natgillin/translations-raw huggingface dataset:
The other PCBs do not exhibit dioxin-like toxicity but have a different toxicological profile and are referred to as ‘non dioxin-like PCB’ (NDL-PCB).
Ostali PCB-ji ne kažejo dioksinom podobne toksičnosti, vendar imajo drugačen toksikološki profil in se imenujejo „dioksinom nepodobni PCB-ji“.
Each congener of dioxins or DL-PCBs exhibits a different level of toxicity.
Vsak kongener dioksinov ali dioksinom podobnih PCB ima drugačno stopnjo toksičnosti.
In order to be able to sum up the toxicity of these different congeners, the concept of toxic equivalency factors (TEFs) was introduced to facilitate risk assessment and regulatory control.
Za določitev toksičnosti teh različnih kongenerjev je bil uveden pojem faktorji ekvivalence toksičnosti (TEF), da bi se omogočila ocena tveganja in regulativni nadzor.
As a result 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 kongenerji dioksinov in dioksinom podobnih PCB-jev, ki so problematični s toksikološkega vidika, izrazijo z izmerljivo enoto, in sicer z ekvivalentom toksičnosti TCDD (TEQ).
The data on the effect of the new TEF values and the recent occurrence are compiled in the European Food Safety Authority’s (EFSA) scientific report ‘Results of the monitoring of dioxin levels in food and feed’ [3].
Podatki o vplivih novih vrednosti TEF in nedavni rezultati prisotnosti so zbrani v znanstvenem poročilu Evropske agencije za varnost hrane (EFSA) „Rezultati spremljanja ravni dioksina v živilih in krmi“ [3].
Therefore, it is appropriate to review the maximum levels of PCBs taking into account these new data.
Zato je ob upoštevanju teh novih podatkov primerno pregledati mejne vrednosti PCB-jev.
The Scientific Panel on Contaminants in the Food Chain of the EFSA on a request from the Commission has adopted an opinion on the presence of NDL-PCBs in feed and food [4].
Znanstveni odbor EFSA o onesnaževalih v prehranski verigi je na zahtevo Komisije sprejel mnenje o prisotnosti dioksinom nepodobnih PCB-jev v krmi in živilih [4].
The sum of the six marker or indicator PCBs (PCB 28, 52, 101, 138, 153 and 180) comprises about half of the amount of total NDL-PCB present in feed and food.
Vsota šestih označevalcev ali kazalnikov PCB-jev (PCB28, PCB52, PCB101, PCB138, PCB153 in PCB180) zajema približno polovico skupne količine dioksinom nepodobnih PCB-jev, prisotnih v krmi in živilih.
That sum is considered as an appropriate marker for occurrence and human exposure to NDL-PCB and therefore should be set as a maximum level.
Navedena vsota velja za primerni označevalec prisotnosti dioksinom nepodobnih PCB-jev in izpostavljenosti ljudi dioksinom nepodobnih PCB-jem ter mora zato biti določena za mejno vrednost.
Maximum levels have been established taking into account recent occurrence data compiled in the EFSA scientific report ‘Results of the monitoring of non dioxin-like PCBs in food and feed’ [5].
Mejne vrednosti so bile določene ob upoštevanju najnovejših podatkov o prisotnosti, ki so bili zbrani v znanstvenem poročilu EFSA „Rezultati spremljanja dioksinom nepodobnih PCB-jev v živilih in krmi“ [5].
Although it is possible to achieve lower limits of quantification (LOQ), it can be observed that a considerable number of laboratories apply an LOQ of 1 μg/kg fat or even 2 μg/kg fat.
Čeprav je mogoče doseči nižje meje določanja, je mogoče opaziti, da znatno število laboratorijev uporablja mejo določanja 1 μg/kg maščobe ali celo 2 μg/kg maščobe.
Expressing the analytical result as an upperbound level would result in some cases in a level close to the maximum level if very strict maximum levels would be established, even if no PCBs have been quantified.
Če bi analitični rezultat izrazili kot zgornjo vrednost, bi v nekaterih primerih lahko nastala vrednost, ki bi bila blizu mejne vrednosti, če bi bile določene zelo stroge mejne vrednosti, čeprav ne bi bili ovrednoteni nobeni PCB-ji.
It was also acknowledged that for certain food categories the data were not very extensive.
Ugotovljeno je bilo tudi, da podatki za nekatere kategorije živil niso bili zelo obsežni.
