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EC number: 231-391-8 | CAS number: 7529-22-8
- 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 cell study: DNA damage and/or repair
- Remarks:
- Type of genotoxicity: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From September 6, 1989 to October 18, 1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 989
- Report date:
- 1989
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 486 (Unscheduled DNA Synthesis (UDS) Test with Mammalian Liver Cells in vivo)
- Deviations:
- yes
- Remarks:
- No exposure time of 12-16 h was taken into account.
- GLP compliance:
- yes
- Type of assay:
- unscheduled DNA synthesis
Test material
- Reference substance name:
- 4-methylmorpholine 4-oxide, monohydrate
- EC Number:
- 231-391-8
- EC Name:
- 4-methylmorpholine 4-oxide, monohydrate
- Cas Number:
- 7529-22-8
- Molecular formula:
- C5H11NO2
- IUPAC Name:
- 4-methyl-4λ⁵-morpholin-4-one
Constituent 1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 89-009-1
- Substance type: Light yellow liquid
- Physical state: Liquid
- Purity: responsibility of the sponsor and recorded in the sponsor's file
- Stability: responsibility of the sponsor and recorded in the sponsor's file
- Storage condition of test material: At ambient temperature
- Other: specific gravity 1.1359 g/ml
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Kingston, NY
- Age at study initiation: twelve week old young adult Fischer 344 rats
- Weight at study initiation: 194-244 grams
- Fasting before study
- Housing: Animals were housed in accordance with the "Guide for the Care and Use of Laboratory Animals"
- Acclimation period: 20 days prior to initiation of the assay
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 °C ± 3°C
- Humidity (%): 30 to 70%
- Photoperiod (hrs dark / hrs light): 12 hour light/dark cycle
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: distilled water
- Amount of vehicle: 10 ml/kg - Details on exposure:
- Dilutions were made just prior to use.
- Duration of treatment / exposure:
- 3 hours
- Frequency of treatment:
- Single dose
- Post exposure period:
- Not applicable
Doses / concentrationsopen allclose all
- Dose / conc.:
- 920 mg/kg bw/day (nominal)
- Dose / conc.:
- 2 300 mg/kg bw/day (nominal)
- Dose / conc.:
- 4 600 mg/kg bw/day (nominal)
- Dose / conc.:
- 9 200 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 3
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Dimethylnitrosamine, via oral gavage at 10 mg/kg.
Examinations
- Tissues and cell types examined:
- The liver was excised and examined.
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
Sponsor recommended that the high dose be 1.0 x LD50 in rats (9200 mg/kg) as an estimate of the maximum tolerated dose. Three lower doses were also evaluated at 920, 2300 and 4600 mg/kg as well as the solvent control, dH2O and the positive control, DMN, at 10 mg/kg.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
Eighteen male Fischer 344 rats were anesthetized with 50 mg/kg of sodium pentobarbital by intraperitoneal injection. The liver was excised and placed in 50 mL of warm serumless WME in a sterile culture dish. The liver was trimmed of fat, excess connective tissue and any sections of liver that still showed signs of blood. The liver was then transferred to a sterile (100 x 25 mm) culture dish containing 50 mL of warm Medium B. The liver was held by the connective tissue in the porta hepatis and the capsular membrane of the liver was opened and removed at several points on the dorsal surface with the aid of a scalpel and forceps. Cells were detached by gently combing the liver with a 3/4" camel's hair brush. Detachment was complete when only fibrous tissue remained. The cells were then aliquotted into a 50 mL centrifuge tube by pipetting gently with a sterile 10 mL polystyrene pipet. The volume of the tube was adjusted to 35-40 mL with WME supplemented with 10% v/v calf serum. The tube was allowed to stand in a vertical position for 10 minutes to flocculate the hepatocytes. Viability of the resuspended hepatocytes was measured by trypan blue dye exclusion.
DETAILS OF SLIDE PREPARATION: 1 x 1E05 viable hepatocytes were inoculated into 12 well cluster dishes containing 15 mm diameter Thermanox plastic coverslips in WME containing 10% calf serum. The hepatocytes were allowed to attach for approximately 2hours in a 37°C incubator. The cultures were rinsed with serum-free medium and refed with WME containing 10 uC/mL of 3H-thymidine and incubated. Four hours after exposure, the cultures were washed once with 2 mL WME and incubated overnight in 3 mL of WME supplemented with 0.25 mM unlabeled thymidine. Fourteen to sixteen hours after incubation, the cultures were washed three times with 3 mL volumes of phosphate buffered saline by aspiration.
