natgillin/translations-raw huggingface dataset:
the implementation or adaption of a quantification methodology for emissions from leakage at storage sites.
izvajanje ali prilagoditev metodologije količinske opredelitve za emisije, ki uhajajo iz območij shranjevanja.
Significant changes to the monitoring plans of an aircraft operator shall include:
Med bistvene spremembe načrtov za spremljanje operaterja zrakoplova spadajo:
with regard to the emission monitoring plan:
v zvezi z načrtom za spremljanje emisij:
a change of tiers related to fuel consumption;
sprememba stopenj, povezanih s porabo goriva;
a change of emission factor values laid down in the monitoring plan;
sprememba vrednosti faktorjev emisije iz načrta za spremljanje;
a change between calculation methods as laid down in Annex III;
uporaba druge metode izračuna iz Priloge III;
a change in the categorisation of source streams where a minor source stream changes to a major source stream;
sprememba kategorizacije tokov vira, kadar se manjši tok vira spremeni v glavni tok vira;
changes in the status of the aircraft operator as a small emitter within the meaning of Article 54(1);
sprememba statusa operaterja zrakoplova kot malega onesnaževalca v smislu člena 54(1);
with regard to the tonne-kilometre data monitoring plan:
v zvezi z načrtom za spremljanje podatkov o tonskih kilometrih:
a change between a non-commercial and commercial status of the air transport service provided;
sprememba med nekomercialnim in komercialnim statusom zagotovljene storitve zračnega prometa;
a change in the object of the air-transport service, the object being passengers, freight or mail.
sprememba objekta storitve zračnega prometa, pri čemer so objekt potniki, tovor ali pošta.
Implementation and recordkeeping of modifications
Izvajanje in evidentiranje sprememb
Prior to receiving the approval or information in accordance with Article 15(2), the operator or aircraft operator may carry out monitoring and reporting using the modified monitoring plan where they can reasonably assume that the proposed modifications are not significant, or where monitoring in accordance with the original monitoring plan would lead to incomplete emission data.
Pred prejetjem odobritve ali informacij v skladu s členom 15(2) lahko upravljavec ali operater zrakoplova izvede spremljanje in poročanje z uporabo spremenjenega načrta za spremljanje, če lahko upravičeno sklepa, da predlagane spremembe niso bistvene, ali če bi se s spremljanjem v skladu s prvotnim načrtom za spremljanje pridobili nepopolni podatki o emisijah.
In case of doubt, the operator or aircraft operator shall carry out all monitoring and reporting, and in the interim documentation, in parallel, using both the modified and the original monitoring plan.
V primeru dvomov upravljavec ali operater zrakoplova izvede spremljanje in dokumentiranje v vmesni dokumentaciji hkrati z uporabo spremenjenega in prvotnega načrta za spremljanje.
Upon the receipt of the approval or information in accordance with Article 15(2), the operator or aircraft operator shall only use the data relating to the modified monitoring plan and carry out all monitoring and reporting using only the modified monitoring plan.
Upravljavec ali operater zrakoplova ob prejetju odobritve ali informacij v skladu s členom 15(2) uporabi le podatke v zvezi s spremenjenim načrtom za spremljanje ter izvede celotno spremljanje in poročanje le z uporabo spremenjenega načrta za spremljanje.
The operator or aircraft operator shall keep records of all modifications of the monitoring plan.
Upravljavec ali operater zrakoplova vodi evidenco vseh sprememb načrta za spremljanje.
In each record, the following shall be specified:
V vsaki evidenci se opredeli:
transparent description of the modification;
pregleden opis spremembe;
a justification for the modification;
utemeljitev spremembe;
the date of notification of the modification to the competent authority;
datum priglasitve spremembe pristojnemu organu;
the date of acknowledgement, by the competent authority, of the receipt of the notification referred to in Article 15(1), where available, and the date of the approval or information referred to in Article 15(2);
datum potrditve prejetja obvestila iz člena 15(1), če je na voljo, s strani pristojnega organa in datum odobritve ali informacij iz člena 15(2);
the starting date of implementation of the modified monitoring plan in accordance with paragraph 2 of this Article.
datum začetka izvajanja spremenjenega načrta za spremljanje v skladu z odstavkom 2 tega člena.
Technical feasibility and unreasonable costs
Tehnična izvedljivost in nerazumno visoki stroški
Technical feasibility
Tehnična izvedljivost
Where an operator or aircraft operator claims that applying a specific monitoring methodology is technically not feasible, the competent authority shall assess the technical feasibility taking the operator’s or aircraft operator’s justification into account.
