reglab/statecodes huggingface dataset:
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 119 - Motor Vehicle Fuel Volatility Requirements › Section 096-119-3 - Prohibition

Current through 2024-29, July 17, 2024
No owner or operator of any bulk gasoline terminal, nor any
				  person who delivers gasoline directly to a gasoline service station or a bulk
				  gasoline plant, shall dispense, sell, or supply as fuel for motor vehicles any
				  gasoline having a RVP greater than 9.0 pounds per square inch during the period
				  from May 1 through September 15 of any calendar year.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 119 - Motor Vehicle Fuel Volatility Requirements › Section 096-119-4 - Reid Vapor Pressure Testing

Current through 2024-29, July 17, 2024
For purposes of showing compliance with this regulation,
				  sampling shall be conducted using one of the sampling methodologies specified
				  in ASTM D4057 as published in June of 2022, ASTM D5842 as published in December
				  of 2019, or ASTM D4177 as published in August of 2022; and any emission test or
				  fuel test required by the Department shall be conducted in accordance with ASTM
				  D5191 as published in August of 2022, or any other method approved by the
				  Commissioner and the United States Environmental Protection Agency.
Copies of the materials incorporated by reference are
					 available from the Department by calling
					 207-287-2811.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 119 - Motor Vehicle Fuel Volatility Requirements › Section 096-119-5 - Records

Current through 2024-29, July 17, 2024
Any owner or operator of a bulk gasoline terminal shall
				  maintain records of the RVP, oxygen content, oxygenate, benzene, aromatics, and
				  sulfur content for each shipment of gasoline delivered to such terminal. Any
				  person who delivers gasoline directly to a gasoline service station or bulk
				  gasoline plant, and any owner of a gasoline service station or bulk gasoline
				  plant, shall maintain records which show at a minimum the RVP of each shipment
				  of gasoline received, the date on which the gasoline is received, and the
				  identity of the person receiving the gasoline. Such records shall be maintained
				  for at least three years and shall be available for inspection during normal
				  business hours, and copies shall be provided to the Department upon
				  request
Any owner or operator of a bulk gasoline terminal shall
				  report to the Department on a quarterly basis data on the RVP, oxygen content,
				  oxygenate, benzene, aromatics, and sulfur content for each shipment of gasoline
				  received by such terminal.
Any company with more than one gasoline dispensing facility
				  may maintain such records at its central office. However, each gasoline
				  dispensing facility of the company must maintain records on the premises for at
				  least the most recent 12-month period.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 119 - Motor Vehicle Fuel Volatility Requirements › Section 096-119-6 - Severability

Current through 2024-29, July 17, 2024
Each Section and Subsection of this Chapter shall be deemed
				  severable, and in the event that any Section of this Chapter is held invalid,
				  the remainder shall continue in full force and effect.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-1 - Scope

Current through 2024-29, July 17, 2024
A.This regulation shall be effective in all
				ambient air quality control regions in the State of Maine.
B.This regulation applies to tank trucks that
				transport and receive gasoline from a bulk gasoline terminal and/or
				plant.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-2 - Definitions

Current through 2024-29, July 17, 2024
A.
Lower Explosive Limit.
"Lower
				Explosive Limit" (LEL) means the concentration above which an explosion of a
				combustible gas can take place.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-3 - Prohibition

Current through 2024-29, July 17, 2024
A. After May 1, 1989, no person owning,
				leasing, or controlling a tank truck excluding any tank truck with a total
				capacity of less than 3500 gallons including all of its compartments which was
				put into service prior to May 22, 1991 that carries gasoline and receives fuel
				from a bulk gasoline terminal subject to Chapter 112 of the Department's
				regulations shall permit or suffer the tank truck to be loaded or unloaded
				unless the tank truck:
(1) has been certified
				as leak-tight according to the procedure specified in Section 5 below;
				and
(2) displays the initials "DEP"
				attached to both the left and right bulkhead of the tank truck in contrasting
				letters that are no less than 2 inches high and displays the date that the test
				was conducted and that the certification expires not more than 12 months after
				the certification test date.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-4 - Tightness Standard

Current through 2024-29, July 17, 2024
A. A tank truck
				subject to the provisions of this Chapter may sustain a pressure change of no
				more than 3 inches of water over five consecutive minutes when pressurized to a
				gauge pressure of 18 inches of water or when evacuated to a gauge pressure of 6
				inches of water when tested using the procedure specified in Section 5.
B. A tank truck certified
				according to Section 5 must remain leak-tight for the 12 months following the
				certification test. To verify that this requirement is being met, spot checks
				with a combustible gas detector must not reveal readings equal to or greater
				than 100 percent LEL (measured as 2.2 percent propane or equivalent percent of
				another calibration gas by volume in air) when measured at a distance of one
				inch (2.5 cm) from potential leak sources, and no visible or audible liquid or
				vapor leaks must be observed.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-5 - Annual Certification Test

