reglab/statecodes huggingface dataset:
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-4 - Human and Animal Crematories › Section 219-4.8 - Record keeping requirements

Current through Register Vol. 46, No. 28, July 10, 2024
(a) The
					 owner or operator of a crematory facility must maintain the following records
					 at the facility for a period of at least five years:
(1) Continuous temperature monitoring records
					 indicating the date and time of each cremation performed;
(2) Operator training and certification
					 records for all operators at the facility;
(3) A record of the date, time, and cause of
					 all malfunctions and any corrective action taken to resolve them;
(4) A record of any maintenance performed on
					 each cremation unit, including the annual inspection required by Section
					 219-4.7 
					 of this Subpart, and the routine replacement of parts and components;
					 and
(5) A copy of each cremation
					 certification form created pursuant to Subdivision
					 219-4.4(e) 
					 of this Subpart.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-4 - Human and Animal Crematories › Section 219-4.9 - Compliance schedule

Current through Register Vol. 46, No. 28, July 10, 2024
(a) The
					 owner or operator of an existing cremation unit shall:
(1) Obtain appropriate operator
					 certifications, as described in Section
					 219-4.6  of this
					 Subpart, within 12 months of the effective date of this Subpart for each
					 uncertified operator at the facility;
2.
					 Demonstrate compliance with the requirements of this Subpart no later than 60
					 months from the effective date of this Subpart. A demonstration of final
					 compliance shall include the following information for each existing cremation
					 unit:
(i) An emissions testing report, as
					 described in Section
					 219-4.5  of
					 this Subpart, indicating that each existing cremation unit meets the
					 particulate matter limitation specified in Subdivision
					 219-4.3(a) 
					 of this Subpart;
(ii) Documentation
					 indicating that each existing cremation unit is capable of meeting the
					 requirements of this Subpart; and
(iii) Documentation of the certification
					 status of each operator at the facility.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-4 - Human and Animal Crematories › Section 219-4.10 - Severability

Current through Register Vol. 46, No. 28, July 10, 2024
Each provision of this Subpart shall be deemed severable,
						and in the event that any portion of this Subpart is held to be invalid, the
						remainder of this Subpart shall continue in full force and
						effect.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-4 - Human and Animal Crematories › Section 219-4.11

Current through Register Vol. 46, No. 28, July 10, 2024
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-7 - Mercury Emission Limitations for Large Municipal Waste Combustors Constructed on or before September 20, 1994 › Section 219-7.1 - Mercury emission limitations

Current through Register Vol. 46, No. 28, July 10, 2024
In addition to the mercury requirements contained in  40
						CFR Part 60, Subpart Cb, incorporated by reference in Part 200 of this Title
						(see Table 2, section
						200.10), the
						emission limitation for mercury is 28 ug/dscm (corrected to seven percent
						oxygen) or 85 percent removal, whichever is less stringent.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-7 - Mercury Emission Limitations for Large Municipal Waste Combustors Constructed on or before September 20, 1994 › Section 219-7.2 - Compliance with mercury emission limitations

Current through Register Vol. 46, No. 28, July 10, 2024
Annual compliance is based on the average of the annual
						stack tests on each municipal waste combustor (MWC) unit at the facility using
						the stack testing procedures contained in
						40 CFR
						60.58b(d)(2), incorporated
						by reference in 6 NYCRR Part 200 (see Table 1, section
						200.9 of this
						Title). This average of all the facility's MWC units must be in compliance with
						the emission limit of 28 ug/dscm (corrected to seven percent oxygen) or 85
						percent removal, whichever is less stringent. However, the average of annual
						stack tests on each MWC unit at the facility must be in compliance with the
						federal limit of 80 ug/dscm (corrected to seven percent oxygen) or 85 percent
						removal, whichever is less stringent. Four years after the effective date of
						this Subpart the averaging of the annual stack tests across all incinerators at
						the facility will end and each of the facility's incinerators must be in
						compliance with the emission limit of 28 ug/dscm (corrected to seven percent
						oxygen) or 85 percent removal, whichever is less stringent. Emission control
						devices must be kept in a satisfactory state of maintenance and repair in
						accordance with ordinary and necessary practices, standards and procedures,
						inclusive of manufacturer's specifications, required to operate such devices
						effectively. Compliance with this Subpart is required within one year of the
						effective date of this Subpart. Initial compliance testing must take place
						within 180 days of the compliance date of this Subpart.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-8 - Emission Guidelines and Compliance Times for Small Municipal Waste Combustion Units Constructed on or before August 30, 1999 › Section 219-8.1 - Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
The Federal requirements of  40 CFR Part 60, Subpart BBBB,
						incorporated by reference in Part 200 (see section
						200.10, Table
						2 of this Title) apply to small municipal waste combustion Class I and Class II
						units that are constructed on or before August 30, 1999.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-8 - Emission Guidelines and Compliance Times for Small Municipal Waste Combustion Units Constructed on or before August 30, 1999 › Section 219-8.2 - Definitions

