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Diss Factsheets
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EC number: 270-414-6 | CAS number: 68439-70-3
- 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
ABIOTIC DEGRADATION
PHOTODEGRATION IN AIR
Direct Photodegradation in Air
Compounds of the DMA category do not absorb light >290 nm (ozone band) and therefore a direct photolysis in air will not occur.
Indirect Photodegradation in Air
OH radical induced indirect photolysis of substances from the DMA category can be estimated with US EPA AOPWIN Program, estimating low degradation half-lives (12 hour day and OH radical concentration of 1500000 radicals/cm3). For C10 DMA and C18 DMA half-lives of 1.42 h and 1.26 h are calculated, respectively.
PHOTODEGRATION IN WATER
Direct Photodegradation in Water
Substances of the DMA category are unlikely to undergo direct photolytical degradation in the hydrosphere because of the lack of a chromophor.
Indirect Photodegradation in Water
OH radical induced indirect photolysis in air can be estimated with US EPA AOPWIN Program estimating low degradation half-lives for the DMA category (C10 DMA 1.42 h, C18 DMA 1.26 h). Therefore DMA category members may also be degraded in water by indirect photolysis if sufficient OH radicals were available. In any case, substances of the DMA category are rapidly biodegraded (see IUCLID Sections 5.2.1 and 5.2.2) and indirect photolysis will play a minor role in degradation
PHOTODEGRATION IN SOIL
Direct Photodegradation in Soil
Substances from the DMA category do not absorb light >290 nm (ozone band) and therefore a direct photolysis on soil surface will not occur.
Indirect Photodegradation in Soil
OH radical induced indirect photolysis of DMA category members in air can be estimated with US EPA AOPWIN Program estimating low degradation half-lives (see chapter 5.1.1). Therefore substances from the DMA category may be degraded on soil surface by indirect photolysis but as the amines are rapidly biodegraded in aerobic soils (see IUCLID Section 5.2.3) indirect photolysis will play a minor role in degradation.
HYDROLYSIS
Substances of the DMA category do not have functional groups which can be hydrolyzed under environmental conditions as stated in OECD Guideline 111. In addition substances of the DMA category are readily biodegradable. The statement given above fulfils the requirement for waiving as given in Regulation (EC) 1907/2006 Annex VIII Column 2, 9.2.2.1 which states: The study need not to be conducted if the substance is readily biodegradable.
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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