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EC number: 200-756-3 | CAS number: 71-55-6
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Conducted for the NTP, using a rigorous protocol. Not GLP, no individual data presented.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 000
Materials and methods
- Principles of method if other than guideline:
- The assessment was made on the pheripheral blood of mice used in a 13 week toxicity study (NTP 2000), blood smears assessed for micronuclei
- GLP compliance:
- no
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 1,1,1-trichloroethane
- EC Number:
- 200-756-3
- EC Name:
- 1,1,1-trichloroethane
- Cas Number:
- 71-55-6
- Molecular formula:
- C2H3Cl3
- IUPAC Name:
- 1,1,1-trichloroethane
- Details on test material:
- Refer to NTP2000/K2KS/repeat toxicity, mouse
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- Balb/c
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Refer to NTP2000/K2KS/repeat toxicity, mouse
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- Placebo capsules
- Duration of treatment / exposure:
- Continuous exposure for 13 weeks.
- Frequency of treatment:
- Continuous, diet
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
5000 ppm
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
10000 ppm
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
20000 ppm
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
40000 ppm
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
80000 ppm
Basis:
nominal in diet
- No. of animals per sex per dose:
- 5 males + 5 females
- Control animals:
- yes, concurrent vehicle
- yes, plain diet
Examinations
- Tissues and cell types examined:
- Pheripheral blood
- Details of tissue and slide preparation:
- After 13 weeks of dietary treatment with 1,1,1-trichloroethane (NTP 2000) peripheral blood samples were obtained from male and female Balb C mice. Smears were prepared, fixed in methanol and then stained with acridine orange. Slides were scanned to determine the frequency of micronuclei in 2,000 normochromatic erythrocytes (NCEs) in each of 5 animals per exposure group.
- Evaluation criteria:
- An individual trial was considered positive if the trend test P value was less than or equal to 0.024 or if the P value for any single exposed group is less than or equal to 0.025 divided by the number of exposed groups. A final call of positive for micronucleus induction is preferable based on reproducibility positive trials. Ultimately, the final decision is determined by the scientific staff after considering the results of statistical analysis, the reproducibility of any effects observed and the magnitudes of those effects.
- Statistics:
- The frequency of micronucleated cells among NCEs was analysed by a statistical software package that tested for increasing trend over exposure groups with a one-tailed Cochran Armitage trend test, followed by pairwise comparisons between each exposure group and the control group. In the presence of excess binomial variation, as detected by a binomial dispersion test, the binomial variance of the Cochran-Armitage test was adjusted upward in proportion to the excess variation.
Results and discussion
- Additional information on results:
- No individaul data presented.
The results in male mice were considered equivocal because there was a statistically significant (P=0.013) trend across the dose groups, however, none of the individual values were significantly increased compared to the control. In females the frequency of normochromatic erythrocytes ate 2,000 ppm was elevated compared to the controls, but because the increase was small and there was no dose response, the results in females mice were negative.
Although no direct measurement of exposure was made administration of the test material was considered to be associated with a decrease in body weight gain and in the 13 week toxicity study (NTP 2000) the NOAEL was identified as 10,000 ppm in both sexes. This observation and the apparent equivocal effect on the bone marrow of 1,1,1-trichloroethane is considered to support systemic exposure of the mice during this test.
No positive control was used in this test and no discussion regarding the change in the context of background data was made.
Any other information on results incl. tables
Table #:Results of in vivo micronucleus test
Dose ppm |
No. of mice |
Micronucleated NCEs/1000 NCEs |
P value (vs control) |
||
mean |
SD |
||||
males |
Untreated control |
5 |
0.80 |
0.34 |
|
|
Vehicle control |
5 |
0.90 |
0.19 |
|
|
5000 |
5 |
1.10 |
0.19 |
0.2519 |
|
20000 |
5 |
1.50 |
0.22 |
0.0520 |
|
40000 |
5 |
1.50 |
0.32 |
0.0520 |
|
80000 |
5 |
0.80 |
0.2 |
0.01515 |
P Value (trend) |
|
0.013 |
|
|
|
females |
Untreated control |
5 |
0.60 |
0.19 |
|
|
Vehicle control |
5 |
0.80 |
0.34 |
|
|
5000 |
5 |
0.80 |
0.12 |
0.3815 |
|
10000 |
5 |
1.20 |
0.12 |
0.0827 |
|
20000 |
5 |
1.70 |
0.25 |
0.0055 |
|
40000 |
5 |
1.20 |
0.25 |
0.0827 |
|
80000 |
5 |
1.20 |
0.20 |
0.0827 |
P value (trend) |
|
0.116 |
|
|
NCE = normochromatic erythrocyte
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): ambiguous
Following 13 weeks dietary exposure to microencapsulated 1,1,1-trichloroethane, at doses between 5,000 and 80,000 ppm, examination of peripheral blood revealed and equivocal elevation of NCE’s in male mice and a negative response in female mice. The dose levels used were associated with a decrease in body weight gain, supporting systemic exposure to the test material. - Executive summary:
Following 13 weeks dietary exposure to microencapsulated 1,1,1-trichloroethane, at doses between 5,000 and 80,000 ppm, examination of peripheral blood revealed and equivocal elevation of micronucleated NCE’s in male mice and a negative response was recorded in female mice. 2000 normochromatic erythrocytes were exaimined for each aniamal. The dose levels used were associated with a decrease in body weight gain, supporting systemic exposure to the test material.
In male mice there was a statistically significant rise (dose-related trend) in the number of micronucleated cells up to 40,000ppm. The mean value at 80,000ppm was the same as the untreated control (0.80). No group mean values were significantly increased compared to the control (dose-related trend only). The current OECD guidelines sate that statistical significance should not be the only determining factor for a positive result. The biological significance of the findings (for example background data) are not discussed in this paper. It is therefore considered that the results give no clear evidence of mutagenicity.
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