natgillin/translations-raw huggingface dataset:
Driftslederen af et transportnet, der anvender metode B, føjer ikke CO2 modtaget fra et andet anlæg tilladt i henhold til direktiv 2003/87/EF til det beregnede emissionsniveau og trækker ikke CO2 overført til et andet anlæg fra det beregnede emissionsniveau.
In cases where CO2 capture is carried out by the same installation as the one from which the captured CO2 originates, the operator shall use zero for Tinput.
Metode A
In cases of stand-alone capture installations, the operator shall consider Ewithout capture to represent the amount of emissions that occur from other sources than the CO2 transferred to the installation for capture.
Hver driftsleder opgør emissioner i overensstemmelse med følgende formel:
The operator shall determine those emissions in accordance with this Regulation.
Emissioner = Samlet CO2-emission fra transportnettet [t CO2],
In the case of stand-alone capture installations, the operator of the installation transferring CO2 to the capture installation shall deduct the amount Tinput from the emissions of its installation in accordance with Article 49.
E egenaktivitet = Udledning fra transportnettets egen aktivitet, dvs. emissioner, der ikke stammer fra transporteret CO2, men inklusive emissioner fra brændsel anvendt i boosterstationer, der overvåges i overensstemmelse med de relevante afsnit af bilag IV
Determination of transferred CO2
T IND,i = Mængde CO2 overført til transportnettet ved indgangsstedet i, bestemt i henhold til artikel 40-46 og artikel 49.
Each operator shall determine the amount of CO2 transferred from and to the capture installation in accordance with Article 49 by means of measurement methodologies carried out in accordance with Articles 40 to 46.
T UD,j = Mængde CO2 overført ud af transportnettet ved udgangsstedet j, bestemt i henhold til artikel 40-46 og artikel 49.
Only where the operator of the installation transferring CO2 to the capture installation demonstrates to the satisfaction of the competent authority that CO2 transferred to the capture installation is transferred in total and to at least equivalent accuracy, may the competent authority allow that operator to use a calculation-based methodology in accordance with Article 24 or 25 to determine the amount Tinput instead of a measurement-based methodology in accordance with Article 40 to 46 and Article 49.
Metode B
DETERMINATION OF GREENHOUSE GAS EMISSIONS FROM THE TRANSPORT OF CO2 BY PIPELINES FOR GEOLOGICAL STORAGE IN A STORAGE SITE PERMITTED UNDER DIRECTIVE 2009/31/EC
Hver driftsleder bestemmer emissioner ved at tage højde for alle emissionsrelevante processer på anlægget samt mængden af CO2, der er opsamlet og overført til transportfaciliteten ved hjælp af følgende formel:
The boundaries for monitoring and reporting emissions from CO2 transport by pipeline shall be laid down in the transport network's greenhouse gas emissions permit, including all ancillary plant functionally connected to the transport network, including booster stations and heaters.
CO 2 fugitiv = Mængde fugitive emissioner [t CO2] fra CO2 transporteret i transportnettet, herunder fra pakninger, mellemliggende kompressorstationer og mellemliggende lagringsfaciliteter
Each transport network shall have a minimum of one start point and one end point, each connected to other installations carrying out one or more of the activities: capture, transport or geological storage of CO2.
CO 2 udluftet = Mængde udluftningsemissioner [t CO2] fra CO2 transporteret i transportnettet
Start and end points may include bifurcations of the transport network and cross national borders.
CO 2 udsivningsuheld = Mængde CO2 [t CO2] transporteret i transportnettet, der udledes som følge af svigt i en eller flere af transportnettets komponenter
Start and end points as well as the installations they are connecting to, shall be laid down in the greenhouse gas emissions permit.
Fugitive emissioner fra transportnettet
B. Quantification Methodologies for CO2
Driftslederen tager højde for fugitive emissioner fra følgende typer udstyr:
The operator of transport networks shall determine emissions using one of the following methods:
pakninger
Method A (overall mass balance of all input and output streams) set out in subsection B.1;
måleanordninger
Method B (monitoring of emission sources individually) set out in subsection B.2.
ventiler
In choosing either Method A or Method B, each operator shall demonstrate to the competent authority that the chosen methodology will lead to more reliable results with lower uncertainty of the overall emissions, using best available technology and knowledge at the time of the application for the greenhouse gas emissions permit and approval of the monitoring plan, without incurring unreasonable costs.
mellemliggende kompressorstationer
Where Method B is chosen each operator shall demonstrate to the satisfaction of the competent authority that the overall uncertainty for the annual level of greenhouse gas emissions for the operator's transport network does not exceed 7,5 %.
mellemliggende lagringsanlæg.
