GreatNorthCollective/greatnorth-canada-federal-laws-text huggingface dataset:
Multi-Sector Air Pollutants Regulations — 96
Air-fuel ratio 96 The responsible person described in subsection 95 (1) must verify, maintain and adjust the air-fuel ratio of the engine so as to ensure that its NO x emission intensity, during the diverse ambient conditions anticipated during a year, does not exceed the following limit or value: (a) the applicable NO x emission intensity limit referred to in sections 54 , 55 , 57 and 58 ; and (b) [Repealed, SOR/2016-151, s. 144] (c) in respect of an engine that belongs to a subgroup, the NO x emission value assigned to the engine under (i) subsection 66 (1), if that emission value is 210 ppmvd 15% or 4 g/kWh, or (ii) subsection 67 (1). SOR/2016-151, s. 144
Multi-Sector Air Pollutants Regulations — 97
Engine registry 97 (1) The Minister is to establish an engine registry in order to carry out the purpose of this Part by facilitating the provision to the Minister of information that is (a) necessary to know whether this Part applies in respect of an engine; and (b) related to the requirements referred to in section 60 that are imposed on engines that belong to a subgroup. Regular-use and low-use engines (2) The following engines must be registered in the engine registry: (a) a modern engine with a rated brake power of at least 75 kW that is regular-use or low-use; and (b) a pre-existing engine with a rated brake power of at least 250 kW that is regular-use or low-use. Registration date — engines in group (3) A responsible person for a regular-use engine that they have designated as belonging to their group must register the engine on or before (a) January 1, 2019, if the designation occurs before that date; and (b) July 1 of the year that follows the year during which the engine is designated as belonging to the group, if the designation occurs on or after January 1, 2019. Registration date — engines not in group (4) An engine referred to in subsection (2) that does not belong to a group must be registered on or before (a) for a pre-existing engine, the later of (i) January 1, 2019, and (ii) July 1 of the year that follows the first year during which there is a responsible person for the engine, and (b) for a modern engine, July 1 of the year that follows the first year during which there is a responsible person for the engine. Re-registration (5) An engine that has been registered in accordance with subsection (4) — or re-registered under this subsection — must be re-registered on or before July 1 of the year that follows the last year during which there remains at least one responsible person for the engine who has registered or re-registered the engine. Registration (6) The registration occurs when the Minister is provided with the information for inclusion in the engine registry in respect of the engine that is set out in Schedule 9.
Multi-Sector Air Pollutants Regulations — 98
Change of information — engine registry 98 (1) If there is a change in the information provided to the Minister for inclusion in the engine registry in respect of an engine or a replacement unit, the Minister must be provided with the updated information (a) within 30 days after the place where a record is kept is changed, if the updated information involves a change in the place where a record is kept; and (b) on or before July 1 of the year that follows the year during which the change occurred but before a compliance report in respect of that year is provided to the Minister, in any other case. Responsible person (2) The updated information must be provided by (a) the responsible person referred to in subsection 97 (3), if the updated information is in respect of an engine referred to in that subsection or in respect of a replacement unit referred to in subsection 64 (4); or (b) a responsible person who has registered or re-registered the engine in the engine registry in accordance with subsection 97 (4) or (5), if the updated information is in respect of an engine referred to in that subsection.
Multi-Sector Air Pollutants Regulations — 99
Compliance reports 99 (1) A compliance report must, on or before July 1 of a year, be provided that contains the information set out in Schedule 10 in respect of the preceding year to the Minister in respect of (a) an engine or replacement unit that, during the preceding year, belongs to a subgroup; or (b) an engine that, during the preceding year, (i) is subject to a NO x emission intensity limit, (ii) is low-use; or (iii) combusts fuel for a period referred to in section 49 . Responsible person (2) The compliance report must be provided by the responsible person for the engine or replacement unit who (a) provided updated information in accordance with paragraph 98 (2)(a) in respect of an engine or replacement unit referred to in that paragraph, if that updated information was provided; (b) provided updated information in accordance with paragraph 98 (2)(b) in respect of an engine referred to in that paragraph, if that updated information was provided; or (c) registered the engine in the engine registry in accordance with subsection 97 ((3) or (4) or re-registered it in the engine registry in accordance with subsection 97 (5), in any other case.
