natgillin/translations-raw huggingface dataset:
Waste management in the Union should be improved and transformed into sustainable material management, with a view to protecting, preserving and improving the quality of the environment, protecting human health, ensuring prudent, efficient and rational utilisation of natural resources, promoting the principles of the circular economy, enhancing the use of renewable energy, increasing energy efficiency, reducing the dependence of the Union on imported resources, providing new economic opportunities and contributing to long-term competitiveness.
Ravnanje z odpadki v Uniji bi bilo treba izboljšati in spremeniti v trajnostno ravnanje z materiali, in sicer zaradi varstva, ohranjanja in izboljševanja kakovosti okolja, varovanja zdravja ljudi, zagotavljanja skrbnega, učinkovitega in preudarnega izkoriščanja naravnih virov, spodbujanja načel krožnega gospodarstva, povečevanja rabe energije iz obnovljivih virov, povečevanja energetske učinkovitosti, zmanjševanja odvisnosti Unije od uvoženih virov, zagotavljanja novih gospodarskih priložnosti in prispevanja k dolgoročni konkurenčnosti.
In order to make the economy truly circular, it is necessary to take additional measures on sustainable production and consumption, by focusing on the whole life cycle of products in a way that preserves resources and closes the loop.
Da bi gospodarstvo postalo resnično krožno, je treba sprejeti dodatne ukrepe za trajnostno proizvodnjo in porabo z osredotočanjem na ves življenjski cikel proizvodov na način, ki ohranja vire in zapre zanko.
The more efficient use of resources would also bring substantial net savings for Union businesses, public authorities and consumers, while reducing total annual greenhouse gas emissions.
Učinkovitejša raba virov bi pripomogla tudi k znatnim neto prihrankom za podjetja, javne organe in potrošnike v Uniji, obenem pa bi pomagala zmanjšati skupne letne emisije toplogrednih plinov.
Improving the efficiency of resource use and ensuring that waste is valued as a resource can contribute to reducing the Union’s dependence on the import of raw materials and facilitate the transition to more sustainable material management and to a circular economy model.
Izboljšanje učinkovitosti rabe virov in zagotavljanje, da se odpadki obravnavajo kot vir, lahko prispevata k zmanjšanju odvisnosti Unije od uvoza surovin in olajšata prehod k trajnejšemu ravnanju z materiali in modelu krožnega gospodarstva.
That transition should contribute to the smart, sustainable and inclusive growth goals set out in the Europe 2020 strategy and create important opportunities for local economies and stakeholders, while helping to increase synergies between the circular economy and energy, climate, agriculture, industry and research policies as well as bringing benefits to the environment in terms of greenhouse gas emission savings and to the economy.
Ta prehod bi moral prispevati k doseganju ciljev pametne, trajnostne in vključujoče rasti iz strategije Evropa 2020 in ustvariti pomembne priložnosti za lokalna gospodarstva in deležnike, obenem pa prispevati k povečanju sinergije med krožnim gospodarstvom in energetsko, podnebno, kmetijsko, industrijsko in raziskovalno politiko ter koristiti okolju v smislu prihrankov emisij toplogrednih plinov in koristiti gospodarstvu.
The targets laid down in Directive 2008/98/EC of the European Parliament and of the Council for preparing for re-use and recycling of waste should be increased to make them better reflect the Union’s ambition to move to a circular economy.
Cilje priprave za ponovno uporabo in recikliranja odpadkov, določene v Direktivi 2008/98/ES Evropskega parlamenta in Sveta, bi bilo treba zvišati, da bi bolje odražali prizadevanje Unije za prehod na krožno gospodarstvo.
The coherence between Directive 2008/98/EC and related Union legislative acts such as Directive 2009/28/EC of the European Parliament and of the Council and Regulation (EC) No 1907/2006 of the European Parliament and of the Council needs to be ensured.
Zagotoviti je treba skladnost Direktive 2008/98/ES s povezanimi zakonodajnimi akti Unije, kot sta Direktiva 2009/28/ES Evropskega parlamenta in Sveta in Uredba (ES) št. 1907/2006 Evropskega parlamenta in Sveta.
Many Member States have not yet completely developed the necessary waste management infrastructure.
Številne države članice še niso v celoti razvile potrebne infrastrukture za ravnanje z odpadki.
It is therefore essential to set clear long-term policy objectives in order to guide measures and investments, notably by preventing the creation of structural overcapacities for the treatment of residual waste and lock-ins of recyclable materials at the lower levels of the waste hierarchy.