The operator of a transport network using Method B shall not add CO2 received from another installation permitted in accordance with Directive 2003/87/EC to its calculated level of emissions, and shall not subtract from its calculated level of emissions any CO2 transferred to another installation permitted in accordance with Directive 2003/87/EC.
Driftslederen bestemmer gennemsnitlige emissionsfaktorer EF (udtrykt i g CO2/tidsenhed) pr. forekomst, hvor fugitive emissioner kan forventes ved driftsstart og senest ved udgangen af det første rapporteringsår, hvor transportnettet er i drift.
Each operator of a transport network shall use Method A for the validation of the results of Method B at least once annually.
Driftslederen reviderer disse faktorer mindst hvert femte år under anvendelse af de bedste foreliggende teknikker og viden på området.
For that validation, the operator may use lower tiers for the application of Method A.
Driftslederen beregner de fugitive emissioner ved at multiplicere antallet af udstyrsdele i hver kategori med emissionsfaktoren og indregne resultaterne for de enkelte kategorier, som vist i ligningen nedenfor:
Method A
Antallet af forekomster (Nforekomst) angiver antallet af dele af det pågældende udstyr pr. kategori multipliceret med antallet af tidsenheder pr. år.
Each operator shall determine emissions in accordance with the following formula:
Emissioner fra udsivningsuheld
Emissions = Total CO2 emissions of the transport network [t CO2];
Driftslederen af transportnettet skal dokumentere nettets integritet ved hjælp af repræsentative (rum- og tidsrelaterede) temperatur- og trykdata.
E own activity = Emissions from the transport network's own activity, meaning not emissions stemming from the CO2 transported, but including emissions from fuel used in booster stations, monitored in accordance with the relevant sections of Annex IV;
Hvis dataene indikerer, at en udsivning har fundet sted, skal driftslederen beregne mængden af udsivet CO2 ved hjælp af en passende metode, som er dokumenteret i overvågningsplanen og baseret på industriens retningslinjer for bedste praksis, herunder ved at sammenholde forskellene i temperatur- og trykdata med de integritetsrelaterede gennemsnitlige tryk- og temperaturværdier.
T IN,i = Amount of CO2 transferred to the transport network at entry point i, determined in accordance with Articles 40 to 46 and Article 49.
Udluftningsemission
T OUT,i = Amount of CO2 transferred out of the transport network at exit point i, determined in accordance with Articles 40 to 46 and Article 49.
Hver driftsleder skal i overvågningsplanen fremlægge en analyse af potentielle situationer, hvor der kan forekomme emission i forbindelse med udluftning, herunder ved vedligeholdelse eller nødsituationer, samt en hensigtsmæssig og dokumenteret metode til beregning af mængden af udluftet CO2, som er baseret på industriens retningslinjer for bedste praksis.
Method B
GEOLOGISK LAGRING AF CO2 PÅ ET LAGRINGSANLÆG TILLADT I HENHOLD TIL DIREKTIV 2009/31/EF
Each operator shall determine emissions considering all processes relevant to emissions at the installation as well as the amount of CO2 captured and transferred to the transport facility using the following formula:
Den kompetente myndighed baserer afgrænsningen for overvågning og rapportering af emission fra geologisk lagring af CO2 på den afgrænsning af lagringsanlægget og lagringskomplekset, som er angivet i tilladelsen i henhold til direktiv 2009/31/EF.
CO 2 fugitive = Amount of fugitive emissions [t CO2] from CO2 transported in the transport network, including from seals, valves, intermediate compressor stations and intermediate storage facilities;
Hvis udsivninger fra lagringskomplekset konstateres, og disse fører til emission eller frigivelse af CO2 til vandsøjlen, gør driftslederen straks følgende:
CO 2 vented = Amount of vented emissions [t CO2] from CO2 transported in the transport network;
underretter den kompetente myndighed
CO 2 leakage events = Amount of CO2 [t CO2] transported in the transport network, which is emitted as the result of the failure of one or more components of the transport network;
inkluderer udsivningen som emissionskilde for det pågældende anlæg
CO 2 installations = Amount of CO2 [t CO2] being emitted from combustion or other processes functionally connected to the pipeline transport in the transport network, monitored in accordance with the relevant sections of Annex IV.
overvåger og rapporterer emissionerne.
Fugitive emissions from the transport network
Først når der er truffet udbedrende foranstaltninger i henhold til artikel 16 i direktiv 2009/31/EF, og når der ikke længere kan spores emission eller frigivelse til vandsøjlen fra den pågældende udsivning, sletter driftslederen den som emissionskilde i overvågningsplanen og indstiller overvågningen og rapporteringen af disse emissioner.
