natgillin/translations-raw huggingface dataset:
Certain farmers may thus have a high proportion of eligible hectares not covered by payment entitlements which may lead to hardship cases as certain support schemes accessory to the basic payment scheme, in particular the payment for agricultural practices beneficial for the climate and environment, are based on the eligible hectares declared for the purpose of activation of payment entitlements.
Zato bi moralo biti pojasnjeno, da imajo države članice možnost dodeliti plačilne pravice iz nacionalne ali regionalne rezerve, kadar na kmeta bistveno vplivajo omejitve iz člena 24(3) do (7) Uredbe (EU) št. 1307/2013.
Therefore, it should be clarified that Member States have the possibility to allocate payment entitlements from the national or regional reserve when a farmer is significantly affected by the limitations provided for in Article 24(3) to (7) of Regulation (EU) No 1307/2013.
Ker za nekatera področja ne veljajo obveznosti zelene komponente ali vključujejo le omejene stroške za izpolnjevanje zahtev za zeleno komponento, bi morale države članice imeti možnost, da takih območij ne upoštevajo pri določanju težavnih okoliščin.
As certain areas are not subject to greening obligations or only involve limited costs of compliance with greening, Member States should further be allowed to decide not to include such areas when determining hardship cases.
Člen 21(4) Uredbe (EU) št. 1307/2013 določa, da plačilne pravice kmeta (v lasti ali zakupu), ki presegajo število upravičenih hektarjev, ki jih ima na voljo, prenehajo.
Pursuant to Article 21(4) of Regulation (EU) No 1307/2013, payment entitlements held by a farmer (owned or leased-in) in excess of the eligible hectares at his disposal expire.
Zaradi pravne varnosti bi bilo treba pojasniti prednostni vrstni red prenehanja navedenih plačilnih pravic in določiti nadaljnja pravila o izvajanju.
For reasons of legal certainty, it is appropriate to clarify the order of priority of expiry of those payment entitlements and to define further rules on implementation.
Poleg tega bi bilo treba državam članicam omogočiti, da te določbe upoštevajo tudi pri določanju vrednosti plačilnih pravic.
Moreover it is appropriate to give Member States the possibility to take this provision into account also in the context of the determination of the value of payment entitlements.
Država članica, ki uporablja shemo enotnega plačila na površino in shemo osnovnega plačila najpozneje od 1. januarja 2018, lahko diferencira shemo enotnega plačila na površino na hektar ob upoštevanju nekaterih plačil, dodeljenih za koledarsko leto 2014.
Having regard to the fact that the single area payment per hectare is calculated every year and that the eligibility to the basic payment is a precondition for access to most of the other direct payment schemes and thus intrinsically connected with them, it is necessary to clarify that only those eligible hectares, which are determined pursuant to point (23)(a) of the second subparagraph of Article 2(1) of Delegated Regulation (EU) No 640/2014 are to be taken into account for the purposes of the relevant schemes.
Če je kmeta v koledarskem letu 2014 prizadela višja sila ali izjemne okoliščine, bi bilo primerno diferenciacijo določiti na podlagi zadnjega leta, v katerem ni bilo primerov višje sile ali izjemnih okoliščin.
Member State applying the single area payment scheme and applying the basic payment scheme as from 1 January 2018 at the latest may differentiate the single area payment per hectare taking into account certain payments granted for calendar year 2014.
Poleg tega bi bilo zaradi pravne varnosti treba določiti pravila za primer dejanskega ali pričakovanega dedovanja.
For the purpose of that differentiation, it is appropriate to specify how those payments should be taken into account and to lay down further criteria necessary in order to respect the decoupled nature of certain schemes.
Poglavje 3 naslova III Uredbe (EU) št. 1307/2013 določa pogoje za dodelitev plačil za kmetijske prakse, ki ugodno vplivajo na podnebje in okolje (plačila za zeleno komponento).
