natgillin/translations-raw huggingface dataset:
The following R-phrases are considered relevant for this product group:
Naslednji stavki R se štejejo za pomembne za to skupino proizvodov:
R 20, R 21, R 22, R 23, R 24, R 25, R 26, R 27, R 28, R 33, R 34, R 35, R 36, R 37, R 38, R 39, R 40, R 41, R 42, R 43, R 45, R 46, R 48, R 49, R 50, R 51, R 52, R 53, R 59, R 60, R 61, R 62, R 63, R 64, R 65, R 66, R 67, R 68, and combinations thereof.
R 20, R 21, R 22, R 23, R 24, R 25, R 26, R 27, R 28, R 33, R 34, R 35, R 36, R 37, R 38, R 39, R 40, R 41, R 42, R 43, R 45, R 46, R 48, R 49, R 50, R 51, R 52, R 53, R 59, R 60, R 61, R 62, R 63, R 64, R 65, R 66, R 67, R 68, in njihove kombinacije.
Assessment and verification of criterion 1
Ocenjevanje in preverjanje merila 1
Conformity with criterion 1 shall be stated in writing and signed by the applicant company.
Skladnost z merilom 1 se navede pisno in podpiše s strani podjetja vlagatelja.
All main components included in the product shall be unambiguously stated, giving their names and where applicable, their Einecs or Elincs number and the concentrations in which they are used.
Vse glavne sestavine v proizvodu se jasno navedejo z nazivi in, če je to primerno, z njihovo številko EINECS ali ELINCS ter s koncentracijami, v katerih se uporabljajo.
The producer of the product shall provide the competent body with:
Proizvajalec proizvoda pristojnemu organu zagotovi:
a product safety data sheet (meeting the requirements of Commission Directive 91/155/EEC [1]).safety data sheets of applicant suppliers (meeting the requirements of Directive 91/155/EEC and Council Directive 67/548/EEC [2]) for each main component.Sufficient data shall be available to allow for the evaluation of the environmental hazards (indicated by the R-phrases: R 50, R 50/53, R 51/53, R 52, R 52/53, R 53), of the product in accordance with Directives 91/155/EEC and 1999/45/EC.
varnostni list proizvoda (ki izpolnjuje zahteve Direktive Komisije 91/155/EGS [1]).varnostne liste vlagateljev dobaviteljev (ki izpolnjujejo zahteve iz Direktive 91/155/EGS in Direktive Sveta 67/548/EGS [2]) za vsako glavno sestavino.Zagotoviti je treba zadostno količino podatkov, da se omogoči ovrednotenje nevarnosti proizvoda za okolje (označene s stavki R: R 50, R 50/53, R 51/53, R 52, R 52/53, R 53) v skladu z direktivama 91/155/EGS in 1999/45/ES.
The evaluation of a product for hazards to the environment shall be performed by the conventional method as indicated in Annex III to Directive 1999/45/EC.
Ovrednotenje nevarnosti proizvoda za okolje se izvede z običajno metodo, kakor je navedena v Prilogi III k Direktivi 1999/45/ES.
However, as defined by part C of Annex III to that Directive, the results of testing the preparation (either the product preparation or the additive package) as such can be used to modify the classification concerning the aquatic toxicity that would have been obtained using the conventional method.
Vendar, kakor je navedeno v delu C Priloge III k navedeni direktivi, se lahko rezultati testiranja pripravka (bodisi pripravka proizvoda ali paketa dodatkov) kot takega uporabijo za spremembo razvrstitve glede strupenosti za vodno okolje, ki bi bili pridobljeni z običajno metodo.
Additional aquatic toxicity requirements
Dodatne zahteve glede strupenosti za vodno okolje
The applicant shall demonstrate compliance by meeting the requirements of either criterion 2.1 or criterion 2.2.
Vlagatelj dokaže skladnost s tem, da zadosti zahtevam po merilu 2.1 ali merilu 2.2.
Criterion 2.1. Requirements for the preparation and main components
Merilo 2.1 Zahteve za pripravek in glavne sestavine
Data are required on the aquatic toxicity of:
Potrebni so podatki o strupenosti za vodno okolje za:
the preparation, and
pripravek, in
the main components.
glavne sestavine.
The critical concentration for the aquatic toxicity of each main component shall be at least 100 mg/l.
Kritična koncentracija strupenosti vsake glavne sestavine za vodno okolje je najmanj 100 mg/l.