Current through 2024-29, July 17, 2024
A tank truck subject to the provisions of this regulation
				  must be tested annually by the owner or his agent using Reference Method 27 (as
				  amended and defined in 40 CFR 60 Appendix A, Method 27), or any other methods
				  as approved by the Department and EPA. The Department must be informed at least
				  24 hours before each certification test.
The owner or his agent conducting the certification test must
				  be registered with the Department.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-6 - Compliance Provisions

Current through 2024-29, July 17, 2024
The owner or operator of any tank truck that fails to meet
				  any of these requirements shall repair and retest the tank truck within 15
				  days. No owner or operator of any tank truck may use or suffer to be used any
				  tank truck which fails to meet all the requirements of this regulation after
				  such retesting.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-7 - Spot Inspection Tests

Current through 2024-29, July 17, 2024
The Department may, at any time without announcement, measure
				  the back pressure during the loading of tank trucks at the loading rack or the
				  emissions (as percent LEL) from a tank truck using a combustible gas detector
				  to determine the compliance of the tank trucks with the requirements set forth
				  above. The leak tightness of a tank truck shall be measured by use of a
				  gasoline leak detection technique which uses a combustible gas detector or by
				  use of such other means as approved by the Department.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-8 - Records

Current through 2024-29, July 17, 2024
Any person owning, leasing, or controlling the day-to-day
				  activities of a tank truck subject to the provisions of this regulation shall
				  maintain the following records:
A. The
				tank identification number (the manufacturer's serial number, vehicle
				identification number (VIN), and/or the owner's identification
				number);
B. The calendar year
				during which the tank was manufactured;
C. The date and location of the
				pressure-vacuum test; if failed, then the date and location of the retest must
				be recorded as well;
D. The name,
				title, and telephone number of the person who conducted the test, and the name
				and address of the company where the person is employed; and
E. A copy of the test record showing the
				following:
(1) the tank pressure at the start
				of the pressure test;
(2) the tank
				pressure at the end of the pressure test;
(3) the tank pressure at the start of the
				vacuum test;
(4) the tank pressure
				at the end of the vacuum test; and
(5) a list of all repairs which were made to
				the tank truck to enable it to pass all applicable requirements of the test
				method.
Copies of the records are to be retained by the owner or
				  operator of the tank truck for a minimum of two years after the date on which
				  the test was conducted. These records shall be available for inspection during
				  normal business hours and copies shall be provided to the Department and/or EPA
				  upon request.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 120 - GASOLINE TANK TRUCK TIGHTNESS SELF-CERTIFICATION › Section 096-120-9 - Equivalency

Current through 2024-29, July 17, 2024
At the discretion of the Department, the requirements for
				  testing and marking gasoline transport vehicles subject to this Chapter may be
				  satisfied if the vehicle undergoes equivalent certification in another
				  state.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 121 - EMISSION LIMITATIONS AND EMISSION TESTING OF RESOURCE RECOVERY FACILITIES › Section 096-121-1 - Scope and Applicability

Current through 2024-29, July 17, 2024
This regulation shall be applicable in all ambient air
				  quality control regions in the State of Maine and shall apply to all new,
				  existing, and modified resource recovery facilities.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 121 - EMISSION LIMITATIONS AND EMISSION TESTING OF RESOURCE RECOVERY FACILITIES › Section 096-121-3 - Incorporation by Reference

Current through 2024-29, July 17, 2024
As indicated in this Chapter, portions of federal regulations
				  codified at 40 C.F.R. Part 60, Subparts A, B, Cb, Eb, and BBBB and Appendices,
				  as amended through July 1, 2018, have been incorporated by reference. This
				  includes the following subparts from 40 C.F.R. Part 60:
Subpart A,
General
				  Provisions
;
Subpart B,
Adoption and Submittal of
				  State Plans for Designated Facilities
;
Subpart Cb,
Emission Guidelines and
				  Compliance Times for Large Municipal Waste Combustors constructed on or before
				  September 20, 1994
;
Subpart Eb,
Standards of Performance for
				  Large Municipal Waste Combustors for which construction commenced after
				  September 20, 1994 or for which modification or reconstruction commenced after
				  June 19, 1996
;
Subpart BBBB,
Emission Guidelines and
				  Compliance Times for Small Municipal Waste Combustion units constructed on or
				  before August 30, 1999
.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 121 - EMISSION LIMITATIONS AND EMISSION TESTING OF RESOURCE RECOVERY FACILITIES › Section 096-121-4 - Definitions