Therefore, it would be appropriate to review the maximum levels in 3 years time, based upon a more extensive database obtained with a method of analysis with sufficient sensitivity for quantifying low levels.
Zato bi bilo mejne vrednosti primerno pregledati čez tri leta na podlagi obsežnejše zbirke podatkov, ki bi jo dobili s tako analitsko metodo, ki bi bila dovolj občutljiva za vrednotenje nizkih vrednosti.
Derogations have been granted to Finland and Sweden to place on the market fish originating in the Baltic region and intended for consumption in their territory with dioxin levels higher than the maximum levels established for dioxins and the sum of dioxins and DL-PCBs in fish.
Odstopanja so bila odobrena za Finsko in Švedsko, da na trg dasta ribe iz baltiške regije in so namenjene prehrani na njunem ozemlju ter imajo vrednosti dioksina višje od mejnih vrednosti, določenih za dioksine ter vsoto dioksinov in dioksinom podobnih PCB-jev v ribah.
Those Member States have fulfilled the conditions as regards the provision of information to consumers on dietary recommendations.
Navedeni državi članici sta izpolnili pogoje v zvezi z zagotovitvijo informacij o prehranskih priporočilih potrošnikom.
Every year they communicate to the Commission the results of their monitoring of the levels of dioxins in fish from the Baltic region and the measures to reduce human exposure to dioxins from the Baltic region.
Vsako leto Komisiji sporočita rezultate spremljanja vrednosti dioksinov v ribah iz baltske regije ter ukrepe, sprejete za zmanjšanje izpostavljenosti ljudi dioksinom iz baltske regije.
On the basis of the results of monitoring of levels of dioxins and DL-PCBs carried out by Finland and Sweden, the derogation granted could be limited to certain fish species.
Na podlagi rezultatov spremljanja vrednosti dioksinov in dioksinom podobnih PCB-jev, ki sta ga opravili Finska in Švedska, je bilo mogoče odstopanje omejiti na nekatere vrste rib.
Given the persistent presence of dioxins and PCBs in the environment and consequently in fish it is appropriate to grant this derogation without a time limit.
Glede na vztrajno prisotnost dioksinov in PCB-jev v okolju in posledično v ribah je primerno odobriti to odstopanje brez časovne omejitve.
As regards wild caught salmon, Latvia has requested a similar derogation as that granted to Finland and Sweden.
V zvezi z lososom iz prostega ulova je Latvija zaprosila za podobno odstopanje, kot je bilo odobreno Finski in Švedski.
To that end, Latvia has demonstrated that human exposure to dioxins and DL-PCBs in its territory is not higher than the highest average level in any of the Member States and that it has a system in place to ensure that consumers are fully informed of dietary recommendations with regard to restrictions on the consumption of fish from the Baltic region by identified vulnerable sections of the population in order to avoid potential health risks.
V ta namen je Latvija dokazala, da izpostavljenost ljudi dioksinom in dioksinom podobnim PCB-jem na njenem ozemlju ni večja od največje povprečne vrednosti v drugih državah članicah ter da ima vzpostavljen sistem za zagotavljanje, da so potrošniki v celoti obveščeni o prehranskih priporočilih glede omejitev uživanja rib iz baltiške regije za opredeljene ranljive skupine prebivalstva, da bi se izognili morebitnemu zdravstvenemu tveganju.
Furthermore, monitoring of the levels of dioxins and DL-PCBs in fish from the Baltic region should be carried out and the results and measures that have been taken to reduce human exposure to dioxins and DL-PCBs from fish from the Baltic region should be reported to the Commission.
Poleg tega je treba spremljati vrednosti dioksinov in dioksinom podobnih PCB-jev v ribah iz baltiške regije, rezultate in ukrepe, ki so bili sprejeti za zmanjšanje izpostavljenosti ljudi dioksinom in dioksinom podobnim PCB-jem v ribah iz baltiške regije, pa je treba sporočiti Komisiji.
The necessary measures have been put in place ensuring that fish and fish products not complying with EU maximum levels for PCBs are not marketed in other Member States.
Sprejeti so bili potrebni ukrepi za zagotovitev, da se ribe in ribiški proizvodi, ki niso v skladu z mejnimi vrednostmi EU za PCB-je, ne dajejo na trg v drugih državah članicah.
