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Diss Factsheets
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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
Specific investigations: other studies
Administrative data
- Endpoint:
- hepatotoxicity
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Study period:
- no data
- Reliability:
- 3 (not reliable)
Data source
Reference
- Reference Type:
- publication
- Title:
- Effects on growth and metabolism of rat liver by halothane and its metabolite trifluoroacetate
- Author:
- Stier, A.; Kunz, H.W.; Walli, A.K. and Schimassek, H.
- Year:
- 1 972
- Bibliographic source:
- Biochemical Pharmacology, 21:2181-2192
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- TFA was administered with the drinking water for 5-6 days. Analysis of fluorine content and biochemical procedures were done to evaluate the effects of TFA on liver growth and metabolism.
- GLP compliance:
- no
- Type of method:
- in vivo
- Endpoint addressed:
- basic toxicokinetics
Test material
- Reference substance name:
- 26-05-1
- Cas Number:
- 26-05-1
- IUPAC Name:
- 26-05-1
- Reference substance name:
- Trifluoroacetic acid
- EC Number:
- 200-929-3
- EC Name:
- Trifluoroacetic acid
- Cas Number:
- 76-05-1
- Molecular formula:
- C2HF3O2
- IUPAC Name:
- trifluoroacetic acid
- Details on test material:
- - Name of test material (as cited in study report): Trifluoroacetate (TFA)
- Analytical purity: no data
- Composition of test material, percentage of components: no data
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: no data
- Age at study initiation: no data
- Weight at study initiation: 200-260 g
- Fasting period before study: no data
- Housing: no data
- Diet: standard commercial rat diet ("Altromin", Lage-Lippe, Germany) ad libitum
- Water (e.g. ad libitum): no data
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS: no data
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
TFA was neutralized with NaOH - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- Not applicable
- Duration of treatment / exposure:
- 5-6 days
- Frequency of treatment:
- Administered with drinking water
- Post exposure period:
- No
Doses / concentrations
- Remarks:
- Doses / Concentrations:
130 µmoles TFA/100 g bw/day
Basis:
nominal in water
- No. of animals per sex per dose:
- No data
- Control animals:
- yes
- Details on study design:
- Every day, two to three rats were removed from the experimental series and killed under ether anaethesia. The series were repeated and the data quoted in the tables represent mean values established on four to six animals per day.
Examinations
- Examinations:
- In liver: determination of substrates, ATP, ADP, AMP, enzymes, protein, glycogen and neutral fat. Total fluorine content was also determined.
- Positive control:
- No
Results and discussion
- Details on results:
- The relative liver weight had increased by 43 % after 5 days of TFA treatment. Total protein content did not change but a 20 % decrease in glycogen content was noted. No change in neutral fat was observed. The most strinking changes in enzymes activities were a 42 % decrease in pyruvate kinase and a 125 % rise in glycerol-1-phosphate oxidase activity. TFA did not augment the acticity of NADPH oxydase.
Between day 1 and day 4-5 of treatment, there was a fall in the level of triose phosphates, with greater decreases in lactate and pyruvate. These changes in substrates levels were apparent after only 1 day of TFA administration, indicating its rapid action on liver. In some of the treated animals a rise in the intracellular content of malate and alpha-ketoglutarate in liver was noted after the fifth day of treatment. The content of glucose and total adenine nucleotides and the ATP-ADp ratio did not change.
Any other information on results incl. tables
The amount of organically bound fluorine in plasma and liver reached a steady level on the second day with a ration 1:1 ratio of liver to plasma concentration, which declined on days 4 and 5. Inorganic fluoride amounted to less than 1 % of total fluorine. The average daily amount of TFA taken up from the drinking water by a rat weighing 200 g is about 260 µmoles. Thus the fluorine content of the liver or of the plasma represents about 10 % of the administered amount of TFA.
Applicant's summary and conclusion
- Conclusions:
- The liver enlargement observed conforms to a co-ordinated growth of hepatic cells including the protein content and some enzyme activities.
- Executive summary:
In this study, TFA was administered to male Wistar rats for 4 -5 days in drinking water at dose level of 130 µmoles/100 g bw/day. Relative liver weight; content of protein, glycogen and neutral fat in livers; activities of some important enzymes in rat livers and content of some important substrates in liver were measured during the study (2 to 3 animals evaluated per day).
TFA causes as much as 40 % enlargement of liver within 4 -5 days. This liver enlargement conforms to a co-ordinated growth of hepatic cells including the protein content and some enzyme activities. There is a marked decrease in the activity of pyruvate kinase and an increase of glycerol 1 -phosphate oxidase. TFA causes a decrease in phosphorylated trioses common to glycolysis and gluconeogenesis, but an increase in certain tricarboxylic acid cycle intermediates.
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