Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 200-929-3 | CAS number: 76-05-1
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Study well conducted but no guideline followed and only few tissues examined for a distribution and metabolism study.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 984
Materials and methods
- Objective of study:
- distribution
- metabolism
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Radiolabelled halothane was administered to pregnant mice by inhalation route and to newborn mice by intraperitoneal injection. Then animals were killed and an autoradiography was performed in order to study the distribution and the metabolism of halothane in maternal tissues and in newborn mice.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Halothane
- EC Number:
- 205-796-5
- EC Name:
- Halothane
- Cas Number:
- 151-67-7
- Molecular formula:
- C2HBrClF3
- IUPAC Name:
- 2-bromo-2-chloro-1,1,1-trifluoroethane
- Details on test material:
- - Name of test material (as cited in study report): Halothane
- Physical state: no data
- Lot/batch No.: no data
- Expiration date of the lot/batch: no data
- Stability under test conditions: assumed to be stable during the test (sponsor responsibility)
- Storage condition of test material: no data
- Other: source: Radiochemical centre, Amersham, England
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 14 C-labelled halothane (specific activity3.59 mCi/mM)
Test animals
- Species:
- mouse
- Strain:
- C57BL
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: no data
- Age at study initiation: about 3 months old and newborn (5 days old)
- Weight at study initiation: male rats: no data
- Housing: no data
- Diet (e.g. ad libitum): pellet diet (R3) (Ewos, Södertälje, Sweden), ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23°C
- Humidity (%): no data
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): no data
IN-LIFE DATES: From: To: no data
Administration / exposure
- Route of administration:
- other: inhalation for pregnant mice and intraperitoneal for newborns
- Vehicle:
- olive oil
- Details on exposure:
- TYPE OF INHALATION EXPOSURE: whole body
GENERATION OF TEST ATMOSPHERE / CHAMPER DESCRIPTION
- Exposure apparatus: the exposure was performed in an all-glass chamber which allows 4 mice to be exposed simultaneously. The chamber used was a modification of an earlier apparatus, described by Bergman (1979). The halothane was diluted with olive oil and liberated from the oil solutions by gentle heating.
- Method of holding animals in test chamber: no data
- Source and rate of air: no data
- Method of conditioning air: no data
- System of generating particulates/aerosols: not applicable
- Composition of vehicle (if applicable): no data
- Concentration of test material in vehicle (if applicable): no data
- Method of particle size determination: not applicable
- Treatment of exhaust air: no data
TEST ATMOSPHERE (if not tabulated): not applicable
- Particle size distribution:
- MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): - Duration and frequency of treatment / exposure:
- 10 min
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Pregnant mice: 100 µCi of 14C-labelled halothane
Newborn: 5 µCi of 14C-halothane
- No. of animals per sex per dose / concentration:
- 36 pregnant mice
4 newborns - Control animals:
- no
- Positive control reference chemical:
- no positve control
- Details on study design:
- no details
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: see table 7.1.1/1
- Time and frequency of sampling: 0, 1, 4 or 24 hrs after the treatment with halothane
- Other:
METABOLITE CHARACTERISATION STUDIES:
- Tissues and body fluids sampled: see Table 7.1.1/1
- Time and frequency of sampling: 0, 1, 4 or 24 hrs after the treatment with halothane
- From how many animals: (samples pooled or not): 4
- Method type(s) for identification: Liquid scintillation counting
- Limits of detection and quantification: no data
- Other:
TREATMENT FOR CLEAVAGE OF CONJUGATES (if applicable): - Statistics:
- No data
Results and discussion
- Preliminary studies:
- not applicable
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- not applicable
- Details on distribution in tissues:
- Autoradiograms of pregnant mice showed a very high uptake of radioactivity in the maternal brain, body fat, nasal mucosa, blood, liver, kidney and lung, immediately after inhalation of 14C-halothane. Non-volatile radioactivity was present in a small but significant amount in the same organs, except body fat and brain, immediately after inhalation. The high levels of volatile radioactivity registered in the brain and body fat only by low-temperature autoradiography indicate an uptake of 14C-halothane itself. Low temperature autoradiography, as compared to autoradiography of freeze-dried and evaporated sections, showed that non-metabolized 14C-halothane was present in the tissues, particulary in body fat, up to 1 hr after the inhalation. In contrast to the volatile radioactivity, 14C-halothane metabolites were retained in relatively large amounts in certain maternal tissues, such as liver, kidney, eye and lungs, with peak values at 4 hrs after inhalation while the levels had decreased considerably at 24 hrs, except in the eyes and bronchi. Non-extractable radioactivity derived from 14C-halothane was seen in nasal mucosa, bronchi and liver at all survival times. The liver radioactivity had a mottled appearance, showing a centrilobular distribution.
