natgillin/translations-raw huggingface dataset:
To allow producing countries to make technological improvements in order to adapt to these maximum levels, the date of application of the maximum levels for cocoa beans and derived products should be deferred.
Da bi državam proizvajalkam omogočili tehnološke izboljšave za prilagoditev tem mejnih vrednostim, je treba odložiti datum začetka uporabe mejnih vrednosti za kakavova zrna in iz njih pridobljene proizvode.
Furthermore, initially a higher maximum level for the sum of the four substances should apply to these products.
Prav tako je treba na začetku za te proizvode uporabiti višjo mejno vrednost za skupno vrednost štirih snovi.
After a transition period of two years a lower maximum level should apply.
Po dveletnem prehodnem obdobju je treba uporabiti nižjo mejno vrednost.
The levels of PAH in cocoa beans and derived products should be regularly monitored with a view to assessing the possibility for further decreasing the maximum levels in future.
Vrednosti PAH v kakavovih zrnih in iz njih pridobljenih proizvodih je treba redno spremljati, da se oceni možnost za dodatno zniževanje mejnih vrednosti v prihodnosti.
Data have shown that coconut oil can contain higher amounts of PAH4 than other vegetable oils and fats.
Podatki so pokazali, da ima lahko kokosovo olje višjo vsebnost PAH4 kot druga rastlinska olja in maščobe.
This is due to the proportionally higher presence of benz(a)anthracene and chrysene which can not be easily removed during refinement of coconut oil.
Razlog za to je sorazmerno višja prisotnost benz(a)antracena in krizena, ki ju je med rafiniranjem kokosovega olja težko odstraniti.
Specific maximum levels for coconut oil should therefore be set at levels as low as reasonably achievable and taking into account the current technological possibilities of producing countries.
Posebne mejne vrednosti za kokosovo olje je zato treba določiti tako, da so razumno dosegljive, pri čemer se upoštevajo sedanje tehnološke možnosti držav proizvajalk.
As technological improvements in producing countries are expected, the levels of PAH in coconut oil should be regularly monitored with a view to assessing the possibility for setting lower levels in future.
Ker se pričakujejo tehnološke izboljšave v državah proizvajalkah, je treba vrednosti PAH v kokosovem olju redno spremljati, da se oceni možnost določitve nižjih vrednosti v prihodnosti.
Current occurrence data on PAH in cereals and vegetables are limited.
Sedanji podatki o prisotnosti PAH v žitih in zelenjavi so omejeni.
The available data indicate that cereals and vegetables contain rather low levels of PAH.
Razpoložljivi podatki kažejo, da žita in zelenjava vsebujejo precej nizke vrednosti PAH.
The low levels seen in the currently available occurrence data do not justify the immediate setting of maximum levels.
Ker trenutno razpoložljivi podatki o prisotnosti kažejo, da so vrednosti nizke, takojšnja določitev mejnih vrednosti ni upravičena.
Nevertheless, EFSA identified cereals and vegetables as being important contributors to human exposure due to their high consumption.
Kljub temu je EFSA opredelila žita in zelenjavo kot živila, ki pomembno prispevajo k izpostavljenosti ljudi zaradi njihove visoke potrošnje.
Therefore, PAH levels in these two product groups should be further monitored.
Zato je treba še naprej spremljati vrednosti PAH v teh dveh skupinah proizvodov.
On the basis of further data, the need for setting maximum levels will be evaluated.
Na podlagi nadaljnjih podatkov bo ocenjena potreba po določitvi mejnih vrednosti.
High levels of PAH have been found in some food supplements.
Visoke vrednosti PAH so bile ugotovljene v nekaterih prehranskih dopolnilih.
Nevertheless, the levels are variable and depend on the specific type of food supplements.
Kljub temu te vrednosti nihajo in so odvisne od posamezne vrste prehranskih dopolnil.
Further data on food supplements are needed and should be collected.
Potrebni so dodatni podatki o prehranskih dopolnilih, pri čemer je treba te podatke zbirati.
Once these data become available, the need for setting maximum levels for PAH in food supplements will be evaluated.
Ko bodo ti podatki na voljo, bo ocenjena potreba po določitvi mejnih vrednosti za PAH v prehranskih dopolnilih.
Member States and food business operators should be allowed time to adapt to the maximum levels established by this Regulation.
