natgillin/translations-raw huggingface dataset:
For the reporting period 2008–12 as a minimum Tier 2 shall be applied unless technically not feasible.
V poročevalnem obdobju 2008–2012 se uporablja vsaj stopnja 2, razen če tehnično ni izvedljiva.
In cases for which it is technically not feasible or would lead to unreasonable costs to apply at least Tier 1 requirements for each emission source (except de minimis sources), the operator shall apply and demonstrate compliance with the appropriate tier for the total annual emission for the emission source as in Section 2, Annex XII.
V primerih, ko uporaba vsaj stopnje 1 za vsak vir emisije (razen virov de minimis) tehnično ni izvedljiva ali bi povzročila nerazumno visoke stroške, upravljavec v skladu z oddelkom 2 Priloge XII uporabi ustrezno stopnjo za skupne letne emisije vira emisije in dokaže skladnost z njo.
For the reporting period 2008–12 the minimum requirement is Tier 2, unless technically not feasible.
Za poročevalno obdobje 2008–2012 se zahteva vsaj stopnja 2, razen če tehnično ni izvedljiva.
Respective installations applying this approach are to be notified by Member States to the Commission pursuant to Article 21 of Directive 2003/87/EC.
Države članice v skladu s členom 21 Direktive 2003/87/ES Komisijo obvestijo o zadevnih napravah, ki uporabljajo ta pristop.
For each emission source a total uncertainty of annual average hourly emissions of less than ± 10 % shall be achieved.
Za vsak vir emisije znaša skupna negotovost letnih povprečnih urnih emisij manj kot ± 10 %.
For each emission source a total uncertainty of annual average hourly emissions of less than ± 7,5 % shall be achieved.
Za vsak vir emisije znaša skupna negotovost letnih povprečnih urnih emisij manj kot ± 7,5 %.
For each emission source a total uncertainty of annual average hourly emissions of less than ± 5 % shall be achieved.
Za vsak vir emisije znaša skupna negotovost letnih povprečnih urnih emisij manj kot ± 5 %.
HOURLY N2O CONCENTRATIONS
URNE KONCENTRACIJE N2O
Hourly N2O concentrations [mg/Nm3] in the flue gas from each emission source shall be determined by continuous measurement at a representative point, after the NOx/N2O abatement equipment (if abatement is used).
Urne koncentracije N2O [mg/Nm3] v dimnem plinu iz vsakega vira emisije se določijo z neprekinjenim merjenjem na reprezentativni točki po izhodu iz opreme za zmanjševanje emisij NOx/N2O (kadar se ta uporablja).
Suitable measuring techniques include IR Spectroscopy, but others can be used in accordance with paragraph 2 of Section 6.1 of Annex I, provided they achieve the required uncertainty level for the N2O emissions.
Primerna merilna tehnika je IR-spektroskopija, vendar se lahko v skladu z odstavkom 2 oddelka 6.1 Priloge I uporabijo tudi druge tehnike, če dosegajo zahtevano raven negotovosti za emisije N2O.
The used techniques must be capable of measuring N2O concentrations of all emission sources during both abated and unabated conditions (for example during periods when abatement equipment fails and concentrations increase).
Z uporabljenimi tehnikami mora biti mogoče izmeriti koncentracije N2O iz vseh virov emisij, in sicer tedaj, ko se uporabljajo naprave za njihovo zmanjševanje, pa tudi tedaj, ko emisije ostajajo nezmanjšane (na primer ob izpadu opreme za zmanjševanje emisij in povečanju koncentracij).
If uncertainties increase during such periods, these must be taken into account in the uncertainty assessment.
Če se med takšnimi obdobji negotovost poveča, je to treba upoštevati v oceni negotovosti.
All measurements shall be adjusted to a dry gas basis and be reported consistently.
Vse meritve so prilagojene glede na suhi plin in se dosledno sporočajo.
DETERMINATION OF FLUE GAS FLOW
DOLOČANJE PRETOKA DIMNEGA PLINA
The methods for monitoring flue gas flow set out in Annex XII shall be used for measuring flue gas flow for N2O emissions monitoring.
