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Diss Factsheets
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EC number: 938-875-4 | CAS number: -
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Alchisor TAL 111 is an alkenes C10 -C11, hydroformylation product, low boiling and can be characterised as a UVCB substance. As defined in the ‘Read-Across Justification Document’ section 13, data provided for the analogue substance Alchisor TAL 123 and the Alchisor TAL 111 consitutent category substances, Category 3 hydrocarbon solvents, are representative of Alchisor TAL 111 and suitable for assessment purposes. Study data for each analogue/constituent category has been evaluated and considered together. The most relevant and reliable study result from across the analogue/constituent categories has been identified and used to address the endpoint in question. The data requirement for bioconcentration is being waived as follows:
Category substances: C9-C14 aliphatics (2-25% aromatics)
Standard tests for the bioaccumulation endpoint are intended for single substances. In the case of C9-C14 aliphatics (2-25% aromatics) the substance is a UVCB hydrocarbon and bioaccumulation testing is not appropriate for this complex substance. However, this endpoint has been calculated for representative hydrocarbon structures using the BCFWIN v2.16 model within EPISuite 3.12 or EUSES as input to the hydrocarbon block method incorporated into the PETRORISK model. The PETRORISK derivations are provided in Section 13 of the CSR. In addition, supporting information reported in CONCAWE’s approach (Lampi et al., 2010), which is also included in Section 13 of the CSR, provides evidence of over-estimation when BCF’s are predicted through modelling approaches. PETRORISK model predictions for hydrocarbons ranged from 45.5 to 21,710.
Supporting information found in the CONCAWE report presents model predictions based on bioconcentration potential in fish and reliable experimental data for algae and Daphnia species. Two types of model prediction are presented; the first is a regression output from the BCFBAF model of EPISuite (US EPA, 2009) in which fish biotransformation of hydrocarbons is not explicitly taken into account. The second prediction uses the BCF model developed by Arnot and Gobas (2003) which includes lipid content predictions as recommended in ECHA Guidance (Chapter R.7C, ECHA, 2008). The report states that there is marked influence of fish biotransformation exerted on the predicted BCFs derived using the two types of modelled results for all hydrocarbon blocks (including, paraffins, iso-parafins (or branched paraffins) and mono-aromatics). The BAF predictions were judged to be inappropriate for hydrocarbons since metabolism in the gut (which is effectively assumed in food chain model calculations) is ignored. The decision to exclude BAF model predictions was supported by the experimental dietary BMF data demonstrating the critical role of gut metabolism in limiting biomagnification of hydrocarbons via the diet. For example, for mono-aromatics C12 to C17, all regression model predictions are above the B (bioaccumulation (B) criterion in PBT assessment) criterion of 2000. When biotransformation is incorporated into the model, none of the predictions are above 2000. Experimentally-derived dietary BCF values which are typically more conservative than aqueous BCF values are below the B criterion for all tested structures (C9 to C16). Aqueous BCFs for all other mono-aromatic hydrocarbons are below 2000. It is concluded by CONCAWE that based on available data, mono-aromatic hydrocarbons are neither bioaccumulative nor very bioaccumulative. Similar assessments for paraffins and branched (or iso-) paraffins concluded that C13 and C14 paraffins and C12-C16 branched paraffins may be bioaccumulative but not very bioaccumulative.
Conclusion
As a consequence of bioaccumulation studies being waived as unsuitable, as for C9-C14 aliphatics (2-25% aromatics), no reliable measured bioconcentration information is required for constituent categories of Alchisor TAL 111. The data requirement for bioconcentration/bioaccumulation is being waived for Alchisor TAL 111 on the basis that the studies are waived for its constituent categories. Alchisor TAL 111 does not meet the bioaccumulative (B) or very bioaccumulative (vB) criteria in PBT assessment.
References:
Lampi et al. 2010. An Evaluation of the Persistence, Bioaccumulation and Toxicity of PetroleumHydrocarbonsPrepared for CONCAWE March 2010.
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.
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