The operator shall consider fugitive emissions from any of the following types of equipment:
Driftslederen for et geologisk lagringsanlæg skal som minimum overveje følgende potentielle CO2-emissionskilder: brændselsanvendelse på tilknyttede boosterstationer og andre forbrændingsaktiviteter, herunder strømgeneratorer på anlægget, udluftning i forbindelse med injektionsaktiviteter eller ved forbedret kulbrinteindvinding, fugitive emissioner ved injektion, undsluppet CO2 i forbindelse med forbedret kulbrinteindvinding og udsivninger.
seals;
B. Kvantificering af CO2-emission
measurement devices;
Driftslederen for en geologisk lagringsaktivitet føjer ikke CO2 modtaget fra et andet anlæg til det beregnede emissionsniveau, og trækker ikke CO2, som lagres geologisk på lagringsanlægget, eller som overføres til et andet anlæg, fra det beregnede emissionsniveau.
valves;
Udluftningsemission og fugitiv emission fra injektion
intermediate compressor stations;
Driftslederen bestemmer emissioner fra udluftning og fugitive emissioner som følger:
intermediate storage facilities.
V CO 2 = mængde af udluftet CO2
The operator shall determine average emission factors EF (expressed in g CO2/unit time) per piece of equipment per occurrence where fugitive emissions can be anticipated at the beginning of operation, and by the end of the first reporting year in which the transport network is in operation at the latest.
F CO 2 = mængde af CO2 fra fugitive emissioner.
The operator shall review those factors at least every 5 years in the light of the best available techniques and knowledge.
Hver driftsleder bestemmer V CO2 ved hjælp af målingsbaserede metoder i henhold til artikel 41-46 i denne forordning.
The operator shall calculate fugitive emissions by multiplying the number of pieces of equipment in each category by the emission factor and adding up the results for the single categories as shown in the following equation:
Uanset det første punktum og efter godkendelse fra den kompetente myndighed kan driftslederen medtage en hensigtsmæssig metode i overvågningsplanen til bestemmelse af V CO2 baseret på industriens bedste praksis, hvis anvendelsen af målingsbaserede metoder vil føre til urimelige omkostninger.
The number of occurrences (Noccurr) shall be the number of pieces of the given equipment per category, multiplied by the number of time units per year.
Driftslederen betragter F CO2 som en kilde, hvilket betyder, at usikkerhedskravene i forbindelse med metodetrinene i overensstemmelse med afsnit 1 i bilag VIII finder anvendelse på den samlede værdi i stedet for på de enkelte emissionspunkter.
Emissions from leakage events
Hver driftsleder fremlægger i overvågningsplanen en analyse af potentielle kilder til fugitive emissioner samt en hensigtsmæssig og dokumenteret metode til beregning eller måling af mængden af F CO2, baseret på industriens retningslinjer for bedste praksis.
The operator of a transport network shall provide evidence of the network integrity by using representative (spatial and time-related) temperature and pressure data.
Til bestemmelse af F CO2 kan driftslederen anvende data, der er indsamlet i henhold til artikel 32-35 og bilag II, afsnit 1.1, litra e) til h), til direktiv 2009/31/EF i forbindelse med injektionsanlægget, for så vidt de opfylder kravene i denne forordning.
Where the data indicates that a leakage has occurred, the operator shall calculate the amount of CO2 leaked with a suitable methodology documented in the monitoring plan, based on industry best practice guidelines, including by use of the differences in temperature and pressure data compared to integrity related average pressure and temperature values.
Udluftningsemission og fugitive emissioner fra forbedret kulbrinteindvinding
Vented emissions
Hver driftsleder overvejer følgende potentielle yderligere emissionskilder fra forbedret kulbrinteindvinding:
Each operator shall provide in the monitoring plan an analysis regarding potential situations of venting emissions, including for maintenance or emergency reasons, and provide a suitable documented methodology for calculating the amount of CO2 vented, based on industry best practice guidelines.
olie-gas-separationsenheder og gasgenanvendelsesanlæg, hvor der vil kunne forekomme fugitive CO2-emissioner
GEOLOGICAL STORAGE OF CO2 IN A STORAGE SITE PERMITTED UNDER DIRECTIVE 2009/31/EC
flareskorstenen, hvor der kan forekomme emissioner pga. anvendelsen af kontinuerlige positive udluftningssystemer og under trykudligning af kulbrinteproduktionsanlægget
The competent authority shall base the boundaries for monitoring and reporting of emissions from geological storage of CO2 on the delimitation of the storage site and storage complex as specified in the permit pursuant to Directive 2009/31/EC.
