natgillin/translations-raw huggingface dataset:
a category C installation, where the average verified annual emissions of the trading period immediately preceding the current trading period, with the exclusion of CO2 stemming from biomass and before subtraction of transferred CO2, are more than 500000 tonnes of CO2(e).
tokovi vira de minimis, če tokovi vira, ki jih izbere upravljavec, skupaj prispevajo manj kot 1000 ton fosilnega CO2 na leto ali prispevali manj kot 2 % do skupnega največjega prispevka 20000 ton fosilnega CO2 na leto, kar koli je višje glede na absolutno vrednost;
By way of derogation from Article 14(2), the competent authority may allow the operator not to modify the monitoring plan where, on the basis of verified emissions, the threshold for the classification of the installation referred to in the first subparagraph is exceeded, but the operator demonstrates to the satisfaction of the competent authority that this threshold has not already been exceeded within the past five reporting periods and will not be exceeded again in subsequent reporting periods.
glavni tokovi vira, če se tokovi vira ne razvrstijo v nobeno od kategorij iz točk (a) in (b).
The operator shall classify each source stream in one of the following categories, comparing it against the sum of all absolute values of fossil CO2 and CO2(e) corresponding to all source streams included in calculation-based methodologies and of all emissions of emission sources monitored using measurement-based methodologies, before subtraction of transferred CO2:
Z odstopanjem od člena 14(2) lahko pristojni organ upravljavcu dovoli, da ne spremeni načrta za spremljanje, če je na podlagi preverjenih emisij prag za razvrstitev toka vira kot manjšega toka vira ali toka vira de minimis iz prvega pododstavka sicer presežen, vendar upravljavec pristojnemu organu dokaže, da ta prag v zadnjih petih poročevalnih obdobjih še ni bil presežen in da v naslednjih poročevalnih obdobjih ne bo več presežen.
minor source streams, where the source streams selected by the operator jointly account for less than 5000 tonnes of fossil CO2 per year or less than 10 %, up to a total maximum of 100000 tonnes of fossil CO2 per year, whichever is greater in terms of absolute value;
Upravljavec vsak vir emisij, za katerega se uporablja metodologija na podlagi meritev, razvrsti v eno od naslednjih kategorij:
de minimis source streams, where the source streams selected by the operator jointly account for less than 1000 tonnes of fossil CO2 per year or less than 2 %, up to a total maximum of 20000 tonnes of fossil CO2 per year, whichever is greater in terms of absolute value;
manjši viri emisij, pri katerih vir emisij izpusti manj kot 5000 ton fosilnega CO2(e) na leto ali prispeva manj kot 10 % do skupnega največjega prispevka naprave 100000 ton fosilnega CO2(e) na leto, kar koli je višje glede na absolutno vrednost;
major source streams, where the source streams do not fall within the categories referred to in points (a) and (b).
večji viri emisij, pri katerih se vir emisij ne razvrsti kot manjši vir emisij.
By way of derogation from Article 14(2), the competent authority may allow the operator not to modify the monitoring plan where, on the basis of verified emissions, the threshold for the classification of a source stream as a minor source stream or a de minimis source stream referred to in the first subparagraph is exceeded, but the operator demonstrates to the satisfaction of the competent authority that this threshold has not already been exceeded within the past five reporting periods and will not be exceeded again in subsequent reporting periods.
Z odstopanjem od člena 14(2) lahko pristojni organ upravljavcu dovoli, da ne spremeni načrta za spremljanje, če je na podlagi preverjenih emisij prag za razvrstitev vira emisij kot manjšega vira emisij iz prvega pododstavka sicer presežen, vendar upravljavec pristojnemu organu dokaže, da ta prag v zadnjih petih poročevalnih obdobjih še ni bil presežen in da v naslednjih poročevalnih obdobjih ne bo več presežen.
The operator shall classify each emission source for which a measurement-based methodology is applied in one of the following categories:
Če povprečne letne potrjene emisije v obdobju trgovanja tik pred sedanjim obdobjem trgovanja za napravo niso na voljo ali niso več reprezentativne za namene odstavka 2, upravljavec za določitev kategorije naprave uporabi konservativno oceno letnih povprečnih emisij, razen CO2 iz biomase, in sicer pred odštetjem prenesenega CO2.
minor emission sources, where the emission source emits less than 5000 tonnes of fossil CO2(e) per year or less than 10 % of the installation's total fossil emissions, up to a maximum of 100000 tonnes of fossil CO2(e) per year, whichever is greater in terms of absolute value;
Člen 20
major emission sources, where the emission source does not classify as a minor emission source.
