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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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: 2e: Study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- [14C]methyl chloroform (1,1,1-trichloroethane): pharmacokinetics in rats and mice following inhalation exposure
- Author:
- SCHUMANN-AM; FOX-TR; WATANABE-PG
- Year:
- 1 982
- Bibliographic source:
- TOXICOL-APPL-PHARMACOL 62 390-401
Materials and methods
- Objective of study:
- metabolism
- GLP compliance:
- no
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:
- Commercial formulation: Chloroethen Vg, Dow Chemical CO. Lot Nos TAO 2168-B and TAO 4259-1. Purity 94 % (stabilizers, 0.2 % aliphatic hydrocarbon impurities)
[14C]Methyl chloroform (2—14C), New England Nuclear, Boston (Lot no.1119-293; 2.51 mCi/mmol) >99 % purity
Refered to as methyl chloroform in the paper
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- 7 days acclimatization. Temperature 22 0C and humidity 50 % with 12 hour light cycle.
Administration / exposure
- Route of administration:
- inhalation: vapour
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- Exposures conducted in a 30 litre glass chamber (5 or 10 litres/min airflow). Vapour was generated in 100-litre bags and metered into the exposure chamber with a Masterfex pump. The concentration in the chamber was analysed at 30-minute intervals by gas chromatography and was within 6 % of the target concetration.
- Duration and frequency of treatment / exposure:
- 6 hours on at least 2 ocassions
Doses / concentrations
- Remarks:
- Doses / Concentrations:
150 or 1500 ppm of [14C]Methyl chloroform for mass balance experiments, and unlabelled substance for plasma level analysis.
- No. of animals per sex per dose / concentration:
- 4 males/group
- Control animals:
- no
- Details on study design:
- Radio-labelled substance was used for mass balance experiments. Non-labelled for TK sampling.
- Details on dosing and sampling:
- For the radio-active metabolism experiment, animals were returned to metabolism cages immediately after their 6-hour exposure period. The amount of CO2 in expired air was measured at 3, 6, 12, 24, 36, 48 and 72 hours using activated charcoal columns. Urine was collected at 12 hour intervals and faeces at 24 hour intervals. After 72 hours skin, liver, kidney and fat sample were removed and the carcass homogenized. Radio activity was measured using liquid scintillation spectrometry.
Blood sampling for plasma levels was conducted in 3 to 4 anesthetized rats/group, at 0, 5, 10, 15, 20, 25, 30, 45, 60, 75, 90, 105, 120, 150 and 180 minutes after exposure. Analysis was by gas chromatography.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- Found in fat, liver and kidney (no other individual tissues examined)
Plasma levels (estimated from graph) were:
1500 ppm: 100, 18, 9, 6 and 5.5 μg/g at 0, 30, 60, 120 and 180 minutes after exposure, respectively
150 ppm: 12, 1.5, 0.8, 0.7 and 0.5 μg/g at 0, 30, 60, 120 and 180 minutes after exposure, respectively
- Details on excretion:
- >96 % in 24 hours
Pulmonary - 87 - 97% of total body burden. 80-90% of which was eliminated in the first 3 hours
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- Tmax: 0 hours (end of exposure period)
- Test no.:
- #1
- Toxicokinetic parameters:
- Cmax: 100 ug/g (after 1500 ppm)
- Test no.:
- #2
- Toxicokinetic parameters:
- Cmax: 12 ug/g (after 150 ppm)
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 1st: 2.0 min (1500 ppm rapid phase)
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 2nd: 12.8 min (1500 ppm slow phase)
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 1st: 1.9 (150 ppm rapid phase)
