natgillin/translations-raw huggingface dataset:
The figures in the following table can be used to determine the number of incremental samples to be taken.
Za določitev števila vzetih primarnih vzorcev se lahko uporablja naslednja preglednica.
Number of incremental samples to be taken depending on the weight of the lot of cereals and cereal products
Število primarnih vzorcev, ki jih je treba vzeti, je odvisno od mase lota žit in žitnih izdelkov
Lot weight (tonnes)
Masa lota (tone)
Number of incremental samples to be taken depending on the weight of the lot of roasted coffee beans, ground roasted coffee, soluble coffee and dried vine fruit
Število primarnih vzorcev, ki jih je treba vzeti, je odvisno od mase lota praženih kavnih zrn, zmlete pražene kave, instant kave in grozdnega soka
the following point 4.6(a) is inserted after point 4.6:
Po točki 4.6 se vstavi točka 4.6.a:
‘4.6(a)
„4.6.a
Sampling provisions for wine and grape juice
Določbe za vzorčenje za vino in grozdni sok
The aggregate sample shall be at least 1 kg except where it is not possible e.g. when the sample consists of 1 bottle.
Sestavljeni vzorec mora imeti vsaj 1 kg, razen če to ni možno, na primer ko vzorec sestavlja 1 steklenica.
The minimum number of incremental samples to be taken from the lot shall be as given in table 4.
Najmanjše število primarnih vzorcev, vzetih iz serije, je isto kot v preglednici 4.
The number of incremental samples determined is function of the usual form in which the products concerned are commercialised.
Določeno število primarnih vzorcev je odvisno od običajne oblike, v kateri so zadevni proizvodi trženi.
In the case of bulk liquid products, the lot shall be thoroughly mixed insofar as possible and insofar as it does not affect the quality of the product, by either manual or mechanical means immediately prior to sampling.
Za razsute tekoče proizvode se serija, kolikor je temeljito mogoče in dokler ne vpliva na kakovost proizvoda, ročno ali mehansko premeša neposredno pred vzorčenjem.
In this case, a homogeneous distribution of ochratoxin A can be assumed within a given lot.
V tem primeru se lahko sklepa na homogeno porazdelitev ohratoksina A v zadevni seriji.
It is therefore sufficient to take three incremental samples from a lot to form the aggregate sample.
Zato zadošča, da se vzamejo trije primarni vzorci iz serije za sestavo sestavljenega vzorca.
The incremental samples, which might frequently be a bottle or a package, shall be of similar weight.
Primarni vzorci, ki so pogosto steklenice ali paketi, so podobne teže.
The weight of an incremental sample should be at least 100 grams, resulting in an aggregate sample of at least about 1 kg.
Teža primarnega vzorca mora biti najmanj 100 g, ki se združijo v sestavljen vzorec, ki tehta najmanj 1 kg.
Departure from this procedure must be recorded in the record provided for in point 3.8.
O odstopanju od tega postopka je treba poročati v zapisniku, predpisanem v točki 3.8.
Minimum number of incremental samples to be taken from the lot
Število primarnih vzorcev, ki jih je treba vzeti iz serije
Form of commercialisation
Oblika, v kateri se predmet trži
Weight of lot (in litres)
Masa serije (v litrih)
Minimum number of incremental samples to be taken
Najmanjše število primarnih vzetih vzorcev
Bulk (grape juice, wine)
Razsuti proizvodi (grozdni sok, vino)
Bottles/packages grape juice
Steklenice/pakiranja grozdnega soka
Bottles/packages wine
Steklenice/pakiranja vina
Depending on the lot weight — see table 2 of this Annex.
Odvisno od mase lota – glej preglednico 2 te priloge.
Depending on the lot weight — see table 3 of this Annex.
Odvisno od mase lota – glej preglednico 3 te priloge.