Current through 2024-29, July 17, 2024
A.
Class I Unit.
"Class I Unit"
				means a small municipal waste combustion unit with aggregate plant combustion
				capacity greater than 250 tons per day of municipal solid waste.
B.
Class II Unit.
"Class II
				Unit" means a small municipal waste combustion unit with aggregate plant
				combustion capacity no more than 250 tons per day of municipal solid
				waste.
C.
Commercial
				Operation.
"Commercial Operation" means the time, not to exceed 180 days
				after initial startup, after which the emission unit achieves operation at the
				maximum production rate at which it will be operated.
D.
Dioxins/furans.
"Dioxins/furansmeans tetra- through octa-chlorinated dibenzo-p-dioxins and
				dibenzofurans, (PCDDs and PCDFs).
E.
Large Municipal Waste Combustor
				Unit.
"Large Municipal Waste Combustor Unit" means a municipal waste
				combustor unit with a maximum municipal solid waste charging rate greater than
				250 tons per day.
F.
Resource
				Recovery Facility.
"Resource Recovery Facility" means any building,
				structure, or installation where municipal wastes are incinerated to produce
				usable energy.
G. The definitions
				contained in and referred to in 40 C.F.R. Part 60, Subparts Cb, Eb, and BBBB
				are hereby incorporated by reference.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 121 - EMISSION LIMITATIONS AND EMISSION TESTING OF RESOURCE RECOVERY FACILITIES › Section 096-121-6 - Large Municipal Waste Combustor Units Subject to 40 C.F.R. Part 60, Subpart Eb

Current through 2024-29, July 17, 2024
For all resource recovery facilities defined as large
				  municipal waste combustors for which construction is commenced after September
				  20, 1994, or for which modification or reconstruction is commenced after June
				  19, 1996, the following shall apply:
A.
Emission limitations
and
				other requirements as specified in 40 C.F.R. Part 60, Subpart Eb; and the
				following:
Dioxins/Furans.
The emission limit for
				  dioxins/furans contained in the gases discharged to the atmosphere from a
				  designated unit constructed, reconstructed, or modified prior to September 20,
				  1994, is 25 nanograms per dry standard cubic meter (total mass), corrected to 7
				  percent oxygen.
For any unit constructed, reconstructed, or modified after
				  September 20, 1994, the emission limit shall be 13 nanograms per dry standards
				  cubic meter (total mass), corrected to 7 percent oxygen.
B.
Performance Testing
				Requirements
Testing during the first two (2) years, following 180 days
				  after initial startup of facility operations, must be conducted at least once
				  in every six-month period, with a minimum of three months between performance
				  tests.
In addition to the performance testing required in 40 C.F.R.
				  Part 60, Subpart Eb, large municipal waste combustor units shall conduct
				  emissions testing for arsenic, nickel, chromium, and beryllium using EPA Method
				  29 (40 C.F.R. Part 60, Appendix A). In no case shall the interval between
				  testing exceed three years.
C.
Reporting and Recordkeeping
				Requirements
All applicable reports required to be submitted under 40
				  C.F.R. Part 60, Subpart Eb shall be submitted to the Department on a quarterly
				  basis within (30) days of the last date of the reporting period.
All emission and performance test reports shall be submitted
				  to the Department within sixty (60) days from the date of test
				  completion.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 121 - EMISSION LIMITATIONS AND EMISSION TESTING OF RESOURCE RECOVERY FACILITIES › Section 096-121-7 - Small Municipal Waste Combustor Class I or Class II Units

Current through 2024-29, July 17, 2024
For all resource recovery facilities, either Class I or Class
				  II units, the following shall apply (except for periods of startup, shutdown,
				  and malfunction) per 40 C.F.R. Part 60, Subpart BBBB:
A.
Emission Limiting Standards.
An owner or operator may request that compliance with the following applicable
				emission standards be determined using carbon dioxide measurements corrected to
				an equivalent of 7 percent oxygen.
(1)
Particulate Matter
(a) For Class
				I units, emission limits for particulate matter are specified in Tables 2 and 3
				of 40 C.F.R. Part 60, Subpart BBBB.
(b) For Class II units, the emission limit
				for particulate matter contained in the gases discharged to the atmosphere is
				23 milligrams per dry standard cubic meter, corrected to 7 percent oxygen. The
				averaging time is specified in Table 4 of 40 C.F.R. Part 60, Subpart
				BBBB.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 121 - EMISSION LIMITATIONS AND EMISSION TESTING OF RESOURCE RECOVERY FACILITIES › Section 096-121-8 - General Requirements for Large and Small Resource Recovery Facilities

Current through 2024-29, July 17, 2024
The following section shall be applicable to all resource
				  recovery facilities including large municipal waste combustor units:
The owner or operator of the resource recovery facility or
				  his representative shall submit to the Department within 60 days of emission
				  test completion the following information:
A.
Facility Operating Status.
A
				summary of facility process data shall be included in the resource recovery
				facility emission test report including:
(1)
				Load Level of waste expressed as
(a) the rate
				of steam production,
(b) the
				percentage of the design capacity steam production,
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 123 - CONTROL OF VOLATILE ORGANIC COMPOUNDS FROM PAPER, FILM AND FOIL COATING OPERATIONS › Section 096-123-1 - Applicability