Current through Register Vol. 46, No. 28, July 10, 2024
(a) Class I units
					 mean small municipal waste combustion units that are located at municipal waste
					 combustion plants with an aggregate plant combustion capacity greater than 250
					 tons per day of municipal solid waste.
(b) Class II units mean small municipal waste
					 combustion units that are located at municipal waste combustion plants with an
					 aggregate plant combustion capacity less than or equal to 250 tons per day of
					 municipal solid waste.
(c)
					 Municipal waste combustion plant capacity means the aggregate municipal waste
					 combustion capacity of all municipal waste combustion units at the plants that
					 are not subject to  40 CFR 60  Subparts Ea, Eb, or AAAA.
(d) Small municipal waste combustion unit
					 means a municipal waste combustion unit that has the capacity to combust at
					 least 35 tons per day but no more than 250 tons per day of municipal solid
					 waste.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-8 - Emission Guidelines and Compliance Times for Small Municipal Waste Combustion Units Constructed on or before August 30, 1999 › Section 219-8.3 - Compliance schedules

Current through Register Vol. 46, No. 28, July 10, 2024
(a)
					 Compliance schedule for Class I units.
(1)
					 Submit a final control plan to the department's appropriate regional air
					 pollution control engineer for review and approval within three months after
					 the effective date of EPA's approval of New York State's Small Municipal Waste
					 Combustor State Plan (State Plan) or by August 6, 2003, whichever is
					 earlier.
(2) Award contracts for
					 emission control systems or for process modifications, or issuance of orders
					 for the purchase of component parts to accomplish emission control or process
					 modification within nine months after the effective date of EPA's approval of
					 the State Plan or by February 6, 2004, whichever is earlier.
(3) Initiate on-site construction or
					 installation of emission control equipment or process changes within 15 months
					 after the effective date of EPA's approval of the State Plan or by August 6,
					 2004, whichever is earlier.
(4)
					 Complete on-site construction or installation of emission control equipment or
					 process changes within 34 months after the effective date of EPA's approval of
					 the State Plan or by October 6, 2005, whichever is earlier.
(5) Achieve full compliance with approved
					 final control plan and requirements of Federal  40 CFR 60, Subpart BBBB (dated
					 December 6, 2000) as incorporated under section
					 200.10  of
					 this Title and this Subpart, as applicable, with 36 months after the effective
					 date of EPA's approval of the State Plan or by December 6, 2005, whichever is
					 earlier.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-9 - EMISSION GUIDELINES AND COMPLIANCE SCHEDULES FOR EXISTING SEWAGE SLUDGE INCINERATION UNITS › Section 219-9.1 - Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
The Federal requirements of  40 CFR part 60, subpart MMMM,
						incorporated by reference in Part 200 of this Title (see Table 2, section
						200.10  of
						this Title), apply to sewage sludge incineration (SSI) units, located at
						wastewater treatment facilities, designed to treat domestic sewage sludge, the
						construction of which commenced on or before October 14,
						2010.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-9 - EMISSION GUIDELINES AND COMPLIANCE SCHEDULES FOR EXISTING SEWAGE SLUDGE INCINERATION UNITS › Section 219-9.2 - Definitions

