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EC number: 212-828-1 | CAS number: 872-50-4
- 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 vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in bacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1978
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 978
- Report date:
- 1978
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- not specified
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- 1-methyl-2-pyrrolidone
- EC Number:
- 212-828-1
- EC Name:
- 1-methyl-2-pyrrolidone
- Cas Number:
- 872-50-4
- Molecular formula:
- C5H9NO
- IUPAC Name:
- 1-methylpyrrolidin-2-one
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- Laboratory identification number 77/585, not further specified
Method
Species / strain
- Species / strain / cell type:
- S. typhimurium, other: TA98, TA1535, TA100, TA1537
- Additional strain / cell type characteristics:
- not specified
- Metabolic activation:
- with and without
- Metabolic activation system:
- metabolic activation (S9 mix from Arochlor 1254 treated male Sprague-Dawley rats)
- Test concentrations with justification for top dose:
- Experiment 1: 3.15, 10, 31.5, 100, 315, 1000, 3000, 10000, and 30000 µL/plate with S9 mix
Experiment 2: 31.5, 100, 315, 1000, 3000, 10000, and 30000 µL/plate without S9 mix - Vehicle / solvent:
- DMSO or water
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 3-methylcholanthrene
- benzo(a)pyrene
- other: 2-aminoanthracene; N-methyl-N-nitro-N-nitrosoguanidine
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (plate incorporation)
DURATION
- Exposure duration: 72 hours
NUMBER OF REPLICATIONS: Concentrations were tested in duplicate
DETERMINATION OF CYTOTOXICITY
- Method: relative total growth - Evaluation criteria:
- Not indicated.
Results and discussion
Test results
- Species / strain:
- S. typhimurium, other: TA98, TA1535, TA100, TA1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
No confounding factors were described.
ADDITIONAL INFORMATION ON CYTOTOXICITY
Since a reduction of the his background lawn was not evident even at the highest dose of N-methylpyrrolidone, an overshadowing of a possible mutagenicity by toxicity is unlikely.
Applicant's summary and conclusion
- Conclusions:
- No mutagenic potential was measured in the in vitro gene mutation study in bacteria.
- Executive summary:
N-Methylpyrrolidone was tested for mutagenicity with Salmonella typhimurium TA 100, TA 1537 and TA 98. Seven different concentrations from 31.5 to 30,000 nl per plate were used in the experiments for direct mutagenicity. In the experiments with S-9 Mix nine concentrations from 3.15 to 30,000 nl per plate were tested. The test compound was dissolved at all concentrations. No mutagenicity was observed with the test compound under all these conditions. This was also the case when an epoxide hydratase inhibitor was added to the S-9 Mix in order to increase the sensitivity of the test towards compounds which are activated to mutagenic epoxides (this experiment was performed with TA 98). Since a reduction of the his background lawn was not evident even at the highest dose of N-methylpyrrolidone, an overshadowing of a possible mutagenicity by toxicity is unlikely.
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