Current through 2024-29, July 17, 2024
A. This regulation applies
				statewide.
B. This regulation
				applies to roll, knife, meyer rod or rotogravure coater(s) and drying oven(s)
				of paper, film and foil coating lines at stationary sources of volatile organic
				compounds.
C.This regulation does
				not apply to the following activities:
(1)
				Size presses and on-machine coaters on papermaking machines that apply sizing
				(e.g., starch) or water-based clays;
(2) Off-machine coaters used in the paper
				making process that use coatings with a VOC content less than 2.9 lbs
				VOC/gallon;
(3) The application of
				inks, coatings or adhesives in association with flexible package printing;
				or
(4) Coating performed on or
				in-line with any offset lithographic, screen, letterpress, flexographic,
				rotogravure, or digital printing press.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 123 - CONTROL OF VOLATILE ORGANIC COMPOUNDS FROM PAPER, FILM AND FOIL COATING OPERATIONS › Section 096-123-3 - Emission Limits

Current through 2024-29, July 17, 2024
The owner or operator of a paper, film or foil coating line
				  subject to this regulation must comply with one of the following limits.
A.
Low solvent content coating
				technology.
The owner or operator of a paper, film or foil coating line,
				except pressure sensitive tape and label coatings, subject to this regulation
				shall not cause, allow or permit the discharge into the atmosphere from any
				coating volatile organic compounds (VOC) in excess of 2.9 pounds of VOC per
				gallon of coating (excluding water and negligibly reactive VOC as defined in
				the definition of VOC in Definitions, 06-096 CMR 100 (last amended October 4,
				2009), delivered to the coating applicator from a paper, film or foil coating
				line. Any averaging of emission limits to meet this emission limit must comply
				with EPA's Emission Trading Policy Statement published on December 4, 1986 (51
				FR 43814) and must be approved by the Department and EPA.
B.
Add-On air pollution control device.
The owner or operator of a paper, film or foil coating line subject to
				this regulation which is controlled by an add-on air pollution control device
				shall operate the add-on control device at all times the paper, film or foil
				coating line is operating such that the overall efficiency of the abatement
				equipment (the efficiency of the capture system multiplied by efficiency of the
				control device) reduces the VOC emissions by 95% or to a rate equal to 4.8
				pounds VOC emitted per gallon of solids applied to the substrate on a
				continuous basis. For incineration or other types of control devices, the
				averaging period to determine compliance with EPA Reference Method 25 is three
				hours, and for carbon adsorption the averaging period to determine compliance
				with EPA Reference Method 25 is the length of the adsorption cycle or 24 hours,
				whichever is less.
C.
Pressure sensitive tape and label coatings.
The owner or operator of a
				pressure sensitive tape and label coating line subject to this regulation shall
				not cause, allow or permit the discharge into the atmosphere from the coating
				line volatile organic compounds (VOC) in excess of 0.20 lb VOC/lb of coating
				solids applied.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 123 - CONTROL OF VOLATILE ORGANIC COMPOUNDS FROM PAPER, FILM AND FOIL COATING OPERATIONS › Section 096-123-4 - Work practices

Current through 2024-29, July 17, 2024
By January 1, 2011, each owner or operator of a paper, film
				  or foil coating line subject to this regulation shall use the following work
				  practices.
A. New and used coating or
				cleaning solvent containing greater than 2.9 lbs VOC/gallon, including a
				coating mixed on the premises, shall be stored in a nonabsorbent, non-leaking
				container. Such container shall be kept closed at all times except when the
				container is being filled, emptied or is otherwise actively in use;
B. Spills and leaks of VOC-containing coating
				or cleaning solvent shall be minimized. Any leaked or spilled VOC-containing
				coating or cleaning solvent shall be immediately absorbed and removed or
				disposed of in accordance with an approved air emission license;
C. Absorbent applicators, such as cloth and
				paper, which are moistened with coating or cleaning solvent containing greater
				than 2.9 lbs VOC/gallon, shall be stored in a closed, nonabsorbent, non-leaking
				container for disposal or recycling;
D. Coating or cleaning solvent containing
				greater than 2.9 lbs VOC/gallon shall be conveyed from one location to another
				in a closed container or pipe; and
E. Cleaning shall be performed to minimize
				associated VOC emissions.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 123 - CONTROL OF VOLATILE ORGANIC COMPOUNDS FROM PAPER, FILM AND FOIL COATING OPERATIONS › Section 096-123-5 - Test Methods

