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Diss Factsheets
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EC number: 200-880-8 | CAS number: 75-57-0
- 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
Two reliable ready biodegradability tests are available for TMAOH, which is structurally related to TMAC. In both tests, TMAOH was ready biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Two reliable ready biodegradability tests are available for TMAOH, which is structurally related to TMAC.
A ready biodegradability test was carried out with 25% TMAOH according to to OECD301 B and GLP (Noack, 2001).
The concentration of the test substance at the beginning of the test was 90 mg/L (corresponding with 22.5 mg TMAOH/L).
Based on the results, it can be concluded that TMAOH is readily biodegradable.
A ready biodegradability test was carried out with 27.5% TMAOH according to to OECD301 B and GLP (CERI, 2002).
The concentration of the test substance at the beginning of the test was 100 mg/L (corresponding with 27.5 mg TMAOH/L).
Based on the data in the SIDS, the test substance shows more than 90% degradation within 14 days, measured according to different methods. The substance TMAOH is therefore considered to be ready biodegradable
Based on the results for TMAOH, it can be concluded that TMAC is ready biodegradable.
Under anaerobic conditions a rapid biodegradation is possible as well:
TMAOH biodegradation was studied in a batch test with sludge from an Upflow Anaerobic Sludge Blanket (UASB) treating TFT-LCD waste water at concentrations varying from 500 - 2000 mg/L. The TMAOH concentrations were determined by ion chromatography at regular intervals. For all concentrations 100% biodegradation was observed within 10 hours. The total volume of accumulated methane gas production was proportional to the amount of TMAOH added, indicating that the anaerobic sludge was able to completely convert TMAH to methane gas and ammonium. Based on these results, it can be concluded that TMAOH is rapidly biodegradable by adapted sludge under anaerobic methanogenic conditions.
Although both ready biodegradability studies were carried out in accordance with OECD guidelines and GLP and have similar results, the study from Noack (2001) was selected as a key study because the original study report was available and thus more details could be evaluated, whereas the study from CERI (2002) had to be summarised and evaluated based on the IUCLID summary from the OECD SIDS of TMAOH (CERI, 2006). Furthermore, in the study from Noack (2001) a toxicity control was included, whereas in the study from CERI (2002), this was not the case.
Biodegradability study results of TMAOH are also valid for TMAC 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.
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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