natgillin/translations-raw huggingface dataset:
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 [5].
Da se spodbudi proaktivni pristop za zmanjšanje 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 [5].
Those 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.
Since the sources of dioxins and dioxin-like PCBs are different, separate action levels should be determined for dioxins on the one hand and for dioxin-like PCBs on the other hand.
Ker so viri dioksinov in dioksinom podobnih PCB različni, je treba določiti ločene pragove za ukrepanje za dioksine in dioksinom podobne PCB.
Directive 2002/32/EC provides for the possibility of setting action levels.
Direktiva 2002/32/ES predvideva možnost določanja pragov za ukrepanje.
The action levels should therefore be transferred from Recommendation 2002/201/EC to Annex II to Directive 2002/32/EC.
Pragove za ukrepanje je zato treba prenesti iz Priporočila 2002/201/ES v Prilogo II k Direktivi 2002/32/ES.
The reduction of human exposure to dioxins and dioxin-like PCBs through food consumption is important and necessary to ensure consumer protection.
Zmanjšanje izpostavljenosti ljudi dioksinom in dioksinom podobnim PCB z uživanjem hrane je pomembno in potrebno, da se zagotovi varstvo potrošnikov.
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 products intended for animal feed 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 proizvodov, namenjenih za živalsko krmo, prek živali, namenjenih proizvodnji živil, do ljudi.
A proactive approach is followed to actively reduce the dioxins and dioxin-like PCBs in feed and food and consequently the maximum levels applicable should be reviewed within a defined period of time with the objective to set lower levels.
Upošteva se proaktivni pristop za aktivno zmanjšanje dioksinov in dioksinom podobnih PCB v krmi in živilih, zato je treba v določenem obdobju ponovno pregledati mejne vrednosti, ki se uporabljajo, da se določijo nižje vrednosti.
Therefore consideration will be given by 31 December 2008 at the latest to significantly reducing the maximum levels for the sum of dioxins and dioxin-like PCBs.
Zato bo najpozneje do 31. decembra 2008 preučeno znatno zmanjšanje mejnih vrednosti za vsoto dioksinov in dioksinom podobnih PCB.
Operators need to make efforts to step up their decontamination capacity to remove effectively dioxins and dioxin-like PCBs from fish oil.
Proizvajalci si morajo prizadevati za povečanje svoje zmogljivosti dekontaminacije za učinkovito odstranjevanje dioksinov in dioksinom podobnih PCB iz ribjih olj.
Further efforts have to done by the operators to investigate the different possibilities to remove dioxins and dioxin-like PCBs from fish meal and fish protein-hydrolysates.
Proizvajalci si morajo še naprej prizadevati za preučitev različnih možnosti odstranjevanja dioksinov in dioksinom podobnih PCB iz ribje moke in ribjih beljakovinskih hidrolizatov.
Once the decontamination technology is also available for fish meal and fish protein hydrolysates, operators will have to do efforts to provide for sufficient decontamination capacity.
Potem ko bo tehnologija dekontaminacije na voljo tudi za ribjo moko in ribje beljakovinske hidrolizate, si bodo morali proizvajalci prizadevati za zagotovitev ustrezne zmogljivosti dekontaminacije.
The significant lower maximum level for the sum of dioxins and dioxin-like PCBs, to which consideration shall be given by 31 December 2008, shall be for fish oil, fish meal and fish protein hydrolysates based on the technical possibilities of the most effective, economically viable, decontamination procedure.
Znatno nižja mejna vrednost za vsoto dioksinov in dioksinom podobnih PCB, ki se preuči do 31. decembra 2008, temelji za ribja olja, ribjo moko in ribje beljakovinske hidrolizate na tehničnih možnostih najučinkovitejšega, gospodarsko upravičenega postopka dekontaminacije.
As regards fish feed, this significant lower level shall be determined based on the technical possibilities of the most effective, economically viable, decontamination procedure for fish oil and fish meal.
V zvezi s krmo za ribe se ta znatno nižja vrednost določi na podlagi tehničnih možnosti najučinkovitejšega, gospodarsko upravičenega postopka dekontaminacije za ribje olje in ribjo moko.
The extraction procedure used for the analysis of dioxins and dioxin-like PCBs has a large influence on the analytical result in particular on products intended for animal feed of mineral origin and it is therefore appropriate to determine before the date of application the extraction procedure to be used for the analysis of dioxins and dioxin-like PCBs.
