natgillin/translations-raw huggingface dataset:
In Annex I to Directive 2002/32/EC, Section V: Dioxins and PCBs is replaced by the following:
V Prilogi I k Direktivi 2002/32/ES se oddelek V: Dioksini in PCB nadomesti z naslednjim:
‘SECTION V:
„ODDELEK V:
DIOXINS AND PCBs
DIOKSINI IN PCB
Products intended for animal feed
Proizvodi, namenjeni za prehrano živali
Maximum content in ng WHO-PCDD/F-TEQ/kg (ppt) [1] relative to a feed with a moisture content of 12 %
Najvišja vsebnost v ng WHO-PCDD/F-TEQ/kg (ppt) [1] pri krmi z 12-odstotno vsebnostjo vlage
Feed materials of plant origin with the exception of:
Posamična krmila rastlinskega izvora, razen:
Other land animal products including milk and milk products and eggs and egg products
drugi proizvodi kopenskih živali, vključno z mlekom in mlečnimi proizvodi ter jajci in jajčnimi proizvodi,
Fish, other aquatic animals, and products derived thereof with the exception of fish oil and fish protein, hydrolysed, containing more than 20 % fat [3]
ribe, druge vodne živali in proizvodi iz njih, razen ribjega olja in hidroliziranih ribjih beljakovin, ki vsebujejo več kot 20 % maščobe [3],
Fish protein, hydrolysed, containing more than 20 % fat
hidrolizirane ribje beljakovine, ki vsebujejo več kot 20 % maščobe.
The feed additives kaolinitic clay, vermiculite, natrolite-phonolite, synthetic calcium aluminates and clinoptilolite of sedimentary origin belonging to the functional groups of binders and anti-caking agents
Krmni dodatki kaolinitne gline, vermikulita, natrolit fonolita, sintetičnih kalcijevih aluminatov in klinoptilolita usedlinskega izvora iz funkcionalnih skupin veziv in sredstev proti strjevanju
Feed additives belonging to the functional group of compounds of trace elements
Krmni dodatki iz funkcionalne skupine spojin elementov v sledeh
Compound feed with the exception of:
Krmne mešanice, razen:
compound feed for pet animals and fish
krmnih mešanic za hišne živali in ribe,
compound feed for fur animals
krmnih mešanic za kožuharje.
Maximum content in ng WHO-PCDD/F-PCB-TEQ/kg (ppt) [1] relative to a feed with a moisture content of 12 %
Najvišja vsebnost v ng WHO-PCDD/F-TEQ/kg (ppt) [1] pri krmi z 12-odstotno vsebnostjo vlage
Maximum content in μg/kg (ppb) relative to a feed with a moisture content of 12 % [1]
Najvišja vsebnost v μg/kg (ppb) pri krmi z 12-odstotno vsebnostjo vlage [1]
Feed materials of plant origin
Posamična krmila rastlinskega izvora
Fish, other aquatic animals and products derived thereof with the exception of fish oil and fish protein, hydrolysed, containing more than 20 % fat [4]
ribe, druge vodne živali in proizvodi iz njih, razen ribjega olja in hidroliziranih ribjih beljakovin, ki vsebujejo več kot 20 % maščobe [4],
ACTION THRESHOLDS TRIGGERING INVESTIGATIONS BY MEMBER STATES, AS REFERRED TO IN ARTICLE 4(2)
PRAGOVI UKREPANJA, PRI KATERIH SE SPROŽIJO PREISKAVE DRŽAV ČLANIC, KOT JE NAVEDENO V ČLENU 4(2)
Action threshold in ng WHO-PCDD/F TEQ/kg (ppt) [2] relative to a feedingstuff with a moisture content of 12 %
Prag ukrepanja v ng WHO-PCDD/F-TEQ/kg (ppt) [2] pri krmni mešanici z 12-odstotno vsebnostjo vlage
Fish, other aquatic animals and products derived thereof with the exception of fish oil and fish protein, hydrolysed, containing more than 20 % fat [3]
ribe, druge vodne živali in proizvodi iz njih, razen ribjega olja in hidroliziranih ribjih beljakovin, ki vsebujejo več kot 20 % maščobe [3],
Feed additives belonging to the functional groups of binders and anti-caking agents
Krmni dodatki iz funkcionalne skupine veziv in sredstev proti strjevanju
Upper-bound concentrations; upper-bound concentrations are calculated on the assumption that all values of the different congeners below the limit of quantification are equal to the limit of quantification.
