natgillin/translations-raw huggingface dataset:
Uanset stk. 1, 2 og 3, men med forbehold af stk. 5, kan en part, som bliver part i nærværende protokol mellem 1. januar 2013 og 31. december 2019, i forbindelse med sin ratifikation, accept, godkendelse eller tiltrædelse af nærværende protokol angive, at den ønsker at forlænge en eller flere tidsfrister for indførelsen af de i artikel 3, stk. 2, 3, 5 og 7, omhandlede grænseværdier, som følger:
Solvent management plan
for eksisterende stationære kilder: op til 15 år efter at nærværende protokol træder i kraft for den pågældende part
Introduction
for brændsel og nye mobile kilder: op til fem år efter at nærværende protokol træder i kraft for den pågældende part
This appendix to the annex on limit values for emissions of VOCs from stationary sources provides guidance on carrying out a solvent management plan.
for flygtige organiske forbindelser i produkter: op til fem år efter at nærværende protokol træder i kraft for den pågældende part.
It identifies the principles to be applied (paragraph 2), provides a framework for the mass balance (paragraph 3) and provides an indication of the requirements for verification of compliance (paragraph 4).
En part, som har valgt at bringe artikel 3a i nærværende protokol i anvendelse i forhold til bilag VI og/eller VII, må ikke også forlænge tidsfristerne i henhold til stk. 4 for det samme bilag.«
Principles
U. Bilag VIII
The solvent management plan serves the following purposes:
Bilag VIII affattes således:
Verification of compliance, as specified in the annex; and
»Grænseværdier for brændstof og nye mobile kilder
Identification of future reduction options.
Dette bilag indeholder emissionsgrænseværdier for NOx, udtrykt som nitrogendioxid-ækvivalenter (NO2), for kulbrinter, der hovedsagelig består af flygtige organiske forbindelser, for kulilte (CO) og for partikler samt miljøspecifikationer for brændstof, der markedsføres til brug i biler.
Definitions
Personbiler og lette køretøjer
Inputs of organic solvents:
Grænseværdierne for motordrevne køretøjer med mindst fire hjul, som anvendes til befordring af passagerer (klasse M) og gods (klasse N), er angivet i tabel 1.
I1 The quantity of organic solvents or their quantity in preparations purchased that are used as input into the process in the time frame over which the mass balance is being calculated;
Tunge køretøjer
I2 The quantity of organic solvents or their quantity in preparations recovered and reused as solvent input into the process.
Grænseværdierne for motorer til tunge køretøjer er angivet i tabel 2 og 3 alt efter de relevante prøvningsprocedurer.
(The recycled solvent is counted every time it is used to carry out the activity.).
Ikke-vejgående køretøjer og maskiner med kompressionstænding og gnisttænding
Outputs of organic solvents:
Grænseværdierne for landbrugs- og skovbrugstraktorer og andre motorer til ikke-vejgående køretøjer/maskiner er anført i tabel 4 til 6.
Emission of VOCs in waste gases;
Grænseværdierne for lokomotiver og togvogne er angivet i tabel 7 og 8.
Organic solvents lost in water, if appropriate taking into account wastewater treatment when calculating O5;
Grænseværdierne for fartøjer på indre vandveje er angivet i tabel 9.
The quantity of organic solvents that remains as contamination or residue in output of products from the process;
Grænseværdierne for lystfartøjer er angivet i tabel 10.
Uncaptured emissions of organic solvents to air.
Motorcykler og knallerter
This includes the general ventilation of rooms, where air is released to the outside environment via windows, doors, vents and similar openings;
Grænseværdierne for motorcykler og knallerter er angivet i tabel 11 og 12.
Organic solvents and/or organic compounds lost due to chemical or physical reactions (including, for example, those that are destroyed, e.g., by incineration or other waste-gas or wastewater, or captured, e.g., by adsorption, as long as they are not counted under O6, O7 or O8);
Brændstofkvalitet
Organic solvents contained in collected waste;
Specifikationerne for miljøkvaliteten af benzin og diesel er angivet i tabel 13 og 14.
Organic solvents, or organic solvents contained in preparations, that are sold or are intended to be sold as a commercially valuable product;
Grænseværdier for personbiler og lette køretøjer
Organic solvents contained in preparations recovered for reuse but not as input into the process, as long as they are not counted under O7;
Referencemasse (RW) (kg)
Organic solvents released in other ways.
