e a t

the facility within 1 hour), yo u must meet one of the tw o

criteria specified in paragraphs (a) and (b) of this

section, depending on the length of time that a qualified

operator is not accessible.

(a) When all qualified operato r s are not accessibl e

for more than 8 hours, but les s than 2 weeks

, the CISW I155

unit may be operated b y other pl a nt personnel familiar wit h

the operation of the CISWI unit who have completed a review

of the information specified in § 60.2660(a) within the pas t

12 months. However, you must record the period when all

qualified operators were not accessible and include thi s

deviation in the annual report as specified under §60.2770.

(b) When all qualified operato r s are not accessibl e

for 2 weeks o r more, yo u must ta k e the two action s that a re

described in paragraphs (b)(1) and (2) of this section.

(1) Notify the Administrator of this deviation i n

writing within 10 days. In the notice, state what caused

this deviation, what you are doing to ensure that a

qualified operator is accessibl e

, and when you anticipate

that a qualified operator will be accessible.

(2) Submit a statu s report to t h e Administrator ever y

4 weeks outlining what you are doing to ensure that a

qualified operator is accessible, stating when you

anticipate that a qualified oper a tor will be accessible an d

requesting approval from the Administrator to continue

operation of the CISWI unit. You must submit the first

status report 4 weeks afte r you n otify the Administrator o f

the deviation under paragraph (b)(1) of this section. If

the Administrator notifies yo u that your reques t t o

continue operation of the CISWI unit is disapproved, the

CISWI unit may continue operati o n for 90 days, the n mus t

cease operation. Operation of the unit may resume if you

meet the two requirement s in pa r agraphs (b)(2)(i) and (i i)

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 operation.156

Model Rule—Emission Limitations and Operating Limits

§60.2670 What emission limita t ions must I mee t and b y

when?

You must meet the emission lim i tations specified in

table 2 of this subpart on the date the initial performance

test is required or completed (whichever is earlier).

(a) You must meet the emission limitations for each

CISWI unit, including bypass stack or vent, specified in

table 2 of this subpart or tables 6 through 9 of thi s

subpart by the final complianc e date under the approve d

state plan, federal plan

, or d elegation, as applicable

. The emission limitations apply at all times the uni t i s

operating including and not lim i ted to startup, shutdown,

or malfunction.

(b) Units that do not use wet scrubbers must maintain

opacity to less than or equal to the percent opacity (three

1-hour blocks consisting of ten 6-minute average opacit y

values) specified in table 2 of this subpart, as

applicable.

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

(a) If you use a wet scrubber ( s) to comply with th e

emission limitations, you must establish operating limits

for up to four operatin g paramet e rs (as specified in tabl e

3 of this subpart) as described in paragraphs (a)(1)

through (4) of thi s section dur i ng the initial performan ce

test.

(1) Maximum charge rate

, calcul a ted using one of th e

two different procedures in para g raph (a)(1)(i) or (ii), a s

appropriate.

(i) For continuous and interm i ttent units, maximum

charge rate is 110 percen t o f the average charge rat e

measured during the most recent performance test

demonstrating compliance with all applicable emission157

limitations.

(ii) For batch units, maximum charge rate is 110

percent of the daily charge rate measured during the most

recent performance test demonstrating compliance with all

applicable emission limitations.

(2) Minimum pressur e drop acro s s the wet particula te

matter scrubber, which is calcu l ated as the lowest 1-hour

90 percent of the average pressure drop across the wet

scrubber measured during the mo s t recent performance test

demonstrating compliance with the particulate matter

emission limitations; or mini m um amperage to the we t

scrubber, which is calculated as the lowest 1-hour 9 0

percent of the average amper a ge to the wet scrubbe r

measured during the most recent performance test

demonstrating compliance with the particulate matter

emission limitations.

(3) Minimum scrubber liquid li q uor flow rate, whic h

is calculated as the lowes t 1 -hour 90 percent of th e

average liquid liquor flow rate at the inlet to the wet

acid gas or particulate matter s c rubber measured during th e

most recent performance test demonstrating compliance with

all applicable emission limitations.

(4) Minimum scrubber liquor pH

, which is calculate d

as as the lowest 1-hour 9 0 perce n t of the average liquor p H

at the inlet to the wet acid gas scrubber measured during

the most recent performance test demonstrating compliance

with the HCl emission limitation.

(b) You must meet the operating limits established

during the initial performance t e st on the date th e initia l

performance test is require d o r completed (whichever i s

earlier). You must conduc t an initial performance

evaluation of each continuous monitoring system and

continuous parameter monitoring system within 60 days o f

installation of the monitoring system.

(c) If yo u use a fabri c filt e r to comply wit h the158

emission limitations, you must o perate each fabric filter

system such that the bag leak detection system alarm does

not sound more than 5 percent of the operating time during

a 6-month period. In calcula t ing this operating tim e

percentage, if inspection of the fabric filter demonstrate s

that no corrective action i s r e quired, no alarm time i s

counted. If correctiv e actio n is required, eac h alar m

shall be counted a s a minimu m of 1 hour. If yo u tak e

longer than 1 hour t o initiate c o rrective action, the alar m

time shall be counted as th e act u al amount of time taken b y

you to initiate corrective action.

(d) If you use an electrostatic precipitator to comply

with the emission limitations, you must measure the

(secondary) voltage and amperage of the electrostatic

precipitator collection plates during the particulate

matter performance test. Calculate the average electric

power value (secondary voltage x secondary current =

secondary electric power) for each test run. The operating

limit for the electrostatic precipitator is calculated as

the lowest 1-hour average secondary electric power measured

during the most recent performance test demonstrating

compliance with the particulate matter emission

limitations.

(e) If you use activated carbon sorbent injection to

comply with the emission limitations, you must measure the

sorbent flow rate during the performance testing. The

operating limit for the carbon sorbent injection is

calculated as the lowest 1-hour average sorbent flow rate

measured during the most recent performance test

demonstrating compliance with the mercury emission

limitations.

(f) If you use selective noncatalytic reduction to

comply with the emission limitations, you must measure the

charge rate, the secondary chamber temperature (if

applicable to your CISWI unit), and the reagent flow rate

during the nitrogen oxides performance testing. The

operating limits for the selective noncatalytic reduction

are calculated as the lowest 1-hour average charge rate,159

secondary chamber temperature, and reagent flow rate

measured during the most recent performance test

demonstrating compliance with the nitrogen oxides emission

limitations.

(g) If you do not use a wet scrubber, electrostatic

precipitator, or fabric filter to comply with the emission

limitations, and if you do not determine compliance with

your particulate matter emission limitation with a

particulate matter continuous emissions monitoring system,

you must maintain opacity to less than or equal to ten

percent opacity (1-hour block average).

§60.2680 What if I do not use a wet scrubber

, fabric

filter, activated carbon injection, selective noncatalytic

reduction, or an electrostati c p recipitator to comply wit h

the emission limitations?

(a) If you use an air pollution control device other

than a wet scrubber

, activated c arbon injection, selectiv e

noncatalytic reduction, fabric filter, or an electrostatic

precipitator or limit emissions in some other manner,

including mass balances, to c omply with the emissio n

limitations under §60.2670, you must petition the EPA

Administrator for specific operating limits to be

established during the initial performance test and

continuously monitored thereafter. You must not conduc t

the initial performance test un t il after the petition ha s

been approved by the Administr a tor. Your petition mus t

include the five item s listed i n paragraphs (a) (1) throu gh

(e) (5) of this section.

( a 1 ) Identification of the sp e cific parameters you

propose to use as additional operating limits.

( b 2 ) A discussion of the rela t ionship between thes e160

parameters and emissions of regulated pollutants,

identifying how emissions of regulated pollutants change

with changes in these parameters

, and how limits on these

parameters will serve to limit emissions of regulated

pollutants.

( c 3 ) A discussion of how you will establish the upper

and/or lower values fo r the s e parameters which wil l

establish the operating limits on these parameters.

( d 4 ) A discussion identifying the methods you will

use to measure and the instruments you will use to monitor

these parameters, as wel l as t he relative accuracy a nd

precision of these methods and instruments.

( e 5 ) A discussion identifying the frequency and

methods for recalibrating th e in s truments you will us e fo r

monitoring these parameters.

(b) [Reserved]

§60.2685 Affirmative Defense for Exceedance of an Emission

Limit During Malfunction.

In response to an actio n to enf o rce the standards se t

forth in paragraph §60.2670 you may assert an affirmativ e

defense to a claim for civil penalties for exceedances of

such standards that are caused b y malfunction, as define d

at §60.2. Appropriate penalties may be assessed, however,

if you fail to meet your burden of proving all of th e

requirements in the affirmative defense. The affirmative

defense shall not be available for claims for injunctive

relief.

(a) To establish the affirmative defense in any actio n

to enforce such a limit

, yo u must timely meet th e

notification requirements in par a graph (b) of this section

, and must prove by a preponderance of evidence that:

(1) The excess emissions:

(i) Were caused by a sudd e n, infrequent, and161

unavoidable failure of air pollu t ion control and monitorin g

equipment, process equipment, or a process to operate i n a

normal or usual manner; and

(ii) Could not hav e been prev e nted through carefu l

planning, proper design or bette r operation and maintenanc e

practices; and

(iii) Did not stem fro m any a c tivity or event tha t

could have been foreseen and avoided, or planned for; and

(iv) Were not part of a recurr i ng pattern indicativ e

of inadequate design, operation, or maintenance; and

(2) Repairs were mad e as expe d itiously as possibl e

when the applicable emission limitations were being

exceeded. Off-shift and overtime labor were used, to the

extent practicable to make these repairs; and

(3) The frequency, amount and d u ration of the exces s

emissions (including any bypas s ) were minimized to th e

maximum extent practicable during periods of such

emissions; and

(4) If the excess emission s resu l ted from a bypass o f

control equipment or a proce s s, then the bypass wa s

unavoidable to prevent loss of life, personal injury, or

severe property damage; and

(5) All possible step s were t a ken to minimize t he

impact of the excess emission s o n ambient air quality, th e

environment and human health; and

(6) All emissions and/or parameter monitoring and

systems, as well as contro l syst e ms, were kept in operatio n

if at all possible, consisten t with safety and good ai r

pollution control practices;

(7) All of the action s in re s ponse to the exces s

emissions were documented by properly signed,

contemporaneous operating logs; and

(8) At all times, th e facilit y was operated in a

manner consistent with good practices for minimizing

emissions; and

(9) A written root cause analys i s has been prepared

,

the purpose of whic h is t o determine, correct, a nd

eliminate the primary causes o f the malfunction and th e

excess emissions resulting from the malfunction event a t

issue. The analysis shall a l so specify, using best

monitoring methods and engineeri n g judgment, the amoun t o f162

excess emissions that were the result of the malfunction.

(b) Notification. The owne r or operator of th e

facility experiencing an exceedance of its emission

limit(s) during a malfunction shall notify the

Administrator by telephone or facsimile (FAX) transmission

as soon as possible, but no later than two business days

after the initial occurrenc e o f the malfunction, i f i t

wishes to avail itself of an affirmative defense to civil

penalties for that malfunction. The owner or operator

seeking to assert a n affirmativ e defense shall als o submi t

a written report to the Administrator within 45 days of the

initial occurrence of the exce e dance of the standard i n

§60.2670 to demonstrate, with all necessary supporting

documentation, that it has met t he requirements set fort h

in paragraph (a) of this section. The owner or operator may

seek an extension of this deadline for up to 30 additional

days by submitting a written re q uest to the Administrato r

before the expiration of the 45 day period. Until a request

for an extension has been approved by the Administrator,

the owner or operator is subject to the requirement to

submit such report within 4 5 day s of the initial occurrenc e

of the exceedances.

What happens during peri od s of s tartup, shutdown, an d

malfunction?

(a) The emission limitations and operating limits

apply at all times except du r ing CISWI unit startups

,

shutdowns, or malfunctions.

(b) Each malfunction must last no longer than 3 hours.

Model Rule—Performance Testing

§60.2690 How do I conduct the initial and annual

performance test?

(a) All performance tests must consist of a minimum

of three test runs conducted under conditions

representative of normal operations.163

(b) You must documen t that th e waste burned durin g

the performance test i s represen t ative of the wast e burne d

under normal operating conditio n s by maintaining a log o f

the quantity of wast e b u rned (as required i n

§60.2740(b)(1)) and the types of waste burned during the

performance test.

(c) All performance test s must b e conducted using th e

minimum run duration specifie d i n table s 2 an d 6 throug h 9

of this subpart.

(d) Method 1 of appendix A of this part must be used

to select the samplin g locatio n and number o f travers e

points.

(e) Method 3 A or 3 B of appendi x A of thi s part mu st

be used for gas composition anal y sis, including measuremen t

of oxygen concentration. Method 3A or 3B o f appendix A o f

this part must be used simultaneously with each method.

(f) All pollutant concentration s

, except for opacity

,

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 oxygen;

C

meas = pollutant concentration measured on a dry basis;

(20.9

− 7)

= 20.9 percent oxygen

− 7 percent oxygen (define d

oxygen correction basis);

20.9 = oxygen concentration in air, percent; and

%O 2 = oxygen concentration measured on a dry basis, percent.164

(g) You must determine dioxins/furans toxic

equivalency by following the procedures in paragraphs

(g)(1) through (3) of this section.

(1) Measure the concentration of each dioxin/furan

tetra- through octa- congener isomer emitted using EPA Method

23 at 40 CFR part 60, appendix A

.

(2) For each dioxin/furan (tetra- through octachlorinated) congener isomer measured in accordance with

paragraph (g)(1) of this section, multiply the

congener isomer concentration by its corresponding toxic

equivalency factor specified in table 4 of this subpart.

(3) Sum the products calculated in accordance with

paragraph (g)(2) of this section to obtain the total

concentration of dioxins/furans emitted in terms of toxic

equivalency.

(h) Method 2 2 at 4 0 CFR par t 60

, appendix A-7 mus t b e

used to determine compliance wit h the fugitive ash emissio n

limit in table 2 of thi s subpar t or tables 6 through 9 o f

this subpart.

(i) If you have an applica b le opacity operatin g

limit, you must determine compli a nce with the opacity limi t

using Method 9 at 40 CFR part 6 0, appendix A-4, based on

three 1-hour blocks consistin g of ten 6-minute averag e

opacity values, unless you are required to install a

continuous opacity monitoring system, consistent with

§60.2710 and §60.2730.

§60.2695 How are the performance test data used?

You use results of performance tests to demonstrate

compliance with the emission lim i tations in table 2 o f thi s165

subpart or tables 6 through 9 of this subpart.

Model Rule—Initial Compliance Requirements

§60.2700 How do I demonstrate i nitial compliance with th e

amended emission limitations and establish the operating

limits?

You must conduct an initial performance test, as

required under §60.8, §§60.2690 and 60.2670, to determine

compliance with the emission lim i tations in table 2 o f thi s

subpart and tables 6 throug h 9 of this subpart

, t o

establish compliance with any o p acity operating limits in

§60.2675, and to establish operating limits using the

procedures in §60.2675 o r § 60.2680. The initia l

performance test must be conduc t ed using the test method s

listed in table 2 of thi s subpar t and tables 6 through 9 o f

this subpart and the procedures in §60.2690. The use of

the bypass stack during a perfor m ance test shall invalidat e

the performance test. You mu s t conduct a performanc e

evaluation of each continuous m o nitoring system within 60

days of installation of the monitoring system.

§60.2705 By what date mus t I conduct the initial

performance test?

(a) The initial performanc e tes t must be conducte d n o

later than 180 days afte r your f inal compliance date. You r

final compliance date is speci f ied in table 1 o f thi s

subpart.

