natgillin/translations-raw huggingface dataset:
On 30 May 2001 the Scientific Committee for Food (SCF) adopted an Opinion on the Risk Assessment of Dioxins and Dioxin-like PCBs in Food, updating its Opinion of 22 November 2000 on this subject on the basis of new scientific information that had become available since the latter’s adoption [3].
Dne 30. maja 2001 je Znanstveni odbor za prehrano (SCF) sprejel mnenje o oceni tveganja za dioksine in dioksinom podobne PCB v živilih, s katerim je posodobil mnenje z dne 22. novembra 2000 o tej temi na podlagi novih znanstvenih podatkov, ki so postali na voljo od sprejetja slednjega mnenja [3].
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 for dioxins only 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 vrednosti uporabljati za dioksine in dioksinom podobne PCB, vendar so bile leta 2001 mejne vrednosti določene le za dioksine, ne pa za dioksinom podobne PCB, ker so bili za dioksinom podobne PCB glede na njihovo razširjenost takrat na voljo zelo skopi podatki.
In the meantime, however, more data on the presence of dioxin-like PCBs have become available.
Zdaj pa je na voljo več podatkov o prisotnosti dioksinom podobnih PCB.
According to Regulation (EC) No 466/2001, the Commission was to review the provisions on dioxins in the light of new data on the presence of dioxins and dioxin-like PCBs, in particular with a view to the inclusion of dioxin-like PCBs in the levels to be set.
V skladu z Uredbo (ES) št. 466/2001 je Komisija morala pregledati določbe o dioksinih glede na nove podatke o prisotnosti dioksinov in dioksinom podobnih PCB, zlasti z namenom vključitve dioksinom podobnih PCB med vrednosti, ki jih je treba določiti.
All operators in the food and feed chain must continue to make all possible efforts and to do all that is necessary to limit the dioxins and PCBs present in feed and food.
Vsi proizvajalci v celotni prehranski verigi od živil do krme si morajo še naprej prizadevati za omejitev dioksinov in PCB, prisotnih v krmi in živilih, ter storiti vse, kar je za to potrebno.
Regulation (EC) No 466/2001 accordingly provides that the maximum levels applicable should be further reviewed by 31 December 2006 at the latest with the aim of significantly reducing the maximum levels and possibly laying down maximum levels for other foodstuffs.
V skladu s tem Uredba (ES) št. 466/2001 določa, da je treba mejne vrednosti, ki se uporabljajo, ponovno pregledati najpozneje do 31. decembra 2006, da se znatno znižajo mejne vrednosti in morda določijo mejne vrednosti za druga živila.
It is proposed to set maximum levels for the sum of dioxins and dioxin-like PCBs expressed in World Health Organisation (WHO) toxic equivalents, using the WHO-TEFs as this is the most appropriate approach from a toxicological point of view.
Predlaga se določitev mejnih vrednosti za vsoto dioksinov in dioksinom podobnih PCB, izraženih v toksičnih ekvivalentih Svetovne zdravstvene organizacije (WHO), z uporabo WHO-TEF, ker je s toksikološkega stališča to najprimernejši pristop.
In order to ensure a smooth transition, for a transitional period the existing levels for dioxins should continue to apply in addition to the newly set levels for the sum of dioxins and dioxin-like PCBs.
Da se zagotovi nemoten prehod, je treba razen na novo določenih vrednosti za vsoto dioksinov in dioksinom podobnih PCB v prehodnem obdobju uporabljati obstoječe vrednosti za dioksine.
The foodstuffs indicated in section 5 of Annex I must comply during that period with the maximum levels for dioxins and with the maximum levels for the sum of dioxins and dioxin-like PCBs.
Živila iz razdelka 5 Priloge I morajo biti v tem obdobju v skladu z mejnimi vrednostmi za dioksine ter mejnimi vrednostmi za vsoto dioksinov in dioksinom podobnih PCB.
Commission Directive 2002/69/EC of 26 July 2002 laying down the sampling methods and the methods of analysis for the official control of dioxins and the determination of dioxin-like PCBs in foodstuffs [4] provides that a lot shall be considered as non-compliant with the established maximum level if the analytical result confirmed by duplicate analysis and calculated as the mean of at least two separate determinations exceeds the maximum level beyond reasonable doubt taking into account the measurement uncertainty.
