natgillin/translations-raw huggingface dataset:
Mr Fernando AFONSO is hereby appointed as Head of Mission of the European Union mission in support of security sector reform in the Republic of Guinea-Bissau (EU SSR GUINEA-BISSAU), from 1 July 2010.
Fernando AFONSO se imenuje za vodjo misije Evropske unije v podporo reformi varnostnega sektorja v Republiki Gvineji-Bissau, (EU RVS GUINEA-BISSAU), in sicer od 1. julija 2010.
Political and Security Committee Decision EU SSR GUINEA-BISSAU/1/2008 of 5 March 2008 is hereby repealed.
Sklep Političnega in varnostnega odbora EU SSR Guinea-Bissau/1/2008 z dne 5 marca 2008 se razveljavi.
Done at Brussels, 15 June 2010.
V Bruslju, 15. junija 2010
OJ L 73, 15.3.2008, p. 34.
UL L 73, 15.3.2008, str. 34.
on guidelines for the calculation of land carbon stocks for the purpose of Annex V to Directive 2009/28/EC
o smernicah za izračun zalog ogljika v zemljišču za namene Priloge V k Direktivi 2009/28/ES
(notified under document C(2010) 3751)
(notificirano pod dokumentarno številko C(2010) 3751)
Having regard to Directive 2009/28/EC of the European Parliament and of the Council of 23 April 2009 on the promotion of the use of energy from renewable sources and amending and subsequently repealing Directives 2001/77/EC and 2003/30/EC [1], and in particular Annex V, part C, point 10 thereof,
ob upoštevanju Direktive 2009/28/ES Evropskega parlamenta in Sveta z dne 23. aprila 2009 o spodbujanju uporabe energije iz obnovljivih virov, spremembi in poznejši razveljavitvi direktiv 2001/77/ES in 2003/30/ES [1] in zlasti točke 10 dela C Priloge V,
Directive 2009/28/EC lays down rules for calculating the greenhouse gas impact of biofuels, bioliquids and their fossil fuel comparators, which take into account emissions from carbon stock changes caused by land use change.
Direktiva 2009/28/ES določa pravila za izračunavanje vpliva pogonskih biogoriv, drugih tekočih biogoriv in njihovih primerjalnih fosilnih goriv na toplogredne pline, ki upoštevajo emisije iz sprememb zalog ogljika zaradi spremenjene rabe zemljišč.
Directive 98/70/EC of the European Parliament and of the Council of 13 October 1998 relating to the quality of petrol and diesel fuels and amending Council Directive 93/12/EEC [2] includes corresponding rules as far as biofuels are concerned.
Direktiva 98/70/ES Evropskega parlamenta in Sveta z dne 13. oktobra 1998 o kakovosti motornega bencina in dizelskega goriva ter spremembi Direktive 93/12/EGS [2] vključuje ustrezna pravila, ki zadevajo biogoriva.
The Commission should draw its guidelines for the calculation of land carbon stocks on the 2006 Intergovernmental Panel on Climate Change (IPCC) Guidelines for National Greenhouse Gas Inventories.
Komisija bi morala pripraviti svoje smernice za izračun zalog ogljika v zemljišču na podlagi smernic za nacionalne evidence toplogrednih plinov Medvladnega foruma o podnebnih spremembah (Intergovernmental Panel on Climate Change – IPCC) iz leta 2006.
Those Guidelines were intended for national greenhouse gas inventories and are not expressed in a form that is readily applicable by economic operators.
Te smernice so bile namenjene za nacionalne evidence toplogrednih plinov in niso izražene v obliki, ki bi bila neposredno uporabna za gospodarske subjekte.
It is therefore appropriate, where IPCC Guidelines for National Greenhouse Gas Inventories lack the necessary information for purposes of biofuel and bioliquid production or where such information is not accessible, to draw on other scientific sources of data.
Kadar v smernicah IPCC za nacionalne evidence toplogrednih plinov ni potrebnih informacij za proizvodnjo pogonskih biogoriv in drugih tekočih biogoriv ali te informacije niso dosegljive, je zato primerno izhajati iz drugih znanstvenih virov podatkov.
For the calculation of the carbon stocks in soil organic matter it is appropriate to take into account climate, soil type, land cover, land management and input.