(b) If you commence or recommen c e combusting a soli d

waste at an existing combustion unit at any commercial or

industrial facility and yo u co n ducted a test consistent

with the provisions of this subpart while combusting the

given solid waste within th e 6 months preceding th e

reintroduction of that solid waste in the combustio n

chamber, you do no t need t o rete s t until 6 month s from th e

date you reintroduce that solid waste.166

(c) If you commence combusting or recommence

combusting a solid waste a t an e xisting combustion unit a t

any commercial or industria l f a cility and you hav e no t

conducted a performance test con s istent with the provision s

of this subpart whil e combusti n g the given soli d wast e

within the 6 months preceding the reintroduction of that

solid waste in the combustion chamber, you must conduct a

performance test within 6 0 days commencing or recommencin g

solid waste combustion.

§60.2706 By what date must I conduct the initial air

pollution control device inspection?

(a) The initial air poll u tion control device

inspection must be conducted within 60 days afte r

installation of the control devi c e and the associated CISW I

unit reaches the charge rate at which it will operate, but

no later than 180 days after the final compliance date for

meeting the amended emission limitations.

(b) Within 10 operating da y s following an ai r

pollution control device inspection, all necessary repairs

must be completed unles s the o wner or operator obtai ns

written approval from th e state agency establishing a da te

whereby all necessary repairs of the designated facilit y

must be completed.

Model Rule—Continuous Compliance Requirements

§60.2710 How do I demonstrate continuous compliance with

the emission limitations and the operating limits?

(a) Compliance with standards.

(1) The emission standards and operating requirements

set forth in this subpart apply at all times.

(2) If you cease combusting solid waste you may opt to

remain subject to the provisions of this subpart

.

Consistent with the definitio n of CISWI unit, you ar e167

subject to the requirements of this subpart at least 6

months following the last date o f solid waste combustion

.

Solid waste combustion is ceased when solid waste is not in

the combustion chamber (i.e., the solid waste feed to the

combustor has been cut off for a period of time not less

than the solid waste residence time).

(3) If you cease combusting solid w a ste you must b e

in compliance with any newly applicable standards on the

effective date of the waste-to- f uel switch. The effective

date of the waste-to-fuel switch is a date selected by you,

that must be at least 6 months from the date that yo u

ceased combusting solid waste, consistent with

§60.2710(a)(2). Your source mus t remain in complianc e wit h

this subpart until th e effectiv e date of th e waste-to-fue l

switch.

(4) If you own o r operate an e x isting commercial o r

industrial combustion unit that combusted a fuel or nonwaste material, and you commenc e or recommence combustion

of solid waste, you are subject to the provisions of this

subpart as of the firs t day yo u introduce or reintroduc e

solid waste to the combustion chamber, and this date

constitutes the effective date o f the fuel-to-waste switch

.

You must complete all initial co m pliance demonstrations fo r

any section 112 standards tha t are applicable to you r

facility before you commence or recommence combustion o f

solid waste. You must provide 30 days prior notice of the

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

notification must identify:

(i) The name of the owner or operator of the CISWI

unit, the location of the sou r ce, the emissions unit(s )

that will cease burning solid waste, and the date of the

notice;168

(ii) The currently applicable subcategory under this

subpart, and any 40 CF R part 6 3 subpart and subcategor y

that will be applicable after you cease combusting solid

waste;

(iii) The fuel(s), non-waste material(s) and solid

waste(s) the CISWI unit is cu r rently combusting and ha s

combusted over the past 6 months, and the fuel(s) or nonwaste materials the unit will commence combusting;

(iv) The date on whic h you b e came subject to th e

currently applicable emission limits;

(v) The date upo n which yo u w ill cease combustin g

solid waste, and the dat e (if d ifferent) that you inten d

for any new requirements to become applicable (i.e., the

effective date of the waste-to-fuel switch), consistent

with (2) and (3)) above.

(5) All air pollutio n control e q uipment necessary fo r

compliance with any newly applic a ble emissions limits whic h

apply as a result o f the ces s ation or commencement o r

recommencement of combusting sol i d waste must b e installe d

and operational as of the effective date of the waste-tofuel, or fuel-to-waste switch.

(6) All monitoring systems necessary for compliance

with any newly applicable monitoring requirements which

apply as a result o f the ces s ation or commencement o r

recommencement of combusting sol i d waste must b e installe d

and operational as of the effective date of the waste-tofuel, or fuel-to-waste switch. All calibration and drif t

checks must be performed as of the effective date of the

waste-to-fuel, or fuel-to-waste switch. Relative accuracy

tests must be performed a s of th e performance test deadlin e

for PM CEMS. Relative accurac y t e sting for other CEMS nee d

not be repeated if that testing was previously performed169

consistent with section 112 monitoring requirements or

monitoring requirements under this subpart.

( a b ) You must conduc t an annua l performance test fo r

the pollutants listed in table 2 of this subpart or tables

6 through 9 of this subpar t for particulate matter

,

hydrogen chloride, and opacit y for each CISWI unit a s

required under §60.8 §60.2690 to determin e compliance with

the emission limitations

. The a n nual performance test mus t

be conducted using the test methods listed in table 2 of

this subpart or table s 6 throug h 9 of this subpar t and th e

procedures in §60.2690. Opacit y m ust be measured usin g EP A

Reference Method 9 at 4 0 CFR p a rt 60. Annual performanc e

tests are not required if yo u use continuous emissio n

monitoring systems CEMS or continuous opacity monitoring

systems to determine compliance.

( b c ) You must continuousl y m onitor the operating

parameters specified in §60.2675 or established under

§60.2680 and as specifie d in §6 0 .2735

. Operation above t he

established maximum or below the established minimum

operating limits constitutes a deviation from the

established operating limits. Three-hour rolling block

average values are used to deter m ine compliance (except fo r

baghouse leak detection system a larms) unless a different

averaging period is establishe d under §60.2680. Operatin g

limits do not apply are confirmed or reestablished durin g

performance tests.

( c d ) You mus t only bur n only t h e same types o f waste

and fuels used t o establish sub c ategory applicability (fo r

ERUs) and operating limits during the performance test.

(e) For energy recover y uni t s, incinerators, and170

small remote units, you mus t perform annual visual

emissions test for ash handling.

(f) For energy recovery units

, you must conduct a n

annual performance test fo r op a city using EPA Referenc e

Method 9 at 40 CFR part 60 (except where particulate matter

continuous monitoring system or continuous parameter

monitoring systems are used) an d the pollutants listed i n

table 7 of this subpart.

(g) For facilities usin g a CEMS to demonstrat e

compliance with the carbon monoxide emission limit,

compliance with the carbon mono x ide emission limit may b e

demonstrated by using the CEMS a ccording to the followin g

requirements:

(1) You must measur e emissions a ccording to §60.13 to

calculate 1-hour arithmetic averages, corrected to 7

percent oxygen. CEMS data durin g startup and shutdown, a s

defined in this subpart, ar e n o t corrected to 7 percen t

oxygen, and are measured a t stac k oxygen content. You mus t

demonstrate initial compliance with the carbon monoxide

emissions limit using a 30-da y rolling average of the 1-

hour arithmetic average emission concentrations, including

CEMS data during startup an d s h utdown as defined in thi s

subpart, calculated using Equati o n 19-19 in sectio n 12.4. 1

of EPA Reference Method 19 at 40 CFR part 60, appendix A–7.

(2) Operate the carbon monoxide continuous emissions

monitoring system in accordance with the applicable

requirements of performance spec i fication 4A of appendi x B

and the quality assurance proced u res of appendix F o f thi s

part.171

(h) For waste-burning kilns, demonstrate continuous

compliance with the particulate matter emissions limit

using a particulate matter continuous emissions monitoring

system according to the procedu r es in §60.2730(n). Energy

recovery units with design heat input capacities greate r

than 250 MMBtu/hr may elect to demonstrate continuous

compliance with the particulate matter emissions limit

using a particulate matter CEMS a ccording to the procedure s

in §60.2730(n) instead of the continuous parameter

monitoring system specified in §60.2710(i).

(i) For energy recovery units w ith design capacities

greater than or equal to 10 MMBTU/hour but less than 250

MMBtu/hr you must install

, opera t e, certify and maintai n a

continuous opacity monitoring system (COMS) according to

the procedures in §60.2730.

(j) For waste-burning kilns, you must conduct an

annual performance test fo r the pollutants (except mercur y

and particulate matter, and hydrogen chloride if no acid

gas wet scrubber is used) listed in table 8 of this

subpart. If your waste-burning k i ln is not equipped wit h a

wet scrubber, you must deter m ine compliance with th e

hydrogen chloride emission limi t using a CEMS a s specifie d

in §60.2730. You must determine c ompliance with the mercur y

emissions limit using a mercu r y CEMS according to th e

following requirements:

(1) Operate a CEMS i n accord a nce with performance

specification 12A at 40 CFR part 60, appendix B or a

sorbent trap based integrated monitor in accordance wit h

performance specification 12B a t 40 CFR part 60, appendi x

B. The duration of the performance test must be a calendar172

month. For each calendar month i n which the waste-burnin g

kiln operates, hourly mercur y c o ncentration data and stac k

gas volumetric flow rate data must be obtained.

(2) Owners or operator s using a mercury continuou s

emissions monitoring systems must install, operate,

calibrate and maintain an instrument for continuously

measuring and recording th e merc u ry mass emissions rat e t o

the atmosphere according to the r equirements of performanc e

specifications 6 and 12 A at 4 0 C F R part 60, appendi x B an d

quality assurance procedure 5 at 40 CFR part 60, appendix

F.

(3) The owner or operato r of a w a ste-burning kiln mus t

demonstrate initial compliance by operating a mercury

continuous emissions monitor whi l e the raw mill o f the inline kiln/raw mill is operating u nder normal conditions an d

while the raw mill of the in-line kiln/raw mill is not

operating.

(k) If you use an air pollution control device to meet

the emission limitations i n thi s subpart, you mus t conduc t

an initial and annual inspect i on of the air pollutio n

control device. The inspectio n m u st include, at a minimum

,

the following:

(1) Inspect air pollution contro l device(s) for prope r

operation.

(2) Develop a site-specific monitoring plan according

to the requirements in paragrap h (l) of this section. Thi s

requirement also applies to yo u if you petition th e EP A

Administrator for alternative monitoring parameters under173

§60.13(i).

(l) For each CMS require d in t h is section, you mus t

develop and submit to th e EPA A d ministrator for approval a

site-specific monitoring plan according to the requirements

of this paragraph (l) that add r esses paragraphs (l)(1)(i)

through (vi) of this section.

(1) You must submit this site-sp e cific monitoring pla n

at least 60 days before you r ini t ial performance evaluation

of your continuous monitoring system.

(i) Installation of the continuous monitoring system

sampling probe or other interfac e at a measurement locatio n

relative to each affected process unit such that the

measurement is representative o f control of th e exhaus t

emissions (e.g., on or downst r eam of the last contro l

device).

(ii) Performance and equipment specifications for the

sample interface, the pollutant concentration or parametric

signal analyzer and the data collection and reduction

systems.

(iii) Performance evaluation procedures and acceptance

criteria ( e.g. , 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 in174

accordance with the general requirements of §60.7(b),(c),

(c)(1), (c)(4), (d), (e), (f) and (g).

(2) You must conduc t a performa n ce evaluation of ea ch

continuous monitoring system i n accordance with your sitespecific monitoring plan.

(3) You must operate and maintain the continuous

monitoring system in continuou s operation according to th e

site-specific monitoring plan.

(m) If you have an operating limit that requires the

use of a flow monitorin g sy s tem, you must meet th e

requirements in paragraphs (l) and (m)(1) through (4) of

this section.

(1) Install the flow sensor and other necessar y

equipment in a position tha t provides a representative

flow.

(2) Use a flow sensor with a m e asurement sensitivity

of no greater than 2 percent of the expected process flow

rate.

(3) Minimize the effect s of swi r ling flow or abnorm al

velocity distributions due to upstream and downstream

disturbances.

(4) Conduct a flow monitoring system performance

evaluation in accordance with y o ur monitoring plan at th e

time of each performance test but no less frequently than

annually.

(n) If you have an operating limit that requires the175

use of a pressure monitoring system, you must meet the

requirements in paragraphs (l) and (n)(1) through (6) of

this section.

(1) Install the pressur e sensor( s ) in a positio n tha t

provides a representative measurement of the pressure

(e.g., PM scrubber pressure drop).

(2) Minimize or eliminate pulsating pressure,

vibration, and internal and external corrosion.

(3) Use a pressure senso r with a minimum tolerance o f

1.27 centimeters of water o r a minimum tolerance of 1

percent of the pressur e monitor i ng system operating range,

whichever is less.

(4) Perform checks at leas t once each process

operating day to ensure pressure measurements are not

obstructed (e.g., check for pressure tap pluggage daily).

(5) Conduct a performance evalu a tion of the pressure

monitoring system in accordance with your monitoring plan

at the time of each performance test but no less frequently

than annually.

(6) If at any time the measured pressure exceeds the

manufacturer's specified maximum operating pressure range,

conduct a performance evaluation of the pressure monitorin g

system in accordance wit h your m onitoring plan and confi rm

that the pressure monitoring sy s tem continues to meet th e

performance requirements in your monitoring plan.

Alternatively, install and verify the operation of a new

pressure sensor.176

(o) If you have an operating limit that requires the

use of a pressure monitoring system, you must meet the

requirements in paragraphs (l) and (n)(1) through (6) of

this section.

(1) Install the pressur e sensor( s ) in a positio n tha t

provides a representative measurement of the pressure

(e.g., PM scrubber pressure drop).

(2) Minimize or eliminate pulsating pressure,

vibration, and internal and external corrosion.

(3) Use a pressure senso r with a minimum tolerance o f

1.27 centimeters of water o r a minimum tolerance of 1

percent of the pressur e monitor i ng system operating range

,

whichever is less.

(4) Perform checks at leas t once each process

operating day to ensure pressure measurements are not

obstructed (e.g., check for pressure tap pluggage daily).

(5) Conduct a performance evalu a tion of the pressure

monitoring system in accordance with your monitoring plan

at the time of each performance test but no less frequently

than annually.

(6) If at any time the measured pressure exceeds the

manufacturer's specified maximum operating pressure range,

conduct a performance evaluation of the pressure monitorin g

system in accordance wit h your m onitoring plan and confi rm

that the pressure monitoring sy s tem continues to meet th e

performance requirements in your monitoring plan.

Alternatively, install and verify the operation of a new177

pressure sensor.

(p) If you have a n operating l imit that requires a

secondary electric power monitoring system for an

electrostatic precipitator, you must meet the requirements

in paragraphs (l) and (p)(1) through (2) of this section.

(1) Install sensors to measure ( s econdary) voltage an d

current to the precipitator collection plates.

(2) Conduct a performance evalu a tion of the electric

power monitoring system i n acco r dance with your monitorin g

plan at the time of each performance test but no less

frequently than annually.

(q) If you have an operating limit that requires the

use of a monitoring system t o measure sorbent injection

rate (e.g., weigh belt, weigh hopper, or hopper flow

measurement device), you must meet the requirements i n

paragraphs (l) and (q)(1) through (3) of this section.

(1) Install the syste m in a pos i tion(s) that provide s

a representative measurement of t he total sorbent injectio n

rate.

(2) Conduct a performance evaluation of the sorben t

injection rate monitoring system in accordance with you r

monitoring plan at the time of each performance test but no

less frequently than annually.

(r) If you elect to use a fabric filter bag leak

detection system to comply with the requirements of this

subpart, you must install, calibrate, maintain, and

continuously operate a ba g l eak detection system a s178

specified in paragraphs (l) an d ( r)(1) through (5) of thi s

section.

(1) Install a bag leak detection sensor(s) in a

position(s) that will b e represe n tative of the relativ e o r

absolute particulate matter loadings for each exhaust

stack, roof vent, o r compartme n t (e.g., for a positiv e

pressure fabric filter) of the fabric filter.

(2) Use a bag leak detection system certified by the

manufacturer to be capabl e of d e tecting particulate matte r

emissions at concentrations o f 10 milligrams per actua l

cubic meter or less.

