natgillin/translations-raw huggingface dataset:
In cases where the goods have been damaged before entry into free circulation and, therefore, the price actually paid or payable is apportioned for the determination of the customs value pursuant to Article 145 of Commission Regulation (EEC) No 2454/93 of 2 July 1993 laying down provisions for the implementation of Council Regulation (EEC) No 2913/92 establishing the Community Customs Code [7], the amount of the anti-dumping duty, calculated on the basis of the fixed amounts set above, shall be reduced by a percentage which corresponds to the apportioning of the price actually paid or payable.
V primerih, ko se blago poškoduje še pred vstopom v prost promet, in se zato dejansko plačana ali plačljiva cena pri določanju carinske vrednosti porazdeli v skladu s členom 145 Uredbe Komisije (EGS) št. 2454/93 z dne 2. julija 1993 o določbah za izvajanje Uredbe Sveta (EGS) št. 2913/92 o carinskem zakoniku Skupnosti [7], se znesek protidampinške dajatve, izračunan na podlagi zgoraj določenih fiksnih zneskov, zmanjša za odstotek, ki ustreza porazdelitvi dejansko plačane ali plačljive cene.
This Regulation shall enter into force on the day following its publication in the Official Journal of the European Union and shall be in force for a period of 5 years.
Ta uredba začne veljati dan po objavi v Uradnem listu Evropske unije in velja za obdobje petih let.
OJ L 189, 21.7.2005, p. 15.
UL L 189, 21.7.2005, str. 15.
OJ C 78, 27.3.2010, p. 4.
UL C 78, 27.3.2010, str. 4.
OJ C 192, 16.7.2010, p. 4.
UL C 192, 16.7.2010, str. 4.
Indian anti-dumping duties against Chinese barium carbonate range from 76,06 USD to 236 USD per ton; US anti-dumping duties against Chinese barium carbonate range from 34,4 to 81,3 %.
Indijske protidampinške dajatve za kitajski barijev karbonat so v višini od 76,06 USD do 236 USD na tono; protidampinške dajatve ZDA za kitajski narijev karbonat so v višini od 34,4 % do 81,3 %.
Source: Chinese export statistics.
Vir: kitajska izvozna statistika.
Solvay Vishnu Barium Private Limited, Hyderabad
Solvay Vishnu Barium Private Limited, Hyderabad;
Commission Implementing Regulation (EU) No 832/2011
Izvedbena uredba Komisije (EU) št. 832/2011
This Regulation shall enter into force on 19 August 2011.
Ta uredba začne veljati 19. avgusta 2011.
Commission Implementing Regulation (EU) No 833/2011
Izvedbena uredba Komisije (EU) št. 833/2011
These prices and duties have been last amended by Commission Implementing Regulation (EU) No 823/2011 [4].
Navedene cene in dolžnosti so bile nazadnje spremenjene z Izvedbeno uredbo Komisije (EU) št. 823/2011 [4].
OJ L 209, 17.8.2011, p. 41.
UL L 209, 17.8.2011, str. 41.
Amended representative prices and additional import duties applicable to white sugar, raw sugar and products covered by CN code 17029095 from 19 August 2011
Spremenjene reprezentativne cene in dodatne uvozne dajatve za beli in surovi sladkor ter proizvode z oznako KN 17029095, ki se uporabljajo od 19. avgusta 2011
Commission Regulation (EU) No 834/2011
Uredba Komisije (EU) št. 834/2011
Regulation (EC) No 689/2008 implements the Rotterdam Convention on the Prior Informed Consent Procedure for certain hazardous chemicals and pesticides in international trade, signed on 11 September 1998 and approved, on behalf of the Community, by Council Decision 2003/106/EC [2].
Rotterdamska konvencija o postopku soglasja po predhodnem obveščanju za določene nevarne kemikalije in pesticide v mednarodni trgovini, ki je bila podpisana 11. septembra 1998 in odobrena v imenu Skupnosti s Sklepom Sveta 2003/106/ES [2], se izvaja z Uredbo (ES) št. 689/2008.
Annex I to Regulation (EC) No 689/2008 should be amended to take into account regulatory action in respect of certain chemicals taken pursuant to Council Directive 91/414/EEC of 15 July 1991 concerning the placing of plant protection products on the market [3], Directive 98/8/EC of the European Parliament and of the Council of 16 February 1998 concerning the placing of biocidal products on the market [4] and Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the registration, evaluation, authorisation and restriction of chemicals (REACH), establishing a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC) No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council Directive 76/769/EEC and Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC [5].