Multi-Sector Air Pollutants Regulations — 100
ctrochemical analyzer used to conduct a sequence of calibration error checks or an emissions check, (i) the serial number, make and model of the electrochemical analyzer, and (ii) a log of operations and maintenance of the electrochemical analyzer; (l) for each sequence of calibration error checks of an analyzer that are conducted under section 83 , (i) the serial number, make and model of the analyzer, (ii) the date on which the sequence was conducted, (iii) the certified concentration of each zero gas and of each span gas for O 2 , CO, NO or NO 2 , (iv) the stabilization periods recorded under subsection 83 (5) for each cell’s response — following the introduction of a span gas for O 2 , CO, NO or NO 2 into the analyzer — to the gas to which the cell is designed to respond, (v) the reading of each cell’s response to a calibration gas referred to in subsection 83 (2), (vi) the calibration error described in subsection 83 (6), for each zero gas and span gas for, as applicable, O 2 , CO, NO or NO 2 , (vii) the flow rate of each span gas that is measured by the analyzer during the sequence, (viii) the reading of the response referred to in subsection 84 (1) for the CO cell and NO cell, and (ix) the CO interference response that is determined under subsection 84 (2) and the NO interference response that is determined under subsection 84 (3); (m) if a performance test or emissions check was conducted on the engine under paragraph 93 (a), information that establishes that it was not operating for each day in the period of its non-operation referred to in that paragraph; (n) a log of operations and maintenance of the systems and components related to the engine that are set out in subsection 95 (2); and (o) for each engine referred to in subsection 95 (1), the type of equipment or method used to control the air-fuel ratio of the engine, and how that ratio was verified and maintained or adjusted, during the diverse ambient conditions in each year, so as to ensure that its NO x emission intensity does not exceed the NO x emission intensity limit or NO x emission value referred to in section 96 .
Multi-Sector Air Pollutants Regulations — 101
Definitions 101 The following definitions apply in this Part and in Schedule 11. cement means a powder that results from the grinding of clinker and the blending of the ground clinker with other materials. ( ciment ) clinker means solid nodules that are produced by the pyroprocessing of feedstock in a kiln. ( clinker ) feedstock means a ground blend of calcium carbonate, silica, alumina, ferrous oxide and any other material that is used to produce clinker. ( matière première ) grey cement means cement that is manufactured from clinker that contains more than 0.5% by weight of ferric oxide. ( ciment gris ) kiln means a thermally insulated chamber into which blended feedstock is introduced for pyroprocessing in order to produce clinker. ( four ) long dry kiln means a kiln that (a) is not equipped with a system for preheating dry feedstock; or (b) is equipped with a system for preheating dry feedstock with at most two stages of preheating before the feedstock is introduced into the kiln. ( four long à voie sèche ) precalciner kiln means a kiln that is equipped with a system for precalcining dry feedstock using, before the feedstock is introduced into the kiln, a secondary burner that has a tertiary supply of combustion air. ( four à précalcinateur ) preheater kiln means a kiln that is equipped with a system for preheating dry feedstock with at least three stages of preheating before the feedstock is introduced into the kiln. ( four à préchauffeur ) wet kiln means a kiln into which feedstock is introduced as a fine slurry with a water content of more than 20% by weight. ( four à voie humide )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
cement means a powder that results from the grinding of clinker and the blending of the ground clinker with other materials. ( ciment )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
clinker means solid nodules that are produced by the pyroprocessing of feedstock in a kiln. ( clinker )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
feedstock means a ground blend of calcium carbonate, silica, alumina, ferrous oxide and any other material that is used to produce clinker. ( matière première )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
grey cement means cement that is manufactured from clinker that contains more than 0.5% by weight of ferric oxide. ( ciment gris )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
kiln means a thermally insulated chamber into which blended feedstock is introduced for pyroprocessing in order to produce clinker. ( four )
Multi-Sector Air Pollutants Regulations — (a)
long dry kiln means a kiln that (a) is not equipped with a system for preheating dry feedstock; or (b) is equipped with a system for preheating dry feedstock with at most two stages of preheating before the feedstock is introduced into the kiln. ( four long à voie sèche )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
precalciner kiln means a kiln that is equipped with a system for precalcining dry feedstock using, before the feedstock is introduced into the kiln, a secondary burner that has a tertiary supply of combustion air. ( four à précalcinateur )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
preheater kiln means a kiln that is equipped with a system for preheating dry feedstock with at least three stages of preheating before the feedstock is introduced into the kiln. ( four à préchauffeur )
Multi-Sector Air Pollutants Regulations — Multi-Sector Air Pollutants Regulations
wet kiln means a kiln into which feedstock is introduced as a fine slurry with a water content of more than 20% by weight. ( four à voie humide )
Multi-Sector Air Pollutants Regulations — 102
Application — grey cement 102 This Part applies in respect of cement manufacturing facilities that produce clinker for use in the manufacture of grey cement.
