natgillin/translations-raw huggingface dataset:
The forms of mercury present in these other foods are mainly not methylmercury and they are therefore considered to be of lower risk.
Oblike živega srebra, prisotnega v drugih živilih, večinoma niso metil živo srebro, zato veljajo za manj tvegane.
In addition to the setting of maximum levels, targeted consumer advice is an appropriate approach in the case of methylmercury for protecting vulnerable groups of the population.
Razen določanja mejnih vrednosti metil živega srebra je ciljno svetovanje potrošnikom ustrezen pristop k zaščiti ranljivih skupin prebivalstva.
An information note on methylmercury in fish and fishery products responding to this need has therefore been made available on the website of the Health and Consumer Protection Directorate-General of the European Commission [26].
Zato je na spletni strani Generalnega direktorata Evropske komisije za zdravje in varstvo potrošnikov na voljo informativno obvestilo o metil živem srebru v ribah in ribiških proizvodih [26].
Several Member States have also issued advice on this issue that is relevant to their population.
Tudi več držav članic je izdalo nasvete v zvezi s tem vprašanjem, ki je pomembno za prebivalstvo.
As regards inorganic tin, the SCF concluded in its opinion of 12 December 2001 [27] that levels of inorganic tin of 150 mg/kg in canned beverages and 250 mg/kg in other canned foods may cause gastric irritation in some individuals.
Znanstveni odbor je v mnenju z dne 12. decembra 2001 [27] ugotovil, da lahko vsebnost anorganskega kositra 150 mg/kg v pijačah v pločevinkah in vsebnost 250 mg/kg v drugih živilih v pločevinkah pri posameznikih povzroči draženje želodca.
To protect public health from this health risk it is necessary to set maximum levels for inorganic tin in canned foods and canned beverages.
Da bi zaščitili javno zdravje pred takšnim zdravstvenim tveganjem, je treba določiti mejne vrednosti za anorganski kositer v živilih v pločevinkah in pijači v pločevinkah.
Until data becomes available on the sensitivity of infants and young children to inorganic tin in foods, it is necessary on a precautionary basis to protect the health of this vulnerable population group and to establish lower maximum levels.
Dokler ni na voljo podatkov o občutljivosti dojenčkov in majhnih otrok na anorganski kositer v živilih, je treba iz preventivnih razlogov zaščititi zdravje te ranljive skupine prebivalstva in določiti nižje mejne vrednosti.
As regards 3-monochloropropane-1,2-diol (3-MCPD) the SCF adopted on 30 May 2001 a scientific opinion as regards 3-MCPD in food [28], updating its opinion of 16 December 1994 [29] on the basis of new scientific information and established a tolerable daily intake (TDI) of 2 μg/kg bw for 3-MCPD.
Znanstveni odbor za hrano je 30. maja 2001 sprejel znanstveno mnenje v zvezi s 3-monokloropropan-1,2-diolom (3-MCPD) v hrani [28], ki posodablja mnenje z dne 16. decembra 1994 [29] na podlagi novih znanstvenih spoznanj, ter določil sprejemljiv dnevni vnos (TDI) 2 μg/kg TT za 3-MCPD.
In the framework of Directive 93/5/EEC the SCOOP-task ‘Collection and collation of data on levels of 3-MCPD and related substances in foodstuffs’ was performed and finalised in June 2004 [30].
V okviru Direktive 93/5/EGS je bila junija 2004 [30] izvedena in dokončana naloga SCOOP „Zbiranje in primerjava podatkov o vrednosti 3-monokloropropan-1,2-diola (3-MCPD) in sorodnih snovi v živilih“.
The main contributors of 3-MCPD to dietary intake were soy sauce and soy-sauce based products.
K vnosu 3-MCPD s hrano so najbolj prispevali sojina omaka in izdelki na osnovi sojine omake.
Some other foods eaten in large quantities, such as bread and noodles, also contributed significantly to intake in some countries because of high consumption rather than high levels of 3-MCPD present in these foods.
Nekatera druga živila, ki se uživajo v večjih količinah, kot so kruh in rezanci, so v nekaterih državah tudi bistveno prispevala k vnosu 3-MCPD s hrano zaradi velikih količin uživanja in ne zaradi visokih vrednosti 3-MCPD, prisotnega v teh živilih.
