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EC number: 204-624-6 | CAS number: 123-39-7
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to Guideline study with acceptable restrictions (partly limited documentation, e.g. no details about the test substance)
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 974
- Report date:
- 1974
- Reference Type:
- publication
- Title:
- Study on the mutagenic effects of formamides and acetamides in the dominant lethal test
- Author:
- Peh J
- Year:
- 1 974
- Bibliographic source:
- Chromosome aberrations by industrial chemicals and vinyl chioride toxicity. Proceedings of 2nd International Symposium, Milano
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 478 (Genetic Toxicology: Rodent Dominant Lethal Test)
- Deviations:
- no
- GLP compliance:
- no
- Type of assay:
- rodent dominant lethal assay
Test material
- Reference substance name:
- monomethylformamide
- IUPAC Name:
- monomethylformamide
- Details on test material:
- no details
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Source: Wiga, Sulzfeld, Germany
Mean body weight at initiation: 31 g;
initial age: 12-14 weeks
single cages except during mating (1 male with 3 virgin females)
Housing condition:
temperature 20-24°C
rel. air humidity: 50-60%
light/dark cycle: 12/12h
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- water
- Details on exposure:
- Dose: 1/5 of the LD50 in male mice
Application volume: 0.1 ml per mouse - Duration of treatment / exposure:
- single application
- Frequency of treatment:
- single application
- Post exposure period:
- 8 weeks for treated males
Doses / concentrations
- Remarks:
- Doses / Concentrations:
560 mg/kg bw
Basis:
- No. of animals per sex per dose:
- 20 males per group
- Control animals:
- yes, concurrent no treatment
- Positive control(s):
- 0.125 mg/kg bw Trenimon®
Examinations
- Tissues and cell types examined:
- Each treated male mice mated with 3 virgin females for 1 week; this procedure was repeated with further virgin females for 7 weeks (totally 8 matings in 8 weeks); each female was sacrificed at day 18 after initiation of mating.
Determined parameters
Number of pregnant dams (conception rate)
total number of implantations
living fetuses
dead fetuses
early resorptions
late resorptions
Mutation index: dead fetuses + early resorptions + late resoptions/total implantations - Evaluation criteria:
- Statistically significant increase of mutation rate/index in the treated group.
- Statistics:
- Level of significance: p<=0.05
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- not specified
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Conception rate in females of the 1st and 2nd week was reduced; this effects was considered to be related to the toxic effects in males; conception rate not altered in week 3-8.
Mean number of implantations was not affected in the treatment group.
Slight but significant increase in mutation index in week 3 but still within the historical control range. In the positive control the mutation index was significantly increased in week 1 -3.
Effects in treated males
General condition of treated males was reduced, 6 males died the day after injection; reduced body weight in the 1st week after treatment, normal thereafter. Necropsy of dead males: intestinal atony, liver congestion; no effects in survivors.
No symptoms in positive control.
Any other information on results incl. tables
Mutations in the dominant lethal assay in mice after i.p. injection of N-methylformamide (NMF)
Specified group |
Mutation index in week |
|||||||
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
|
Untreated control |
11.5 |
9.8 |
9.4 |
13.0 |
11.2 |
13.2 |
7.7 |
9.2 |
Positive control |
40.5* |
46.1* |
26.5* |
6.9 |
6.1 |
9.2 |
11.3 |
8.8 |
NMF treated |
13.2 |
8.1 |
15.4* |
8.9 |
9.3 |
12.7 |
8.3 |
8.6 |
*: significant
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
No germ cell mutation was detected in the mouse dominant lethal test at toxic dose levels. - Executive summary:
Comparable to Guideline study with acceptable restrictions (partly limited documentation, e.g. no details about the test substance; no vehicle control but untreated control).
In the dominant lethal assay 20 male NMRI mice received a single i.p. injection of 560 mg/kg bw. Treated males, concurrent untreated and positive controls were mated with virgin females (1 male/3 females) the week after treatment; mating for one week with further females was repeated for 7 weeks (totally 8 matings for each male). Females were sacrificed day18 after mating initiation; conception rate and mutation index (dead fetuses and all resorptions per total number of implantations) were determined. The conception rate was reduced in week 1 and 2 in the treatment group due to toxic effects (6/20 males were found dead). However, no effects were detected on the mutation index. The positive control was valid.
Conclusion: No germ cell mutation was detected in the mouse dominant lethal test at toxic dose levels.
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