Cell fixation: The cells on coverslips were swelled in 1% sodium citrate for 10-15 minutes and fixed in three 10-minute changes of 100% ethanol:glacial acetic acid (3:1). The fixed cultures were then washed twice with approximately 2 mL volumes of dH2O. The coverslips were air dried and mounted cell surface up on glass slides with permount. Slides were dipped in NTB-2 photographic emulsion in the dark, allowed to dry overnight and stored at 4°C in light-proof slide boxes containing desiccant for one week.
Staining: After seven days of exposure time, the autoradiographs were developed in D19 at approximately 15°C for 4 minutes, washed in deionized water with 5 mL glacial acetic acid for 30 seconds, immersed in Fixer for 10 minutes, washed in running tap water for 5 minutes and dried. They were then stained in Harris Alum hematoxylin followed by a dip rinse in acid alcohol, rinsed in running tap water for 2-5 minutes and a dip rinse in ammonium water. The slides were then rinsed in running tap water for 2-5 minutes, dipped in 70% ethyl alcohol followed by a 10-60 second dip in eosin solution. The slides were then rinsed in 3 separate baths of 95% ethyl acohol for 2 minute intervals, followed by rinsing in 3 separate baths of 100% ethyl alcohol for 2 minute intervals. The slides were air dried, and coverslipped in permount. Excess emulsion was scraped off.
METHOD OF ANALYSIS: Unscheduled DNA repair synthesis, evidenced by a net increase in black silver grains over the nucleus, is quantified by determining nuclear and cytoplasmic grain counts using an Artek 880 automated colony counter with microscopic/video camera attachment interfaced to an Apple II computer for data acquisition. A total of 450 cells/dose point (50 cells/coverslip, 3 coverslips/rat and 3 rats/dose point) were counted for autoradiographic UDS determination. Slides were coded before being counted. A correction coefficient was calculated by th following method. An area/grain ratio was obtained by visually scoring an area of each slide containing 3-5 nuclear grains and then obtaining an object area count with Artek Model 880 Colony Counter. Five such areas were scored, the differences summed and the mean obtained. This value serves as a correction coefficient. The cytoplasimc grain count was quantitated by randomly selecting the highest of three nuclear-sized areas adjacent to each nucleus. This value was subtracted from the uncorrected nuclear grain count to determine the net nuclear grain count. Both nuclei of binucleated cells were recorded separately. Replicative DNA synthesis was evidenced by nuclei blackened with grains too numerous to count. The data of the HPC/DNA Repair Assay are reported as mean grains/nucleus from the triplicate wells. The solvent control should have a net nuclear grain count of < or = 0 or the study will be repeated. Also the positive control, DMN, should yield a mean net nuclear grain count > or = 5. - Evaluation criteria:
- The test article is reported positive when the minimum net grain count of 5 per nuclei is consistently observed in triplicate wells. Where possible a dose response profile should be observed. When an adequate dose response is not attained, the chemical may be classified as a "suspect" genotoxicant. To resolve the genotoxic potential of the chemical, the sponsor may choose to initiate a second experiment with dose levels closely bracketing the positive response which resulted in classifying the chemical as a "suspect" genotoxicant.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- None of the treated cultures produced mean net nuclear grain counts that were substantially greater than the solvent control. The positive control DMN gave a mean net nuclear grain count greater than the solvent control.
Applicant's summary and conclusion
- Conclusions:
- The substance was negative in inducing unscheduled DNA synthesis in the liver of Fischer 344 rats in vivo at doses of 920, 2300, 4600 and 9200 mg/kg.
- Executive summary:
In an in vivo unscheduled DNA synthesis assay in the liver, performed equivalent/similar to OECD TG 486, 4-methylmorpholine 4-oxide in distilled water was administered to Fischer 344 rats as a single dose via oral gavage at dose levels of 920, 2300, 4600 and 9200 mg/kg bw for 3 hours.
The test material was tested up to doses exceeding the limit dose of 2000 mg/kg bw.
The positive control dimethylnitrosamine (DMN at 10 mg/kg bw) gave a mean net nuclear grain count greater than the solvent control and therefore induced the appropriate response.
None of the treated cultures produced mean net nuclear grain counts that were substantially greater than the solvent control.
There was no evidence that unscheduled DNA synthesis as determined by radioactive tracer procedures was induced.
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