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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
Endpoint summary
Administrative data
Description of key information
There are numerous acute oral and inhalation studies conducted in animals showing very low acute toxicity (LD 50’s in the region of 10,000 mg/kg or ppm). Dermal data is less prevailant but again the LD 50 is in the region of 15,000 mg/kg. A recent ATSDR review (2006) found lethal inhalation doses in humans to be in the region of 6000 to 20 000 ppm. 1,1,1-trichloroehtane can therefore be considered to be of no serious acute hazard. However, it should be noted that in humans exposure to 175 ppm for 3.5 hours results in reduced psychomotor abilities.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 10 300 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- LC50
- Value:
- 14 250 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
Additional information
1,1,1-trichloroethane is of low acute toxicity following oral (gavage) exposure. The dog is the most sensitive species, having an LD50 of 750 mg/kg bwt, follwed by the rabbit with an LD50 or 5660 mg/kg bwt. In the rat and mosue LD 50 values range from 9700 to 17148 mg/kg bwt.
Summary of acute toxicity via the oral route
Author |
Reliability |
Species |
sex |
LD50 |
remarks |
ISIS |
IUCLID 4 |
Dog |
|
750 mg/kg bw |
|
ISIS |
IUCLID 4 |
rabbit |
|
5660 mg/kg bw |
|
Janssen |
IUCLID 4 (GLP) |
rat |
|
> 2000 mg/kg bw |
|
Torkelson |
3 |
rat |
Male |
14600 mg/kg bw |
inhibited product |
Male |
12300 mg/kg bw |
uninhibited product |
|||
Female |
11000 mg/kg bw |
inhibited product |
|||
Female |
10300 mg/kg bw |
uninhibited product |
|||
mouse |
Female |
9700 mg/kg bw |
inhibited product |
||
11240 mg/kg bw |
uninhibited product |
||||
guinea pig |
Male/Female |
8600 mg/kg bw |
inhibited product |
||
Male |
9470 mg/kg bw |
uninhibited product |
|||
rabbit |
Male/Female |
10500 mg/kg bw |
inhibited product |
||
Female |
10500mg/kg bw |
uninhibited product |
|||
Bruckner |
2 |
rat |
Male |
NOEL 4000 mg/kg bwt |
|
ASTDR |
2 |
mouse |
Male |
17148 mg/kg bwt |
|
Female |
12996 mg/kg bwt |
|
The value for the dog is not cross referenced in any other reviews (eg ASTDR, WHO or RAIS) and is therefore not considered reliable.
Studies of animal mortality following acute inhalation exposure to 1,1,1-trichloroethane are numerous. Median lethal concentrations (LC50 values) have been calculated for rats and mice. For rats, LC50 values from 14250 to 38,000 ppm were reported. For mice, reported LC50 values ranged from 3,911 to 29492 ppm. Much of the variation in these data can be attributed to differences in the exposure duration (higher LC50 values were generally obtained in studies with short exposure periods).
Summary of acute toxicity via the inhalation route
Author |
Reliability |
Species |
sex |
LC50 |
remarks |
|
ISIS |
IUCLID 4 |
mouse |
|
3911 ppm |
2 hours |
|
ISIS |
IUCLID 4 |
rat |
|
18000 ppm |
4 hours |
|
Siegel |
IUCLID 4 |
rat |
|
18400 ppm |
4 minutes |
|
Moser |
IUCLID 4 |
mouse |
Male |
29492 ppm |
10 minutes |
|
Moser |
IUCLID 4 |
mouse |
Male |
20616 ppm |
30 minutes |
|
Woolverton |
IUCLID 4 |
mouse |
Male |
22241 ppm |
30 minutes |
|
Moser |
IUCLID 4 |
mouse |
18358 ppm |
60 minutes |
||
Gradiski |
IUCLID 4 |
Mouse/rat |
Female |
13410 ppm |
6 hours |
|
Clark |
IUCLID 4 |
rat |
Male and female |
38000 ppm |
15 minutes |
|
Adams |
3 |
rat |
Male and female |
18000 ppm |
3 hours |
|
Adams |
3 |
rat |
Male and female |
14250 ppm |
7 hours |
|
Clark |
2 |
rat |
Male and female |
3.8 % in air (38000 ppm) |
15 minutes |
|
Clark |
2 |
dog |
|
0.7 % in air for cardiac changes |
5 minutes |
|
Inhalation exposure is the most likely route of exposure in man and the US Agency for Toxic Substances and Disease Registry (ATSDR) recently (July 2006) produced a full toxicological profile for 1,1,1-trichloroehtane. In this review it is reported that the lethal concetraion of 1,1,1-trichlorethane in humans is between 6000 and 20000 ppm and that human death following exposure is usually attributed to either depression of the central nervous system, which results in respiratory arrest or sensitisation of the heart to epinephrine which results in severe cardiac arrhythmias. Also reported in this review is the lowest-observed-adverse-effect level (LOAEL) of 175 ppm for reduced performance of psychomotor tests in a human study by Mackay et al. (1987). Individuals exposed to 175 or 350 ppm of 1,1,1-trichloroethane for 3.5 hours demonstrated impaired performance of psychomotor tests. This is supported by results of other human studies. Gamberale and Hultengren (1973) found psychophysiological test performance deficits in exposed individuals, although at a higher concentration than the LOAEL of 175 ppm identified by Mackay et al. (1987). Muttray et al. (1999, 2000) found EEG changes consistent with increased drowsiness and slight irritant nasal responses in volunteers exposed to 200 ppm. (ATSDR 2006).
Only limited data is available regarding the acute effects of dermal exposure to 1,1,1-trichloroethane and the volatile nature of the substance means that contact, unless covered, is likely to be brief. Exposure in the rabbit suggests that 1,1,1-trichloroethane is only lethal at very high doses, the LD 50 being greater than 15,800 mg/kg
Summary of acute toxicity via the dermal route
Author |
Reliability |
Species |
sex |
LD50 |
remarks |
Janssen |
IUCLID 4 (GLP) |
rat |
> 2000 mg/kg bw |
|
|
Torkelson |
IUCLID 4 |
rabbit |
> 15800 mg/kg bw |
|
A number of studies using the intraperitoneal route have also demonstrated relatively low acute toxicity, the LD50 being between 2000 to 5080 mg/kg bwt; although it should be noted that one limit study conducted at 2 mL/kg was associated with 4/5 deaths in the male rat group only.
Summary of acute toxicity via the intra peritoneal route
Author |
Reliability |
Species |
sex |
LD50 |
remarks |
ISIS |
IUCLID 4 |
dog |
3100 mg/kg bw |
|
|
ISIS |
IUCLID 4 |
rat |
3593 mg/kg bw |
|
|
Gradiski |
IUCLID 4 |
mouse |
female |
3700 mg/kg bw |
|
Klassen |
IUCLID 4 |
dog |
Male |
4140 mg/kg bw |
|
mouse |
male |
5080 mg/kg bw |
|
||
Lombard |
1 |
rat |
Male |
2 ml/kg bw |
|
female |
> 2ml/kg bw |
|
References
DAUGHERTY-MW; FORSYTH-CSToxicities Profiles - Toxicity Summary for 1,1,1-TRICHLOROETHANE
RAIS
Toxicological profile for 1,1,1-Trichloroethane.
ATSDR 2006
1,1,1-Trichloroethane in drinking-water.
WHO 2003
Justification for classification or non-classification
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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