Commission Directive 2005/6/EC
Direktiva Komisije 2005/6/ES
amending Directive 71/250/EEC as regards reporting and interpretation of analytical results required under Directive 2002/32/EC
o spremembi Direktive 71/250/EGS glede poročanja in razlage rezultatov analiznega preskušanja, zahtevanih po Direktivi 2002/32/ES
Having regard to the Council Directive 70/373/EEC of 20 July 1970 on the introduction of Community methods of sampling and analysis for the official control of feeding-stuffs [1], and in particular Article 2 thereof,
ob upoštevanju Direktive Sveta 70/373/EGS z dne 20. julija 1970 o uvedbi metod vzorčenja in analiz Skupnosti za uradni nadzor krme [1], in zlasti člena 2 Direktive,
Commission Directive 71/250/EEC of 15 June 1971 establishing Community methods of analysis for the official control of feeding-stuffs [2] includes provisions concerning the expression of results.
Direktiva Komisije 71/250/EGS z dne 15. junija 1971 o določitvi analitskih metod Skupnosti za uradni nadzor krme [2] vključuje določbe glede podajanja rezultatov.
To ensure a harmonised implementation approach to Directive 2002/32/EC of the European Parliament and of the Council of 7 May 2002 on undesirable substances in animal feed [3] in all Member States, it is of major importance that analytical results are reported and interpreted in a uniform way.
Za zagotovitev usklajenega izvajanja Direktive Evropskega Parlamenta in Sveta 2002/32/ES z dne 7. maja 2002 o nezaželenih snoveh v živalski krmi [3] v vseh državah članicah, je zelo pomembno, da se o rezultatih analitskega preskušanja poroča in se jih razloži na enoten način.
Directive 71/250/EEC should therefore be amended accordingly.
Direktivo 71/250/EGS je zato treba ustrezno spremeniti.
Directive 71/250/EEC is amended as follows:
Direktiva 71/250/EGS se spremeni:
In Article 1 the following paragraph is added after the second paragraph:
V členu 1 se za drugim odstavkom doda naslednji odstavek:
‘As regards undesirable substances within the meaning of Directive 2002/32/EC of the European Parliament and of the Council including dioxins and dioxin-like PCBs, point C(3) of Part 1 of the Annex to this Directive shall apply.’
„Za nezaželene snovi po Direktivi Evropskega parlamenta in Sveta 2002/32/ES, vključno z dioksini in dioksinom podobnimi PCB-ji, se uporablja točka C(3) dela 1 Priloge k tej direktivi.“
The Annex is amended in accordance with the Annex to this Directive.
Priloga se spremeni 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 twelve months after the entry into force.
Države članice sprejmejo zakone in druge predpise, potrebne za uskladitev s to direktivo, dvanajst mesecev po njenem začetku veljavnosti.
Member States shall communicate to the Commission the texts of the provisions of national law which they adopt in the field covered by this Directive.
Države članice posredujejo Komisiji besedila predpisov nacionalne zakonodaje, ki jih sprejmejo na področju, zajetem v tej direktivi.
Directive as last amended by Commission Directive 1999/27/EC (OJ L 118, 6.5.1999, p. 36).
Direktiva, kakor je bila nazadnje spremenjena z Direktivo Komisije 1999/27/ES (UL L 118, 6.5.1999, str. 36).
In point C, application of methods of analysis and expression of results, of Part 1, general provisions on methods of analysis for feedingstuffs, of the Annex to Directive 71/250/EEC the following point 3 is added:
V točki C, uporaba metod analize in podajanje rezultatov, dela 1 – splošne določbe o metodah analize za krmo Priloge k Direktivi 71/250/EGS se doda točka 3:
As regards undesirable substances within the meaning of Directive 2002/32/EC, including dioxins and dioxin-like PCBs, a product intended for animal feed shall be considered as non compliant with the established maximum content, if the analytical result is deemed to exceed the maximum content taking into account expanded measurement uncertainty and correction for recovery.
Za nezaželene snovi po Direktivi 2002/32/ES, vključno z dioksini in dioksinom podobnimi PCB-ji, se proizvod, namenjen za živalsko krmo šteje za neskladnega z določeno najvišjo vsebnostjo, če se za rezultat analitskega preskušanja šteje, da presega najvišjo vsebnost, ob upoštevanju razširjene nezanesljivosti meritev in popravka za izkoristek.