Accordingly maximum levels should be set for 3-MCPD in hydrolysed vegetable protein (HVP) and soy sauce taking into account the risk related to the consumption of these foods.
V skladu s tem morajo biti mejne vrednosti določene za 3-MCPD v hidroliziranem rastlinskem proteinu (HVP) in sojini omaki, ob upoštevanju tveganja, povezanega z uživanjem teh živil.
Member States are requested to examine other foodstuffs for the occurrence of 3-MCPD in order to consider the need to set maximum levels for additional foodstuffs.
Države članice morajo preveriti navzočnost 3-MCPD tudi v drugih živilih, da bo mogoče pretehtati potrebo po določitvi mejnih vrednosti še za druga živila.
As regards dioxins and PCBs, the SCF adopted on 30 May 2001 an opinion on dioxins and dioxin-like PCBs in food [31], updating its opinion of 22 November 2000 [32] fixing a tolerable weekly intake (TWI) of 14 pg World Health Organisation toxic equivalent (WHO-TEQ)/kg bw for dioxins and dioxin-like PCBs.
Znanstveni odbor za hrano je 30. maja 2001 sprejel mnenje o dioksinih in dioksinom podobnih PCB v hrani [31], ki posodablja mnenje z dne 22. novembra 2000 [32] o določanju sprejemljivega tedenskega vnosa (TWI) 14 pg toksičnega ekvivalenta Svetovne zdravstvene organizacije (WHO-TEQ)/kg TT za dioksine in dioksinom podobne PCB.
Dioxins as referred to in this Regulation cover a group of 75 polychlorinated dibenzo-p-dioxin (PCDD) congeners and 135 polychlorinated dibenzofuran (PCDF) congeners, of which 17 are of toxicological concern.
Dioksini, kot so navedeni v tej uredbi, zajemajo skupino 75 vrst polikloriranih dibenzo-p-dioksinov (PCDD) in 135 vrst polikloriranih dibenzofuranov (PCDF), od katerih je 17 toksikološko pomembnih.
Polychlorinated biphenyls (PCBs) are a group of 209 different congeners which can be divided into two groups according to their toxicological properties: 12 congeners exhibit toxicological properties similar to dioxins and are therefore often termed dioxin-like PCBs.
Poliklorirani bifenili (PCB) so skupina 209 različnih sorodnih spojin, ki jih lahko razdelimo na dve skupini glede na njihove toksikološke lastnosti: 12 sorodnih spojin kaže podobne toksikološke lastnosti kot dioksini, in se zato pogosto imenujejo dioksinom podobni PCB.
The other PCBs do not exhibit dioxin-like toxicity but have a different toxicological profile.
Ostali PCB ne kažejo dioksinom podobne strupenosti vendar imajo drugačen toksikološki profil.
Each congener of dioxins or dioxin-like PCBs exhibits a different level of toxicity.
Vsaka spojina iz skupine dioksinov ali dioksinom podobnih PCB ima drugačno stopnjo strupenosti.
In order to be able to sum up the toxicity of these different congeners, the concept of toxic equivalency factors (TEFs) has been introduced to facilitate risk assessment and regulatory control.
Za določitev strupenosti teh različnih sorodnih spojin je bil uveden pojem faktorji toksične ekvivalence (TEF), da bi se omogočila ocena nevarnosti in regulativni nadzor.
This means that the analytical results relating to all the individual dioxin and dioxin-like PCB congeners of toxicological concern are expressed in terms of a quantifiable unit, namely the TCDD toxic equivalent (TEQ).
To pomeni, da se analitični rezultati v zvezi z vsemi posameznimi spojinami dioksinov in dioksinom podobnimi spojinami PCB, ki so toksikološko pomembne, izrazijo z izmerljivo enoto, in sicer z ekvivalentom toksičnosti TCDD (TEKV).
Exposure estimates taking into account the SCOOP-task ‘Assessment of dietary intake of dioxins and related PCBs by the population of EU Member States’ finalised in June 2000 [33] indicate that a considerable proportion of the Community population has a dietary intake in excess of the TWI.
Ocene izpostavljenosti, ob upoštevanju naloge SCOOP „Ocena izpostavljenosti prebivalstva držav članic EU dioksinom in dioksinom podobnih PCB v hrani“, ki je bila dokončana junija 2000 [33], kažejo, da ima velik del prebivalstva Skupnosti prevelik TWI.