Državam članicam in nosilcem živilske dejavnosti je treba zagotoviti dovolj časa za prilagoditev na mejne vrednosti, ki jih določa ta uredba.
The date of application of this Regulation should therefore be deferred.
Zato je treba odložiti datum začetka veljavnosti te uredbe.
A transitional period should be provided for the products already placed on the market before the date of application of the amendments introduced by this Regulation.
Za proizvode, ki so dani na trg že pred začetkom uporabe sprememb, uvedenih s to uredbo, je treba določiti prehodno obdobje.
The Annex to Regulation (EC) No 1881/2006 is amended in accordance with the Annex to this Regulation.
Priloga k Uredbi (ES) št. 1881/2006 se spremeni v skladu s Prilogo k tej uredbi.
Foodstuffs not complying with the maximum levels applicable from 1 September 2012 pursuant to Section 6 "Polycyclic aromatic hydrocarbons" of the Annex to Regulation (EC) No 1881/2006, as amended by this Regulation, which are lawfully placed on the market prior to 1 September 2012, may continue to be marketed after that date until their date of minimum durability or use-by-date.
Živila, ki niso v skladu z mejnimi vrednostmi, ki veljajo od 1. septembra 2012 v skladu z oddelkom 6 „Policiklični aromatski ogljikovodiki“ Priloge k Uredbi (ES) št. 1881/2006, kakor je bila spremenjena s to uredbo, pri čemer so ta živila zakonito dana na trg pred 1. septembrom 2012, se lahko tržijo po navedenem datumu do datuma minimalnega roka trajanja ali roka uporabe.
Foodstuffs not complying with the maximum levels applicable from 1 September 2014 pursuant to points 6.1.4 and 6.1.5 of the Annex to Regulation (EC) No 1881/2006, as amended by this Regulation, which are lawfully placed on the market prior to 1 September 2014, may continue to be marketed after that date until their date of minimum durability or use-by-date.
Živila, ki niso v skladu z mejnimi vrednostmi, ki veljajo od 1. septembra 2014 v skladu s točkama 6.1.4 in 6.1.5 Priloge k Uredbi (ES) št. 1881/2006, kakor je bila spremenjena s to uredbo, pri čemer so ta živila zakonito dana na trg pred 1. septembrom 2014, se lahko tržijo po navedenem datumu do datuma minimalnega roka trajanja ali roka uporabe.
Foodstuffs not complying with the maximum levels applicable from 1 April 2013 pursuant to point 6.1.2 of the Annex to Regulation (EC) No 1881/2006, as amended by this Regulation, which are lawfully placed on the market prior to 1 April 2013, may continue to be marketed after that date until their date of minimum durability or use-by-date.
Živila, ki niso v skladu z mejnimi vrednostmi, ki veljajo od 1. aprila 2013 v skladu s točko 6.1.2 Priloge k Uredbi (ES) št. 1881/2006, kakor je bila spremenjena s to uredbo, pri čemer so ta živila zakonito dana na trg pred 1. aprilom 2013, se lahko tržijo po navedenem datumu do datuma minimalnega roka trajanja ali roka uporabe.
Foodstuffs not complying with the maximum level applicable from 1 April 2015 pursuant to point 6.1.2 of the Annex to Regulation (EC) No 1881/2006, as amended by this Regulation, which are lawfully placed on the market prior to 1 April 2015, may continue to be marketed after that date until their date of minimum durability or use-by-date.
Živila, ki niso v skladu z mejno vrednostjo, ki velja od 1. aprila 2015 v skladu s točko 6.1.2 Priloge k Uredbi (ES) št. 1881/2006, kakor je bila spremenjena s to uredbo, pri čemer so ta živila zakonito dana na trg pred 1. aprilom 2015, se lahko tržijo po tem datumu do datuma minimalnega roka trajanja ali roka uporabe.
It shall apply from 1 September 2012.
Uporablja se od 1. septembra 2012.
Opinion of the Scientific Committee on Food on the risks to human health of Polycyclic Aromatic Hydrocarbons in food (expressed on 4 December 2002).http://ec.europa.eu/food/fs/sc/scf/out153_en.pdf
Mnenje Znanstvenega odbora za hrano o tveganju za zdravje ljudi zaradi policikličnih aromatskih ogljikovodikov v hrani (izraženo 4. decembra 2002).Http://ec.europa.eu/food/fs/sc/scf/out153_en.pdf.
