natgillin/translations-raw huggingface dataset:
According to the Swedish authorities, the lower pH level in Swedish soils may lead to higher uptake of cadmium in crops, which in turn can lead to higher exposure of the population, as exposure depends to a great extent on the intake of cadmium through food, above all food of plant origin.
Po trditvah švedskih organov lahko nižje vrednosti pH švedskih tal vodijo do višjega vnosa kadmija v poljščine, kar lahko nato vodi do večje izpostavljenosti prebivalstva, saj je izpostavljenost večinoma odvisna od vnosa kadmija s hrano, predvsem rastlinskega izvora.
The Commission requested a further opinion of SCHER on whether the risks to human health identified by the Swedish authorities are specific to Sweden and have arisen after the adoption of Regulation (EC) No 2003/2003 [16].
Komisija je ZOZOT prosila za nadaljnje mnenje o tem, ali so tveganja za zdravje ljudi, ki so jih ugotovili švedski organi, specifična za Švedsko in ali so se pojavila po sprejetju Uredbe (ES) št. 2003/2003 [16].
With regard to the question whether the situation in Sweden is different compared to other parts of Europe, SCHER agreed that soil pH is on average lower in Sweden than in other parts of Europe.
Glede vprašanja, ali so razmere na Švedskem v primerjavi z ostalimi deli Evrope drugačne, se je ZOZOT strinjal, da je pH tal na Švedskem v povprečju nižji kot v drugih delih Evrope.
However, as cadmium removal from the soil by leaching is also increasing with lower soil pH value, the net cadmium soil accumulation is lower in Sweden than in most parts of Europe at comparable cadmium concentration and fertiliser application rates.
Ker pa se odstranjevanje kadmija iz tal z izpiranjem z nižjo vrednostjo pH tudi povečuje, je neto kopičenje kadmija v tleh na Švedskem nižje kot v večjem delu Evrope pri primerljivi koncentraciji kadmija in stopnji uporabe gnojil.
SCHER agrees that the lower pH increases cadmium bioavailability and uptake by crops, hence that the soil cadmium availability to wheat is somewhat larger than in most European countries.
ZOZOT se strinja, da nižji pH povečuje biološko dostopnost kadmija in njegov vnos v poljščine, zato je dostopnost kadmija v tleh za pšenico nekoliko večja kot v večini evropskih držav.
However, SCHER notes that if that low pH is maintained, the future trends in crop cadmium concentrations are smaller (lower increase) in Sweden compared to most other trends in Europe because soil cadmium increases at a lower rate at equal input.
Vendar navaja, da je na Švedskem v primerjavi z večino drugih gibanj po Evropi prihodnje gibanje koncentracij kadmija v poljščinah manjše (manjše povečanje), če se ohranja nizek pH, saj kadmij v tleh pri enakem vnosu narašča počasneje.
With regard to dietary exposure to cadmium, SCHER concludes that the Swedish report does not provide data suggesting that dietary cadmium exposure is larger in Sweden than in the rest of Europe neither at the mean nor at the upper percentiles of exposure.
Glede izpostavljenosti kadmiju s hrano ZOZOT ugotavlja, da v švedskem poročilu ni podatkov, iz katerih bi bilo razvidno, da je izpostavljenost kadmiju s hrano večja na Švedskem kot v ostali Evropi, in sicer niti pri povprečju niti pri zgornjih percentilih izpostavljenosti.
Recent trends do not suggest an increasing trend in dietary exposure, including body burden cadmium in the general population.
Iz nedavnih gibanj ni razvidno povečanje izpostavljenosti s hrano, vključno z obremenitvijo organizma s kadmijem pri vsem prebivalstvu.
Lastly, SCHER notes that the Swedish report provides evidence that effects of cadmium on human health in Sweden can be noted at a body burden of cadmium that is lower than that reported before, however it does not provide evidence that the Swedish population is more sensitive or became more sensitive to cadmium than those in other European countries.
