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Diss Factsheets
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EC number: 223-276-6 | CAS number: 3806-34-6
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
Description of key information
Based on QSAR modelling, the BCF value for the test substance is estimated to be 3.162 L/kg ww.
In accordance with Column 2 (specific rules for adaptation from Column 1) of Annex IX of Regulation (EC) No. 1907/2006, the bioaccumulation in aquatic species study, required under information point 9.3.2, can be omitted if direct and indirect exposure of the aquatic compartment is unlikely. Exposure to the aquatic environment is predicted to be unlikely, therefore testing is not required.
Key value for chemical safety assessment
- BCF (aquatic species):
- 3.162 L/kg ww
Additional information
The test substance was assessed for bioaccumulation potential using recognised QSAR derivation software as follows:
US EPA On-Line EPI Suite™v4.11 model BCFBAF
US EPA T.E.S.T. (version 4.1) (Toxicity Estimation Software Tool)
BCF model (CAESAR) (version 2.1.11)
BCF model (Meylan) (version 1.0.0)
BCF Read-Across (version 1.0.0)
The QSAR modelling was conducted using the SMILES codes for the three most abundant structures present in the substance (> 10% w/w).
It is understood that Annex XI, section 1.3 allows adaptation of the standard testing requirements by making use of (Q)SAR only if the following conditions are met:
(i) results are derived from a (Q)SAR model whose scientific validity has been established,
(ii) the substance falls within the applicability domain of the (Q)SAR model,
(iii) results are adequate for the purpose of classification and labelling and/or risk assessment, and
(iv) adequate and reliable documentation of the applied method is provided.
Within the five models used, the conditions (i) through (iv) are considered to be met for one of the models:
• US EPA On-Line EPI Suite™v4.0 model BCFBAF
The structures assessed with this model were deemed to mainly fall within the applicability domain of the model, and this is demonstrated within the relevant QPRF. This study is assigned as a Klimisch 2 level study because it is a QSAR assessment.
Within the five models used, the conditions (i), (iii) and (iv) are considered to be met for four of the models:
• BCF model (CAESAR) (version 2.1.11)
• BCF model (Meylan) (version 1.0.0)
• BCF Read-Across (version 1.0.0)
• US EPA T.E.S.T. (version 4.1) (Toxicity Estimation Software Tool)
Within these models, condition (ii) was not fulfilled for various reasons including the following:
- no similar compounds with known experimental value in the training set have been found
- only moderately similar compounds with known experimental value in the training set have been found
- accuracy of prediction for similar molecules found in the training set is not optimal
- similar molecules found in the training set have experimental values that strongly disagree with the target compound predicted value
- the maximum error in prediction of similar molecules found in the training set has a high value, considering the experimental variability
- some atom centered fragments of the compound have not been found in the compounds of the training set or are rare fragments
- descriptors for this compound have values outside the descriptor range of the compounds of the training set
These studies were therefore assigned as Klimisch 3 level studies and the values obtained using these studies were not used to determine the estimated BCF value.
Overall
On the basis of a weight of evidence approach, there is sufficient information available to state that the substance is not bioaccumulative. Whilst it is not possible to provide a definitive BCF value for the substance due to the variation in the results, none of the values determined via QSAR are above the threshold value quoted in the REACH Regulation of 2000 or 5000 which indicates the potential to bioaccumulate.
The substance is predicted to have a high Kow value (16.4) and a value in excess of 4.5 is considered to be of concern as potential for bioaccumulation, according to screening criteria for bioaccummulation in ECHA guidance (Chapter R.11 PBT Assessment). The likely reliability of the log Kow is, however, considered to diminish above a value of 6, as noted in Appendix R.11-1 Annex 1 of ECHA guidance on PBT Assessment. Substances with log Kow between 4.5 and 6 are considered likely to be highly accumulating; however no substantial bioconcentration is assumed for compounds having log Kow values greater than 6. For compounds having log Kow greater than 6, a gradual decrease of the BCF is observed and it has been hypothesised within the published literature that a high log Kow is more an effect of solubility than a tendency of the substance to be lipophilic.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.