Grænseværdier [68]
Guidance on use of the solvent management plan for verification of compliance
Kulilte
The use of the solvent management plan will be determined by the particular requirement which is to be verified, as follows:
Kulbrinter i alt (HC)
Verification of compliance with the reduction option mentioned in paragraph 6 (a) of the annex, with a total limit value expressed in solvent emissions per unit product, or as otherwise stated in the annex:
Nitrogenoxider
For all activities using the reduction option mentioned in paragraph 6 (a) of the annex, the solvent management plan should be put into effect annually to determine consumption.
Kulbrinter og nitrogenoxider samlet
Consumption can be calculated by means of the following equation:
Partikler
C = I1 – O8
Partikelantal [68] (P)
A parallel exercise should also be undertaken to determine solids used in coating in order to derive the annual reference emission and the target emission each year;
L6 (#/km)
For assessing compliance with a total limit value expressed in solvent emissions per unit product or as otherwise stated in the annex, the solvent management plan should be put into effect annually to determine emission of VOCs.
Kategori
Emission of VOCs can be calculated by means of the following equation:
Klasse, anvendelsesdato [67]
E = F + O1
Benzin
Where F is the fugitive emission of VOC as defined in subparagraph (b) (i) below.
Alle
The emission figure should be divided by the relevant product parameter;
1305 < RW ≤ 1760
Determination of fugitive emission of VOCs for comparison with fugitive emission values in the annex:
RW 1305
Methodology: The fugitive emission of VOC can be calculated by means of the following equation:
Grænseværdier for tunge køretøjer — ESC-test (stationær funktionstest) og ELR-test (belastningsresponstest)
This quantity can be determined by direct measurement of the quantities.
Anvendelsesdato
Alternatively, an equivalent calculation can be made by other means, for instance by using the capture efficiency of the process.
Kulilte (g/kWh)
The fugitive emission value is expressed as a proportion of the input, which can be calculated by means of the following equation:
Kulbrinter (g/kWh)
Frequency: Fugitive emission of VOCs can be determined by a short but comprehensive set of measurements.
Kulbrinter i alt (g/kWh)
This need not to be done again until the equipment is modified.
Nitrogenoxider (g/kWh)
T. Annex VII
Partikler (g/kWh)
For annex VII there is substituted the following:
Røg
‘Timescales under article 3
B2 (»EURO V«) [71]
The timescales for the application of the limit values referred to in article 3, paragraphs 2 and 3, shall be:
»EURO VI« [72]
For new stationary sources, one year after the date of entry into force of the present Protocol for the Party in question; and
Grænseværdier for tunge køretøjer — ETC-test (cyklustest med glidende overgang)
For existing stationary sources, one year after the date of entry into force of the present Protocol for the Party in question or 31 December 2020, whichever is the later.
Note: PI = Styret tænding.
The timescales for the application of the limit values for fuels and new mobile sources referred to in article 3, paragraph 5, shall be the date of entry into force of the present Protocol for the Party in question or the dates associated with the measures specified in annex VIII, whichever is the later.
CI = Kompressionstænding.
The timescales for the application of the limit values for VOCs in products referred to in article 3, paragraph 7, shall be one year after the date of entry into force of the present Protocol for the Party in question.
Anvendelsesdato [73]
Notwithstanding paragraphs 1, 2 and 3, but subject to paragraph 5, a Party to the Convention that becomes a Party to the present Protocol between January 1, 2013, and December 31, 2019, may declare upon ratification, acceptance, approval of, or accession to, the present Protocol that it will extend any or all of the timescales for application of the limit values referred to in article 3, paragraphs 2, 3, 5 and 7, as follows:
Kulbrinter bortset fra metan (g/kWh)
For existing stationary sources, up to fifteen years after the date of entry into force of the present Protocol for the Party in question;
Metan [74] (g/kWh)
For fuels and new mobile sources, up to five years after the date of entry into force of the present Protocol for the Party in question; and
Partikler (g/kWh) [75]
For VOCs in products, up to five years after the date of entry into force of the present Protocol for the Party in question.
B2 »EURO V« [76]
A Party that has made an election pursuant to article 3bis of the present Protocol with respect to annex VI and/or VIII may not also make a declaration pursuant to paragraph 4 applicable to the same annex.’