Prilogo I k Uredbi (ES) št. 689/2008 je treba spremeniti, da bi se upoštevali ureditveni ukrepi za nekatere kemikalije, sprejeti v skladu z Direktivo Sveta 91/414/EGS z dne 15. julija 1991 o dajanju fitofarmacevtskih sredstev v promet [3], Direktivo 98/8/ES Evropskega parlamenta in Sveta z dne 16. februarja 1998 o dajanju biocidnih pripravkov v promet [4] in Uredbo (ES) št. 1907/2006 Evropskega Parlamenta in Sveta z dne 18. decembra 2006 o registraciji, evalvaciji, avtorizaciji in omejevanju kemikalij (REACH), o ustanovitvi Evropske agencije za kemikalije ter spremembi Direktive 1999/45/ES ter razveljavitvi Uredbe Sveta (EGS) št. 793/93 in Uredbe Komisije (ES) št. 1488/94 ter Direktive Sveta 76/769/EGS in direktiv Komisije 91/155/EGS, 93/67/EGS, 93/105/ES in 2000/21/ES [5].
The substances ethalfluralin, indolylacetic acid and thiobencarb have not been included as active substances in Annex I to Directive 91/414/EEC, with the effect that those active substances are banned for pesticide use and thus should be added to the lists of chemicals contained in Parts 1 and 2 of Annex I to Regulation (EC) No 689/2008.
Snovi etalfluralin, indolilocetna kislina in tiobenkarb niso bile vključene kot aktivne snovi v Prilogo I k Direktivi 91/414/EGS in se tako ne smejo uporabljati kot pesticidi ter jih je treba dodati na seznama kemikalij iz delov 1 in 2 Priloge I k Uredbi (ES) št. 689/2008.
The substance guazatine has not been included as an active substance in Annex I to Directive 91/414/EEC and guazatine, as referred to as guazatine triacetate, has not been included as an active substance in Annex I, IA or IB to Directive 98/8/EC, with the effect that guazatine is banned for pesticide use and thus should be added to the lists of chemicals contained in Parts 1 and 2 of Annex I to Regulation (EC) No 689/2008.
Snov guazatin ni bila vključena kot aktivna snov v Prilogo I k Direktivi 91/414/EGS, guazatin, t. i. guazatin triacetat, pa ni bil vključen kot aktivna snov v Prilogo I, IA ali IB k Direktivi 98/8/ES in se tako ne sme uporabljati kot pesticid ter ga je zato treba dodati na seznama kemikalij iz delov 1 in 2 Priloge I k Uredbi (ES) št. 689/2008.
Therefore, the substance guazatine should be added to the lists of chemicals contained in Parts 1 and 2 of Annex I to Regulation (EC) No 689/2008.
Ta novi zahtevek je vlagatelj umaknil, tako da ni več razloga, da snovi ne bi vključili v Prilogo I. Snov guazatin je zato treba dodati na sezname kemikalij iz delov 1 in 2 Priloge I k Uredbi (ES) št. 689/2008.
The substance 1,3-dichloropropene has not been included as an active substance in Annex I to Directive 91/414/EEC, with the effect that 1,3-dichloropropene is banned for pesticide use and thus should be added to the lists of chemicals contained in Parts 1 and 2 of Annex I to Regulation (EC) No 689/2008.
Snov 1,3-dikloropropen ni bila vključena kot aktivna snov v Prilogo I k Direktivi 91/414/EGS in se ne sme uporabljati kot pesticid ter jo je zato treba dodati na seznama kemikalij iz delov 1 in 2 Priloge I k Uredbi (ES) št. 689/2008.
The addition of 1,3-dichloropropene to Part 2 of Annex I was suspended due to a new application for inclusion in Annex I to Directive 91/414/EEC submitted pursuant to Article 13 of Regulation (EC) No 33/2008.
Vključitev 1,3-dikloropropena v del 2 Priloge I je bila odložena, ker je bil na podlagi člena 13 Uredbe (ES) št. 33/2008 vložen nov zahtevek za vključitev v Prilogo I k Direktivi 91/414/EGS.