Koncentracije na zgornji meji; koncentracije na zgornji meji so izračunane ob domnevi, da so vse vrednosti različnih kongenerov pod mejo določanja enake meji določanja.
Once source is identified, take appropriate measures, where possible, to reduce or eliminate source of contamination.
Potem ko je vir določen, se po možnosti sprejmejo ustrezni ukrepi za zmanjšanje ali odpravo vira kontaminacije.
In many cases it might not be necessary to perform an investigation into the source of contamination as the background level in some areas is close to or above the action level.
V številnih primerih morda ne bo treba opraviti preiskave vira kontaminacije, ker je raven prisotnosti na nekaterih območjih blizu praga za ukrepanje ali nad njim.
However, in cases where the action level is exceeded, all information, such as sampling period, geographical origin, fish species etc., shall be recorded with a view to future measures to manage the presence of dioxins and dioxin-like compounds in these materials for animal nutrition.’
Vseeno se v primerih, ko je prag za ukrepanje presežen, zapišejo vse informacije, kot so čas vzorčenja, geografsko poreklo, vrste rib itd., glede na prihodnje ukrepe za upravljanje prisotnosti dioksinov in dioksinom podobnih spojin v teh snoveh za prehrano živali.“
Fresh fish and other aquatic animals directly delivered and used without intermediate processing for the production of feed for fur animals are not subject to the maximum levels, while maximum levels of 3,5 ng WHO-PCDD/F-TEQ/kg product and 6,5 ng WHO-PCDD/F-PCB-TEQ/kg product are applicable to fresh fish and 20,0 ng WHO-PCDD/F-PCB-TEQ/kg product is applicable to fish liver used for the direct feeding of pet animals, zoo and circus animals or used as feed material for the production of pet food.
Sveže ribe in druge vodne živali, neposredno dostavljene in porabljene brez vmesne predelave za proizvodnjo krme za kožuharje, so izvzete iz mejnih vrednosti, medtem ko se mejne vrednosti 3,5 ng WHO-PCDD/F-TEQ na kg proizvoda in 6,5 ng WHO-PCDD/F-PCB-TEQ na kg proizvoda uporabljajo za sveže ribe, 20,0 ng WHO-PCDD/F-PCB-TEQ na kg proizvoda pa za ribja jetra, ki se uporabljajo za neposredno prehrano hišnih živali ter živali v živalskih vrtovih in cirkusih oziroma za posamično krmilo za proizvodnjo hrane za hišne živali.
The products or processed animal proteins produced from these animals (fur animals, pet animals, zoo and circus animals) cannot enter the food chain and cannot be fed to farmed animals which are kept, fattened or bred for the production of food.
Proizvodi ali predelane živalske beljakovine, proizvedene iz teh živali (kožuharji, hišne živali ter živali v živalskih vrtovih in cirkusih), ne morejo vstopati v prehransko verigo in jih je prepovedano krmiti rejnim živalim, ki se gojijo, pitajo ali vzrejajo za proizvodnjo hrane.
Fresh fish and other aquatic animals directly delivered and used without intermediate processing for the production of feed for fur animals are not subject to the maximum levels, while maximum levels of 75 μg/kg product are applicable to fresh fish and 200 μg/kg product are applicable to fish liver used for the direct feeding of pet animals, zoo and circus animals or used as feed material for the production of pet food.
Sveže ribe in druge vodne živali, neposredno dostavljene in porabljene brez vmesne predelave za proizvodnjo krme za kožuharje, so izvzete iz mejnih vrednosti, medtem ko se mejne vrednosti 75 μg na kg proizvoda uporabljajo za sveže ribe, 200 μg na kg proizvoda pa za ribja jetra, ki se uporabljajo za neposredno prehrano hišnih živali ter živali v živalskih vrtovih in cirkusih oziroma za posamično krmilo za proizvodnjo hrane za hišne živali.
The products or processed animal proteins produced from these animals (fur animals, pet animals, zoo and circus animals) cannot enter the food chain and cannot be fed to farmed animals which are kept, fattened or bred for the production of food.’
Proizvodi ali predelane živalske beljakovine, proizvedene iz teh živali (kožuharji, hišne živali ter živali v živalskih vrtovih in cirkusih), ne morejo vstopati v prehransko verigo in jih je prepovedano krmiti rejnim živalim, ki se gojijo, pitajo ali vzrejajo za proizvodnjo hrane.“
Expressing the analytical result as an upper-bound level would already result in some cases in a level close to the maximum level even if no PCBs have been quantified.