Direktiva Komisije 2002/69/ES z dne 26. julija 2002 o metodah vzorčenja in analitskih metodah za uradni nadzor dioksinov ter o določitvi dioksinu podobnih PCB-jev v živilih [4] določa, da se serija šteje, da ni skladna z določeno mejno vrednostjo, če analitični rezultat, potrjen s ponovljeno analizo in izračunan kot srednja vrednost vsaj dveh ločenih določitev, nedvomno presega mejno vrednost ob upoštevanju nezanesljivosti meritev.
There are different possibilities to estimate the expanded uncertainty [5].
Za oceno razširjene nezanesljivosti obstajajo različne možnosti [5].
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 2002/201/EC of 4 March 2002 on the reduction of the presence of dioxins, furans and PCBs in feedingstuffs and foodstuffs [6].
Za spodbuditev proaktivnega pristopa k zmanjšanju dioksinov in dioksinom podobnih PCB, prisotnih v živilih in krmi, so bili določeni pragovi za ukrepanje s Priporočilom Komisije 2002/201/ES z dne 4. marca 2002 o zmanjšanju prisotnosti dioksinov, furanov in PCB v krmi in živilih [6].
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 ustrezno določiti vir kontaminacije in sprejeti ukrepe za njeno zmanjšanje ali odpravo.
Recommendation 2002/201/EC will therefore be amended accordingly.
Priporočilo 2002/201/ES je zato treba ustrezno spremeniti.
Derogations have been granted to Finland and Sweden to place on the market fish originating in the Baltic region and intended for consumption in the territory with dioxin levels higher than those set in point 5.2 of section 5 of Annex I to Regulation (EC) No 466/2001.
Finski in Švedski je bilo odobreno odstopanje, da smeta na svojem ozemlju dati v promet ribe za prehrano, ki izvirajo iz baltske regije in vsebujejo vrednosti dioksinov, višje od določenih v točki 5.2 razdelka 5 Priloge I k Uredbi (ES) št. 466/2001.
Those Member States have fulfilled the conditions as regards the provision of information to consumers on dietary recommendations.
Ti državi članici sta izpolnili pogoje v zvezi z zagotovitvijo informacij o prehranskih priporočilih potrošnikom.
Every year they have communicated the results of their monitoring of the levels of dioxins in fish from the Baltic region to the Commission and have reported on the measures to reduce human exposure to dioxins from the Baltic region.
Vsako leto sta Komisiji sporočili rezultate spremljanja vrednosti dioksinov v ribah iz baltske regije in poročali o ukrepih, sprejetih za zmanjšanje izpostavljenosti ljudi dioksinom iz baltske regije.
On the basis of the results of monitoring of levels of dioxins and dioxin-like PCBs carried out by Finland and Sweden, the transitional period during which the derogations granted to those Member States apply should be extended, but those derogations should be limited to certain fish species.
Na podlagi rezultatov spremljanja vrednosti dioksinov in dioksinom podobnih PCB, ki sta ga opravili Finska in Švedska, je treba podaljšati prehodno obdobje, v katerem velja odstopanje, odobreno tema državama članicama, vendar je treba to odstopanje omejiti na nekatere vrste rib.
Those derogations apply to the maximum levels for dioxins and to the maximum levels for the sum of dioxins and dioxin-like PCBs set in point 5.2 of section 5 of Annex I to Regulation (EC) No 466/2001.
To odstopanje se uporablja za mejne vrednosti za dioksine ter mejne vrednosti za vsoto dioksinov in dioksinom podobnih PCB, določene v točki 5.2 razdelka 5 Priloge I k Uredbi (ES) št. 466/2001.
As food contamination is directly related to feed contamination, an integrated approach must be adopted to reduce dioxin and dioxin-like PCB incidence throughout the food chain, i.e. from feed materials through food-producing animals to humans.
Ker je kontaminacija živil neposredno povezana s kontaminacijo krme, je treba sprejeti celosten pristop za zmanjšanje razširjenosti dioksina in dioksinom podobnih PCB v celotni prehranski verigi, tj. od krmil prek živali, namenjenih prehrani, do ljudi.
Operators need to make efforts to step up their capacity effectively to remove dioxins, furans and dioxin-like PCBs from marine oil.
Proizvajalci si morajo prizadevati za povečanje svoje zmogljivosti za učinkovito 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.
Znatno nižja vrednost, ki se preuči do 31. decembra 2008, temelji na tehničnih možnostih najučinkovitejšega postopka dekontaminacije.
