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Diss Factsheets
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EC number: 915-790-0 | 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
Description of key information
The EPM strategy that we applied to sediment follows the rules set out in the integrated testing strategy (ITS) detailed in R.7.8.14, Chapter R.7b of the ECHA Guidance on information requirements and chemical safety assessment (v3.0, Feb. 2016, pp.157 -158). No adequate toxicity datum is available for toxicity of the substance to sediment organisms. Therefore, both freshwater and marine sediment PNECs were derived from their respective aquatic PNECs, using the EPM method. The subsequent calculated RCRs are all inferior to 1 for both compartments and no further testing is therefore required to cover the risk for both sediment compartments. This information is presented in the CSA. It has to be noted that both octanol-water partition (log Kow) and adsorption (log Koc) coefficients are inferior to 3. Consequently, a chemical safety assessment for the sediment compartment was not mandatory, as stated in R.7.8.7, Chapter R.7b of the ECHA Guidance on information requirements and chemical safety assessment (v3.0, Feb. 2016, p.159): “ The main property of a substance that triggers the assessment for the sediment compartment is the potential to adsorb or bind onto sediment. [...] A log Kow of 3 should be used as trigger value for a sediment assessment.”. However, a chemical safety assessment is yet provided. It indicates an acceptable risk (all RCRs < 1) for both sediment compartments (both freshwater and marine).
Key value for chemical safety assessment
Additional information
An unreliable toxicity study for sediment-dwelling organisms relating to the test substance is available and included in the dossier.
Torp (1997) conducted a (Klimisch 3) GLP compliant study following methods based on OSPAR 1995Protocols on Methods for the Testing of Chemicals Used in the Offshore Oil Industry, Part A: A sediment bioassay using a amphipod, Corophium sp. Adult Corophium volutator were exposed to sediment spiked with the test substance at nominal concentrations of 20, 54, 163, 514, 1592, 4996 (mg/kg dry sediment weight) for 10 days. At the end of the test, control mortality was 3%. The 10 day LC50 was 1260 mg/kg dry weight. Although this study is considered not reliable, it is included for comparison. PNECsediment is calculated based on koc and equilibrium partitioning coefficient method.
In accordance with REACH Regulation 1907/2006, Annex X, Column 2, studies of the effects on sediment organisms need not be conducted if exposure assessment indicates no concern for exposure to environmental compartments. The substance is not expected to adsorb to sediment or soil as the log kow is low (2.51). Additionally, reliable model results indicate that the adsorption coefficient is low (Log Koc of <3), indicating low adsorption potential. No significant exposure of the sediment compartment is therefore expected and additional information on the effects of the substance and its degradation products on soil micro-organisms are therefore not required.
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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