(3) Conduct a performance evalu a tion of the bag lea k

detection system in accordance with your monitoring pla n

and consistent with th e guidanc e provided in EPA–454/R–98–

015 (incorporated by reference, see §60.17).

(4) Use a bag lea k detection s y stem equipped with a

device to continuously record the output signal from the

sensor.

(5) Use a bag lea k detection s y stem equipped with a

system that will sound an alarm when an increase in

relative particulate matter emi s sions over a preset level

is detected. The alarm must be located where it is observed

readily by plant operating personnel.

(s) For facilities usin g a CEMS to demonstrat e

compliance with the sulfur dioxide emission limit,

compliance with the sulfur dioxide emission limit may be

demonstrated by using the CEM S specified in §60.2730 t o179

measure sulfur dioxide an d cal c ulating a 30-day rollin g

average emission concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 at 40 CFR part

60, appendix A-7. The sulfu r dio x ide CEMS must be operate d

according to performance specif i cation 2 in appendix B o f

this part and must follow the procedures and methods

specified in this paragrap h (s )

. For sources tha t hav e

actual inlet emissions less tha n 100 parts per million dr y

volume, the relative accuracy criterion for inlet sulfu r

dioxide CEMS should be no greater than 20 percent of the

mean value of the reference method test data in terms of

the units of the emission standard, or 5 parts per million

dry volume absolute value of the mean difference between

the reference method and the CEMS, whichever is greater.

(1) During each relative accurac y test run of th e CEMS

required by performance specification 2 in appendix B of

this part, collect sulfur diox i de and oxygen (or carbo n

dioxide) data concurrently (or within a 30- to 60-minute

period) with both the continuous emissions monitors and th e

test methods specified in paragraphs (s)(1)(i) and

(s)(1)(ii) of this section.

(i) For sulfur dioxide, EP A Refe r ence Method 6 or 6C

,

or as an alternative ANSI/ASME P T C 19.10–1981 (incorporate d

by reference, see §60.17) must be used.

(ii) For oxygen (o r carbon di o xide), EPA Referenc e

Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10–

1981 (incorporated by reference, see §60.17), as

applicable, must be used.

(2) The span valu e of th e continuous emissions180

monitoring system at the inlet to the sulfur dioxide

control device must be 12 5 perce n t of the maximum estimate d

hourly potential sulfur dioxide emissions of the unit

subject to this rule

. The span value of the CEM S at th e

outlet of the sulfur dioxide control device must be 50

percent of the maximum estimated hourly potential sulfu r

dioxide emissions of the unit subject to this rule.

(3) Conduct accuracy determinations quarterly and

calibration drift tests dail y i n accordance with procedur e

1 in appendix F of this part.

(t) For facilities usin g a CEMS to demonstrat e

continuous compliance with the nitrogen oxides emission

limit, compliance with the nitr o gen oxides emission limit

may be demonstrated by usin g the CEMS specified in §60.273 0

to measure nitrogen oxides and c a lculating a 30-day rollin g

average emission concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 at 40 CFR part

60, appendix A-7. The nitroge n o x ides CEMS must be operate d

according to performance specif i cation 2 in appendix B o f

this part and must follow the procedures and methods

specified in paragraphs (t)(1) through (t)(5) of this

section.

(1) During each relative accurac y test run of th e CEMS

required by performance specification 2 of appendix B of

this part, collect nitrogen oxides and oxygen (or carbon

dioxide) data concurrently (or within a 30- to 60-minute

period) with both the CEMS and the test methods specified

in paragraphs (t)(1)(i) and (t)(1)(ii) of this section.

(i) For nitrogen oxides, EP A Ref e rence Method 7 or 7 E181

at 40 CFR part 60, appendix A-4 must be used.

(ii) For oxygen (o r carbon di o xide), EPA Referenc e

Method 3A or 3B, or as an alternative ANSI/ASME PTC 19.10–

1981 (incorporated by reference, see §60.17), as

applicable, must be used.

(2) The span valu e of th e CEMS m ust be 125 percen t o f

the maximum estimated hourly potential nitrogen oxide

emissions of unit.

(3) Conduct accuracy determinations quarterly and

calibration drift tests dail y i n accordance with procedur e

1 in appendix F of this part.

(4) The owner or operato r of a n affected facility may

request that compliance with th e nitrogen oxides emission

limit be determined using carbon dioxide measurements

corrected to an equivalent of 7 percent oxygen. If carbon

dioxide is selected for use i n diluent corrections, th e

relationship between oxygen an d carbon dioxide levels mus t

be established during the initial performance test

according to the procedures a nd methods specified i n

paragraphs (t)(4)(i) through (t)(4)(iv) of this section.

This relationship may be reestablished during performance

compliance tests.

(i) The fuel factor equation in Method 3B must be used

to determine the relationshi p b etween oxygen and carbo n

dioxide at a sampling location. Method 3A, 3B, or as an

alternative ANSI/ASME PTC 19.10–1981 (incorporated by

reference, see §60.17), a s app l icable, must be use d t o

determine the oxygen concentrati o n at the sam e location as182

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.

(u) For facilities using a continuous emissions

monitoring system to demonstrate continuous compliance with

any of the emission limit s o f this subpart, you mus t

complete the following:

(1) Demonstrate compliance with the appropriate

emission limit(s) using a 30-day rolling average,

calculated using Equation 19-19 in section 12.4.1 of EPA

Reference Method 19 at 40 CFR part 60, appendix A-7.

(2) Operate all continuous emissions monitoring system

in accordance with the applicable procedures under

appendices B and F of this part.

(v) Use of the bypass stack at any time is an

emissions standards deviation for particulate matter, HCl,

Pb, Cd, Hg, NO x , SO 2 , and dioxin/furans.

(w) For energy recovery unit s wi t h a design heat inpu t

capacity of 100 MMBt u per hou r o r greater that d o not us e a

carbon monoxide CEMS, you mu s t install, operate, an d

maintain a oxygen analyzer system as defined in §60.2875

according to the procedures in paragraphs (w)(1) through

(4) of this section.183

(1) The oxygen analyzer system must be installed by

the initial performance test date specified in §60.2675.

(2) You must operate the oxygen trim system with the

oxygen level set at th e minimu m percent oxygen by volum e

that is established as the o p erating limit for oxyge n

according to paragraph (w)(3) of this section.

(3) You must maintain the oxygen level such that it is

not below the lowest hourly av e rage oxygen concentration

measured during the most recent CO performance test.

(4) You must calculate and re c ord a 30-day rollin g

average oxygen concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 of Appendix A-7

of this part.

(x) For energy recovery units w i th design heat inpu t

capacities greater than or equ a l to 250 MMBtu/hour, yo u

must install, certify, maintai n

, and operate a PM CP MS

monitoring emissions discharged to the atmosphere and

record the output of th e system as specified in paragraph s

(x)(1) through (5) of this section. For other energy

recovery units, you may elect to use PM CPMS operated in

accordance with this section in lieu of using other CMS for

monitoring PM compliance (e.g.

, bag leak detectors

, ES P

secondary power, PM scrubber pressure)

(1) Install, certify, operate, and maintain your P M

CPMS according to the procedur e s in your approved sitespecific monitoring plan developed in accordance with

§60.2710(l) and (x)(1)(i) through (iii) of this section.184

(i) The operating principle o f the PM CPMS must b e

based on in-stack or extract i ve light scatter, ligh t

scintillation, or beta attenuation of the exhaust gas or

representative exhaust gas sample. The reportable

measurement output from the P M CPMS may be expressed a s

milliamps, stack concentration, or other raw data signal.

(ii) The PM CPMS must have a cycle time (i.e., period

required to complete sampling, measurement, and reporting

for each measurement) no longer than 60 minutes.

(iii) The PM CPMS mus t be cap a ble of detecting an d

responding to particulate matter concentrations of no

greater than 0.5 mg/actual cubic meter.

(3) Collect PM CPMS hourl y avera g e output data for al l

energy recovery unit operating h ours. Express the PM CPM S

output as millamps, PM concent r ation, or other raw dat a

signal value.

(4) Calculate the arithmetic 30- d ay rolling average of

all of the hourly average PM CPMS output collected during

all energy recovery unit ope r ating hours data (e.g.

,

milliamps, PM concentration, raw data signal).

§60.2715 By what date must I conduct the annua l

performance test?

You must conduct annual perform a nce tests for particulate

matter, hydrogen chloride, an d opacity within 12 month s

following between 11 and 1 3 mont h s of the initial previou s185

performance test. Conduct subsequent annual performance

tests within 12 months fol lowing the previous one.

§60.2716 By what date must I conduct the annual air

pollution control device inspection?

On an annual basis (no more than 12 months following

the previous annual air pollution control device

inspection), you must complete the air pollution contro l

device inspection as described in §60.2706.

§60.2720 May I conduct performance testing less often?

(a) You must conduct annual performance tests

according to the schedule speci f ied in §60.2715, with th e

following exceptions:

(1) You may conduct a repeat performance test at any

time to establish new value s f o r the operating limits t o

apply from that point forward, as specified in §60.2725.

The Administrator may reques t a repeat performance test at

any time.

(2) You must repeat the perfo r mance test within 6 0

days of a process change, as defined in §60.2875.

(3) If the initia l or an y subse q uent performance tes t

for any pollutant in table 2 or tables 6 through 9 of this

subpart, as applicable, demonstrates that the emission

level for the pollutant i s no greater than the emissio n

level specified in paragrap h ( a )(3)(i) or (a)(3)(ii) o f186

this section, as applicable, an d you are not require d t o

conduct a performance test fo r t h e pollutant in response t o

a request by the Administrato r i n paragraph (a)(1) of thi s

section or a process chang e i n paragraph (a)(2) of thi s

section, you may elect to ski p conducting a performanc e

test for the pollutant for the next 2 years. You must

conduct a performance test fo r the pollutant during th e

third year and no more than 37 months following the

previous performance test for the pollutant. For cadmiu m

and lead, both cadmium and lead must be emitted at emission

levels no greater tha n their r espective emission level s

specified in paragraph (a)(3)(i) of this section for yo u t o

qualify for less frequent testing under this paragraph.

(i) For particulate matter, hydrogen chloride,

mercury, carbon monoxide, nitrogen oxides, sulfur dioxide,

cadmium, lead, and dioxins/furan s

, the emission level equa l

to 75 percent of the applicable emission limit in table 2

or tables 6 through 9 of this subpart, as applicable, to

this subpart.

(ii) For fugitive emissions, visible emissions (of

combustion ash from the as h conv e ying system) for 2 percen t

of the time during eac h of the three 1-hour observation s

periods.

(4) If you are conductin g less f requent testing for a

pollutant as provided in paragr a ph (a)(3) of this sectio n

and a subsequent performanc e test for th e pollutan t

indicates that your CISWI unit does not meet the emission

level specified in paragrap h ( a )(3)(i) or (a)(3)(ii) o f

this section, as applicable, you must conduct annua l

performance tests for the po l lutant according to th e187

schedule specified in paragraph (a) of this section unti l

you qualify for less frequen t te s ting for the pollutant a s

specified in paragraph (a)(3) of this section.

(a) You can test les s often fo r a given pollutant i f

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 year s

show that you comply wit h the e m ission limitation. In thi s

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.

(b) If your CISWI unit continues to meet the emission

limitation for particulate matter, hydrogen chloride, or

opacity you may choose to con d uct performance tests fo r

these pollutants every third yea r, but each test mus t b e

within 36 months of the previous performance test.

(c) 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 unti l a l l performance tests over a

3

- year period show compliance.

§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 ne w value s for the operating limits

.

The Administrator may reques t a repeat performance test at

any time.

(b) You must repeat the performance test if your feed

stream is different than the feed streams used during any188

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 sc r ubber to comply with

the emission limitation under § 6 0.2670, you must install,

calibrate (to manufacturers' specifications), maintain, and

operate devices (or establish m e thods) for monitoring the

value of the operatin g para m eters used to determin e

compliance with the operating limits listed in table 3 of

this subpart. These device s (o r methods) must measure an d

record the values for these o p erating parameters at th e

frequencies indicated in table 3 of this subpart a t al l

times except as specified in §60.2735(a).

(b) If yo u use a fabri c filt e r to comply wit h the

requirements of this subpart

, y o u must install, calibrate

,

maintain, and continuously ope r ate a bag lea k detectio n

system as specified in paragra p hs (b)(1) through (8) o f

this section.

(1) You must install and operate a bag leak detection

system for each exhaust stack of the fabric filter.

(2) Each bag lea k detection sys t em must be installed

,

operated, calibrated, and mainta i ned in a manner consisten t

with the manufacturer's written specifications and

recommendations.

(3) The bag leak detection system must be certified

by the manufacturer t o be capab l e of detecting particula te

matter emissions at concentrat i ons of 10 milligram s pe r

actual cubic meter or less.189

(4) The bag lea k detection syst e m sensor must provid e

output of relative or absolute particulate matter loadings.

(5) The bag lea k detection sy s tem must be equippe d

with a device to continuousl y re c ord the output signal fro m

the sensor.

(6) The bag lea k detection sy s tem must be equippe d

with an alarm system tha t will a l ert sound automatically a n

operator when an increase in r e lative particulate matter

emissions over a preset level is detected. The alarm must

be located where it is observ e d easily heard by plan t

operating personnel.

(7) For positive pressure fabric filter systems, a

bag leak detection system mu s t be installed in eac h

baghouse compartment or cell. For negative pressure o r

induced air fabric filters, the bag leak detector must be

installed downstream of the fabric filter.

(8) Where multiple detector s are required, th e

system’s instrumentation and a l arm may be shared amon g

detectors.

(c) If you are using something other than a wet

scrubber

, activated carbon

, selective non-catalyti c

reduction, or an electrostati c p recipitator to comply wit h

the emission limitations unde r § 60.2670, you must install

,

calibrate (to the manufacturers’ specifications), maintain,

and operate the equipment neces s ary to monitor compliance

with the site-specific operating limits established using

the procedures in §60.2680.

(d) If you use activated carbon injection to comply

with the emission limitations i n this subpart, you mus t

measure the minimum sorbent flow rate once per hour.190

(e) If you us e selective nonc a talytic reduction t o

comply with the emission limitat i ons, you must complete th e

following:

(1) Following the dat e o n which the initia l

performance test is complete d or is require d to be

completed under §60.2690, whichever date comes first,

ensure that the affected facility does not operate above

the maximum charge rate, or b e low the minimum secondar y

chamber temperature (if applica b le to your CISWI unit) or

the minimum reagent flo w rate measured as 3-hour blo ck

averages at all times.

(2) Operation of the affected facility above the

maximum charge rate, below the minimum secondary chamber

temperature and below th e m i nimum reagent flow rat e

simultaneously constitute a violation of the nitrogen

oxides emissions limit.

(f) If you use an electrostati c p recipitator to comply

with the emission limits o f thi s subpart, you must monito r

the secondary power to the electrostatic precipitator

collection plates and maintain t h e 3-hour block averages a t

or above the operating limit s established during th e

mercury or particulate matter performance test.

(g) For waste-burning kilns not equipped with a wet

scrubber, in place of hydrogen chloride testing with EPA

Method 321 at 40 CFR part 63, appendix A, an owner o r

operator must install, calibrat e

, maintain, and operate a

CEMS for monitoring hydrogen chloride emissions discharged

to the atmosphere and record the output of the system. To

demonstrate continuous compliance with the hydrogen191

chloride emissions limit for uni t s other than waste-burnin g

kilns not equipped with a wet scrubber, a facility may

substitute use of a hydrogen ch l oride continuous emission s

monitoring system for conducting the hydrogen chloride

annual performance test, monitoring the minimum hydrogen

chloride sorbent flow rate and monitoring the minimum

scrubber liquor pH.

(h) To demonstrate continuous compliance with the

particulate matter emissions limit, a facility may

substitute use of a particulate m atter continuous emission s

monitoring system for conducting the particulate matter

annual performance test and moni t oring the minimum pressur e

drop across the wet scrubber, if applicable.