Meje za spremljanje
By way of derogation from Article 14(2), the competent authority may allow the operator not to modify the monitoring plan where, on the basis of verified emissions, the threshold for the classification of an emission source as a minor emission source referred to in the first subparagraph is exceeded, but the operator demonstrates to the satisfaction of the competent authority that this threshold has not already been exceeded within the past five reporting periods and will not be exceeded again in subsequent reporting periods.
Upravljavec določi meje za spremljanje za vsako napravo.
Where the average annual verified emissions in the trading period immediately preceding the current trading period for the installation are not available or no longer representative for the purpose of paragraph 2, the operator shall use a conservative estimate of annual average emissions, with the exclusion of CO2 stemming from biomass and before subtraction of transferred CO2, to determine the category of the installation.
Znotraj teh meja upravljavec vključi vse ustrezne emisije toplogrednih plinov iz vseh virov emisij in tokov virov, ki spadajo pod dejavnosti, ki se izvajajo v napravi in so navedene v Prilogi I k Direktivi 2003/87/ES, ter dejavnosti in toplogredne pline, ki jih vključi država članica, v kateri se naprava nahaja, v skladu s členom 24 navedene direktive.
Article 20
Upravljavec vključi tudi emisije iz rednega delovanja in nenormalnih dogodkov, vključno z zagonom in zaustavitvijo ter izrednimi razmerami v poročevalnem obdobju, razen emisij iz premičnih strojev, namenjenih za prevoz.
Monitoring boundaries
Pri določitvi postopka spremljanja in poročanja upravljavec vključi sektorske zahteve iz Priloge IV.
Operators shall define the monitoring boundaries for each installation.
Če je ugotovljeno uhajanje iz širšega prostora za shranjevanje v smislu Direktive 2009/31/ES, ki povzroča emisije ali izpust CO2 v vodni steber, se to šteje kot vir emisij za zadevno napravo in spremlja v skladu z oddelkom 23 Priloge IV k tej uredbi.
Within those boundaries, the operator shall include all relevant greenhouse gas emissions from all emission sources and source streams belonging to activities carried out at the installation and listed in Annex I to Directive 2003/87/EC, and from activities and greenhouse gases included by the Member State in which the installation is situated, pursuant to Article 24 of that Directive.
Z odobritvijo pristojnega organa se lahko vir emisij v obliki uhajanja izključi iz postopka spremljanja in poročanja, po tem, ko so v skladu s členom 16 Direktive 2009/31/ES izvedeni popravni ukrepi ter ni več mogoče ugotoviti emisij ali izpusta v vodni steber zaradi uhajanja.
The operator shall also include emissions from regular operations and abnormal events, including start-up, shut-down and emergency situations, over the reporting period, with the exception of emissions from mobile machinery for transportation purposes.
Člen 21
When determining the monitoring and reporting process, the operator shall include the sector-specific requirements laid down in Annex IV.
Izbira metodologije spremljanja
Where leakages from a storage complex within the meaning of Directive 2009/31/EC are identified and lead to emissions or release of CO2 to the water column, they shall be considered as emission sources for the installation in question and shall be monitored in accordance with section 23 of Annex IV to this Regulation.
Za spremljanje emisij naprave upravljavec izbere uporabo metodologije na podlagi izračuna ali metodologije na podlagi meritev, in sicer glede na posebne določbe te uredbe.
The competent authority may allow the exclusion of a leakage emission source from the monitoring and reporting process, once corrective measures pursuant to 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.
Metodologijo na podlagi izračuna sestavlja določanje emisij iz tokov vira na podlagi podatkov o dejavnosti, pridobljenih z merilnimi sistemi in dodatnimi parametri iz laboratorijskih analiz ali privzetimi vrednostmi.
Article 21
Metodologija na podlagi izračuna se lahko izvaja po standardni metodologiji iz člena 24 ali metodologiji masne bilance iz člena 25.
Choice of the monitoring methodology
Metodologijo na podlagi meritev sestavlja določanje emisij iz virov emisij z neprekinjenim merjenjem koncentracije ustreznega toplogrednega plina v dimnem plinu in v pretoku dimnega plina, vključno s spremljanjem prenosov CO2 med napravami, kadar se merita koncentracija CO2 in pretok prenesenega plina.
For the monitoring of the emissions of an installation, the operator shall choose to apply either a calculation-based methodology or a measurement-based methodology, subject to specific provisions of this Regulation.
Kadar se uporabi metodologija na podlagi izračuna, upravljavec za vsak tok vira v načrtu za spremljanje določi, ali se uporabi standardna metodologija ali metodologija masne bilance, vključno z ustreznimi stopnjami v skladu s Prilogo II.