The analysed concentration corrected for recovery and the expanded measurement uncertainty subtracted from the analytical result is used to assess compliance.
Analizirana koncentracija s popravkom za izkoristek in odšteto razširjeno nezanesljivostjo meritev se uporabi za oceno skladnosti.
This procedure is only applicable in cases where the method of analysis enables the estimation of measurement uncertainty and correction for recovery (eg. Not possible in case of microscopic analysis)
Slednja se uporabi le v primerih, kjer metoda analize omogoča oceno nezanesljivosti meritev in popravka za izkoristek (npr. ni možna v primeru mikroskopske analize).
The analytical result shall be reported as follows (in so far the used method of analysis enables to estimate the measurement uncertainty and recovery rate):
O rezultatu analiznega preskušanja se poroča (če uporabljena metoda analize omogoča ocenitev nezanesljivosti meritev in popravka za izkoristek):
corrected or uncorrected for recovery, the manner of reporting and the level of recovery being indicated;
če je za izkoristek pravilen ali nepravilen; način poročanja in raven izkoristka sta navedena;
as “x +/- U”, whereby x is the analytical result and U is the expanded measurement uncertainty, using a coverage factor of 2 which gives a level of confidence of approximately 95 %.’
kot ‚x +/- U‘, kjer je x rezultat analiznega preskušanja in je U razširjena nezanesljivost meritev, ob uporabi faktorja za zajetje 2, ki daje stopnjo zanesljivosti približno 95 %.“
Commission Directive 2005/7/EC
Direktiva Komisije 2005/7/ES
amending Directive 2002/70/EC establishing requirements for the determination of levels of dioxins and dioxin-like PCBs in feedingstuffs
o spremembi Direktive 2002/70/ES o določitvi zahtev za določanje vrednosti dioksinov in dioksinom podobnih PCB-jev v krmi
Having regard to Council Directive 70/373/EEC of 20 July 1970 on the introduction of Community methods of sampling and analysis for the official control of feeding-stuffs [1], and in particular Article 2 thereof,
ob upoštevanju Direktive Sveta 70/373/EGS z dne 20. julija 1970 o uvedbi metod vzorčenja in analiz Skupnosti za uradni nadzor krme [1], in zlasti člena 2 Direktive,
Commission Directive 2002/70/EC of 26 July 2002 establishing requirements for the determination of levels of dioxins and dioxin-like PCBs in feedingstuffs [2], lays down specific provisions concerning the methods of analysis to be applied for the official control provided for in Directive 70/373/EEC.
Direktiva Komisije 2002/70/ES z dne 26. julija 2002 o določitvi zahtev za določanje vrednosti dioksinov in dioksinom podobnih PCB-jev v krmi [2] določa posebne določbe glede metod analize, ki jih je treba uporabiti za uradni nadzor, določen v Direktivi 70/373/EGS.
The sampling procedure laid down in Commission Directive 76/371/EEC of 1 March 1976 establishing Community methods of sampling for the official control of feedingstuffs [3] has to be applied for the official control of the levels of dioxins and the determination of dioxin-like PCBs in certain feedingstuffs.
Postopek vzorčenja, določen v Direktivi Komisije 76/371/EGS z dne 1. marca 1976 o določitvi metod Skupnosti za vzorčenje pri uradnem nadzoru krme [3] se morajo uporabljati za uradni nadzor vrednosti dioksinov in določitev dioksinom podobnih PCB-jev v krmi.
It is appropriate to specify that the quantitative requirements in relation to the control of substances or products uniformly distributed throughout the feedingstuffs should be applied.
Priporočljivo je določiti, naj se uporabljajo zahteve v zvezi s količino glede nadzora snovi ali proizvodov, enakomerno porazdeljenih v krmi.
It is of major importance that analytical results are reported and interpreted in a uniform way in order to ensure a harmonised implementation approach in all Member States.