ZOZOT še ugotavlja, da so v švedskem poročilu dokazi, da je mogoče vpliv kadmija na zdravje ljudi na Švedskem opaziti pri nižji obremenitvi organizma s kadmijem kot v prejšnjih poročilih, kar pa ne dokazuje, da je švedsko prebivalstvo bolj občutljivo ali da je postalo bolj občutljivo na kadmij kot prebivalstvo v drugih evropskih državah.
Overall, SCHER concludes that the Swedish report contains a detailed and updated assessment of long-term effects of cadmium from fertilisers on human health via the food chain.
ZOZOT na splošno ugotavlja, da švedsko poročilo vsebuje podrobno in posodobljeno oceno dolgotrajnih vplivov kadmija iz gnojil na zdravje ljudi prek prehranske verige.
SCHER notes that the report does not provide convincing arguments to show that the Swedish case is a unique one or that data which appeared after the adoption of Regulation (EC) No 2003/2003 suggest specific reasons for additional concern.
ZOZOT navaja, da v poročilu ni prepričljivih argumentov, ki bi kazali, da je švedski primer edinstven, ali da so podatki, ki so se pojavili po sprejetju Uredbe (ES) št. 2003/2003, poseben razlog za dodatno skrb.
In conclusion, the Commission considers that the Kingdom of Sweden has not provided justification for the intended national measure with regard to the maximum content of cadmium in fertilisers on the basis of new scientific evidence relating to the protection of the environment on grounds of a specific problem in Sweden having arisen after the adoption of Regulation (EC) No 2003/2003.
Komisija meni, da Kraljevina Švedska ni utemeljila načrtovanega nacionalnega ukrepa v zvezi z največjo dovoljeno vsebnostjo kadmija v gnojilih na podlagi novih znanstvenih spoznanj o varstvu okolja zaradi problema, ki je specifičen za Švedsko in je nastal po sprejetju Uredbe (ES) št. 2003/2003.
The Commission notes that the Swedish notification does not refer to the protection of the working environment as a ground for introducing the notified measure.
Komisija navaja, da v švedski priglasiti uvedba priglašenega ukrepa ni utemeljena z varstvom delovnega.
Article 114(5) TFEU requires that, if a Member State deems it necessary to introduce national provisions in derogation from Union harmonisation measures, the national provisions must be justified by new scientific evidence relating to the protection of the environment or the working environment, there must be a problem specific to the State making the request, and the problem must have arisen after the adoption of the harmonisation measure.
Če država članica meni, da je treba z odstopanjem od usklajevalnih ukrepov Unije uvesti nacionalne določbe, morajo biti nacionalne določbe v skladu s členom 114(5) PDEU utemeljene z novimi znanstvenimi spoznanji o varstvu okolja ali delovnega okolja ter mora obstajati problem, ki je specifičen za državo članico, ki je predložila zahtevo, in je posledica sprejetja usklajevalnega ukrepa.
In this case, after having examined the Swedish request, the Commission considers that the Kingdom of Sweden has not provided new scientific evidence relating to the protection of the environment or working environment demonstrating that there is a specific problem within its territory which arose following the adoption of Regulation (EC) No 2003/2003 relating to fertilisers, and which makes it necessary to introduce the notified national measures.
Komisija v tej zadevi po proučitvi švedskega zahtevka meni, da Kraljevina Švedska ni zagotovila novih znanstvenih spoznanj o varstvu okolja ali delovnega okolja, s katerimi bi dokazala, da obstaja specifičen problem na njenem ozemlju, ki je nastal po sprejetju Uredbe (ES) št. 2003/2003 o gnojilih, in zaradi katerega je treba sprejeti priglašene nacionalne ukrepe.
Consequently, the request from the Kingdom of Sweden for introducing national measures to lower the content of cadmium allowed in phosphorous fertilisers to a maximum level of 46 grams of cadmium per tonne of phosphorous does not fulfil the conditions set out in Article 114(5).
Zato zahtevek Kraljevine Švedske za uvedbo nacionalnih ukrepov, s katerimi bi se znižala dovoljena vsebnost kadmija v fosfornih gnojilih na največ 46 gramov kadmija na tono fosforja, ne izpolnjuje pogojev iz člena 114(5).