The substance haloxyfop-P has been included as an active substance in Annex I to Directive 91/414/EEC, with the effect that haloxyfop-P is no longer banned for pesticide use.
Snov haloksifop-P je bila vključena kot aktivna snov v Prilogo I k Direktivi 91/414/EGS in je tako ni več prepovedano uporabljati kot pesticid.
Consequently the active substance, as referred to as haloxyfop-R, should be deleted from Part 1 of Annex I to Regulation (EC) No 689/2008.
Zato je treba aktivno snov, t. i. haloksifop-R, črtati iz dela 1 Priloge I k Uredbi (ES) št. 689/2008.
In order to allow enough time for Member States and industry to take the measures necessary for the implementation of this Regulation, its application should be deferred.
Da bi države članice in industrija imele dovolj časa, da sprejmejo potrebne ukrepe za izvajanje te uredbe, je treba njeno uporabo odložiti.
Indolylacetic acid +
Indolilocetna kislina +
‘Haloxyfop-R +
„Haloksifop-R +
in Part 2 the following entries are added:
Del 2 se spremeni dodajo se naslednji vnosi:
‘1,3-dichloropropene
„1,3-dikloropropen
Indolylacetic acid
Indolilocetna kislina
The addition of guazatine to Annex I was suspended due to a new application for inclusion in Annex I to Directive 91/414/EEC submitted pursuant to Article 13 of Commission Regulation (EC) No 33/2008 of 17 January 2008 laying down detailed rules for the application of Council Directive 91/414/EEC as regards a regular and an accelerated procedure for the assessment of active substances which were part of the programme of work referred to in Article 8(2) of that Directive but have not been included into its Annex I [6]. This new application has been withdrawn by the applicant with the effect that the reason for suspending the addition to Annex I disappeared.
Vključitev guazatina v Prilogo I je bila začasno odložena zaradi vložitve nove vloge za vključitev v Prilogo I k Direktivi 91/414/EGS na podlagi člena 13 Uredbe Komisije (ES) št. 33/2008 z dne 17. januarja 2008 o podrobnih pravilih za izvajanje Direktive Sveta 91/414/EGS glede rednega in pospešenega postopka za oceno aktivnih snovi, ki so bile del programa dela iz člena 8(2) navedene direktive, vendar niso bile vključene v Prilogo I [6].
This new application resulted again in the decision not to include the substance 1,3-dichloropropene as an active substance in Annex I to Directive 91/414/EEC with the effect that 1,3-dichloropropene remains banned for pesticide use and that the reason for suspending the addition to Part 2 of Annex I disappeared. Therefore, the substance 1,3-dichloropropene should be added to the list of chemicals contained in Part 2 of Annex I to Regulation (EC) No 689/2008.
Zaradi tega novega zahtevka je bilo ponovno odločeno, da se snov 1,3-dikloropropen ne vključi kot aktivna snov v Prilogo I k Direktivi 91/414/EGS, zaradi česar se ne sme uporabljati kot pesticid ter ni več razloga, da 1,3-dikloropropena ne bi vključili v del 2 Priloge I. Snov 1,3-dikloropropen je zato treba dodati na seznam kemikalij iz dela 2 Priloge I k Uredbi (ES) št. 689/2008.
Commission Regulation (EU) No 835/2011
Uredba Komisije (EU) št. 835/2011
amending Regulation (EC) No 1881/2006 as regards maximum levels for polycyclic aromatic hydrocarbons in foodstuffs
o spremembi Uredbe Komisije (ES) št. 1881/2006 glede mejnih vrednosti policikličnih aromatskih ogljikovodikov v živilih
Commission Regulation (EC) No 1881/2006 setting maximum levels for certain contaminants in foodstuffs [2] sets maximum levels for benzo(a)pyrene in a range of foodstuffs.
Uredba Komisije (ES) št. 1881/2006 o določitvi mejnih vrednosti nekaterih onesnaževal v živilih [2] določa mejne vrednosti benzo(a)pirena v izboru živil.
Benzo(a)pyrene belongs to the group of polycyclic aromatic hydrocarbons (PAH) and is used as a marker for the occurrence and effect of carcinogenic PAH in food based on a scientific opinion of the former Scientific Committee on Food (SCF) [3].