Zelo pomembno je, da se o rezultatih analiznega preskušanja poroča in se jih razlaga na enovit način, da se zagotovi usklajeno izvajanje v vseh državah članicah.
Directive 2002/70/EC should therefore be amended accordingly.
Zato je Direktivo 2002/70/ES treba ustrezno spremeniti.
The measures provided for in this Directive are in accordance with the opinion of the Standing Committee on the Food Chain and Animal Health,
Ukrepi, predvideni s to direktivo, so v skladu z mnenjem Stalnega odbora za živilsko verigo in zdravstveno varstvo živali –
The Annexes to Directive 2002/70/EC are amended in accordance with the Annex to this Directive.
Priloge k Direktivi 2002/70/ES se spremenijo skladno s Prilogo k tej direktivi.
Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive 12 months after the entry into force at the latest.
Države članice sprejmejo zakone in druge predpise, potrebne za uskladitev s to direktivo, najpozneje dvanajst mesecev po začetku veljavnosti Direktive.
They shall forthwith communicate to the Commission the text of those provisions and a correlation table between those provisions and this Directive.
Komisiji nemudoma posredujejo besedilo navedenih predpisov in korelacijsko tabelo med navedenimi predpisi in to direktivo.
Member States shall communicate to the Commission the texts of the provisions of national law which they adopt in the field covered by this Directive.
Države članice posredujejo Komisiji besedila predpisov nacionalne zakonodaje, ki jo sprejmejo na področju, zajetem v tej direktivi.
The Annexes to Directive 2002/70/EC are amended as follows:
Priloge k Direktivi 2002/70/ES se spremenijo:
Purpose and scope
Namen in področje uporabe
The samples intended for the official control of the levels of dioxins (PCDD/PCDF) content, as well for the determination of the content of dioxin like PCBs in feedingstuffs, shall be taken in accordance with the provisions of Directive 76/371/EEC.
Vzorci, ki so namenjeni za uradni nadzor vsebnosti dioksinov (PCDD/PCDF) kot tudi za opredelitev vsebnosti dioksinom podobnih PCB-jev v krmi, se odvzamejo v skladu z določbami Direktive 76/371/EGS. Izpolnjene morajo biti zahteve v zvezi s količino glede nadzora snovi ali proizvodov, ki so enakomerno porazdeljeni v krmi v skladu s točko 5.A.
The quantitative requirements in relation to the control of substances or products uniformly distributed throughout the feedingstuffs as provided for in point 5.A of the Annex to Directive 76/371/EEC have to be applied.
Priloge k Direktivi 76/371/EGS.
Aggregate samples thus obtained shall be considered as representative for the lots or sublots from which they are taken.
Tako dobljeni sestavljeni vzorci se štejejo za reprezentativne za serije ali podserije, iz katerih so vzeti.
Compliance with maximum levels laid down in Directive 2002/32/EC of the European Parliament and of the Council shall be established on the basis of the levels determined in the laboratory samples.2.
Skladnost z mejnimi vrednostmi iz Direktive 2002/32/ES Evropskega parlamenta in Sveta se ugotavlja na osnovi vrednosti, določenih v laboratorijskih vzorcih.2.
Compliance of the lot or sublot with the specification
Skladnost serij ali podserij s specifikacijo
The lot is accepted if the analytical result of a single analysis does not exceed the respective maximum level as laid down in Directive 2002/32/EC taking into account the measurement uncertainty.
Serija je sprejeta, če rezultat analiznega preskušanja posamezne analize ne presega zadevne zgornje meje vrednosti, določene v Direktivi 2002/32/ES ob upoštevanju nezanesljivosti meritev.
The lot is non-compliant with the maximum level as laid down in Directive 2002/32/EC, if the analytical result confirmed by duplicate analysis and calculated as mean of at least two separate determinations exceeds the maximum level beyond reasonable doubt taking into account the measurement uncertainty.