Pri spremljanju emisij N2O se za merjenje pretoka dimnega plina uporabljajo metode spremljanja pretoka dimnega plina, ki so določene v Prilogi XII.
For nitric acid production, Method A shall be applied unless it is not technically feasible, in which case an alternative method, such as a mass balance approach based on significant parameters (such as ammonia input load) or determination of flow by continuous emissions flow measurement, can be used provided it is approved by the competent authority as part of the evaluation of the monitoring plan and the monitoring methodology therein.
Pri proizvodnji dušikove kisline se uporablja metoda A, razen če to tehnično ni izvedljivo in se namesto nje uporabi nadomestna metoda, npr. pristop z masno bilanco, ki temelji na pomembnih parametrih (kot je vnos amoniaka), ali določanje pretoka z neprekinjenim merjenjem pretoka emisij, vendar le v primeru, da jo ob oceni načrta za spremljanje in njegove metodologije spremljanja potrdi pristojni organ.
For other activities, other methods for monitoring flue gas flow described in Annex XII can be used, provided they are approved by the competent authority as part of the evaluation of the monitoring plan and the monitoring methodology therein.
Pri drugih dejavnostih se lahko za spremljanje pretoka dimnega plina uporabljajo druge metode, opisane v Prilogi XII, če jih odobri pristojni organ kot del ocene načrta za spremljanje in njene metodologije spremljanja.
Method A — nitric acid production
Metoda A – proizvodnja dušikove kisline
The flue gas flow shall be calculated in accordance with the following formula:
Pretok dimnega plina se izračuna z naslednjo enačbo:
Vflue gas flow
Vpretok dimnega plina
= Vair
= Vzrak
V air
V zrak
total input air flow in Nm3/h at standard conditions;
skupni vnos pretoka zraka v Nm3/h pri standardnih pogojih
O 2 air
O 2 zrak
volume fraction of O2 in dry air [= 0,2095];
prostorninski delež O2 v suhem zraku [= 0,2095]
O 2 flue gas
O 2 dimni plin
volume fraction of O2 in flue gas.
prostorninski delež O2 v dimnem plinu
The Vair shall be calculated as the sum of all air flows entering the nitric acid production unit.
Vzrak se izračuna kot vsota celotnega pretoka zraka, ki se dovaja proizvodni enoti za dušikovo kislino.
The installation shall apply the following formula, unless stated otherwise in its monitoring plan:
Če v svojem načrtu za spremljanje ne navede drugače, uporablja naprava naslednjo enačbo:
Vair = Vprim + Vsec + Vseal
Vzrak = Vprim + Vsek + Vzap
Primary input air flow in Nm3/h at standard conditions;
primarni vnos pretoka zraka v Nm3/h pri standardnih pogojih
Secondary input air flow in Nm3/h at standard conditions;
sekundarni vnos pretoka zraka v Nm3/h pri standardnih pogojih
V seal
V zap
Seal input air flow in Nm3/h at standard conditions.
zaporni vnos pretoka zraka v Nm3/h pri standardnih pogojih
The Vprim is determined by continuous flow measurement before the mixing with ammonia takes place.
Vprim se določi z neprekinjenim merjenjem pretoka, preden se zrak pomeša z amoniakom.
The Vsec is determined by continuous flow measurement e.g. before the heat recovery unit.
Vsek se določi z neprekinjenim merjenjem pretoka, npr. pred enoto za rekuperacijo toplote.
The Vseal is the purged airflow within the nitric acid production process (if relevant).
Vzap je prečiščeni zračni pretok v postopku proizvodnje dušikove kisline (po potrebi).
For input air streams accounting for cumulatively less than 2,5 % of the total air flow, the competent authority may accept estimation methods for determination of this air flow rate proposed by the operator based on industry best practices.
Za dovajani tok zraka, katerega skupni delež znaša manj kot 2,5 % celotnega pretoka zraka, lahko pristojni organ za določanje te stopnje zračnega pretoka sprejme metode ocenjevanja, ki jih upravljavec predlaga na podlagi najboljših praks industrije.
The operator shall provide evidence through measurements under normal operation conditions that the flue gas flow measured is sufficiently homogeneous to allow for the proposed measurement method.