(i) To demonstrate continuous compliance with the

dioxin/furan emissions limit, a f acility may substitute us e

of a continuous automated sampling system for th e

dioxin/furan annual performance test. You must record the

output of the system an d analy z e the sample according t o

EPA Method 23 a t 40 CF R part 60

, appendix A-7. Thi s optio n

to use a continuou s automated s a mpling system takes effe ct

on the date a final performanc e s pecification applicable to

dioxin/furan from continuous mo n itors is published in the

Federal Register. The owner o r operator who elects t o

continuously sample dioxin/furan emissions instead of

sampling and testing using EPA M e thod 23 at 40 CFR par t 60

,

appendix A-7 must install

, cali b rate, maintain and operat e

a continuous automated sampling s ystem and must comply wit h

the requirements specified in §60.58b(p) and (q).

(j) To demonstrate continuous compliance with the

mercury emissions limit, a facil i ty may substitute use o f a192

continuous automated sampling sy s tem for the mercury annua l

performance test. You must recor d the output of th e syste m

and analyze the sample a t set i n tervals using any suitabl e

determinative technique that can meet performance

specification 12B criteria. This option to use a continuou s

automated sampling system takes e ffect on the date a fina l

performance specification applicable to mercury from

monitors is published in th e Fed e ral Register. The owner o r

operator who elects to continuously sample mercury

emissions instead of samplin g an d testing using EP A Metho d

29 or 30B at 40 CFR part 60, a p pendix A-8, ASTM D6784-02

(Reapproved 2008) (incorporated by reference, see §60.17),

or an approved alternativ e met h od for measuring mercur y

emissions, must install, calibra t e, maintain and operat e a

continuous automated sampling s y stem 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 ma y substitut e

use of a continuous emissions monitoring system for th e

nitrogen oxides annual performance test to demonstrate

compliance with the nitrogen oxides emissions limits.

(1) Install, calibrate, maintain and operate a CEMS

for measuring nitrogen oxides e m issions discharged to the

atmosphere and record the ou t put of the system. Th e

requirements under performance specification 2 of appendix

B of this part, th e quality assurance procedure 1 o f

appendix F of this par t and t h e procedures under §60.1 3

must be followed for installatio n

, evaluation and operatio n

of the CEMS.

(2) Following the date that th e initial performance193

test for nitrogen oxides is completed or is required to be

completed under §60.2690, compliance with the emission

limit for nitrogen oxides requir e d under §60.52b(d) must b e

determined based on the 30-da y rolling average of th e

hourly emission concentrations u s ing CEMS outlet data

. Th e

1-hour arithmetic averages must be expressed in parts pe r

million by volume (dry basis) and used to calculate the 30-

day rolling average concentrations. The 1-hour arithmetic

averages must be calculate d usin g the data point s require d

under §60.13(e)(2).

(l) To demonstrate continuous compliance with the

sulfur dioxide emissions limit, a facility may substitute

use of a continuous automate d sampling system for th e

sulfur dioxide annual performance test to demonstrate

compliance with the sulfur dioxide emissions limits.

(1) Install, calibrate, maintain and operate a CEMS

for measuring sulfur dioxide emissions discharged to th e

atmosphere and record the ou t put of the system. Th e

requirements under performance specification 2 of appendix

B of this part, the quality assurance requirements o f

procedure 1 of appendix F of this part and the procedures

under §60.13 must b e followed f o r installation, evaluatio n

and operation of the CEMS

.

(2) Following the date that th e initial performance

test for sulfur dioxide is completed or is required to be

completed under §60.2690, compliance with the sulfur

dioxide emission limit may be determined based on the 30-

day rolling average of the h ourly arithmetic averag e

emission concentrations using CE M S outlet data. Th e 1-hou r194

arithmetic averages must b e expr e ssed in parts pe r millio n

corrected to 7 percent oxyge n (dry basis) and used t o

calculate the 30-day rolling average emission

concentrations. 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 wet

scrubber, fabric filter wit h ba g leak detection system

, o r

particulate matter CEMS, you mus t install, operate, certif y

and maintain a continuous opacity monitoring system

according to the procedures in paragraphs (m)(1) through

(5) of this section b y the co m pliance date specified i n

§60.2670. Energy recovery unit s that use a particulat e

matter continuous emissions monitoring system to

demonstrate initial and continuing compliance according to

the procedures in §60.2730(n) ar e not required to instal l a

continuous opacity monitoring s y stem and must perform the

annual performance tests for opacity consistent with

§60.2710(f).

(1) Install, operate and maintain each continuous

opacity monitoring system according to performance

specification 1 at 40 CFR part 60, appendix B.

(2) Conduct a performance evaluation of each

continuous opacity monitoring system according to the

requirements in §60.13 and according to performance

specification 1 at 40 CFR part 60, appendix B.

(3) As specified in §60.13(e)(1), each continuous

opacity monitoring system must complete a minimum of one

cycle of sampling and analyzin g for each successive 10-195

second period and one cycle of data recording for each

successive 6-minute period.

(4) Reduce the continuous opacity monitoring system

data as specified in §60.13(h)(1).

(5) Determine and recor d all t he 6-minute average s

(and 1-hour block averages as applicable) collected.

(n) For energy recovery units w ith design capacities

greater than 250 MMBtu/hr and wa s te-burning kilns, in plac e

of particulate matter testing with EPA Method 5 at 40 CFR

part 60, appendix A-3, an owner or operator must install,

calibrate, maintain and operate a CEMS for monitoring

particulate matter emissions discharged to the atmosphere

and record the output of the system. The owner or operator

of an affected facility who continuously monitors

particulate matter emissions instead of conducting

performance testing using EPA Method 5 at 40 CFR part 60,

appendix A-3 must install

, cali b rate, maintain and operat e

a CEMS and must comply with the requirements specified in

paragraphs (n)(1) through (n)(14) of this section.

(1) Notify the Administrator 1 month before starting

use of the system.

(2) Notify the Administrator 1 month before stopping

use of the system.

(3) The monitor must be installed, evaluated and

operated in accordance with the r equirements of performanc e

specification 11 of appendix B of this part and qualit y

assurance requirements of proced u re 2 of appendix F of thi s196

part and §60.13.

(4) The initial performance evaluation must be

completed no later than 18 0 days after the final complianc e

date for meeting the amended emission limitations, as

specified under §60.2690 or with i n 180 days of notificatio n

to the Administrator of use of the continuous monitoring

system if the owne r or operato r was previously determinin g

compliance by Method 5 at 40 CFR part 60, appendix A-3

performance tests, whichever is later.

(5) The owner or operato r of a n 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 betwee n oxygen and carbo n dioxid e

levels for the affected faci l ity must be establishe d

according to the procedures a nd methods specified i n

§60.2710(s)(5)(i) through (s)(5)(iv).

(6) The owner or operato r of an a ffected facility mus t

conduct an initial performanc e t est for particulate matte r

emissions as required under §60

. 2690. Compliance with the

particulate matter emission li m it must be determine d b y

using the CEMS specified in paragraph (n) of this section

to measure particulate matter and calculating a 30-da y

rolling average emission concentration using Equation 19-19

in section 12.4.1 of EPA Referen c e Method 19 at 40 CF R par t

60, appendix A-7 of this part.

(7) Compliance with the particulate matter emission

limit must be determined based on the 30-day rolling

average calculated using Equati o n 19-19 in section 12.4.1197

of EPA Reference Metho d 19 a t 4 0 CFR part 60

, Appendix A- 7

of the part from the 1-hour arithmetic average of the CEMS

outlet data.

(8) At a minimum, valid contin u ous monitoring system

hourly averages must be obtained as specified §60.2735.

(9) The 1-hour arithmetic averages required under

paragraph (n)(7) of this sect i on must be expressed i n

milligrams per dry standar d cu b ic meter corrected t o 7

percent oxygen (or carbon dioxi d e)(dry basis) and must b e

used to calculate the 30-day rolling average emission

concentrations. The 1-hour arithmetic averages must be

calculated using the data points required under

§60.13(e)(2).

(10) All valid CEMS data must be used in calculating

average emission concentrations even if the minimum CEM S

data requirements of paragraph ( n)(8) of this section ar e

not met.

(11) The CEMS mus t be op e rated according t o

performance specification 11 in appendix B of this part.

(12) During each relative accu r acy test run of th e

CEMS required by performance spe c ification 11 in appendix B

of this part, particulat e matt e r and oxygen (o r carbo n

dioxide) data must be collected concurrently (or within a

30-to 60-minute period) by both the continuous emissions

monitors and the following test methods.

(i) For particulate matter

, EPA Reference Method 5 at

40 CFR part 60, appendix A-3 must be used.198

(ii) For oxygen (o r carbon di o xide), EPA Referenc e

Method 3A or 3 B at 4 0 CFR p a rt 60, appendix A-2

, a s

applicable, must be used.

(13) Quarterly accuracy determinations and daily

calibration drift tests mus t b e performed in accordanc e

with procedure 2 in appendix F of this part.

(14) When particulate matter emissions data are

missing because of CEMS breakdowns, repairs, calibration

checks and zero an d span adju s tments, you must colle ct

emissions data by usin g oth e r monitoring systems a s

approved by the Administrator o r EPA Reference Method 19 a t

40 CFR part 60, appendix A-7 to provide, as necessary,

valid emissions data for a minimum of 85 percent of the

hours per day, 90 percent of the hours per calendar

quarter, and 95 percent of the hours per calendar year that

the affected facility is operated and combusting waste.

(o) To demonstrate continuous compliance with the

carbon monoxide emissions limit

, a facility ma y substitut e

use of a continuous automate d sampling system for th e

carbon monoxide annual performance test to demonstrate

compliance with the carbon monoxide emissions limits.

(1) Install, calibrate, maintai n

, and operate a CEMS

for measuring carbon monoxide e m issions discharged to the

atmosphere and record the ou t put of the system. Th e

requirements under performance specification 4B of appendix

B of this part, th e quality assurance procedure 1 o f

appendix F of this par t and t h e procedures under §60.1 3

must be followed for installation, evaluation, and

operation of the CEMS.199

(2) Following the date that th e initial performance

test for carbon monoxide is completed or is required to be

completed under §60.2690, compliance with the carbon

monoxide emission limit may b e d e termined based on the 30-

day rolling average of the h ourly arithmetic averag e

emission concentrations, including CEMS data during startup

and shutdown as defined i n this subpart, using CEMS outle t

data. Except for CEMS dat a durin g startup and shutdown, a s

defined in this subpart

, the 1 -hour arithmetic average s

must be expressed in part s pe r million corrected to 7

percent oxygen (dry basis) an d u s ed to calculate the 30-da y

rolling average emission concentrations. CEMS data during

startup and shutdown, as defined in this subpart, are not

corrected to 7 percent oxygen

, and are measured at stac k

oxygen content. The 1-hour ar i thmetic averages must b e

calculated using the data points required under

§60.13(e)(2).

(p) The owner/operator of an affected source with a

bypass stack shall install, calibrate (to manufacturers’

specifications), maintain and operate a device or metho d

for measuring the use of the bypass stack including date,

time and duration.

(q) For energy recovery unit s wi t h a design heat inpu t

capacity of 100 MMBt u per hou r o r greater that d o not us e a

carbon monoxide CEMS, you mu s t install, operate, an d

maintain a oxygen analyzer system as defined in §60.2875

according to the procedures in paragraphs (q)(1) through

(4) of this section.

(1) The oxygen analyzer system must be installed by

the initial performance test date specified in §60.2675.200

(2) You must operate the oxygen trim system with the

oxygen level set at th e minimu m percent oxygen by volum e

that is established as the o p erating limit for oxyge n

according to paragraph (q)(3) of this section.

(3) You must maintain the oxygen level such that it is

not below the lowest hourly av e rage oxygen concentration

measured during the most recent CO performance test.

(4) You must calculate and re c ord a 30-day rollin g

average oxygen concentration using Equation 19-19 in

section 12.4.1 of EPA Reference Method 19 of Appendix A-7

of this part.

(r) For energy recovery units w i th design heat inpu t

capacities greater than or equ a l to 250 MMBtu/hour, yo u

must install, certify, maintai n

, and operate a PM CP MS

monitoring emissions discharged to the atmosphere and

record the output of th e system as specified in paragraph s

(r)(1) through (5) of this section. For other energy

recovery units, you may elect to use PM CPMS operated in

accordance with this section in lieu of using other CMS for

monitoring PM compliance (e.g.

, bag leak detectors

, ES P

secondary power, PM scrubber pressure)

(1) Install, certify, operate, and maintain your P M

CPMS according to the procedur e s in your approved sitespecific monitoring plan developed in accordance with

§60.2710(l) and (r)(1)(i) through (iii) of this section.

(i) The operating principle o f the PM CPMS must b e

based on in-stack or extract i ve light scatter, ligh t

scintillation, or beta attenuation of the exhaust gas or201

representative exhaust gas sample. The reportable

measurement output from the P M CPMS may be expressed a s

milliamps, stack concentration, or other raw data signal.

(ii) The PM CPMS must have a cycle time (i.e., period

required to complete sampling, measurement, and reporting

for each measurement) no longer than 60 minutes.

(iii) The PM CPMS mus t be cap a ble of detecting an d

responding to particulate matter concentrations of no

greater than 0.5 mg/actual cubic meter.

(2) Collect PM CPMS hourl y avera g e output data for al l

energy recovery unit operating h ours. Express the PM CPM S

output as millamps, PM concent r ation, or other raw dat a

signal value.

(3) Calculate the arithmetic 30- d ay rolling average o f

all of the hourly average PM CPMS output collected during

all energy recovery unit ope r ating hours data (e.g.

,

milliamps, PM concentration, raw data signal).

§60.2735 Is there a minimum a m ount of monitoring data I

must obtain?

For each continuous monitoring system required or

optionally allowed under §60.2 7 30, you must monito r an d

collect data according to this section:

(a) You must operate the monitor i ng system and collec t

data at all required intervals at all times compliance is

required except for periods of monitoring system202

malfunctions or out-of-control periods, repairs associated

with monitoring system malfunctions or out-of-control

periods (as specified in §60.2 7 70(o) of this part), an d

required monitoring system quality assurance or quality

control activities including, as applicable, calibration

checks and required zero and spa n adjustments. A monitorin g

system malfunction is any sudden, infrequent, not

reasonably preventable failure o f the monitoring syste m t o

provide valid data. Monitorin g system failures that ar e

caused in part by poor maintenance or careless operation

are not malfunctions. You are re q uired to effect monitorin g

system repairs in response to monitoring system

malfunctions or out-of-control periods and to return th e

monitoring system to operation as expeditiously as

practicable.

(b) You may not use data recorded during th e

monitoring system malfunctions, repairs associated with

monitoring system malfunctions or out-of control periods,

or required monitoring syste m q u ality assurance or contro l

activities in calculations use d to report emissions o r

operating levels. You must us e all the data collecte d

during all other periods i n asse s sing the operation of th e

control device and associated control system.

(c) Except for periods of monitoring system

malfunctions or out-of-control periods, repairs associated

with monitoring system malfunctions or out-of-control

periods, and required monitoring system quality assurance

or quality control activities including, as applicable,

calibration checks and require d zero and span adjustments

,

failure to collect required data is a deviation of the203

monitoring requirements.

(a) Except for monitoring malfunctions, associated

repairs, and required qualit y a s surance or quality contro l

activities (including, as applicable, calibration checks

and required zero and span adjustments of the monitoring

system), you must conduct all monitoring at all times the

CISWI unit is operating.

(b) Do not us e data record e d during monitorin g

malfunctions, associated repairs, and required quality

assurance or quality contro l a c tivities for meeting th e

requirements of this su bpart, i n cluding data averages and

calculations. You must use all the data collected during

all other periods in assess i ng compliance with the

operating limits.

Model Rule

— Recordkeeping and Reporting

§60.2740 What records must I keep?

