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Diss Factsheets
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EC number: 200-882-9 | CAS number: 75-59-2
- 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 and sediment: simulation tests
Administrative data
Link to relevant study record(s)
Description of key information
In accordance with Column 2 of Annex IX Sections 9.2.1.2 and 9.2.1.4 of the REACH regulation, a water and sediment simulation study does not need to be conducted as the substance is readily biodegradable. However, two studies are available in which the behaviour of the structurally related substance TMAC (see read-across justification in IUCLID section 13) was simulated. From the key study by Ripley and Hossain (1997), it can be concluded that an acclimated bench-scale activated sludge system that treats waste water containing TMACl at a concentration upto 100 mg/L can remove >98% of TMACl.
Key value for chemical safety assessment
Additional information
Biodegradability study results of TMAC are also valid for TMAOH because both substances dissociate in water to tetramethylammonium and hydroxide or chloride ions and it is the tetramethylammonium cation that biodegrades. Further justification is given in the attached Read Across document.
The biodegradation of TMACl and its effect on the operation of a municipal wastewater treatment plant were examined by Ripley and Hossain (1997) in a bench-scale activated sludge system. Based on the results, it can be concluded that an acclimated bench-scale activated sludge system that treats waste water containing TMACl at a concentration up to 100 mg/L can remove >98% of TMACl. Acclimation of the biomass to TMACl was critical. While some of the TMACl removal may have been due to physical adsorption, the primary mechanism was biological oxidation. This was demonstrated by increased oxygen uptake rates, increased production of nitrate+nitrite and decreased mixed liquor pH resulting from nitrification.
The degradation of components in TFT-LCD wastewater, which also contains a high concentration of TMAOH (which is structurally related to TMAC) was studied by Lei et al. (2008) in experiments with an anoxic/oxic sequence batch reactor with adapted sludge. It was concluded that an Anoxic/Oxic Sequencing Batch Reactor with adapted sludge can remove 99% of TMAOH at an influent concentration up to 190 mg/L.
Biodegradability study results of TMAC are also valid for TMAOH because both substances dissociate in water to tetramethylammonium and chloride or hydroxide ions and it is the tetramethylammonium cation that biodegrades. Further read-across justification is attached to IUCLID section 13.
The simulation study of Ripley and Hossain (1997) can be regarded as representative for a municipal waste water treatment plant treating a waste water stream with TMACl. The result (98% removal) can be used in the risk assessment of TMAOH, for a waste water treatment plant that receives waste water containing the substance on a regular basis, as acclimation of the biomass was needed in the study.
The study of Lei et al. are related to a very specific waste water stream (TFT-LCD waste water) and a specific reactor and can therefore only be regarded as indicative.
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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