Izražanje analitskega rezultata kot na zgornji meji bi v nekaterih primerih že pomenilo, da je vrednost blizu mejne vrednosti, čeprav PCB niso bili količinsko določeni.
It was also acknowledged that for certain feed categories the data were not very extensive.
Ugotovljeno je bilo tudi, da podatki za nekatere kategorije krme niso bili zelo obsežni.
Table of TEF (= toxic equivalency factors) for dioxins, furans and dioxin-like PCBs:WHO-TEFs for human risk assessment based on the conclusions of the World Health Organisation (WHO) – International Programme on Chemical Safety (IPCS) expert meeting which was held in Geneva in June 2005 (Martin van den Berg et al., The 2005 World Health Organisation Re-evaluation of Human and Mammalian Toxic Equivalency Factors for Dioxins and Dioxin-like Compounds. Toxicological Sciences 93(2), 223–241 (2006))Abbreviations used: “T” = tetra; “Pe” = penta; “Hx” = hexa; “Hp” = hepta; “O” = octa; “CDD” = chlorodibenzodioxin; “CDF” = chlorodibenzofuran; “CB” = chlorobiphenyl.
Razpredelnica TEF (faktorji toksične ekvivalentosti) za dioksine, furane in dioksinom podobne PCB:WHO-TEF za oceno tveganja za ljudi temeljijo na sklepih Svetovne zdravstvene organizacije – strokovnega srečanja Mednarodnega programa za kemijsko varnost (IPCS) junija 2005 v Ženevi (Martin van den Berg in sod., Ponovna ocena faktorjev toksične ekvivalentosti za dioksine in dioksinom podobne spojine pri ljudeh in sesalcih, Svetovna zdravstvena organizacija, 2005 (The 2005 World Health Organization Re-evaluation of Human and Mammalian Toxic Equivalency Factors for Dioxins and Dioxin-like Compounds). Toxicological Sciences 93(2), 223–241 (2006))Uporabljene okrajšave: „T“ = tetra; „Pe“ = penta; „Hx“ = heksa; „Hp“ = hepta; „O“ = okta; „CDD“ = klorodibenzodioksin; „CDF“ = klorodibenzofuran; „CB“ = klorobifenil.
CongenerTEF valueDibenzo-para-dioxins (“PCDDs”) and Dibenzo-para-furans (PCDFs) 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-HpCDD0,01OCDD0,00032,3,7,8-TCDF0,11,2,3,7,8-PeCDF0,032,3,4,7,8-PeCDF0,31,2,3,4,7,8-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-HpCDF0,01OCDF0,0003“Dioxin-like” PCBs: Non-ortho PCBs + Mono-ortho PCBs Non-ortho PCBsPCB 770,0001PCB 810,0003PCB 1260,1PCB 1690,03Mono-ortho PCBsPCB 1050,00003PCB 1140,00003PCB 1180,00003PCB 1230,00003PCB 1560,00003PCB 1570,00003PCB 1670,00003PCB 1890,00003
KongenerVrednost TEFDibenzo-para-dioksini („PCDD“) in dibenzo-para-furani ( „PCDF“) 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-HpCDD0,01OCDD0,00032,3,7,8-TCDF0,11,2,3,7,8-PeCDF0,032,3,4,7,8-PeCDF0,31,2,3,4,7,8-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-HpCDF0,01OCDF0,0003„Dioksinom podobni“ PCB: neorto PCB + monoorto PCB Neorto PCBPCB 770,0001PCB 810,0003PCB 1260,1PCB 1690,03Monoorto PCBPCB 1050,00003PCB 1140,00003PCB 1180,00003PCB 1230,00003PCB 1560,00003PCB 1570,00003PCB 1670,00003PCB 1890,00003
Corrigendum to Political and Security Committee Decision EU BAM Rafah/1/2012 of 3 July 2012 on the appointment of the Head of European Union Border Assistance Mission for the Rafah Crossing Point (EU BAM Rafah)
Popravek Sklepa Političnega in varnostnega odbora EU BAM Rafah/1/2012 z dne 3. julija 2012 o imenovanju vodje misije pomoči Evropske unije za mejni prehod Rafa (EU BAM Rafah)
In the contents on the cover and on page 30, number of the Decision:
Naslov na naslovnici in na strani 30, številka Sklepa:
‘(2012/382/EU)’,
„(2012/382/EU)“
‘(2012/382/CFSP)’.