Za izračun zalog ogljika v organski snovi tal je primerno upoštevati podnebje, vrsto tal, pojave na zemeljskem površju, upravljanje zemljišč in vnos.
For mineral soils, the IPCC Tier 1 methodology for soil organic carbon is an appropriate method to use for this purpose as it covers the global level.
Za mineralna tla je metodologija IPCC kategorije 1 za organski ogljik v tleh primerna metoda za ta namen, ker obsega svetovno raven.
For organic soils, the IPCC methodology addresses in particular carbon loss following soil drainage and does this only through annual losses.
Za organska tla pa metodologija IPCC obravnava predvsem izgubo ogljika zaradi izsuševanja tal in sicer samo na podlagi letnih izgub.
As soil drainage normally results in high carbon stock loss that cannot be compensated by the greenhouse gas saving of biofuels or bioliquids and as drainage of peatland soil is prohibited by the sustainability criteria laid down by Directive 2009/28/EC, it suffices to lay down general rules for determining soil organic carbon or carbon losses in organic soils.
Ker izsuševanje tal običajno povzroči velike izgube zalog ogljika, ki se ne morejo nadomestiti s prihranki toplogrednega plina iz pogonskih biogoriv ali drugih tekočih biogoriv, in ker je izsuševanje šotišč prepovedano s trajnostnimi merili iz Direktive 2009/28/ES, za opredeljevanje organskega ogljika v tleh ali izgub ogljika v organskih tleh zadošča določitev splošnih pravil.
For the calculation of carbon stock in living biomass and dead organic matter a low complexity approach corresponding to IPCC Tier 1 methodology for vegetation should be an appropriate method.
Za izračun zalog ogljika v živi biomasi in odmrli organski snovi bi moral biti nezahteven pristop, ki ustreza kategoriji 1 metodologije IPCC za vegetacijo, ustrezna metoda.
In accordance with that methodology it is reasonable to assume that all carbon stock in living biomass and dead organic matter is lost from the land upon conversion.
V skladu s to metodologijo je smiselno predpostaviti, da zemljišče po spremembi namembnosti izgubi vso zalogo ogljika v živi biomasi in odmrli organski snovi.
Dead organic matter is usually of low significance in land conversion for the establishment of crops for the production of biofuels and bioliquids, but should be taken into account at least for closed forests.
Odmrla organska snov je običajno pri spremembi namembnosti zemljišča za določitev posevkov za proizvodnjo pogonskih biogoriv in drugih tekočih biogoriv manj pomembna, vendar jo je treba upoštevati vsaj pri strnjenih gozdnih površinah.
In calculating the greenhouse gas impact of land conversion, economic operators should be able to use actual values for the carbon stocks associated with the reference land use and the land use after conversion.
Pri izračunavanju vpliva spremembe namembnosti zemljišč na toplogredne pline bi morali gospodarski subjekti imeti možnost uporabe dejanskih vrednosti za zaloge ogljika, povezanih z referenčno rabo zemljišč in rabo zemljišč po spremembi namembnosti.
They should also be able to use standard values and it is appropriate for these guidelines to provide them.
Morali bi imeti tudi možnost uporabe standardnih vrednosti, zato je primerno, da jim jih te smernice zagotovijo.
It is not necessary, however, to provide standard values for improbable combinations of climate and soil type.
Vendar ni potrebno zagotavljati standardnih vrednosti za malo verjetne kombinacije podnebja in vrste tal.
Annex V to Directive 2009/28/EC sets out the method for calculating greenhouse gas impacts and contains rules for the calculation of annualised emissions of carbon stock changes from land use changes.
Priloga V k Direktivi 2009/28/ES določa način za izračun vplivov na toplogredne pline in vsebuje pravila za izračun letnih emisij sprememb zalog ogljika zaradi sprememb rabe zemljišč.
The guidelines annexed to this Decision establish rules for the calculation of land carbon stocks, completing the rules laid down in the Annex V,
Smernice, ki so priložene k temu sklepu, določajo pravila za izračun zalog ogljika v zemljišču in dopolnjujejo pravila iz Priloge V –
The guidelines for the calculation of land carbon stocks for the purpose of Annex V to Directive 2009/28/EC are set out in the Annex to this Decision.