Given that the contamination pattern of NDL-PCBs in fish from the Baltic region show similarities with the contamination of dioxins and DL-PCBs and given that also NDL-PCBs are very persistent in the environment, it is appropriate to grant a similar derogation as regards the presence of NDL-PCBs as for dioxins and DL-PCBs in fish from the Baltic region.
Ker je vzorec onesnaženja rib iz baltiške regije z dioksinom nepodobnimi PCB-ji podoben onesnaženju z dioksini in dioksinom podobnimi PCB-ji ter ker so dioksinom nepodobni PCB-ji tudi zelo obstojni v okolju, je primerno podobno odstopanje kot za dioksine in dioksinom podobne PCB-je v ribah iz baltiške regije odobriti tudi za prisotnost dioksinom nepodobnih PCB-jev.
EFSA has been requested to provide scientific opinion as regards the presence of dioxins and dioxin-like PCBs in sheep and deer liver and the appropriateness to establish maximum levels for dioxins and PCBs in liver and derived products on product basis rather than on a fat basis, as is currently the case.
EFSA je bila zaprošena, da pripravi znanstveno mnenje o prisotnosti dioksinov in dioksinom podobnih PCB-jev v jetrih ovac in jelenov ter o primernosti določitve mejnih vrednosti za dioksine in PCB-je v jetrih in proizvodih iz njih za celoten proizvod in ne za maščobo, kakor trenutno velja.
Therefore, the provisions on liver and derived products should be reviewed in particular the provisions as regards sheep and deer liver once the EFSA opinion is available.
Takoj ko bo na voljo mnenje EFSA, je zato treba pregledati določbe o jetrih in proizvodih iz njih, zlasti določbe v zvezi z jetri ovac in jelenov.
In the meantime it is appropriate to set the maximum level for dioxins and PCBs on a fat basis.
Do takrat je primerno določiti mejno vrednost za dioksine in PCB-je za maščobo.
Foods with less than 1 % fat were until now excluded from the maximum level for dioxins and DL-PCBs, given that those foods are generally minor contributors to the human exposure.
Živila z manj kot 1 % maščobe so bila doslej izključena iz mejne vrednosti za dioksine in dioksinom podobne PCB-je, ker navedena živila običajno v manjši meri prispevajo k izpostavljenosti ljudi.
However, there have been cases with food containing less than 1 % fat but with very high levels of dioxins and DL-PCBs in the fat.
Vendar so se pojavili primeri živil z manj kot 1 % maščobe, vendar z zelo visokimi vrednostmi dioksina in dioksinom podobnih PCB-jev v maščobi.
Therefore, it is appropriate to apply the maximum level to such foods, but on a product basis.
Zato je primerno uporabiti mejno vrednost za taka živila, vendar za celotno živilo.
Taking into account that a maximum level is established on product basis for certain low fat containing foods, it is appropriate to apply a maximum level on product basis for foods containing less than 2 % fat.
Ob upoštevanju, da je mejna vrednost za nekatera živila z nizko vsebnostjo maščobe določena za celotno živilo, je primerno uporabiti mejno vrednost za celotno živilo za živila, ki vsebujejo manj kot 2 % maščobe.
In the light of the monitoring data for dioxins and DL-PCBs in foods for infants and young children it is appropriate to set specific lower maximum levels for dioxins and DL-PCBs in foods for infants and young children.
Glede na rezultate spremljanja dioksinov in dioksinom podobnih PCB-jev v hrani za dojenčke in majhne otroke je primerno določiti posebne nižje mejne vrednosti za dioksine in dioksinom podobne PCB-je v hrani za dojenčke in majhne otroke.
The Federal Institute for Risk Assessment from Germany has addressed to EFSA a specific request to assess the risk for infants and young children of the presence of dioxins and dioxin-like PCBs in foods for infants and young children.
Nemški zvezni inštitut za oceno tveganja je posebej zaprosil EFSA, da oceni tveganje za dojenčke in majhne otroke glede prisotnosti dioksinov in dioksinom podobnih PCB-jev v hrani za dojenčke in majhne otroke.
Therefore, the provisions on foods for infants and young children should be reviewed once the EFSA opinion is available.
Ko bo na voljo mnenje EFSA, bo zato treba preveriti določbe o hrani za dojenčke in majhne otroke.
The title ‘Temporary derogations’ is replaced by ‘Derogations’;
Naslov „Prehodna odstopanja“ se nadomesti z „Odstopanja“.