„(2012/382/SZVP)“.
Commission Regulation (EU) No 278/2012
Uredba Komisije (EU) št. 278/2012
amending Regulation (EC) No 152/2009 as regards the determination of the levels of dioxins and polychlorinated biphenyls
o spremembi Uredbe (ES) št. 152/2009 glede določanja ravni dioksinov in polikloriranih bifenilov
Directive 2002/32/EC of the European Parliament and of the Council of 7 May 2002 on undesirable substances in animal feed [2] lays down maximum levels for dioxins, furans and polychlorinated biphenyls (PCBs) in feed and action thresholds triggering investigations by Member States to identify the sources of those substances.
Direktiva 2002/32/ES Evropskega parlamenta in Sveta z dne 7. maja 2002 o nezaželenih snoveh v živalski krmi [2] določa mejne vrednosti za dioksine, furane in poliklorirane bifenile (PCB) v krmi ter pragove ukrepanja, pri katerih se sprožijo preiskave držav članic za ugotovitev virov navedenih snovi.
Commission Regulation (EC) No 152/2009 of 27 January 2009 laying down the methods of sampling and analysis for the official control of feed [3] includes methods for the determination of the levels of polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) and dioxin-like polychlorinated biphenyls (PCBs) in feed.
Uredba Komisije (ES) št. 152/2009 z dne 27. januarja 2009 o določitvi metod vzorčenja in analitskih metod za uradni nadzor krme [3] vključuje metode za določanje ravni polikloriranih dibenzo-p-dioksinov (PCDD, polikloriranih dibenzofuranov (PCDF) in dioksinom podobnih polikloriranih bifenilov (PCB) v krmi.
A screening method of analysis with widely acceptable validation and high throughput can be used to identify the samples with significant levels of PCDD/Fs and dioxin-like PCBs (preferably selecting samples exceeding action thresholds and ensuring the selection of samples exceeding maximum levels).
Za določitev vzorcev z znatno vsebnostjo PCDD/F in dioksinom podobnih PCB je mogoče uporabiti presejalno analitsko metodo s splošno sprejemljivo validacijo in veliko prepustnostjo (po možnosti z zaznavo vzorcev, ki presegajo pragove ukrepanja, in zagotavljanjem zaznave vzorcev, ki presegajo mejne vrednosti).
That is important for the follow-up of time trends, exposure assessment and for the re-evaluation of maximum and action thresholds.
To je pomembno za spremljanje časovnih gibanj, oceno izpostavljenosti ter ponovno oceno mejnih vrednosti in pragov ukrepanja.
The modification of the maximum levels for dioxins and dioxin-like PCBs and the establishment of non-dioxin-like PCBs in Directive 2002/32/EC and the need to update the criteria for screening methods makes it necessary to amend the rules on the determination of dioxins and PCBs in feed, as laid down by Part B of Annex V to Regulation (EC) No 152/2009.
Zaradi spremembe mejnih vrednostih za dioksine in dioksinom podobne PCB, vključitve dioksinom nepodobnih PCB v Direktivo 2002/32/ES ter potrebe po posodobitvi meril za presejalne metode je treba spremeniti pravila za določanje dioksinov in PCB v krmi iz dela B Priloge V k Uredbi (ES) št. 152/2009.
For reasons of clarity and comprehensibility, it is appropriate to replace Part B of Annex V.
Zaradi jasnosti in razumljivosti je primerno nadomestiti del B k Prilogi V.
It is of major importance that analytical results are reported and interpreted in a uniform way in order to ensure a harmonised enforcement approach throughout the Union.
Zelo pomembno je, da se analitski rezultati navajajo in interpretirajo enotno, da se tako zagotovi usklajeno ravnanje po celotni Uniji.
Annex V to Regulation (EC) No 152/2009 should therefore be amended accordingly.
Prilogo V k Uredbi (ES) št. 152/2009 je zato treba ustrezno spremeniti.
Part B of Annex V to Regulation (EC) No 152/2009 is amended in accordance with the Annex to this Regulation.
Del B Priloge V k Uredbi (ES) št. 152/2009 se spremeni v skladu s Prilogo k tej uredbi.