Postopek ekstrakcije, ki se uporablja za analizo dioksinov in dioksinom podobnih PCB, močno vpliva na analitični rezultat, zlasti na proizvode, namenjene za živalsko krmo, mineralnega izvora, zato je primerno pred datumom uporabe določiti postopek ekstrakcije, ki se bo uporabljal za analizo dioksinov in dioksinom podobnih PCB.
Directive 2002/32/EC should therefore be amended accordingly.
Direktivo 2002/32/ES je zato treba ustrezno spremeniti.
Annexes I and II to Directive 2002/32/EC are amended in accordance with the Annex to this Directive.
Prilogi I in II k Direktivi 2002/32/ES se spremenita v skladu s Prilogo k tej direktivi.
Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive by 4 November 2006 at the latest.
Države članice sprejmejo zakone in druge predpise, potrebne za uskladitev s to direktivo, najpozneje do 4. novembra 2006.
They shall forthwith communicate to the Commission the text of those provisions and a correlation table between those provisions and this Directive.
Besedilo teh določb s primerjalno tabelo med določbami in to direktivo takoj pošljejo Komisiji.
Directive as last amended by Directive 2005/87/EC (OJ L 318, 6.12.2005, p. 19).
Direktiva, kakor je bila nazadnje spremenjena z Direktivo 2005/87/ES (UL L 318, 6.12.2005, str. 19).
Opinion of the Scientific Committee on Food on the Risk Assessment of Dioxins and Dioxin-like PCBs in Food adopted on 30 May 2001 — Update based on new scientific information available since the adoption of the SCF opinion of 22 November 2000 (http://europa.eu.int/comm/food/fs/sc/scf/out90_en.pdf).
Mnenje Znanstvenega odbora za prehrano o oceni tveganja za dioksine in dioksinom podobne PCB v hrani, sprejeto 30. maja 2001 – Posodobitev na podlagi novih znanstvenih podatkov, ki so postali na voljo od sprejetja mnenja SCF z dne 22. novembra 2000 (http://europa.eu.int/comm/food/fs/sc/scf/out90_en.pdf).
Directive as amended by Directive 2005/7/EC (OJ L 27, 29.1.2005, p. 41).
Direktiva, kakor je bila spremenjena z Direktivo 2005/7/ES (UL L 27, 29.1.2005, str. 41).
Information on different ways for the estimation of the expanded uncertainty and on the value of the measurement uncertainty can be found in the report ‘Report on the relationship between analytical results, measurement uncertainty, recovery factors and the provisions of EU food and feed legislation’ — http://europa.eu.int/comm/food/food/chemicalsafety/contaminants/report-sampling_analysis_2004_en.pdf
Informacije o različnih načinih za oceno razširjene nezanesljivosti in o vrednosti nezanesljivosti meritev so na voljo v poročilu z naslovom „Poročilo o razmerju med analitičnimi rezultati, nezanesljivostjo meritev, faktorji izplena in določbami zakonodaje EU o krmi in živilih“ – http://europa.eu.int/comm/food/food/chemicalsafety/contaminants/report-sampling_analysis_2004_en.pdf
Point 27 in Annex I to Directive 2002/32/EC is replaced by the following:
Točka 27 Priloge I k Direktivi 2002/32/ES se nadomesti z naslednjim:
Maximum content relative to a feedingstuff with a moisture content of 12 %
Največja vsebnost pri krmi z 12-odstotno vsebnostjo vlage
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 [1]
Dioksini (vsota polikloriranih dibenzo-para-dioksinov (PCDD) in polikloriranih dibenzofuranov (PCDF), izražena v toksičnih ekvivalentih Svetovne zdravstvene organizacije (WHO) z uporabo WHO-TEF (faktorji toksične ekvivalence, 1997) [1]
Feed materials of plant origin with the exception of vegetable oils and their by-products
Posamična krmila rastlinskega izvora, razen rastlinskih olj in njihovih stranskih proizvodov
Vegetable oils and their by-products
Rastlinska olja in njihovi stranski proizvodi
Feed materials of mineral origin
Posamična krmila mineralnega izvora
Animal fat, including milk fat and egg fat
Živalska maščoba, vključno z mlečno maščobo in jajčno maščobo
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, their products and by-products with the exception of fish oil and fish protein hydrolysates containing more than 20 % fat [4]
Ribe, druge vodne živali, njihovi proizvodi in stranski proizvodi, razen ribje olje in ribji beljakovinski hidrolizati, ki vsebujejo več kot 20 % maščobe [4]