A calculation-based methodology shall consist in determining emissions from source streams on the basis of activity data obtained by means of measurement systems and additional parameters from laboratory analyses or default values.
Upravljavec lahko z dovoljenjem pristojnega organa združi standardno metodologijo, metodologijo masne bilance in metodologijo na podlagi meritev za različne vire emisij in tokove vira, ki pripadajo eni napravi, če pri tem v zvezi z emisijami ne pride do vrzeli ali dvojnega štetja.
The calculation-based methodology may be implemented according to the standard methodology set out in Article 24 or the mass-balance methodology set out in Article 25.
Če je zaradi sektorskih zahtev iz Priloge IV potrebna uporaba posebne metodologije spremljanja, upravljavec uporabi to metodologijo ali metodologijo na podlagi meritev.
A measurement-based methodology shall consist in determining emissions from emission sources by means of continuous measurement of the concentration of the relevant greenhouse gas in the flue gas and of the flue-gas flow, including the monitoring of CO2 transfers between installations where the CO2 concentration and the flow of the transferred gas are measured.
Upravljavec lahko izbere drugačno metodologijo le, če pristojnemu organu dokaže, da uporaba takšne metodologije tehnično ni izvedljiva ali bi povzročila nerazumno visoke stroške ali da bi druga metodologija omogočila večjo splošno točnost podatkov o emisijah.
Where the calculation-based methodology is applied, the operator shall determine for each source stream, in the monitoring plan, whether the standard methodology or the mass-balance methodology is used, including the relevant tiers in accordance with Annex II.
Člen 22
Subject to approval by the competent authority, the operator may combine standard methodology, mass-balance and measurement-based methodologies for different emission sources and source streams belonging to one installation, provided that neither gaps nor double counting concerning emissions occur.
Metodologija spremljanja, ki ne temelji na stopnjah
Where sector-specific requirements laid down in Annex IV require the use of a specific monitoring methodology, the operator shall use that methodology or a measurement-based methodology.
Z odstopanjem od člena 21(1) lahko upravljavec uporabi metodologijo spremljanja, ki ne temelji na stopnjah (v nadaljnjem besedilu: nadomestna metodologija) za izbrane tokove vira ali vire emisij, če so izpolnjeni vsi naslednji pogoji:
The operator may choose a different methodology only if it provides the competent authority with evidence that the use of the required methodology is technically not feasible or incurs unreasonable costs, or that the alternative methodology leads to a higher overall accuracy of emissions data.
uporaba vsaj stopnje 1 po metodologiji na podlagi izračunov za enega ali več glavnih tokov vira ali manjših tokov vira in metodologije na podlagi meritev za vsaj en vir emisij, povezan z istimi tokovi vira, tehnično ni izvedljiva ali bi povzročila nerazumno visoke stroške;
Article 22
upravljavec vsako leto oceni in količinsko opredeli negotovost vseh parametrov, ki se uporabljajo za določanje letnih emisij v skladu s standardom ISO – Navodila za izražanje negotovosti pri merjenju (JCGM 100:2008) ali drugim enakovrednim mednarodno sprejetim standardom, in rezultate vključi v letno poročilo o emisijah;
Monitoring methodology not based on tiers
upravljavec pristojnemu organu dokaže, da z uporabo takšne nadomestne metodologije spremljanja splošni pragovi negotovosti za letno raven emisij toplogrednih plinov za celotno napravo ne presegajo 7,5 % za naprave kategorije A, 5,0 % za naprave kategorije B in 2,5 % za naprave kategorije C.
By way of derogation from Article 21(1), the operator may use a monitoring methodology that is not based on tiers (hereinafter ‘the fall-back methodology’) for selected source streams or emission sources, provided that all of the following conditions are met:
Člen 23
applying at least tier 1 under the calculation-based methodology for one or more major source streams or minor source streams and a measurement-based methodology for at least one emission source related to the same source streams is technically not feasible or would incur unreasonable costs;
Začasne spremembe metodologije spremljanja
the operator assesses and quantifies each year the uncertainties of all parameters used for the determination of the annual emissions in accordance with the ISO guide to the expression of uncertainty in measurement (JCGM 100:2008) or another equivalent internationally accepted standard, and includes the results in the annual emissions report;
Če iz tehničnih razlogov začasno ni mogoče uporabiti stopnje iz načrta za spremljanje, kot ga je odobril pristojni organ, zadevni upravljavec uporabi najvišjo dosegljivo stopnjo ali, če ni mogoče uporabiti stopnje, konservativen pristop brez stopenj, dokler se ponovno ne vzpostavijo pogoji za uporabo stopnje, ki je bila odobrena v načrtu za spremljanje.
the operator demonstrates to the satisfaction of the competent authority that by applying such a fall-back monitoring methodology, the overall uncertainty thresholds for the annual level of greenhouse gas emissions for the whole installation do not exceed 7,5 % for category A installations, 5,0 % for category B installations and 2,5 % for category C installations.
