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EC number: 208-849-0 | CAS number: 543-80-6
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
Under aerobic conditions, acetate is readily broken down to carbon dioxide and water. It is thus used as a reference compound in OECD guideline 301 (1992) on "Ready Biodegradability" in the form of sodium acetate to check the protocol. Acetate reliably meets the criterium of ready biodegradability (i.e. 70% removal of DOC and 60% of ThOD or ThCO2 production for respirometric methods within a 10-d window within the 28-d period of the test) even when an inoculum is not deliberately added.
The key study of Zahn and Wellens (1980), conducted according to Zahn and Wellens (1974; later on adopted as “Zahn-Wellens-Test” in OECD guideline 302 B “inherent biodegradability”), investigated the biodegradation of acetic acid using 1 g dry weight COD/L of a non-adapted, activated sludge from an organic plant of the company Hoechst, Frankfurt, Germany. After 3 days (including an adaption time of 1 day), acetic acid was degraded by > 90 % with a post-adaption degradation time of 40 % COD/day. The test was valid and sensitive (> 70 % (i.e. 100 %) degradation of diethylene glycol in 14 days, gradual COD and DOC removal, biocidal effects refuted by short adaption time) and confirms that acetic acid is ready biodegradable.
The supporting study of Billen et al. 1980, determined turn-over rates (utilization rates) of acetate by natural microbial populations in estuarine, coastal and seawater after addition of 14C-acetate as a substrate and an adjacent sample incubation at in situ temperature for 4 hours. The results were used to extrapolate mean DT50 values of 0.3, 9.8 and 46 days for estuarine, coastal and seawater, respectively. The results suggest that acetate is ready biodegradable in estuarine and coastal water and that biodegradation is slower in open marine water. However, considering that the data were extrapolated from a 4-h laboratory experiment, the conclusions should not be over-interpreted.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
The key study of Zahn and Wellens (1980) used a method representing a preceding version of the “Zahn-Wellens-Test” in OECD Guideline 302 B “inherent biodegradability”. Therefore, despite its scarce information, the present paper is considered “reliable 2”. According to the most recent version of OECD 302 B (1992) the publication lacks of the following information: temperature, pH, dissolved oxygen concentration, light regime, preparation of inoculum, controls and blank controls, medium, analytical method as well as source and purity of the test compound. Nevertheless, validity and sensitivity were assessable.
The supporting study of Billen et al. 1980 did not follow a specific guideline and used 14C-labbeled acetic acid of an unknown source and purity. It therefore was ranked “reliable 3”.
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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