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Diss Factsheets
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EC number: 439-270-3 | CAS number: 260408-02-4
- 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
No reliable BCF can be determined from this study, because the test concentrations of the three components that were analysed were above the maximum water solubility limit of (any component of) the test substance. The report does not contain any information of the concentration of the truly dissolved test substance and no substance was detected in fish.
An expert evaluation of the BCF was performed and used as supporting evidence for the determination of the potentional B/vB for the PBT assessment.
Key value for chemical safety assessment
Additional information
A bioconcentration study for SPS-100 was performed in common carp (Cyprinus carpio) based on a method similar to OECD 305 and according to GLP principles. Following a 56 day (8 weeks) uptake period, steady state bioconcentration factor (BCF) was determined. A depuration phase was not performed since the determined BCFs were low.The study was performed at nominal concentrations of 100 and 1000 µg/L that were achieved via dispersion with emulsifier HCO-40. During the exposure phase, samples from the test solutions were analysed by HPLC, with quantification of the concentration of Peak no. 1. From the report it is not clear which component is indicated by peak 1. The water solubility of SPS-100 was determined based on the analysis of three components: the water solubility of these components were concluded to be <4 µg/L, <28 µg/L and <44 µg/L, respectively (point 4.8 in the IUCLID file). In the bioconcentration study, the measured concentrations of peak 1 in the test solutions were 94-96 µg/L and 960-1030 µg/L for the low and high level, respectively. These concentrations were therefore much higher than the water solubility of (any component of) the test substance. The report does not contain any information of the concentration of truly dissolved test substance. In fish, the concentration of peak 1 was always <2 µg/g, irrespective of the nominal concentration. Furthermore relevant details on test conditions (e.g. photoperiod, mortality in control and treated fish) were not reported and the documentation of the analytical method and results is poor. Therefore the study is considered to be irreliable.In a worst-case approach, it may be assumed that the actual concentration of peak 1 in the test solutions was <4 µg/L. In line with the OECD guidance document on difficult test substances, the concentration in the test solution is taken to be half the LOD (of 4 µg/L), i.e. 2 µg/L. This leads to a provisional BCF value of <2 [µg/g] / 2 [µg/L] = <1 L/g or <1000 L/kg.The current-day OECD 305 guideline for a bioconcentration test in fish indicates that for substances with very low solubility in the aquatic environment, exposure via water may be of limited importance in comparison to the dietary route. This is also indicated by ECHA in IR/CSR Guidance Chapter R.11. Thus, for SPS-100, the bioconcentration study is of limited value.
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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