Smernice za izračun zalog ogljika v zemljišču za namene Priloge V k Direktivi 2009/28/ES so določene v Prilogi k temu sklepu.
Guidelines for the calculation of land carbon stocks for the purpose of Annex V to Directive 2009/28/EC
Smernice za izračun zalog ogljika v zemljišču za namene Priloge V k Direktivi 2009/28/ES
Consistent representation of land carbon stocks
Dosledna predstavitev zalog ogljika v zemljišču
Calculation of carbon stocks
Izračun zalog ogljika
Soil organic carbon stock
Zaloga organskega ogljika v tleh
Above and below ground vegetation carbon stock
Zaloga ogljika v nadzemni in podzemni vegetacij
Standard soil carbon stock in mineral soils
Standardna zaloga ogljika v prsti v mineralnih tleh
Factors reflecting the difference in soil organic carbon compared to the standard soil organic carbon
Faktorji, ki odražajo razliko med organskim ogljikom v tleh in standardnim organskim ogljikom v tleh
Carbon stock values for above and below ground vegetation carbon stock
Vrednosti zalog ogljika za zalogo ogljika v nadzemni in podzemni vegetaciji
These guidelines establish the rules for the calculation of land carbon stocks, both for the reference land use (CSR, as defined in point 7 of Annex V to Directive 2009/28/EC) and the actual land use (CSA, as defined in point 7 of Annex V to Directive 2009/28/EC).
Te smernice določajo pravila za izračun zalog ogljika v zemljišču za referenčno rabo zemljišča (CSR, kakor je opredeljena v točki 7 Priloge V k Direktivi 2009/28/ES) in dejansko rabo zemljišča (CSA, kakor je opredeljena v točki 7 Priloge V k Direktivi 2009/28/ES).
In point 2 rules are provided in order that land carbon stocks are consistently determined.
V točki 2 so opredeljena pravila za dosledno opredelitev zalog ogljika v zemljišču.
Point 3 provides the general rule for the calculation of carbon stocks, which consist of two components: soil organic carbon and carbon stock in the above and below ground vegetation.
Točka 3 določa splošno pravilo za izračun zalog ogljika, ki ga sestavljata dva elementa: organski ogljik v tleh in zaloga ogljika v nadzemni in podzemni vegetaciji.
Point 4 provides detailed rules for determining the soil organic carbon stock.
Točka 4 določa podrobna pravila za opredelitev zaloge organskega ogljika v tleh.
For mineral soils it provides the option of following a method that allows the use of values provided for in the guidelines, while the option of using alternative methods is also provided for.
Za mineralna tla določa možnost uporabe metode, ki omogoča uporabo vrednosti, določenih v smernicah, zagotovljena pa je tudi možnost uporabe alternativnih metod.
For organic soils methods are described, but the guidelines do not contain values for determining soil organic carbon stock in organic soils.
Za organska tla so metode opisane, vendar pa smernice ne vsebujejo vrednosti za opredeljevanje zalog organskega ogljika v organskih tleh.
Point 5 provides detailed rules for carbon stock in vegetation, but is only relevant in the case the choice is made not to use values for above and below ground vegetation carbon stock provided in point 8 of the guidelines (the use of the values provided in point 8 is not obligatory and for certain cases it may not contain the appropriate values).
Točka 5 določa podrobna pravila za zalogo ogljika v vegetaciji, vendar je primerna samo takrat, kadar se sprejme odločitev, da se ne uporabljajo vrednosti za zaloge ogljika v nadzemni in podzemni vegetaciji, ki jih določa točka 8 smernic (uporaba vrednosti, ki je določena v točki 8, ni obvezna in v nekaterih primerih morda ne obsega ustreznih vrednosti).
Point 6 provides the rules to select the appropriate values in case the choice is made to use the guidelines’ values related to soil organic carbon in mineral soils (these values are provided in points 6 and 7).
Točka 6 določa pravila za izbiro ustreznih vrednosti v primeru odločitve o uporabi vrednosti iz smernice, ki zadevajo organski ogljik v mineralnih tleh (te vrednosti so določene v točkah 6 in 7).
In these rules reference is made to data layers on climate regions and soil type available through the online Transparency platform established by Directive 2009/28/EC.
Ta pravila se sklicujejo na podatkovne plasti o podnebnih območjih in vrsti tal, ki so na voljo v spletni platformi za preglednost, ki jo je uvedla Direktiva 2009/28/ES.