Upravljavec na podlagi meritev, izvedenih v normalnih pogojih, dokaže, da je izmerjeni pretok dimnega plina dovolj homogen, da omogoča uporabo predlagane merilne metode.
If non-homogeneous flow is confirmed through these measurements, this must be taken into account when determining appropriate monitoring methods and when calculating the uncertainty in the N2O emissions.
Če se s temi meritvami izkaže, da je pretok nehomogen, je treba to upoštevati pri določanju ustreznih metod spremljanja in pri izračunu negotovosti emisij N2O.
OXYGEN (O2)
KISIK (O2)
Oxygen concentrations in the flue gas shall be measured if needed for calculating the flue gas flow according to Section 2.4.
Koncentracije kisika v dimnem plinu se merijo, kadar je to potrebno za izračun pretoka dimnega plina v skladu z oddelkom 2.4.
Requirements described for concentration measurements within Section 6 of Annex I shall apply. Suitable measurement techniques include: paramagnetic alternating pressure, magnetic torsion balance or zirconium dioxide probe.
Pri meritvah koncentracij veljajo zahteve iz oddelka 6 Priloge I. Med primerne merilne tehnike spadajo: metoda paramagnetnega spremenljivega pritiska, magnetna torzijska tehtnica in sonda iz cirkonijevega dioksida.
Uncertainty of O2 concentration measurements shall be taken into account in determining the uncertainty in the N2O emissions.
Pri določanju negotovosti emisij N2O se upošteva negotovost meritev koncentracij O2.
CALCULATION OF N2O EMISSIONS
IZRAČUN EMISIJ N2O
For specific periodic, unabated emissions of N2O from adipic acid, caprolactam, glyoxal and glyoxylic acid production (such as unabated emissions from venting for safety reasons and/or when abatement plant fails) where continuous emissions monitoring of N2O is not technically feasible, calculation of N2O emissions using a mass balance approach can be applied.
Kadar v določenem obdobju emisije N2O, ki nastajajo pri proizvodnji adipinske kisline, kaprolaktama, glioksala in glioksilne kisline, ostajajo nezmanjšane (npr. nezmanjšane emisije zaradi zračenja iz varnostnih razlogov in/ali v primeru izpada naprav za zmanjševanje emisij) in kadar neprekinjeno spremljanje emisij N2O tehnično ni izvedljivo, se lahko emisije N2O izračunajo z uporabo pristopa z masno bilanco.
The calculation method shall be based on the maximum potential emission rate of N2O from the chemical reaction taking place at the time and the period of the emission.
Metoda izračuna temelji na največji možni stopnji emisij N2O pri kemični reakciji, ki poteka med nastajanjem emisije.
The specific calculation approach shall be approved by the competent authority as part of the evaluation of the monitoring plan and the monitoring methodology therein.
Posebno osnovo izračuna odobri pristojni organ kot del ocene načrta za spremljanje in njegove metodologije spremljanja.
The uncertainty in any calculated emissions for a specific emission source shall be taken into account in determining the annual average hourly uncertainty for the emission source.
Pri določanju letne povprečne urne negotovosti vira emisije se upošteva negotovost vseh emisij, izračunanih za posebni vir emisije.
The same tiers as for emissions measured entirely with continuous emissions measurement shall be applied to calculated emissions, or where a combination of calculation and continuous measurement are used to determine N2O emissions.
Za izračunane emisije ali kadar se za določanje emisij N2O uporablja kombinacija izračuna in neprekinjenega merjenja, se uporabljajo enake stopnje, kakor za emisije, ki se v celoti izmerijo z neprekinjenim merjenjem.
CALCULATION OF ANNUAL CO2 EQUIVALENTS (CO2(e))
IZRAČUN LETNEGA EKVIVALENTA CO2 (CO2(e))
The total annual N2O emissions from all emissions sources (measured in tonnes to three decimal places) shall be converted to annual CO2(e) emissions (rounded tonnes) using the following formula:
Skupne letne emisije N2O iz vseh virov emisij (izmerjene v tonah na tri decimalna mesta natančno) se z naslednjo enačbo pretvorijo v letne emisije CO2(e) (zaokroženo na tone):
Oannual
Oletne
For emissions during the period 2008–12, the Global Warming Potential GWPN2O = 310 t CO2(e)/t N2O shall be used, which is the value provided in the Intergovernmental Panel on Climate Change’s Second Assessment Report (1995 IPCC GWP value).