Zato je bistvenega pomena, da se določijo jasni dolgoročni cilji politike za usmerjanje ukrepov in naložb, zlasti s preprečevanjem ustvarjanja strukturnih presežkov zmogljivosti za obdelavo preostankov odpadkov in izgube materialov, ki so primerni za recikliranje, na nižjih ravneh hierarhije ravnanja z odpadki.
Municipal waste constitutes approximately between 7 and 10 % of the total waste generated in the Union.
Komunalni odpadki predstavljajo med 7 in 10 % vseh odpadkov, ki nastanejo v Uniji.
That waste stream, however, is amongst the most complex ones to manage, and the way it is managed generally gives a good indication of the quality of the overall waste management system in a country.
Vendar je ta tok odpadkov med najzahtevnejšimi, kar zadeva ravnanje z odpadki, in način ravnanja z njim v splošnem dobro odraža kakovost celotnega sistema ravnanja z odpadki v državi.
The challenges of municipal waste management result from its highly complex and mixed composition, direct proximity of the generated waste to citizens, a very high public visibility and its impact on the environment and human health.
Izzivi, povezani z ravnanjem s komunalnimi odpadki, so posledica njihove kompleksne in mešane sestave, neposredne bližine nastalih odpadkov državljanom, zelo visoke stopnje prepoznavnosti v javnosti in njihovega vpliva na okolje in zdravje ljudi.
As a result, the management of municipal waste requires a highly complex system including an efficient collection scheme, an effective sorting system and a proper tracing of waste streams, the active engagement of citizens and businesses, an infrastructure adjusted to the specific waste composition, and an elaborate financing system.
Zato se za ravnanje s komunalnimi odpadki zahteva zelo kompleksen sistem, vključno z učinkovitim sistemom zbiranja, učinkovitim sistemom za sortiranje in primernim sledenjem tokovom odpadkov, dejavnim sodelovanjem državljanov in podjetij, infrastrukturo, prilagojeno specifični sestavi odpadkov, ter dodelanim sistemom financiranja.
Countries which have developed efficient municipal waste management systems generally perform better in overall waste management, including the attainment of the recycling targets.
Države, ki so razvile učinkovit sistem ravnanja s komunalnimi odpadki, na splošno dosegajo boljše rezultate pri celotnem ravnanju z odpadki, vključno z doseganjem ciljev recikliranja.
Experience has shown that, irrespective of the allocation of responsibilities for waste management between public and private actors, waste management systems can help to achieve a circular economy and that the decision on the allocation of responsibilities frequently depends on geographical and structural conditions.
Izkušnje so pokazale, da lahko sistemi ravnanja z odpadki ne glede na to, kako so pristojnosti za ravnanje z odpadki razporejene med javne in zasebne akterje, pripomorejo k vzpostavitvi krožnega gospodarstva, in da je razporeditev pristojnosti pogosto odvisna od geografskih in strukturnih pogojev.
The rules laid down in this Directive allow for waste management systems where the municipalities have the general responsibility for collecting municipal waste, for systems where such services are contracted out to private operators, or for any other type of allocation of responsibilities between public and private actors.
Pravila iz te direktive dopuščajo vzpostavitev sistemov ravnanja z odpadki, v katerih so občine splošno pristojne za zbiranje komunalnih odpadkov, sistemov, v katerih te storitve opravljajo zasebni izvajalci, ali kakršnih koli drugih sistemov, v katerih so pristojnosti razdeljene med javne in zasebne akterje.
The choice for any such systems, and whether or not to change them, remains the responsibility of Member States.
Izbira enega od teh sistemov in odločitev o tem, ali jih je treba spremeniti, ostajata v pristojnosti držav članic.
Plant-based substances from the agri-food industry and food of non-animal origin no longer intended for human consumption which are destined for oral animal feeding should, in order to avoid duplication of rules, be excluded from the scope of Directive 2008/98/EC if in full compliance with Union feed legislation.
Snovi rastlinskega izvora iz agroživilske industrije in živila neživalskega izvora, ki niso več namenjena za prehrano ljudi, ki so namenjena za oralno hranjenje živali, bi morala biti, če so v celoti skladna z zakonodajo Unije o krmi, izločena iz področja uporabe Direktive 2008/98/ES, da bi se tako izognili podvajanju pravil.
Directive 2008/98/EC should therefore not apply to those products and substances when used for feed, and the scope of that Directive needs to be clarified accordingly.
Direktiva 2008/98/ES se zato ne bi smela uporabljati za te proizvode in snovi, če se uporabljajo za krmo, področje uporabe navedene direktive pa je treba ustrezno pojasniti.