Moreover, where a farmer was affected by force majeure or exceptional circumstances affecting calendar year 2014, it is appropriate to establish the differentiation on the basis of the last year not affected by force majeure or exceptional circumstances.
Zahteve v zvezi s plačili za zeleno komponento, kot so določene v osnovnem aktu, so posplošene (veljajo po enakem vzorcu za vse upravičence) ter urejajo nepogodbene ukrepe, s čimer na splošno zagotavljajo, da kmetijstvo EU temelji na praksah, ki presegajo zahteve navzkrižne skladnosti.
In addition, for the sake of legal certainty, rules should be provided for the case of an actual or anticipated inheritance.
Ta načela iz osnovnega akta se upoštevajo pri določanju natančnih pravil glede praks zelene komponente.
Chapter 3 of Title III of Regulation (EU) No 1307/2013 establishes the conditions for the granting of the payment for agricultural practices beneficial for the climate and the environment (‘greening’ payment).
Za ustrezno stopnjo zanesljivosti glede obveznosti iz člena 43(3) Uredbe (EU) št. 1307/2013 v zvezi z enakovrednimi praksami, ki so zajete v nacionalnih ali regionalnih shemah certificiranja, bi bilo treba določiti merila glede imenovanja javnih ali zasebnih certifikacijskih organov.
The requirements tied to the greening payment as stipulated in the basic act are generalised (applicable following the same pattern for all beneficiaries) and provide for non-contractual actions, globally ensuring that EU agriculture is based on practices going beyond the requirements of cross compliance.
Za spoštovanje načela preprečevanja dvojnega financiranja je treba določiti pravila za izračun plačil za nekatere posebne obveznosti, ki zajemajo prakse iz točk 3 in 4 oddelka I in točke 7 oddelka III iz Priloge IX k Uredbi (EU) št. 1307/2013.
These principles laid down in the basic act shall be taken into account when specifying the detailed rules concerning the greening practices.
Ker navedene obveznosti zadevajo enakovredne prakse, ki kmetom omogočajo prevzem takšnih obveznosti, da izpolnijo eno ali več zahtev, da bi lahko prejeli plačilo „za zeleno komponento“ iz poglavja 3 naslova III Uredbe (EU) št. 1307/2013, bi se morala plačila za te obveznosti v primerjavi z normalnim plačilom, ki ga določa člen 28(6) Uredbe (EU) št. 1305/2013 Evropskega parlamenta in Sveta [11], zmanjšati za znesek, ki se izračuna na podlagi stopnje plačila za zeleno komponento v zadevni državi članici ali regiji ali v specifičnih primerih na podlagi posameznega plačila za zeleno komponento kmetu.
In order to have an appropriate level of assurance as regards the obligations set by Article 43(3) of Regulation (EU) No 1307/2013 relating to equivalent practices covered by national or regional certification schemes, criteria should be established as regards the designation of public or private certification authorities.
Člen 44 Uredbe (EU) št. 1307/2013 določa obveznosti v zvezi s številom kmetijskih rastlin in njihovimi sorazmernimi deleži na orni zemlji.
In order to respect the principle of no double funding, rules for the calculation of the payments for some specific commitments covering practices referred to in points 3 and 4 of Section I and point 7 of Section III of Annex IX to Regulation (EU) No 1307/2013 need to be provided for.
Določiti je treba pravila o natančnem izračunu deležev različnih kmetijskih rastlin.
As those commitments concern equivalent practices that allow farmers taking up such commitments to fulfil one or more obligations in order to receive the ‘greening’ payment referred to in Chapter 3 of Title III of Regulation (EU) No 1307/2013, the payments for those commitments, compared to the normal payment provided for under Article 28(6) of Regulation (EU) No 1305/2013 of the European Parliament and of the Council [11], should be reduced by an amount that is to be calculated on the basis of the level of the greening payment in the Member State or region concerned or in specific cases based on the individual greening payment of the farmer.