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 majhne otroke glede na podatke spremljanja, pridobljene s programi za spremljanje dioksinov in dioksinom podobnih PCB v hrani za dojenčke in majhne otroke iz leta 2005, 2006 in 2007.
Paragraph 1a is replaced by the following:
Odstavek 1a se nadomesti z naslednjim:
By way of derogation from paragraph 1, Finland and Sweden are authorised, for a transitional period extending to 31 December 2011, to place on their market salmon (Salmo salar), herring (Clupea harengus), river lamprey (Lampetra fluviatilis), trout (Salmo trutta), char (Salvelinus spp.) and roe of vendace (Coregonus albula) originating in the Baltic region and intended for consumption in their territory with levels of dioxins and/or levels of the sum of dioxins and dioxin-like PCBs higher than those set in point 5.2 of section 5 of Annex I, 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 these fish species from the Baltic region by identified vulnerable sections of the population in order to avoid potential health risks.
Z odstopanjem od odstavka 1 smeta Finska in Švedska v prehodnem obdobju, podaljšanem do 31. decembra 2011, dajati v promet na svojem ozemlju lososa (Salmo salar), sled (Clupea harengus), rečnega piškurja (Lampetra fluviatilis), postrv (Salmo trutta), zlatovčice (Salvelinus spp) in male ozimice (Coregonus albula), ki izvirajo iz baltske regije in so namenjene prehrani na njihovem ozemlju, z vrednostmi dioksinov in/ali vrednostmi vsote dioksinov in dioksinom podobnih PCB, višjimi od vrednosti iz točke 5.2 razdelka 5 Priloge I, pod pogojem, da deluje sistem, ki potrošnikom zagotavlja, da so v celoti obveščeni o prehranskih priporočilih glede omejitev porabe teh vrst rib iz baltske regije s strani opredeljenih občutljivih skupin prebivalstva, da bi se izognili morebitnemu zdravstvenemu tveganju.
By 31 March each year, Finland and Sweden shall communicate to the Commission the results of their monitoring of the levels of dioxins and dioxin-like PCBs in fish from the Baltic region obtained in the preceding year and shall report on the measures taken to reduce human exposure to dioxins and dioxin-like PCBs from fish from the Baltic region.
Do 31. marca vsako leto Finska in Švedska sporočita Komisiji rezultate spremljanja vrednosti dioksinov in dioksinom podobnih PCB v ribah iz baltske regije, pridobljene v prejšnjem letu, in poročata o ukrepih, sprejetih za zmanjšanje izpostavljenosti ljudi dioksinom in dioksinom podobnim PCB, ki jih vsebujejo ribe iz baltske regije.
Finland and Sweden shall continue to implement the necessary measures to ensure that fish and fish products not complying with point 5.2 of Section 5 of Annex I are not marketed in other Member States.’
Finska in Švedska še naprej izvajata potrebne ukrepe za zagotovitev, da ribe in proizvodi iz rib, ki niso v skladu s točko 5.2 razdelka 5 Priloge I, niso dani v promet v drugih državah članicah.“
The maximum levels specified in the Annex I shall apply to the edible part of the foodstuffs concerned, unless otherwise specified in that Annex.’
Mejne vrednosti, opredeljene v Prilogi I, se uporabljajo za užitni del zadevnih živil, razen če je v tej prilogi določeno drugače.“
Article 4a is replaced by the following:
Člen 4a se nadomesti z naslednjim:
With regard to dioxins and the sum of dioxins and dioxin-like PCBs in products as referred to in section 5 of Annex I, it shall be prohibited:
Glede dioksinov in vsoto dioksinov in dioksinom podobnih PCB v proizvodih iz razdelka 5 Priloge I je prepovedano:
to mix products complying with the maximum levels with products exceeding those maximum levels;
mešati proizvode, ki so v skladu z mejnimi vrednostmi, s proizvodi, ki presegajo te mejne vrednosti;
to use products not complying with the maximum levels as ingredients in the manufacture of other foodstuffs.’
uporabljati proizvode, ki niso v skladu z mejnimi vrednostmi, kot sestavine za proizvodnjo drugih živil.“
Article 5, paragraph 3 is deleted.
Člen 5(3) se črta.
It shall apply from 4 November 2006.
Uporablja se od 4. novembra 2006.