»EURO VI« (CI) [77]
U. Annex VIII
»EURO VI« (PI) [77]
For annex VIII the following text is substituted:
Nettoeffekt (P) (kW)
This annex specifies emission limit values for NOx, expressed as nitrogen dioxide (NO2) equivalents, for hydrocarbons, most of which are volatile organic compounds, for carbon monoxide (CO) and for particulate matter as well as environmental specifications for marketed fuels for vehicles.
Anvendelsesdato [78]
The timescales for applying the limit values in this annex are laid down in annex VII.
130 ≤ P ≤ 560
Passenger cars and light-duty vehicles
75 ≤ P < 130
Limit values for power-driven vehicles with at least four wheels and used for the carriage of passengers (category M) and goods (category N) are given in table 1.
56 ≤ P < 75
Heavy-duty vehicles
37 ≤ P < 56
Limit values for engines for heavy-duty vehicles are given in tables 2 and 3 on the applicable test procedures.
Grænseværdier for dieselmotorer til ikke-vejgående mobile maskiner, landbrugs- og skovbrugstraktorer (fase IV)
Compression-ignition (CI) and spark-ignition (SI) non-road vehicles and machines
Anvendelsesdato [80]
Limit values for agricultural and forestry tractors and other non-road vehicle/ machine engines are listed in tables 4 to 6.
Note: Parterne tillader, undtagen for så vidt angår maskiner og motorer, som er beregnet til eksport til lande, der ikke er parter i nærværende protokol, kun registrering (hvis dette er relevant) og markedsføring af nye motorer — hvad enten de er installeret i maskiner eller ej — hvis de overholder de grænseværdier, der er anført i tabellen.
Limit values for recreational crafts are listed in table 10.
Sum of kulbrinter og nitrogenoxider (g/kWh) [81]
Fuel quality
Ikke-håndholdte motorer
Limit values [68]
66 ≤ slagvol.
NMVOC
100 ≤ slagvol.
Nitrogen oxides
Slagvol. ≥ 225
Hydrocarbons and nitrogen oxides combined
Grænseværdier for motorer til fremdrift af lokomotiver
Particulate matter
Grænseværdier for motorer til fremdrift af motortog
Number of particles [68] (P)
Grænseværdier til fremdrift af fartøjer på indre vandveje
L6(#/km)
Slagvolumen (liter pr. cylinder/kW)
Category
Slagvol.
Class, application date [67]
Effekt ≥ 37 kW
Petrol
0,9 ≤ slagvol.
Diesel
1,2 ≤ slagvol.
Euro 5
2,5 ≤ slagvol.
All
5,0 ≤ slagvol.
I, 1.1.2014
15 ≤ slagvol.
II, 1.1.2014
Effekt < 3300 kW
1305 < RW ≤ 1760
Effekt > 3300 kW
III, 1.1.2014
25 ≤ slagvol.
Euro 6
= Ikke relevant.
I, 1.9.2015
Motortype
RW ≤ 1305
Kulbrinter (HC) (g/kWh)
II, 1.9.2016
Firetaktsmotor
III, 1.9.2016
Ikke rel.
Limit values for heavy-duty vehicles steady-state cycle load-response tests
Grænseværdier for motorcykler (> 50 cm3, > 45 km/time)
Application date
Note: Parterne tillader, undtagen for så vidt angår køretøjer, som er beregnet til eksport til lande, der ikke er parter i nærværende protokol, kun registrering (hvis dette er relevant) og markedsføring, hvis de overholder de grænseværdier, der er anført i tabellen.
Carbon monoxide (g/kWh)
Motorstørrelse
Hydrocarbons (g/kWh)
Grænseværdier
Total hydrocarbons (g/kWh)
Motorcykel < 150 cc
Nitrogen oxides (g/kWh)
HC = 0,8 g/km
Particulate matter (g/kWh)
NOx = 0,15 g/km
Smoke
Motorcykel > 150 cc
B2 (“EURO V”) [71]
Grænseværdier for knallerter (< 50 cm3, < 45 km/time)
“EURO VI” [72]
Tabel 13
Limit values for heavy-duty vehicles — transient cycle tests
Miljøspecifikationer for brændstof, som markedsføres til brug i køretøjer med motor med styret tænding — type: Benzin
Note: PI = Positive ignition.
Enhed
CI = Compression ignition.
Grænser
Application date [73]
Min.
Non-methane hydrocarbons (g/kWh)
Maks.
