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Diss Factsheets
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EC number: 237-600-9 | CAS number: 13863-31-5
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
LC50 (96 h) Zebra fish > 100 mg/l
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 100 mg/L
Additional information
The short-term toxicity to fish was tested on 3b-A in one reliable study (Bionomics Inc., 1971) with EC50 greater than 85 mg/l, but no analytical concentrations measures were performed. Based on the described physicochemical properties it can be expected that the substance is stable in the testing environment, therefore it is assumed that the nominal concentration will correspond to the measured. Furthermore, two summaries are available: both describe a test performed at 48 h on trout. In one case the LC50 was stated at 140 mg/l (Ciba-Geigy Ltd. 1978 and Ciba-Geigy Ltd., 1979), while in the second one the LC50 was stated at 45 mg/l (Ciba-Geigy Ltd. 1975 and Ciba-Geigy Ltd., 1989). Test procedures are scientifically acceptable, nevertheless many detail are missing; furthermore there are no evidence that the concentration of the substance being tested has been satisfactorily maintained throughout the test.
In general the studies performed on the substance under registration present some deficiencies, therefore studies performed on similar substances (3a-A(NaK) and 3a-A(Na) have been taken as main reference. Justification for Read Across is given in Section 13 of IUCLID.
In the case of 3a-A(NaK) the presence of potassium ion has no relevant toxicological influence for the endpoint. For all the analogous water solubility is higher from 3b-A, therefore they are more bioavailable in the water compartment and can be considered as conservative examples.
The chemical structures are very similar, with Tanimoto similarity higher than 95 %: the 3b-A has a methyl group where the analogues has a hydroxyethyl substituent on the nitrogen atom. Based on the OECD Toolbox modelling of the liver metabolisation, both structures share the same monohyroxy derivative as main metabolite. Biological reactivity for the substance under registration is therefore not expected higher that the considered analogues substances.
All analogues tested showed a LC50 > 100 mg/l on fish at 96h.
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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