Multi-Sector Air Pollutants Regulations — 103
Obligation — over two consecutive years 103 (1) As of January 1, 2020, a cement manufacturing facility must not — over any two consecutive years — emit NO x or SO 2 in a quantity that exceeds the emission limit for each of those years for that substance, as determined in accordance with sections 104 and 105 , respectively. Obligation — yearly (2) If a cement manufacturing facility does not comply with that emission limit for either NO x or SO 2 over a period of two consecutive years, it must not — during each year after that period — emit either NO x or SO 2 in a quantity that exceeds its emission limit for that year, as determined in accordance with sections 104 and 105 .
Multi-Sector Air Pollutants Regulations — 104
Emission limit — NO x 104 (1) The emission limit for a year for the emission of NO x from a cement manufacturing facility is determined by the formula Σ i (EI NOx i × P i )/Σ i P i where EI NOx i is the maximum emission intensity for the year for the emission of NO x from the ith kiln stack in the cement manufacturing facility — namely, the maximum quantity of NO x emitted per tonne of clinker produced at the ith kiln in the cement manufacturing facility in the year — which is (a) for preheater kilns and precalciner kilns, 2.25 kg/t, and (b) for wet kilns and long dry kilns, as elected in accordance with subsection (2), (i) 2.55 kg/t, or (ii) determined by the formula EI 2006 – (0.3 × EI 2006 ) where EI 2006 is the quantity of NO x , expressed in kg, that was emitted at the cement manufacturing facility in 2006 per tonne of clinker produced, as reported in respect of the cement manufacturing facility to the Minister in accordance with the Notice with respect to reporting of information on air pollutants, greenhouse gases and other substances for the 2006 calendar year , published in the Canada Gazette , Part I, Volume 141, No. 49, on December 8, 2007; i is ith kiln in the cement manufacturing facility, where i goes from 1 to n and where n is the number of kilns in the cement manufacturing facility; and P i is the quantity of clinker, expressed in t, that is produced by the ith kiln in the cement manufacturing facility in the year. Election — 2020 (2) A responsible person for the cement manufacturing facility who provides the Minister with a compliance report required by section 108 in respect of the year 2020 must, in that compliance report, make the election referred to in paragraph (b) of the description of EI NOx i in subsection (1). Election — subsequent years (3) The maximum emission intensity for the emission of NO x from the ith kiln in the cement manufacturing facility for the year 2020 that is elected by the responsible person also applies for each subsequent year.