Methane [74] (g/kWh)
Motoroktantal
B2 “EURO V” [76]
Reid-damptryk, sommer [84]
“EURO VI” (CI) [77]
Destillation:
“EURO VI” (PI) [77]
Fordampet ved 100 °C
Limit values for diesel engines for non-road mobile machines, agricultural and forestry tractors (stage IIIB)
Fordampet ved 150 °C
Net power (P) (kW)
olefin
130 ≤ P ≤ 560
benzen
56 ≤ P < 75
Iltindhold
37 ≤ P < 56
Oxygenater:
Limit values for diesel engines for non-road mobile machines, agricultural and forestry tractors (stage IV)
Metanol, stabilisatorer skal tilsættes
Application date [80]
Etanol, stabilisatorer kan være tilsat
56 ≤ P < 130
Isopropylalkohol
Limit values for spark-ignition engines for non-road mobile machines
Tertbutylalkohol
Note: With the exception of machinery and engines intended for export to countries that are not Parties to the present Protocol, Parties shall permit the registration, where applicable, and the placing on the market of new engines, whether or not installed in machinery, only if they meet the respective limit values set out in the table.
Isobutylalkohol
Hand-held engines
Ethere med fem kulstofatomer pr. molekyle og derover
Displacement (cm3)
Andre oxygenater [86]
Sum of hydrocarbons and oxides of nitrogen (g/kWh) [81]
Svovlindhold
Disp < 20
Miljøspecifikationer for brændstof, som markedsføres til brug i køretøjer med motor med kompressionstænding — type: Dieselolie
20 ≤ disp.
Cetantal
< 50
Massefylde ved 15 °C
Disp ≥ 50
Destillationspunkt: 95 %
Non-hand-held engines
Grænseværdierne til begrænsning af emissionen fra brændsel og mobile kilder vil blive bestemt, hvor det er relevant, under hensyntagen til oplysninger om begrænsningsteknologi, grænseværdier, som anvendes i andre lande, og følgende dokumenter:
Disp < 66
Passenger Automobile and Light Truck Greenhouse Gas Emission Regulations, SOR/2010-201
66 ≤ disp.
Marine Spark-Ignition Engine, Vessel and Off-Road Recreational Vehicle Emission Regulations, SOR/2011-10
< 100
Renewable Fuels Regulations, SOR/2010-189
100 ≤ disp.
Regulations for the Prevention of Pollution from Ships and for Dangerous Chemicals, SOR/2007-86
< 225
Off-Road Compression-Ignition Engine Emission Regulations, SOR/2005-32
Disp ≥ 225
On-Road Vehicle and Engine Emission Regulations, SOR/2003-2
Limit values for engines used for propulsion of locomotives
Off-Road Small Spark-Ignition Engine Emission Regulations, SOR/2003-355
Limit values for engines used for propulsion of railcars
Sulphur in Diesel Fuel Regulations, SOR/2002-254
Limit values for engines for propulsion of inland waterways vessels
Gasoline and Gasoline Blend Dispensing Flow Rate Regulations SOR/2000-43
Displacement (liters per cylinder/kW)
Sulphur in Gasoline Regulations, SOR/99-236
Disp.
Benzene in Gasoline Regulations, SOR/97-493
Power ≥ 37 kW
Gasoline Regulations, SOR/90-247
0,9 ≤ disp.
Federal Mobile PCB Treatment and Destruction Regulations, SOR/90-5
1,2 ≤ disp.
Environmental Code of Practice for Aboveground and Underground Storage Tank Systems Containing Petroleum and Allied Petroleum Products
2,5 ≤ disp.
Canada-Wide Standards for Benzene, Phase 2
5,0 ≤ disp.
Environmental Code of Practice for Vapour Recovery in Gasoline Distribution Networks.
Power < 3300 kW
PN 1057
Power > 3300 kW
Environmental Code of Practice for Light Duty Motor Vehicle Emission Inspection and Maintenance Programs — 2nd Edition.
25 ≤ disp.
Joint Initial Actions to Reduce Pollutant Emissions that Contribute to Particulate Matter and Ground-level Ozone
Limit values for engines in recreational crafts Abbreviation: Not Appl.
Indførelse af et program til reduktion af emissionen fra mobile kilder — lette køretøjer, lette lastvogne, tunge lastvogne og brændstoffer i det omfang, det kræves i Clean Air Act, paragraf 202 a), g) og h), gennemført ved:
= Not Applicable.