Current through Register Vol. 46, No. 28, July 10, 2024
(a) To the extent
					 that they are not inconsistent with the specific definitions in subdivision (b)
					 of this section, the general definitions of Parts 200 and 201 of this Title,
					 and  40 CFR part 60, subpart MMMM apply (see Table 2, section
					 200.10  of
					 this Title).
(b) For the purpose of
					 this Subpart, the following definitions apply:
(1) Fluidized bed incinerator means an
					 enclosed device in which organic matter and inorganic matter in sewage sludge
					 are combusted in a bed of particles suspended in the combustion chamber
					 gas.
(2) Multiple hearth
					 incinerator means a circular steel furnace that contains a number of solid
					 refractory hearths and a central rotating shaft; rabble arms that are designed
					 to slowly rake the sludge on the hearth are attached to the rotating shaft.
					 Dewatered sludge enters at the top and proceeds downward through the furnace
					 from hearth to hearth, pushed along by the rabble arms.
(3) Sewage sludge means solid, semisolid, or
					 liquid residue generated during the treatment of domestic sewage in a treatment
					 works. Sewage sludge includes, but is not limited to, domestic septage; scum or
					 solids removed in primary, secondary, or advanced wastewater treatment
					 processes; and a material derived from sewage sludge. Sewage sludge does not
					 include ash generated during the firing of sewage sludge in a sewage sludge
					 incineration unit or grit and screenings generated during preliminary treatment
					 of domestic sewage in a treatment works.
(4) Sewage sludge incineration (SSI) unit
					 means an incineration unit combusting sewage sludge for the purpose of reducing
					 the volume of the sewage sludge by removing combustible matter. Sewage sludge
					 incineration unit designs include fluidized bed and multiple hearth. A SSI unit
					 also includes, but is not limited to, the sewage sludge feed system, auxiliary
					 fuel feed system, grate system, flue gas system, waste heat recovery equipment,
					 bottom ash system, and all ash handling systems connected to the bottom ash
					 handling system. The combustion unit bottom ash system ends at the truck
					 loading station or similar equipment that transfers the ash to final disposal.
					 The SSI unit does not include air pollution control equipment or the
					 stack.
(5) State plan approval
					 means the effective date of EPA's approval of New York State's SSI State
					 Plan.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-9 - EMISSION GUIDELINES AND COMPLIANCE SCHEDULES FOR EXISTING SEWAGE SLUDGE INCINERATION UNITS › Section 219-9.3 - Compliance/closure schedules

Current through Register Vol. 46, No. 28, July 10, 2024
Owners or operators of applicable SSI units must achieve
						full compliance with the requirements of   40 CFR part 60, subpart MMMM (see
						Table 2, section
						200.10  of
						this Title), and this Subpart by either complying with one of the two schedules
						specified in subdivisions (a) and (b) of this section, or permanently closing
						the SSI unit as specified in subdivision (c) of this section.
(a) One year compliance schedule. If
					 compliance will be achieved less than one year after State plan approval, the
					 two increments of progress specified in paragraphs (1) and (2) of this
					 subdivision must be met.
(1) Submit a final
					 control plan to the department's appropriate regional air pollution control
					 engineer for review and approval by the earlier of the following two dates:
					 three months after State plan approval, or September 21, 2012. The final
					 control plan must include:
(i) a description
					 of the proposed air pollution control devices that will be installed and
					 process changes that will be used to comply with the emission limits, standards
					 and other requirements of this Subpart;
(ii) the type(s) of waste that is(are)
					 proposed to be combusted, if waste other than sewage sludge is combusted in the
					 unit;
(iii) the maximum design
					 capacity of the SSI;
(iv) if
					 applicable, the petition for site-specific operating limits pursuant to
					 40
					 CFR part 60.5175 (see Table 2, section
					 200.10  of
					 this Title).
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-9 - EMISSION GUIDELINES AND COMPLIANCE SCHEDULES FOR EXISTING SEWAGE SLUDGE INCINERATION UNITS › Section 219-9.4 - Title v permit application compliance schedule

Current through Register Vol. 46, No. 28, July 10, 2024
Owners or operators of an applicable SSI unit not subject
						to an earlier permit application deadline must submit a complete title V permit
						application to the department for review and approval by the earlier of the
						following two dates: 12 months after State plan approval, or March 21,
						2014.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-10 - Emission Guidelines and Compliance Schedules for Existing Sewage Sludge Incineration Units › Section 219-10.1 - Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
This Subpart applies to all new, modified and existing
						municipal and private solid waste incineration units.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-10 - Emission Guidelines and Compliance Schedules for Existing Sewage Sludge Incineration Units › Section 219-10.2 - Control Requirements