By way of derogation from Article 1, Finland, Sweden and Latvia may authorise the placing on their market of wild caught salmon (Salmo salar) and products thereof originating in the Baltic region and intended for consumption in their territory with levels of dioxins and/or dioxin-like PCBs and/or non-dioxin-like PCBs higher than those set out in point 5.3 of the Annex, provided that a system is in place to ensure that consumers are fully informed of the dietary recommendations with regard to the restrictions on the consumption of wild caught salmon from the Baltic region and products thereof by identified vulnerable sections of the population in order to avoid potential health risks.
Z odstopanjem od člena 1 lahko Finska, Švedska in Latvija odobrijo dajanje na svoj trg lososa iz prostega ulova (Salmo salar) in proizvodov iz njega iz baltiške regije in so namenjeni prehrani na njihovem ozemlju ter imajo vrednosti dioksinov in/ali dioksinom podobnih PCB-jev in/ali dioksinom nepodobnih PCB-jev višje od vrednosti iz točke 5.3 Priloge, če je vzpostavljen sistem, ki potrošnikom zagotavlja, da so v celoti obveščeni o prehranskih priporočilih glede omejitev uživanja lososa iz prostega ulova iz baltiške regije in proizvodov iz njega za opredeljene ranljive skupine prebivalstva, da bi se izognili morebitnemu zdravstvenemu tveganju.
Finland, Sweden and Latvia shall continue to apply the necessary measures to ensure that wild caught salmon and products thereof not complying with point 5.3 of the Annex are not marketed in other Member States.
Finska, Švedska in Latvija še naprej izvajajo potrebne ukrepe za zagotovitev, da se divje ulovljeni losos in proizvodi iz njega, ki niso v skladu s točko 5.3 Priloge, ne dajejo na trg v drugih državah članicah.
Finland, Sweden and Latvia will report yearly to the Commission the measures they have taken to effectively inform the identified vulnerable sections of the population of the dietary recommendations and to ensure that wild caught salmon and products thereof not compliant with the maximum levels is not marketed in other Member States.
Finska, Švedska in Latvija bodo vsako leto Komisiji sporočile ukrepe, ki so jih sprejele za učinkovito obveščanje opredeljenih ranljivih skupin prebivalstva o prehranskih priporočilih ter za zagotavljanje, da se losos iz prostega ulova in proizvodi iz njega, ki niso v skladu z mejnimi vrednostmi, ne dajejo na trg v drugih državah članicah.
They shall furthermore provide evidence of the effectiveness of these measures.’;
Poleg tega morata dokazati učinkovitost teh ukrepov.“
By way of derogation from Article 1, Finland and Sweden may authorise the placing on their market of wild caught herring larger than 17 cm (Clupea harengus), wild caught char (Salvelinus spp.), wild caught river lamprey (Lampetra fluviatilis) and wild caught trout (Salmo trutta) and products thereof originating in the Baltic region and intended for consumption in their territory with levels of dioxins and/or dioxin-like PCBs and/or non dioxin-like PCBs higher than those set out in point 5.3 of the Annex, provided that a system is in place to ensure that consumers are fully informed of the dietary recommendations with regard to the restrictions on the consumption of wild caught herring larger than 17 cm, wild caught char, wild caught river lamprey and wild caught trout from the Baltic region and products thereof by identified vulnerable sections of the population in order to avoid potential health risks.
Z odstopanjem od člena 1 lahko Finska in Švedska odobrita dajanje na trg sleda iz prostega ulova (Clupea harengus), večjega od 17 cm, zlatovčice iz prostega ulova (Salvelinus spp.), rečnega piškurja iz prostega ulova (Lampetra fluviatilis) in postrvi iz prostega ulova (Salmo trutta) ter proizvodov iz njih iz baltiške regije in so namenjeni prehrani na njunem ozemlju ter imajo vrednosti dioksinov in/ali dioksinom podobnih PCB-jev in/ali dioksinom nepodobnih PCB-jev višje od vrednosti iz točke 5.3 Priloge, če je vzpostavljen sistem, ki potrošnikom zagotavlja, da so v celoti obveščeni o prehranskih priporočilih glede omejitev uživanja sleda iz prostega ulova, večjega od 17 cm, zlatovčice iz prostega ulova, rečnega piškurja iz prostega ulova in postrvi iz prostega ulova iz baltiške regije ter proizvodov iz njih za opredeljene ranljive skupine prebivalstva, da bi se izognili morebitnemu zdravstvenemu tveganju.