Določiti bi bilo treba pravila o obdobju za izračun relativnega deleža kmetijskih rastlin ter pri tem upoštevati dejansko časovno razporeditev njihovega pridelovanja in potrebo po enostavni administraciji.
Article 44 of Regulation (EU) No 1307/2013 lays down obligations with respect to the number of crops and the relative shares of crops on arable land.
Da bi se zagotovila večja jasnost za kmete in države članice ter da bi se prispevalo k varstvu elementov krajine na ornih poljih, je treba stanje pojasniti glede na površino, ki ima te krajinske lastnosti.
Rules concerning the precise calculation of the shares of different crops need to be established.
Za izračun deležev različnih kmetijskih rastlin je treba določiti tudi dodatna pravila za posebne primere mešanih kmetijskih rastlin, gojenih v različnih vrstah, setev podsevkov in uporabo mešanic semen.
Rules on the period that will be taken into account for the calculation of the relative share of crops should be set, taking account of the practical timing of crop cultivation activities and the need to allow a simple administration.
Takšne površine travinja, ki predstavljajo območja visokega okoljskega interesa se nahajajo tudi zunaj omrežja Natura 2000.
For the sake of clarity for farmers and Member States and to contribute to the protection of landscape elements situated within arable fields, it is necessary to clarify the situation with respect to the area occupied by landscape features.
Za površine, ki se nahajajo zunaj omrežja, je za zagotovitev njihovega učinkovitega varovanja potrebno vzpostaviti okvir, po katerem bodo države članice določale takšne površine in ki bi moral dopuščati, da upoštevajo pogoje v državi članici ter bi moral nadgrajevati sinergije z obstoječimi okoljskimi politikami.
Article 45(1) of Regulation (EU) No 1307/2013 lays down obligations which ai m at preserving the permanent grassland areas that contribute most to the protection of the environment and in particular carbon sequestration, biodiversity and soil protection.
Člen 45(2) Uredbe (EU) št. 1307/2013 določa ohranjanje deleža trajnega travinja glede na celotno kmetijsko površino.
Such grasslands, which constitute areas of high environmental interest, are located within but also outside of the Natura 2000 network.
Za dosego tega cilja bi morale države članice spremljati razvoj deleža trajnih pašnikov.
For those which are located outside, it is necessary in order to secure their effective protection, to establish a framework for Member States for their designation which should allow them to take account of conditions in the Member State and should build on the synergy with existing environmental policies.
Omogočiti bi jim bilo treba, da vzpostavijo sistem predhodne odobritve.
In order to provide for the protection of such permanent grassland areas over the years, rules should be established on the reconversion of such areas in case of a breach of the strict protection by the farmer.
Posamične ponovne spremembe in prepoved nadaljnjih sprememb bi se morale zahtevati v primeru zmanjšanja za več kot 5 %.
Article 45(2) of Regulation (EU) No 1307/2013 provides for the protection of the share of permanent grassland compared to the total agricultural area.
Zaradi jasnosti in sorazmernega izvajanja bi bilo treba določiti pravila za kmete in površine, za katere so potrebne odobritve in ponovne spremembe.
In order to achieve this goal, Member States should monitor the evolution of the share of permanent grassland.
Določiti bi bilo treba pravila za metodo določanja razmerja trajnega travinja in kmetijske površine, da bi se preprečili primeri, v katerih bi se površine trajnega travinja upoštevale dvakrat zaradi prakse dolgoročnega kolobarjenja travinja, ter da bi se preprečilo, da bi spremembe, ki jih izvedejo majhni in ekološki kmetje, ki so izvzeti iz obveznosti ponovnih sprememb, neposredno vplivale na obveznost ponovne spremembe zemljišča drugih kmetov.
They should be allowed to establish a system of prior authorisation.
Državam članicam bi bilo treba omogočiti, da v utemeljenih primerih prilagodijo svoje referenčno razmerje.
Individual reconversions and a prohibition of further conversions should be required in case of a decrease beyond 5 %.