Serija je neskladna z zgornjo mejo vrednosti, določeno v Direktivi 2002/32/ES, če je rezultat analiznega preskušanja potrjen z dvakratno analizo, izračunano povprečje vsaj dveh ločenih določitev pa skoraj gotovo presega zgornjo mejo vrednosti, ob upoštevanju nezanesljivosti meritev.
Measurement uncertainty may be taken into account according to one of the following approaches:
Nezanesljivost meritev se lahko upošteva v skladu z enim 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 za zajetje 2, ki da raven zanesljivosti približno 95 %;
by establishing the decision limit (CCα) in accordance with Commission Decision 2002/657/EC (point 3.1.2.5 of the Annex — the case of substances with established permitted level).The present interpretation rules apply for the analytical result obtained on the sample for official control.
z določitvijo meje, potrebne za odločitev (CCα) v skladu z Odločbo Komisije 2002/657/ES (točka 3.1.2.5. Priloge – v primeru snovi z določeno dovoljeno vrednostjo).Sedanja pravila za razlaganje se uporabljajo za rezultat analiznega preskušanja, dobljenega na vzorcu za uradni nadzor.
It does not affect the right of Member States to apply national rules to analyses for defence or referee purposes referred to in Article 18 of Directive 95/53.’
To ne posega v pravico držav članic, da uporabljajo nacionalna pravila za analize za namene obrambe ali sodnega izvedenstva iz člena 18 Direktive 95/53.“
In Annex II, the following paragraph is added at the end of point 2 Background:
V Prilogi se naslednji odstavek doda na koncu točke 2. Ozadje:
‘For the purposes of this Directive only, the accepted specific limit of quantification of an individual congener is the concentration of an analyte in the extract of a sample which produces an instrumental response at two different ions to be monitored with an S/N (signal/noise) ratio of 3:1 for the less sensitive signal and fulfilment of the basic requirements such as e.g. retention time, isotope ratio according to the determination procedure as described in EPA method 1613 revision B.’
„Za namene samo te direktive je sprejemljiva meja določljivosti posameznega kongenerja koncentracija analita v izvlečku (ekstraktu) vzorca, ki ustvari instrumentalni odziv na dva različna iona, ki se ju spremlja z razmerjem S/N (signal/šum) 3:1 za manj občutljivi signal, in izpolnitev osnovnih zahtev, kot so retencijski čas, razmerje izotopov v skladu s postopkom določanja, kakor je naveden v metodi EPA 1613, revizija B.“
Table of dioxin-like PCBsAbbreviations used: “T” = tetra; “Pe” = penta; “Hx” = hexa; “Hp” = hepta; “O” = octa; “CDD” = chlorodibenzo-p-dioxin; “CDF” = chlorodibenzofuran; “CB” = chlorobiphenyl.
Preglednica dioksinom podobnih PCB-jevUporabljene kratice: ‚T’ = tetra; ‚Pe’ = penta; ‚Hx’ = heksa; ‚Hp’ = hepta; ‚O’ = okta; ‚CDD’ = klorodibenzo-p-dioksin; ‚CDF’ = klorodibenzofuran; ‚CB’ = klorobifenil.
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” PCBs: Non-ortho PCBs + Mono-ortho PCBs)Non-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 1890,0001
KongenerVrednost faktorja toksične ekvivalence (TEF)Dibenzo-p-dioksini (‚PCDD-ji’) 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-ji’) 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‚Dioksinom podobni’ PCB-ji: neorto PCB-ji + monoorto PCB-jiNeorto PCB-jiPCB 770,0001PCB 810,0001PCB 1260,1PCB 1690,01Monoorto PCB-jiPCB 1050,0001PCB 1140,0005PCB 1180,0001PCB 1230,0001PCB 1560,0005PCB 1570,0005PCB 1670,00001PCB 1890,0001
Commission Directive 2005/8/EC
Direktiva Komisije 2005/8/ES
amending Annex I to Directive 2002/32/EC of the European Parliament and of the Council on undesirable substances in animal feed
o spremembi Priloge I k Direktivi Evropskega parlamenta in Sveta 2002/32/ES o nezaželenih snoveh v živalski krmi
Having regard to Directive 2002/32/EC of the European Parliament and of the Council of 7 May 2002 on undesirable substances in animal feed [1], and in particular Article 8(1) thereof,
ob upoštevanju Direktive Evropskega parlamenta in Sveta 2002/32/ES z dne 7. maja 2002 o nezaželenih snoveh v živalski krmi [1] in zlasti člena 8(1) Direktive,
Directive 2002/32/EC provides that the use of products intended for animal feed which contain levels of undesirable substances exceeding the maximum levels laid down in Annex I thereto is prohibited.