Upravljavec sprejme vse potrebne ukrepe, da omogoči takojšnje nadaljnje izvajanje načrta za spremljanje, ki ga je odobril pristojni organ.
Article 23
Zadevni upravljavec brez nepotrebnega odlašanja obvesti pristojni organ o začasni spremembi metodologije spremljanja iz odstavka 1, pri čemer navede:
Temporary changes to the monitoring methodology
razloge za odstopanje od načrta za spremljanje, kot ga je odobril pristojni organ;
Where it is for technical reasons temporarily not feasible to apply the monitoring plan as approved by the competent authority, the operator concerned shall apply the highest achievable tier, or a conservative no-tier approach if application of a tier is not achievable, until the conditions for application of the tier approved in the monitoring plan have been restored.
podrobnosti vmesne metodologije spremljanja, ki jo uporablja upravljavec za določanje emisij, dokler se ponovno ne vzpostavijo pogoji za uporabo načrta za spremljanje, kot ga je odobril pristojni organ;
The operator shall take all necessary measures to allow the prompt resumption of the application of the monitoring plan as approved by the competent authority.
ukrepe, ki jih sprejme upravljavec za ponovno vzpostavitev pogojev za uporabo načrta za spremljanje, kot ga je odobril pristojni organ;
The operator concerned shall notify the competent authority of the temporary change referred to in paragraph 1 to the monitoring methodology without undue delay to the competent authority, specifying:
predviden čas ponovnega začetka uporabe načrta za spremljanje, kot ga je odobril pristojni organ.
the reasons for deviating from the monitoring plan as approved by the competent authority;
Metodologija na podlagi izračuna
the details of the interim monitoring methodology that the operator is using to determine the emissions until the conditions for the application of the monitoring plan as approved by the competent authority have been restored;
Pododdelek 1
the measures the operator is taking to restore the conditions for the application of the monitoring plan as approved by the competent authority;
Splošno
the anticipated point in time when application of the monitoring plan as approved by the competent authority will be resumed.
Člen 24
Calculation-based methodology
Izračun emisij po standardni metodologiji
Subsection 1
Po standardni metodologiji upravljavec izračuna emisije iz izgorevanja goriv za posamezni tok vira tako, da podatke o dejavnosti, povezane s količino goriva, ki izgori, izražene v terajoulih na podlagi neto kalorične vrednosti (NKV), pomnoži z ustreznim faktorjem emisije, izraženim v tonah CO2 na terajoule (t CO2/TJ) skladno z uporabo NKV, in z ustreznim faktorjem oksidacije.
General
Pristojni organ lahko dovoli uporabo faktorjev emisije za goriva, izraženih v t CO2/t ali t CO2/Nm3.
Article 24
V takih primerih upravljavec določi emisije iz izgorevanja goriv tako, da podatke o dejavnosti, povezane s količino goriva, ki izgori, izražene v tonah ali normalnih kubičnih metrih, pomnoži z ustreznim faktorjem emisije in ustreznim faktorjem oksidacije.
Calculation of emissions under the standard methodology
Upravljavec emisije iz proizvodnih procesov za posamezni tok vira določi tako, da podatke o dejavnosti, povezane s porabo materiala, pretokom ali obsegom proizvodnje, izražene v tonah ali normalnih kubičnih metrih, pomnoži z ustreznim faktorjem emisije, izraženim v t CO2/t ali t CO2/Nm3, ter ustreznim faktorjem pretvorbe.
Under the standard methodology, the operator shall calculate combustion emissions source stream by multiplying the activity data related to the amount of fuel combusted, expressed as terajoules based on net calorific value (NCV), by the corresponding emission factor, expressed as tonnes of CO2 per terajoule (t CO2/TJ) consistent with the use of NCV, and the corresponding oxidation factor.
Kadar faktor emisije stopnje 1 ali 2 že vključuje učinek nedokončanih kemijskih reakcij, se faktor oksidacije ali faktor pretvorbe nastavi na 1.
The competent authority may allow the use of emission factors for fuels expressed as t CO2/t or t CO2/Nm3.
Člen 25
In such cases, the operator shall determine combustion emissions by multiplying the activity data related to the amount of fuel combusted, expressed as tonnes or normal cubic metres, by the corresponding emission factor and the corresponding oxidation factor.