Current through Register Vol. 46, No. 28, July 10, 2024
(a) No
					 owner or operator of a municipal or private solid waste incineration unit shall
					 cause or allow emissions of NO from any municipal or private solid waste
					 incineration unit in excess of the applicable limit in Table 1 of this Subpart
					 on a 24-hour arithmetic average basis, excluding periods of start-up, shutdown,
					 and malfunction.
Table 1 - 24-Hour Average NOx Emission
						Limits
Combustion Technology
NOx Emission Limit
									 (ppmv, dry corrected to 7% oxygen)
Mass Burn Waterwall
150
Rotary Combustor
170
Other Technologies
*
* See Subdivision 219-10.2(c)  of this Section
(b) No owner or operator of a
					 municipal or private solid waste incineration facility shall cause or allow
					 emissions of NOx from any municipal or private solid waste incineration unit in
					 excess of the applicable limit in Table 2 of this Subpart on an annual rolling
					 arithmetic average basis, excluding periods of start-up, shutdown, and
					 malfunction.
Table 2 - Annual Average NOx Emission
						Limits
Combustion Technology
NOx Emission Limit
									 (ppmv, dry corrected to 7% oxygen)
Mass Burn Waterwall
150
Rotary Combustor
150
Other Technologies
*
* See Subdivision 219-10.2(c)  of this Section
(c) The owner or operator of a
					 municipal or private solid waste incineration unit that employs a combustion
					 technology not listed in Table 1 or Table 2 of this Section shall develop and
					 propose a facility specific 24-hour and annual average NO emission limitation.
					 A proposal prepared pursuant to this Subdivision shall consider:
(1) The available NO control technologies,
					 the projected effectiveness of the technologies considered, and the costs for
					 installation and operation for each of the technologies; and
(2) The technology and the appropriate
					 emission limit selected as RACT considering the costs for installation and
					 operation of the technology.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-10 - Emission Guidelines and Compliance Schedules for Existing Sewage Sludge Incineration Units › Section 219-10.3 - Compliance demonstration

Current through Register Vol. 46, No. 28, July 10, 2024
(a) The
					 owner or operator of a municipal or private solid waste incineration unit
					 subject to this Subpart shall conduct an initial compliance demonstration
					 within one year of the date of issuance of a permit modification issued
					 pursuant to the requirements of this Subpart. The initial compliance
					 demonstration shall be conducted using the continuous emissions monitoring
					 system required by Subdivision (b) of this Section.
(b) The owner or operator of a municipal or
					 private solid waste incinerator unit subject to this Subpart shall install,
					 calibrate, maintain, and operate a continuous emission monitoring system for
					 measuring oxides of nitrogen discharged to the atmosphere, and shall record the
					 output of that system.
(c)
					 Following the date that the initial compliance demonstration required by
					 Subdivision (a) of this Section is completed, the owner or operator of a unit
					 subject to this Subpart shall demonstrate compliance with the applicable
					 24-hour oxides of nitrogen emission limit using the 24-hour daily arithmetic
					 average of the hourly emissions concentrations measured by the continuous
					 emissions monitoring system. Each 1-hour average shall be:
(1) Each 1-hour average shall be:
(i) Based on at least two data points
					 collected during that hour; and
(ii) Expressed in units of parts per million
					 by volume on a dry basis, and corrected to seven percent oxygen using the
					 1-hour arithmetic average oxygen continuous monitoring system data.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 219 - Incinerators › Subpart 219-10 - Emission Guidelines and Compliance Schedules for Existing Sewage Sludge Incineration Units › Section 219-10.4 - Severability

Current through Register Vol. 46, No. 28, July 10, 2024
Each provision of this Subpart shall be deemed severable,
						and in the event that any portion of this Subpart is held to be invalid, the
						remainder of this Subpart shall continue in full force and
						effect.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-1 - Portland Cement Plants › Section 220-1.1 - Definitions

Current through Register Vol. 46, No. 28, July 10, 2024
(a) For the purpose
					 of this Subpart, the general definitions of Part 200 of this Title
					 apply.
(b) For the purpose of this
					 Subpart, the following definitions also apply:
(1) Dry process plant. A portland cement
					 plant where the raw material kiln feed entering the kiln in a powder form has a
					 moisture content of one percent or less by weight.
(2) Feed to the kiln. The weight of all
					 materials, excluding fuels and uncombined water, introduced into the kiln
					 during the time when a stack sample is being taken to determine compliance with
					 sections
					 220-1.2
					 and
					 220-1.3 
					 of this Subpart.
(3) Clinker. The
					 product of a portland cement kiln from which finished cement is manufactured by
					 milling and grinding.
(4) Portland
					 cement kiln. A system, including any solid, gaseous, or liquid fuel combustion
					 equipment, used to calcine and fuse raw materials (including limestone and
					 clay) to produce clinker.
(5)
					 Portland cement plant. Any facility manufacturing portland cement by either the
					 wet or dry process.
(6) Wet process
					 plant. A portland cement plant where the raw material kiln feed enters the kiln
					 in the form of a water slurry of approximately 30 to 40 percent water by
					 weight.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-1 - Portland Cement Plants › Section 220-1.2 - Particulate emissions from existing kilns and clinker coolers