Če upravljavec ali operater zrakoplova trdi, da uporaba določene metodologije spremljanja tehnično ni izvedljiva, pristojni organ oceni tehnično izvedljivost, pri čemer upošteva utemeljitev upravljavca ali operaterja zrakoplova.
That justification shall be based on the operator or aircraft operator having technical resources capable of meeting the needs of a proposed system or requirement that can be implemented in the required time for the purposes of this Regulation.
Ta utemeljitev temelji na tem, da ima upravljavec ali operater zrakoplova tehnične vire, ki lahko izpolnijo potrebe predlaganega sistema ali zahteve v zahtevanem času za namene te uredbe.
Those technical resources shall include availability of required techniques and technology.
Ti tehnični viri vključujejo razpoložljivost potrebnih tehnik in tehnologije.
Unreasonable costs
Nerazumno visoki stroški
Where an operator or aircraft operator claims that applying a specific monitoring methodology incurs unreasonable costs, the competent authority shall assess the unreasonable nature of the costs, taking into account the operator’s justification.
Če upravljavec ali operater zrakoplova trdi, da uporaba določene metodologije spremljanja povzroča nerazumno visoke stroške, pristojni organ oceni, kako nerazumno visoki so ti stroški, pri čemer upošteva utemeljitev upravljavca.
The competent authority shall consider costs unreasonable where the cost estimation exceeds the benefit.
Pristojni organ šteje stroške za nerazumno visoke, kadar so ocenjeni stroški višji od koristi.
To that end, the benefit shall be calculated by multiplying an improvement factor with a reference price of EUR 20 per allowance and costs shall include an appropriate depreciation period based on the economic lifetime of the equipment.
V ta namen se koristi izračunajo tako, da se faktor izboljšanja pomnoži z referenčno ceno 20 EUR na pravico, pri stroških pa se upošteva ustrezno obdobje amortizacije, ki temelji na ekonomski življenjski dobi opreme.
When assessing the unreasonable nature of the costs with regard to the choice of tier levels for activity data, the competent authority shall use as the improvement factor referred to in paragraph 1 the difference between the uncertainty currently achieved and the uncertainty threshold of the tier which would be achieved by the improvement multiplied by the average annual emissions caused by that source stream over the three most recent years.
Pri oceni nerazumno visokih stroškov pristojni organ, kar zadeva izbiro stopenj za podatke o dejavnosti, kot faktor izboljšanja iz odstavka 1 uporabi razliko med trenutno doseženo negotovostjo in pragom negotovosti za stopnjo, ki bi se dosegla z izboljšanjem, pomnoženim s povprečnimi letnimi emisijami tega toka vira v zadnjih treh letih.
In the absence of the average annual emissions caused by that source stream over the three most recent years, the operator or aircraft operator shall provide a conservative estimate of the annual average emissions, with the exclusion of CO2 stemming from biomass and before subtraction of transferred CO2.
Če povprečne letne emisije, ki jih povzroči ta tok vira v zadnjih treh letih, niso na voljo, upravljavec ali operater zrakoplova zagotovi konservativno oceno povprečnih letnih emisij, razen emisij CO2 iz biomase, in sicer pred odštetjem prenesenega CO2.
For measuring instruments under national legal metrological control, the uncertainty currently achieved may be substituted by the maximum permissible error in service allowed by the relevant national legislation.
Pri merilnih instrumentih, ki so predmet nacionalnega zakonsko urejenega meroslovnega nadzora, se lahko trenutna dosežena negotovost nadomesti z največjo dopustno napako med uporabo, ki je dovoljena v skladu z ustrezno nacionalno zakonodajo.
When assessing the unreasonable nature of the costs with regard to measures increasing the quality of reported emissions but without direct impact on the accuracy of activity data, the competent authority shall use an improvement factor of 1 % of the average annual emissions of the respective source streams of the three most recent reporting periods.
Pri oceni nerazumno visokih stroškov pristojni organ, kar zadeva ukrepe, ki izboljšujejo kakovost sporočenih emisij, vendar ne vplivajo neposredno na točnost podatkov o dejavnosti, uporabi faktor izboljšanja 1 % povprečnih letnih emisij zadevnih tokov virov v zadnjih treh letih.