The test shall be carried out on algae and daphnia (OECD 201 and 202).
Test se izvaja na algah in vodni bolhi (OECD 201 in 202).
For hydraulic oils the critical concentration for the aquatic toxicity shall be at least 100 mg/l.
Za hidravlična olja je kritična koncentracija strupenosti za vodno okolje najmanj 100 mg/l.
For greases, chainsaw oils, concrete release agents and other total loss lubricants the critical concentration for the aquatic toxicity shall be at least 1000 mg/l.
Za masti, olja za verižne žage, sredstva za razkalupljanje betona in druga maziva, ki gredo v celoti v izgubo, je kritična koncentracija strupenosti za vodno okolje najmanj 1000 mg/l.
Greases may be evaluated by providing data for the preparation and the main components only if the thickener shows ultimate biodegradation (see criterion 3) or inherent biodegradation according to:
Masti se lahko ovrednoti z zagotovitvijo podatkov za pripravek in glavne sestavine samo, če sredstvo za zgoščevanje pokaže končno biorazgradnjo (glej merilo 3) ali inherentno biorazgradnjo v skladu z:
a biodegradation > 70 % in the OECD 302 C test for inherent biodegradation or equivalent test methods, or
biorazgradnjo > 70 % pri testu OECD 302 C za inherentno biorazgradnjo ali enakovrednih testnih metodah, ali
a biodegradation > 20 % but < 60 % after 28 days in the OECD 301 tests based on oxygen depletion or carbon dioxide generation, or
biorazgradnjo > 20 % toda < 60 % po 28 dneh pri testih OECD 301 na podlagi izčrpanosti kisika ali na podlagi proizvajanja ogljikovega dioksida, ali
biodegradation > 60 % in ISO 14593 (CO2 headspace test).
biorazgradnjo > 60 % pri ISO 14593 (test parne faze CO2).
The test on the preparation shall be carried out on all three groups of species (OECD 201, 202, and 203).
Test na pripravku se izvede na vseh treh skupinah vrst (OECD 201, 202 in 203).
Table 1 summarises the requirements for the different product subgroups according to criterion 2.1.
Razpredelnica 1 povzema zahteve za različne podskupine proizvodov v skladu z merilom 2.1.
Table 1
Razpredelnica 1
Aquatic toxicity requirements for the different product subgroups — Data requirements for the preparation and main components
Zahteve glede strupenosti za vodno okolje za različne podskupine proizvodov – Zahteve glede podatkov za pripravek in glavne sestavine
Criterion 2.1
Merilo 2.1
Hydraulic fluids
Hidravlične tekočine
Greases [3]
Masti [3]
Chainsaw oils, concrete release agents and other total loss lubricants
Olja za verižne žage, sredstva za razkalupljanje betona in druga maziva, ki gredo v celoti v izgubo
Two-stroke oils
Olja za dvotaktni motor
Aquatic toxicity for the fully formulated product in all three of the acute toxicity tests OECD 201, 202 and 203
Strupenost za vodno okolje za v celoti oblikovan proizvod pri vseh treh testih akutne strupenosti OECD 201, 202 in 203
Aquatic toxicity for each individual main component in OECD 201 and 202
Akutna strupenost za vsako posamezno glavno sestavino pri OECD 201 in 202
Assessment and verification of criterion 2.1
Ocenjevanje in preverjanje merila 2.1
Reports shall be submitted to the competent body including the data on the aquatic toxicity of the preparation and all main components by making use of either existing material from registrations or new tests, allowing compliance to be demonstrated with the requirements set out in table 1.
Pristojnemu organu se zagotovijo poročila, vključno s podatki o strupenosti pripravka in vseh glavnih sestavin na vodno okolje z uporabo bodisi obstoječega materiala iz registracij ali iz novih testov, kar omogoča, da se skladnost dokaže z zahtevami iz razpredelnice 1.
The aquatic toxicity of the preparation shall be determined according to the OECD 201, 202 and 203 or equivalent methods.
Strupenost pripravka za vodno okolje se določi v skladu z OECD 201, 202 in 203 ali enakovrednimi metodami.
The aquatic toxicity of each individual main component shall be determined according to the OECD 201 and 202 or equivalent methods.
Strupenost vsake posamezne glavne sestavine za vodno okolje se določi v skladu z OECD 201 in 202 ali enakovrednimi metodami.