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 2nd: 14.8 min (1500 ppm slow phase)
Any other information on results incl. tables
Recovery of radioactivity after 6 hours inhalation exposure to 150 or 1500 ppm 1,1,1-trichloroethane in male B6C3F1 mice
Exposure concentration |
150 ppm |
1500 ppm |
||
N = 4 Mean + SD |
Methyl chloroform (μmol-eq) |
Percentage (of total recovered) |
Methyl chloroform (μmol-eq) |
Percentage (of total recovered) |
Expired air |
|
|||
Methyl chloroform |
4.32 + 0.97 |
86.7 + 5.0 |
38.70 + 12.93 |
96.7 + 1.5 |
Carbon Dioxide |
0.06 + 0.01 |
1.2 + 0.4 |
0.18 + 0.09 |
0.4 + 0.2 |
Urine |
0.43 + 0.21 |
8.8 + 3.9 |
0.82 + 0.26 |
2.3 + 1.4 |
Faeces |
0.03 + 0.02 |
0.8 + 0.7 |
0.19 + 0.05 |
0.5 + 0.2 |
Carcass |
0.01 + 0.00 |
0.2 + 0.1 |
ND |
ND |
Cage wash |
0.12 + 0.07 |
2.5 + 1.2 |
ND |
ND |
Body burden |
|
|||
μmol-eq/rat |
4.97 + 0.96 |
|
39.90 + 12.89 |
|
μmol-eq/kg body wt |
183 + 30 |
|
1416 + 471 |
|
μmol-eq metabolised |
0.65 + 0.27 |
13.3 + 5.0 |
1.19 + 0.26 |
3.3 + 1.5 |
μmol-eq metabolized/kg body wt |
24.26 + 10.28 |
|
42.06 + 8.61 |
|
ND = not detected
Table # Distribution and clearance of radioactivity following a 6 hours inhalation exposure to 150 or 1500 ppm 1,1,1-trichloroethane
N = 4 Mean + SD |
nmol-eq 1,1,1-trichloroethane/g of tissue |
|||
0 |
24 |
48 |
72 |
|
150 ppm |
|
|
|
|
Liver |
76.0 + 7.5 |
5.0 + 0.8 |
2.8 + 1.0 |
4.4 + 0.7 |
Kidney |
74.6 + 6.7 |
7.0 + 2.0 |
5.8 + 0.6 |
3.0 + 1.5 (3) |
Fat |
1329 + 123 |
10.2 (1) |
7.6 (1) |
ND |
1500 ppm |
|
|
|
|
Liver |
631 + 144 |
ND |
ND |
ND |
Kidney |
1103 + 579 |
ND |
ND |
ND |
Fat |
16198 + 1792 |
ND |
ND |
ND |
ND = not detected
Value in paranthesis is number above the detection limit
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): low bioaccumulation potential based on study results Cleared rapidly from the fat
Male mice were exposed to radio-labeled 1,1,1-trichloroethane vapour for 6 hours at 150 or 1500 ppm. At the end of the exposure period the elimination of 14C activity was measured for 72 hours. Blood samples, following exposure to non-labeled test material were also analysed for 1,1,1-trichlorethane.
The major route of elimination was exhalation of unchanged chemical and 87 – 97% of the total radio activity was recovered from this route. The remaining 2 – 13 % was detected as metabolized 1,1,1-trichlorethane in the expired air (14 CO2) and as nonvolatile radioactivity in the urine, faeces, carcass and cage wash. The radio labeled substance was more concentrated in the fat, than in the liver or kidneys, however it was rapidly cleared from the fate so that by 24 hours less than 2 % of the initial radioactivity remained; showing little potential for significant bioaccumulation. - Executive summary:
Male mice were exposed to radio-labeled 1,1,1-trichloroethane vapour for 6 hours at 150 or 1500 ppm. At the end of the exposure period the elimination of 14C activity was followed for 72 hours. Blood samples, following exposure to non-labeled test material were also analysed for 1,1,1-trichlorethane.
The major route of elimination was exhalation of unchanged chemical and 87 to 97% of the total radio activity was recovered from this route. The remaining 2 to 13 % was detected as metabolized 1,1,1-trichlorethane in the expired air (14 CO2) and as nonvolatile radioactivity in the urine, faeces, carcass and cage wash. The radio labeled substance was more concentrated in the fat, than in the liver or kidneys, however it was rapidly cleared from the fate so that by 24 hours less than 2 % of the initial radioactivity remained; showing little potential for significant bioaccumulation.
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