Benzo(a)piren spada v skupino policikličnih aromatskih ogljikovodikov (PAH) in se uporablja kot kazalnik prisotnosti in vpliva rakotvornih PAH v hrani na podlagi znanstvenega mnenja nekdanjega Znanstvenega odbora za hrano (SCF) [3].
In its opinion of December 2002, the SCF recommended that further analyses of the relative proportions of these PAH in foods would be necessary for a future review of the suitability of maintaining benzo(a)pyrene as a marker.
Znanstveni odbor za hrano je v svojem mnenju iz decembra 2002 priporočil, da bi bile nadaljnje analize relativnih deležev teh PAH v hrani nujne za prihodnji pregled primernosti nadaljnje uporabe benzo(a)pirena kot kazalnika.
New data on occurrence of carcinogenic PAH in foodstuffs have been collected by the Member States in the framework of Commission Recommendation 2005/108/EC [4].
Nove podatke o prisotnosti rakotvornih PAH v živilih so zbrale države članice v okviru Priporočila Komisije 2005/108/ES [4].
The Commission asked the European Food Safety Authority (EFSA) to review the SCF opinion taking into account the new occurrence data, other relevant new scientific information as well as the Margin of Exposure (MOE) approach.
Komisija je pozvala Evropsko agencijo za varnost hrane (EFSA), da pregleda mnenje Znanstvenega odbora za hrano, pri čemer naj upošteva nove podatke o prisotnosti, druge ustrezne nove znanstvene informacije ter pristop stopenj izpostavljenosti (MOE).
Within this review, EFSA was asked to re-assess the suitability of maintaining benzo(a)pyrene as a marker.
V okviru tega pregleda je bila EFSA pozvana, da ponovno oceni primernost nadaljnje uporabe benzo(a)pirena kot kazalnika.
The Scientific Panel on Contaminants in the Food Chain (CONTAM Panel) of EFSA adopted an opinion on Polycyclic Aromatic Hydrocarbons in Food on 9 June 2008 [5].
Znanstveni odbor za onesnaževalce v prehranjevalni verigi (odbor CONTAM) Evropske agencije za varnost hrane je 9. junija 2008 sprejel mnenje o policikličnih aromatskih ogljikovodikih v hrani [5].
In this opinion EFSA concluded that benzo(a)pyrene is not a suitable marker for the occurrence of polycyclic aromatic hydrocarbons in food and that a system of four specific substances (PAH4 [6]) or eight specific substances (PAH8 [7]) would be the most suitable indicators of PAH in food.
V tem mnenju je EFSA ugotovila, da benzo(a)piren ni primeren kazalnik prisotnosti policikličnih aromatskih ogljikovodikov v hrani ter da bi bil najprimernejši pokazatelj PAH v hrani sistem štirih posebnih snovi (PAH4 [6]) ali osmih posebnih snovi (PAH8 [7]).
EFSA also concluded that a system of eight substances (PAH8) would not provide much added value compared to a system of four substances (PAH4).
EFSA je ugotovila tudi, da se s sistemom osmih snovi (PAH8) ne bi zagotovila večja dodana vrednost v primerjavi s sistemom štirih snovi (PAH4).
Furthermore, the CONTAM Panel concluded, using the Margin of Exposure (MOE) approach, that there is low concern for consumer health at the average estimated dietary exposures.
Poleg tega je odbor CONTAM z uporabo pristopa stopenj izpostavljenosti ugotovil, da je stopnja ogroženosti zdravja potrošnikov pri povprečno ocenjeni prehranski izpostavljenosti nizka.
However, for high level consumers the MOEs were close to or less than 10000, which indicates a potential concern for consumer health.
Kljub temu so bile stopnje izpostavljenosti pri nadpovprečnih potrošnikih blizu ali manjše od 10000, kar kaže na morebitno ogroženost zdravja potrošnikov.
Based on the conclusions of EFSA, the current system of using benzo(a)pyrene as the only marker for the group of polycyclic aromatic hydrocarbons, can not be maintained.
Na podlagi ugotovitev Evropske agencije za varnost hrane sedanjega sistema uporabe benzo(a)pirena kot edinega kazalnika za skupino policikličnih aromatskih ogljikovodikov ni mogoče ohraniti.
An amendment of Regulation (EC) No 1881/2006 is therefore necessary.
Sprememba Uredbe (ES) št. 1881/2006 je tako nujna.