From a toxicological point of view, any level set should apply to both dioxins and dioxin-like PCBs, but in 2001 maximum levels were set on Community level only for dioxins and not for dioxin-like PCBs, given the very limited data available at that time on the prevalence of dioxin-like PCBs.
S toksikološkega stališča bi se morale vse določene vrednosti uporabljati tako za dioksine kot za dioksinom podobne PCB, vendar so bile leta 2001 mejne vrednosti na ravni Skupnosti določene le za dioksine, ne pa za dioksinom podobne PCB, ker so bili o razširjenosti dioksinom podobnih PCB takrat na voljo le zelo skopi podatki.
Since 2001, however, more data on the presence of dioxin-like PCBs have become available, therefore, maximum levels for the sum of dioxins and dioxin-like PCBs have been set in 2006 as this is the most appropriate approach from a toxicological point of view.
Od leta 2001 je na voljo več podatkov o prisotnosti dioksinom podobnih PCB, zato so bile leta 2006 določene mejne vrednosti za vsoto dioksinov in dioksinom podobnih PCB, ker je s toksikološkega vidika to najprimernejši pristop.
In order to ensure a smooth transition, the levels for dioxins should continue to apply for a transitional period in addition to the levels for the sum of dioxins and dioxin-like PCBs.
Da se zagotovi nemoten prehod, je treba razen vrednosti za vsoto dioksinov in dioksinom podobnih PCB v prehodnem obdobju še naprej uporabljati vrednosti za dioksine.
Foodstuffs must comply during that transitional period with the maximum levels for dioxins and with the maximum levels for the sum of dioxins and dioxin-like PCBs.
Živila morajo biti v tem prehodnem obdobju v skladu z mejnimi vrednostmi za dioksine ter mejnimi vrednostmi za vsoto dioksinov in dioksinom podobnih PCB.
Consideration will be given by 31 December 2008 to dispensing with the separate maximum levels for dioxins.
Do 31. decembra 2008 bo preučena odprava ločenih mejnih vrednosti za dioksine.
In order to encourage a proactive approach to reducing the dioxins and dioxin-like PCBs present in food and feed, action levels were set by Commission Recommendation 2006/88/EC of 6 February 2006 on the reduction of the presence of dioxins, furans and PCBs in feedingstuffs and foodstuffs [34].
Da se spodbudi proaktivni pristop za zmanjšanje dioksinov in dioksinom podobnih PCB, prisotnih v živilih in krmi, so bili s Priporočilom Komisije 2006/88/ES z dne 6. februarja 2006 o zmanjšanju prisotnosti dioksinov, furanov in PCB v krmi in živilih [34] določeni pragovi za ukrepanje.
These action levels are a tool for competent authorities and operators to highlight those cases where it is appropriate to identify a source of contamination and to take measures to reduce or eliminate it.
Ti pragovi za ukrepanje so orodje, s katerim lahko pristojni organi in proizvajalci ugotovijo, v katerih primerih je primerno določiti vir onesnaženja in sprejeti ukrepe za njeno zmanjšanje ali odpravo.
Since the sources of dioxins and dioxin-like PCBs are different, separate action levels are determined for dioxins on the one hand and for dioxin-like PCBs on the other hand.
Ker so viri dioksinov in dioksinom podobnih PCB različni, so določeni ločeni pragovi za ukrepanje za dioksine in dioksinom podobne PCB.
This proactive approach to actively reduce the dioxins and dioxin-like PCBs in feed and food and consequently, the maximum levels applicable should be reviewed within a defined period of time with the objective to set lower levels.
Ta proaktivni pristop za aktivno zmanjšanje dioksinov in dioksinom podobnih PCB v krmi in živilih ter posledično mejne vrednosti, ki se uporabljajo, je treba v določenem obdobju ponovno pregledati, da se določijo nižje vrednosti.
Therefore, consideration will be given by 31 December 2008 to significantly reducing the maximum levels for the sum of dioxins and dioxin-like PCBs.
Zato bo do 31. decembra 2008 preučeno bistveno zmanjšanje mejnih vrednosti za vsoto dioksinov in dioksinom podobnih PCB.
Operators need to make efforts to step up their capacity to remove dioxins, furans and dioxin-like PCBs from marine oil.