As regards the maximum levels for the sum of dioxins and dioxin-like PCBs, this Regulation shall not apply to products that were placed on the market before 4 November 2006 in accordance with the provisions applicable.
V zvezi z mejnimi vrednostmi za vsoto dioksinov in dioksinom podobnih PCB se ta uredba ne uporablja za proizvode, ki so bili dani v promet pred 4. novembrom 2006 v skladu z določbami, ki se uporabljajo.
The burden of proving when the products were placed on the market shall be borne by the food business operator.
Nosilec živilske dejavnosti dokaže, kdaj so bili proizvodi dani v promet.
Directive as amended by Commission Directive 2004/44/EC (OJ L 113, 20.4.2004, p. 17).
Direktiva, kakor je bila spremenjena z Direktivo Komisije 2004/44/ES (UL L 113, 20.4.2004, str. 17).
Section 5 of Annex I to Regulation (EC) No 466/2001 is replaced by the following:
Razdelek 5 Priloge I k uredbi (ES) št. 466/2001 se nadomesti z naslednjim:
‘Section 5.
„Razdelek 5.
Dioxins (sum of polychlorinated dibenzo-para-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs), expressed in World Health Organisation (WHO) toxic equivalents using the WHO-TEFs (toxic equivalency factors, 1997), and sum of dioxins and dioxin-like PCBs (sum of polychlorinated dibenzo-para-dioxins (PCDDs)), polychlorinated dibenzofurans (PCDFs) and polychlorinated biphenyls (PCBs), expressed in World Health Organisation (WHO) toxic equivalents using the WHO-TEFs (toxic equivalency factors, 1997) [1])
Dioksini (vsota polikloriranih dibenzo-para-dioksinov (PCDD) in polikloriranih dibenzofuranov (PCDF), izraženih v toksičnih ekvivalentih Svetovne zdravstvene organizacije (WHO) z uporabo WHO-TEF (faktorji toksične ekvivalence, 1997) ter vsota dioksinov in dioksinom podobnih PCB (vsota polikloriranih dibenzo-para-dioksinov (PCDD)), polikloriranih dibenzofuranov (PCDF) in polikloriranih bifenilov (PCB), izraženih v toksičnih ekvivalentih Svetovne zdravstvene organizacije (WHO) z uporabo WHO-TEF (faktorji ekvivalence toksičnosti, 1997) [1])
Maximum levels
Mejne vrednosti
Sum of dioxins and furans (WHO-PCDD/F-TEQ) [2]
Vsota dioksinov in furanov (WHO-PCDD/F-TEKV) [2]
Sum of dioxins, furans and dioxin-like PCBs (WHO-PCDD/F-PCB-TEQ) [2]
Vsota dioksinov, furanov in dioksinom podobnih PCB (WHO-PCDD/F-PCB-TEKV) [2]
Methods of sampling and performance criteria for methods of analysis
Metode vzorčenja in merila zmogljivosti za analitske metode
Meat and meat products [3]
Meso in proizvodi iz mesa [3]
Directive 2002/69/EC [5]
Direktiva Komisije 2002/69/ES [5]
of ruminants (bovine animals, sheep)
prežvekovalcev (govedo, ovce)
3,0 pg/g fat [4]
3,0 pg/g maščobe [4]
4,5 pg /g fat [4]
4,5 pg/g maščobe [4]
2,0 pg/g fat [4]
2,0 pg/g maščobe [4]
4,0 pg/g fat [4]
4,0 pg/g maščobe [4]
1,0 pg/g fat [4]
1,0 pg/g maščobe [4]
1,5 pg/g fat [4]
1,5 pg/g maščobe [4]
Liver of terrestrial animals and derived products thereof
Jetra in predelani proizvodi kopenskih živali
6,0 pg/g fat [4]
6,0 pg/g maščobe [4]
12,0 pg/g fat [4]
12,0 pg/g maščobe [4]
Muscle meat of fish and fishery products and products thereof with the exception of eel [6] [7]
Meso mišic rib in ribiški proizvodi ter njihovi proizvodi, razen jegulj [6], [7]
4,0 pg/g fresh weight
4,0 pg/g sveže teže
8,0 pg/g fresh weight
8,0 pg/g sveže teže
Muscle meat of eel (Anguilla anguilla) and products thereof
Meso mišic jegulj (Anguilla anguilla) in njihovi proizvodi
12,0 pg/g fresh weight
12,0 pg/g sveže teže
Animal fat
živalska maščoba
of ruminants
prežvekovalcev
3,0 pg/g fat
3,0 pg/g maščobe
4,5 pg/g fat
4,5 pg/g maščobe
2,0 pg/g fat
2,0 pg/g maščobe
4,0 pg/g fat
4,0 pg/g maščobe
marine oil (fish body oil, fish liver oil and oils of other marine organisms intended for human consumption)
olje morskih organizmov (olje iz trupov rib, olje ribjih jeter in olja drugih morskih organizmov za prehrano ljudi)
10,0 pg/g fat
10,0 pg/g maščobe
WHO TEFs for human risk assessment based on the conclusions of the World Health Organisation meeting in Stockholm, Sweden, 15 to 18 June 1997 (Van den Berg et al., (1998) Toxic Equivalency Factors (TEFs) for PCBs, PCDDs, PCDFs for Humans and for Wildlife.