Criterion 2.2. Requirements for each constituent substance
Merilo 2.2 Zahteve za vsako sestavno snov
Aquatic toxicity data shall be provided for each constituent substance intentionally added in the product.
Podatki o strupenosti za vodno okolje se zagotovijo za vsako sestavno snov, ki se namerno doda proizvodu.
One or more substances exhibiting a certain degree of aquatic toxicity are allowed in the lubricant for a cumulative mass concentration as indicated in Table 2.
Ena ali več snovi, ki izkazujejo določeno stopnjo strupenosti za vodno okolje, so dovoljene za kumulativno masno koncentracijo v mazivu, kakor je navedeno v razpredelnici 2.
Table 2
Razpredelnica 2
Aquatic toxicity requirements for the different product subgroups — Data requirements for each constituent substance
Zahteve glede strupenosti za vodno okolje za različne podskupine proizvodov – Zahteve za podatke za vsako sestavno snov
Criterion 2.2
Merilo 2.2
Cumulative mass concentration of substances present in
Kumulativna masna koncentracija snovi, prisotnih v
10 mg/l < Acute toxicity [4] ≤ 100 mg/l or 1 mg/l < NOEC ≤ 10 mg/l
10 mg/l < Akutna strupenost [4] ≤ 100 mg/l ali 1 mg/l < NOEC ≤ 10 mg/l
1 mg/l < Acute toxicity [4] ≤ 10 mg/l or 0,1 mg/l < NOEC ≤ 1 mg/l
1 mg/l < Akutna strupenost [4] ≤ 10 mg/l ali 0,1 mg/l < NOEC ≤ 1 mg/l
Acute toxicity [4] < 1 mg/l or NOEC ≤ 0,1 mg/l
Akutna strupenost [4] < 1 mg/l ali NOEC ≤ 0, 1 mg/l
Assessment and verification of criterion 2.2
Ocenjevanje in preverjanje merila 2.2
Reports shall be submitted to the competent body including the data on the aquatic toxicity of each constituent substance by making use of either existing material from registrations or new tests, demonstrating compliance with the requirements set out in Table 2.
Pristojnemu organu se zagotovijo poročila, vključno s podatki o strupenosti vsake sestavne snovi na vodno okolje z uporabo bodisi obstoječega materiala iz registracij ali iz novih testov, s katerimi se dokaže skladnost z zahtevami iz razpredelnice 2.
The aquatic toxicity of each constituent substance shall be determined according to the OECD 201 and 202 or equivalent methods.
Strupenost vsake sestavne snovi za vodno okolje se določi v skladu z OECD 201 in 202 ali enakovrednimi metodami.
Assessment and verification of both criteria 2.1 and 2.2
Ocenjevanje in preverjanje meril 2.1 in 2.2
In the case of slightly soluble components (< 10 mg/l) the method of the water accommodated fraction (WAF) can be used in the aquatic toxicity determination.
V primeru rahlo topljivih sestavin (< 10 mg/l) se za določitev strupenosti za vodno okolje lahko uporabi metoda Water Accommodated Fraction (WAF).
The established loading level, sometimes referred to as LL50 and related to the lethal loading, may be used directly in the classification criteria.
Za merila razvrščanja se lahko neposredno uporabi uveljavljena dozirna stopnja, ki se včasih navaja kot LL50, in je povezana s smrtno stopnjo.
The preparation of a water accommodated fraction shall follow the recommendations set out according to one of the following guidelines; ECETOC Technical Report No 20 (1986), Annex III to OECD 1992 301 or the ISO Guidance document ISO 10634, or ASTM D6081-98 (Standard practice for Aquatic Toxicity Testing for Lubricants: Sample Preparation and Results Interpretation or equivalent methods).
Pripravek Water Accommodated Fraction sledi priporočilom, določenim v skladu z eno od naslednjih smernic; Tehnično poročilo ECETOC št. 20 (1986), Priloga III k OECD 1992 301 ali smernica ISO dokument ISO 10634 ali ASTM D6081-98 (Standardna praksa za testiranje strupenosti maziv na vodno okolje: Priprava vzorcev in tolmačenje rezultatov ali enakovrednih metod).
