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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
Toxicity to reproduction
Administrative data
- Endpoint:
- toxicity to reproduction
- Remarks:
- other: Spermhead morphology assay (reproductive function)
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: Test method was not according to any guideline. It provides information on the observed effects on the spermhead morphology. No data on GLP.
Data source
Reference
- Reference Type:
- publication
- Title:
- Genotoxicity Studies of Sodium Dichloroacetate and Sodium Trichloroacetate.
- Author:
- Meier JR, Stewart BE, Blazak WF
- Year:
- 1 997
- Bibliographic source:
- Environmental Sciences, 5, 2, 095-108.
Materials and methods
- Principles of method if other than guideline:
- A spermhead morphology assay was performed in mice with sodium trichloroacetate. B6C3F1 mice (24/group) were given 0, 625, 1250, or 2500 mg/kg bw/day of test substance for five consecutive days by oral gavage. Twelve mice per treatment group were sacrificed at 21 and 35 days after the first treatment. These sacrifice times correspond to treatment of cells at the late spermatogonial and primary spermatocyte periods, respectively, assuming no treatment-related delays in sperm development. Body weights were recorded for each animal during the dosing phase and at sacrifice, and testes and cauda epididymidal weights were recorded at sacrifice. Ten animals from each treatment/sacrifice group were randomly selected to be evaluated for sperm count and morphology. The types and frequencies of spermhead abnormalities were based on the scoring of 500 sperm per animal.
- GLP compliance:
- not specified
- Limit test:
- yes
Test material
- Reference substance name:
- TCA
- EC Number:
- 211-479-2
- EC Name:
- TCA
- Cas Number:
- 650-51-1
- Molecular formula:
- C2HCl3O2.Na
- IUPAC Name:
- sodium trichloroacetate
- Details on test material:
- - Name of test material (as cited in study report): TCA
- Analytical purity: > 99 %
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Simonsen Laboratories, lnc., Gilroy, CA, USA.
- Age at study initiation: Eleven-week-old
- Weight at study initiation: 20-30 g
- Housing: The animals were housed six per cage with wood shavings used for bedding, and beddings were changed weekly.
- Diet (e.g. ad libitum): Certified Purina Lab Chow, #5002C, ad libitum.
- Water (e.g. ad libitum): Recirculated, deionized, UV -treated water was available to the animals throughout the study.
- Acclimation period: min. 5 days
ENVIRONMENTAL CONDITIONS
- Photoperiod: 12 hrs dark / 12 hrs light.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- A forty percent (w/v) solution of the acid as its sodium salt was prepared by dissolving sodium trichloroacetate in distilled water and titrating the pH to 7.0 with NaOH.
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 5 days
- Frequency of treatment:
- Daily
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
625 mg/kg bw/day
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
1250 mg/kg bw/day
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
2500 mg/kg bw/day
Basis:
nominal conc.
- No. of animals per sex per dose:
- 24 male mice per group were used.
- Control animals:
- yes, concurrent vehicle
Examinations
- Parental animals: Observations and examinations:
- Twelve mice per treatment group were sacrificed at 21 and 35 days after the first treatment. These sacrifice times correspond to treatment of cells at the late spermatogonial and primary spermatocyte periods, respectively, assuming no treatment-related delays in sperm development.
Body weights were recorded for each animal during the dosing phase and at sacrifice, and testes and cauda epididymidal weights were recorded at sacrifice. - Sperm parameters (parental animals):
- Ten animals from each treatment/sacrifice group were randomly selected to be evaluated for sperm count and morphology.
The types and frequencies of spermhead abnormalities were based on the scoring of 500 sperm per animal. - Statistics:
- Initial and sacrifice body weights, testes and cauda epididymal weights, testes to final body weight ratios, and sperm concentration/mg of cauda epididymis were analyzed by one-way analysis of variance (ANOVA) at a significance level of p < 0.05. When significant differences were found, Dunnett's test was applied to compare the different treatment group means with the negative control means. The numbers of morphologically abnormal sperm were analyzed by the Kruskall-Wallis and Mann-Whitney U tests, with differences considered significant at the p < 0.05 level. These latter tests are nonparametric alternatives to ANOVA and Dunnett's test, respectively.
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- not specified
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Histopathological findings: non-neoplastic:
- not specified
- Other effects:
- not specified
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- no effects observed
- Reproductive performance:
- not examined
Details on results (P0)
Effect levels (P0)
- Dose descriptor:
- NOEL
- Effect level:
- >= 2 500 mg/kg bw/day
- Sex:
- male
- Basis for effect level:
- other: overall effects
- Remarks on result:
- other: Generation not specified (migrated information)
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
The NOEL value at 21 and at 35 days wqas equal or greater than 2500 mg/kg bw/day.
Applicant's summary and conclusion
- Conclusions:
- The NOEC value at 21 and at 35 days was equal or greater than 2500 mg/kg bw/day.
- Executive summary:
A spermhead morphology assay was performed in mice with sodium trichloroacetate. B6C3F1 mice (24/group) were given 0, 625, 1250, or 2500 mg/kg bw/day of test substance for five consecutive days by oral gavage. Twelve mice per treatment group were sacrificed at 21 and 35 days after the first treatment. These sacrifice times correspond to treatment of cells at the late spermatogonial and primary spermatocyte periods, respectively, assuming no treatment-related delays in sperm development. Body weights were recorded for each animal during the dosing phase and at sacrifice, and testes and cauda epididymidal weights were recorded at sacrifice. Ten animals from each treatment/sacrifice group were randomly selected to be evaluated for sperm count and morphology. The types and frequencies of spermhead abnormalities were based on the scoring of 500 sperm per animal. Initial and sacrifice body weights, testes and cauda epididymal weights, testes to final body weight ratios, and sperm concentration/mg of cauda epididymis were analyzed by one-way analysis of variance (ANOVA) at a significance level of p < 0.05. When significant differences were found, Dunnett's test was applied to compare the different treatment group means with the negative control means. The numbers of morphologically abnormal sperm were analyzed by the Kruskall-Wallis and Mann-Whitney U tests, with differences considered significant at the p < 0.05 level. These latter tests are nonparametric alternatives to ANOVA and Dunnett's test, respectively.
The testes-to-final-body weight ratio, the number of sperm per milligram of cauda epididymis, and the percentage of abnormal spermheads were unaffected in the treated animals either at 21 or 35 days following oral gavage administration.
The NOEL value at 21 and at 35 days was equal or greater than 2500 mg/kg bw/day.
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