Current through Register Vol. 46, No. 28, July 10, 2024
Except as provided in section
						220-1.3 
						of this Subpart, no person shall cause or allow emission of particulates to the
						outdoor atmosphere from a portland cement kiln or clinker cooler in excess of
						the following emission rates:
(a) for
					 process weight per hour less than or equal to 100,000 pounds, E = 0.024P0.665
					 where E is the emission rate in pounds per hour and P is the process weight per
					 hour; or
(b) for process weight per
					 hour in excess of 100,000 pounds, 0.05 grains per standard cubic foot of gas on
					 a dry basis.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-1 - Portland Cement Plants › Section 220-1.3 - Particulate emissions from new or modified kilns and clinker coolers

Current through Register Vol. 46, No. 28, July 10, 2024
(a) No person will
					 cause or allow emission of particulates to the outdoor atmosphere in excess of
					 0.30 pounds per ton of feed to the kiln from a portland cement kiln, portland
					 cement kiln with in-line raw mill, and/or related air cleaning device which
					 commenced construction or modification after August 17, 1971.
(b) No person will cause or allow emission of
					 particulates to the outdoor atmosphere in excess of 0.10 pounds per ton of feed
					 to the kiln from a portland cement clinker cooler and/or related air cleaning
					 device which commenced construction or modification after August 17,
					 1971.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-1 - Portland Cement Plants › Section 220-1.4 - Opacity limits for portland cement processes

Current through Register Vol. 46, No. 28, July 10, 2024
(a) Except as provided in subdivision (b) of
					 this section, no person will cause or allow emissions to the outdoor atmosphere
					 of any material that has an average six-minute opacity of 20 percent or
					 greater, except uncombined water, from a portland cement kiln, portland cement
					 kiln with in-line raw mill, clinker cooler, or any other confined processes at
					 a portland cement plant.
(b) No
					 person will cause or allow emissions to the outdoor atmosphere of any material
					 that has an average six-minute opacity of 10 percent or greater, except
					 uncombined water, from a clinker cooler, raw mill system, finish mill system,
					 raw mill dryer, raw material storage, clinker storage, finished product
					 storage, conveyor transfer points, bagging and bulk loading and unloading
					 systems which commenced construction or modification after August 17,
					 1971.
(c) Any person who owns or
					 operates an area, parking lot, clinker gallery, railcar loading shed, conveyor
					 tunnel, access road, stockpile, building opening or refuse disposal area, at a
					 portland cement plant that has the potential to emit visible emissions for one
					 continuous hour or longer, must apply corrective measures to eliminate such
					 potential.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-1 - Portland Cement Plants › Section 220-1.5 - Particulate emissions from dust dumps

Current through Register Vol. 46, No. 28, July 10, 2024
(a) The owner or operator of any portland
					 cement dust dump will operate such dust dump in a manner which will minimize
					 the horizontal dimensions of the working face.
(b) In cases where the dump is within 1,500
					 feet of any receptor, the owner and/or operator must seal the dust dump either
					 by crusting or backfill twice yearly.
(c) If dumping procedures do not provide
					 adequate protection from dust reentrainment, the owner and/or operator must
					 install a windbreak. If visible emissions still reach the property line, the
					 owner and/or operator must precondition the waste dust.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-1 - Portland Cement Plants › Section 220-1.6 - Gaseous emissions from kiln stacks

