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Diss Factsheets
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EC number: 639-566-4 | CAS number: 165184-98-5
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Some abiotic degradation of aldehydes in aqueous solution is expected but no hydrolysis study was performed as the substance was found to be readily biodgradable and is rather insoluble (1.6 mg/L in pure water). Photodegradation in water and hydrolysis have both been observed in preparatory work performed prior to undertaking an algae study (see 6.1.5) however half-lives in water cannot be accurately quantified from this data for use in risk assessment. It should be noted that a photolysis study is not a required endpoint under REACH.
Two valid ready biodegradability studies are available on the biodegradability of the substance. One achieved >60% biodegradation but failed the 10 day window, using a modified Sturm test under closed conditions to prevent loss due to volatility. In a second study following OECD Guideline 301F, the test substance was almost completely mineralised (97% ) within 28 days meeting the 10 day window criterion.
Due to the log Kow of 5.3, the substance meets the criterion for potential B however, A BCF test for fish requires stable testing conditions with accurate analytical measurement of test substance concentrations in water and fish tissue over a significant period of time (weeks).This substance has a relatively low water solubility (1.6 mg/L in pure water and is expected to be lower in test medium). At this stage there are still significant technical problems associated with determining the water solubility limit in test media. The test substance is known to photodegrade rapidly and to hydrolyse in water. It is known to biodegrade rapidly and is expected to be metabolised rapidly in fish tissues. Moreover, it is expected to adsorb to the test system. All these elements contribute to the technical unfeasibility of this study following OECD BCF guidelines. Currently, other methods which could be used to determine a Bioconcentration factor for fish do not have regulatory acceptance.
A valid study was performed to estimate the adsorption coefficient (Koc) of the substance by HPLC using method C19 and the OECD Guideline 121. The substance was determined to have a log Koc value of 4.2 (equivalent Koc=15800).
Due to its rather low volatility (0.068 Pa at 20°C) and its rather low water solubility, the substance is expected to partition to the sediment compartment, but due to its ready biodegrability its half-life in sediment is expected to be low.
It should be noted that the substance disappeared fairly rapidly in the sediment compartment (almost complete loss within 28 days) during the sediment toxicity study with removal at lower concentrations faster than those at higher ones. No HCA was observed in the pelagic compartment at all during the sediment study which also confirms the highly adsorptive nature expected in sediment and rapid degradability of the substance in both water and sediment.
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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