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EC number: 296-665-1 | CAS number: 92908-36-6
- 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 somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 25 AUG 2010 to 28 SEP 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 011
- Report date:
- 2011
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- During the acclimation phase of the animals used for the pre-experiment the relative humidity was between 45 ¿ 71 % for a maximum of 9 hours.
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- During the acclimation phase of the animals used for the pre-experiment the relative humidity was between 45 ¿ 71 % for a maximum of 9 hours.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- in accordance to German Chemikaliengesetz and Directive 2004/9/EEC
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Urea, reaction products with formaldehyde, glyoxal and methanol
- EC Number:
- 296-665-1
- EC Name:
- Urea, reaction products with formaldehyde, glyoxal and methanol
- Cas Number:
- 92908-36-6
- Molecular formula:
- C2 H2 O2 .C H4 N2 O .C H4 O .C H2 O
- IUPAC Name:
- Urea, reaction products with formaldehyde, glyoxal and methanol
- Test material form:
- liquid: viscous
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Batch No.of test material: OP1
- Expiration date of the lot/batch: October 16, 2014
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Sulzfeld, Germany
- Age at study initiation: 8 to 12 weeks
- Weight at study initiation: males mean: 37.6 g (SD +/- 1.8 g)
- Assigned to test groups randomly: yes
- Housing: single in Makrolon cages Type II/III, with wire mesh top
- Diet: pelleted standard diet (Harlan Laboratories B.V., AD Horst, The Netherlands), ad libitum
- Water: community tap water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24
- Humidity (%): 45-71
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle used: sterile water
- dose volume: 10 mL/kg bw
- Justification for choice of vehicle: relative non-toxicity. - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
- test material was dissolved in sterile water on the day of the experiment
- analysis of concentration, homogeneity and stability was not performed
JUSTIFICATION FOR ROUTE OF EXPOSURE:
Oral application is appropriate since Dimethylol dihydroxyethylene urea, a substance with similar structure, is well absorbed from the gastrointestinal tract, through the skin and from the blood circulation, and more than 90% is excreted unchanged in the urine. Thus there is no evidence that the substance, or reactive metabolites, will not reach the target tissue
- Duration of treatment / exposure:
- 0, 500, 1000 and 2000 mg/kg group: 24 hrs
2000 mg/kg group: 48 hrs - Frequency of treatment:
- single
- Post exposure period:
- none
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 7 males per dose and exposure duration
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - cyclophosphamide
- Route of administration: orally, once
- Doses / concentrations: 40 mg/kg
- Exposure duration: 24 hrs
Examinations
- Tissues and cell types examined:
- bone marrow cells from the femur
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
- maximum recommended dose level and two lower dose levels
- since no gender differences occurred in the pre-experiment on toxicity the main study was performed using male animals only
DETAILS OF SLIDE PREPARATION:
- femur was dissected from each animal, aspirated with foetal calf serum and bone marrow smears were prepared following centrifugation and re-suspension. Smears were air-dried and stained with May-Grünwald/Giemsa. Cover slips were mounted with EUKITT. At least one slide was made from each bone marrow sample.
METHOD OF ANALYSIS:
- blind examination with light microscopy (coded slides, NIKON microscopes with 100x oil immersion objectives)
- Per animal 2000 polychromatic erythrocytes (PCE) were analysed for micronuclei.
- To describe a cytotoxic effect the ratio between polychromatic and normochromatic erythrocytes was determined in the same sample and expressed in polychromatic erythrocytes per 2000 erythrocytes. - Evaluation criteria:
- A test item is classified as mutagenic if:
- it induces either a dose-related increase or
-a clear increase in the number of micronucleated polychromatic erythrocytes in a single dose group.
A test item that fails to produce a biological relevant increase in the number of micronucleated polychromatic erythrocytes is considered non-mutagenic in this system. - Statistics:
- nonparametric Mann-Whitney test
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range:2000 mg/kg bw, oral
- Clinical signs of toxicity in test animals: neither male nor female animals expressed any toxic reactions
RESULTS OF DEFINITIVE STUDY
GENOTOXICITY
- PCEs with Micronuclei (%):
group mean for control group: 0.114;
- treatment groups did not deviate significantly
- 500 mg/kg bw 24 hrs: 0.107
- 1000 mg/kg bw 24 hrs: 0.071
- 2000 mg/kg bw 24 hrs: 0.121
- 2000 mg/kg bw 48 hrs: 0.093
positive control gave expected result:
- 40 mg/kg bw 24 hrs: 1.829
CYTOTOXICITY
(ratio between PCE and NCE was determined in the same samples and reported as no. of PCEs per 2000 erythrocytes, fesults are presented below)
- control group: 1176
- 500 mg/kg bw 24 hrs: 1113
- 1000 mg/kg bw 24 hrs: 1123
- 2000 mg/kg bw 24 hrs: 1226
- 2000 mg/kg bw 48 hrs: 1172
positive control:
- 40 mg/kg bw 24 hrs: 1122
Any other information on results incl. tables
There was no statistically significant increase in the frequency of micronucleated PCE's and in the PCE/NCE ratio in any dose group when compared to the concurrent vehicle control groups.
The positive control goup showed a marked increase in the incidence of micronucleated PCE.
Applicant's summary and conclusion
- Conclusions:
- The test item was considered to be non-genotoxic under the conditions of this in vivo micronuclei assay.
- Executive summary:
Genetic toxicity of the test item has been investigated in an in vivo micronucleus assay in male NMRI mice (7 per dose group). The test item was administered once orally at the maximum recommended dose level of 2000 mg/kg bw, with 1000 and 500 mg/kg bw as the two lower dose levels. Animals were killed 24 or 48 hours later. Evaluation of polychromatic (PCE) or normochromatic (NCE) erythrocytes did not reveal any evidence of an increase in the incidence of micronucleated cells. No significant change in the PCE/NCE ratio was observed after dosing with the test item, and no signs of systemic toxicity were observed in animals dosed with the test item. The positive control material produced a marked increase in the frequency of micronucleated PCE. The test material was considered to be non-genotoxic under the conditions of the test.
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