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EC number: 200-927-2 | CAS number: 76-03-9
- 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
Key value for chemical safety assessment
Additional information
Trichloroacetic acid has been tested for in vitro genotoxicity in a series of Ames tests, DNA damage and/or repair assays and point mutation assay in Aspergillus nidulans. In all these studies, trichloroacetic acid gave negative results, except in one, in which dimethyl sulfoxide (DMSO) was used as a solubiliser. The evidence supports the hypothesis that a reaction between trichloroacetic acid and DMSO produces a short-lived intermediate product(s) that could be responsible of the time-limited mutagenicity found to be induced by this solution.
Two in vitro cytogenetic assays in human lymphocytes were conducted with trichloroacetic acid. In the first, trichloroacetic acid, as free acid, was added to whole blood cultures in the presence and absence of an auxiliary metabolic activation system (rat liver S9-mix). In the second assay, neutralised trichloroacetic acid was tested also in the presence and absence of S9-mix. Dose-related statistically significant increases in the incidence of chromosomal aberrations, associated with significant reductions in the pH of the cultures treated with trichloroacetic acid were observed. Treatment with neutralised trichloroacetic acid did not result in the induction of chromosomal aberrations. The authors concluded from the results of these two in vitro cytogenetic assays that trichloroacetic acid shows no intrinsic potential to induce cytogenetic damage in the human lymphocyte chromosomal aberration assay when tested up to cytotoxic concentrations.
An in vitro gene mutation assay (method similar to OECD guideline 476) was performed. Trichloroacetic acid was mutagenic only in the presence of S9 activation in L5178Y/TK+/- -3.7.2c mouse lymphoma cells. The authors noted that trichloroacetic acid was the least potent mutagens that they had evaluated.
In-vivo tests were conducted on chromosomal aberrations, DNA strand breaks, oxidative DNA damage and DNA synthesis. An in vivo well conducted bone marrow micronucleus study in mice reported negative results (Mackay et al. 1995). In contrast, statistically significant (but non-dose related) increases in the frequency of cells containing micronuclei were observed in the Bhunya and Behera study (1987). Mackay et al. proposed that the positive results previously observed with trichloroacetic acid may have been due to a non-genotoxic mechanism, possible caused by physicochemically induced stress, resulting from intraperitoneal pH changes.
Short description of key information:
Genetic toxicity in vitro:
Weight of evidence: Results on bacterial reverse mutation assay from several independent sources leading to the conclusion that trichloroacetic acid did not cause point mutations in the microbial systems.
Key study: in vitro gene mutation assay (method similar to OECD guideline 476). Trichloroacetic acid was mutagenic only in the presence of S9 activation in L5178Y/TK+/- -3.7.2c mouse lymphoma cells. The authors noted that trichloroacetic acid was the least potent mutagens that they had evaluated.
Key study: in vitro chromosomal aberration assay in human lymphocytes (method similar to OECD guideline 473). The substance caused an increase in chromosomal aberrations in the presence and absence of metabolic activation but these aberrations were associated with a trichloroacetic acid-induced decrease in pH. When incubations were conducted with neutralised trichloroacetic acid at the same concentrations, significant increases in the incidence of aberrant cells were not observed.
Genetic toxicity in vivo: Key study: Bone marrow micronucleus study in mice. No statistically or biologically significant increases in the incidence of micronucleated polychromatic erythrocytes compared with the solvent control dosed animals were observed in either sex at the 6 h sampling time or in the females at the 24 hr sampling time. A small but statistically significant increase in micronucleated polychromatic erythrocytes was observed in male mice 24 hr after a dose of 675 mg/kg (50% MLD). Since no increases were noted at the 25 or 80% MLD, and the levels recorded are within the range of the concurrent solvent control values, the small increase observed in the males at the 50% MLD is considered not to be biologically significant. No other increases in the micronuclei were observed.
Endpoint Conclusion: No adverse effect observed (negative)
Justification for classification or non-classification
Based on the discussion presented above, it is considered that the available evidence does not suggest that trichloroacetic acid is a mutagen.
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