Current through 2024-29, July 17, 2024
A. The owner or
				operator of any paper, film or foil coating line subject to this regulation
				shall, at his own expense, demonstrate compliance using the methods in 5(C) and
				5(D) below. All tests shall be made by, or under the direction of a person
				qualified by training and/or experience in the field of air pollution
				testing.
B. No results from
				volatile organic compound emissions compliance testing will be accepted as a
				compliance demonstration, nor the results accepted, unless prior notification
				has been supplied to the Department and the Department has granted approval.
				Any person proposing to conduct a volatile organic compound emissions test
				shall notify the Department of the intent to test not less than 30 days before
				the proposed initiation of the tests so the Department may at its option
				observe the test.
C. For
				determining the volatile content of surface coatings, the applicant shall use
				EPA Reference Method 24, or any other method approved by the Department and
				EPA. When determining the volatile fraction of a coating using EPA Reference
				Method 24, or any other method approved by the Department and EPA; the bake
				time must be one hour. For determining the percent solids by volume of a
				coating, until an applicable EPA Reference Method is promulgated, the source
				shall use the manufacturer's formulation data.
D. For determining the volatile organic
				compound emission control system efficiency, the applicant shall determine the
				removal efficiency of the control device using EPA Reference Method 18, 25,
				25A, or 25B or any other method approved by the Department and EPA. For
				incineration or other types of control devices, the averaging period to
				determine compliance with EPA Reference Method 25 is three hours, and for
				carbon adsorption the averaging period to determine compliance with EPA
				Reference Method 25 is the length of the adsorption cycle or 24 hours,
				whichever is less. The applicant shall determine the capture efficiency using
				any method approved by the Department and EPA.
E.Alternative test methods. Other test
				methods demonstrated to provide results that are acceptable for the purposes of
				determining compliance with Section 3(A) and 3(C), after review and approval in
				writing by the Department and EPA, also may be used.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 123 - CONTROL OF VOLATILE ORGANIC COMPOUNDS FROM PAPER, FILM AND FOIL COATING OPERATIONS › Section 096-123-6 - Recordkeeping and Reporting

Current through 2024-29, July 17, 2024
A. Within 60 days
				from the date upon which this regulation becomes applicable to a source, that
				source shall submit the following information to the Department for each
				coating line subject to this regulation:
(1)
				Coating line number;
(2) Hours of
				operation per day and per year;
(3)
				Method of application;
(4) Number
				and types of coats applied to substrate;
(5) Drying method; and
(6) Substrate type.
The source shall submit revised information to the Department
				  whenever it makes changes to the coating line.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 123 - CONTROL OF VOLATILE ORGANIC COMPOUNDS FROM PAPER, FILM AND FOIL COATING OPERATIONS › Section 096-123-7 - Additional Recordkeeping and Reporting for Sources with Add-on Air Pollution Control Device

Current through 2024-29, July 17, 2024
A.Within 60 days
				from the date upon which this regulation becomes applicable to a source, that
				source shall submit the following information to the Department for each
				control device:
(1) Control device
				identification number and model number;
(2) Manufacturer;
(3) Installation date;
(4) Coating line(s) controlled;
(5) Whether or not the control device always
				is in operation when the line(s) it is serving is in operation;
(6) Type of control device;
(7) Destruction or removal
				efficiency;
(8) Date tested (If not
				tested, method of determining destruction efficiency);
(9) For thermal incinerators - design
				combustion temperature (oF);
(10) For catalytic incinerators - design
				exhaust gas temperature (oF), design temperature
				rise across catalyst bed (oF), anticipated frequency
				of catalyst change;
(11) For a
				condenser - design inlet temperature of cooling medium
				(oF), design exhaust gas temperature
				(oF);
(12) For a carbon adsorber - design pressure
				drop across the adsorber, VOC concentration at breakthrough;
(13) Emission test results - inlet VOC
				concentration (ppm), outlet VOC concentration (ppm), method of concentration
				determination, date of determination;
(14) Type and location of capture
				system;
(15) Capture efficiency
				(%); and
(16) Method of determining
				capture efficiency.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 123 - CONTROL OF VOLATILE ORGANIC COMPOUNDS FROM PAPER, FILM AND FOIL COATING OPERATIONS › Section 096-123-8 - Compliance

Current through 2024-29, July 17, 2024
Except as otherwise specifically noted, the owner or operator
				  of any paper coating line subject to this regulation shall comply with this
				  regulation as of the effective of the regulation. The owner of any film and
				  foil coating line subject to this regulation shall comply with this regulation
				  by January 1, 2011. The compliance deadline for Section
				  4, Work Practices, for all paper, film
				  and foil coating lines is January 1, 2011.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 124 - TOTAL REDUCED SULFUR CONTROL FROM KRAFT PULP MILLS › Section 096-124-1 - Scope/Applicability