Proizvajalci si morajo prizadevati za povečanje svoje zmogljivosti za odstranjevanje dioksinov, furanov in dioksinom podobnih PCB iz olj morskih organizmov.
The significant lower level, to which consideration shall be given by 31 December 2008, shall be based on the technical possibilities of the most effective decontamination procedure.
Bistveno nižja vrednost, ki bo preučena do 31. decembra 2008, temelji na tehničnih možnostih najučinkovitejšega postopka odstranitve onesnaževal.
As regards the establishment of maximum levels for other foodstuffs by 31 December 2008, particular attention shall be paid to the need to set specific lower maximum levels for dioxins and dioxin-like PCBs in foods for infants and young children in the light of the monitoring data obtained through the 2005, 2006 and 2007 programmes for monitoring dioxins and dioxin-like PCBs in foods for infants and young children.
V zvezi z določitvijo mejnih vrednosti za druga živila do 31. decembra 2008 je posebna pozornost namenjena potrebi po določitvi posebnih nižjih mejnih vrednosti za dioksine in dioksinom podobne PCB v hrani za dojenčke in male otroke glede na podatke spremljanja, pridobljene s programi za spremljanje dioksinov in dioksinom podobnih PCB v hrani za dojenčke in majhne otroke v letih 2005, 2006 in 2007.
As regards polycyclic aromatic hydrocarbons, the SCF concluded in its opinion of 4 December 2002 [35] that a number of polycyclic aromatic hydrocarbons (PAH) are genotoxic carcinogens.
Znanstveni odbor za hrano je v mnenju z dne 4. decembra 2002 [35] sklenil, da je veliko policikličnih aromatskih ogljikovodikov (PAH) genotoksičnih rakotvornih snovi.
The Joint FAO/WHO Expert Committee on Food Additives (JECFA) performed in 2005 a risk assessment on PAHs and estimated margins of exposure (MOE) for PAH as a basis for advice on compounds that are both genotoxic and carcinogenic [36].
Skupni strokovni odbor FAO/WHO za aditive v hrani (JECFA) je leta 2005 izvedel oceno tveganja PAH in določil stopnje izpostavljenosti (MOE) za PAH kot podlago za svetovanje o spojinah, ki so genotoksične in rakotvorne [36].
According to the SCF, benzo(a)pyrene can be used as a marker for the occurrence and effect of carcinogenic PAH in food, including also benz(a)anthracene, benzo(b)fluoranthene, benzo(j)fluoranthene, benzo(k)fluoranthene, benzo(g,h,i)perylene, chrysene, cyclopenta(c,d)pyrene, dibenz(a,h)anthracene, dibenzo(a,e)pyrene, dibenzo(a,h)pyrene, dibenzo(a,i)pyrene, dibenzo(a,l)pyrene, indeno(1,2,3-cd)pyrene and 5-methylchrysene.
Po mnenju Znanstvenega odbora za hrano se lahko benzo(a)piren uporablja kot kazalnik prisotnosti in vpliva rakotvornih PAH v hrani, vključno z benz(a)antracenom, benzo(b)fluorantenom, benzo(j)fluorantenom, benzo(k)fluorantenom, benzo(g,h,i)perilenom, krizenom, ciklopenta(c,d)pirenom, dibenz(a,h)antracenom, dibenzo(a,e)pirenom, dibenzo(a,h)pirenom, dibenzo(a,i)pirenom, dibenzo(a,l)pirenom, indeno(1,2,3-cd)pirenom in 5-metilkrizenom.
Further analyses of the relative proportions of these PAH in foods would be necessary to inform a future review of the suitability of maintaining benzo(a)pyrene as a marker.
Da se lahko v prihodnji pregled primernosti vključi benzo(a)piren kot kazalnik, so potrebne nadaljnje analize relativnih sorazmerij teh PAH v živilih.
In addition benzo(c)fluorene should be analysed, following a recommendation of JECFA.
Razen tega mora biti ob upoštevanju priporočila JECFA analiziran tudi benzo(c)fluoren.
PAH can contaminate foods during smoking processes and heating and drying processes that allow combustion products to come into direct contact with food.
PAH lahko onesnažijo živila med postopki prekajevanja ter segrevanja in sušenja, pri katerih produkti zgorevanja pridejo v neposreden stik z živilom.