You must maintain the 13 items (as applicable) as

specified in paragraphs (a)

, (b), and (e) through ( m u ) of

this section for a period of at least 5 years:

(a) Calendar date of each record.

(b) Records of the data describe d in paragraphs (b)(1 )

through (6) of this section:

(1) The CISWI unit charge dates

, times, weights, an d

hourly charge rates.204

(2) Liquor flow rate to the wet scrubber inlet every

15 minutes of operation, as applicable.

(3) Pressure drop across the we t scrubber system every

15 minutes of operation o r amp e rage to the wet scrubbe r

every 15 minutes of operation, as applicable.

(4) Liquor pH as introduce d to t he wet scrubber ever y

15 minutes of operation, as applicable.

(5) For affected CISW I units th a t establish operatin g

limits for controls other t h an wet scrubbers under

§60.2675(d) through (f) or §60.2 6 80, you must maintain dat a

collected for all operating parameters used to determin e

compliance with the operating limits.

(6) If a fabric filter is used to comply with the

emission limitations, you must r ecord the date, time, an d

duration of each alarm and the time corrective action was

initiated and completed, and a brief description of th e

cause of the alarm an d the co r rective action taken. Yo u

must also record the percen t of operating time during eac h

6-month period that th e ala r m sounds, calculated a s

specified in §60.2675(c).

(c) [Reserved] Identification o f calendar dates an d

times for which monitoring s ystems used to monitor

operating limits were inoperative, inactive,

malfunctioning, or out of con t rol (except for downtim e

associated with zero and span an d other routine calibratio n

checks). Identify the operating parameters not measured,

the duration, reasons for no t o btaining the data, and a

description of corrective actions taken.

(d) [Reserved] Identification of calendar dates,

times, and durations o f malfunct i ons, and a descriptio n o f

the malfunction and the corrective action taken.205

(e) Identification of calenda r dates and times fo r

which data show a deviatio n fr o m the operating limits i n

table 3 of this subpart or a deviation from other operating

limits established under §60.2675(d) through (f) or

§60.2680 with a descriptio n of t he deviations, reasons f or

such deviations, and a description of corrective action s

taken.

(f) The results of the initial, annual, and any

subsequent performance tests conducted to determine

compliance with the emissio n l i mits and/or to establis h

operating limits, as applicabl e

. Retain a copy of th e

complete test report including calculations.

(g) Records showing th e names o f CISWI unit operato rs

who have completed review of th e information in §60.2660(a)

as required by §60.2660(b), i n cluding the date of th e

initial review and all subsequent annual reviews.

(h) Records showing the names o f the CISWI operator s

who have completed the operator t raining requirements unde r

§60.2635, met the criteria for qualification under

§60.2645, and maintained or renewed their qualification

under §60.2650 or §60.2655. Records must include

documentation of training, the dates of the initial an d

refresher training, and the dates of their qualificatio n

and all subsequent renewals of such qualifications.

(i) For each qualified operat o r, the phone and/o r

pager number at which the y can b e reached during operatin g

hours.

(j) Records of calibration of a ny monitoring devices

as required under §60.2730.

(k) Equipment vendor specifications and related

operation and maintenance requirements for the incinerator,206

emission controls, and monitoring equipment.

(l) The information listed in §60.2660(a).

(m) On a daily basis, keep a l o g of the quantity of

waste burned and th e types of waste burned (alwa ys

required).

(n) Maintain records of the annual air pollution

control device inspections that a re required for each CISW I

unit subject to the emissions limits in table 2 of this

subpart or tables 6 through 9 of this subpart, any required

maintenance and any repairs no t c ompleted within 10 days o f

an inspection or the timefram e established by the stat e

regulatory agency.

(o) For continuously monitored pollutants or

parameters, you must document and keep a record of the

following parameters measured using continuous monitoring

systems.

(1) All 6-minute 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. You must in d icate which data are CEM S

data during startup and shutdown.

(5) All 1-hour average concentrations of particulate

matter emissions.207

(6) All 1-hour average concentrations of mercury

emissions.

(7) All 1-hour average concentrations of hydrogen

chloride emissions.

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

(9) All 1-hour average PM CPM S r e adings or particulate

matter continuous emissions monitor outputs.

(p) Records indicating use o f the bypass stack

,

including dates, times and durations.

(q) If you choose to stack test less frequently than

annually, consistent with §60.27 2 0(a) through (c), you mus t

keep annual records that document that your emissions in

the previous stack test(s) were less than 75 percent of the

applicable emission limit and document that there was no

change in source operation s inc l uding fuel composition an d

operation of air pollutio n con t rol equipment that woul d

cause emissions of the relevant pollutant to increase

within the past year.

(r) Records of the occurrence and duration of eac h

malfunction of operation (i.e., process equipment) or the

air pollution control and monitoring equipment.

(s) Records of all required ma i ntenance performed on

the air pollution control and monitoring equipment.

(t) Records of action s take n during periods o f

malfunction to minimize emissions in accordance with

§60.11(d), including corrective actions to restore208

malfunctioning process and air pollution control and

monitoring equipment to its n o rmal or usual manner o f

operation.

(u) For operating units that combust non-hazardous

secondary materials that have b een determined not to b e

solid waste pursuant to §241. 3 (b)(1), you must keep a

record which documents ho w th e secondary material meet s

each of the legitimacy criteria. If you combust a fuel that

has been processed from a discar d ed non-hazardous secondar y

material pursuant to §241.3(b)(4 )

, you must keep records a s

to how the operations tha t produ c ed the fuel satisfies th e

definition of processing in §241

. 2. If the fuel receive d a

non-waste determination pursuant to the petition process

submitted under §241.3(c), yo u must keep a recor d tha t

documents how the fuel satisfies the requirements of the

petition process.

§60.2745 Where and in what format must I keep my records?

All records must be available o n site in either pape r

copy or computer-readable forma t that can be printed upo n

request, unless an alternative format is approved by 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 plan?

You must submit the waste man a gement plan no late r209

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 report s

must be signed by the facilities manager.

(a) The complet e test rep o rt for the initi al

performance test results obtained under §60.2700, as

applicable.

(b) The values for th e site-spe c ific operating limits

established in §60.2675 or §60.2680.

(c) If you are using a fabric filter to comply wit h

the emission limitations, docu m entation that a ba g lea k

detection system has bee n instal l ed and is bein g operated

,

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 subse q uent reports no more tha n

12 months following the previou s report. (If the uni t i s

subject to permitting requireme n ts under title V of th e

Clean Air Act, yo u may b e requir e d by the permi t to submi t

these reports more frequently.)

§60.2770 What information mus t I include i n my annua l

report?

The annual report required under §60.2765 must includ e

the ten items listed in paragraphs (a) through (j) of this210

section. If you have a deviatio n from the operating limit s

or the emission limitations, you must also submit deviatio n

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 the

accuracy of the content of the report.

(c) Date of report and beginning and ending dates of

the reporting period.

(d) The values for the operat i ng limits establishe d

pursuant to §60.2675 or §60.2680.

(e) If no deviation from any emission limitation or

operating limit that applies t o you has been reported

, a

statement that there was no d e viation from the emissio n

limitations or operating limits during the reporting

period

. , and that no monitoring system used to determine

compliance with the operating limits was inoperative,

inactive, malfunctioning or out of control.

(f) The highest recorded 3- h our average and th e

lowest recorded 3-hour average

, as applicable, fo r eac h

operating parameter recorded for the calendar year bein g

reported.

(g) Information recorded under § 60.2740(b)(6) and (c )

through (e) for the calendar year being reported.

(h) If a performanc e test was conducted during th e

reporting period, the results of that test.

(i) If you me t the requireme n ts of §60.2720(a) o r

(b), and did not conduct a performance test during the

reporting period, you must s tate that you met th e211

requirements of §60.2720(a) o r (b), and, therefore, yo u

were not required to conduc t a p erformance test during th e

reporting period.

(j) Documentation of periods wh e n all qualified CISW I

unit operators were unavailable f or more than 8 hours

, bu t

less than 2 weeks.

(k) If you ha d a malfunctio n during the reportin g

period, the compliance report must include the number

,

duration, and a brie f descri p tion for each typ e o f

malfunction that occurred durin g the reporting period and

that caused or ma y have cause d any applicable emissi on

limitation to be exceeded. The report must also include a

description of actions taken b y a n owner or operator durin g

a malfunction of an affected so u rce to minimize emission s

in accordance with §60.11(d), including actions taken t o

correct a malfunction.

(l) For each deviation from an emission or operatin g

limitation that occurs for a CISWI unit for which you are

not using a CMS to comply with the emission or operating

limitations in this subpart, the annual report must contai n

the following information.

(1) The total operating time of the CISWI unit at

which the deviation occurred during the reporting period.

(2) Information on th e number, d uration, and cause of

deviations (including unknown cause, if applicable), as

applicable, and the corrective action taken.

(m) If there wer e periods durin g which the continuo us

monitoring system, including th e CEMS, was out of contro l212

as specified in paragraph (o) of this section, the annual

report must contain the follo w ing information for eac h

deviation from an emission or operating limitation

occurring for a CISWI unit for which you are using a

continuous monitoring system to comply with the emissio n

and operating limitations in this subpart.

(1) The date and time that each malfunction started

and stopped.

(2) The date, time, an d durati o n that each CMS wa s

inoperative, except for zero (low-level) and high-level

checks.

(3) The date, time

, and duratio n that each continuo us

monitoring system was out-of-control, including start and

end dates and hour s and descrip t ions of corrective actio ns

taken.

(4) The date and tim e that eac h 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, an d the total duration a s a

percent of the tota l source o p erating time during th at

reporting period.

(6) A breakdown of the tot a l duration of th e

deviations during the reportin g p eriod into those tha t ar e

due to control equipmen t proble m s, process problems, othe r

known causes, and other unknown causes.

(7) A summary o f the tota l d u ration of continuou s213

monitoring system downtime durin g the reporting period, an d

the total duration of continuous monitoring system downtim e

as a percent o f the tota l operat i ng time of th e CISWI uni t

at which the continuous monitori n g system downtime occurre d

during that reporting period.

(8) An identification o f each p a rameter and pollutan t

that was monitored at the CISWI unit.

(9) A brief description of the CISWI unit.

(10) A brief descriptio n of th e continuous monitoring

system.

(11) The date of th e latest continuous monitoring

system certification or audit.

(12) A description of any c h anges in continuou s

monitoring system, processes, or controls since the las t

reporting period.

(n) If there wer e periods durin g which the continuo us

monitoring system, including t h e CEMS, was not out o f

control as specified in paragra p h (o) of this section

, a

statement that there wer e not periods during which t he

continuous monitoring system wa s out of control durin g th e

reporting period.

(o) A continuous monitoring sys t em is out of contro l

if any of the following occur.

(1) The zero (low-level), mid-level (if applicable),

or high-level calibration drift exceeds two times the

applicable calibration drift specification in the214

applicable performance specification or in the relevant

standard.

(2) The continuous monitoring system fails a

performance test audit (e.g., cy l inder gas audit), relativ e

accuracy audit, relative accurac y test audit, o r linearit y

test audit.

(3) The continuous opacity monitoring system

calibration drift exceeds two times the limit in the

applicable performance specification in the relevant

standard.

(p) For energy recovery units, i n clude the annual hea t

input and average annual heat input rate of all fuels being

burned in the unit t o verify w h ich subcategory of energ y

recovery unit applies.

§60.2775 What else must I rep o rt if I have a deviatio n

from the operating limits or the emission limitations?

(a) You must submit a deviation report if any

recorded 3-hour average param e ter level is above th e

maximum operating limit or be l ow the minimum operatin g

limit established under this s ubpart, if the bag lea k

detection system alarm sounds f o r more than 5 percen t o f

the operating time for th e 6-mon t h reporting period, or i f

a performance test was conduct e d that deviated from an y

emission limitation.

(b) The deviation repor t must b e submitted by Augus t

1 of that yea r for dat a collecte d during the firs t half o f

the calendar year (January 1 t o J une 30), and by February 1

of the following year fo r dat a you collected during th e

second half of the calendar year (July 1 to December 31).215

§60.2780 What must I include in the deviation report?

In each report required unde r §60.2775, for an y

pollutant or parameter that d e viated from the emissio n

limitations or operating limit s specified in this subpart

,

include the six items described in paragraphs (a) throug h

(f) of this section.

(a) The calendar dates and times your unit deviated

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 E ach deviatio n from the e m ission limitations or

operating limits and your corrective actions.

(2) Bypass events and your corrective actions.

(d) A copy o f the operatin g l imit monitoring data

during each deviation and any test report that documents

the emission levels.

(e) The dates, times, number, duration, and causes

for monitoring downtime incidents (other than downtime

associated with zero, span, an d other routine calibration

checks).

(f) Whether each deviation occ u rred during a perio d

of startup, shutdown, o r malfu n ction, or during anothe r

period.

§60.2785 What else must I rep o rt if I have a deviatio n216

from the requirement to have a qualified operato r

accessible?

(a) If all qualifie d operators a re not accessible fo r

2 weeks or more, you must take the two actions in

paragraphs (a)(1) and (2) of this section.

(1) Submit a notificatio n of t h e deviation within 1 0

days that includes th e three it e ms in paragraphs (a)(1)( i)

through (iii) of this section.

(i) A statement of what caused the deviation.

(ii) A description of what you are doing to ensure

that a qualified operator is accessible.

(iii) The date when you anticipate that a qualified

operator will be available.

(2) Submit a statu s report t o t h e Administrator ever y

4 weeks that includes the t h ree items in paragraph s

(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 whe n you antici p ate that a qualifie d

operator will be accessible.

(iii) Request approval fro m the Administrator to

continue operation of the CISWI unit.

(b) If your unit was shut down by the Administrator,

under the provisions of §60.2665 ( b)(2), due to a failur e t o

provide an accessible qualified operator, you must notify

the Administrator that you are resuming operation once a

qualified operator is accessible.217

§60.2790 Are there any other notifications or reports

that I must submit?

(a) Yes. You mus t submit notifi c ations as provided by

§60.7.

(b) If you cease combusting sol i d waste but continu e

to operate, you must provide 30 days prior notice of the

effective date of the waste-to-f u el switch, consistent wit h

§60.2710(a). The notification must identify:

(1) The name of the owner or operator of the CISWI

unit, the location of the sou r ce, the emissions unit(s )

that will cease burning solid waste, and the date of the

notice;

(2) The currently applicable subcategory under this

subpart, and any 40 CF R part 6 3 subpart and subcategor y

that will be applicable after you cease combusting solid

waste;

(3) The fuel(s), non-waste material(s) and solid

waste(s) the CISWI unit is cu r rently combusting and ha s

combusted over the past 6 months, and the fuel(s) or nonwaste materials the unit will commence combusting;

(4) The date on whic h you b e came subject to th e

currently applicable emission limits;

(5) The date upo n which yo u w ill cease combustin g

solid waste, and the dat e (if d ifferent) that you inten d

for any new requirements to become applicable (i.e., the

effective date of the waste-to-fuel switch), consistent

with (2) and (3)) above.218

§60.2795 In what form can I submit my reports?

(a) Submit initial, annual

, and deviation reports

electronically or in pape r forma t

, postmarked on o r befor e

the submittal due dates.

(b) After December 31, 2011

, wit h in 60 days after th e

date of completing each performance evaluation or

performance test, as they are d e fined in §63.2, conducte d

to demonstrate compliance with t his subpart, the owner o r

operator of the affecte d facilit y must submit th e relativ e

accuracy test audit dat a and pe r formance test data, exce pt

opacity data, to EPA by successfully submitting the data

electronically to EPA’s Centra l Data Exchange (CDX) b y

using the Electronic Reporting Tool (ERT) (see

http://www.epa.gov/ttn/chief/ert/ert_tool.html)

.

§60.2800 Can reporting dates be changed?