Direktiva 2002/32/ES prepoveduje rabo proizvodov, namenjenih živalski krmi, ki vsebujejo vrednosti nezaželenih snovi, ki presegajo najvišje mejne vrednosti iz Priloge I.
When Directive 2002/32/EC was adopted, the Commission stated that the provisions laid down in Annex I to that Directive would be reviewed on the basis of updated scientific risk assessments and taking into account the prohibition of any dilution of contaminated non-complying products intended for animal feed.
Pri sprejemu Direktive 2002/32/ES je Komisija navedla, da se bodo določbe iz Priloge I k navedeni direktivi ponovno pregledale na podlagi najnovejše znanstvene ocene tveganja in z upoštevanjem prepovedi razredčenja kontaminiranih proizvodov, namenjenih živalski krmi, ki ne izpolnjujejo zahtev.
Before a complete review based on an updated scientific risk assessment can be carried out, it is necessary to provide for certain amendments in the light of developments in scientific and technical knowledge.
Preden bo mogoče opraviti popoln pregled na podlagi najnovejše znanstvene ocene tveganja, je treba sprejeti nekatere spremembe glede na razvoj znanstvenih in tehničnih dognanj.
It is appropriate to clarify the term green fodder.
Primerno je pojasniti izraz zelena krma.
Since the supply of calcium carbonate, an essential and valuable feed material, could be endangered because the level of total mercury due to normal background contamination is close to or exceeds the maximum level laid down in the Annex I to Directive 2002/32/EC, that maximum level should be amended, taking into account that mercury is present in calcium carbonate in its inorganic form and that the Scientific Committee for Animal Nutrition confirms that mercury in inorganic form is significantly less toxic than organic mercury, in particular methyl mercury.
Ker je lahko ogrožena dobava kalcijevega karbonata, ki je bistveno in dragoceno krmilo, saj se vrednost skupnega živega srebra zaradi normalne izvorne kontaminacije približuje ali presega najvišjo mejno vrednost iz Priloge I k Direktivi 2002/32/ES, je treba to najvišjo mejno vrednost spremeniti z upoštevanjem, da je živo srebro navzoče v kalcijevem karbonatu v njegovi neorganski obliki in da Znanstveni odbor za živalsko prehrano potrjuje, da je živo srebro v neorganski obliki občutno manj toksično kot organsko živo srebro in zlasti metil živo srebro.
The maximum level for fluorine in other complementary feedingstuffs is 125 mg/kg per 1 % phosphorus.
Najvišja mejna vrednost fluora v drugih dopolnilnih krmnih mešanicah je 125 mg/kg na 1 % fosforja.
For environmental reasons, the level of phosphorus in animal feed is restricted and the digestibility and bioavailability of phosphorus is improved by making use of an enzyme such as phytase.
Zaradi okoljskih razlogov je vrednost fosforja v živalski krmi omejena, prebavljivost in biološka uporabnost pa izboljšani z uporabo encima, kot je fitaza.
It is therefore no longer appropriate to establish the maximum level as per 1 % of phosphorus but to establish the maximum level for complementary feed relative to a feedingstuff with a moisture content of 12 %.
Zaradi tega ni več primerno določiti najvišje mejne vrednosti glede na 1 % fosforja, ampak jo je za dopolnilno krmo treba določiti glede na krmno mešanico z 12 % vsebnostjo vlage.
Directive 2002/32/EC should therefore be amended accordingly.
Direktivo 2002/32/ES je treba ustrezno spremeniti.