New maximum levels for the sum of four substances (PAH4) (benzo(a)pyrene, benz(a)anthracene, benzo(b)fluoranthene and chrysene) should be introduced, whilst maintaining a separate maximum level for benzo(a)pyrene.
Uvesti je treba nove mejne vrednosti za skupno vrednost štirih snovi (PAH4) (benzo(a)piren, benz(a)antracen, benzo(b)fluoranten in krizen), pri tem pa ohraniti ločeno mejno vrednost za benzo(a)piren.
Such system would ensure that PAH levels in food are kept at levels that do not cause health concern and that the amount of PAH can also be controlled in those samples in which benzo(a)pyrene is not detectable, but where other PAH are present.
S takim sistemom bi se zagotovilo, da so vrednosti PAH v hrani v mejah, ki ne ogrožajo zdravja, ter da je količino PAH mogoče nadzirati tudi v vzorcih, v katerih benzo(a)pirena ni mogoče zaznati, prisotni pa so drugi PAH.
The separate maximum level for benzo(a)pyrene is maintained to ensure comparability of previous and future data.
Ločena mejna vrednost za benzo(a)piren se ohrani, da se zagotovi primerljivost s predhodnimi in prihodnjimi podatki.
After a certain time of implementation of this amendment and on basis of new data that will be generated in future, the need for retaining a separate maximum level for benzo(a) pyrene should be re-assessed.
Po določenem času izvajanja te spremembe in na podlagi novih podatkov, ki bodo pridobljeni v prihodnosti, je treba ponovno oceniti potrebo po ohranitvi ločene mejne vrednosti za benzo(a) piren.
As regards the sum of the four substances (PAH4), lower bound concentrations should be used as the basis for compliance decisions.
Kar zadeva skupno vrednost štirih snovi (PAH4), je treba odločitve o skladnosti sprejeti na podlagi spodnjih koncentracij.
Maximum levels for polycyclic aromatic hydrocarbons must be safe and as low as reasonably achievable (ALARA) based upon good manufacturing and agricultural/fishery practices.
Mejne vrednosti za policiklične aromatske ogljikovodike morajo biti varne in tako nizke, kot jih je razumno še mogoče doseči (ALARA) na podlagi dobre proizvodne in kmetijske/ribiške dejavnosti.
The new PAH occurrence data show that background levels of PAH are lower than previously thought in some food commodities.
Novi podatki o prisotnosti PAH kažejo, da so v nekaterih živilih ravni prisotnosti PAH, kot je veljalo doslej.
Benzo(a)pyrene maximum levels have therefore been adapted to reflect more realistic lower background levels in fresh and smoked bivalve molluscs.
Mejne vrednosti benzo(a)pirena so bile zato prilagojene, tako da izražajo bolj realne nižje ravni prisotnosti v svežih in prekajenih školjkah.
Data for smoked fish and smoked meat have also shown that lower maximum levels are achievable.
Tudi podatki za prekajene ribe in prekajeno meso so pokazali, da je mogoče doseči nižje mejne vrednosti.
Nevertheless, adaptations of current smoking technology may be necessary in some cases.
Kljub temu bodo v nekaterih primerih morda nujne prilagoditve sedanje tehnologije prekajevanja.
Therefore, a two step procedure should be established for smoked meat and smoked fish which grants a transition of two years from the date of application of this Regulation before lower maximum levels become applicable.
Zato je treba za prekajeno meso in prekajene ribe določiti postopek v dveh korakih, ki omogoča, da se od začetka veljavnosti te uredbe do začetka uporabe nižjih mejnih vrednosti uporablja dveletno prehodno obdobje.
Smoked sprats and canned smoked sprats have been found to contain higher levels of PAH than other smoked fish.
Ugotovljeno je bilo, da prekajene papaline in konzervirane prekajene papaline vsebujejo višje vrednosti PAH kot druge prekajene ribe.
Specific maximum levels should be established for smoked sprats and canned smoked sprats in order to reflect what is achievable in these foodstuffs.
Za prekajene papaline in konzervirane prekajene papaline je treba določiti posebne mejne vrednosti, da bi se upoštevale dosegljive vrednosti za ta živila.
Previously a maximum level for benzo(a)pyrene in "muscle meat of fish other than smoked fish" was established as an indicator for potential environmental pollution.