In addition, environmental pollution may cause contamination with PAH, in particular in fish and fishery products.
Razen tega je lahko onesnaženost živil s PAH zlasti v ribah in ribiških proizvodih posledica onesnaženja okolja.
In the framework of Directive 93/5/EEC, a specific SCOOP-task ‘Collection of occurrence data on PAH in food’ has been performed in 2004 [37].
V okviru Direktive 93/5/EGS je bila leta 2004 izvedena posebna naloga SCOOP „Zbiranje podatkov o prisotnosti PAH v hrani“ [37].
High levels were found in dried fruits, olive pomace oil, smoked fish, grape seed oil, smoked meat products, fresh molluscs, spices/sauces and condiments.
Visoke vrednosti so bile ugotovljene v suhem sadju, olju iz oljčnih tropin, prekajeni ribi, olju iz semen grozdnih jagod, prekajenih mesnih izdelkih, svežih mehkužcih, dišavnicah/omakah in začimbah.
In order to protect public health, maximum levels are necessary for benzo(a)pyrene in certain foods containing fats and oils and in foods where smoking or drying processes might cause high levels of contamination.
Zato da se zaščiti javno zdravje, so mejne vrednosti potrebne za benzo(a)piren v nekaterih živilih, ki vsebujejo maščobe in olja, ter v živilih, v katerih lahko postopki prekajevanja ali sušenja povzročijo visoke ravni onesnaženosti.
Maximum levels are also necessary in foods where environmental pollution may cause high levels of contamination, in particular in fish and fishery products, for example resulting from oil spills caused by shipping.
Mejne vrednosti so potrebne tudi za živila, pri katerih lahko onesnaženje okolja povzroči visoke ravni onesnaženosti, zlasti za ribe in ribiške proizvode, na primer zaradi razlitja nafte zaradi ladijskega prometa.
In some foods, such as dried fruit and food supplements, benzo(a)pyrene has been found, but available data are inconclusive on what levels are reasonably achievable.
V nekaterih živilih, kot so suho sadje in prehranska dopolnila, je bil ugotovljen benzo(a)piren, vendar razpoložljivi podatki ne določajo razumsko dosegljivih vrednosti.
Further investigation is needed to clarify the levels that are reasonably achievable in these foods.
Da se pojasnijo vrednosti, ki so razumsko dosegljive v teh živilih, je potrebna nadaljnja preiskava.
In the meantime, maximum levels for benzo(a)pyrene in relevant ingredients should apply, such as in oils and fats used in food supplements.
Medtem se morajo uporabljati mejne vrednosti za benzo(a)piren v ustreznih sestavinah, na primer v oljih in maščobah, ki se uporabljajo v prehranskih dopolnilih.
The maximum levels for PAH and the appropriateness of setting a maximum level for PAH in cocoa butter should be reviewed by 1 April 2007, taking into account the progress in scientific and technological knowledge on the occurrence of benzo(a)pyrene and other carcinogenic PAH in food.
Mejne vrednosti za PAH in primernost določitve mejne vrednosti za PAH v kakavovem maslu je treba pregledati do 1. aprila 2007, ob upoštevanju novih znanstvenih in tehnoloških spoznanj v zvezi s prisotnostjo benzo(a)pirena ter drugih rakotvornih PAH v hrani.
The foodstuffs listed in the Annex shall not be placed on the market where they contain a contaminant listed in the Annex at a level exceeding the maximum level set out in the Annex.
Živila iz Priloge se ne dajejo v promet, če vsebujejo onesnaževalo iz Priloge, katerega vrednosti presegajo mejno vrednost iz Priloge.
The maximum levels specified in the Annex shall apply to the edible part of the foodstuffs concerned, unless otherwise specified in the Annex.
Mejne vrednosti iz Priloge se uporabljajo za užitni del zadevnih živil, razen če je v Prilogi določeno drugače.