Those data layers are detailed layers underlying figures 1 and 2 below.
Te podatkovne plasti so podrobne plasti, ki so podlaga za sliki 1 in 2 v nadaljevanju.
Point 8 provides values for carbon stock in the above and below ground vegetation and related parameters.
Točka 8 navaja vrednosti za zalogo ogljika v nadzemni in podzemni vegetaciji ter ustrezne parametre.
Points 7 and 8 provide values for four different land use categories: cropland, perennial crops, grassland and forest land.
Točki 7 in 8 navajata vrednosti za štiri različne kategorije rabe zemljišč: obdelovalna zemljišča, trajne posevke, travinje in gozdna zemljišča.
Climate regions
Podnebna območja
Legend: 1 = Tropical, montane; 2 = Tropical, wet; 3 = Tropical, moist, 4 = Tropical, dry; 5 = Warm temperate, moist; 6 = Warm temperate, dry; 7 = Cool temperate, moist; 8 = Cool temperate, dry; 9 = Boreal, moist; 10 = Boreal, dry; 11 = Polar, moist; 12 = Polar, dry.
Legenda: 1 = Tropsko, gorsko; 2 = Tropsko, mokro; 3 = Tropsko, vlažno; 4 = Tropsko, suho; 5 = Zmerno toplo, vlažno; 6 = Zmerno toplo, suho; 7 = Zmerno hladno, vlažno; 8 = Zmerno hladno, suho; 9 = Severno, vlažno; 10 = Severno, suho; 11 = Polarno, vlažno; 12 = Polarno, suho.
Geographic distribution of soil types
Geografska porazdelitev vrste tal
Legend: 1 = Organic; 2 = Sandy Soils; 3 = Wetland Soils; 4 = Volcanic Soils; 5 = Spodic Soils; 6 = High Activity Clay Soils; 7 = Low Activity Clay Soils; 8 = Other Areas.
Legenda: 1 = Organska; 2 = Peščena tla; 3 = Tla z mokrišči; 4 = Vulkanska tla; 5 = Spodična tla; 6 = Visoko aktivna ilovnata tla; 7 = Nizko aktivna ilovnata tla; 8 = Druga območja.
CONSISTENT REPRESENTATION OF LAND CARBON STOCKS
DOSLEDNA PREDSTAVITEV ZALOG OGLJIKA V ZEMLJIŠČIH
For determining the carbon stock per unit area associated with CSR and CSA the following rules shall apply:
Za opredeljevanje zaloge ogljika na enoto površine, povezane s CSR in CSA, se uporabljajo naslednja pravila:
the area for which the land carbon stocks are calculated shall for the entire area have similar:
Površina, za katero se izračunavajo zaloge ogljika v zemljišču, mora imeti za celotno površino podobne:
biophysical conditions in terms of climate and soil type;
biofizikalne pogoje glede podnebja in vrste tal;
management history in terms of tillage;
zgodovino upravljanja v zvezi z obdelovanjem tal;
input history in terms of carbon input to soil.
zgodovino vnosa ogljika v tla.
the carbon stock of the actual land use, CSA, shall be taken as:
Zaloga ogljika pri dejanski rabi zemljišča, CSA, se upošteva:
in the case of loss of carbon stock: the estimated equilibrium carbon stock that the land will reach in its new use,
v primeru izgube zaloge ogljika: kot ocenjena ravnotežna zaloga ogljika, ki jo bo zemljišče doseglo z novo rabo;
in the case of carbon stock accumulation: the estimated carbon stock after 20 years or when the crop reaches maturity, whichever the earlier.
v primeru akumulacije zaloge ogljika: kot ocenjena zaloga ogljika po 20 letih ali ko pridelek dozori, kar koli od tega je prej.