Nekdaj je bila mejna vrednost za benzo(a)piren v „mišičnini rib, razen prekajenih rib“, določena kot pokazatelj morebitne onesnaženosti okolja.
Nevertheless, it has been shown that PAH are quickly metabolised in fresh fish and do not accumulate in the muscle meat.
Kljub temu je bilo ugotovljeno, da se PAH pri svežih ribah hitro prebavijo in se ne nabirajo v mišičnini.
Therefore, maintaining a maximum level for PAH in fresh fish is no longer appropriate.
Zato ohranitev mejne vrednosti za PAH pri svežih ribah ni več primerna.
High levels of PAH have been found in some types of heat treated meat and heat treated meat products sold to the final consumer.
Visoke vrednosti PAH so bile ugotovljene pri nekaterih vrstah toplotno obdelanega mesa in toplotno obdelanih mesnih izdelkov, ki se prodajajo končnim potrošnikom.
These levels are avoidable if appropriate processing conditions and equipment are used.
Tem vrednostim se je mogoče izogniti ob ustreznih pogojih obdelave in uporabi ustrezne opreme.
It is therefore appropriate to establish maximum levels for PAH in meat and meat products that have undergone a heat treatment process known to potentially result in formation of PAH, i.e. only grilling and barbecuing.
Zato je primerno določiti mejne vrednosti za PAH v mesu in mesnih izdelkih, ki so bili toplotno obdelani s postopkom, za katerega je znano, da lahko povzroči prisotnost PAH, tj. samo pečenje in priprava na žaru.
Cocoa butter was temporarily exempted from the existing maximum level for benzo(a)pyrene in oils and fats under Regulation (EC) No 1881/2006 and a review of the appropriateness of setting a maximum level for PAH in cocoa butter was foreseen by 1 April 2007.
Kakavovo maslo je bilo začasno izvzeto iz obstoječe mejne vrednosti za benzo(a)piren v oljih in maščobah v skladu z Uredbo (ES) št. 1881/2006, pri čemer je bil pregled primernosti določitve mejne vrednosti za PAH v kakavovem maslu predviden do 1. aprila 2007.
The review was then postponed pending the result of the then ongoing scientific re-assessment of PAH by EFSA.
Ta pregled je bil nato odložen zaradi čakanja na rezultate ponovne znanstvene ocene PAH, ki jo je takrat izvajala EFSA.
Cocoa butter contains higher levels of PAH than other oils and fats.
Kakavovo maslo vsebuje višje vrednosti PAH kot druga olja in maščobe.
This is mainly due to inappropriate drying practices of the cocoa beans and the fact that cocoa butter can not be refined as other vegetable oils and fats.
Vzrok za to so predvsem neprimerni načini sušenja kakavovih zrn in dejstvo, da kakavovega masla ni mogoče rafinirati, tako kot druga rastlinska olja in maščobe.
Cocoa butter is a main constituent of cocoa raw products (e.g. cocoa beans, cocoa mass, cocoa nibs or cocoa liquor) and is present in chocolate and other cocoa products often consumed by children.
Kakavovo maslo je glavna sestavina surovih kakavovih proizvodov (npr. kakavova zrna, kakavova masa, kakavova jedra ali kakavov liker), pri čemer je prisotno v čokoladi in drugih kakavovih proizvodih, ki jih pogosto uživajo otroci.
It thereby contributes to human exposure, in particular to exposure of children.
Tako prispeva k izpostavljenosti ljudi, zlasti otrok.
It is therefore necessary to establish maximum levels for PAH in cocoa beans and derived products, thereby also including cocoa butter.
Zato je nujno določiti mejne vrednosti za PAH v kakavovih zrnih in iz njih pridobljenih proizvodih, kar vključuje tudi kakavovo maslo.
Maximum levels for PAH in cocoa beans should be established at levels as low as reasonably achievable and taking into account the current technological possibilities of producing countries.
Mejne vrednosti za PAH v kakavovih zrnih je treba določiti tako nizko, kot jih je razumno še mogoče doseči, pri čemer je treba upoštevati sedanje tehnološke možnosti držav proizvajalk.
They should be established on a fat basis since PAH concentrate in the fat fraction, the cocoa butter.
Določiti jih je treba na podlagi maščobe, saj so PAH koncentrirani v maščobnih frakcijah, torej v kakavovem maslu.