Člen 46 Uredbe (EU) št. 1307/2013 navaja značilnosti in površine, ki jih države članice lahko uporabljajo kot površine z ekološkim pomenom.
In order to have an effective use of the authorisation procedure for the conversion of permanent grassland, Member States should be granted the flexibility to select priority areas or groups of farmers for the granting of the authorisation based on objective criteria.
Da bi dosegli cilj biotske raznovrstnosti, bi morala navedena merila zagotoviti ohranitev in izboljšanje biotske raznovrstnosti na kmetijah.
Rules should be provided for the method to determine the ratio of permanent grassland to agricultural land in order to avoid situations in which permanent grassland areas are counted twice due to the practice to have grassland in a long rotation and to avoid that the conversions by small and organic farmers, that are exempted from obligations to reconvert, have a direct impact on the reconversion obligation of other farmers.
Hkrati bi morala merila upoštevati že obstoječa prizadevanja kmetov.
Member States should be allowed to adapt their reference ratio in justified cases.
Na zemljišču v prahi prepoved proizvodnje, s katero se bo omejila uporaba pesticidov in gnojil, ne bi smela izključiti prostovoljnih ukrepov, kot je sejanje mešanice divjih cvetlic, saj se tako lahko izboljšajo koristi biotske raznovrstnosti.
Article 46 of Regulation (EU) No 1307/2013 lists the features and areas that can be applied as ecological focus area by Member States.
Pojasniti bi bilo treba, da zemljišče, ki je zaradi izpolnitve zahteve po površinah z ekološkim pomenom več kot 5 let v prahi, ostane orno zemljišče in se ne opredeli kot trajno travinje.
Further criteria to qualify those features and areas as ecological focus areas need to be laid down.
Zaradi raznolikosti strukture teras po Uniji bi morale biti države članice tiste, ki na podlagi nacionalnih ali regionalnih posebnosti določijo podrobne pogoje, pri čemer upoštevajo njihovo vrednost za biotsko raznovrstnost.
In order to meet the biodiversity objective, those criteria should ensure the safeguarding and improvement of biodiversity on farms.
Zaradi jasnosti bi bilo treba navesti vse krajinske značilnosti, ki se lahko štejejo za površino z ekološkim pomenom, pojasniti pa bi bilo treba tudi povezavo z značilnostmi, ki so v državah članicah že zaščitene v okviru navzkrižne skladnosti.
Those criteria should also take into account the efforts already made by farmers.
Za nekatere značilnosti bi bilo treba določiti najmanjšo ali največjo velikost, kar bi pomagalo pri njihovi identifikaciji in zagotovitvi, da je površina pretežno kmetijska.
On land lying fallow, the requirement of having no production, which will result in limiting the application of pesticides or fertilisers, should not exclude voluntary actions such as the seeding of wildflower mixtures with a view to improve the biodiversity benefits.
Varovalni pasovi, ki se nahajajo blizu meje ornih polj vzdolž vodnih tokov ali pa na samih poljih višje na pobočju, so koristni za zmanjševanje odtekanja onesnaževal v površinske vode.
It should be clarified that the land lying fallow for more than five years for the purpose of the ecological focus area requirement is to remain arable land and does not fall under the definition of permanent grassland.
Za povečanje koristi biotske raznovrstnosti bi bilo treba določiti, da se površine, opredeljene kot površine z ekološkim pomenom, ne smejo uporabljati za proizvodnjo, s čimer se bo mogoče izogniti tudi uporabi pesticidov ter omejiti uporabo gnojil.
As regards terraces, given the variety in their construction across the Union, it should be up to Member States to define detailed conditions based on national or regional specificities, taking account of their value for biodiversity.
Da bi še dodatno povečali koristi biotske raznovrstnosti, se ne bi smelo izključiti prostovoljnih ukrepov, kot so sejanje mešanic divjih cvetlic.
For the sake of clarity, landscape features that count as ecological focus area should be listed and the link with features already protected in Member States under cross compliance should be clarified.