The acute aquatic toxicity study on algae and daphnia (OECD 201 and 202) does not need to be conducted when:
Študije o akutni strupenosti na vodno okolje na algah in vodnih bolhah (OECD 201 in 202) ni potrebno izvajati, kadar:
the substance is unlikely to cross biological membranes MM > 800 or molecular diameter > 1,5 nm (> 15 Å),
snov po vsej verjetnosti ne bo prekoračila bioloških membran MM > 800 ali molekularnega premera > 1,5 nm (> 15 Å),
or the substance is highly insoluble in water (water solubility < 10 μg/l),
ali če je snov visoko topna v vodi (topnost v vodi < 10 μg/l),
as such substances are not regarded as toxic for algae and daphnia in the aquatic system.
kot take se snovi ne štejejo za strupene za alge in vodne bolhe v vodnem sistemu.
Similarly, the acute aquatic toxicity study on daphnia (OECD 202) does not need to be considered when a long-term toxicity study on Daphnia’s according to OECD 211 or equivalent one is available.
Prav tako ni treba izvesti študije akutne strupenosti na vodno okolje na vodnih bolhah (OECD 202), kadar je razpoložljiva dolgoročna ali enakovredna študija o strupenosti na vodne bolhe v skladu z OECD 211.
The water solubility of substances shall be determined where appropriate according to OECD 105 (or equivalent tests).
Topnost snovi v vodi se določi, kadar je primerno, v skladu z OECD 105 (ali enakovrednimi testi).
If chronic toxicity data are available (results of OECD 210 and 211 tests or equivalent methods), these may be used instead of acute aquatic toxicity data.
Če so na razpolago podatki o kronični strupenosti (rezultati testov OECD 210 in 211 ali ustreznih metod), se lahko ti uporabijo namesto podatkov o akutni strupenosti na vodno okolje.
Absence of chronic toxicity data shall be stated in writing and signed by the applicant.
Kadar ni podatkov o kronični strupenosti, vlagatelj predloži pisno podpisano izjavo.
Biodegradability and bioaccumulative potential
Biorazgradljivost in bioakumulativni potencial
The product shall not contain substances that are both:
Proizvod ne sme vsebovati snovi, ki so hkrati:
non-biodegradable,
biološko nerazgradljive,
(potentially) bioaccumulative.
(potencialno) bioakumulativne.
However, the product may contain one or more substances with a certain degree of degradability and potential or actual bioaccumulation up to a cumulative mass concentration as indicated in Table 3.
Vendar proizvod lahko vsebuje eno ali več snovi z določeno stopnjo razgradljivosti in potencialno ali dejansko bioakumulacijo do kumulativne masne koncentracije, kakor je navedeno v razpredelnici 3.
Table 3
Razpredelnica 3
Requirements for biodegradability and bioaccumulative potential
Zahteve za biorazgradljivost in za bioakumulativni potencial
Cumulative mass concentration of substances is
Kumulativna masna koncentracija snovi je
Non-biodegradable [5]
Biološko nerazgradljivo [5]
Inherently aerobically biodegradable
Inherentno aerobno biorazgradljivo
Ultimately aerobically biodegradable
Končno aerobno biorazgradljivo
Assessment and verification of criterion 3
Ocenjevanje in preverjanje merila 3
Conformity shall be demonstrated by providing the following information:
Skladnost se dokazuje s predložitvijo naslednjih podatkov:
reports including the data on the biodegradability of each constituent substance if this is not adequately shown on the safety data sheets provided for each substance,
poročili s podatki o biorazgradljivosti vsake sestavne snovi, če to ni ustrezno prikazano na varnostnih listih, podanih za vsako sestavino,
reports including the data on the bioaccumulative potential of each constituent substance:
poročili s podatki o bioakumulativnem potencialu vsake sestavne snovi:
for non-biodegradable substances, and
za biološko nerazgradljive snovi, in
for toxic and very toxic substances that are readily biodegradable (for classification purposes).
za strupene in zelo strupene snovi, ki so biološko lahko razgradljive (za namene razvrstitve).
The biodegradability shall be determined for each constituent substance in the product separately by test methods specified below (or equivalent tests).
Biološka razgradljivost se določi ločeno za vsako sestavno snov v proizvodu s testnimi metodami, opredeljenimi spodaj (ali enakovrednimi testi).