Those measures may include:
Ti ukrepi lahko vključujejo:
a switch from default values to analyses for the determination of calculation factors;
prehod s privzetih vrednosti na analize za določanje faktorjev za izračun;
an increase of the number of analyses per source stream;
povečanje števila analiz na tok vira;
where the specific measuring task does not fall under national legal metrological control, the substitution of measuring instruments with instruments complying with relevant requirements of legal metrological control of the Member State in similar applications, or to measuring instruments meeting national rules adopted pursuant to Directive 2004/22/EC or Directive 2009/23/EC of the European Parliament and of the Council [10];
če posamezna naloga spremljanja ni predmet nacionalnega zakonsko urejenega meroslovnega nadzora, nadomestitev merilnih instrumentov z instrumenti, ki izpolnjujejo ustrezne zahteve zakonsko urejenega meroslovnega nadzora države članice pri podobnih vlogah, ali z merilnimi instrumenti, ki izpolnjujejo nacionalne predpise, sprejete v skladu z Direktivo 2004/22/ES ali Direktivo 2009/23/ES Evropskega parlamenta in Sveta [10];
shortening of calibration and maintenance intervals of measuring instruments;
skrajšanje intervalov kalibracije in vzdrževanja merilnih instrumentov;
improvements of data flow activities and control activities reducing the inherent or control risk significantly.
izboljšanje dejavnosti pretoka podatkov in nadzornih dejavnosti, s čimer se pomembno zmanjša tveganje pri delovanju ali nadzoru.
Measures relating to the improvement of an installation’s monitoring methodology in accordance with Article 69 shall not be deemed to incur unreasonable costs up to an accumulated amount of EUR 2000 per reporting period.
Za ukrepe v zvezi z izboljšanjem metodologije spremljanja za napravo se v skladu s členom 69 ne šteje, da povzročajo nerazumno visoke stroške, do skupnega zneska 2000 EUR na poročevalno obdobje.
For installations with low emissions that threshold shall be EUR 500 per reporting period.
Pri napravah z nizkimi emisijami je ta prag 500 EUR na poročevalno obdobje.
MONITORING OF EMISSIONS OF STATIONARY INSTALLATIONS
SPREMLJANJE EMISIJ NEPREMIČNIH NAPRAV
Categorisation of installations and source streams
Kategorizacija naprav in tokov vira
Each operator shall determine the category of its installation pursuant to paragraph 2, and, where relevant, of each source stream pursuant to paragraph 3 for the purpose of monitoring emissions and determining the minimum requirements for tiers.
Vsak upravljavec določi kategorijo naprave v skladu z odstavkom 2 in vsakega toka vira, če je to primerno, v skladu z odstavkom 3 za namene spremljanja emisij in določanja najmanjših zahtev za stopnje.
The operator shall classify each installation in one of the following categories:
Upravljavec razvrsti vsako napravo v eno od naslednjih kategorij:
a category A installation, where 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 equal to or less than 50000 tonnes of CO2(e);
naprava kategorije A, če so povprečne potrjene letne emisije v obdobju trgovanja tik pred sedanjim obdobjem trgovanja, razen CO2 iz biomase, in sicer pred odštetjem prenesenega CO2, enake ali nižje od 50000 ton CO2(e);
a category B 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 50000 tonnes of CO2(e) and equal to or less than 500000 tonnes of CO2(e);
naprava kategorije B, če so povprečne potrjene letne emisije v obdobju trgovanja tik pred sedanjim obdobjem trgovanja, razen CO2 iz biomase, in sicer pred odštetjem prenesenega CO2, višje od 50000 ton CO2(e) in enake ali nižje od 500000 ton CO2(e);
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).
naprava kategorije C, če so povprečne potrjene letne emisije v obdobju trgovanja tik pred sedanjim obdobjem trgovanja, razen CO2 iz biomase, in sicer pred odštetjem prenesenega CO2, višje od 500000 ton CO2(e).
The operator shall classify each source stream, comparing the source stream 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, in one of the following categories:
Upravljavec razvrsti posamezne tokove vira, pri čemer tok vira primerja z vsoto vseh absolutnih vrednosti fosilnega CO2 in CO2(e), ki ustrezajo vsem tokovom vira, vključenim v metodologije na podlagi izračunov, in vseh emisij virov emisij, ki se spremljajo z metodologijami na podlagi meritev, pred odštetjem prenesenega CO2, v eno od naslednjih kategorij:
minor source streams, where the source streams selected by the operator jointly correspond to less than 5000 tonnes of fossil CO2 per year or to less than 10 %, up to a total maximum contribution of 100000 tonnes of fossil CO2 per year, whichever is the highest in terms of absolute value;
manjši tokovi vira, ki pomenijo tokove vira, za katere upravljavec določi, da bodo skupaj izpustili manj kot 5000 ton fosilnega CO2 na leto ali prispevali manj kot 10 % do skupnega največjega prispevka 100000 ton fosilnega CO2 na leto, kar je višje glede na absolutno vrednost;
de-minimis source streams, where the source streams selected by the operator jointly correspond to less than 1000 tonnes of fossil CO2 per year or to less than 2 %, up to a total maximum contribution of 20000 tonnes of fossil CO2 per year, whichever is the highest in terms of absolute value;
tokovi vira de minimis, ki pomenijo tokove vira, za katere upravljavec določi, da bodo skupaj izpustili manj kot 1000 ton fosilnega CO2 na leto ali prispevali manj kot 2 % do skupnega največjega prispevka 20000 ton fosilnega CO2 na leto, kar je višje glede na absolutno vrednost;
major source streams, where the source streams do not classify in any category referred to in points (a) and (b).