If the Administrator agrees, you may change th e

semiannual or annual reportin g dates. See §60.19(c) fo r

procedures to seek approval to change your reporting 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 CISW I unit an d ai r curtain incinerato r219

subject to standards under t h is subpart must operat e

pursuant to a permit issue d un d er Clean Air Act section s

129(e) and T t itle V. of the Clean Air Act

. by the later of

the two dates in paragraphs (a) and (b) of this section.

(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 u nit is subject to

title V as a resul t of some trig g ering requirement(s) othe r

than this subpart (for example

, b eing a major source), the n

your unit may b e required t o app l y for and obtai n a titl e V

permit prior to the deadlines noted above. If more than on e

requirement triggers the require m ent to apply for a title V

permit, the 12

- month timefram e for filing a title V

application is triggered b y th e requirement which firs t

causes the source to be subject to title V.

Model Rule—Air Curtain Incinerators

§60.2810 What is an air curtain incinerator?

(a) An air curtain incinerato r o perates by forcefully

projecting a curtain of air across an open chamber or open

pit in which combustion occurs

. Incinerators of this typ e

can be constructed above o r b elow ground and with o r

without refractory walls and floor. (Air curtain

incinerators are not to be confused with conventional

combustion devices with enclosed fireboxes and controlled

air technology such as mass burn, modular, and fluidized

bed combustors.)

(b) Air curtain incinerator s that burn only th e

materials listed in paragraphs ( b)(1) through (3) of thi s

section are only required to meet the requirements under

“Air Curtain Incinerators” (§§60.2810 through 60.2870).220

(1) 100 percent wood waste.

(2) 100 percent clean lumber.

(3) 100 percent mixtur e of o n ly wood waste, clea n

lumber, and/or yard waste.

§60.2815 What are my requirements for meeting increments

of progress and achieving final compliance?

If you plan to achiev e complia n ce more than 1 yea r

following the effective date of State plan approval, you

must meet the two increments of progress specified i n

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 progress?

Table 1 of this subpart specifie s compliance dates fo r

each of the increments of progress.

§60.2825 What must I includ e in the notifications o f

achievement of increments of progress?

Your notification of achievement of increments of

progress must include the t h ree items described in

paragraphs (a) through (c) of this section.

(a) Notification that the incr e ment 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 the221

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 after the

compliance date for the increment.

§60.2835 What if I do not meet an increment of progress?

If you fail to meet an increment of progress, you must

submit a notification to the Administrator postmarked

within 10 business days after the date for that increment

of progress in table 1 o f this s u bpart. You must inform th e

Administrator that you did no t m e et the increment, and yo u

must continue to submit reports each subsequent calenda r

month until the increment of progress is met.

§60.2840 How do I comply with the increment of progres s

for submittal of a control plan?

For your control pla n increment of progress, you mu st

satisfy the two requirements specified in paragraphs (a )

and (b) of this section.

(a) Submit the final control plan, including a

description of any devices for air pollution control and

any process changes that you will use to comply with 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 progres s

for achieving final compliance?222

For the final compliance increment of progress, yo u

must complete all process change s and retrofit constructio n

of control devices, as specifie d in the final control plan

,

so that, if the affecte d inciner a tor is brought online, al l

necessary process changes and ai r pollution control device s

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 plan, you

must meet the increments of progress specified in §60.2815.

(b) If you close your incinerator but will restart it

after your final complianc e date, you must complet e

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 t o close you r in c inerator rather tha n

comply with the Stat e plan, sub m it a closure notificatio n,

including the date of closure

, t o the Administrator by th e

date your final control plan is due.

§60.2860 What are the emission limitations for air

curtain incinerators?

(a) After the date th e initial s tack test is require d

or completed (whichever i s ear l ier), you must mee t th e

limitations in paragraphs (a) (1) and ( b 2 ) of this section.

(a) Maintain opacity to less than or equal to 10

percent opacity (as determined by the average of three 1-

hour blocks consisting of te n 6-minute average opacit y223

values), except as described i n paragraph (b) of thi s

section.

(b) Maintain opacity to less than or equal to 35

percent opacity (as determined by the average of three 1-

hour blocks consisting of te n 6-minute average opacit y

values) during the startup perio d that is within th e firs t

30 minutes of operation.

(1) The opacity limitatio n is 10 percent (6

- minut e

average), except as described i n paragraph (a)(2) of thi s

section.

(2) The opacity limitatio n is 35 percent (6

- minut e

average) during the startup peri o d that is within th e firs t

30 minutes of operation.

(b) Except during malfunctions, the requirements of

this subpart apply at al l times

, and each malfunction mus t

not exceed 3 hours.

§60.2865 How must I monitor opacity for air curtain

incinerators?

(a) Use Method 9 of appendi x A of this part t o

determine compliance with the opacity limitation.

(b) Conduct an initia l test fo r opacity as specifie d

in §60.8 no later than 180 days after your final compliance

date.

(c) After the initial test for opacity, conduc t

annual tests no more tha n 12 ca l endar months following th e

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 annual224

opacity tests onsite in eithe r paper copy or electroni c

format, unless the Administrator approves another format,

for at least 5 years.

(b) Make all records available for submittal to the

Administrator or for an inspector's onsite review.

(c) Submit an initial report no later than 60 days

following the initial opacit y test that includes th e

information specified in paragra p hs (c) (1) and (2 ) of thi s

section.

(1) The types of materials you plan to combust in your

air curtain incinerator.

(2) The results ( as determined by the average of

three 1-hour blocks consistin g o f ten each 6-minute average

opacity values ) of the initial opacity tests.

(d) Submit annua l opacity te s t results within 12

months following the previous report.

(e) Submit initial an d annual o p acity test reports a s

electronic or paper copy on or before the applicable

submittal date and kee p a copy onsite for a perio d of 5

years.

Model Rule—Definitions

§60.2875 What definitions must I know?

Terms used but not define d in th i s subpart are define d

in the Clean Air Act and subparts A and B of this part.

Administrator means the Administrator of the U.S.

Environmental Protection Agency or his/her authorized

representative or Administrator of a State Air Pollutio n225

Control Agency.

Affirmative defense means, i n the context of a n

enforcement proceeding, a respo n se or defense put forward

by a defendant, regarding whi c h the defendant has th e

burden of proof, and th e merits of which are independentl y

and objectively evaluated in a judicial or administrative

proceeding.

Agricultural waste means ve g etative agricultura l

materials such as nut and grain hulls and chaff (e.g.,

almond, walnut, peanut, rice

, a n d wheat), bagasse, orchar d

prunings, corn stalks, coffee b e an hulls and grounds, an d

other vegetative waste material s generated as a result o f

agricultural operations.

Air curtain incinerator means an incinerator that

operates by forcefully projecti n g a curtain of air acros s

an open chamber o r pit i n which combustion occurs

.

Incinerators of this type ca n be constructed above or belo w

ground and with or withou t refra c tory walls and floor. (Ai r

curtain incinerators are no t to be confuse d wit h

conventional combustion devices with enclosed fireboxes and

controlled air technology such a s mass burn, modular, an d

fluidized bed combustors.)

Annual heat input means the heat input for the 12

months preceding the compliance demonstration.

Auxiliary fuel means natural gas, liquified petroleum

gas, fuel oil, or diesel fuel.

Average annual heat input rate m e ans annual heat inpu t226

divided by the hours of operation for the 12 months

preceding the compliance demonstration.

Bag leak detection syste m means an instrument that is

capable of monitoring particulate matter loadings in th e

exhaust of a fabric filte r (i. e

., baghouse) in order t o

detect bag failures. A bag lea k detection system includes

,

but is not limited to

, an in s trument that operates o n

triboelectric, light scattering, light transmittance, or

other principle to monitor relative particulate matter

loadings.

Burn-off oven means any rack r e clamation unit, part

reclamation unit, or drum reclam a tion unit. A burn-off ove n

is not an incinerator, waste

- burning kiln, an energ y

recovery unit or a small, rem o te incinerator under thi s

subpart.

Bypass stack means a device used for discharging

combustion gases to avoi d se v ere damage to th e ai r

pollution control device or other equipment.

Calendar quarter means three consecutive months

(nonoverlapping) beginning on: J a nuary 1, April 1

, July 1,

or October 1.

Calendar year means 365 consecu t ive days starting on

January 1 and ending on December 31.

CEMS data during startu p and s hutdown means carbo n

monoxide CEMS data collected du r ing the first 4 hour s o f

operation of energy recovery uni t startup from a col d star t

and the hour of operatio n follow i ng the cessation of wast e

material being fed to th e ener g y recovery unit during a

unit shutdown.227

Chemical recovery unit means combustion units burning

materials to recover chemical constituents or to produc e

chemical compounds where there is an existing commercia l

market for such recovered chemical constituents or

compounds. A chemical recover y u n it is not a n incinerator

,

waste-burning kiln, an energy r ecovery unit or a small

,

remote incinerator under thi s s u bpart. The following seve n

types of units are considered chemical recovery units:

(1) Units burning only pulping liquors (i.e., black

liquor) that are reclaimed in a pulping liquor recover y

process and reused in the pulping process.

(2) Units burning only spent s ulfuric acid used t o

produce virgin sulfuric acid.

(3) Units burning only woo d or c oal feedstock for th e

production of charcoal.

(4) Units burning only manufacturing byproduct

streams/residue containing catalyst metals that are

reclaimed and reused as catalysts or used to produce

commercial grade catalysts.

(5) Units burning only coke t o p r oduce purified carbon

monoxide that is used a s an int e rmediate in the productio n

of other chemical compounds.

(6) Units burning only hydrocar b on liquids or solids

to produce hydrogen, carbo n mo n oxide, synthesis gas, o r

other gases for use in other manufacturing processes.

(7) Units burning only photographic film to recove r

silver.228

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 wo o d products that hav e

been cut or shaped an d include wet, air-dried, and kilndried wood products. Clean lum b er does not include woo d

products that have been painted, pigment-stained, or

pressure-treated by compounds such as chromate copper

arsenate, pentachlorophenol, and creosote.

Commercial and industrial solid waste incineration

(CISWI) unit means any distin c t operating unit of an y

commercial or industrial facil i ty that combusts, o r ha s

combusted in the preceding 6 m o nths, any solid waste a s

that term is defined in 40 CFR p art 241. If the operatin g

unit burns materials other t h an traditional fuels a s

defined in §241.2 that have been discarded, and you do not

keep and produce records as required by §60.2740(u), the

material is a solid waste an d th e operating unit is a CISW I

unit. While not all CISWI units will include all of the

following components, a CISWI u nit includes, but is no t

limited to, the solid wast e feed system, grate system, flu e

gas system, waste hea t recover y equipment, if any

, an d

bottom ash system. The CISWI unit does not include air

pollution control equipment or the stack. The CISWI unit

boundary starts at the solid wa s te hopper (if applicable )

and extends through two areas : t h e combustion unit flue ga s

system, which ends immediately after the last combustio n

chamber or after the wast e heat r ecovery equipment, if any ;

and the combustion unit botto m ash system, which ends a t

the truck loading statio n o r similar equipment tha t229

transfers the ash to final d isposal. The CISWI uni t

includes all ash handling syste m s connected to the botto m

ash handling system. mean s a ny combustion unit tha t

combusts commercial or industria l waste (as defined in thi s

subpart), that is a distinc t operating unit o f an y

commercial or industrial facility (including field erected,

modular, and custom built incine r ation units operating wit h

starved or excess air), and a n y air curtain incinerato r

that is a dis tinct operating unit of any commercial or

industrial facility that does n o t comply with the opacit y

limits under this subpar t a p plicable to air curtai n

incinerators burning commercial or industrial waste. While

not all CISWI units wil l incl u de all of the f ollowin g

components, a CISWI unit includes, but is not limited to,

the commercial or industrial sol i d waste feed system, grat e

system, flue gas system

, waste h eat recovery equipment, if

any, and bottom ash system. The CISWI unit does not include

air pollut ion control equipmen t or the stack. The CISW I

unit boundary starts a t the comm ercial or industrial was te

hopper (if applicable) and exte n ds through two areas: Th e

combustion unit flue ga s syste m

, which ends immediatel y

after the last combustion chamber or after the waste heat

recovery equipment, if any ; and the combustion unit bott om

ash system, which ends at the truck loading station or

similar equipment that transfers the ash to final disposal

.

The CISWI unit include s all as h handling systems connecte d

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, n o r does it include an y

combustion turbine or reciprocating internal combustion

engine.230

Commercial or industrial waste m eans solid waste (as

defined in this subpart) th a t is combusted at an y

commercial or industrial facility using controlled flame

combustion in an enclosed, dist i nct operating unit: Whose

design does not provide fo r ener g y recovery (as defined i n

this subpar t); or operated wi t hout energy recovery (a s

defined in this subpart). Commercial or industrial wast e

also means solid waste (as d efined in this subpart )

combusted in an air curtai n inci n erator that is a distinc t

operating unit of any commercial or industri al facility.

Contained gaseous material mean s gases that are in a

container when that container is combusted.

Continuous monitoring system (CMS) means the total

equipment, required under the emission monitoring sections

in applicable subparts, used to sample and condition (if

applicable), to analyze, an d to provide a permanent reco rd

of emissions or proces s parame t ers. A particulate matter

continuous parameter monitoring s ystem (PM CPMS) i s a ty pe

of CMS.

Cyclonic barrel burner burn barrel means a combustion

device for waste materials that is attached to a 55 gallon,

open-head drum. The device cons i sts of a lid, whic h fit s

onto and encloses the drum

, a nd a blower that force s

combustion air into the dru m in a cyclonic manner t o

enhance the mixing of wast e ma t erial and air. A cycloni c

burn barrel is not an incinerat o r, waste-burning kiln, a n

energy recovery unit or a small

, remote incinerator under

this subpart.

Deviation means any instance i n which an affecte d

source subject to this subpart, or an owner or operator of

such a source:

(1) Fails to meet any requi r ement or obligatio n231

established by this subpart, in c luding but not limited t o

any emission limitation, operating limit, or operator

qualification and accessibility requirements

. ;

(2) Fails to meet an y term o r condition that i s

adopted to implement an appli c able requirement in thi s

subpart and that is include d i n the operating permit fo r

any affected source required to obtain such a permit

. ; or

(3) Fails to meet any emission limitation, operating

limit, or operator qualification and accessibility

requirement in this subpart during startup, shutdown, o r

malfunction, regardless or whet h er or not s uch failure i s

permitted by this subpart.

Dioxins/furans means tetra-through octa

- chlorinated

dibenzo-p-dioxins and dibenzofurans.

Discard means, for purposes o f t h is subpart and 40 CF R

part 60, subpart DDDD, only

, bur n ed in an incineration uni t

without energy recovery.

Drum reclamation unit means a un i t that burns residue s

out of drums (e.g.

, 55 gallo n dr u ms) so that th e drums ca n

be reused.

Energy recovery means the process of recovering

thermal energy from combustio n f o r useful purposes suc h a s

steam generation or process heating.

Energy recovery unit means a combustion unit

combusting solid waste (as that term is defined by the

Adminitrator under Resource Conservation and Recovery Act

in 40 CFR 241) for energy recovery. Energy recovery units

include units that woul d be con s idered boilers and proce ss

heaters if they did not combust solid waste.232

Fabric filter means an add

- on a ir pollution control

device used to captur e particula t e matter by filterin g ga s

streams through filter media, also known as a baghouse.

Energy recovery unit designed to burn biomass

(Biomass) means an energy recovery unit that burns solid

waste, biomass, and non-coa l sol i d materials but les s tha n

10 percent coal, on a heat input basis on an annual

average, either alone o r in com b ination with liquid wast e,

liquid fuel or gaseous fuels.

Energy recovery unit designed to burn coal (Coal)

means an energy recovery unit that burns solid waste and at

least 10 percent coal on a hea t input basis on an annual

average, either alone o r in com b ination with liquid wast e,

liquid fuel or gaseous fuels.