Benzo(a)pyrene, Chrysene, Benz(a)anthracene, benzo(b)fluoranthene.
Benzo(a)piren, krizen, benz(a)antracen, benzo(b)fluoranten.
Benzo(a)pyrene, Chrysene, Benz(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene, benzo(g,h,i)perylene, dibenz(a,h)anthracene and indeno(1,2,3-c,d)pyrene.
Benzo(a)piren, krizen, Benz(a)antracen, benzo(b)fluoranten, benzo(k)fluoranten, benzo(g,h,i)perilen, dibenz(a,h)antracen in indeno(1,2,3-c,d)piren.
Section 6: Polycyclic aromatic hydrocarbons is replaced by the following:
Oddelek 6: Policiklični aromatski ogljikovodiki se nadomesti z naslednjim:
"Section 6:
„Oddelek 6:
Benzo(a)pyrene, benz(a)anthracene, benzo(b)fluoranthene and chrysene
benzo(a)piren, benz(a)antracen, benzo(b)fluoranten in krizen
Benzo(a)pyrene
benzo(a)piren
Sum of benzo(a)pyrene, benz(a)anthracene, benzo(b)fluoranthene and chrysene [1]
skupna vrednost benzo(a)pirena, benz(a)antracena, benzo(b)fluorantena in krizena [1]
Oils and fats (excluding cocoa butter and coconut oil) intended for direct human consumption or use as an ingredient in food
olja in maščobe (razen kakavovega masla in kokosovega olja), namenjeni neposredni prehrani ljudi ali uporabi kot sestavina živil
Cocoa beans and derived products
kakavova zrna in iz njih pridobljeni proizvodi
5,0 μg/kg fat as from 1.4.2013
5,0 μg/kg maščobe od 1. 4. 2013
35,0 μg/kg fat as from 1.4.2013 until 31.3.2015
35,0 μg/kg maščobe od 1. 4. 2013 do 31. 3. 2015
30,0 μg/kg fat as from 1.4.2015
30,0 μg/kg maščobe od 1. 4. 2015
Coconut oil intended for direct human consumption or use as an ingredient in food
kokosovo olje za neposredno prehrano ljudi ali kot sestavina živil
Smoked meat and smoked meat products
prekajeno meso in prekajeni mesni izdelki
Smoked sprats and canned smoked sprats (25) [3] (sprattus sprattus); bivalve molluscs (fresh, chilled or frozen) (26); heat treated meat and heat treated meat products [2] sold to the final consumer
prekajene papaline in konzervirane prekajene papaline (25) [3] (sprattus sprattus); školjke (sveže, hlajene ali zamrznjene) (26); toplotno obdelano meso in toplotno obdelani mesni izdelki [2] , ki se prodajajo končnim potrošnikom
Bivalve molluscs (36) (smoked)
školjke (36) (prekajene)
Processed cereal-based foods and baby foods for infants and young children (3)(29)
žitne kašice ter otroška hrana za dojenčke in majhne otroke (3)(29)
Infant formulae and follow-on formulae, including infant milk and follow-on milk (8)(29)
začetne in nadaljevalne formule za dojenčke, vključno z začetnim mlekom in nadaljevalnim mlekom (8)(29) za dojenčke
Dietary foods for special medical purposes (9)(29) intended specifically for infants
živila za posebne zdravstvene namene (9)(29), posebej za dojenčke
Endnote (35) is deleted.
Končna opomba (35) se črta
Lower bound concentrations are calculated on the assumption that all the values of the four substances below the limit of quantification are zero.
Spodnje koncentracije se izračunajo ob predpostavki, da so vse vrednosti štirih snovi pod mejo določanja enake nič.
Meat and meat products that have undergone a heat treatment potentially resulting in formation of PAH, i.e. only grilling and barbecuing.
Meso in mesni izdelki, ki so bili toplotno obdelani s postopkom, ki lahko povzroči prisotnost PAH, npr. samo pečenje in priprava na žaru.
For the canned product the analysis shall be carried out on the whole content of the can.
Pri konzerviranih izdelkih se analizira celotna vsebina konzerve.
As regards the maximum level for the whole composite product Art. 2(1)(c) and 2(2) shall apply."