A substance is considered ultimately biodegradable (aerobic) if:
Snov se šteje za končno biološko razgradljivo (aerobno), če:
In a 28-day biodegradation study according to OECD 301 A-F or equivalent tests the following levels of biodegradation are achieved:
se v 28-dnevni študiji o biorazgradljivosti v skladu z OECD 301 A-F ali v enakovrednih testih dosežejo naslednje stopnje biorazgradljivosti:
in OECD 301 tests based upon dissolved organic carbon ≥ 70 %,
v testih OECD 301 na podlagi raztopljenega organskega ogljika ≥ 70 %,
in OECD 301 tests based upon oxygen depletion or carbonic dioxide generation ≥ 60 % of the theoretical maxima.
v testih OECD 301 na podlagi izčrpanosti kisika ali na podlagi proizvajanja ogljikovega dioksida ≥ 60 % teoretičnih maksimumov.
The BOD5/ThOD or BOD5/COD ratio is larger than 0,5.
Je količnik med BOD5/ThOD ali BOD5/COD večji od 0,5.
In the OECD test the 10-day window principle will not necessarily apply.
Pri testih OECD ni nujno, da se uporablja 10-dnevni princip okna.
If the substance reaches the biodegradation pass level within 28 days but not within the 10-day time-window, a slower degradation rate is assumed.
Če snov doseže stopnjo praga biorazgradljivosti v 28 dneh in ne v 10-dnevnem časovnem oknu, se predvideva počasnejša stopnja razgradljivosti.
A substance is considered inherently biodegradable if it shows:
Snov se šteje za inherentno biološko razgradljivo, če kaže:
a biodegradation > 70 % in the OECD 302 C test for inherent biodegradation or equivalent test method, or
biorazgradnjo > 70 % pri testu OECD 302 C za inherentno biorazgradnjo ali pri enakovredni testni metodi, ali
biodegradation ≥ 60 % in ISO 14593 (CO2 headspace test).
biorazgradnjo ≥ 60 % pri ISO 14593 (test parne faze CO2).
A substance whose primary function is thickening shall be considered inherently aerobically biodegradable if it shows a biodegradation higher than 20 % in the OECD 302 C for inherent biodegradation or equivalent test methods.
Snov, katere osnovna funkcija je zgoščevanje, se šteje za inherentno aerobno biorazgradljivo, če kaže biorazgradnjo, ki je višja od 20 % pri testih OECD 302 C za inherentno biorazgradnjo ali enakovrednih testnih metodah.
All of the aquatic toxicity requirements shall then apply also to the degradation products, which have been scientifically proven to be derivates of the thickener, after exposure to the aquatic environment.
V tem primeru morajo razkrojni produkti, ki so bili znanstveno dokazani za derivate sredstev za zgoščevanje, prav tako ustrezati, po izpostavljenosti v vodnem okolju, vsem zahtevam v zvezi s strupenostjo za vodno okolje.
A substance is non-biodegradable if it fails the criteria for ultimate and inherent biodegradability.
Snov biološko ni razgradljiva, če ne izpolnjuje meril za končno in inherentno biorazgradljivost.
A substance does not bioaccumulate if its MM > 800 or has a molecular diameter > 1,5 nm (> 15 Å).
Snov ne bioakumulira, če je njen MM > 800 ali ima molekularni premer > 1,5 nm (> 15 Å).
A substance with MM < 800 or molecular diameter < 1,5 nm (< 15 Å) does not bioaccumulate if:
Snov z MM < 800 ali molekularnim premerom < 1,5 nm (< 15 Å) ne bioakumulira, če:
the octanol-water partition coefficient log Kow < 3 or > 7, or
je koeficient porazdelitve oktanol/voda log Kow < 3 ali > 7, ali
the measured BCF is ≤ 100.
je izmerjeni BCF ≤ 100.
Since most substances used in lubricants are quite hydrophobic the BCF-value should be based on the lipid weight content and care must be shown to ensure a sufficient exposure time.
Ker je večina snovi v mazivih precej hidrofobnih, bi morala vrednost BCF temeljiti na vsebnosti teže lipidov in paziti se mora na to, da se zagotovi zadostni čas izpostavljenosti.
Test methods
Testne metode
The tests to be applied for the determination of ready biodegradability are the OECD 301 A-F series, or ISO and ASTM equivalents or the BOD5/(ThOD or COD) ratio.
Testi, ki se uporabljajo za določitev hitre biorazgradljivosti, so OECD 301, serije A-F, ali enakovredni testi ISO in ASTM ali količnik BOD5/(ThOD ali COD).
The BOD5/(ThOD or COD) ratio can only be used if no data based on the OECD 301 or any other equivalent test methods are available.