Energy recovery unit designed to burn liquid wastes

material and gas (Liquid/gas) me a ns an energy recovery uni t

that burns a liquid waste with liquid or gaseous fuels not

combined with any solid fuel or waste materials.

Energy recovery unit designe d t o burn solid material s

(Solids) includes energy recovery units designed to bur n

coal and energy recovery units designed to burn biomass.

Fabric filter means an add-on a ir pollution control

device used to captur e particula t e matter by filterin g ga s

streams through filter media, also known as a baghouse.

Foundry sand thermal reclamatio n unit means a typ e o f

part reclamation unit that rem o ves coatings that are o n

foundry sand. A foundry sand thermal reclamation unit is

not an incinerator, waste-burnin g kiln, an energ y recover y233

unit or a small, remote incinerator under this subpart.

Homogeneous wastes are stable, consistent in

formulation, have known fue l p r operties, have a define d

origin, have predictable chemical and physical attributes,

and result in consistent combustion characteristics and

have a consistent emissions profile.

Incinerator means any furnace u s ed in the process o f

combusting solid waste (as th e term is defined b y th e

Administrator under Resource Conservation and Recovery Act

in 40 CFR 241) for the purpose of reducing the volume of

the waste by removing combust i ble matter. Incinerato r

designs include single chamber and two-chamber.

Kiln means an oven or fur n ace, including any

associated preheater or precalciner devices, used for

processing a substance by burnin g

, firing or drying. Kiln s

include cement kilns that pr o duce clinker by heatin g

limestone and other material s f o r subsequent production o f

Portland Cement.

Laboratory analysis unit means u n its that burn sample s

of materials for the purpose of chemical or physical

analysis. A laboratory analysis u nit is not an incinerator

,

waste-burning kiln, an energy r ecovery unit or a small

,

remote incinerator under this subpart.

Low-level radioactive waste means waste material which

contains radioactive nuclides emitting primarily beta or

gamma radiation, or both, in c o ncentrations or quantities

that exceed applicable Federal or State standards for

unrestricted release. Low-level radioactive waste is not

high-level radioactive waste, spent nuclear fuel, or byproduct material as defined b y the Atomic Energy Act o f

1954 (42 U.S.C. 2014(e)(2)).234

Malfunction means any sudden, infrequent, and not

reasonably preventable failure of air pollution control

equipment, process equipment, or a process to operate i n a

normal or usual manner. Failure s that are caused, in part

,

by poor maintenance or careless operation are no t

malfunctions.

Minimum voltage or amperage means 90 percent of the

lowest test-run average volt a ge or amperage to the

electrostatic precipitator measured from the pressure drop

and liquid flow rate monitors during the most recent

particulate matter or mercury performance test

demonstrating compliance with the applicable emission

limits.

Modification or modified CISWI u n it means a CISWI unit

that has been you have change d l a ter than June 1, 2001

, an d

that meets one of two criteria:

(1) The cumulative cost of the changes over the life

of the unit exceeds 50 percent of the original cost of

building and installing the CIS W I unit (not including th e

cost of land) updated to curren t costs (current dollars)

.

To determine what systems ar e w ithin the boundary of th e

CISWI unit used to calculat e these costs, see th e

definition of CISWI unit.

(2) Any physical change in the CISWI unit or change

in the method of operating it that increases the amount of

any air pollutant emitted for which Clean Air Act section

129 or section 111 of the Clean Air Act has established

standards.

Opacity means the degree to whic h emissions reduce th e

transmission of light and obscure the view of an object in

the background.

Operating day means a 24-hour period between 12:0 0235

midnight and the following midni g ht during which any amoun t

of solid waste is combusted at any time in the CISWI unit.

Oxygen analyzer system means all equipment required t o

determine the oxygen content of a gas stream and used to

monitor oxygen in the boiler flue gas or firebox. This

definition includes oxygen trim systems. The source owner

or operator is responsible to in s tall, calibrate, maintain

,

and operate the oxygen analyzer system in accordance wit h

the manufacturer’s recommendations.

Oxygen trim system means a syste m of monitors that i s

used to maintain excess air at the desired level in a

combustion device. A typical sys t em consists of a flu e ga s

oxygen and/or carbon monoxide monitor that automatically

provides a feedback signa l to the combustion ai r

controller.

Part reclamation unit means a un i t that burns coating s

off parts (e.g., tools, equipment) so that the parts can be

reconditioned and reused.

Particulate matter means total particulate matter

emitted from CISWI units as measured by Method 5 or Method

29 of appendix A of this part.

Pathological waste means waste material consisting of

only human or animal remains

, anatomical parts, and/o r

tissue, the bags/containers use d to collect and transport

the waste material, and animal bedding (if applicable).

Performance evaluation means the conduct of relative

accuracy testing, calibration error testing, and other

measurements used in validating the continuous monitoring

system data.236

Performance test means the collection of data

resulting from the executio n o f a test metho d (usuall y

three emission test runs) used to demonstrate compliance

with a relevant emission stan d ard as specified in th e

performance test section of the relevant standard.

Process change means a significant permit revision,

but only with respec t to thos e p ollutant-specific emission

units for which the proposed per m it revision is applicable

,

including but not limited to a change in the air pollution

control devices used to compl y w i th the emission limits fo r

the affected CISWI unit (e.g., change in the sorbent used

for activated carbon injection).

Rack reclamation unit mean s a unit that burns t he

coatings off racks used t o hold s mall items for applicatio n

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 ma y be added or remove d fro m

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 d r yer. 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 begin s on or after June 1

,

2001.

(2) The cumulative cos t of th e construction over the

life of the incineration uni t e xceeds 50 percent of th e237

original cost of building and installing the CISWI uni t

(not including land) updated t o current costs (curren t

dollars). To determine what syst e ms are within the boundar y

of the CISWI unit used to calculate these costs, see the

definition of CISWI unit.

Refuse-derived fuel means a type of municipal soli d

waste produced by processin g mu n icipal solid waste throug h

shredding and size classification. This includes all

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 o f tim e after all waste ha s

been combusted in the primary chamber.

Small, remote incinerator means an incinerator that

combusts solid waste (as tha t term is defined b y th e

Administrator in 40 CFR 241) an d combusts 3 tons per day o r

less solid waste and is more than 25 miles driving distance

to the nearest municipal solid waste landfill.

Solid waste means any garbage, r efuse, sludge from a

waste treatment plant, water sup p ly treatment plant, or ai r

pollution control facility and other discarded material,

including solid, liquid, semisolid, or contained gaseous

material resulting from industrial, comme rcial, 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 unde r section 402 of the Federa l

Water Pollution Control Act, as amended (33 U.S.C. 1342)

,

or source, special nuclear, o r byproduct material a s238

defined by the Atomic Energy Act of 1954, as amended (42

U.S.C. 2014).

Soil treatment unit means a uni t that thermally treats

petroleum–contaminated soils for the sole purpose of sit e

remediation. A soil treatemen t u nit may be direct-fired o r

indirect fired. A soil tre a tment unit is not a n

incinerator, waste-burning kiln, an energy recovery unit o r

a small, remote incinerator under this subpart.

Solid waste incineration unit means a distinct

operating unit of any facilit y w h ich combusts any solid (a s

that term is defined by the Administrator in 40 CFR part

241) waste material from commercial or industrial

establishments or the genera l p u blic (including single an d

multiple residences, hotels and m otels). Such term does no t

include incinerators or othe r u nits required to hav e a

permit under section 3005 o f th e Solid Waste Disposal Act

.

The term "solid waste incinerat i on unit" does not includ e

(A) materials recovery facilities (including primary or

secondary smelters) which comb u st waste for th e primar y

purpose of recovering metals, (B) qualifying small powe r

production facilities, as defined in section 3(17)(C) o f

the Federal Power Act (16 U.S.C

. 769(17)(C)), or qualifying

cogeneration facilities, as defi n ed in section 3(18)(B ) o f

the Federal Power Act (16 U.S.C. 796(18)(B)), which burn

homogeneous waste (such as units which burn tires or used

oil, but not includin g refu s e-derived fuel) for th e

production of electric energy o r in the case of qualifyin g

cogeneration facilities which burn homogeneous waste for

the production of electric ene r gy and steam or form s o f

useful energy (such as heat ) whi c h are used for industrial

,239

commercial, heating or cooling p u rposes, or (C) air curtai n

incinerators provided that such i ncinerators only burn woo d

wastes, yard wastes and clean lumber and that such air

curtain incinerators comply wit h opacity limitations t o b e

established by the Administrator by rule.

Space heater means a usually p o rtable appliance for

heating a relatively small area. A space heater is not an

incinerator, waste-burning kiln, an energy recovery unit o r

a small, remote incinerator under this subpart.

Standard conditions, when referring to units of

measure, means a temperature of 68 °F (20 °C) and a

pressure of 1 atmosphere (101.3 kilopascals).

Startup period means the period of time between the

activation of the system and the first charge to the unit.

Waste-burning kiln means a kil n that is heated, i n

whole or in part, by combustin g s olid waste (as the term i s

defined by the Administrator in 40 CFR 241). A waste-burning

kiln does not include a kiln th a t is feeding non-hazardou s

secondary ingredients exclusivel y into the col d end o f th e

kiln.

Wet scrubber means a n add-on a ir pollution contro l

device that uses utilizes an aqu e ous or alkaline scrubbing

liquor to collect particulate matter (including nonvaporous

metals and condensed organics ) and/or to absor b an d

neutralize acid gases.

Wood waste means untreate d woo d and untreated woo d240

products, including tree stump s (whole or chipped), trees

,

tree limbs (whole or chipped )

, bark, sawdust, chips

,

scraps, slabs, millings, an d sha v ings. Wood waste doe s no t

include:

(1) Grass, grass clippings, bushes, shrubs, and

clippings from bushes and shrubs from residential,

commercial/retail, institutional, or industrial sources as

part of maintaining yards or other private or public lands.

(2) Construction, renovation, or demolition wastes.

(3) Clean lumber.

Table 1 to Subpart DDD D of Part 6 0—Model Rule—Increments o f

Progress and Compliance Schedules

Comply with these increments

of progress By these dates a

Increment 1— Submit fina l

control plan (Dates to be specified i n

s S tate plan)

Increment 2—Final compliance (Dates to be specified i n

s S tate plan) b

a Site-specific schedules can b e used at the discretio n o f

the state.

b The date can be n o later than 3 years after the effecti ve

date of s S tate plan approval or December 1, 2005 for CISWI

units that commenced constructio n on or before November 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 THE DATE OF PUBLICATION OF THE FINAL

RULE IN THE FEDERA L REGISTER ] for CISWI unit s tha t

commenced construction on or bef o re June 4, 2010

. Fo r smal l

remote incinerators, the date can be no later than 3 years

after the effective date o f ap p roval of a revised stat e

plan or March 21, 2016 for small remote incinerator CISWI241

units that commenced construct i on on or befor e June 4,

2010.

Table 2 to Subpar t DDDD o f P a rt 60—Model Rule—Emissio n

Limitations That Apply Befor e [ Date to be specifie d i n

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

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

( For Method 26,

collect a

minimum volume

of 120 liters Performance

test (Method 26

or 26A at 40

CFR part 60, of

appendix A -8 of242

per run. For

Method 26A,

collect a 1 hour

minimumvolume

of 1 dry

standard cubic

meter sample

time per run) this part )

Lead 0.04

milligrams

per dry

standard

cubic meter 3- run average ( 1

hour minimum

sample time pe r

run) Performance

test (Method 2 9

of appendix A

of this part)

Mercury 0.47

milligrams

per dry

standard

cubic meter 3-run average (1

hour minimum

sample time pe r

run) Performance

test (Method 29

or 30B at 40

CFR part 60, of

appendix A -8 o f

this part ) or

ASTM D6784-02

(Reapproved

2008) c

Opacity 10 percent Three 1-hour

blocks

consisting of

ten 6-minute

average opacity

values 6

- minute

averages Performance

test (Method 9

at 40 CFR part

60, of appendix

A -4 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 at 40 CFR243

part 60, of

appendix A -4 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 pe r

run) Performance

test (Method 6

or 6c o f

appendix A o f

this part)

a All emission limitations (excep t for opacity) are measure d

at 7 percent oxygen, dry basis at standard conditions.

b The date specified i n the stat e plan can be n o later tha n

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].

c Incorporated by reference, see §60.17.

Table 3 to Subpart DDDD o f Pa r t 60—Model Rule—Operating

Limits for Wet Scrubbers

For these

operating

parameters You must

establish

these

operating

limits And monitor using these minimum

frequencies

Data

measurement Data

recording Averaging time

Charge rate Maximum

charge

rate Continuous Every

hour Daily (batch

units). 3- hour

rolling

(continuous and244

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 o f Part 60—Model Rule—Toxic

Equivalency Factors

Dioxin/furan congener isomer 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-p- 0.1245

dioxin

1,2,3,4,6,7,8-heptachlorinated

dibenzo-p-dioxin 0.01

octachlorinated dibenzo-p-dioxin 0.001

2,3,7,8-tetrachlorinated dibenzofuran 0.1

2,3,4,7,8-pentachlorinated

dibenzofuran 0.5

1,2,3,7,8-pentachlorinated

dibenzofuran 0.05

1,2,3,4,7,8-hexachlorinated

dibenzofuran 0.1

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

dibenzofuran 0.1

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

dibenzofuran 0.1

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

dibenzofuran 0.1

1,2,3,4,6,7,8-heptachlorinated

dibenzofuran 0.01

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

dibenzofuran 0.01

octachlorinated dibenzofuran 0.001

Table 5 to Subpart DDD D of Par t 60—Model Rule—Summary o f

Reporting Requirements a246

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

test • Complete tes t

report for th e

initial

performance test

• The values fo r

the site- specific

operating limits

• Installation o f

bag leak

detection systems

for fabric

filters §60.2760.

Annual

Report No later than

12 months

following the

subm ission of

the initial

test report.

Subsequent

reports are

to be

submitted no

more than 12

months

following the

previous • Name and

address

• Statement and

signature by

responsible

official

• Date of report

• Values for the

operating limits

• If no

d eviations or

malfunctions were

reported, a

statement that no §§60.2765 and

60.2770.247

report deviations

occurred during

the reporting

period

• Highest

recorded 3-hour

average and the

lowest 3-hour

average, as

applicable, for

each operating

parameter

recorded for the

calendar year

being reported

• Information for

deviations or

malfunctions

recorded under

§60.2740(b)(6)

and (c) through

(e)

• 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 that248

the requirements

of

§60. 2720 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

• If you are

conducting

performance tests

once every 3

years consistent

with §60.2720(a),

the date of the

last 2

performance

tests, a

comparison of the

emission level

you achieved in

the last 2

performance tests

to the 75 percent

emission limit

threshold

required in

§60.2720(a) and a

statement as to

whether there249

have been any

operational

changes since the

last performance

test that could

increase

emissions.

Emission

L l imitation

or

O o perating

L l imit

d D eviation

r R eport 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 for 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

• Whether each

deviation

occurred during a

period of

startup,

shutdown, or

malfunction §§60.2775 and

60.2780.250

Qualified

Operator

Deviation

Notification Within 10

days of

deviation • Statement o f

cause of

deviation

• Description o f

efforts to hav e

an accessible

qualified

operator

• The date a

qualified

operator will b e

accessible §60.2785(a)(1).

Qualified

Operator

Deviation

Status

Report Every 4 weeks

following

deviation • Description o f

efforts to hav e

an accessible

qualified

operator

• The date a

qualified

operator will b e

accessible

• Request fo r

app roval to

continue

operation §60.2785(a)(2).

Qualified

Operator

Deviation

Notification

of Resumed

Operation Prior to

resuming

operation • Notification

that you ar e

resuming

operation §60.2785(b)

a This table is onl y a summary, s ee the referenced section s251

of the rule for the complete requirements.