CO2-udluftningssystemet, som skal undgå flareslukning pga. høje CO2-koncentrationer.
Where leakages from the storage complex are identified and lead to emissions or release of CO2 into the water column, the operator shall immediately carry out all of the following:
Hver driftsleder opgør fugitive emissioner eller udluftet CO2 i overensstemmelse med underafsnit B.1 i dette afsnit af bilag IV.
notify the competent authority;
Hver driftsleder bestemmer emissioner fra flareskorstenen i overensstemmelse med underafsnit D i afsnit 1 i dette bilag, idet der tages højde for potentielt indeholdt CO2 i flaregassen i henhold til artikel 48.
include the leakage as an emission source for the respective installation;
Udsivning fra lagringskomplekset
monitor and report the emissions.
Emission og frigivelser til vandsøjlen kvantificeres som følger:
Only when corrective measures in accordance with Article 16 of Directive 2009/31/EC have been taken and emissions or release into the water column from that leakage can no longer be detected shall the operator delete the respective leakage as emission source from the monitoring plan and no longer monitor and report those emissions.
L CO 2 = masse af udledt eller frigivet CO2 pr. kalenderdag på grund af udsivningen i henhold til nedenstående:
Each operator of a geological storage activity shall consider at least the following potential emission sources for CO2 overall: fuel use by associated booster stations and other combustion activities including on-site power plants; venting from injection or enhanced hydrocarbon recovery operations; fugitive emissions from injection; breakthrough CO2 from enhanced hydrocarbon recovery operations; and leakages.
for hvert kalenderår udsivningen overvåges, skal driftslederen beregne L CO2 som den gennemsnitlige udsivning pr. time [t CO2/h] multipliceret med 24
B. Quantification of CO2 emissions
driftslederen bestemmer massen af udsivningen pr. time i overensstemmelse med bestemmelserne i den godkendte overvågningsplan for lagringsanlægget og udsivningen
The operator of the geological storage activity shall not add CO2 received from another installation to its calculated level of emissions, and shall not subtract from its calculated level of emissions any CO2 which is geologically stored in the storage site or which is transferred to another installation.
for hver kalenderdag forud for overvågningens påbegyndelse sætter driftslederen den udsivede masse pr. dag lig med den udsivede daglige masse den første overvågningsdag og sikrer, at der ikke sker en undervurdering
Vented and fugitive emissions from injection
T start = den senest forekommende af følgende:
The operator shall determine emissions from venting and fugitive emissions as follows:
den seneste dato, hvor der ikke blev rapporteret emission eller frigivelse af CO2 til vandsøjlen fra den undersøgte kilde
V CO 2 = amount of CO2 vented;
den dato, hvor CO2-injektionen blev påbegyndt
F CO 2 = amount of CO2 from fugitive emissions.
en anden dato, hvor det over for den kompetente myndighed kan godtgøres, at emissionen eller frigivelsen til vandsøjlen ikke kan være startet før den dato.
Each operator shall determine V CO2 using measurement-based methodologies in accordance with Articles 41 to 46 of this Regulation.
T slut = den dato, hvor der er truffet udbedrende foranstaltninger i henhold til artikel 16 i direktiv 2009/31/EF, og hvor der ikke længere kan konstateres emission eller frigivelse af CO2 til vandsøjlen.
By way of derogation from the first sentence and upon approval by the competent authority, the operator may include in the monitoring plan an appropriate methodology for determining V CO2 based on industry best practice, where the application of measurement-based methodologies would incur unreasonable costs.
Den kompetente myndighed godkender og tillader anvendelsen af andre metoder til kvantificering af emission eller frigivelse af CO2 til vandsøjlen fra udsivninger, hvis driftslederen over for den kompetente myndighed kan dokumentere, at sådanne metoder fører til en højere grad af præcision end den beskrevne metode i dette underafsnit.
The operator shall consider F CO2 as one source, meaning that the uncertainty requirements associated with the tiers in accordance with section 1 of Annex VIII are applied to the total value instead of the individual emission points.
Driftslederen kvantificerer mængden af emissioner som følge af udsivning fra lagringskomplekset for hvert udsivningsuheld med en maksimal samlet usikkerhed i rapporteringsperioden på 7,5 %.
Each operator shall provide in the monitoring plan an analysis regarding potential sources of fugitive emissions, and provide a suitable documented methodology to calculate or measure the amount of F CO2, based on industry best practice guidelines.