glavni tokovi vira, če se tokovi vira ne razvrstijo v nobeno od kategorij iz točk (a) in (b).
Where the average annual verified emissions of the trading period immediately preceding the current trading period for the installation are not available or inaccurate, 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.
Če povprečne letne potrjene emisije v obdobju trgovanja tik pred sedanjim obdobjem trgovanja za napravo niso na voljo ali niso točne, upravljavec za določitev kategorije naprave uporabi konservativno oceno letnih povprečnih emisij, razen CO2 iz biomase, in sicer pred odštetjem prenesenega CO2.
Monitoring boundaries
Meje za spremljanje
An operator shall define the monitoring boundaries for each installation.
Upravljavec določi meje za spremljanje za vsako napravo.
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, as well as from activities and greenhouse gases included by a Member State pursuant to Article 24 of Directive 2003/87/EC.
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 skladu s členom 24 Direktive 2003/87/ES.
The operator shall also include emissions from regular operations and abnormal events including start-up and shut-down and emergency situations over the reporting period, with the exception of emissions from mobile machinery for transportation purposes.
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.
When defining the monitoring and reporting process, the operator shall include the sector specific requirements laid down in Annex IV.
Pri opredelitvi postopka spremljanja in poročanja upravljavec vključi zahteve, značilne za sektor, iz Priloge IV.
Where leakages from a storage complex pursuant to 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 respective installation and shall be monitored in accordance with section 23 of Annex IV to this Regulation.
Če je ugotovljeno uhajanje iz širšega prostora za shranjevanje v skladu z Direktivo 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.
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.
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 stolp zaradi uhajanja.
Choice of the monitoring methodology
Izbira metodologije spremljanja
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.
Za spremljanje emisij naprave upravljavec izbere uporabo metodologije na podlagi izračuna ali metodologije na podlagi meritev, in sicer glede na posebne določbe te uredbe.
A calculation-based methodology shall consist in determining emissions from source streams based on activity data obtained by means of measurement systems and additional parameters from laboratory analyses or default values.
Metodologijo na podlagi izračuna sestavlja določanje emisij iz tokov vira na podlagi podatkov o dejavnosti, pridobljenih s sistemi za merjenje in dodatnimi parametri iz laboratorijskih analiz ali privzetimi vrednostmi.
The calculation-based methodology may be implemented through the standard methodology set out in Article 24 or the mass balance methodology set out in Article 25.
Metodologija na podlagi izračuna se lahko izvaja s standardno metodologijo iz člena 24 ali metodologijo masne bilance iz člena 25.
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.
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.
Where the calculation-based methodology is applied, the operator shall for each source stream define, in the monitoring plan, whether the standard methodology or the mass balance methodology is used, including the relevant tiers in accordance with Annex II.
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.
An operator may combine, subject to approval by the competent authority, 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.
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 nastanejo vrzeli ali dvojno štetje.
Where the operator does not choose a measurement-based methodology, the operator shall choose the methodology required by the relevant section of Annex IV, unless he provides evidence to the competent authorities that the use of such methodology is technically not feasible or incurs unreasonable costs, or that another methodology leads to a higher overall accuracy of emissions data.
Če upravljavec ne izbere metodologije na podlagi meritev, izbere metodologijo, ki se zahteva v skladu z ustreznim oddelkom Priloge IV, razen če pristojnim organom dokaže, da uporaba takšne metodologije tehnično ni izvedljiva ali bi povzročila nerazumno visoke stroške ali da bi druga metodologija pomenila večjo splošno točnost podatkov o emisijah.
Monitoring methodology not based on tiers
Metodologija spremljanja, ki ne temelji na stopnjah
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:
Ne glede na člen 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:
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;
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;