Current through 2024-29, July 17, 2024
A.This regulation applies in all ambient air
				quality control regions in the State of Maine.
B. The provisions of this Chapter apply to
				TRS emissions from processes that occur in Kraft pulp mills.
C.Unless otherwise indicated, any reference
				in this Chapter to provisions of the Code of Federal Regulations is to that
				version of the regulation in effect as of July 1, 1998.
Kraft pulp mills may also be subject to the Environmental
				  Protection Agency's (EPA's) New Source Performance Standard (NSPS) for Kraft
				  Pulp Mills ( 40 CFR Part 60, Subpart BB).
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 124 - TOTAL REDUCED SULFUR CONTROL FROM KRAFT PULP MILLS › Section 096-124-3 - Standards

Current through 2024-29, July 17, 2024
A. Unless otherwise specified in this rule,
				no owner or operator subject to this Chapter shall discharge into the
				atmosphere any gases which contain TRS in excess of 0.75 pounds per hour or
				five (5) parts per million (ppm) by volume dry basis on a twelve (12)-hour
				block average basis, and which are from a LVHC system, or after the dates in
				Section 3(D), 3(E), and 3(L), from HVLC systems, steam stripper collection
				systems or alternative TRS control systems unless at least one of the following
				conditions is met:
(1) The gases are
				combusted in a lime kiln subject to the provisions of Section 3(K) and Section
				4(A) of this Chapter, and the requirements of
				40 CFR Section
				60.283(a)(5), as applicable;
				or
(2) The gases are combusted in a
				recovery furnace subject to the provisions of Section 3(H), 3(I), and Section
				4(A) of this Chapter, and the requirements of
				40 CFR Sections
				60.283(a)(2) or (a)(3), as
				applicable; or
(3) The gases are
				combusted in an incinerator, boiler, or other device subject to the provisions
				of Section 4(B), and are subjected to a minimum temperature of
				1200oF for at least 0.5 seconds.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 124 - TOTAL REDUCED SULFUR CONTROL FROM KRAFT PULP MILLS › Section 096-124-4 - Monitoring of Emissions and Operations

Current through 2024-29, July 17, 2024
Any owner or operator subject to this Chapter must install,
				  calibrate, maintain, and operate monitors, and perform stack tests, in
				  accordance with the following requirements:
A.For any lime kiln or recovery furnace, a
				continuous emissions monitoring system to monitor and record the concentration
				of TRS emissions on a dry basis and the percent of oxygen by volume on a dry
				basis in the gases discharged into the atmosphere. These systems must be
				located downstream of the control device(s), and the spans of these continuous
				emissions monitoring system(s) must be set as follows:
(1) For TRS, a concentration of thirty (30)
				or fifty (50) ppm for the TRS continuous monitoring system on any lime kiln or
				Kraft recovery furnace; and
(2) At
				twenty (20)% oxygen for the continuous oxygen monitoring system, or such other
				concentration as may be approved by the Department for a particular source as
				specified in the source's air emission license.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 124 - TOTAL REDUCED SULFUR CONTROL FROM KRAFT PULP MILLS › Section 096-124-5 - Recordkeeping and Reporting

Current through 2024-29, July 17, 2024
A. Except when the
				conditions of Sections 3(A)(3) or 3(J) of this Chapter are met, any owner or
				operator subject to this Chapter shall perform the following recordkeeping and
				reporting requirements:
(1) For each recovery
				furnace or lime kiln, calculate and record on a daily basis, twelve (12)-hour
				block average TRS concentrations for the two (2) periods of each operating day.
				Each twelve (12)-hour block average shall be determined as the arithmetic mean
				of the appropriate twelve (12) contiguous one (1)-hour average TRS
				concentrations provided by each continuous emissions monitoring system
				installed pursuant to Section 4(A) and (D);
(2) For each recovery furnace or lime kiln,
				calculate and record on a daily basis twelve (12)-hour block average oxygen
				concentrations for the two (2) consecutive periods of each operating day. These
				twelve (12)-hour block averages must correspond to the twelve (12)-hour block
				average TRS concentrations under Section 5(A)(1) of this Chapter and shall be
				determined as an arithmetic mean of the appropriate twelve (12) contiguous one
				(1)-hour average oxygen concentrations provided by each continuous emissions
				monitoring system installed pursuant to Section 4(A), and (D); and
(3) All concentrations of TRS required to be
				measured from lime kilns, incinerators, or other combustion devices shall be
				corrected to ten (10)% oxygen by volume and those concentrations from recovery
				furnaces shall be corrected to eight (8)% oxygen by volume. These corrections
				shall be made in the following manner:
corr = meas x (21 - X) /(21 - Y)
Where: corr = The concentration corrected for oxygen.
meas = The concentration uncorrected for oxygen.
X = The volumetric oxygen concentration in percentage to be
				  corrected to eight (8)% for recovery furnaces and ten (10)% for lime kilns,
				  incinerators, or other combustion devices.
Y = The measured twelve (12)-hour block average volumetric
				  oxygen concentration; and
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 124 - TOTAL REDUCED SULFUR CONTROL FROM KRAFT PULP MILLS › Section 096-124-6 - Test Methods