Za emisije N2O v obdobju 2008–2012 se šteje, da je potencial globalnega segrevanja GWPN2O = 310 t CO2(e)/t N2O, kar ustreza vrednosti, ki jo je v svojem drugem poročilu o oceni navedel Medvladni forum o podnebnih spremembah (1995 IPCC GWP value).
The total annual CO2(e) generated by all emission sources and any direct CO2 emissions from other emission sources (if included in the greenhouse gas permit) shall be added to the total annual CO2 emissions generated by the installation and shall be used for reporting and surrendering allowances.
Skupna letna vrednost CO2(e) iz vseh virov emisij in morebitne neposredne emisije CO2 iz drugih virov emisij (če so vključene v dovoljenje za emisije toplogrednih plinov) se dodajo skupnim letnim emisijam CO2, ki nastajajo v napravi, ter se uporabijo pri poročanju in predaji pravic.
DETERMINATION OF ACTIVITY PRODUCTION RATES
DOLOČANJE STOPENJ PROIZVODNJE, POVEZANIH Z DEJAVNOSTJO
Production rates shall be calculated using daily production reports and hours of operation.
Stopnje proizvodnje se izračunajo na podlagi dnevnih poročil o proizvodnji in ur delovanja.
MONITORING PLAN
NAČRT SPREMLJANJA
In addition to requirements set out in Annex I, Section 4.3(a), (b), (c), (d), (j), (k), (m) and (n), monitoring plans for installations covered by this Annex shall contain the following information:
Izpolnjene morajo biti zahteve iz točk (a), (b), (c), (d), (j), (k), (m) in (n) oddelka 4.3 Priloge I, poleg tega pa načrt spremljanja za naprave, ki jih zajema ta priloga, vsebuje še naslednje podatke:
all relevant emissions points during typical operation, and during restrictive and transition phases (e.g. breakdown periods or commissioning phases) shown in a process diagram;
vse ustrezne točke emisije v obdobjih običajnega in omejenega delovanja ter prehodnih obdobjih (npr. izpad proizvodnje ali zagon obratovanja), prikazane v procesnem diagramu;
the method and parameters used to determine the quantity of materials (e.g. ammonia) used in the production process and the maximum quantity of material used at full capacity;
metoda in parametri, uporabljeni za določitev količine materialov (npr. amoniaka), uporabljenih pri proizvodnih postopkih, in največja količina materiala, uporabljenega pri polni zmogljivosti;
the method and parameters used to determine the quantity of product produced as an hourly load, expressed as nitric acid (100 %), adipic acid (100 %), glyoxal and glyoxylic acid and caprolactam per hour respectively;
metoda in parametri, uporabljeni za določitev količine proizvoda, izdelanega na uro, izraženega kot količina proizvedene dušikove kisline (100 %), adipinske kisline (100 %), glioksala, glioksilne kisline oziroma kaprolaktama na uro;
the method and parameters used to determine the N2O concentration in the flue gas from each emission source, its operating range, and its uncertainty, and details of any alternative methods to be applied if concentrations fall outside the operating range and the situations when this may occur;
metoda in parametri, uporabljeni za določitev koncentracije N2O v dimnem plinu iz vsakega vira emisije, merilno območje metode, njena negotovost in podrobnosti o nadomestnih metodah, ki se uporabijo, kadar koncentracije niso v merilnem območju, ter okoliščine, v katerih se to lahko zgodi;
the method used to determine the total flue gas flow rate (expressed in Nm3 per hour) from each emission source, its operating range and its uncertainty.
metoda, uporabljena za določitev skupne stopnje pretoka dimnega plina (izražena v Nm3 na uro) iz vsakega vira emisije, merilno območje metode in njena negotovost.