Dried, diluted, processed and compound foodstuffs
Sušena, razredčena, predelana in sestavljena živila
When applying the maximum levels set out in the Annex to foodstuffs which are dried, diluted, processed or composed of more than one ingredient, the following shall be taken into account:
Pri uporabljanju mejnih vrednosti iz Priloge za živila, ki so sušena, razredčena, predelana ali sestavljena iz več kot ene sestavine, se upoštevajo:
changes of the concentration of the contaminant caused by drying or dilution processes;
spremembe koncentracije onesnaževala zaradi postopkov sušenja ali razredčevanja;
changes of the concentration of the contaminant caused by processing;
spremembe koncentracije onesnaževala zaradi postopkov predelave;
the relative proportions of the ingredients in the product;
relativna sorazmerja sestavin v proizvodu;
the analytical limit of quantification.
meje določanja delovnega območja analitske metode.
The specific concentration or dilution factors for the drying, dilution, processing and/or mixing operations concerned or for the dried, diluted, processed and/or compound foodstuffs concerned shall be provided and justified by the food business operator, when the competent authority carries out an official control.
Posebno koncentracijo ali faktorje razredčenja za zadevne postopke sušenja, razredčevanja, predelave in/ali mešanja ali za zadevna sušena, razredčena, predelana in/ali sestavljena živila določi in odobri nosilec živilske dejavnosti, ko pristojni organ izvede uradni nadzor.
If the food business operator does not provide the necessary concentration or dilution factor or if the competent authority deems that factor inappropriate in view of the justification given, the authority shall itself define that factor, based on the available information and with the objective of maximum protection of human health.
Če nosilec živilske dejavnosti ne določi potrebne koncentracije ali faktorja razredčenja ali pristojni organ meni, da je ta faktor neustrezen s stališča dane utemeljitve, ta faktor določi zadevni organ na podlagi razpoložljivih informacij in za zagotovitev največjega varstva zdravja ljudi.
Paragraphs 1 and 2 shall apply in so far as no specific Community maximum levels are fixed for these dried, diluted, processed or compound foodstuffs.
Odstavka 1 in 2 se uporabljata, če za navedena sušena, razredčena, predelana ali sestavljena živila niso določene mejne vrednosti Skupnosti.
As far as Community legislation does not provide for specific maximum levels for foods for infants and young children, Member States may provide for stricter levels.
Če zakonodaja Skupnosti ne določa posebnih mejnih vrednosti živil za dojenčke in majhne otroke, lahko države članice določijo strožje vrednosti.
Prohibitions on use, mixing and detoxification
Prepovedi uporabe, mešanja in razstrupljanja
Foodstuffs not complying with the maximum levels set out in the Annex shall not be used as food ingredients.
Živila, ki niso v skladu z mejnimi vrednostmi iz Priloge, se ne uporabljajo kot sestavine živil.
Foodstuffs complying with the maximum levels set out in the Annex shall not be mixed with foodstuffs which exceed these maximum levels.
Živila, ki so v skladu z mejnimi vrednostmi iz Priloge, se ne mešajo z živili, ki presegajo te mejne vrednosti.
Foodstuffs to be subjected to sorting or other physical treatment to reduce contamination levels shall not be mixed with foodstuffs intended for direct human consumption or with foodstuffs intended for use as a food ingredient.
Živila, za katera je potrebno sortiranje ali drug način mehanske obdelave za zmanjšanje vednosti onesnaženosti, se ne mešajo z živili, namenjenimi neposredni prehrani ljudi, ali z živili za uporabo kot sestavina živil.
Foodstuffs containing contaminants listed in section 2 of the Annex (Mycotoxins) shall not be deliberately detoxified by chemical treatments.
Živila z onesnaževali iz oddelka 2 Priloge (mikotoksini) se ne razstrupljajo namerno s kemijskimi postopki.
Specific provisions for groundnuts, nuts, dried fruit and maize
Posebne določbe za zemeljske oreške, lupinarje, suho sadje in koruzo
Groundnuts, nuts, dried fruit and maize not complying with the appropriate maximum levels of aflatoxins laid down in points 2.1.3, 2.1.5 and 2.1.6 of the Annex can be placed on the market provided that these foodstuffs:
Zemeljski oreški, lupinarji, suho sadje in koruza, ki niso v skladu z ustreznimi mejnimi vrednostmi aflatoksinov iz točk 2.1.3, 2.1.5 in 2.1.6 Priloge, se lahko dajejo v promet, če:
are not intended for direct human consumption or use as an ingredient in foodstuffs;
niso namenjeni neposredni prehrani ljudi ali niso uporabljeni kot sestavina živil;