Current through 2024-29, July 17, 2024
A.For the purpose
				of determining compliance with Section 3 of this Chapter, the following EPA
				Reference Methods from Appendix A of 40 CFR Part 60 and Chapter 117 shall be
				used:
(1) Method 16 or, at the discretion of
				the owner or operator, Method 16A or, Method 16B as approved by the Department,
				for the concentration of TRS;
(2)
				Method 3 for gas analysis; and
(3)
				When determining compliance with Section 3(J) of this Chapter, the owner or
				operator of a system subject to this Chapter must use the results of Method 2,
				Method 16, Method 16A, Method 16B and the black liquor solids feed rate in the
				following equation to determine the TRS emission rate on an equivalent
				H2S basis.
E=(CTRS) (F)
				  (Qsd)/BLS
Where: E=mass of TRS emitted per unit of black liquor solids
				  (g/kg) or (lb./ton).
CTRS= average combined concentrations
				  of TRS (ppm), as determined by Method 16, 16A or 16B during the test
				  period.
F=0.001417 g
				  H2S/m3 ppm for metric
				  units.
=0.08844 x 10-6 lb.
				  H2S/ft3ppm for English
				  units.
Qsd= dry volumetric stack gas flow
				  rate (dscm/hr or dscf/hr), corrected to standard conditions.
BLS= black liquor solids feed rate (kg/hr or ton/hr).
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 124 - TOTAL REDUCED SULFUR CONTROL FROM KRAFT PULP MILLS › Section 096-124-7 - Compliance

Current through 2024-29, July 17, 2024
Compliance with this Chapter, except where otherwise
				  specified herein, shall be met no later than January 8, 1991.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 125 - PERCHLOROETHYLENE DRY CLEANER REGULATION › Section 096-125-1 - Scope and Applicability

Current through 2024-29, July 17, 2024
A.
General
				Applicability.
This regulation applies to all new and existing area
				source dry cleaners that use perchloroethylene in the State of Maine upon the
				effective date of the regulation unless otherwise specified in the
				regulation.
B.
Applicability
				Categories
1 Area source dry cleaners
				are those sources with a twelve-month rolling total consumption of
				perchloroethylene of 2100 gallons or less.
2 Major source dry cleaners are those sources
				with a twelve-month rolling total consumption of perchloroethylene greater than
				2100 gallons. Major sources of perchloroethylene must comply with 40 C.F.R.
				Part 63, Subpart M.
3 Co-located
				dry cleaners are those sources that meet the definition of co-located in
				subsection 2(D) of this Chapter.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 125 - PERCHLOROETHYLENE DRY CLEANER REGULATION › Section 096-125-3 - Emission Limitations and Performance Standard Requirements

Current through 2024-29, July 17, 2024
A.
Requirements for co-located dry
				cleaners
1 Beginning on June 24, 2009,
				no new or relocated perchloroethylene dry cleaning system may be installed in a
				co-located facility.
2 Any new or
				relocated dry cleaning system located in a building with a residence which
				commenced construction on or after December 21, 2005 must comply with
				40
				C.F.R. Parts 63.320(b)(2)
				and
				63.320(b)(3)
				as amended up to July 19, 2013.
3
				After December 21, 2020, all co-located dry cleaners must completely eliminate
				perchloroethylene use and remove all perchloroethylene dry cleaning equipment
				from the building.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 125 - PERCHLOROETHYLENE DRY CLEANER REGULATION › Section 096-125-4 - Control Device Operation and Maintenance

Current through 2024-29, July 17, 2024
A.
Carbon Adsorbers
1 All exhaust
				from the washer, dryer, filter purification system, holding "tanks" and
				attendant piping and valves must be routed through the carbon adsorber. The
				carbon adsorber shall be operated at an air flow capacity at least equal to the
				unrestricted total exhaust gas flow rate of the dry cleaning
				machines.
2 Any dry cleaner which
				uses a carbon adsorber to comply with this Chapter must regenerate the carbon
				bed in accordance with the manufacturer's recommendations, except that the
				carbon bed shall be regenerated no less than either weekly, or after twenty
				five (25) loads, whichever period is greater.
a The 100 ppmv emission limit from the carbon
				adsorber must be met regardless of the regeneration requirements of this
				Section
b The carbon adsorber must
				not be bypassed to the atmosphere during regeneration.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 125 - PERCHLOROETHYLENE DRY CLEANER REGULATION › Section 096-125-5 - Compliance Methods and Monitoring Requirements

