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EC number: 203-481-7 | CAS number: 107-31-3
- 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 vitro / ex vivo
- Type of information:
- calculation (if not (Q)SAR)
- Remarks:
- Migrated phrase: estimated by calculation
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Meets generally accepted scientific standards and is reported in sufficient detail.
Data source
Reference
- Reference Type:
- publication
- Title:
- Toxicokinetic modelling of methyl formate exposure and implications for biological monitoring.
- Author:
- Nihlén A and Droz P-O
- Year:
- 2 000
- Bibliographic source:
- Int Arch Occup Environ Health 73, 479-487.
Materials and methods
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- A toxicokinetic model to describe human inhalation exposure, and to predict the urinary excretion of the metabolites methanol and formic acid, was developed. The model was validated against human experimental data.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Methyl formate
- EC Number:
- 203-481-7
- EC Name:
- Methyl formate
- Cas Number:
- 107-31-3
- Molecular formula:
- Câ‚‚Hâ‚„Oâ‚‚
- IUPAC Name:
- methyl formate
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- human
Administration / exposure
- Route of administration:
- inhalation
- Duration and frequency of treatment / exposure:
- 6 hour(s)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Males: 100 ppm
- No. of animals per sex per dose / concentration:
- Males: 40
Results and discussion
Toxicokinetic / pharmacokinetic studies
Toxicokinetic parameters
- Test no.:
- #1
- Toxicokinetic parameters:
- half-life 1st: 0.1 min
Metabolite characterisation studies
- Metabolites identified:
- yes
Any other information on results incl. tables
1. Prediction of individual urinary metabolite level time
course
Assuming an 8-h inhalation exposure to 100 ppm MFT the model
predicted 8-h MeOH level of 0.119 mM which fitted well with
the measured average 0.113 mM. Further the model predicted
FA levels of 0.76 mmol/g creatinine, compared to the average
measured 0.70 mmol/g creatinine.
The rate constants used were derived from 16 subjects
exposed to 100 ppm MF:
KMF (oxidation and hydrolysis of MF) = 6.7 (6.1-7.3) 1/min,
and
FMF (fraction of hydrolysis) = 97 (95-100)%.
2. Predictions of urinary metabolite excretion after 8-h
exposure to MF
2.1. Methanol
The model predicted a linear relation between the urinary
concentration of MeOH and increasing MF exposure levels in
the range 0 - 150 ppm MF, both at rest and at light work
load. The predicted levels of urinary MeOH were higher at
the end of the work-shift compared to the level before
shift. The prediction fitted well with values measured after 8 h
occupational MF exposure (Berode et al., 2000).
2.2. Formic acid
A nonlinear relationship was noted between formic acid in
urine after a 8-h work-shift and increasing concentrations
of MF
in the air. The curve was relatively flat at
background levels and up to approx. 50 ppm, and much steeper
at MF concentrations >50 ppm.
2.3 Urinary metabolite time course
The model was used to calculate the urinary concentration
vs. time curve for MeOH and FA. During the 8-h work shift
the concentrations increased and declined thereafter. FA
returned to background levels within 2-4 h after the end of
exposure. The elimination of MeOH was much slower, as
background levels were not reached until 8-12 h after the
end of exposure.
Table: Urinary exretion ; selected values (human exposure during 0-8 hours):
=====================================================
MF in air Time urinary FA urinary MeOH
(ppm) (hours) (nmol/g creat.) (mM)
-----------------------------------------------------
Background 0 0.30 0.054
50 ppm 8 1.0 0.14
12 0.3 0.08
24 0.3 0.054
100 ppm 8 2.4 0.24
12 0.4 0.125
24 0.3 0.054
=====================================================
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
- Executive summary:
Conclusion:
The authors developed a TK-model that fitted well into measured data and allows prediction of time-concentration curves for metabolites of methyl formate. Background levels for urinary methanol (MeOH; 0.054 mM) and formic acid (0.30 nmol/g creatinine) were provided. A mean rate constant for the global oxidation and hydrolysis metabolism of methyl formate in human subjects (n=16) was provided (6.7 (6.1-7.3)), which compares to a halflife time as follows: t1/2= ln 2/k (1st order reaction) = 0.69/6.7 = 0.01 minutes. Hydrolysis of methyl formate to formic acid and MeOH accounts for 97 (95-100) %. Oxidation is therefore a minor metabolic pathway. Formic acid is more rapidly eliminated compared to MeOH.
Both urinary formic acid and MeOH could be used as markers for biomonitoring. MeOH is more suitable at lower exposures, whereas formic acid is more sensitive at higher exposures. Both paramters were clearly increased after an 8 -hour exposure period at 50 ppm and at 100 ppm, but the increase at 50 ppm was relatively small compared to the background level. 50 ppm is currently the German OEL.
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