Multi-Sector Air Pollutants Regulations — 105
Emission limit — SO 2 105 The emission limit for a year for the emission of SO 2 from a cement manufacturing facility is determined by the formula Σ i (EI SO2 i × P i )/Σ i P i where EI SO2 i is the maximum emission intensity for the year for the emission of SO 2 from the ith kiln stack in the cement manufacturing facility — namely, the maximum quantity of SO 2 emitted per tonne of clinker produced at the ith kiln in the cement manufacturing facility in the year — which is 3.0 kg/t; i is the ith kiln in the cement manufacturing facility, where i goes from 1 to n and where n is the number of kilns in the cement manufacturing facility; and P i is the quantity of clinker, expressed in t, that is produced by the ith kiln in the cement manufacturing facility in the year.
Multi-Sector Air Pollutants Regulations — 106
Quantity of NO x and SO 2 — CEMS 106 As of January 1, 2018, the quantity, expressed in kg, of NO x and SO 2 emitted, during a given year, from each kiln stack in a cement manufacturing facility must be determined by means of a CEMS.
Multi-Sector Air Pollutants Regulations — 107
Quantity of clinker 107 (1) For the purpose of determining the value for P i in sections 104 and 105 , the quantity of clinker that is produced at each kiln in the cement manufacturing facility in the year must be determined by (a) weighing that quantity directly using the measuring devices that were used for inventory purposes; (b) using a method of calculation that is based on the measuring devices that were used for inventory purposes; or (c) applying a feedstock-to-clinker conversion factor, specific to the kiln, to a direct measurement of the quantity of feedstock introduced into the kiln during that year, which accurately determines the quantity of clinker that is produced from a given quantity of feedstock introduced. Accuracy of feedstock-to-clinker conversion factor (2) The accuracy of the feedstock-to-clinker conversion factor must be verified (a) at least once per year, but at least four months after a previous verification; and (b) as soon as feasible after a major change in the clinker production processes that could affect the accuracy of the factor. Record-making (3) A record of that verification must be made that demonstrates the accuracy of the feedstock-to-clinker conversion factor.
Multi-Sector Air Pollutants Regulations — 108
Compliance report 108 As of January 1, 2019, on or before June 1 of every year a compliance report that contains the information for the cement manufacturing facility that is set out in Schedule 11 in respect of the preceding year must be provided to the Minister.
Multi-Sector Air Pollutants Regulations — 109
CEMS Reference Method — compliance 109 If a CEMS is used to determine a NO x emission intensity under Part 1 or a quantity of emissions under section 106 , the CEMS Reference Method must be complied with, notably (a) the design specifications and any related requirements that are set out in (i) Section 3.0 of the EC CEMS Code entitled “Design Specifications and Test Procedures”, or (ii) Section 2.0 of the Alberta CEMS Code entitled “Design Specifications”; (b) the installation specifications and any related requirements that are set out in (i) Section 4.0 of the EC CEMS Code entitled “Installation Specifications”, or (ii) Section 3.0 of the Alberta CEMS Code entitled “Installation Specifications”; (c) the performance specifications and any related requirements, particularly in respect of testing, that are set out in (i) Section 5.0 of the EC CEMS Code entitled “Certification Performance Specifications and Test Procedures”, including certification of the CEMS and the conduct of relative accuracy tests and bias tests of the relative accuracy test audit (RATA), or (ii) Section 4.0 of the Alberta CEMS Code entitled “Performance Specifications and Test Procedures”, including certification of the CEMS and the conduct of relative accuracy tests and bias tests of the relative accuracy test audit (RATA); and (d) the requirements concerning the development and implementation of manuals or plans for quality assurance and quality control that are set out in (i) Section 6.0 of the EC CEMS Code entitled “Quality Assurance and Quality Control”, or (ii) Section 5.0 of the Alberta CEMS Code entitled “Quality Assurance and Quality Control”.