CALCULATION OF CARBON STOCKS
IZRAČUN ZALOG OGLJIKA
For the calculation of CSR and CSA the following rule shall apply:
Za izračun CSR in CSA se uporablja naslednje pravilo:
the carbon stock per unit area associated with the land use i (measured as mass of carbon per unit area, including both soil and vegetation);
zaloga ogljika na enoto površine, povezana z dejansko rabo zemljišča i (merjena kot masa ogljika na enoto površine, vključno s prstjo in vegetacijo);
SOC soil organic carbon (measured as mass of carbon per hectare), calculated in accordance with point 4;
SOC organski ogljik v tleh (merjen kot masa ogljika na hektar), izračunan v skladu s točko 4;
above and below ground vegetation carbon stock (measured as mass of carbon per hectare), calculated in accordance with point 5 or selected from the appropriate values in point 8;
zaloga ogljika v nadzemni in podzemni vegetaciji (merjena kot masa ogljika na hektar), izračunana v skladu s točko 5 ali izbrana med ustreznimi vrednostmi v točki 8;
A factor scaling to the area concerned (measured as hectares per unit area).
A faktor razmerja do zadevne površine (merjen v hektarih na enoto površine).
SOIL ORGANIC CARBON STOCK
ZALOGA ORGANSKEGA OGLJIKA V TLEH
Mineral soils
Mineralna tla
For the calculation of SOC the following rule may be used:
Za izračun SOC se lahko uporabi naslednje pravilo:
SOC soil organic carbon (measured as mass of carbon per hectare);
SOC organski ogljik v tleh (merjen kot masa ogljika na hektar);
land use factor reflecting the difference in soil organic carbon associated with the type of land use compared to the standard soil organic carbon;
standardni organski ogljik v tleh v 0–30-centimetrski vrhnji plasti prsti (merjen kot masa ogljika na hektar);
management factor reflecting the difference in soil organic carbon associated with the principle management practice compared to the standard soil organic carbon;
faktor rabe zemljišča, ki odraža razliko med organskim ogljikom v tleh, povezanim z vrsto rabe zemljišča, in standardnim organskim ogljikom v tleh;
input factor reflecting the difference in soil organic carbon associated with different levels of carbon input to soil compared to the standard soil organic carbon.
faktor vnosa, ki odraža razliko med organskem ogljikom v tleh, povezanim z različnimi ravnmi vnosa, in standardnim organskim ogljikom v tleh.
For SOCST the appropriate values presented in point 6 shall apply.
Za SOCST se uporabljajo ustrezne vrednosti, predstavljene v točki 6.
For FLU, FMG and FI the appropriate values presented in point 7 shall apply.
Za FLU, FMG and FI se uporabljajo ustrezne vrednosti, predstavljene v točki 7.
As an alternative to using the above rule, other appropriate methods, including measurements, may be used to determine SOC.
Kot druga možnost se lahko za opredelitev SOC namesto zgornjega pravila uporabljajo druge ustrezne metode, vključno z meritvami.
As far as such methods are not based on measurements, they shall take into account climate, soil type, land cover, land management and inputs.
Če te metode ne temeljijo na meritvah, morajo upoštevati podnebje, vrsto tal, pojave na zemeljskem površju, upravljanje zemljišč in vnose.
Organic soils (histosols)
Organska tla (histosoli)
For determining SOC, appropriate methods shall be used.
Za opredelitev SOC se uporabljajo ustrezne metode.
Such methods shall take into account the entire depth of the organic soil layer as well as climate, land cover and land management and input.
Te metode upoštevajo celotno debelino organske plasti tal, pa tudi podnebje, pojave na zemeljskem površju ter upravljanje zemljišč in vnos.
Such methods may include measurements.
Te metode lahko vključujejo meritve.
Where carbon stock affected by soil drainage is concerned, losses of carbon following drainage shall be taken into account by appropriate methods.
Kjer gre za zaloge ogljika, na katere vpliva izsuševanje tal, je treba z ustreznimi metodami upoštevati izgube ogljika zaradi izsuševanja.
Such methods may be based on annual losses of carbon following drainage.
Te metode lahko temeljijo na letnih izgubah ogljika zaradi izsuševanja.