Fish protein hydrolysates containing more than 20 % fat
Ribji beljakovinski hidrolizati, ki vsebujejo več kot 20 % maščobe
The additives kaolinitic clay, calcium sulphate dihydrate, vermiculite, natrolite-phonolite, synthetic calcium aluminates and clinoptilolite of sedimentary origin belonging to the functional groups of binders and anti-caking agents
Dodatki kaolinitne gline, dihidriranega kalcijevega sulfata, vermikulita, natrolit fonolita, sintetičnih kalcijevih aluminatov in klinoptilolita usedlinskega izvora iz funkcionalne skupine vezalcev in sredstev proti strjevanju
Additives belonging to the functional group of compounds of trace elements
Dodatki iz funkcionalne skupine spojin elementov v sledeh
Compound feedingstuffs, with the exception of feed for fur animals, pet foods and feed for fish
Krmne mešanice, razen krme za kožuharje, hrane za hišne živali in krme za ribe
Feed for fish.
Krma za ribe
Pet foods
Hrana za hišne živali
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]
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 toksične ekvivalence, 1997) [1]
Additives belonging to the functional groups of binders and anti-caking agents
Dodatki iz funkcionalne skupine vezalcev in sredstev proti strjevanju
Annex II to Directive 2002/32/EC is replaced by the following:
Priloga II k Direktivi 2002/32/ES se nadomesti z:
‘Undesirable substances
„Nezaželene snovi
Action threshold relative to a feedingstuff with a moisture content of 12 %
Prag za ukrepanje pri krmi z 12-odstotno vsebnostjo vlage
Comments and additional information (e.g. nature of investigations to be performed)
Pripombe in dodatni podatki (npr. vrsta preiskav, ki jih je treba opraviti)
Dioxins (sum of polychlorinated dibenzo-para-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) expressed in World Health Organisation (WHO) toxic equivalents, using the WHO-TEFs (toxic equivalency factors, 1997 [5]
Dioksini (vsota polikloriranih dibenzo-para-dioksinov (PCDD) polikloriranih dibenzofuranov (PCDF), izraženih v toksičnih ekvivalentih Svetovne zdravstvene organizacije (WHO) z uporabo WHO-TEF (faktorji toksične ekvivalence, 1997) [5]
Identification of source of contamination.
Določitev vira kontaminacije.
Once source is identified, take appropriate measures, where possible, to reduce or eliminate source of contamination.
Potem ko je vir določen, se sprejmejo ustrezni ukrepi, kjer je to mogoče, 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 veliko 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., should 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 je treba, če je prag za ukrepanje presežen, zapisati 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.
Fish, other aquatic animals, their products and by-products with the exception of fish oil and fish protein hydrolysates containing more than 20 % fat
Ribe, druge vodne živali, njihovi proizvodi in stranski proizvodi, razen ribje olje in ribji beljakovinski hidrolizati, ki vsebujejo več kot 20 % maščobe
However, in cases where the action level is exceeded, all information, such as sampling period, geographical origin, fish species etc., must 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 je treba, če je prag za ukrepanje presežen, zapisati 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.
Compound feedingstuffs, with the exception of feedingstuffs for fur animals, pet foods and feedingstuffs for fish
Krmne mešanice, razen krme za kožuharje, hrane za hišne živali in krme za ribe
Dioxin like PCBs (sum of polychlorinated biphenyls (PCBs) expressed in World Health Organisation (WHO) toxic equivalents, using the WHO-TEFs (toxic equivalency factors, 1997 [5]
Dioksinom podobni PCB (vsota polikloriranih bifenilov (PCB), izražena v ekvivalentih toksičnosti Svetovne zdravstvene organizacije (WHO) z uporabo WHO-TEF (faktorji toksične ekvivalentov toksičnosti, 1997) [5]
WHO-TEFs for human risk assessment based on the conclusions of the World Health Organisation meeting in Stockholm, Sweden, 15-18 June 1997 (Van den Berg et al., (1998) Toxic Equivalency Factors (TEFs) for PCBs, PCDDs, and PCDFs for Humans and for Wildlife.