Multi-Sector Air Pollutants Regulations — 110
Annual audit 110 (1) For each year during which a responsible person uses a CEMS to determine a NO x emission intensity under Part 1 or a quantity of emissions under section 106 , the responsible person must ensure that an auditor evaluates whether, in the auditor’s opinion, the responsible person has complied with the CEMS Reference Method and, in particular, whether (a) the CEMS has met the specifications set out in the CEMS Reference Method; (b) the results of each relative accuracy test and each bias test for each of the relative accuracy test audits (RATA) for the 12 months preceding the auditor’s audit have not exceeded the applicable limit referred to in the CEMS Reference Method; and (c) the responsible person has established a Quality Assurance/Quality Control manual that complies with Section 6.0 of the EC CEMS Code or a Quality Assurance Plan that complies with Section 5.1 of the Alberta CEMS Code and, if so, whether (i) the responsible person has implemented it, (ii) its implementation ensures that the data generated by the CEMS is complete, accurate and precise, and (iii) it has been updated in accordance with the CEMS Reference Method. Auditor’s report (2) The responsible person must, within 30 days after the day on which the auditor completes their audit, obtain a report, signed by the auditor, that contains the information set out in Schedule 12. Request for auditor’s report (3) The responsible person must, on the Minister’s request, provide the Minister with a copy of an auditor’s report within 15 days after the request. Provision of auditor’s report to Minister (4) A responsible person who uses a CEMS to determine a NO x emission intensity under Part 1 must, for each year during which they use a CEMS, provide the Minister with a copy of the auditor’s report for that year by June 1 of the following year, if the opinion stated by the auditor in the report is that the responsible person has not complied with any aspect of the CEMS Reference Method. Auditor (5) For the purpose of this section, an auditor is a person who (a) is independent of the responsible person who uses a CEMS; and (b) has demonstrated knowledge of and experience in (i) the certification, operation and relative accuracy test audit (RATA) of Continuous Emission Monitoring Systems, (ii) quality assurance and quality control procedures in relation to those systems, and (iii) the conducting of audits in relation to those systems.
Multi-Sector Air Pollutants Regulations — 111
Installation, operation, maintenance and calibration 111 Unless otherwise provided by these Regulations, any measuring device that is used to determine a quantity for the purpose of these Regulations must be installed, operated, maintained and calibrated in accordance with the manufacturer’s specifications or any applicable generally recognized national or international industry standard.
Multi-Sector Air Pollutants Regulations — 112
le — read in the entire context of the rule that is to be replaced, including the context of the document within which that replaced rule is found, and read harmoniously within the scheme of these Regulations — is at least as rigorous and effective as the rule that is to be replaced; (f) information that identifies the boiler, heater, engine or kiln, including (i) for the boiler or heater, (A) an indication as to whether it is a boiler or a heater, (B) the name of its manufacturer, along with its serial number, make and model, (C) its rated capacity, and (D) in respect of the facility where it is located, its identifier, if any, within that facility and the facility’s (I) civic address, (II) National Pollutant Release Inventory identification number assigned by the Minister for the purpose of section 48 of the Act, and (III) provincial identification number, (ii) for the engine, (A) its serial number or, if the serial number is not known or cannot be obtained, its unique alphanumeric identifier, (B) its make and model, and (C) in respect of the facility where it is located, its identifier, if any, within that facility and the facility’s (I) civic address or, if there is no civic address, its latitude and longitude, (II) National Pollutant Release Inventory identification number assigned by the Minister for the purpose of section 48 of the Act, and (III) provincial identification number, (iii) for the kiln , (A) the name of the cement manufacturing facility where it is located, (B) the civic address of the cement manufacturing facility or, if there is no civic address, its latitude and longitude, (C) the cement manufacturing facility’s National Pollutant Release Inventory identification number assigned by the Minister for the purpose of section 48 of the Act, (D) information that identifies the kiln, and (E) the kiln’s type, that is, whether it is (I) a precalciner kiln, (II) a preheater kiln, (III) a wet kiln, or (IV) a long dry kiln; and (g) any other information that is necessary to consider in order to grant the application. Paragraph (4)(e) — concentration of NO x (5) If a proposed alternative rule described in paragraph (3)(b) concerns the determination of the concentration of NO x in a gas, other than by means of a CEMS, the demonstration referred to in paragraph (4)(e) must compare its rigour and effectiveness to the rigour and effectiveness of making that determination based on EPA Method 7E or ASTM D6522-11.