ABOVE AND BELOW GROUND VEGETATION CARBON STOCK
ZALOGA OGLJIKA V NADZEMNI IN PODZEMNI VEGETACIJI
Except where a value for CVEG set out in point 8 is used, for the calculation of CVEG the following rule shall apply:
Razen takrat, ko se za CVEG uporablja vrednost iz točke 8, se za izračun CVEG uporablja naslednja pravilo:
above and below ground vegetation carbon stock (measured as mass of carbon per hectare);
zaloga ogljika v nadzemni in podzemni vegetaciji (merjena kot masa ogljika na hektar);
above and below ground carbon stock in living biomass (measured as mass of carbon per hectare), calculated in accordance with point 5.1;
zaloga ogljika v živi biomasi nadzemne in podzemne vegetacije (merjena kot masa ogljika na hektar), izračunana v skladu s točko 5.1;
above and below ground carbon stock in dead organic matter (measured as mass of carbon per hectare), calculated in accordance with point 5.2.
zaloga ogljika v odmrli organski snovi nadzemne in podzemne vegetacije (merjena kot masa ogljika na hektar), izračunana v skladu s točko 5.2;
For CDOM the value of 0 may be used, except in the case of forest land — excluding forest plantations — having more than 30 % canopy cover.
Za CDOM se lahko uporablja vrednost 0, razen za gozdna zemljišča – razen gozdnih nasadov – katerih krošnje pokrivajo več kot 30 % površine.
Living biomass
Živa biomasa
For the calculation of CBM the following rule shall apply:
Za izračun CBM se uporablja naslednje pravilo:
above and below ground carbon stock in living biomass (measured as mass of carbon per hectare);
nadzemna in podzemna zaloga ogljika v živi biomasi (merjena kot masa ogljika na hektar);
above ground carbon stock in living biomass (measured as mass of carbon per hectare), calculated in accordance with point 5.1.1;
nadzemna zaloga ogljika v živi biomasi (merjena kot masa ogljika na hektar), izračunana v skladu s točko 5.1.1;
below ground carbon stock in living biomass (measured as mass of carbon per hectare), calculated in accordance with point 5.1.2.
podzemna zaloga ogljika v živi biomasi (merjena kot masa ogljika na hektar), izračunana v skladu s točko 5.1.2.
Above ground living biomass
Za izračun
For the calculation of CAGB the following rule shall apply:
For the calculation of CAGBse uporablja naslednje pravilo:
above ground carbon stock in living biomass (measured as mass of carbon per hectare);
nadzemna zaloga ogljika v živi biomasi (merjena kot masa ogljika na hektar);
weight of above ground living biomass (measured as mass of dry matter per hectare);
teža nadzemne žive biomase (merjena kot masa suhe snovi na hektar);
carbon fraction of dry matter in living biomass (measured as mass of carbon per mass of dry matter).
delež ogljika v suhi snovi žive biomase (merjen kot masa ogljika v masi suhe snovi).
For cropland, perennial crops and forest plantations the value for BAGB shall be the average weight of the above ground living biomass during the production cycle.
Za obdelovalna zemljišča, trajne posevke in gozdne nasade je vrednost za BAGB enaka povprečni teži nadzemne žive biomase v proizvodnem ciklu.
For CFB the value of 0,47 may be used.
Za CFB se lahko uporablja vrednost 0,47.
Below ground living biomass
Podzemna živa biomasa
For the calculation of CBGB one of the following two rules shall be used:
Za izračun CBGB se uporablja eno od naslednjih dveh pravil:
below ground carbon stock in living biomass (measured as mass of carbon per hectare);
podzemna zaloga ogljika v živi biomasi (merjena kot masa ogljika na hektar);
weight of below ground living biomass (measured as mass of dry matter per hectare);
teža podzemne žive biomase (merjena kot masa suhe snovi na hektar);
For cropland, perennial crops and forest plantations the value for BBGB shall be the average weight of the below ground living biomass during the production cycle.
Za obdelovalna zemljišča, trajne posevke in gozdne nasade je vrednost za BBGB enaka povprečni teži podzemne žive biomase v proizvodnem ciklu.
R ratio of below ground carbon stock in living biomass to above ground carbon stock in living biomass.
R razmerje med podzemno zalogo vodika v živi biomasi in nadzemno zalogo vodika v živi biomasi.
Appropriate values for R set out in point 8 may be used.
Za R se lahko uporabljajo ustrezne vrednosti iz točke 8.
Dead organic matter
Odmrla organska snov
For the calculation of CDOM the following rule shall apply:
Za izračun CDOM se uporablja naslednje pravilo:
above and below ground carbon stock in dead organic matter (measured as mass of carbon per hectare);
nadzemna in podzemna zaloga ogljika v odmrli organski snovi (merjena kot masa ogljika na hektar);