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EC number: 213-382-0 | CAS number: 941-69-5
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1985
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: test guideline is not identified but according to OECD407. Study was not performed to GLP and no FOB was undertaken.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- Deviations:
- yes
- Remarks:
- test period: 5 days 6 weeks
- Principles of method if other than guideline:
- exposure period: 30 days instead of 14 or 28 days defined by OECD 407
- GLP compliance:
- no
- Limit test:
- no
Test material
- Reference substance name:
- N-phenylmaleimide
- EC Number:
- 213-382-0
- EC Name:
- N-phenylmaleimide
- Cas Number:
- 941-69-5
- Molecular formula:
- C10H7NO2
- IUPAC Name:
- 1-phenyl-2,5-dihydro-1H-pyrrole-2,5-dione
- Details on test material:
- purity: >99.9%
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: arabic gum
- Details on oral exposure:
- test substance was suspended in 5% (w/v) arabic gum water solution
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 30 days
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 3.5, 11.0, 35.0 mg/kg/day
Basis:
actual ingested
- No. of animals per sex per dose:
- 10
- Control animals:
- other: concurrent no treatment and concurrent vehicle
- Details on study design:
- Post-exposure period: none
Examinations
- Observations and examinations performed and frequency:
- General symptoms and measurement of BW: observed everyday and measured 3 times a week.
Food and water intakes: measured once a week.
Urinalysis: animals were fasted for 10 and several hours after the final administration.
Hematological examination: same as above.
weights of organs and histopathological examination: all rats were autopsied after blood collection. - Statistics:
- t-test
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- effects observed, treatment-related
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- effects observed, treatment-related
- Details on results:
- 1. Depressed weight gain observed in both sexes of 35 mg/kg group is attributed to loss of appetite due to marked injury in the stomach mucous membrane in comparison with other drug-treated groups.
Depressed appetite reduced food intake and induced emaciation as a general symptom.
Water intake of this group fluctuated more largely than those for other groups.
This fluctuation is attributable to secretion of gastric juice and nausea resulting from changes in the stomach.
2. Hematological examination revealed reduced hemoglobin level indicating hypochromic blood in 35 and 11 mg/kg groups.
Leucocyte count was increased or tended to be increased in the groups.
This change is thought to be an inflammatory reaction due to gastritis.
In particular, increased neutrophil count in 35 mg/kg group is compatible with histopathological findings.
3. Of results of blood chemical examination, the rise of GOT value in 35 and 11 mg/kg groups is remarkable.
This elevation is attributable to inflammatory reaction due to gastritis.
The elevating tendancy of potassium level in the 2 groups are thought to result from destruction of tissues relationg to gastritis.
In particular, the level was slightly elevated in 35 mg/kg group in which marked changes were observed in the forestomach and glandular stomach.
The chrolide level was higher in 35 mg/kg groupshowing serious injury in the glandular stomach than in other drug-related groups.
It is presumed that there is some relationship between this elevation and secretion of gastric juice.
The change in the creatinine level varied between males and females.
The relation between this finding and test material was unclear.
The levels of total protein and glucose were markedly fell in both sexes of 35 mg/kg group.
These low levels are attributable to decreased food intake resulting from symptoms of gastritis which were revealed by histopathogical examination.
The change in A:G ratio is also a result of aggravated nutrition and biological response.
4. As to weights of organs, absolute weights in males of 35 mg/kg group were reduced due to aggravated nutrition.
The increase in relative weights is explained by that aggravated nutrition affected the fatty tissue of the body more greatly than organs.
In females, while absolute weights were unchanged, relative weights were increased.
The increase is attributed to weight loss due to decreased food intake.
5. Of histopathological findings, changes in the atomach mucous membrane were remarkable.
As described above the changes were very severe in 35 mg/kg group and relatively slight in 11 mg/kggroups.
In 3.5 mg/kg group, slight simptoms of gastritis were found in half of males, and the changes tended to be improved in some rats.
In females no changes were observed.
These results of various examinations are correlated one another and indicate changes caused by administration of the test material.
On the basis of these resuls, the test material is thought to be irritative to the mucous membrane in the body.
The maximum non-effective dose is presumed to be about 3.5 mg/kg for both sexes.
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 3.5 other: mg/kg
- Based on:
- test mat.
- Sex:
- male/female
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- It is concluded from the resuls of the present study that the test material, N-phenyl maleimide, induces toxic changes due to irritation.
The maximum non-effective dose is presumed to be 3.5 mg/kg in oral administration.
It is thought that safety can be assured by preventing the test material from entering into the body. - Executive summary:
In a subchronic toxicity study.PMI provided byNIPPON SHOKUBAI on 1984.08.20 was administered to SPF SD rats four weeks /male and female/dose in susupendid 5 (w/v) % aranbic gum water solution, by gavage at dose levels of 0, 3.5, 11.0, 35.0 mg/kg bw/day.
PMI induces toxic changes due to irritation.
The NOAEL is 3.5 mg/kg/day based on irritative property in Rats by the 30 days oral administration.
There is another screening study by OECD 422, this sudy's result shows irritative property of this substance causes local effects but absence of systemic effects. On the view point of the endpoint on repeat toxicity consideration, male' adverse effect during 51 days exposure is effective but female's adverse effect during this exposure period is not reliable due to maternal toxicity in this combined repeat dose and reproductive/developmental toxicity screening study.
The NOEL and LOAEL for oral repeat dose in male is 2.5 mg/kg/day by using OECD 422 test method
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