Izračun emisij po metodologiji masne bilance
The operator shall determine process emissions per source stream by multiplying the activity data related to the material consumption, throughput or production output, expressed in tonnes or normal cubic metres, by the corresponding emission factor, expressed in t CO2/t or t CO2/Nm3, and the corresponding conversion factor.
Upravljavec z uporabo metodologije masne bilance izračuna količino CO2, ki ustreza vsakemu toku vira, vključenemu v masno bilanco, tako, da pomnoži podatke o dejavnosti, povezane s količino goriva ali materiala, ki vstopa v meje masne bilance ali izstopa iz njih, z vsebnostjo ogljika v gorivu ali materialu, ki se pomnoži s 3,664 t CO2/t C, pri čemer se uporabi oddelek 3 Priloge II.
Where a tier 1 or tier 2 emission factor already includes the effect of incomplete chemical reactions, the oxidation factor or conversion factor shall be set to 1.
Ne glede na člen 49 so emisije skupnega procesa, ki jih vključuje masna bilanca, vsota količin CO2, ki ustrezajo vsem tokovom vira, ki jih vključuje masna bilanca.
Article 25
CO, sproščen v ozračje, se izračuna v masni bilanci kot emisija molarne enakovredne količine CO2.
Calculation of emissions under the mass balance methodology
Člen 26
Under the mass balance methodology, the operator shall calculate the quantity of CO2 corresponding to each source stream included in the mass balance by multiplying the activity data related to the amount of fuel or material entering or leaving the boundaries of the mass balance, with the fuel's or material's carbon content multiplied by 3,664 t CO2/t C, applying section 3 of Annex II.
Veljavne stopnje
Notwithstanding Article 49, the emissions of the total process covered by the mass balance shall be the sum of the CO2 quantities corresponding to all source streams covered by the mass balance.
Vsak upravljavec pri določanju ustreznih stopenj za glavne in manjše tokove vira v skladu s členom 21(1), da določi podatke o dejavnosti in vse faktorje za izračun, uporabi:
CO emitted to the atmosphere shall be calculated in the mass balance as emission of the molar equivalent amount of CO2.
najmanj stopnje iz Priloge V, če gre za napravo kategorije A ali če se zahteva faktor za izračun za tok vira, ki je komercialno standardno gorivo;
Article 26
v primerih, ki niso primeri iz točke (a), najvišjo stopnjo iz Priloge II.
Applicable tiers
Vseeno lahko upravljavec pri glavnih tokovih vira za naprave kategorije C uporabi stopnjo, ki je eno raven nižja od stopenj, zahtevanih v skladu s prvim pododstavkom, za naprave kategorij A in B pa stopnjo, ki je do dve ravni nižja, pri čemer uporabi vsaj stopnjo 1, če pristojnemu organu dokaže, da stopnja, zahtevana v skladu s prvim pododstavkom, tehnično ni izvedljiva ali bi povzročila nerazumno visoke stroške.
When defining the relevant tiers for major and minor source streams in accordance with Article 21(1), to determine the activity data and each calculation factor, each operator shall apply the following:
Pristojni organ lahko v prehodnem obdobju, za katerega se dogovori z upravljavcem, upravljavcu za glavne tokove vira odobri stopnje, ki so nižje od tistih iz drugega pododstavka, pri čemer uporabi vsaj stopnjo 1, pod pogojem, da:
at least the tiers listed in Annex V, in the case of a category A installation, or where a calculation factor is required for a source stream that is a commercial standard fuel;
upravljavec pristojnemu organu dokaže, da stopnja, zahtevana v skladu z drugim pododstavkom, tehnično ni izvedljiva ali bi povzročila nerazumno visoke stroške; ter
in other cases than those referred to in point (a), the highest tier as defined in Annex II.
upravljavec predloži načrt za izboljšanje, v katerem je navedeno, kako in kdaj bo dosežena vsaj stopnja, zahtevana v skladu z drugim pododstavkom.
However, for major source streams the operator may apply a tier one level lower than required in accordance with the first subparagraph for category C installations and up to two levels lower for category A and B installations, with a minimum of tier 1, where it shows to the satisfaction of the competent authority that the tier required in accordance with the first subparagraph is technically not feasible or incurs unreasonable costs.
Za manjše tokove vira lahko upravljavec uporabi stopnjo, ki je nižja od stopenj, zahtevanih v skladu s prvim pododstavkom odstavka 1, pri čemer uporabi najmanj stopnjo 1, če pristojnemu organu dokaže, da stopnja, zahtevana v skladu s prvim pododstavkom odstavka 1, tehnično ni izvedljiva ali bi povzročila nerazumno visoke stroške.