WHO-TEF za oceno nevarnosti 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 PCB ne-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.
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.
Zgornje koncentracije; zgornje koncentracije so izračunane ob predpostavki, da so vse vrednosti različnih spojin pod mejo določanja enake meji določanja.
The products intended for animal feed mentioned in point 27a have to comply both with the maximum levels for dioxins and with the maximum levels for the sum of dioxins and dioxin-like PCBs during that temporary period.
Proizvodi, namenjeni za živalsko krmo iz točke 27a, morajo biti v tem začasnem obdobju v skladu z mejnimi vrednostmi za dioksine ter mejnimi vrednostmi za vsoto dioksinov in dioksinom podobnih PCB.
Fresh fish directly delivered and used without intermediate processing for the production of feed for fur animals is not subject to the maximum levels, while maximum levels of 4,0 ng WHO-PCDD/F-TEQ/kg product and 8,0 ng WHO-PCDD/F-PCB-TEQ/kg product are applicable to fresh fish used for the direct feeding of pet animals, zoo and circus animals.
Sveže ribe, neposredno dostavljene in porabljene brez vmesne predelave za proizvodnjo krme za kožuharje, so izvzete iz mejnih vrednosti, mejni vrednosti 4,0 ng WHO–PCDD/F–TEKV/kg proizvoda in 0,8 ng WHO–PCDD/F–TEKV/kg proizvoda pa se uporabljata za sveže ribe, ki se uporabljajo za neposredno prehrano hišnih živali ter živali v živalskih vrtovih in cirkusih.
The products, 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, predelani živalski proteini, proizvedeni iz teh živali (kožuharji, hišne živali ter živali v živalskih vrtovih in cirkusih), ne morejo vstopati v prehrambeno verigo in jih je prepovedano krmiti gojenim živalim, ki se gojijo, vzrejajo ali razmnožujejo za proizvodnjo hrane.“
WHO-TEFs for human risk assessment based on the conclusions of the World Health Organisation meeting in Stockholm, Sweden, 15-18 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 nevarnosti 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.
The Commission will review these action levels by 31 December 2008 at the latest at the same time as it reviews the maximum levels for the sum of dioxins and dioxin-like PCBs.’
Komisija bo te pragove za ukrepanje preučila najpozneje do 31. decembra 2008, hkrati s preučitvijo mejnih vrednosti za vsoto dioksinov in dioksinom podobnih PCB.“
Feedingstuffs for fish.
Krma za ribe
0,75 ng WHO-PCDD/F-TEQ/kg [2] [3]
0,75 ng WHO-PCDD/F-TEKV/kg [2] [3]
1,0 ng WHO-PCDD/F-TEQ/kg [2] [3]
1,0 ng WHO-PCDD/F-TEKV/kg [2] [3]
2,0 ng WHO-PCDD/F-TEQ/kg [2] [3]
2,0 ng WHO-PCDD/F-TEKV/kg [2] [3]
6,0 ng WHO-PCDD/F-TEQ/kg [2] [3]
6,0 ng WHO-PCDD/F-TEKV/kg [2] [3]
1,25 ng WHO-PCDD/F-TEQ/kg [2] [3]
1,25 ng WHO-PCDD/F-TEKV/kg [2] [3]
2,25 ng WHO-PCDD/F-TEQ/kg [2] [3]
2,25 ng WHO-PCDD/F-TEKV/kg [2] [3]
1,25 ng WHO-PCDD/F-PCB-TEQ/kg [2]
1,25 ng WHO-PCDD/F-PCB-TEKV/kg [2]
1,5 ng WHO-PCDD/F-PCB-TEQ/kg [2]
1,5 ng WHO-PCDD/F-PCB-TEKV/kg [2]
3,0 ng WHO-PCDD/F-PCB-TEQ/kg [2]
3,0 ng WHO-PCDD/F-PCB-TEKV/kg [2]
24,0 ng WHO-PCDD/F-PCB-TEQ/kg [2]
