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Diss Factsheets
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EC number: 219-588-7 | CAS number: 2469-55-8
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
Toxicity to algae: 72 hour NOEC 100 mg/l (nominal; highest concentration tested) (OECD TG 201), in terms of the substance as tested, when the pH is maintained near neutral (pH ca. 8.1 throughout exposure period).
In the same study, 72 hour ErC50 56.3 mg/l and ErC10 35.5 mg/l (nominal) (OECD TG 201), in terms of the substance as tested, were determined under parallel exposures without adjustment of pH (maximum pH of 9.92).
The observations in this study are attributed to the exposure of test organisms to the parent substance in the test system.
Key value for chemical safety assessment
- EC10 or NOEC for freshwater algae:
- 100 mg/L
Additional information
A 72 hour ErC50 value of >100 mg/l and NOEC of ≥100 mg/l (nominal) have been determined for the effects of the registration substance on growth rate of Pseudokirchneriella subcapitata, at pH-neutral conditions. In view of the test media preparation method and exposure regime it is likely that the test organisms were exposed predominantly to the tested substance at least at the start of the test, although hydrolysis may have occurred to some extent during the exposure period.
In parallel testing under conditions in which the pH was not adjusted to neutral, a 72 hour ErC50 value of 56.3 mg/l and ErC10 of 35.5 mg/l (nominal) were determined. The findings are consistent with other amine-containing substances in that toxicity is often significantly higher under near-neutral pH conditions similar to the wider environment, than when the pH is allowed to vary (algal respiration can cause significant elevation of pH under laboratory test conditions). It is inferred by the reviewer that the non-protonated form of the amine is considerably more toxic than the protonated form (as is the case with other amines, ammonium salts, and ammonia). At elevated pHs, the proportion of the non-protonated form is much higher.
The study was supported by TOC analysis of the parent substance and concentrations ranged between 91.5 and 102% of nominal (highest two test concentrations) and <LOQ - 183% of nominal (lowest three test concentrations) with consistent TOC measurements at the start and end of the test suggesting no losses occurred by physicochemical processes, although this non-specific method cannot identify degradation by hydrolysis.
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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