Količnik BOD5/(ThOD ali COD) se lahko uporablja samo, če ni na razpolago podatkov na podlagi testov OECD 301 ali kakršnih koli drugih enakovrednih testnih metod.
The BOD5 shall be assessed according to C.5 (Commission Directive 92/69/EEC [6]) or equivalent methods while the COD according to C.6 (Directive 92/69/EEC) or equivalent methods.
se oceni v skladu s C.5 (Direktiva Komisije 92/69/EGS [6]) ali enakovrednimi metodami, medtem ko se COD oceni v skladu s C.6 (Direktiva 92/69/EGS) ali enakovrednimi metodami.
For the determination of the inherent biodegradability the OECD 302 C or equivalent test methods are to be applied.The applicant may also use read-across data to estimate the biodegradability of a substance.
Za določitev inherentne biorazgradljivosti se uporabljajo OECD 302 C ali enakovredne testne metode.Za oceno biorazgradljivosti snovi vlagatelj lahko uporabi tudi podatke o referenčni snovi.
‘Read-across’ for the assessment of the biodegradability of a substance shall be acceptable if the reference substance differs by only one functional group or fragment from the substance applied in the product.
Za oceno biorazgradljivosti snovi so podatki o referenčni snovi sprejemljivi, če se referenčna snov razlikuje samo za eno funkcionalno skupino ali fragment od snovi, uporabljene v proizvodu.
If the reference substance is readily or inherently biodegradable and the functional group has a positive effect on the aerobic biodegradation then the applied substance may also be regarded as readily or inherently biodegradable.
Če je referenčna snov hitro ali inherentno biorazgradljiva in ima funkcionalna skupina pozitivni učinek na aerobno biorazgradljivost, potem se tudi uporabljena snov lahko šteje za hitro ali inherentno biorazgradljivo.
Functional groups or fragments with a positive effect on the biodegradation are: aliphatic and aromatic alcohol [-OH], aliphatic and aromatic acid [-C(=O)-OH], aldehyde [-CHO], Ester [-C(=O)-O-C], amide [-C(=O)–N of -C(=S)–N].
Funkcionalne skupine ali fragmenti s pozitivnim učinkom na biorazgradljivost so: alifatski in aromatski alkohol [-OH], alifatske in aromatske kisline [-C(=O)-OH], aldehidi [-CHO], estri [-C(=O)-O-C], amidi [-C(=O)-N od -C(=S)-N].
Adequate and reliable documentation of the study on the reference substance should be provided.
Treba je zagotoviti ustrezno in zanesljivo dokumentacijo študije o referenčni snovi.
In case of a comparison with a fragment, not included here above, adequate and reliable documentation of the studies should be provided on the positive effect of the functional group on the biodegradation of structurally similar substances.
V primeru primerjave s fragmentom, ki ni vključen zgoraj, je treba zagotoviti ustrezno in zanesljivo dokumentacijo študij o pozitivnih učinkih funkcionalne skupine na biorazgradljivost strukturno podobnih snovi.
The log octanol/water partition coefficient (log Kow) shall be assessed according to OECD 107, 117 or the draft 123 or any other equivalent test method.
Koeficient porazdelitve oktanol/voda log (log Kow) se oceni v skladu z OECD 107, 117 ali osnutkom 123 ali katero koli drugo enakovredno metodo.
The bioconcentration factor (BCF) shall be assessed according to OECD 305.
Biokoncentracijski faktor (BCF) se oceni v skladu z OECD 305.
Log Kow values are applicable to organic chemicals only.
Vrednosti log Kow se uporabljajo samo za organske kemikalije.
To assess the bioaccumulation potential of non-organic compounds, some surfactants, and some organo-metallic compounds, BCF measurements shall be carried out.
Za oceno bioakumulacijskega potenciala anorganskih spojin, nekaterih površinsko aktivnih snovi in nekaterih organsko-kovinskih spojin se izvedejo merjenja BCF.
If the test cannot be performed (e.g. the substance has a high surface activity or does not dissolve in water or in octanol), a calculated value for log Kow as well as details of the calculation method shall be provided.
Če se testa ne more izvesti (npr. snov je površinsko zelo aktivna ali se ne topi v vodi ali v oktanolu), je treba zagotoviti izračunano vrednost za log Kow ter tudi podrobnosti o metodi izračuna.