24,0 ng WHO-PCDD/F-PCB-TEKV/kg [2]
4,5 ng WHO-PCDD/F-PCB-TEQ/kg [2]
4,5 ng WHO-PCDD/F-PCB-TEKV/kg [2]
11,0 ng WHO-PCDD/F-PCB-TEQ/kg [2]
11,0 ng WHO-PCDD/F-PCB-TEKV/kg [2]
7,0 ng WHO-PCDD/F-PCB-TEQ/kg [2]
7,0 ng WHO-PCDD/F-PCB-TEKV/kg [2]
0,5 ng WHO-PCDD/F-TEQ/kg [6] [7]
0,5 ng WHO-PCDD/F-TEKV/kg [6] [7]
1,0 ng WHO-PCDD/F-TEQ/kg [6] [7]
1,0 ng WHO-PCDD/F-TEKV/kg [6] [7]
5,0 ng WHO-PCDD/F-TEQ/kg [6] [7]
5,0 ng WHO-PCDD/F-TEKV/kg [6] [7]
1,75 ng WHO-PCDD/F-TEQ/kg [6] [7]
1,75 ng WHO-PCDD/F-TEKV/kg [6] [7]
0,35 ng WHO-PCB-TEQ/kg [6] [7]
0,35 ng WHO-PCB-TEKV/kg [6] [7]
0,5 ng WHO-PCB-TEQ/kg [6] [7]
0,5 ng WHO-PCB-TEKV/kg [6] [7]
0,75 ng WHO-PCB-TEQ/kg [6] [7]
0,75 ng WHO-PCB-TEKV/kg [6] [7]
14,0 ng WHO-PCB-TEQ/kg [6] [7]
14,0 ng WHO-PCB-TEKV/kg [6] [7]
2,5 ng WHO-PCB-TEQ/kg [6] [7]
2,5 ng WHO-PCB-TEKV/kg [6] [7]
7,0 ng WHO-PCB-TEQ/kg [6] [7]
7,0 ng WHO-PCB-TEKV/kg [6] [7]
3,5 ng WHO-PCB-TEQ/kg [6] [7]
3,5 ng WHO-PCB-TEKV/kg [6] [7]
Commission Directive 2006/14/EC
Direktiva Komisije 2006/14/ES
amending Annex IV to Council Directive 2000/29/EC on protective measures against the introduction into the Community of organisms harmful to plants or plant products and against their spread within the Community
o spremembi Priloge IV k Direktivi Sveta 2000/29/ES o varstvenih ukrepih proti vnosu organizmov, škodljivih za rastline ali rastlinske proizvode, v Skupnost in proti njihovemu širjenju v Skupnosti
The FAO International Standard for Phytosanitary Measures (ISPM) No 15 on ‘Guidelines for regulating wood packaging material in international trade’ was adopted in March 2002 by the Fourth Interim Commission on Phytosanitary Measures (ICPM).
Mednarodni standard za fitosanitarne ukrepe (ISPM) št. 15 FAO o „Smernicah za zakonsko urejanje lesene embalaže v mednarodni trgovini“ je bil sprejet marca 2002 na četrti začasni komisiji o fitosanitarnih ukrepih (ICPM).
The relevant provisions of Directive 2000/29/EC were brought in line with those Guidelines by Commission Directive 2004/102/EC of 5 October 2004 amending Annexes II, III, IV and V to Council Directive 2000/29/EC on protective measures against the introduction into the Community of organisms harmful to plants or plant products and against their spread within the Community [2].
Ustrezne določbe Direktive 2000/29/ES so bile usklajene z navedenimi smernicami z Direktivo Komisije 2004/102/ES z dne 5. oktobra 2004 o spremembi prilog II, III, IV in V k Direktivi Sveta 2000/29/ES o varstvenih ukrepih proti vnosu organizmov, škodljivih za rastline ali rastlinske proizvode, v Skupnost in proti njihovemu širjenju v Skupnosti [2].
In addition to the measures approved under ISPM 15, Directive 2004/102/EC includes a requirement that imported wood packaging material be made from debarked round wood.
Poleg teh ukrepov, ki so odobreni s standardom ISPM št. 15, Direktiva 2004/102/ES vključuje zahtevo, da je uvoženi leseni material za embalažo izdelan iz olupljene hlodovine.
ISPM No 15 made this an option subject to technical justification.
Po standardu ISPM št. 15 je to druga možnost k tehnični ustreznosti.