Hvis den samlede usikkerhed for den anvendte kvantificeringsmetode overstiger 7,5 %, anvender hver driftsleder følgende tilpasning:
For the determination of F CO2 the operator may use data collected in accordance with Article 32 to 35 and Annex II(1.1)(e) to (h) of Directive 2009/31/EC for the injection facility, where they comply with the requirements of this Regulation.
CO2,rapporteret [t CO2] = CO2,kvantificeret [t CO2] * (1 + (UsikkerhedSystem [%]/100) – 0,075)
Vented and fugitive emissions from enhanced hydrocarbon recovery operations
CO 2,rapporteret = mængde CO2, der skal medtages i den årlige emissionsrapport, for så vidt angår det pågældende udsivningsuheld
Each operator shall consider the following potential additional emission sources from enhanced hydrocarbon recovery (EHR):
CO 2,kvantificeret = mængde CO2 bestemt gennem den anvendte kvantificeringsmetode for det pågældende udsivningsuheld,
the oil-gas separation units and gas recycling plant, where fugitive emissions of CO2 could occur;
Usikkerhed System = den grad af usikkerhed, der forbindes med kvantificeringsmetoden, som anvendes for det pågældende udsivningsuheld.
the flare stack, where emissions might occur due to the application of continuous positive purge systems and during depressurisation of the hydrocarbon production installation;
International Aluminium Institute; The Aluminium Sector Greenhouse Gas Protocol; October 2006; US Environmental Protection Agency and International Aluminium Institute; Protocol for Measurement of Tetrafluoromethane (CF4) and Hexafluoroethane (C2F6) Emissions from Primary Aluminum Production; April 2008.
the CO2 purge system, to avoid high concentrations of CO2 extinguishing the flare.
BILAG V
Each operator shall determine fugitive emissions or vented CO2 in accordance with subsection B.1 of this section of Annex IV.
Minimumskrav til metodetrin til beregningsbaserede fremgangsmåder i forbindelse med anlæg i kategori A og beregningsfaktorer for standardhandelsbrændsler, der anvendes af anlæg i kategori B og C (artikel 26, stk. 1)
Each operator shall determine emissions from the flare stack in accordance with subsection D of section 1 of this Annex, taking into account potential inherent CO2 in the flare gas in accordance with Article 48.
Minimumsmetodetrin, der skal anvendes ved beregningsbaserede metoder for anlæg i kategori A, og for så vidt angår beregningsfaktorer for standardhandelsbrændsel for alle anlæg i henhold til artikel 26, stk. 1, litra a)
Leakage from the storage complex
(»i.r.« betyder »ikke relevant«).
Emissions and release to the water column shall be quantified as follows:
Aktivitets-/kildestrømstype
L CO 2 = the mass of CO2 emitted or released per calendar day due to the leakage in accordance with all of the following:
Emissionsfaktor
for each calendar day for which leakage is monitored, each operator shall calculate L CO2 as the average of the mass leaked per hour [t CO2/h] multiplied by 24;
Kompositionsdata (kulstofindhold)
each operator shall determine the mass leaked per hour in accordance with the provisions in the approved monitoring plan for the storage site and the leakage;
Oxidations-faktor
for each calendar day prior to commencement of monitoring, the operator shall take the mass leaked per day to equal the mass leaked per day for the first day of monitoring ensuring no under-estimation occurs;
Omregnings-faktor
T start = the latest of:
Mængde af brændsel eller materiale
the last date when no emissions or release of CO2 into the water column from the source under consideration were reported;
Nedre brændværdi
the date the CO2 injection started;
Forbrænding af brændsler
another date such that there is evidence demonstrating to the satisfaction of the competent authority that the emission or release into the water column cannot have started before that date.
i.r.
T end = the date by which corrective measures in accordance with Article 16 of Directive 2009/31/EC have been taken and emissions or release of CO2 into the water column can no longer be detected.
Massebalancemetode for gasbehandlingsterminaler
The competent authority shall approve and allow the use of other methods for the quantification of emissions or release of CO2 into the water column from leakages where the operator can show to the satisfaction of the competent authority that such methods lead to a higher accuracy than the methodology set out in this subsection.
Afbrænding af gas uden nyttiggørelse
The operator shall quantify the amount of emissions leaked from the storage complex for each of the leakage events with a maximum overall uncertainty over the reporting period of 7,5 %.
Røggasvask (karbonat)
Where the overall uncertainty of the applied quantification methodology exceeds 7,5 %, each operator shall apply an adjustment, as follows:
Røggasvask (gips)
CO2,Reported [t CO2] = CO2,Quantified [t CO2] × (1 + (UncertaintySystem [%]/100) – 0,075)