Kar zadeva mejno vrednost za celoten sestavljen izdelek, velja člen 2(1)(c) in (2).“
Muscle meat of smoked fish and smoked fishery products (25)(36), excluding fishery products listed in points 6.1.6 and 6.1.7. The maximum level for smoked crustaceans applies to muscle meat from appendages and abdomen (44). In case of smoked crabs and crab-like crustaceans (Brachyura and Anomura) it applies to muscle meat from appendages.
mišičnina prekajenih rib in prekajeni ribiški proizvodi (25)(36), razen ribiških proizvodov iz točk 6.1.6 in 6.1.7.; mejna vrednost za prekajene rake se uporablja za mišičnino z okončin in trebušnega predela (44); v primeru prekajenih rakov ter rakovic in raznorepcev (Brachyura in Anomura) se uporablja za mišičnino z okončin
Commission Regulation (EU) No 836/2011
Uredba Komisije (EU) št. 836/2011
amending Regulation (EC) No 333/2007 laying down the methods of sampling and analysis for the official control of the levels of lead, cadmium, mercury, inorganic tin, 3-MCPD and benzo(a)pyrene in foodstuffs
o spremembi Uredbe (ES) št. 333/2007 o določitvi metod vzorčenja in analitskih metod za uradni nadzor vsebnosti svinca, kadmija, živega srebra, anorganskega kositra, 3-MCPD in benzo(a)pirena v živilih
Commission Regulation (EC) No 1881/2006 of 19 December 2006 setting maximum levels for certain contaminants in foodstuffs [2] established, inter alia, maximum levels for the contaminant benzo(a)pyrene.
Uredba Komisije (ES) št. 1881/2006 z dne 19. decembra 2006 o določitvi mejnih vrednosti nekaterih onesnaževal v živilih [2] določa med drugim mejne vrednosti onesnaževala benzo[a]pirena.
The Scientific Panel on Contaminants in the Food Chain of the European Food Safety Authority (EFSA) adopted an opinion on Polycyclic Aromatic Hydrocarbons in Food on 9 June 2008 [3].
Znanstveni odbor za onesnaževalce v prehranski verigi Evropske agencije za varnost hrane (EFSA) je 9. junija 2008 [3] sprejel mnenje o policikličnih aromatskih ogljikovodikih v živilih.
The EFSA concluded that benzo(a)pyrene is not a suitable marker for the occurrence of polycyclic aromatic hydrocarbons (PAH) in food and that a system of four specific substances or eight specific substances would be the most suitable markers of PAH in food.
EFSA je ugotovila, da benzo[a]piren ni primeren kazalnik prisotnosti policikličnih aromatskih ogljikovodikov (PAH) v živilih in da bi bil sistem štirih posebnih snovi ali osmih posebnih snovi najboljši kazalnik za PAH v živilih.
The EFSA also concluded that a system of eight substances would not provide much added value compared to a system of four substances.
EFSA je ugotovila tudi, da sistem osmih snovi ne bi zagotovil dosti večjo dodano vrednost v primerjavi s sistemom štirih snovi.
As a consequence Commission Regulation (EU) No 835/2011 [4] amended Regulation (EC) No 1881/2006 in order to set maximum levels for the sum of four polycyclic aromatic hydrocarbons (benzo(a)pyrene, benz(a)anthracene, benzo(b)fluoranthene and chrysene).
Zato je Uredba Komisije (EU) št 835/2011 [4] spremenila Uredbo (ES) št. 1881/2006, da bi določila najvišje vrednosti za vsoto štirih policikličnih aromatskih ogljikovodikov (benzo[a]pirena, benz[a]antracena, benzo[b]fluorantena in krizena).
Commission Regulation (EC) No 333/2007 [5] lays down analytical performance criteria only for benzo(a)pyrene.
Uredba Komisije (ES) št. 333/2007 [5] določa analitična izvedbena merila samo za benzo[a]piren.
It is therefore necessary to lay down analytical performance criteria for the other three substances for which maximum levels are now set out in Regulation (EC) No 1881/2006.
Zato je treba določiti analitična izvedbena merila za druge tri snovi, za katere so mejne vrednosti določene v Uredbi (ES) št. 1881/2006.
The European Union Reference Laboratory for Polycyclic Aromatic Hydrocarbons (EU-RL PAH) in collaboration with the national reference laboratories carried out a survey among official control laboratories to assess which analytical performance criteria would be achievable for benzo(a)pyrene, benz(a)anthracene, benzo(b)fluoranthene and chrysene in relevant food matrices.