Without prejudice to other Union provisions applicable in the field of animal nutrition, animal by-products destined to be used as feed materials in accordance with Regulation (EC) No 767/2009 of the European Parliament and of the Council are already excluded from the scope of Directive 2008/98/EC to the extent that they are covered by other Union legislation.
Brez poseganja v druge veljavne predpise Unije na področju prehrane živali so živalski stranski proizvodi, ki so v skladu z Uredbo (ES) št. 767/2009 Evropskega parlamenta in Sveta namenjeni uporabi kot posamična krmila, že izločeni iz področja uporabe Direktive 2008/98/ES, če so zajeti v drugi zakonodaji Unije.
Definitions of non-hazardous waste, municipal waste, construction and demolition waste, food waste, material recovery, backfilling and extended producer responsibility scheme need to be included in Directive 2008/98/EC so that the scope of these concepts is clarified.
Opredelitve pojmov nenevaren odpadek, komunalni odpadki, gradbeni odpadki in odpadki iz rušenja objektov, odpadna hrana, snovna predelava, zasipanje in sistem razširjene odgovornosti proizvajalca je treba vključiti v Direktivo 2008/98/ES, da se pojasni področje uporabe teh pojmov.
To ensure that preparing for re-use and recycling targets are based on reliable and comparable data and to enable a more effective monitoring of progress in attaining those targets, the definition of municipal waste in Directive 2008/98/EC should be in line with the definition used for statistical purposes by Eurostat and the Organisation for Economic Cooperation and Development (OECD), on the basis of which Member States have been reporting data for several years.
Za zagotovitev, da cilji priprave za ponovno uporabo in recikliranja temeljijo na zanesljivih in primerljivih podatkih, in da bi se omogočilo učinkovitejše spremljanje napredka pri doseganju teh ciljev, bi morala biti opredelitev pojma komunalni odpadki v Direktivi 2008/98/ES skladna z opredelitvami tega pojma, ki jih v statistične namene uporabljata Eurostat in Organizacija za gospodarsko sodelovanje in razvoj (OECD), na podlagi katerih države članice svoje podatke sporočajo že nekaj let.
Municipal waste is defined as waste from households and waste from other sources, such as retail, administration, education, health services, accommodation and food services, and other services and activities, which is similar in nature and composition to waste from households.
Komunalni odpadki so opredeljeni kot odpadki iz gospodinjstev in odpadki iz drugih virov, kot so trgovina na drobno, uprava, izobraževanje, zdravstvene storitve, storitve nastanitev in prehrane ter druge storitve in dejavnosti, ki so po naravi in sestavi podobni odpadkom iz gospodinjstev.
Therefore, municipal waste includes, inter alia, waste from park and garden maintenance, such as leaves, grass and tree clippings, and waste from market and street cleaning services, such as the content of litter containers and sweepings except materials such as sand, rock, mud or dust.
Zato med komunalne odpadke med drugim spadajo odpadki, ki nastanejo pri vzdrževanju parkov in vrtov, kot so odpadli listi, pokošena trava in odpadki, ki nastanejo pri obrezovanju dreves, ter odpadki, ki nastanejo pri čiščenju tržnic in cest, kot so vsebina košev za smeti in odpadki, ki nastanejo pri pometanju, razen materialov, kot so pesek, kamenje, blato ali prah.
Member States are to ensure that waste from large commerce and industry which is not similar to waste from households is not included in the scope of municipal waste.
Države članice morajo zagotoviti, da odpadki velikih trgovskih in industrijskih subjektov, ki niso podobni odpadkom iz gospodinjstev, niso vključeni v področje uporabe komunalnih odpadkov.
Waste from production, agriculture, forestry, fishing, construction and demolition, septic tanks and sewage network and treatment, and end-of-life vehicles are excluded from the scope of municipal waste.
Odpadki iz proizvodnje, kmetijstva, gozdarstva, ribištva, gradbeni odpadki in odpadki iz rušenja objektov, greznic, kanalizacije in čiščenja odplak ter izrabljenih vozil so izključeni iz področja uporabe komunalnih odpadkov.
Waste falling under other chapters of that list is not to be considered as municipal waste except in cases where municipal waste undergoes treatment and is assigned codes listed in Chapter 19 of that list.
Opredelitev pojma komunalni odpadki v tej direktivi je uvedena z namenom, da se določijo področje uporabe ciljev priprave za ponovno uporabo in recikliranja in pravila za njihov izračun.
Member States may use relevant categories in that list for statistical purposes.
Neodvisna je od tega, ali ima izvajalec ravnanja z odpadki status javnega ali zasebnega subjekta, in zato vključuje odpadke iz gospodinjstev in drugih virov, s katerimi upravljajo občine – oz. se z njimi upravlja v njihovem imenu – ali neposredno zasebni izvajalci.