Table 6 to Subpart DDDD of Part 60—Model Rule—Emission

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 0.0026

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

2 dry standard

cubic meters) Performance

test (Method

29 at 40 CFR

part 60,

appendix A8). Use ICPMS

for the

analytical

finish.

Carbon

monoxide 36 parts per

million dry

volume 3-run average (1

hour minimum

sample time per

run) Performance

test (Method

10 at 40 CFR

part 60,

appendix A4).

Dioxins/furans

(total mass

basis) 4.6

nanograms

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

2 dry standard

cubic meters) Performance

test (Method

23 at 40 CFR

part 60,

appendix A7).

Dioxins/furans

(toxic 0.13

nanograms 3-run average

(collect a Performance

test (Method252

For the air

pollutant You must

meet this

emission

limitation b Using this

averaging time And

determining

compliance

using this

method

equivalency

basis) per dry

standard

cubic meter minimum volume of

2 dry standard

cubic meters) 23 at 40 CFR

part 60,

appendix A7).

Hydrogen

chloride 29 parts per

million dry

volume 3-run average

(For Method 26,

collect a minimum

volume of 60

liters per run.

For Method 26A,

collect a minimum

volume of 1 dry

standard cubic

meter per run) Performance

test (Method

26 or 26A at

40 CFR part

60, appendix

A-8).

Lead 0.0036

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume of

2 dry standard

cubic meters) Performance

test (Method

29 at 40 CFR

part 60,

appendix A8). Use ICPMS

for the

analytical

finish.

Mercury 0.0054

milligrams

per dry

standard

cubic meter 3-run average

(For Method 29 an

ASTM D6784-02

(Reapproved

2008) b , collect a Performance

test (Method

29 or 30B at

40 CFR part

60, appendix253

For the air

pollutant You must

meet this

emission

limitation b Using this

averaging time And

determining

compliance

using this

method

minimum volume of

2 dry standard

cubic meters per

run. For Method

30B, collect a

minimum sample as

specified in

Method 30B at 40

CFR part 60,

appendix A) A-8) or ASTM

D6784-02

(Reapproved

2008) c

.

Oxides of

nitrogen 53 parts per

million dry

volume 3-run average

(for Method 7E, 1

hour minimum

sample time per

run) Performance

test (Method

7 or 7E at 40

CFR part 60,

appendix A4).

Particulate

matter

filterable 34

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 at 40

CFR part 60,

appendix A-3

or appendix

A-8).

Sulfur dioxide 11 parts per

million dry

volume 3-run average (1

hour minimum

sample time per

run) Performance

test (Method

6 or 6c at 40

CFR part 60,

appendix A-4.254

For the air

pollutant You must

meet this

emission

limitation b Using this

averaging time And

determining

compliance

using this

method

Fugitive ash Visible

emissions

for no more

than 5% of

the hourly

observation

period Three 1-hour

observation

periods Visible

emission test

(Method 22 at

40 CFR part

60, appendix

A-7).

a The dat e specified i n the s t ate plan can b e no lat er

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].

b All emission limitations are measured at 7 percent

oxygen, dry basis at standard conditions. For

dioxins/furans, you must meet e i ther the total mass basi s

limit or the toxic equivalency basis limit.

c Incorporated by reference, see §60.17.

Table 7 to Subpar t DDDD o f P a rt 60—Model Rule—Emissio n

Limitations That Apply To Energy Recovery Units After [Dat e

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 Liquid/Gas Solids255

For the air

pollutant You must meet this

emission

limitation b Using this

averaging time And

determining

compliance

Cadmium 0.023

milligrams

per dry

standard

cubic meter Biomass -

0.00078

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 2 dry

standard cubic

meters) Performance

test (Method

29 at 40 CFR

part 60,

appendix A8). Use ICPMS

for the

analytical

finish. Coal - 0.058

milligrams

per dry

standard

cubic meter

Carbon

monoxide 36 parts

per million

dry volume Biomass –

490 parts

per million

dry volume 3-run average

(1 hour

minimum sample

time per run) Performance

test (Method

10 at 40 CFR

part 60,

appendix A4). Coal – 46

parts per

million dry

volume

Dioxins/furans

(total mass

basis) 2.9

nanograms

per dry

standard

cubic meter Biomass -

0.52

nanograms

per dry

standard

cubic meter c 3-run average

(collect a

minimum volume

of 1 dry

standard cubic

meter) Performance

test (Method

23 at 40 CFR

part 60,

appendix A7).

Coal -0.51

nanograms

per dry

standard

cubic meter c256

For the air

pollutant You must meet this

emission

limitation b Using this

averaging time And

determining

compliance

Dioxins/furans

(toxic

equivalency

basis) 0.32

nanograms

per dry

standard

cubic meter Biomass -

0.12

nanograms

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 4 dry

standard cubic

meters) Performance

test (Method

23 at 40 CFR

part 60,

appendix A7).

Coal - 0.075

nanograms

per dry

standard

cubic meter c

Hydrogen

chloride 14 parts

per million

dry volume 0.50 parts

per million

dry volume 3-run average

(for Method

26, collect a

minimum of 120

liters; for

Method 26A,

collect a

minimum volume

of 1 dry

standard cubic

meter) Performance

test (Method

26 or 26A at

40 CFR part

60, appendix

A-8).

Lead 0.096

milligrams

per dry

standard

cubic meter Biomass -

0.0019

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 2 dry

standard cubic

meters) Performance

test (Method

29 at 40 CFR

part 60,

appendix A8). Use ICPMS257

For the air

pollutant You must meet this

emission

limitation b Using this

averaging time And

determining

compliance

Coal -

0.0031

milligrams

per dry

standard

cubic meter for the

analytical

finish.

Mercury 0.031

milligrams

per dry

standard

cubic meter 0.0020

milligrams

per dry

standard

cubic meter 3-run average

(For Method 29

and ASTM

D6784-02

(Reapproved

2008) b

,

collect a

minimum volume

of 2 dry

standard cubic

meters per

run. For

Method 30B,

collect a

minimum sample

as specified

in Method 30B

at 40 CFR part

60, appendix

A) Performance

test (Method

29 or 30B at

40 CFR part

60, appendix

A-8) or ASTM

D6784-02

(Reapproved

2008) d

.

Oxides of

nitrogen 76 parts

per million

dry volume Biomass –

290 parts

per million

dry volume 3-run average

(for Method

7E, 1 hour

minimum sample Performance

test (Method

7 or 7E at 40

CFR part 60,258

For the air

pollutant You must meet this

emission

limitation b Using this

averaging time And

determining

compliance

Coal – 340

parts per

million dry

volume time per run) appendix A4).

Particulate

matter

filterable 110

milligrams

per dry

standard

cubic meter Biomass - 11

milligrams

per dry

standard

cubic meter

or 30-day

rolling

average if

PM CEMS is

required or

being used 3-run average

(collect a

minimum volume

of 1 dry

standard cubic

meter) Performance

test (Method

5 or 29 at 40

CFR part 60,

appendix A-3

or appendix

A-8) if the

unit has a

design

capacity less

than or equal

to 250

MMBtu/hr; or

PM CEMS

(performance

specification

11 of

appendix B

and procedure

2 of appendix

F of this

part) if the

unit has a

design

capacity

greater than

250 MMBtu/hr. Coal - 86

milligrams

per dry

standard

cubic meter

or 30-day

rolling

average if

PM CEMS is

required or

being used259

For the air

pollutant You must meet this

emission

limitation b Using this

averaging time And

determining

compliance

Use Method 5

or 5I of

Appendix A of

this part and

collect a

minimum

sample volume

of 1 dscm for

the PM CEMS

correlation

testing.

Sulfur dioxide 720 parts

per million

dry volume Biomass –

7.3 parts

per million

dry volume 3-run average

(1 hour

minimum sample

time per run) Performance

test (Method

6 or 6c at 40

CFR part 60,

appendix A- 4. Coal – 650

parts per

million dry

volume

Fugitive ash Visible

emissions

for no more

than 5

percent of

the hourly

observation

period Visible

emissions

for no more

than 5

percent of

the hourly

observation

period Three 1-hour

observation

periods Visible

emission test

(Method 22 at

40 CFR part

60, appendix

A-7).

a The date specifie d in th e stat e plan can b e no late r tha n260

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]

b All emission limitation s ( except for opacity) ar e

measured at 7 percent oxygen

, dry basis at standar d

conditions. For dioxins/furans, you must meet either th e

total mass basis limit or th e toxic equivalency basi s

limit.

c If you ar e conducting st a ck tests to demonstra te

compliance and your performance tests for this pollutan t

for at least 2 consecutive years show that your emissions

are at or below this limit, you can skip testing according

to §60.2720 if all of the other provision of §60.2720 are

met. For all other pollutants that do not contain a

footnote “c”, your performance t e sts for this pollutant fo r

at least 2 consecutive year s mus t show that your emission s

are at or 75 percent of this limit in order to qualify for

skip testing.

d Incorporated by reference, see §60.17.

Table 8 to Subpart DDDD of Part 60—Model Rule—Emission

Limitations That Apply to Waste-burning Kilns 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 0.00082

milligrams

per dry

standard

cubic meter 3-run

average

(collect a

minimum

volume of 2

dry standard

cubic Performance test

(Method 29 at 40

CFR part 60,

appendix A-8).261

For the air

pollutant You must meet

this emission

limitation b Using this

averaging

time And determining

compliance using

this method

meters)

Carbon

monoxide 120 (long

kilns) / 410

(preheater /

precalciner)

parts per

million dry

volume 3-run

average (1

hour minimum

sample time

per run) Performance test

(Method 10 at 40

CFR part 60,

appendix A-4).

Dioxins/furans

(total mass

basis) 3.6 nanograms

per dry

standard

cubic meter 3-run

average

(collect a

minimum

volume of 1

dry standard

cubic

meters) Performance test

(Method 23 at 40

CFR part 60,

appendix A-7).

Dioxins/furans

(toxic

equivalency

basis) 0.075

nanograms per

dry standard

cubic meter c 3-run

average

(collect a

minimum

volume of 1

dry standard

cubic meter) Performance test

(Method 23 at 40

CFR part 60,

appendix A-7).

Hydrogen

chloride 3.0 parts per

million dry

volume c 3-run

average

(collect a

minimum

volume of 1

dry standard

cubic meter) Performance test

(Method 321 at 40

CFR part 63,

appendix A of this

part) or HCl CEMS

if a wet scrubber

is not used.262

For the air

pollutant You must meet

this emission

limitation b Using this

averaging

time And determining

compliance using

this method

or 30-day

rolling

average if

HCl CEMS is

being used

Lead 0.0043

milligrams

per dry

standard

cubic meter 3-run

average

(collect a

minimum

volume of 2

dry standard

cubic

meters) Performance test

(Method 29 at 40

CFR part 60,

appendix A-8).

Mercury 0.011

milligrams

per dry

standard

cubic meter 30-day

rolling

average Mercury CEMS or

sorbent trap

monitoring system

(performance

specification 12A

or 12B,

respectively, of

appendix B of this

part.)

Oxides of

nitrogen 630 parts per

million dry

volume 3-run

average ( for

Method 7E, 1

hour minimum

sample time

per run) Performance test

(Method 7 or 7E at

40 CFR part 60,

appendix A-4). Use

a span gas with a

concentration of

1000 ppm or less.

Particulate 9.2 30-day PM CEMS263

For the air

pollutant You must meet

this emission

limitation b Using this

averaging

time And determining

compliance using

this method

matter

filterable milligrams

per dry

standard

cubic meter rolling

average (performance

specification 11 of

appendix B and

procedure 2 of

appendix F of this

part; Use Method 5

or 5I of Appendix A

of this part and

collect a minimum

sample volume of 2

dscm for the PM

CEMS correlation

testing.).

Sulfur dioxide 830 parts per

million dry

volume 3-run

average ( for

Method 6,

collect a

minimum of

20 liters;

for Method

6C, 1 hour

minimum

sample time

per run) Performance test

(Method 6 or 6c at

40 CFR part 60,

appendix A-4).

a The date specifie d in th e stat e plan can b e no late r tha n

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]

b All emission limitations are measured at 7 percent

oxygen, dry basis at standard conditions. For

dioxins/furans, you must meet e i ther the total mass basi s264

limit or the toxic equivalency basis limit.

c If you ar e conducting st a ck tests to demonstra te

compliance and your performance tests for this pollutan t

for at least 2 consecutive years show that your emissions

are at or below this limit, you can skip testing according

to §60.2720 if all of the other provision of §60.2720 are

met. For all other pollutants that do not contain a

footnote “c”, your performance t e sts for this pollutant fo r

at least 2 consecutive year s mus t show that your emission s

are at or 75 percent of this limit in order to qualify for

skip testing.

Table 9 to Subpart DDDD of Part 60—Model Rule—Emission

Limitations That Apply to Small, Remote Incinerators 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 0.61

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 1 dry

standard cubic

meter) Performance

test (Method 29

at 40 CFR part

60, appendix A8).

Carbon

monoxide 20 parts per

million dry

volume 3-run average

(1 hour minimum

sample time per

run) Performance

test (Method 10

at 40 CFR part

60, appendix A4).

Dioxins/furans 1,200 3-run average Performance265

For the air

pollutant You must meet

this emission

limitation b Using this

averaging time And determining

compliance

using this

method

(total mass

basis) nanograms per

dry standard

cubic meter (collect a

minimum volume

of 1 dry

standard cubic

meter) test (Method 23

at 40 CFR part

60, appendix A7).

Dioxins/furans

(toxic

equivalency

basis) 57 nanograms

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 1 dry

standard cubic

meter) Performance

test (Method 23

at 40 CFR part

60, appendix A7).

Hydrogen

chloride 220 parts per

million dry

volume 3-run average

(For Method 26,

collect a

minimum volume

of 120 liters

per run. For

Method 26A,

collect a

minimum volume

of 1 dry

standard cubic

meter per run) Performance

test (Method 26

or 26A at 40

CFR part 60,

appendix A-8).

Lead 2.7

milligrams

per dry

standard

cubic meter 3-run average

(collect a

minimum volume

of 1 dry

standard cubic

meter) Performance

test (Method 29

at 40 CFR part

60, appendix A8).266

For the air

pollutant You must meet

this emission

limitation b Using this

averaging time And determining

compliance

using this

method

Mercury 0.0057

milligrams

per dry

standard

cubic meter 3-run average

(For Method 29

and ASTM D6784-

02 (Reapproved

2008) b , collect

a minimum

volume of 2 dry

standard cubic

meters per run.

For Method 30B,

collect a

minimum sample

as specified in

Method 30B at

40 CFR part 60,

appendix A) Performance

test (Method 29

or 30B at 40

CFR part 60,

appendix A-8)

or ASTM D6784-

02 (Reapproved

2008) c

.

Oxides of

nitrogen 240 parts per

million dry

volume 3-run average

( for Method 7E,

1 hour minimum

sample time per

run) Performance

test (Method 7

or 7E at 40 CFR

part 60,

appendix A-4).

Particulate

matter

filterable 230

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 at 40 CFR

part 60,

appendix A- 3 or

appendix A-8).

Sulfur dioxide 420 parts per

million dry 3-run average

(for Method 6, Performance

test (Method 6267

For the air

pollutant You must meet

this emission

limitation b Using this

averaging time And determining

compliance

using this

method

volume collect a

minimum of 20

liters per run;

for Method 6C,

1 hour minimum

sample time per

run) or 6c at 40 CFR

part 60,

appendix A-4).

Fugitive ash Visible

emissions for

no more than

5 percent of

the hourly

observation

period Three 1-hour

observation

periods Visible

emission test

(Method 22 at

40 CFR part 60,

appendix A-7).

a The date specifie d in th e stat e plan can b e no late r tha n

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].

b All emission limitation s ( except for opacity) ar e

measured at 7 percent oxygen

, dry basis at standar d

conditions. For dioxins/furans, you must meet either th e

total mass basis limit or th e toxic equivalency basi s

limit.

c Incorporated by reference, see §60.17.