Referenčni laboratorij Evropske unije za policiklične aromatske ogljikovodike (EU-RL PAH) je v sodelovanju z nacionalnimi referenčnimi laboratoriji izvedel raziskavo med laboratoriji za uradni nadzor, da bi ocenil, katera analitična izvedbena merila bi bila lahko določena za benzo[a]piren, benz[a]antracen, benzo[b]fluoranten in krizen v ustreznih živilskih matricah.
The outcome of this survey was summarised by the EU-RL PAH in the Report on ‘Performance characteristics of analysis methods for the determination of 4 polycyclic aromatic hydrocarbons in food’ [6].
Rezultat te raziskave je povzel EU-RL PAH v poročilu o „Izvedbenih značilnostih analitskih metod za določanje štirih policikličnih aromatskih ogljikovodikov v živilih“ [6].
The results of the survey show that the analytical performance criteria currently applicable to benzo(a)pyrene are also suitable for the other three substances.
Ugotovitve raziskave kažejo, da so analitična izvedbena merila, ki se zdaj uporabljajo za benzo[a]piren, prav tako primerna za ostale tri snovi.
Experience acquired while implementing Regulation (EC) No 333/2007 revealed that in some cases the current sampling provisions may be impracticable or may lead to unacceptable economic damage to the sampled lot.
Izkušnje, dobljene pri izvajanju Uredbe (ES) št. 333/2007, so pokazale možnost, da bi bile v nekaterih primerih sedanje določbe za vzorčenje neizvedljive ali bi vodile k nesprejemljivi gospodarski škodi za vzorčeni lot.
For such cases, departure from the sampling procedures should be allowed, provided that sampling remains sufficiently representative of the sampled lot or sublot and that the procedure used is fully documented.
Za take primere je treba dovoliti odstopanje od vzorčnih postopkov, pod pogojem, da vzorčenje ostane dovolj reprezentativno za vzorčeni lot ali sublot in da je uporabljeni postopek v celoti dokumentiran.
For sampling at the retail stage, flexibility to depart from the sampling procedures existed already.
Za vzorčenje na ravni trgovine na drobno je prožnost glede odstopanja od postopkov vzorčenja že obstajala.
The provisions for sampling at retail stage should be aligned with the general sampling procedures.
Določbe za vzorčenje na ravni trgovine na drobno je treba uskladiti s splošnimi postopki vzorčenja.
More detailed provisions are needed as regards the material of sampling containers when samples are taken for PAH analysis.
Podrobnejše določbe so potrebne glede materiala posod za vzorčenje, ko se jemljejo vzorci za analizo PAH.
Plastic containers are widely used by enforcement authorities, but they are not suitable when sampling is carried out for PAH analysis, as the PAH content of the sample can be altered by these materials.
Izvršni organi na široko uporabljajo plastične posode, vendar te niso primerne za izvajanje vzorčenja za analizo PAH, saj ti materiali lahko spremenijo vsebino PAH.
Clarification is needed for some aspects of the specific requirements for analytical methods, in particular the requirements regarding the use of the performance criteria and the ‘fitness-for-purpose’ approach.
Potrebna je pojasnitev glede nekaterih vidikov posebnih zahtev za analitske metode, zlasti zahtev glede uporabe izvedbenih meril in pristopa „ustreznost namenu“.
Furthermore, the presentation of the tables with the performance criteria should be modified to appear more uniform across all analytes.
Poleg tega je treba spremeniti prikaz preglednic z izvedbenimi merili, da bi bile bolj poenotene za vse analite.
Regulation (EC) No 333/2007 should therefore be amended accordingly.
Uredbo (ES) št. 333/2007 je zato treba ustrezno spremeniti.
Since Regulation (EU) No 835/2011 and this Regulation are inter-linked, both Regulations should become applicable on the same date.
Ker sta Uredba (EU) št 835/2011 in ta uredba med seboj povezani, morata obe uredbi začeti veljati na isti datum.