The definition of municipal waste in this Directive is introduced for the purposes of determining the scope of application of the preparing for re-use and recycling targets and their calculation rules.
Opredelitev pojma gradbeni odpadki in odpadki iz rušenja objektov se nanaša na odpadke, ki na splošno nastanejo pri gradnji in rušenju, vključuje pa tudi tiste odpadke, ki nastanejo pri manjših gradbenih in rušilnih delih, ki jih ljudje opravijo sami v zasebnih gospodinjstvih.
It is neutral with regard to the public or private status of the operator managing the waste and therefore includes waste from households and other sources that is managed by or on behalf of municipalities or directly by private operators.
Gradbene odpadke in odpadke iz rušenja objektov bi bilo treba razumeti kot vrste odpadkov iz poglavja 17 iz seznama odpadkov iz Sklepa 2014/955/EU v različici, veljavni na dan 4. julija 2018.
While the definition of construction and demolition waste refers to waste that results from construction and demolition activities in a general way, it also includes waste arising from minor do-it-yourself construction and demolition activities within private households.
Vključiti bi bilo treba opredelitev pojma snovna predelava, da bi tako zaobjeli oblike predelave, ki niso energetska predelava, in niso ponovna predelava odpadkov v snovi, ki se uporabljajo kot gorivo ali druga sredstva za pridobivanje energije.
Construction and demolition waste should be understood as corresponding to the types of waste included in Chapter 17 of the list of waste established by Decision 2014/955/EU in the version in force on 4 July 2018.
Vključuje pripravo za ponovno uporabo, recikliranje in zasipanje ter druge oblike snovne predelave, kot je ponovna predelava odpadkov v sekundarne surovine za inženirske namene pri gradnji cest ali druge infrastrukture.
A definition of material recovery should be introduced to cover forms of recovery other than energy recovery and other than the reprocessing of waste into materials used as fuels or other means to generate energy.
Odvisno od posebnih dejanskih okoliščin takšna ponovna predelava lahko spada v opredelitev pojma recikliranje, če uporaba materialov temelji na ustreznem nadzoru kakovosti in izpolnjuje vse ustrezne standarde, norme, specifikacije in z okoljem in varstvom zdravja povezane zahteve, ki veljajo za specifično uporabo.
It includes preparing for re-use, recycling and backfilling and other forms of material recovery such as the reprocessing of waste into secondary raw materials for engineering purposes in construction of roads or other infrastructure.
Vključiti bi bilo treba opredelitev pojma zasipanje, da bi pojasnili, da pomeni vsakršen postopek predelave primernih nenevarnih odpadkov za namene pridobivanja zemljišč na območjih izkopavanja ali za inženirske namene pri urejanju krajine.
Depending on the specific factual circumstances, such reprocessing can fulfil the definition of recycling if the use of materials is based on proper quality control and meets all relevant standards, norms, specifications and environmental and health protection requirements for the specific use.
Odpadke, ki se uporabljajo pri zasipanju, bi bilo treba omejiti na količino, nujno potrebno za uresničitev teh namenov.
A definition of backfilling should be introduced to clarify that it means any recovery operation of suitable non-hazardous waste for the purposes of reclamation in excavated areas or for engineering purposes in landscaping.
Vključiti bi bilo treba opredelitev pojma sistem razširjene odgovornosti proizvajalca, da bi pojasnili, da pomeni sklop ukrepov, ki jih sprejmejo države članice, s katerimi od proizvajalcev proizvodov zahtevajo, da nosijo finančno ali finančno in organizacijsko odgovornost za ravnanja v fazi odpadkov v življenjskem ciklu proizvoda, vključno z ločenim zbiranjem, sortiranjem in postopki obdelave.
The waste used for backfilling should be limited to the amount strictly necessary to achieve those purposes.
Ta obveznost lahko zajema tudi organizacijsko odgovornost in odgovornost prispevati k preprečevanju odpadkov ter k ponovni uporabljivosti proizvodov in njihovi reciklabilnosti.
A definition of extended producer responsibility scheme should be introduced to clarify that it means a set of measures taken by Member States requiring producers of products to bear financial or financial and organisational responsibility for the management of the waste stage of a product’s life cycle including separate collection, sorting and treatment operations.
Proizvajalci proizvodov lahko obveznosti iz sistema razširjene odgovornosti proizvajalca izpolnjujejo posamično ali skupinsko.
That obligation can also include organisational responsibility and a responsibility to contribute to waste prevention and to the reusability and recyclability of products.
