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The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 203-620-1 | CAS number: 108-83-8
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
The 2,6-dimethylheptan-4-one substance has a low vapor pressure (227 Pa at 20 °C), and only moderate solubility in water. Therefore, emission of the substance to water or soil have high potential to volatilize to the atmosphere. In the atmosphere, the fate of this, and most organic substances, is dominated by reaction with photochemically-generated hydroxyl radical. The half-life for this indirect photolysis is extimated to be 22 hrs. Because the substance can absorb UV light at wavelenghts > 290 nm, the potential for direct photolysis also exists, but is expected to be of much lesser importance. The atmospheric half-life is close to the 24 hr. half-life criterion for identification of persistent atmospheric pollutants. Therefore, the substance may have potential for relatively long-range transport in the atmosphere.
This substance can be emitted directly to surface waters as a result of its manufacture and use, and indirectly emitted to water and soil by deposition of atmospheric emissions of the volatile substance. The substance has an octanol-water partition coefficient (log Kow) of 3.71, indicating some potential for bioaccumulation in aquatic organisms. However, actual bioaccumulation is expected to be low, due to the potential for rapid metabolism/excretion in these organisms. The organic carbon-normalized adsorption coefficient (log Koc) of 2.07 indicates that migration of the substance through soil will be only slightly retarded, and contamination of groundwater via emissions to surface soil is possible. However, as is the case for most aliphatic ketone substances, this substance is readily biodegradable, and is therefore not expected to persist in surface water, soil, or sediments; and is expected to be effectively removed during activated sludge sewage treatment. The substance does not posses structural/functional groups which are susceptible to hydrolysis, and while direct photolysis is possible based on ability to absorb UV light at > 290 nm, this also is not expected to be an important fate process. Biodegradation is expected to be the dominant process affecting the fate and lifetime of this substance in the environment; and will prevent the substance and its components from becoming persistent pollutants.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.