Finland and Sweden shall continue to apply the necessary measures to ensure that wild caught herring larger than 17 cm, wild caught char, wild caught river lamprey and wild caught trout and products thereof not complying with point 5.3 of the Annex are not marketed in other Member States.
Finska in Švedska še naprej izvajata potrebne ukrepe za zagotovitev, da se sled iz prostega ulova, večji od 17 cm, zlatovčica iz prostega ulova, rečni piškur iz prostega ulova in postrv iz prostega ulova ter proizvodi iz njih, ki niso v skladu s točko 5.3 Priloge, ne dajejo na trg v drugih državah članicah.
Finland and Sweden will report yearly to the Commission the measures they have taken to effectively inform the identified vulnerable sections of the population of the dietary recommendations and to ensure that fish and products thereof not compliant with the maximum levels is not marketed in other Member States.
Finska in Švedska bosta vsako leto Komisiji sporočili ukrepe, ki sta jih sprejeli za učinkovito obveščanje opredeljenih ranljivih skupin prebivalstva o prehranskih priporočilih ter za zagotavljanje, da se ribe in proizvodi iz njih, ki niso v skladu z mejnimi vrednostmi, ne dajejo na trg v drugih državah članicah.
EFSA Journal (2005) 284, p. 1, http://www.efsa.europa.eu/en/efsajournal/doc/284.pdf
EFSA Journal (2005) 284, str. 1, http://www.efsa.europa.eu/en/efsajournal/doc/284.pdf.
Section 5: Dioxins and PCBs of the Annex to Regulation (EC) No 1881/2006 is amended as follows:
Oddelek 5: Dioksini in PCB Priloge k Uredbi (ES) št. 1881/2006 se spremeni:
Section 5: Dioxins and PCBs is replaced by the following:
Oddelek 5: Dioksini in PCB se nadomesti z naslednjim:
‘Section 5:
„Oddelek 5:
Dioxins and PCBs (31)
Dioksini in PCB-ji (31)
Maximum levels
MEJNE VREDNOSTI
Sum of dioxins (WHO-PCDD/F-TEQ) (32)
VSOTA DIOKSINOV (SZO-PCDD/F-TEQ) (32)
Sum of dioxins and dioxin-like PCBS (WHO-PCDD/F-PCB-TEQ) (32)
VSOTA DIOKSINOV IN DIOKSINOM PODOBNIH PCB-jev (SZO-PCDD/F-TEQ) (32)
Sum of PCB28, PCB52, PCB101, PCB138, PCB153 and PCB180 (ICES – 6) (32)
VSOTA PCB28, PCB52, PCB101, PCB138, PCB153 in PCB180 (ICES – 6) (32)
Meat and meat products (excluding edible offal) of the following animals (6):
meso in mesni izdelki (razen užitnih klavničnih odpadkov) naslednjih živali (6):
bovine animals and sheep
goveda in ovc
2,5 pg/g fat (33)
2,5 pg/g maščobe (33)
4,0 pg/g fat (33)
4,0 pg/g maščobe (33)
40 ng/g fat (33)
40 ng/g maščobe (33)
1,75 pg/g fat (33)
1,75 pg/g maščobe (33)
3,0 pg/g fat (33)
3,0 pg/g maščobe (33)
1,0 pg/g fat (33)
1,0 pg/g maščobe (33)
1,25 pg/g fat (33)
1,25 pg/g maščobe (33)
Liver of terrestrial animals referred to in 5.1 (6), and derived products thereof,
jetra kopenskih živali iz točke 5.1 (6) in proizvodi iz njih
4,5 pg/g fat (33)
4,5 pg/g maščobe (33)
10,0 pg/g fat (33)
10,0 pg/g maščobe (33)
Muscle meat of fish and fishery products and products thereof (25) (34), with the exemption of:
mišičnina rib in ribiških proizvodov ter proizvodi iz nje (25) (34), razen
wild caught eel
jegulj iz prostega ulova
wild caught fresh water fish, with the exception of diadromous fish species caught in fresh water
sladkovodnih rib iz prostega ulova, razen diadromnih vrst rib, ujetih v sladki vodi
fish liver and derived products
ribjih jeter in proizvodov iz njih
marine oils
olj morskih organizmov
3,5 pg/g wet weight
3,5 pg/g mokre teže
6,5 pg/g wet weight
6,5 pg/g mokre teže
75 ng/g wet weight