Current through Register Vol. 46, No. 28, July 10, 2024
(a) The owner or operator of a portland
					 cement kiln may purchase and use fuel with a sulfur content exceeding the fuel
					 sulfur limitations required by Subpart 225-1 of this Title, provided that the
					 burning of such fuel will not result in emissions of sulfur compounds
					 (expressed as sulfur dioxide) to the outdoor atmosphere at a rate greater than
					 would result through the use of fuels otherwise mandated by Subpart
					 225-1.
(b) The owner or operator of
					 a portland cement kiln must submit a reasonably available control technology
					 (RACT) analysis to the department for emissions of oxides of nitrogen (NO
					 x) from the kiln that proposes a RACT emission limit(s),
					 and identifies the procedures and monitoring equipment to be used to
					 demonstrate compliance with the proposed RACT emission limit(s). The RACT
					 emissions limit(s) shall be expressed in pounds of NO x
					 per ton of clinker produced.
(1) By December
					 1, 2010 the owner or operator of a portland cement kiln that was in operation
					 prior to the effective date of this Subpart must submit a RACT analysis, and an
					 application for a permit modification in accordance with the provisions of
					 Subpart 201-6 of this Title unless the existing NO x
					 control equipment and emission limit(s) are determined to be RACT. RACT, as
					 approved by the department, must be implemented by July 1, 2012.
(2) The owner or operator of a portland
					 cement kiln that was not in operation prior to the effective date of this
					 Subpart must submit a RACT analysis prior to start up of the kiln. RACT, as
					 approved by the department, must be implemented upon start up.
(3) RACT analyses must include the available
					 NO x control technologies, the projected effectiveness
					 of the technologies considered, the costs for installation and operation for
					 each of the technologies, and the technology and the appropriate emission
					 limit(s) selected as RACT considering the costs for installation and operation
					 of the technology. For a portland cement kiln that was in operation prior to
					 the effective date of this Subpart and for which the existing NO
					 x control equipment has been determined to not be RACT,
					 the RACT analysis must also include a schedule for installation of control
					 equipment.
(4) Approved RACT
					 determinations will be submitted by the department to the United States
					 Environmental Protection Agency for approval as separate State Implementation
					 Plan revisions.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-2 - Glass Plants › Section 220-2.1 - Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
The requirements of this Subpart apply to any glass plant
						that is a major facility of oxides of nitrogen (NO
						x).
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-2 - Glass Plants › Section 220-2.2 - Definitions

Current through Register Vol. 46, No. 28, July 10, 2024
(a) For the purpose
					 of this Subpart, the definitions of Parts 200 and 201 of this Title
					 apply.
(b) For the purpose of this
					 Subpart, the following definitions also apply:
(1) Glass melting furnace. A refractory
					 vessel in which raw materials are charged, melted at high temperature, refined,
					 and conditioned to produce molten glass. The furnace includes foundations,
					 superstructure and retaining walls, raw material charger systems, heat
					 exchangers, melter cooling system, exhaust system, refractory brick work, fuel
					 supply and electrical boosting equipment, integral control systems and
					 instrumentation, and appendages for conditioning and distributing molten glass
					 to forming apparatuses. The forming apparatuses, including the float bath used
					 in flat glass manufacturing and flow channels in wool fiberglass and textile
					 fiberglass manufacturing, are not considered part of the glass melting
					 furnace.
(2) Glass plant. Any
					 facility using a glass melting furnace to manufacture glass.
(3) Glass produced or glass production. The
					 weight of glass removed from a glass melting furnace.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 220 - Portland Cement Plants And Glass Plants › Subpart 220-2 - Glass Plants › Section 220-2.3 - Gaseous emissions from glass melting furnaces

Current through Register Vol. 46, No. 28, July 10, 2024
(a) The owner or operator of a glass melting
					 furnace located at a glass plant that meets the applicability requirements of
					 section
					 220-2.1  of this
					 Subpart must submit a reasonably available control technology (RACT) analysis
					 to the department for emissions of oxides of nitrogen (NO
					 x) from the furnace that proposes a RACT emission
					 limit(s), and identifies the procedures and monitoring equipment to be used to
					 demonstrate compliance with the proposed RACT emission limit(s). The RACT
					 emissions limit(s) shall be expressed in pounds of NO x
					 per ton of glass produced.
(1) By December 1,
					 2010 the owner or operator of a glass melting furnace that was in operation
					 prior to the effective date of this Subpart must submit a RACT analysis, and an
					 application for a permit modification in accordance with the provisions of
					 Subpart 201-6 of this Title unless the existing NO x
					 control equipment and emission limit(s) are determined to be RACT. RACT, as
					 approved by the department, must be implemented by July 1, 2012.
(2) The owner or operator of a glass melting
					 furnace that was not in operation prior to the effective date of this Subpart
					 must submit a RACT analysis prior to start up of the furnace. RACT, as approved
					 by the department, must be implemented upon start up.
(3) RACT analyses must include the available
					 NO x control technologies, the projected effectiveness
					 of the technologies considered, the costs for installation and operation for
					 each of the technologies, and the technology and the appropriate emission
					 limit(s) selected as RACT considering the costs for installation and operation
					 of the technology. For a glass melting furnace that was in operation prior to
					 the effective date of this Subpart and for which the existing NO
					 x control equipment has been determined to not be RACT,
					 the RACT analysis must also include a schedule for installation of control
					 equipment.
(4) Approved RACT
					 determinations will be submitted by the department to the United States
					 Environmental Protection Agency for approval as separate State Implementation
					 Plan revisions.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 221 - Asbestos-containing Surface Coating Material › Section 221.1 - Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
This Part shall apply throughout the State of New
					 York.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 221 - Asbestos-containing Surface Coating Material › Section 221.2 - Prohibition