Under Article 114(6) of the EC Treaty, the Commission is either to approve or reject the draft national provisions in question after verifying whether or not they are a means of arbitrary discrimination or a disguised restriction to trade between Member States, and whether or not they shall constitute an obstacle to the functioning of the internal market.
Komisija v skladu s členom 114(6) Pogodbe ES odobri ali zavrne zadevne osnutke nacionalnih določb, potem ko preveri, ali so morda sredstvo samovoljne diskriminacije ali prikrita omejitev trgovine med državami članicami in ali ovirajo delovanje notranjega trga.
Since the request made by the Kingdom of Sweden does not fulfil the basic conditions set out in Article 114(5), there is no need for the Commission to verify the conditions in Article 114(6).
Ker zahtevek Kraljevine Švedske ne izpolnjuje osnovnih pogojev iz člena 114(5), Komisiji ni treba preveriti pogojev iz člena 114(6).
In the light of the foregoing, it can be concluded that the request of the Kingdom of Sweden for introducing national provisions derogating from Regulation (EC) No 2003/2003 is admissible but does not fulfil the conditions set out in Article 114(5) TFEU, as Sweden did not provide new scientific evidence relating to the protection of the environment on grounds of a problem specific to their territory arising after the adoption of Regulation (EC) No 2003/2003.
Ob upoštevanju navedenega je mogoče sklepati, da je bil zahtevek Kraljevine Švedske za uvedbo nacionalnih določb, ki odstopajo od Uredbe (ES) št. 2003/2003, dopusten, vendar ne izpolnjuje pogojev iz člena 114(5) PDEU, saj Švedska ni zagotovila novih znanstvenih spoznanj o varstvu okolja zaradi problema, ki je specifičen za njeno ozemlje in je nastal po sprejetju Uredbe (ES) št. 2003/2003.
The Commission therefore considers that the notified national provisions cannot be approved in accordance with Article 114(6) TFEU,
Komisija zato meni, da priglašenih nacionalnih določb ni mogoče odobriti v skladu s členom 114(6) PDEU –
The envisaged national provisions intended to lower the content of cadmium allowed in phosphorous fertilisers from the current maximum level of 100 grams of cadmium per tonne of phosphorus to a level of 46 grams, which the Kingdom of Sweden notified to the Commission on 17 October 2011, are rejected.
Načrtovane nacionalne določbe za znižanje trenutno največje dovoljene vsebnosti kadmija v fosfornih gnojilih s sedanjih 100 gramov kadmija na tono fosforja na 46 gramov, ki jih je Kraljevina Švedska priglasila Komisiji 17. oktobra 2011, se zavrnejo.
Swedish Code of Statutes (SFS Svensk Författningssamling) of 14 July 1998.
Švedska zbirka predpisov (SFS Svensk Författningssamling) z dne 14. julija 1998.
Swedish Code of Statutes (SFS Svensk Författningssamling) of 4 June 2009.
Švedska zbirka predpisov (SFS Svensk Författningssamling) z dne 4. junija 2009.
Commission Decision 2012/230/EU of 18 April 2012 extending the period referred to in Article 114(6) of the Treaty on the Functioning of the European Union in relation to national provisions concerning the maximum admissible content of cadmium in fertilisers notified by the Kingdom of Sweden pursuant to Article 114(5) of the TFEU (OJ L 116, 28.4.2012, p. 29).
Sklep Komisije 2012/230/EU z dne 18. aprila 2012 o podaljšanju roka iz člena 114(6) Pogodbe o delovanju Evropske unije v zvezi z nacionalnimi določbami glede največje dovoljene vsebnosti kadmija v gnojilih, ki jih je v skladu s členom 114(5) PDEU uradno sporočila Kraljevina Švedska (UL L 116, 28.4.2012, str. 29).