If derived by calculation, details for each monitored flue gas stream shall be given;
Če se vrednost pridobi z izračunom, se navedejo podrobnosti za vsak tok dimnega plina, ki se spremlja;
the calculation method used to determine N2O emissions from periodic, unabated sources in adipic acid, caprolactam, glyoxal and glyoxylic acid production;
metoda izračuna, uporabljena za določitev emisij N2O iz periodično nastopajočih virov nezmanjšanih emisij pri proizvodnji adipinske kisline, kaprolaktama, glioksala in glioksilne kisline;
the way in which or the extent to which the installation operates with variable loads, and the manner in which the operational management is carried out;
način in obseg obratovanja naprave pri spremenljivi obremenjenosti ter način upravljanja obratovanja;
the method and any calculation formulae used to determine the annual N2O emissions of each emission source;
metoda in morebitne enačbe za izračun letnih emisij N2O iz vsakega vira emisije;
the process conditions that deviate from normal operations, an indication of the potential frequency and the duration of such conditions, as well as an indication of the volume of the N2O emissions during the deviating process conditions (such as abatement equipment malfunction);
stanja, ki odstopajo od normalnega obratovanja, navedba možne pogostosti in trajanja takšnih stanj ter navedba prostornine emisij N2O med takšnimi izjemnimi stanji (npr. okvara opreme za zmanjševanje emisij);
the assessment used to show that the tier uncertainty requirements referred in Section 2 of this Annex are complied with and the tier achieved;
ocena, ki lahko pokaže, da so bile zahteve o vrednosti negotovosti za stopnjo v skladu z oddelkom 2 te priloge izpolnjene in stopnja dosežena;
the value expressed in kg/N2O per hour which has been determined in accordance with Annex I, Sections 6.3(a) and (b) in order to be used in case the measuring instrument fails or does not function properly;
vrednost, izražena v kg/N2O na uro, ki je bila določena v skladu s točkama (a) in (b) oddelka 6.3 Priloge I, da bi se lahko uporabila ob okvari ali nepravilnem delovanju merilnega instrumenta;
Details of any deviations from the requirements of general standards such as EN 14181 and ISO 14956:2002.
podrobnosti o morebitnem odstopanju od zahtev splošnih standardov, npr. EN14181 in ISO 14956:2002.
In addition to the requirements in Annex I, Section 4.3, a substantial change to the monitoring methodology as part of the monitoring plan shall be subject to the approval of the competent authority if it concerns:
Izpolnjene morajo biti zahteve iz oddelka 4.3 Priloge I, poleg tega pa je za bistveno spremembo metodologije spremljanja kot dela načrta za spremljanje v naslednjih primerih potrebna odobritev pristojnega organa:
significant changes in the functioning of the installation that affect the total level of N2O emissions, the N2O concentration, the flow rate or other parameters of the flue gas, especially if N2O abatement measures are installed or replaced,
bistvene spremembe delovanja naprave, ki vplivajo na skupno raven emisij N2O, koncentracijo N2O, stopnjo pretoka ali druge parametre dimnega plina, zlasti pri vgradnji ali zamenjavi naprave za zniževanje emisij N2O,
changes in the methods used to determine N2O emissions, including changes in the continuous measurement of concentrations, oxygen concentrations and flue gas flow, or calculation method which significantly affect the total uncertainty of the emissions,
spremembe metod za določanje emisij N2O, vključno s spremembami neprekinjenega merjenja koncentracij, koncentracij kisika in pretoka dimnega plina ali metode izračuna, ki bistveno vpliva na skupno negotovost emisij,
changes in the parameters used to determine annual emissions and/or production of nitric acid, adipic acid, caprolactam, glyoxal and glyoxylic acid,
spremembe parametrov, ki se uporabljajo za določitev letnih emisij in/ali proizvodnje dušikove kisline, adipinske kisline, kaprolaktama, glioksala in glioksilne kisline,
changes in uncertainty assessment.
spremembe ocene negotovosti.
SAMPLING RATES
STOPNJE VZORČENJA
Valid hourly averages shall be calculated in accordance with Section 6.3(a) of Annex I for:
Veljavne urne povprečne vrednosti se izračunajo v skladu z oddelkom 6.3(a) Priloge I za:
concentration of N2O in the flue gas,
koncentracijo N2O v dimnem plinu,
total flue gas flow where this is measured directly and where required,
skupni pretok dimnega plina, kadar se ta meri neposredno in se to zahteva,
all gas flows and oxygen concentrations necessary to determine the total flue gas flow indirectly.
vse pretoke dimnega plina in koncentracije kisika, potrebne za posredno določitev skupnega pretoka dimnega plina.