Current through Register Vol. 46, No. 28, July 10, 2024
No person shall engage in or allow surface coating by the
					 spraying of asbestos or asbestos-containing materials.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 221 - Asbestos-containing Surface Coating Material › Section 221.3 to 221.5 - Renumbered

Current through Register Vol. 46, No. 28, July 10, 2024
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 221 - Asbestos-containing Surface Coating Material › Section 221.6 to 221.11 - Renumbered

Current through Register Vol. 46, No. 28, July 10, 2024
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 222 - Distributed Generation Sources › Section 222.1 - Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
This Part applies to owners and operators of distributed
					 gen eration sources classified as economic dispatch sources located in the New
					 York City metropolitan area with a maximum mechanical output rating of 200
					 horsepower or greater where the potential to emit oxides of nitrogen (NOx) at a
					 facility is less than 25 tons per year.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 222 - Distributed Generation Sources › Section 222.3 - Notification of Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
(a)
				  An owner or operator of a distributed generation source must obtain a
				  registration certificate or permit issued in accordance with Part 201 of this
				  Title prior to operation as an economic dispatch source.
(b) An owner or operator of a distributed
				  generation source that will operate as an economic dispatch source and is
				  subject to a registration or permit issued by the Department prior to the
				  effective date of this Part, must notify the Department in writing by March 15,
				  2021 or 30 days prior to operating the source as an economic dispatch source,
				  whichever is later.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 222 - Distributed Generation Sources › Section 222.4 - Control requirements

Current through Register Vol. 46, No. 28, July 10, 2024
(a)
				  Effective May 1, 2021, owners or operators of economic dispatch sources subject
				  to this Part must comply with the following requirements:
(1) combustion turbines firing natural gas:
				  must be of model year 2000 or newer or must have a NOx emission rate less than
				  or equal to 2.96 pounds per megawatt-hour as certified in writing by a pro
				  fessional engineer;
(2) combustion
				  turbines firing oil: must be of model year 2000 or newer or must have a NOx
				  emission rate less than or equal to 2.96 pounds per megawatt-hour as certified
				  in writing by a professional engineer;
(3) compression-ignition engines: must be of
				  model year 200 0 or newer or must have a NOx emission rate less than or equal
				  to 2.96 pounds per megawatt-hour as certified in writing by a professional
				  engineer;
(4) lean-burn engines:
				  must be of model year 2000 or newer or must have a NOx emission rate less than
				  or equal to 2.96 pounds per megawatt- hour as certified in writing by a
				  professional engineer; or
(5)
				  rich-burn engines: must be equipped with three-way catalyst emission controls.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 222 - Distributed Generation Sources › Section 222.5 - Emissions testing

Current through Register Vol. 46, No. 28, July 10, 2024
(a)
				  Emissions test reports demonstrating compliance with subdivision
				  222.4(b) 
				  must be submitted to and approved by the Department before an economic dispatch
				  may operate on or after May 1, 2025.
(b) Emission test requirements.
(1) The owner or operator of an economic
				  dispatch source must notify the Regional Air Pollution Control Engineer in
				  writing at least 15 calendar days prior to the scheduled date of an emissions
				  test. Written test protocols are required only if the test method listed in
				  paragraph 222. 5(b)(2) will not be used during the emissions testing. In such
				  case, the emissions test may not commence until 15 calendar days following the
				  Department's approval of the protocols.
(2) Emission test method. Method 7E pursuant
				  to  40 CFR 60, Appendix A (see Table 1, Section
				  200.9 
				  of this Title).
(3) Additional
				  protocols.
(i) Each emissions test must be
				  conducted at the maximum load relief of the economic dispatch source.
(ii) The span of the monitoring system must
				  be selected such that the pollutant gas concentration equivalent to the
				  emission limit is not less than 30 percent of the span.
(4) Emission test reports. The owner or
				  operator of an economic dispatch source subject to this section must submit an
				  electronic copy of the emission test report to the Department within 60
				  calendar days after the completion of the tests. In addition, the data
				  collected during the test must be available to the Department in an electronic
				  format acceptable to the Department.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 222 - Distributed Generation Sources › Section 222.6 - Recordkeeping