Opinions of SCHER are available at: http://ec.europa.eu/health/scientific_committees/environmental_risks/opinions/index_en.htm#id5
Mnenja ZOZOT so na voljo na: http://ec.europa.eu/health/scientific_committees/environmental_risks/opinions/index_en.htm#id5
SCHER adopted its opinion on 27 February 2012 [9].
ZOZOT je o tem sprejel mnenje 27. februarja 2012 [9].
SCHER concluded that the risk assessment report prepared by the Swedish authorities was of good scientific quality and that in general the scenarios studied were appropriate and most parameter values used in the scenarios acceptable.
Ugotovil je, da je poročilo o oceni tveganja švedskih organov z znanstvenega vidika kakovostno, da so obravnavani scenariji na splošno primerni in da je večina uporabljenih vrednosti parametrov v scenarijih sprejemljiva.
To support their request for lowering the existing limit value in Sweden, the Swedish authorities have conducted a new risk assessment of cadmium in the Swedish environment, which was finalised in January 2011.
Švedski organi so svoj zahtevek po znižanju veljavne mejne vrednosti na Švedskem utemeljili z novo oceno tveganja za kadmij v švedskem okolju, ki so jo zaključili januarja 2011.
It compares the predicted no effect concentrations (PNECs) for organisms representative for various environmental compartments with the cadmium concentrations in the Swedish environment taking on the basis of various scenarios for cadmium input from fertilisers and other sources.
V njej primerjajo predvidene koncentracije brez učinka za organizme, ki predstavljajo različne dele okolja, s koncentracijami kadmija v švedskem okolju na podlagi različnih scenarijev vnosa kadmija iz gnojil in drugih virov.
SCHER notes that the Swedish report itself (summary of Annex IV) supports SCHER’s conclusion as it states: ‘It was difficult to unambiguously show whether there are specific conditions in Sweden that make Swedish soils more vulnerable to Cd input than those in central Europe. However, pH is a major factor that regulates the uptake of cadmium from soils to crops and pH in Swedish soil appears to be around one pH unit lower than the general average for Europe. This is probably related to the scarcity of lime-bearing bedrock in Sweden. Swedish wheat also contains cadmium in levels that are comparable to those in many other European countries, in spite of the fact that cadmium concentrations in Swedish soils are relatively low’. SCHER comments that while input data on atmospheric deposition have been updated in the Swedish report, the scenarios for mass balance calculation were already included in the scenarios considered in the opinion of the CSTEE of 2002, and there is no new information suggesting that these would not be applicable anymore.
ZOZOT ugotavlja, da švedsko poročilo (povzetek Priloge IV) podpira ugotovitve tega odbora, saj je v njem navedeno: „Težko je bilo nedvoumno pokazati, ali na Švedskem obstajajo specifične razmere, zaradi katerih so švedska tla bolj ranljiva na vnos Cd kot tista v Srednji Evropi. Vendar je pH najpomembnejši dejavnik, ki ureja vnos kadmija iz tal v poljščine, in zdi se, da je pH švedskih tal za približno eno enoto pH nižji od splošnega povprečja za Evropo. To je verjetno povezano s pomanjkanjem apnenčaste kamninske podlage na Švedskem. Švedska pšenica vsebuje ravni kadmija, ki so primerljive s tistimi v mnogih drugih evropskih državah, kljub dejstvu, da so koncentracije kadmija relativno nizke.“ Kljub temu, da so vhodni podatki za atmosfersko depozicijo v švedskem poročilu posodobljeni, ZOZOT pojasnjuje, da so bili scenariji za izračun masne bilance že vključeni v scenarije, obravnavane v mnenju Znanstvenega odbora za strupenost, strupenost za ekosisteme in okolje iz leta 2002, ter da ni novih informacij, ki bi kazale, da ti niso več veljavni.
establishing the ecological criteria for the award of the EU Ecolabel for Industrial and Institutional Automatic Dishwasher Detergents
o okoljskih merilih za podeljevanje znaka EU za okolje detergentom za strojno pomivanje posode za uporabo v industriji in ustanovah
(notified under document C(2012) 8054)
(notificirano pod dokumentarno številko C(2012) 8054)
Under Regulation (EC) No 66/2010, the EU Ecolabel may be awarded to those products with a reduced environmental impact during their entire life cycle.