In Annex V to Regulation (EC) No 152/2009, Part (B) ‘DETERMINATION OF THE LEVELS OF DIOXINS (PCDD/PCDF) AND DIOXIN-LIKE PCBs’ is replaced by the following:
V Prilogi V k Uredbi (ES) št. 152/2009 se del (B) DOLOČANJE RAVNI DIOKSINOV (PCDD/PCDF) IN DIOKSINOM PODOBNIH PCB nadomesti z naslednjim:
DETERMINATION OF THE LEVELS OF DIOXINS (PCDD/PCDF) AND PCBs
DOLOČANJE RAVNI DIOKSINOV (PCDD/PCDF) IN PCB
Methods of sampling and interpretation of analytical results
Metode vzorčenja in razlaga rezultatov analize
The samples intended for the official control of the levels of polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), dioxin-like polychlorinated biphenyls (PCBs) and non-dioxin-like PCBs in feed shall be taken in accordance with the provisions of Annex I. The quantitative requirements in relation to the control of substances or products uniformly distributed throughout the feed as provided for in point 5.A of Annex I shall be applied. Aggregate samples thus obtained shall be considered representative for the lots or sub-lots from which they are taken.
Vzorci za uradni nadzor ravni polikloriranih dibenzo-p-dioksinov (PCDD), polikloriranih dibenzofuranov (PCDF), dioksinom podobnih polikloriranih bifenilov (PCB) in dioksinom nepodobnih PCB v krmi se odvzamejo v skladu z določbami iz Priloge I. Upoštevajo se količinske zahteve za nadzor snovi ali proizvodov, enakomerno razporejenih po krmi, iz točke 5.A Priloge I. Tako pridobljeni sestavljeni vzorci se obravnavajo kot reprezentativni za serije in podserije, iz katerih so odvzeti.
Compliance with maximum levels laid down in Directive 2002/32/EC shall be established on the basis of the levels determined in the laboratory samples.
Skladnost z mejnimi vrednostmi, določenimi v Direktivi 2002/32/ES, se ugotavlja na podlagi vrednosti, ugotovljenih v laboratorijskih vzorcih.
For the purposes of this Part of Annex V, the definitions laid down in Annex I to Commission Decision 2002/657/EC of 14 August 2002 implementing Council Directive 96/23/EC concerning the performance of analytical methods and interpretation of results shall apply.
V tem delu Priloge V se uporabljajo opredelitve pojmov iz Priloge I k Odločbi Komisije 2002/657/ES z dne 14. avgusta 2002 o izvajanju Direktive Sveta 96/23/ES glede opravljanja analitskih metod in razlage rezultatov.
Compliance of the lot or sub-lot with the specification
Skladnost serije ali subserije s specifikacijo
The lot complies with the specification if the analytical result does not exceed the maximum level of non-dioxin-like PCBs laid down by Directive 2002/32/EC, taking into account the measurement uncertainty.
Serija je v skladu s specifikacijami, če rezultat analiznega preskušanja ne presega mejne vrednosti dioksinom nepodobnih PCB iz Direktive 2002/32/ES ob upoštevanju merilne negotovosti.
The lot does not comply with the specification if the upper-bound analytical result confirmed by duplicate analysis exceeds the maximum level laid down by Directive 2002/32/EC, taking into account the measurement uncertainty.
Serija ni v skladu s specifikacijami, če rezultat analiznega preskušanja na zgornji meji, potrjen z dvakratno analizo , presega mejne vrednosti iz Direktive 2002/32/ES ob upoštevanju merilne negotovosti.
The measurement uncertainty shall be taken into account according to one of the following approaches:
Merilna negotovost se upošteva po enem od naslednjih pristopov:
by calculating the expanded uncertainty, using a coverage factor of 2 which gives a level of confidence of approximately 95 %.
z izračunom razširjene nezanesljivosti ob uporabi faktorja zajetja 2, ki zagotavlja 95-odstotno stopnjo zaupanja.
A lot or sub-lot is non-compliant if the measured value minus U is above the maximum level,
Serija ali subserija je neskladna, če je izmerjena vrednost minus U nad mejno vrednostjo,
by establishing the decision limit (CCα) in accordance with point 3.1.2.5 of Annex I to Decision 2002/657/EC.
z določitvijo odločitvene meje (CCα) v skladu s točko 3.1.2.5 Priloge I k Odločbi 2002/657/ES.
A lot or sub-lot is non-compliant if the measured value is equal to or above the CCα.
Serija ali subserija je neskladna, če je izmerjena vrednost enaka ali večja od CCα.
These interpretation rules shall apply for the analytical result obtained on the sample for official control.
Ta pravila razlage se uporabljajo za rezultat analiznega preskušanja, pridobljen na vzorcu za uradni nadzor.