WHO-TEF za oceno tveganja za zdravje ljudi na podlagi sklepov zasedanja Svetovne trgovinske organizacije v Stockholmu na Švedskem, 15.–18. junija 1997 (Van den Berg et al., (1998) Toxic Equivalency Factors (TEFs) for PCBs, PCDDs, PCDFs for Humans and for Wildlife.
Environmental Health Perspectives, 106(12), 775).CongenerTEF valueDibenzo-p-dioxins (PCDDs)2,3,7,8-TCDD11,2,3,7,8-PeCDD11,2,3,4,7,8-HxCDD0,11,2,3,6,7,8-HxCDD0,11,2,3,7,8,9-HxCDD0,11,2,3,4,6,7,8-HpCDD0,01OCDD0,0001Dibenzofurans (PCDFs)2,3,7,8-TCDF0,11,2,3,7,8-PeCDF0,052,3,4,7,8-PeCDF0,51,2,3,4,7,8-HxCDF0,11,2,3,6,7,8-HxCDF0,11,2,3,7,8,9-HxCDF0,12,3,4,6,7,8-HxCDF0,11,2,3,4,6,7,8-HpCDF0,011,2,3,4,7,8,9-HpCDF0,01OCDF0,0001“Dioxin-like” PCBsNon-ortho PCBs + Mono-ortho PCBsNon-ortho PCBsPCB 770,0001PCB 810,0001PCB 1260,1PCB 1690,01Mono-ortho PCBsPCB 1050,0001PCB 1140,0005PCB 1180,0001PCB 1230,0001PCB 1560,0005PCB 1570,0005PCB 1670,00001PCB 1890,0001Abbreviations used: “T” = tetra; “Pe” = penta; “Hx” = hexa; “Hp” = hepta; “O” = octa; “CDD” = chlorodibenzodioxin; “CDF” = chlorodibenzofuran; “CB” = chlorobiphenyl.
Environmental Health Perspectives, 106(12), 775)SpojinaVrednost TEFDibenzo-p-dioksini (PCDD)2,3,7,8-TCDD11,2,3,7,8-PeCDD11,2,3,4,7,8-HxCDD0,11,2,3,6,7,8-HxCDD0,11,2,3,7,8,9-HxCDD0,11,2,3,4,6,7,8-HpCDD0,01OCDD0,0001Dibenzofurani (PCDF)2,3,7,8-TCDF0,11,2,3,7,8-PeCDF0,052,3,4,7,8-PeCDF0,51,2,3,4,7,8-HxCDF0,11,2,3,6,7,8-HxCDF0,11,2,3,7,8,9-HxCDF0,12,3,4,6,7,8-HxCDF0,11,2,3,4,6,7,8-HpCDF0,011,2,3,4,7,8,9-HpCDF0,01OCDF0,0001Dioksinom podobni PCBne-orto PCB + mono-orto PCBNe-orto PCBPCB 770,0001PCB 810,0001PCB 1260,1PCB 1690,01Mono-orto PCBPCB 1050,0001PCB 1140,0005PCB 1180,0001PCB 1230,0001PCB 1560,0005PCB 1570,0005PCB 1670,00001PCB 1890,0001Uporabljene okrajšave: ‚T‘ = tetra; ‚Pe‘ = penta; ‚Hx‘ = heksa; ‚Hp‘ = hepta; ‚O‘ = okta; ‚CDD‘ = klorodibenzodioksin; ‚CDF‘ = klorodibenzofuran; ‚CB‘ = klorobifenil.