Da bi prispevale k doseganju ciljev iz Direktive 2008/98/ES, bi morale države članice uporabiti ekonomske instrumente in druge ukrepe za spodbujanje uporabe hierarhije ravnanja z odpadki, kot so tisti, navedeni v Prilogi IVa, ki med drugim vključujejo dajatve za odlaganje na odlagališča in sežiganje, sisteme „ plačaj, kolikor zavržeš“, sisteme razširjene odgovornosti proizvajalca, lažje doniranje hrane in spodbude za lokalne organe, ali druge ustrezne instrumente in ukrepe.
Producers of products can fulfil the obligations of the extended producer responsibility scheme individually or collectively.
Za spodbujanje trajnostne rabe virov in industrijske simbioze bi morale države članice sprejeti ustrezne ukrepe za olajšanje tega, da se snov ali predmet, ki nastane pri proizvodnem procesu, pri čemer glavni namen tega procesa ni proizvodnja te snovi ali predmeta, prizna za stranski proizvod, če se spoštujejo harmonizirani pogoji, uvedeni na ravni Unije.
In order to contribute to achieving the objectives laid down in Directive 2008/98/EC, Member States should make use of economic instruments and other measures to provide incentives for the application of the waste hierarchy such as those indicated in Annex IVa, which includes, inter alia, landfill and incineration charges, pay-as-you-throw schemes, extended producer responsibility schemes, facilitation of food donation, and incentives for local authorities, or other appropriate instruments and measures.
Na Komisijo bi bilo treba prenesti pooblastilo, da sprejeme izvedbene akte, s katerimi določi podrobna merila za uporabo statusa stranskega proizvoda, pri čemer bi morala nameniti prednost ponovljivim praksam industrijske simbioze.
In order to promote sustainable use of resources and industrial symbiosis, Member States should take appropriate measures to facilitate the recognition as a by-product of a substance or an object resulting from a production process the primary aim of which is not the production of that substance or object if the harmonised conditions established at Union level are respected.
Da bi izvajalcem dejavnosti na trgih sekundarnih surovin zagotovile več varnosti glede tega, ali imajo snovi ali predmeti status odpadka ali ne, ter za spodbujanje enakih konkurenčnih pogojev, je pomembno, da države članice sprejmejo ustrezne ukrepe, s katerimi zagotovijo, da za odpadek, ki je bil predelan, velja, da preneha biti odpadek, če izpolnjuje pogoje iz člena 6(1) Direktive 2008/98/ES, kakor je bila spremenjena s to direktivo.
The Commission should be empowered to adopt implementing acts in order to establish detailed criteria on the application of the by-product status, prioritising replicable practices of industrial symbiosis.
Taki ukrepi lahko vključujejo sprejetje zakonodaje za prenos teh pogojev, podprte s postopki za njihovo izvajanje, kot so oblikovanje meril za prenehanje statusa odpadka, ki se nanašajo na specifičen material in specifično uporabo, smernice, odločitve za vsak posamezen primer in drugi postopki za ad hoc uporabo harmoniziranih pogojev, uvedenih na ravni Unije.
In order to provide operators in markets for secondary raw materials with more certainty as to the waste or non-waste status of substances or objects and to promote a level playing field, it is important that Member States take appropriate measures to ensure that waste that has undergone a recovery operation is considered to have ceased to be waste if it complies with all the conditions laid down in Article 6(1) of Directive 2008/98/EC as amended by this Directive.
Taki ukrepi bi morali vsebovati določbe o izvrševanju, da se preveri, da je odpadek, za katerega se šteje, da ni več odpadek, ker je šel skozi postopek predelave, skladen s pravom Unije na področju odpadkov, kemikalij in proizvodov, pri čemer je treba dati prednost zlasti tokovom odpadkov, ki zaradi svoje narave in obsega predstavljajo večje tveganje za zdravje ljudi in okolje, odpadkom, ki se predelujejo v inovativnih postopkih predelave, ali odpadkom, ki so predelani za namene nadaljnje uporabe v drugih državah članicah.
Such measures may include the adoption of legislation transposing those conditions supported by procedures for their implementation, such as the establishment of material and application-specific end-of-waste criteria, guidance documents, case-by-case decisions and other procedures for the ad hoc application of the harmonised conditions established at Union level.
Ukrepi lahko vključujejo tudi določitev zahteve za izvajalce, ki predelujejo odpadke, ali za imetnike predelanih odpadnih materialov, da bi tako dokazali skladnost s pogoji iz člena 6(1) Direktive 2008/98/ES, kakor je bila spremenjena s to direktivo.