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EC number: 231-177-4 | CAS number: 7440-69-9
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
No reliable data are available for the long-term toxicity of bismuth to aquatic invertebrates and the requirement for new test results is waived.
Section 2 of Annex XI of Regulation (EC) 1907/2006 states that testing for a specific endpoint may be omitted if it is technically not possible to conduct the study as a consequence of the properties of the substance. The physico-chemical characteristics of a chemical may limit the possibility for performing certain (eco)toxicity assays such as low solubility. A stock solution at a loading rate of 100 mg bismuth/L was prepared by dissolving 2.74 g of bismuth subnitrate in 20 L of the medium used for the acute invertebrate test, according to the guidance on transformation dissolution of metals and metal compounds (OECD, 2001). After agitation for seven days by using a horizontal laboratory shaker (100 rpm) at ambient temperature in the dark to keep the test item in permanent suspension, the Bi concentration in the water accommodated fraction (filtered through 0.6 µm glass fibre filter) was below detection limit (0.0375 mg Bi/L, Egeler et al., 2010). Therefore it can be concluded that it may neither be possible nor relevant to try and conduct certain ecotoxicological tests, as it is difficult to maintain a high enough and constant concentration of bismuth in the water.
Column 2 of Annex IX of Regulation (EC) 1907/2006 also states that "Long-term (aquatic) toxicity studies shall be proposed by the registrant if the CSA according to Annex I indicates the need to investigate further the effect to aquatic organisms". Because all acute tests show the absence of toxic effects and therefore the absence of a classification for the environment for bismuth, there is no need for further investigation of effects to aquatic organisms.
Conclusively, it is proposed to waive further chronic testing with aquatic invertebrates based on the following arguments:
- Significantly higher solubility of bismuth between acute and chronic test set-ups is not expected to occur.
- All of the acute toxicity tests with invertebrate, fish and algae resulted in the absence of any ecotoxicological signal at the largest dose tested (NOEC and L(E)C50 ≥ 100 mg/L).
OECD (2001). Guidance Document on Transformation/Dissolution of Metals and Metal Compounds in Aqueous Media. OECD Series on Testing and Assessment Number 29. ENV/JM/MONO(2001)9. Organisation for Economic Co-Operation and Development, Paris.
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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