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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
Exposure related observations in humans: other data
Administrative data
- Endpoint:
- exposure-related observations in humans: other data
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Meets generally accepted scientific standards and is described in sufficient detail.
Data source
Reference
- Reference Type:
- publication
- Title:
- Urinary methanol and formic acid as indicators of|occupational exposure to methyl formate.
- Author:
- Berode M, Sethre T, Laubli T and Savolainen H
- Year:
- 2 000
- Bibliographic source:
- nt Arch Occup Environ Health 73(6), 410-414.
Materials and methods
- Type of study / information:
- Type of experience: other: Biomonitoring and background levels
- 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
Results and discussion
Any other information on results incl. tables
RS-Freetext:
The volunteers exposed to 100 ppm MF vapour at rest for 8 h
excreted 3.62 +/- 1.13 mg MeOH/l (mean +/- SD) at the end of
the exposure. This was statistically different (P < 0.001)
from pre-exposure MeOH excretion (2.15 +/- 0.80 mg/1), or
from that of controls (1.69 +/- 0.48 mg/l).
In foundrymen, the urinary FA excretion after the 8 h
workshift exposure to a time weighted average (TWA)
concentration of 2 to 156 ppm MF showed a dose-dependent
increase best modelled by a polynomial function. The highest
urinary FA concentration was 129 mg/g creatinine. The
pre-shift urinary FA of the foundrymen (18.3 +/- 5.6 mg/g
creatinine) did not differ from that of controls (13.8 +/-
7.9 mg/g creatinine). The urinary MeOH excretion of the
foundrymen after the shift, varied from < 1 to 15.4 mg/l,
while the correlation with the preceding MF exposure was
poor. The foundrymen excreted more (P = 0.01) FA (2.12 +/-
3.56 mg/g creatinine) after the workshift than
experimentally, once-exposed volunteers (0.32 +/- 0.11 mg/g
creatinine) at a similar inhaled MF level of 1 ppm).
Applicant's summary and conclusion
- Executive summary:
The urinary FA excretion was 32.2 +/- 11.3 mg/g creatinine after the exposure, which was statistically different (P < 0.001) from
pre-exposure excretion (18.0 +/- 9.3 mg/g creatinine) or that of controls (13.8 +/- 7.9 mg/g creatinine).The authors concluded that, in spite of its high background level in non-exposed subjects, urinary FA seems to be a useful biomarker
of methyl formate exposure. There remain questions regarding the reason for the differences in chronic and acute exposure, respectively.
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