75 ng/g mokre teže
Muscle meat of wild caught fresh water fish, with the exception of diadromous fish species caught in fresh water, and products thereof (25)
mišičnina sladkovodnih rib iz prostega ulova, razen diadromnih vrst rib, ujetih v sladki vodi, in proizvodi iz nje (25)
125 ng/g wet weight
125 ng/g mokre teže
Muscle meat of wild caught eel (Anguilla anguilla) and products thereof
mišičnina jegulj iz prostega ulova (Anguilla anguilla) in proizvodi iz nje
10,0 pg/g wet weight
10,0 pg/g mokre teže
300 ng/g wet weight
300 ng/g mokre teže
Fish liver and derived products thereof with the exception of marine oils referred to in point 5.7
ribja jetra in proizvodi iz njih, razen olj morskih organizmov iz točke 5.7
20,0 pg/g wet weight (38)
20,0 pg/g mokre teže (38)
200 ng/g wet weight (38)
200 ng/g mokre teže (38)
Marine oils (fish body oil, fish liver oil and oils of other marine organisms intended for human consumption)
olja morskih organizmov (olje iz trupov rib, olje iz ribjih jeter in olja iz drugih morskih organizmov za prehrano ljudi)
1,75 pg/g fat
1,75 pg/g maščobe
200 ng/g fat
200 ng/g maščobe
Raw milk (6) and dairy products (6), including butter fat
surovo mleko (6) in mlečni izdelki (6), vključno z mlečno maščobo
5,5 pg/g fat (33)
5,5 pg/g maščobe (33)
Hen eggs and egg products (6)
kokošja jajca in jajčni proizvodi (6)
5,0 pg/g fat (33)
5,0 pg/g maščobe (33)
2,5 pg/g fat
2,5 pg/g maščobe
40 ng/g fat
40 ng/g maščobe
1,25 pg/g fat
1,25 pg/g maščobe
2,50 pg/g fat
2,50 pg/g maščobe
Foods for infants and young children (4)
hrana za dojenčke in majhne otroke (4)
0,1 pg/g wet weight
0,1 pg/g mokre teže
0,2 pg/g wet weight
0,2 pg/g mokre teže
1,0 ng/g wet weight’
1,0 ng/g mokre teže“
footnote 31 is replaced by the following:
Opomba 31 se nadomesti z naslednjim:
Abbreviations used: “T” = tetra; “Pe” = penta; “Hx” = hexa; “Hp” = hepta; “O” = octa; “CDD” = chlorodibenzodioxin; “CDF” = chlorodibenzofuran; “CB” = chlorobiphenyl.’
Uporabljene okrajšave: „T“ = tetra; „Pe“ = penta; „Hx“ = heksa; „Hp“ = hepta; „O“ = okta; „CDD“ = klorodibenzodioksin; „CDF“ = klorodibenzofuran; „CB“ = klorobifenil.“
TEF value
Vrednost TEF
Dibenzo-p-dioxins (‘PCDDs’)
dibenzo-p-dioksini („PCDD“)
Dibenzofurans (‘PCDFs’)
dibenzofurani („PCDF“)
“Dioxin-like” PCBs Non-ortho PCBs + Mono-ortho PCBs
„dioksinom podobni“ PCB: ne-orto PCB + mono-orto PCB
Non-ortho PCBs
ne-orto PCB
Mono-ortho PCBs
mono-orto PCB
footnote 33 is replaced by the following:
Opomba 33 se nadomesti z naslednjim:
The maximum level expressed on fat is not applicable for foods containing < 2 % fat.
Mejna vrednost za maščobo se ne uporablja za živila, ki vsebujejo manj kot 2 % maščobe.
For foods containing less than 2 % fat, the maximum level applicable is the level on product basis corresponding to the level on product basis for the food containing 2 % fat, calculated from the maximum level established on fat basis, making use of following formula:
Za živila, ki vsebujejo manj kot 2 % maščobe, mejna vrednost za celotno živilo ustreza vrednosti za živila, ki vsebujejo 2 % maščobe, kar se izračuna iz mejne vrednosti, določene za maščobo, z uporabo naslednje formule:
Maximum level expressed on product basis for foods containing less than 2 % fat = maximum level expressed on fat for that food x 0,02’.
mejna vrednost za celotno živilo pri živilih, ki vsebujejo manj kot 2 % maščobe = mejna vrednost za maščobo za navedeno živilo x 0,02“