Current through Register Vol. 46, No. 28, July 10, 2024
(a) The Department
				  may enter a facility during normal operating hours to inspect an economic
				  dispatch source subject to the requirements of this Part, and any records,
				  papers, log books, and operational data maintained pursuant to this Part. Upon
				  request, all records, papers, lo g books and operational data maintained
				  pursuant to this Part must be made available to the Department.
(b) Emission test results must be maintained
				  at a facility for five years from the date of the emission test.
(c) The following operational data must be
				  recorded for each economic dispatch source subject to this Part in a format
				  acceptable to the Department. The following data must be recorded monthly and
				  maintained at the facility for five years from the date the data were recorded:
(1) hours of operation;
(2) type and quantity of fuel(s) used or
				  purchased; and
(3) electricity
				  generated by economic dispatch source in kilowatt- hours.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 222 - Distributed Generation Sources › Section 222.7 - Severability

Current through Register Vol. 46, No. 28, July 10, 2024
Each provision of this Part shall be deemed severable. If
					 any provision of this Part is held to be invalid, the remainder of this Part
					 shall continue in full force and effect.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 223 - Petroleum Refineries › Section 223.1 - Applicability

Current through Register Vol. 46, No. 28, July 10, 2024
This Part shall apply to all petroleum refineries, except
					 for sections
					 223.7
					 and
					 223.10  which
					 apply only to those petroleum refineries located in a nonattainment area for
					 ozone.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 223 - Petroleum Refineries › Section 223.3 - Particulate emissions

Current through Register Vol. 46, No. 28, July 10, 2024
(a)
				  Existing emission sources. No person shall cause or allow emission of
				  particulates to the outdoor atmosphere from any existing fluid catalytic
				  cracking unit catalyst regenerator or fluid catalytic unit incinerator-waste
				  heat boiler in excess of 0.15 grain per cubic foot of exhaust gas, expressed at
				  standard conditions on a dry gas basis. An existing emission source is one for
				  which an application for a permit to construct was received, pursuant to Part
				  201 of this Subchapter, prior to June 12, 1973.
(b) New emission sources and modifications.
(1) No person shall cause or allow emission
				  of particulates to the outdoor atmosphere from any fluid catalytic cracking
				  unit catalyst regenerator or fluid catalytic cracking unit incinerator-waste
				  heat boiler or modification thereof, for which an application for a permit to
				  construct is received by the commissioner pursuant to Part 201 of this Title,
				  subsequent to June 11, 1973, in excess of 1.0 pound per 1,000 pounds of coke
				  burn-off in the catalyst regenerator.
(2) In those instances in which auxiliary
				  liquid and/or solid fuels are burned in the fluid catalytic cracking unit
				  incinerator-waste heat boiler, particulates in excess of that permitted by
				  subdivision (a) of this section may be emitted to the outdoor atmosphere,
				  except that the incremental rate of particulate emissions shall not exceed 0.10
				  lb per million Btu heat input attributable to such liquid and/or solid
				  fuel.
New York Codes, Rules and Regulations › Title 6 - DEPARTMENT OF ENVIRONMENTAL CONSERVATION › Chapter III - AIR RESOURCES › Subchapter A - PREVENTION AND CONTROL OF AIR CONTAMINATION AND AIR POLLUTION › Part 223 - Petroleum Refineries › Section 223.4 - Opacity of emissions

Current through Register Vol. 46, No. 28, July 10, 2024
(a) No
				  person subject to the provisions of this Part will allow or cause emissions to
				  the outdoor atmosphere of gases from any fluid catalytic cracking unit catalyst
				  regenerator exhibiting greater than 30 percent opacity except for one
				  six-minute average opacity reading in any one-hour period.
(b) Except as provided in subdivision (a) of
				  this section, no person subject to the provisions of this Part shall allow or
				  cause emissions to the outdoor atmosphere having an opacity of 20 percent or
				  greater.
(c) All refinery flares
				  shall be equipped with smokeless tips.