Registration of fuels and fuel additives — 40 C.F.R del 79
Engine type
Regulation of fuels and fuel additives — 40 C.F.R del 80, herunder: afsnit A — general provisions; afsnit B — controls and prohibitions; afsnit D — reformulated gasoline; afsnit H — gasoline sulphur standards; afsnit I — motor vehicle diesel fuel; non-road, locomotive, and marine diesel fuel; and ECA marine fuel; afsnit L — gasoline benzene
Hydrocarbons (HC) (g/kWh)
Control of emissions from new and in-use highway vehicles and engines — 40 C.F.R del 85 og 86.
troke
Standarder for ikke-vejgående motorer og køretøjer er anført i følgende dokumenter:
Not Appl.
Fuel sulphur standards for non-road diesel engines — 40 C.F.R del 80, afsnit I
Limit values for motorcycles (> 50 cm3; > 45 km/h)
Aircraft engines — 40 C.F.R del 87
Note: With the exception of vehicles intended for export to countries that are not Parties to the present Protocol, Parties shall permit the registration, where applicable, and the placing on the market only if they meet the respective limit values set out in the table.
Exhaust emission standards for non-road diesel engines — Tier 2 and 3; 40 C.F.R del 89
Engine size
Non-road compression-ignition engines — 40 C.F.R del 89 og 1039
Limit values
Non-road and marine spark-ignition engines — 40 C.F.R del 90, 91, 1045 og 1054
Motorcycle < 150 cc
Locomotives — 40 C.F.R del 92 og 1033
HC = 0,8 g/km
Marine compression-ignition engines — 40 C.F.R del 94 og 1042
NOx = 0,15 g/km
New large non-road spark-ignition engines — 40 C.F.R del 1048
Motorcycle > 150 cc
Recreational engines and vehicles — 40 C.F.R del 1051
Limit values for mopeds (< 50 cm3; < 45 km/h)
Control of evaporative emissions from new and in-use non-road and stationary equipment — 40 C.F.R. del 1060
Table13
Engine testing procedures — 40 C.F.R del 1065
Environmental specifications for marketed fuels to be used for vehicles equipped with positive-ignition engines — Type: Petrol
General compliance provisions for non-road programs — 40 C.F.R del 1068.«
Parameter
V. Bilag IX
Unit
Det sidste punktum i punkt 6 udgår.
Limits
Det sidste punktum i punkt 9 udgår.
Minimum
Note 1 udgår.
Maximum
Bilag X
Research octane number
Følgende nye bilag X tilføjes:
Motor octane number
BILAG X
Reid vapour pressure, summer period [84]
Grænseværdier for emission af partikler fra stationære kilder
Distillation:
I denne del forstås ved »emissionsgrænseværdi« den maksimale mængde af støv og/eller TSP, som må være indeholdt i spildgasser fra et anlæg.
Evaporated at 100 °C
Medmindre andet angives, beregnes dette tal som det forurenende stofs masse i et givet volumen af forbrændingsgasser (udtrykt som mg/m3) under forudsætning af standardtemperatur- og trykforhold for tør gas (volumen ved 273,15 K, 101,3 kPa).
Evaporated at 150 °C
For spildgassernes iltindhold gælder de værdier, som er angivet i nedenstående tabeller for hver enkelt kildekategori.
Hydrocarbon analysis:
Emissionen overvåges under alle omstændigheder gennem målinger eller beregninger med mindst samme nøjagtighed.
olefins
Overholdelsen af grænseværdier kontrolleres ved hjælp af kontinuerlige eller diskontinuerlige målinger, typegodkendelse eller andre teknisk forsvarlige metoder.
aromatics
Ved kontinuerlig måling betragtes grænseværdien som overholdt, hvis den validerede månedlige gennemsnitsværdi ikke overstiger emissionsgrænseværdierne.
benzene
Ved diskontinuerlig måling eller andre egnede bestemmelses- eller beregningsprocedurer betragtes emissionsgrænseværdierne som overholdt, hvis gennemsnitsværdien af et passende antal målinger under repræsentative forhold ikke overstiger værdien af emissionsstandarden.
Oxygen content
Der kan i forbindelse med kontrollen tages højde for målingsmetodernes unøjagtighed.
Oxygenates:
6.