Upperbound concentrations: Upperbound concentrations are calculated on the assumption that all the values of the different congeners below the limit of quantification are equal to the limit of quantification.
Zgornje koncentracije: Zgornje koncentracije so izračunane ob predpostavki, da so vse vrednosti različnih sorodnih spojin pod mejo določanja enake meji določanja.
Meat of bovine animals, sheep, pig, poultry and farmed game as defined in Annex I to Regulation (EC) No 853/2004 of the European Parliament and of the Council (OJ L 139, 30.4.2004.
Meso goveda, ovc, prašičev, perutnine in gojene divjadi, kot je opredeljeno v Prilogi I k Uredbi (ES) št. 853/2004 Evropskega parlamenta in Sveta (UL L 139, 30.4.2004.
Corrected version in OJ L 226, 25.6.2004, p. 22) but not including edible offal as defined in that Annex.
Popravljena različica v UL L 226, 25.6.2004, str. 22), razen užitne drobovine, kot je opredeljena v navedeni prilogi.
The maximum levels are not applicable for food products containing < 1 % fat.
Mejne vrednosti se ne uporabljajo za živila, ki vsebujejo < 1 % maščobe.
Directive as last amended by Directive 2004/44/EC (OJ L 113, 20.4.2004, p. 17).
Direktiva, kakor je bila nazadnje spremenjena z Direktivo 2004/44/ES (UL L 113, 20.4.2004, str. 17).
The maximum level applies to crustaceans, excluding the brown meat of crab and excluding head and thorax meat of lobster and similar large crustaceans (Nephropidae and Palinuridae) and to cephalopods without viscera.
Mejna vrednost se uporablja za rake, razen rjavega mesa rakov ter mesa glave in prsi jastoga in podobnih velikih rakov (Nephropidae in Palinuridae), ter za glavonožce brez drobovine.
Where fish are intended to be eaten whole, the maximum level applies to the whole fish.
Če se ribe uživajo cele, velja mejna vrednost za celo ribo.
Milk (raw milk, milk for the manufacture of milk-based products and heat-treated milk as defined in Annex I to Regulation (EC) No 853/2004).
Mleko (surovo mleko, mleko za izdelavo proizvodov na osnovi mleka in toplotno obdelano mleko, kot je opredeljeno v Prilogi I k Uredbi (ES) št. 853/2004.
Hen eggs and egg products as defined in Annex I to Regulation (EC) No 853/2004.’
Kokošja jajca in jajčni proizvodi, kot so opredeljeni v Prilogi I k Uredbi (ES) št. 853/2004.“
Commission Regulation (EC) No 200/2006
Uredba Komisije (ES) št. 200/2006
These prices and duties were last amended by Commission Regulation (EC) No 159/2006 [4].
Navedene cene in dolžnosti so bile nazadnje spremenjene z Uredbo Komisije (ES) št. 159/2006 [4].
OJ L 25, 28.1.2006, p. 19.
UL L 25, 28.1.2006, str. 19.
Amended representative prices and additional duties applicable to imports of white sugar, raw sugar and products covered by CN code 17029099 applicable from 4 February 2006
Spremenjeni zneski reprezentativnih cen in dodatnih uvoznih dajatev za beli sladkor, surovi sladkor in proizvode pod oznako KN 17029099, ki se uporabljajo od 4. februarja 2006
Commission Regulation (EC) No 201/2006
Uredba Komisije (ES) št. 201/2006
altering the export refunds on white sugar and raw sugar exported in the natural state fixed by Regulation (EC) No 186/2006
o spremembi izvoznih nadomestil za beli sladkor in surovi sladkor, izvožena v nespremenjenem stanju, določenih z Uredbo (ES) št. 186/2006
The export refunds on white sugar and raw sugar exported in the natural state were fixed by Commission Regulation (EC) No 186/2006 [2]
Nadomestila za beli sladkor in surovi sladkor, izvožena v nespremenjenem stanju, so bila določena z Uredbo Komisije (ES) št. 186/2006 [2]
Since the data currently available to the Commission are different to the data at the time Regulation (EC) No 186/2006 was adopted, those refunds should be adjusted,
Podatki, s katerimi Komisija trenutno razpolaga, se razlikujejo od podatkov v času sprejetja Uredbe (ES) št. 186/2006, zato je treba ta nadomestila spremeniti –