Current through 2024-29, July 17, 2024
A.
Carbon Adsorber Systems.
The owner/operator of any dry cleaning
				system using a carbon adsorber to comply with the Control Technology
				Requirements found in section 3 of this Chapter must establish a program of
				regular carbon bed desorption and compliance monitoring.
1 Carbon bed desorption shall be conducted in
				accordance with the manufacturer's recommendations, except that the carbon bed
				shall be regenerated no less than either weekly, or after twenty five (25)
				loads, whichever period is greater. The owner/operator shall maintain a record
				of all carbon bed desorptions which shall include date of desorption and number
				of loads between desorptions as well as any other evidence demonstrating that
				the carbon adsorber has been properly installed, operated and maintained.
2 The exhaust of the carbon
				adsorber shall be measured weekly with a perchloroethylene gas analyzer used in
				accordance with the manufacturer's instructions. The measurement shall be taken
				in front of and at a distance of no greater than 3 feet from the dry-cleaning
				drum opening immediately after the door of the dry cleaning machine is opened
				and the clothing has been removed. The owner/operator shall maintain a record
				of all analyzer readings.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 125 - PERCHLOROETHYLENE DRY CLEANER REGULATION › Section 096-125-6 - Recordkeeping Requirements

Current through 2024-29, July 17, 2024
A.All dry cleaning
				facilities must keep a copy of the design specifications and operating manual
				for each dry cleaning system on-site; and keep receipts of perchloroethylene
				purchases and record in a log the following:
1 The volume of perchloroethylene purchased
				each month. This number represents the perchloroethylene purchases for a given
				month.
2 The calculated value of
				the twelve-month rolling total perchloroethylene consumption limit. To
				calculate the twelve-month rolling total perchloroethylene consumption limit,
				the owner/operator shall perform the following calculations on the first day of
				every month:
a Sum up the volume of
				perchloroethylene purchases made in each of the previous 12 months, as recorded
				in the log.
b If no
				perchloroethylene purchases were made in a given month, then the
				perchloroethylene consumption for that month is zero gallons.
c The highest twelve-month rolling total is
				the facility's perchloroethylene consumption limit.
3 The dates when the dry cleaning system was
				inspected for leaks in compliance with subsection 5(C) of this Chapter, and the
				name and location of any dry cleaning system parts where detectable leaks were
				found.
4 The dates of repair and
				records of written or verbal orders for repair parts to demonstrate compliance
				with subsection 3(G)(3) of this Chapter.
5 The date and monitoring results
				(temperature sensor or pressure gauge) for compliance with subsection 54(B) of
				this Chapter.
6 The date and gas
				analyzer monitoring results, if a carbon adsorber is used for compliance with
				section 3(B),3(C), 3(D), and 3(E).
7 The date of desorption and the number of
				loads between desorption of the carbon adsorber.
The log, perchloroethylene receipts, all manufacturer design
				  specifications and operation manuals for each dry cleaning system located at
				  the facility must be maintained on site for at least five (5) years and must be
				  made available to the Department upon request. An owner that operates more than
				  one dry cleaner may store records older than one year from all facilities at
				  one dry cleaner location or at a centralized office located in the State of
				  Maine.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 125 - PERCHLOROETHYLENE DRY CLEANER REGULATION › Section 096-125-7 - Registration Requirements

Current through 2024-29, July 17, 2024
A.The owners or
				operators of all dry cleaners shall register with the Department
				annually.
B.Registration shall be
				on a form prescribed by the Department and shall include but is not limited to
				the following information:
1 Name of facility
				and the name of the owner or operator who is responsible;
2 Facility address and telephone;
3 Whether the dry cleaner is located in a
				building with a residence (even if the residence is vacant at the time of this
				notification), or with a day care center, a health care facility, a prison, an
				elementary school, a middle or high school, a children's pre-school, a senior
				center, a youth center or other facility inhabited by children or the
				elderly;
4 Type of control device
				or devices in use for each dry cleaning system;
5 Number and type of dry cleaning machines,
				and when they were installed;
6
				Number and type of emission control devices and when they were
				installed;
7 The total
				perchloroethylene consumption for each of the previous twelve months as
				required under subsection 5(A)(2) of this Chapter;
8 A certification of the source applicability
				category, i.e. whether a facility is a major source or an area source;
				and
9 An estimate of the hazardous
				waste that was shipped off-site.
Code of Maine Rules › 06 - DEPARTMENT OF ENVIRONMENTAL PROTECTION › 096 - DEPARTMENT OF ENVIRONMENTAL PROTECTION - GENERAL › Chapter 126 - CAPTURE EFFICIENCY TEST PROCEDURES › Section 096-126-2 - Procedures

Current through 2024-29, July 17, 2024
The testing procedures and specifications described in this
				  Chapter as "Procedure F.1", "Procedure F.2", "Procedure G.1", "Procedure G.2",
				  "Procedure L", and "Procedure T" are attached to this rule as Appendix A and
				  are incorporated herein by reference.