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EC number: 202-928-3 | CAS number: 101-25-7
- 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 somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Evaluation of some formaldehyde-release compounds and other biocides in the mouse micronucleus test
- Author:
- C.R. Richardson, J.A. Styles and B. Burlinson
- Year:
- 1 983
- Bibliographic source:
- Mutation Research, 124 (1983) 241-246 (Elsevier)
Materials and methods
- GLP compliance:
- not specified
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- 3,7-dinitroso-1,3,5,7-tetraazabicyclo[3.3.1]nonane
- EC Number:
- 202-928-3
- EC Name:
- 3,7-dinitroso-1,3,5,7-tetraazabicyclo[3.3.1]nonane
- Cas Number:
- 101-25-7
- Molecular formula:
- C5H10N6O2
- IUPAC Name:
- 3,7-dinitroso-1,3,5,7-tetraazabicyclo[3.3.1]nonane
- Test material form:
- solid
- Details on test material:
- - Chemical name: Dinitrosopentamethylenetetramine
- CAS: 101-25-7
- EC: 202-928-3
- MW: 186.17 g/mol
- pale yellow crystalline powder
Constituent 1
- Specific details on test material used for the study:
- DNPT supplied by Organics Division, ICI PLC, Blackley, Manchester, Great Britain
Test animals
- Species:
- mouse
- Strain:
- C57BL
- Remarks:
- /6J
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- ANIMALS
Male C57Bl/6J mice (6-8 weeks old) were used for both the main study and the LD50 determinations.
HUSBANDRY
On arrival the mice were housed 5 per cage on mobile mouse racks and given food (Porton Combined Diet [PCD] supplied by BP Nutrition Ltd., Stepfield, Witham, Essex, Great Britain) and water ad libitum.
The animal cell was maintained at a mean temperature of 21°C (range 20-22°C), a relative humidity mean of 44% (range 29-58%) with 22 air changes/h.
Lighting was cycled with 12 h light and 12 h dark each 24 h.
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- not specified
- Details on exposure:
- Animals were dosed with 2 consecutive daily doses administered 24 h apart using doses equivalent to 80% and 50% of the LD50/7 by intraperitoneal injection.
The lower dose level was used to ensure a test result in the event of deaths in the top-dose group and to provide additional data in the event of a positive result. - Duration of treatment / exposure:
- 24 h
- Frequency of treatment:
- 2 consecutive daily doses administered 24 h apart
- Post exposure period:
- 24-48 h
Doses / concentrations
- Dose / conc.:
- 160 other: mg/kg
- No. of animals per sex per dose:
- - Negative control a: 10 (24h) / 11 (48h)
- DNPT: 7 (24h) / 6 (48h)
- Positive control: 9 (48h) - Control animals:
- yes
- Positive control(s):
- Cyclophosphamide (75 mg/kg)
Examinations
- Tissues and cell types examined:
- polychromtic erythrocytes (PCEs) from bone marrow (femur)
- Details of tissue and slide preparation:
- The animals were killed by cervical dislocation either 24 or 48 h after the last dose of compound. Femurs were removed and stripped clean of muscle. The iliac end of the femur was removed and a fine paint brush wetted with a solution of albumen (6% w/v in water) was dipped into the marrow canal. 3-4 streaks of marrow suspension were then applied to appropriately labelled clean dry microscope slides.
The slides were allowed to air-dry and then stained in Leishman's stain using an Ames Hema-Tek staining machine (Miles Laboratories Inc., Ames Division, Stoke Court, Stoke Poges, Slough, Bucks., Great Britain). Slides were coded and scored blind: 500 polychromatic erythrocytes (PCEs) were examined for each animal and the number containing micronuclei scored. The ratio of polychromatic to mature erythrocytes was also determined as a measure of cytotoxicity.
Slides prepared from animals dosed at 50% of the LD50/7 were removed before coding. In the event of a positive result being observed with any of the test chemicals, the relevant slides from the low-dose groups were randomised with positive and negative control slides and scored for the presence of micronuclei. - Statistics:
- The results were analysed for significant differences from the control groups using a one-sided Student's ' t ' test.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- 80% of the LD50 based on preliminary toxicity test
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- DNPT gave negative results at both the sampling times used.
The system positive control (cyclophosphamide) gave a greatly elevated and statistically significant increase in micronuclei.
Any other information on results incl. tables
Incidence of micronuclei/1000 cells (2 sampling times)
Substance | Dose | 24h sampling | 48h sampling |
NC (Control a) | 1.6 +/- 2.1 | 1.4 +/- 1.6 | |
DNPT | 160 mg/kg | 1.4 +/- 1.5 | 1.3 +/- 1 |
PC (Cyclophosphamide) | 75 mg/kg | - | 64.1 +/- 18 |
There was no undue influence of cytotoxicity on the results generated, since the ratios of PCEs to mature erythrocytes did not deviate from the normally expected range.
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of this test, the test item did not show clastogenic activity.
- Executive summary:
A number of biocidal chemicals were tested for clastogenic activity in the micronucleus test using C57Bl/6J mice.
N, N-dinitrosopentamethylenetetramine (DNPT) was tested as the negative control.
DNPT did not increase the incidence of micronuclei.
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