Low-temperature autoradiography showed that 14C-halothane itself passed over the embryo and foetus at all studied stages of gestation. In early gestation (day 11), the radioactivity was rather evenly distributed between the different embryonic structures. In mid- (day 14) and late (day 17) gestation, there were more differentiated foetal distribution patterns with a higher concentration of radioactivity in blood and liver, as compared with other foetal organs.
At 1 hr after inhalation of 14C-halothane, autoradiograms obtained by low temperature and conventional autoradiography showed the same distribution patterns in foetal tissues, indicating that the major part of the volatile 14C-halothane had left the foetus. An interesting observation was the high concentration (among the highest in the body) in amniotic fluid, which was seen at 1 hr through 24 hrs after inhalation. Autoradiograms revealed low levels of radioactivity in embryonic and foetal tissues immediately after inhalation. The level was increasing with time, with a peak value at 4 hrs after inhalation. In early gestation, especially the neuroepithelium but also other structures revealed high concentrations. In late gestation, on the contrary, the foetal brain had a low concentration as compared to foetal tissues. All radioactivity in foetal tissues and in amniotic fluid was extractable in early as well as in late gestation.
Autoradiograms of the 5 day old mice injected intraperitoneally with 14C-halothane showed that volatile as well as non-volatile radioactivity was distributed in the same organs as was the case in adult mice exposed by inhalation. This pertains to extracted tissues as well, where a retention was observed in liver and respiratory epithelium (nasal mucosa and bronchi).
See details in Table 7.1.1/1
Transfer into organs
- Test no.:
- #1
- Transfer type:
- blood/placenta barrier
- Observation:
- distinct transfer
- Remarks:
- Halothane accumulated in the amniotic fluid. Accumulation is relatively slow (peak at 4 hrs). As halothane is a lipid-soluble compound, it easily passed membranes including those of the placenta. An accumulation in the fluids of the maternal eyes occurred
- Details on excretion:
- Not applicable
Metabolite characterisation studies
- Metabolites identified:
- no
Any other information on results incl. tables
Table 7.1.1/1: Concentrations in maternal organs, in amniotic fluid, in foetuses and placentas of non-volatile radioactivity at 0, 4, and 24 hrs after a 10 min. inhalation period of 14C-halothane. Concentrations are expressed in dpm per µL or mg +/- SEM (n=4)
|
0 hr |
4 hrs |
24 hrs |
Brain |
6.6 ± 2.4 |
67 ± 22 |
2.0 ± 0.2 |
Lungs |
89 ± 33 |
223 ± 48 |
5.1 ± 2.4 |
Trachea |
106 ± 46 |
414 ± 99 |
13 ± 2.6 |
Heart |
17 ± 8.6 |
174 ± 47 |
4.4 ± 0.7 |
Liver |
28 ± 19 |
285 ± 75 |
7.4 ± 1.3 |
Kidneys |
15 ± 9 |
131 ± 25 |
4.1 ± 0.7 |
Ovaries |
15 ± 5.7 |
181 ± 85 |
5.6 ± 0.9 |
Fat |
35 ± 27 |
195 ± 22 |
1.9 ± 0.5 |
Serum |
19 ± 9.5 |
179 ± 37 |
8.6 ± 2.9 |
Foetuses |
2.4 ± 0.9 |
175 ± 25 |
5.1 ± 0.5 |
Placentas |
4.2 ± 1.9 |
190 ± 37 |
5.5 ± 0.8 |
Amniotic fluid |
0.2 ± 0.1 |
86 ± 19 |
6.8 ± 1.4 |
Dpm : desintegration per minute
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): high bioaccumulation potential based on study results
Under the test conditions, halothane accumulated in the amniotic fluid. The accumulation is relatively slow (peak at 4 hrs). As halothane is a lipid-soluble compound, it easily passed membranes including those of the placenta. In addition to the amniotic fluid, an accumulation in the fluids of the maternal eyes occurred, which was more apparent at low temperature autoradiography. - Executive summary:
In a distribution and metabolism study, halothane (99%) was administered to C57BL pregnant mice by inhalation or to 5 days old newborn mice by intraperitoneal injection. The pregnant mice were exposed to vapors of carbon 14 labelled halothane diluted in olive oil at the dose of 100 µCi for 10 min at different stages of gestation (11, 14 or 17 days of gestation). Newborn mice were exposed to 5 µCi 14C-halothane in a single injection by intraperitoneal route.
At different time point after the exposure (0, 1, 4 or 24 hrs), the mice were killed and the animals were examined by conventional whole-body autoradiography or by low temperature autoradiography which allowed the registration of volatile radioactivity. Radioactivity was quantified by liquid scintillation counting.
Under the test conditions, halothane accumulated in the amniotic fluid. The accumulation is relatively slow (peak at 4 hrs). As halothane is a lipid-soluble compound, it easily passed membranes including those of the placenta. In addition to the amniotic fluid, an accumulation in the fluids of the maternal eyes occurred, which was more apparent at low temperature autoradiography.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.