Države članice bi se morale same odločiti, ali sta na varovalnih pasovih paša in košnja za krmo dovoljena ali ne.
For some features, a minimum or maximum size should be established in order to help their identification and help guarantee that the area is predominantly agricultural.
Kar zadeva hektarje kmetijsko-gozdnih površin, bi bilo treba pojasniti, da so površine, ki jih je treba upoštevati, tiste površine ornih zemljišč, ki se nahajajo na površini, vključeni v kmetijsko-gozdarski sistem, ki še vedno izpolnjuje pogoje, na podlagi katerih prejema ali je prejela podporo za razvoj podeželja.
Buffer strips, to be located near the border of arable fields along water courses or within fields higher upon a slope, are beneficial for the purpose of reducing runoff to surface waters of pollutants.
Države članice, ki za izpolnitev obveznosti glede površine z ekološkim pomenom izberejo navedene površine, bi morale pri oblikovanju dodatnih pogojev za prejemanje podpore za uvedbo kmetijsko-gozdarskih sistemov v svojih programih razvoja podeželja upoštevati cilj biotske raznovrstnosti.
In the interest of biodiversity benefits, it should be provided that all those areas counted as ecological focus area may not be used for production, which will also avoid the application of pesticides and limit the application of fertilisers.
Kar zadeva pasove upravičenih hektarjev ob gozdu, bi morale države članice same odločati, ali bodo na njih prepovedale pridelavo, kar bi onemogočilo uporabo vložkov na pasu ob gozdu, s čimer bi se ustvaril varovalni prehod do gozda.
In order to further enhance the biodiversity benefits, voluntary actions such as the seeding of wildflower mixtures should not be excluded.
Takšna prepoved bo zagotovila višjo vrednost površine z ekološkim pomenom, kar bi se moralo kazati v spremenjeni vrednosti za utežni faktor za to vrsto površine.
Member States should be able to decide whether or not on buffer strips grazing and cutting for forage is allowed.
Omejena uporaba vložkov, ki so potrebni za pridelavo hitro rastočega panjevca, posredno koristno vpliva na biotsko raznovrstnost.
As regards hectares of agro-forestry, it should be clarified that the areas to be taken into account are the areas of arable land that are located in an area under an agro-forestry system that is still fulfilling the conditions under which it receives or received rural development support.
Zaradi tega bi morale države članice določiti pogoje, ki se uporabljajo za to vrsto površine z ekološkim pomenom, in sicer z opredelitvijo drevesnih vrst, ki se lahko uporabljajo, in pravil v zvezi z uporabo vložkov.
Member States that select those areas for the fulfilment of the ecological focus area obligation should take the biodiversity objective into account when establishing the additional conditions for receiving support for the establishment of agro-forestry systems in their rural development programmes.
Da bi se omogočilo izvajanje, ki je prilagojeno nacionalnim pogojem, ter za optimalno uporabo zmogljivosti naknadnih posevkov in travne ruše, da učinkovito absorbirajo preostali dušik z namenom, da se prepreči gola zemlja in razpršeno onesnaževanje podtalnice, bi morale države članice določiti datume za setev teh rastlin.
As regards strips of eligible hectares along forest edges, it should be up to the Member States to decide whether to establish a requirement of no cultivation which will avoid the use of inputs on a set strip adjacent to the forest in order to create a buffering transition to the bordering forest.
Naknadni posevki ali travne ruše bi morale nastati s setvijo mešanice vrst kmetijskih rastlin ali setvijo podsevkov trave za optimizacijo kmetijskih in okoljskih rezultatov v smislu biotske raznovrstnosti.
Such a requirement will provide a higher value of ecological focus area which should be reflected in a differentiated value for the weighting factor for this type of area.
Države članice lahko v področje uporabe dobrih kmetijskih in okoljskih pogojev 4, kakor so določeni v Prilogi II k Uredbi (EU) št. 1306/2013, dodajo datume, po katerih je dovoljeno mehansko uničenje naknadnih posevkov in travne ruše.