In case of analysis for defence or reference purposes, the national rules shall apply.
Pri analizi za dopolnilno izvedensko mnenje ali referenčne namene se uporabljajo nacionalna pravila.
As regards PCDD/F and dioxin-like PCBs
Glede PCDD/F in dioksinom podobnih PCB
The lot complies with the specifications if the analytical result of a single analysis,
Serija je v skladu s specifikacijami, če rezultat posamezne analize,
performed by a screening method with a false-compliant rate below 5 %, indicates that the level does not exceed the respective maximum level of PCDD/PCDFs and the sum of PCDD/PCDFs and dioxin-like PCBs laid down by Directive 2002/32/EC,
opravljene s presejalno metodo, pri kateri je delež lažno skladnih rezultatov manjši kot 5 %, pokaže, da vsebnost ne presega zadevne mejne vrednosti PCDD/PCDF ter vsote PCDD/PCDF in dioksinom podobnih PCB iz Direktive 2002/32/ES,
performed by a confirmatory method, does not exceed the respective maximum level of PCDD/PCDFs and the sum of PCDD/PCDFs and dioxin-like PCBs laid down by Directive 2002/32/EC, taking into account the measurement uncertainty.
opravljene s potrditveno metodo, ne presega zadevne mejne vrednosti PCDD/PCDF ter vsote PCDD/PCDF in dioksinom podobnih PCB iz Direktive 2002/32/ES ob upoštevanju merilne negotovosti.
For screening assays a cut-off value shall be established for decisions on sample compliance with the respective levels of interest set for either PCDD/PCDFs, or for the sum of PCDD/PCDFs and dioxin-like PCBs.
Za presejalne teste se določi izločitvena vrednost za odločitev o skladnosti vzorca z zadevnimi predpisanimi vrednostmi, določenimi za PCDD/PCDF ali za vsoto PCDD/PCDF in dioksinom podobnih PCB.
The lot does not comply with the specification if the upper-bound analytical result obtained with a confirmatory method and confirmed by duplicate analysis exceeds the maximum level laid down by Directive 2002/32/EC, taking into account the measurement uncertainty .
Serija ni v skladu s specifikacijami, če rezultat analiznega preskušanja na zgornji meji, pridobljen s potrditveno metodo in potrjen z dvakratno analizo, presega mejne vrednosti iz Direktive 2002/32/ES ob upoštevanju merilne negotovosti .
A lot or sub-lot is non-compliant if the measured value minus U is above the maximum level.
Serija ali subserija je neskladna, če je izmerjena vrednost minus U nad mejno vrednostjo.
In case of a separate determination of PCDD/PCDFs and dioxin-like-PCBs, the sum of the estimated expanded uncertainty of the separate analytical results of PCDD/PCDFs and dioxin-like PCBs shall be used for the sum of PCDD/PCDFs and dioxin-like PCBs,
Pri ločenem preskušanju za določitev PCDD/PCDF in dioksinom podobnih PCB se vsota ocenjene razširjene negotovosti ločenih rezultatov analize vsebnosti PCDD/PCDF in dioksinu podobnih PCB uporablja za vsoto PCDD/PCDF in dioksinom podobnih PCB,
by establishing the decision limit (CCα) in accordance with point 3.1.2.5 of the Annex I to Decision 2002/657/EC.
z določitvijo odločitvene meje (CCα) v skladu s točko 3.1.2.5 Priloge I k Odločbi 2002/657/ES.
Results exceeding action thresholds as laid down in Annex II to Directive 2002/32/EC
Rezultati, ki presegajo pragove ukrepanja iz priloge II k Direktivi 2002/32/ES
Identical explanation and requirements for duplicate analysis for control of action thresholds as in footnote [5] The concept of “upper-bound” requires using the limit of quantification for the contribution of each non-quantified congener to the toxic equivalent (TEQ).
Enaka razlaga in zahteve za dvakratno analizo za nadzor pragov ukrepanja kot v opombi [5] Pojem „na zgornji meji“ zahteva, da se za izračun prispevka k toksičnemu ekvivalentu (TEQ) vsakega kongenera, ki ni določen, uporablja vrednost meje določanja.
The concept of “lower-bound” requires using zero for the contribution of each non-quantified congener to the TEQ.
Pojem „na spodnji meji“ zahteva, da se za izračun prispevka k toksičnemu ekvivalentu (TEQ) vsakega kongenera, ki ni določen, uporablja vrednost nič.