MISSING DATA
MANJKAJOČI PODATKI
The operator shall take all practical steps to ensure that continuous emissions monitoring equipment is not out of operation for more than one week in any calendar year.
Upravljavec ukrene vse potrebno, da oprema za neprekinjeno spremljanje emisij ne bi bila v okvari dlje kot en teden v vsakem koledarskem letu.
If this occurs, the operator shall inform the competent authority immediately.
Če se to zgodi, upravljavec o tem takoj obvesti pristojne organe.
DE MINIMIS SOURCES OF N2O
VIRI N2O DE MINIMIS
‘De minimis source streams’ for N2O emission sources means one or more minor, unabated source streams selected by the operator and jointly emitting 1000 tonnes of CO2(e) or less per year, or that emit less that 20000 tonnes of CO2(e) per year and contribute less than 2 % of the total annual emissions of CO2(e) of that installation.
‚Tokovi vira de minimis‘ za vire emisij N2O pomeni enega ali več manjših tokov vira nezmanjšanih emisij, ki jih izbere upravljavec in skupaj na leto bodisi sprostijo 1000 ton CO2(e) ali manj bodisi sprostijo manj kot 20000 ton CO2(e) na leto in prispevajo manj kot 2 % k skupnim letnim emisijam CO2(e) te naprave.
Subject to approval by the competent authority, the operator may apply approaches for monitoring and reporting using his own no-tier estimation method for de minimis source streams of N2O.
Upravljavec lahko za spremljanje in poročanje uporabi lastne metode ocenjevanja tokov virov N2O de minimis brez stopenj, če mu to odobri pristojni organ.
CORROBORATING CALCULATION OF EMISSIONS
POTRDITVENI IZRAČUN EMISIJ
Annex I, Section 6.3(c) shall apply to corroborating reported emissions of N2O (from continuous emissions measurement and calculation) and performed using production data, the 2006 IPCC Guidelines and the approach specified in Annex I, Section 10.3.3 “Horizontal approach”.
Sporočeni podatki o emisijah N2O (pridobljeni z neprekinjenim merjenjem emisij in izračunom) se potrjujejo v skladu z oddelkom 6.3(c) Priloge I na podlagi podatkov o proizvodnji, smernic IPCC iz leta 2006 in ‚horizontalnega pristopa‘, opredeljenega v oddelku 10.3.3.
UNCERTAINTY ASSESSMENTS
OCENA NEGOTOVOSTI
Uncertainty assessments required to demonstrate compliance with relevant tiers in Section 2 shall be determined by means of an error propagation calculation taking into account the uncertainty of all relevant elements of the emission calculation.
Ocena negotovosti, ki je potrebna za dokazovanje skladnosti z ustreznimi stopnjami v oddelku 2, se določa z izračunom propagacije napak, pri čemer se upošteva negotovost vseh pomembnih elementov izračuna emisij.
For the continuous measurement the following sources of uncertainty should be assessed in accordance with EN 14181 and ISO 14956:2002:
Pri neprekinjenem merjenju je treba v skladu z EN 14181 in ISO 14956:2002 oceniti naslednje vire negotovosti:
the specified uncertainty of continuous measurement equipment, including sampling,
opredeljena negotovost opreme za neprekinjeno merjenje, vključno z vzorčenjem,
uncertainties associated to the calibration, and
negotovost, povezana s kalibracijo, in
additional uncertainty connected to how the monitoring equipment is used in practice.
dodatna negotovost, povezana s tem, kako se v praksi uporablja oprema za spremljanje.
For the calculation of the total uncertainty to be used in Section 2.2, hourly N2O concentrations as determined pursuant to Section 2.3 shall be used.
Za izračun celotne negotovosti v skladu z oddelkom 2.2 se uporabijo urne koncentracije N2O, kot so določene v skladu z oddelkom 2.3.