The limited use of inputs needed for the cultivation of short rotation coppice results in indirect benefits for biodiversity.
Kar zadeva površine s kmetijskimi rastlinami, ki vežejo dušik, bi morale države članice določiti pravila, ki bodo preprečila, da bi gojenje kmetijskih rastlin, ki vežejo dušik, na površinah z ekološkim pomenom vodilo do povečanja izpiranja dušika in poslabšanja kakovosti vode, kar ne bi bilo skladno s cilji Direktive Sveta 91/676/EGS [12] in Direktive Evropskega parlamenta in Sveta 2000/60/ES [13] ter bi ogrozilo cilj biotske raznovrstnosti.
For that purpose, Member States should lay down the conditions that apply to this type of ecological focus area, by specifying the list of tree species that may be used and the rules as regards the use of inputs.
Države članice bi morale vzpostaviti tudi seznam kmetijskih rastlin, ki vežejo dušik in za katere se šteje, da prispevajo k izboljšanju biotske razn ovrstnosti.
In order to allow an implementation that is adapted to national conditions and for an optimal use of the capacity of catch crops and green cover to effectively take up residual nitrogen and with a view to avoiding bare soil and diffuse pollution in groundwater, Member States should fix the dates for the sowing of such covers.
Za povečanje koristi površine z ekološkim pomenom na ornem zemljišču in za zagotovitev, da površine z ekološkim pomenom zajemajo odstotek iz člena 46(1) Uredbe (EU) št. 1307/2013, bi bilo treba v interesu učinkovitega upravljanja jasno določiti, da se pri izpolnjevanju zahteve po površini z ekološkim pomenom parcela ali krajinska značilnost ne sme šteti dvakrat v istem letu.
Catch crops or green covers should be established by sowing of a mixture of crop species or by under-sowing of grass in order to optimise the agronomic and environmental outcome in terms of biodiversity.
Določiti bi bilo treba tudi pravila glede določanja površin z namenom, da se pri izvajanju kmetijskih in okoljskih politik Unije ustvarijo sinergije.
Member States may establish in the scope of GAEC 4 as referred to in Annex II to Regulation (EU) No 1306/2013, the dates after which mechanical destruction of the catch crops and the green cover is allowed.
Za namen odločitve, ki jo sprejmejo države članice in ki kmetom omogoča, da polovico njihove individualne obveznosti glede površine z ekološkim pomenom izpolnijo prek skupinskega izvajanja, kot je določeno v členu 46(6) Uredbe (EU) št. 1307/2013, bi bilo treba uvesti pravila, ki bodo podobna pravilom o regionalnem izvajanju, glede značilnosti, ki se lahko uporabijo pri vzpostavitvi sosednjih površin z ekološkim pomenom za zagotovitev dodane vrednosti za okolje in prispevka k izboljšanju zelene infrastrukture.
As regards areas with nitrogen-fixing crop, Member States should lay down rules that will avoid that the growing of nitrogen-fixing crops on ecological focus areas would lead to increased nitrogen leaching and deteriorated water quality, which would not be compatible with the objectives of Council Directive 91/676/EEC [12] and Directive 2000/60/EC of the European Parliament and of the Council [13] and would compromise the biodiversity objective.
Pravila o merilih, ki jih morajo izpolnjevati kmetje, bi morala določati, da se njihova kmetijska gospodarstva nahajajo v neposredni bližini, hkrati pa bi morala ta pravila dopuščati dovolj prožnosti, da države članice lahko upoštevajo različne upravne strukture.
Member States should also establish the list of nitrogen-fixing crops that are considered to contribute to improving biodiversity.
Zaradi pravne jasnosti bi bilo treba določiti pravila o vsebini pisnega dogovora, ki se sklene med vsemi sodelujočimi z namenom, da se določijo pravice in obveznosti vsakega od njih.