Methanol, stabilizing agents must be added
Særlige bestemmelser om fyringsanlæg, jf. stk. 7:
Ethanol, stabilizing agents may be necessary
En part kan i følgende tilfælde fritages for forpligtelsen til at overholde emissionsgrænseværdierne i stk. 7:
Iso-propyl alcohol
For eksisterende anlæg, som ikke drives i mere end 17500 driftstimer i perioden fra 1. januar 2016 og indtil den 31. december 2023.
Tert-butyl alcohol
Fyringsanlæg med en nominel indfyret effekt på over 50 MWth [1].
Iso-butyl alcohol
Grænseværdier for støvemission fra fyringsanlæg [2]Brændselstype
Ethers containing 5 or more carbon atoms per molecule
Emissionsgrænseværdi for støv (mg/m3) [3]
Other oxygenates [86]
20 (kul, brunkul og andet fast brændsel)
Sulphur content
20 (biomasse, tørv)
Environmental specifications for marketed fuels to be used for vehicles equipped with compression-ignition engines — Type: Diesel fuel
30 (kul, brunkul og andet fast brændsel)
Cetane number
30 (biomasse, tørv)
Density at 15 °C
25 (kul, brunkul og andet fast brændsel)
Distillation point: 95 %
10 (kul, brunkul og andet fast brændsel)
Polycyclic aromatic hydrocarbons
30 (generelt)
Limit values for controlling emissions from fuels and mobile sources will be determined, as appropriate, taking into account information on available control technologies, limit values applied in other jurisdictions, and the documents below:
50 (til forbrænding af destillations- og omdannelsesrester på raffinaderier fra råolieraffinering til eget forbrug på fyringsanlæg)
Passenger Automobile and Light Truck Greenhouse Gas Emission Regulations, SOR/2010–201;
25 (generelt)
Marine Spark-Ignition Engine, Vessel and Off-Road Recreational Vehicle Emission Regulations, SOR/2011–10;
20 (generelt)
Renewable Fuels Regulations, SOR/2010–189;
30 (for stålindustrigasser, som kan anvendes andre steder)
Regulations for the Prevention of Pollution from Ships and for Dangerous Chemicals, SOR/2007–86;
Grænseværdier for støvemissioner fra mineralolie- og gasraffinaderier
Off-Road Compression-Ignition Engine Emission Regulations, SOR/2005–32;
Emissionskilde
On-Road Vehicle and Engine Emission Regulations, SOR/2003–2;
Emissionsgrænseværdi for støv (mg/m3)
Off-Road Small Spark-Ignition Engine Emission Regulations, SOR/2003–355;
FCC-regeneratorer
Sulphur in Diesel Fuel Regulations, SOR/2002–254;
Fremstilling af cementklinker:
Gasoline and Gasoline Blend Dispensing Flow Rate Regulations SOR/2000–43;
Grænseværdier for støvemission fra fremstilling af cement [4]
Sulphur in Gasoline Regulations, SOR/99–236;
Cementanlæg, ovne, valseværker og klinkerkølere
Benzene in Gasoline Regulations, SOR/97–493;
Fremstilling af kalk:
Gasoline Regulations, SOR/90–247;
Grænseværdier for støvemission fra fremstilling af kalk [5]
Federal Mobile PCB Treatment and Destruction Regulations, SOR/90–5;
Kalkbrænding
Environmental Code of Practice for Aboveground and Underground Storage Tank Systems Containing Petroleum and Allied Petroleum Products;
Metalfremstilling og -forarbejdning:
Canada-Wide Standards for Benzene, Phase 2;
Grænseværdier for støvemission fra primær jern- og stålfremstilling
PN 1180;
Aktivitet og kapacitetstærskel
Environmental Code of Practice for Vapour Recovery in Gasoline Distribution Networks.
Sintringsanlæg
PN 1057;
Pelleteringsanlæg
Environmental Code of Practice for Light Duty Motor Vehicle Emission Inspection and Maintenance Programs — 2nd Edition.
20 for knusning, formaling og tørring
Joint Initial Actions to Reduce Pollutant Emissions that Contribute to Particulate Matter and Ground-level Ozone; and
15 for alle andre procestrin
Implementation of a mobile source emission control programme for light-duty vehicles, light-duty trucks, heavy-duty trucks and fuels to the extent required by sections 202 (a), 202 (g) and 202 (h) of the Clean Air Act, as implemented through:
Højovne: Recuperatorer (> 2,5 t/time)
Registration of fuels and fuel additives — 40 C.F.R Part 79;