Regulation (EC) No 333/2007 is amended as follows:
Uredba (ES) št. 333/2007 se spremeni:
‘Commission Regulation (EC) No 333/2007 of 28 March 2007 laying down the methods of sampling and analysis for the official control of the levels of lead, cadmium, mercury, inorganic tin, 3-MCPD and polycyclic aromatic hydrocarbons in foodstuffs’;
„Uredba Komisije (ES) št. 333/2007 z dne 28. marca 2007 o določitvi metod vzorčenja in analitskih metod za uradni nadzor vsebnosti svinca, kadmija, živega srebra, anorganskega kositra, 3-MCPD in policikličnih aromatskih ogljikovodikov v živilih“;
in Article 1, paragraph 1 is replaced by the following:
člen 1(1) se nadomesti z naslednjim:
Sampling and analysis for the official control of the levels of lead, cadmium, mercury, inorganic tin, 3-MCPD and polycyclic aromatic hydrocarbons (“PAH”) listed in Sections 3, 4 and 6 of the Annex to Regulation (EC) No 1881/2006 shall be carried out in accordance with the Annex to this Regulation.’;
Vzorčenje in analize za uradni nadzor vsebnosti svinca, kadmija, živega srebra, anorganskega kositra, 3-MCPD in policikličnih aromatskih ogljikovodikov (‚,PAH‘), navedene v oddelkih 3, 4 in 6 Priloge k Uredbi (ES) št. 1881/2006, se izvajajo v skladu s Prilogo k tej uredbi.“;
The EFSA Journal (2008) 724, p. 1.
EFSA Journal (2008) 724, str. 1.
JRC Report 59046, 2010.
Poročilo JRC št. 59046, 2010.
The Annex to Regulation (EC) No 333/2007 is amended as follows:
Priloga k Uredbi (ES) št. 333/2007 se spremeni:
in point B.1.7 ‘Packaging and transmission of samples’, the following second paragraph is added:
v točki B.1.7 „Pakiranje in prenos vzorcev“ se doda naslednji drugi odstavek:
‘In case of sampling for PAH analysis plastic containers shall be avoided if possible as they could alter the PAH content of the sample. Inert, PAH-free glass containers, adequately protecting the sample from light, shall be used wherever possible. Where this is practically impossible, at least direct contact of the sample with plastics shall be avoided, e.g. in case of solid samples by wrapping the sample in aluminium foil before placing it in the sampling container.’;
„V primeru vzorčenja za analizo PAH se po možnosti plastične posode ne uporabljajo, saj bi lahko spremenile vsebino PAH vzorca. Kadar je mogoče se uporablja steklena posoda brez PHA, iz inertnih materialov, ki vzorec ustrezno ščiti pred svetlobo. Kadar je to dejansko nemogoče uporabiti, je treba preprečiti neposreden stik med vzorcem in plastiko, na primer z zavijanjem trdnih vzorcev v aluminijevo folijo, preden se jih da v posodo za vzorčenje.“;
points B.2 and B.3 are replaced by the following:
točki B.2 in B.3 se nadomestita z naslednjim:
For products traded in bulk consignments (e.g. cereals) Table 1 shall apply.
Za izdelke, ki se tržijo v razsutem stanju (npr. žito), se uporablja preglednica 1.
The aggregate sample shall be at least 1 kg or 1 litre except where it is not possible, e.g. when the sample consists of 1 package or unit.
Masa sestavljenega vzorca mora imeti maso najmanj 1 kilogram ali 1 liter, razen, kjer to ni mogoče, npr. kadar se vzorči eno samo pakiranje ali enota.
The minimum number of incremental samples to be taken from the lot or sublot shall be as given in Table 3.
Najmanjše število posamičnih vzorcev, ki se odvzamejo iz lota ali sublota, je navedeno v preglednici 3.
In the case of bulk liquid products the lot or sublot shall be thoroughly mixed in so far as possible and in so far it does not affect the quality of the product, by either manual or mechanical means immediately prior to sampling.
Za razsute tekoče izdelke se lot ali sublot, kolikor je mogoče temeljito, ročno ali mehansko premeša neposredno pred vzorčenjem, če to ne vpliva na kakovost izdelka.
It is therefore sufficient to take three incremental samples from a lot or sublot to form the aggregate sample.
Zato zadošča, da se za oblikovanje sestavljenega vzorca odvzamejo trije posamični vzorci iz lota ali sublota.
The incremental samples shall be of similar weight/volume.
Posamični vzorci imajo podobno maso/volumen.
The weight/volume of an incremental sample shall be at least 100 grams or 100 millilitres, resulting in an aggregate sample of at least about 1 kg or 1 litre.
Masa/volumen posamičnega vzorca mora biti najmanj 100 gramov ali 100 mililitrov, kar tvori sestavljeni vzorec, z maso najmanj 1 kilogram ali 1 liter.