V skladu z Uredbo (ES) št. 66/2010 se lahko znak EU za okolje podeli proizvodom, ki imajo zmanjšan vpliv na okolje v celotnem življenjskem krogu.
Regulation (EC) No 66/2010 provides that specific EU Ecolabel criteria are to be established according to product groups.
Uredba (ES) št. 66/2010 določa, da se uvedejo posebna merila za podelitev znaka EU za okolje po skupinah proizvodov.
The new criteria, as well as the related assessment and verification requirements, should be valid for four years from the date of adoption of this Decision.
Nova merila ter z njimi povezane zahteve za ocenjevanje in preverjanje bi morala veljati štiri leta od datuma sprejetja tega sklepa.
The product group ‘Industrial and Institutional Automatic Dishwasher Detergents’ shall comprise single and multi-component dishwasher detergents, rinse and pre-soaks, designed for use in professional dishwashers.
Skupina proizvodov „detergenti za strojno pomivanje posode za uporabo v industriji in ustanovah“ zajema eno- in večkomponentne detergente za strojno pomivanje, izpiranje in predpomivanje posode za profesionalne pomivalne stroje.
The following products are excluded from the scope of this product group: consumer automatic dishwasher detergents, detergents intended to be used in washers of medical devices or in special machines for cleaning industrial equipment, including in special machines for the food industry.
V to skupino proizvodov se ne uvrščajo naslednji proizvodi: detergenti za strojno pomivanje posode za uporabo v gospodinjstvih, detergenti za strojno pomivanje medicinskih pripomočkov ali za uporabo v posebnih strojih za čiščenje industrijske opreme, vključno s posebnimi stroji za živilsko industrijo.
Sprays not dosed via automatic pumps are excluded from this product group.
Razpršila, ki se ne odmerjajo s samodejnimi črpalkami, se v to skupino proizvodov ne uvrščajo.
In order to be awarded the EU Ecolabel under Regulation (EC) No 66/2010, an item of automatic dishwasher detergent shall fall within the product group ‘Industrial and Institutional Automatic Dishwasher Detergents’ as defined in Article 1 of this Decision and shall comply with the criteria as well as the related assessment and verification requirements set out in the Annex to this Decision.
Detergentu za strojno pomivanje posode se podeli znak EU za okolje na podlagi Uredbe (ES) št. 66/2010, če spada v skupino proizvodov „detergenti za strojno pomivanje posode za uporabo v industriji in ustanovah“ iz člena 1 tega sklepa ter izpolnjuje merila in s tem povezane zahteve za ocenjevanje in preverjanje iz Priloge k temu sklepu.
The criteria for the product group ‘Industrial and Institutional Automatic Dishwasher Detergents’, as well as the related assessment and verification requirements, shall be valid for four years from the date of adoption of this Decision.
Merila za skupino proizvodov „detergenti za strojno pomivanje posode za uporabo v industriji in ustanovah“ ter s tem povezane zahteve za ocenjevanje in preverjanje veljajo štiri leta od datuma sprejetja tega sklepa.
For administrative purposes the code number assigned to the product group ‘Industrial and Institutional Automatic Dishwasher Detergents’ shall be ‘038’.
Za upravne namene se skupini proizvodov „detergenti za strojno pomivanje posode za uporabo v industriji in ustanovah“ dodeli kodna številka „038“.
The criteria aim, in particular, at promoting products that have a reduced impact on aquatic ecosystems, contain a limited amount of hazardous substances and whose performance has been tested.
S temi merili naj bi se spodbudili zlasti proizvodi, ki imajo manjši vpliv na vodne ekosisteme, vsebujejo omejeno količino nevarnih snovi in katerih učinkovitost je preskušena.
Toxicity to aquatic organisms: Critical Dilution Volume (CDV)
Strupenost za vodne organizme: kritična volumska razredčitev (CDV)
Biodegradability
Biorazgradljivost
Packaging requirements
Zahteve glede embalaže
Automatic dosing systems
Sistemi za samodejno odmerjanje
User information — Information appearing on the EU Ecolabel
Informacije za uporabnike – informacije na znaku EU za okolje
Where the applicant is required to provide declarations, documentation, analyses test reports or other evidence to show compliance with the criteria, it is understood that these may originate from the applicant and/or his supplier(s) and/or their supplier(s) etc., as appropriate.
Če se od vlagatelja zahteva, da predloži izjave, dokumentacijo, analize, poročila o preskusih ali druga dokazila o izpolnjevanju meril, lahko ti po potrebi izvirajo od vlagatelja in/ali njegovega dobavitelja in/ali dobaviteljev slednjega itd.
Where possible, the testing should be performed by laboratories that meet the general requirements of EN ISO 17025 or equivalent.
Če je možno, morajo preskuse opraviti laboratoriji, ki izpolnjujejo splošne zahteve standarda EN ISO 17025 ali drugega enakovrednega standarda.
Where appropriate, test methods other than those indicated for each criterion may be used if the competent body assessing the application accepts their equivalence.
Po potrebi se lahko namesto preskusnih metod, navedenih za posamezno merilo, uporabijo tudi druge, če njihovo enakovrednost potrdi pristojni organ, ki ocenjuje vlogo.
Appendix I makes reference to the detergent ingredient database (DID list) which contains the most widely used ingoing substances used in detergent formulations.
Dodatek I se sklicuje na podatkovno bazo sestavin detergentov (seznam DID), v kateri so navedene dodane snovi, ki se najpogosteje uporabljajo v formulacijah detergentov.
It shall be used for deriving the data for the calculations of the Critical Dilution Volume (CDV) and for the assessment of the biodegradability of the ingoing substances.
Uporablja se pri pridobivanju podatkov za izračune kritične volumske razredčitve (CDV) in pri ocenjevanju biorazgradljivosti dodanih snovi.
For substances not present on the DID list, guidance is given on how to calculate or extrapolate the relevant data.
Za snovi, ki niso navedene na seznamu DID, so pripravljena navodila za izračun ali ekstrapolacijo ustreznih podatkov.
Measurement thresholds
Spodnje mejne vrednosti meritev
Compliance with the ecological criteria is required for substances intentionally added, as well as for by-products and impurities from raw materials, the concentration of which equals or exceeds 0,010 % by weight of final formulation.
Okoljska merila morajo izpolnjevati namenoma dodane snovi ter stranski produkti in nečistoče iz surovin, katerih koncentracija v končni formuli je enaka ali večja od 0,010 masnega %.
For biocides and colouring agents compliance with the criteria is required regardless of their concentration.
Biocidi in barvila morajo ta merila izpolnjevati ne glede na koncentracijo.
Substances meeting the threshold limit as listed above are hereby referred to as ‘Ingoing substances’.
Snovi, ki presegajo navedene spodnje mejne vrednosti, se v tem dokumentu imenujejo „dodane snovi“.
The functional unit for this product group shall be expressed in g/l washing solution (grams per litre washing solution).
Funkcionalna enota za to skupino proizvodov je izražena kot g/l pomivalne raztopine (grami na liter pomivalne raztopine).
Requirements relating to assessment and verification of the functional unit:
Zahteve v zvezi z ocenjevanjem in preverjanjem funkcionalne enote:
The full formulation indicating trade name, chemical name, CAS No, DID No [1], the ingoing quantity including and excluding water, the function and the form of all the ingoing substances (regardless of concentration) in the product must be submitted to the competent body.
Pristojnemu organu se sporoči celotna formulacija proizvoda, pri čemer se navedejo trgovsko ime, kemijsko ime, št. CAS, št. DID [1], dodana količina z vodo in brez nje ter funkcija in oblika vsake od dodanih snovi (ne glede na njihovo koncentracijo) v proizvodu.