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EC number: 204-500-1 | CAS number: 121-82-4
- 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 vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: It is a GLP study following international guidelines and has been published in a peer reviewed journal.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2005
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Perhydro-1,3,5-trinitro-1,3,5-triazine
- EC Number:
- 204-500-1
- EC Name:
- Perhydro-1,3,5-trinitro-1,3,5-triazine
- Cas Number:
- 121-82-4
- Molecular formula:
- C3H6N6O6
- IUPAC Name:
- 1,3,5-trinitro-1,3,5-triazinane
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: well known breeder
- Age at study initiation:
- Weight at study initiation:
- Assigned to test groups randomly: [no/yes, under following basis: ]
- Fasting period before study:
- Housing:
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C):18-26°C
- Humidity (%):30% to 70%
- Photoperiod (hrs dark / hrs light):12hrs dark /12 hrs light
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil
- Concentration of test material in vehicle:
- Amount of vehicle (if gavage or dermal): 10ml/kg
- Lot/batch no. (if required):lot no. 12-394
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Test article wasdissolved in corn oil - Duration of treatment / exposure:
- 24h and 48h
- Frequency of treatment:
- single dose
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
62.5 mg/kg
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
125 mg/kg
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
250 mg/kg
Basis:
actual ingested
- No. of animals per sex per dose:
- 5 males/dose for the negative and positive control and the 62.5 and 125 mg/kg and 10/sex/dose for the 250 mg/kg
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide in sterile deionized water
- Route of administration: gavage
- Doses / concentrations: 80mg/kg
Examinations
- Tissues and cell types examined:
- Bone marrow. micronuclei in polychromatic erythrocytes (PCEs) and norchromatic erythrocytes (NCEs)
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:Based upon the result of the dose range-finding study, the estimated maximum tolerated doses was 250 mglkg after one oral gavage administration
SAMPLING TIMES ( in addition to information in specific fields): 24h and 48h
DETAILS OF SLIDE PREPARATION:Bone marrow smears were prepared and allowed to air dry. The slides were then fixed in methanol, stained in May-Grunwald-Giemsa stain and protected by permanently mounted cover slips.
METHOD OF ANALYSIS:The slides were blind scored for micronuclei in polychromatic erythrocytes (PCEs) and norchromatic erythrocytes (NCEs) and determination of PCE/NCE ratios to access possible bone marrow cytotoxicity.
The micronucleus frequency (expressed as percent micronucleated cell) wasdetennlned by analyzing number of micronucleated PCEs from at least 2000 PCEs per animal. The PCE:NCE ratio was determined by scoring the number of PCEs and NCEs observed while scoring at least the first 500 erythrocytes per animal. - Evaluation criteria:
- The criteria for the identification of micronuclei were those of Schmid (1976).
- Statistics:
- Yes but no details
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Remarks:
- (no significant decreases in the PCE:NCE ratios observed at any RDX dose or bone marrow sampling time point)
- Toxicity:
- no effects
- Remarks:
- no effects RDX at doses 62.5, 125, and 250 mg/kg were not cytotoxic to bone marrow (i.e.no statistically significant decrease in PCE:NCE ratios)
- Vehicle controls validity:
- valid
- Negative controls validity:
- not specified
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: up to 500 mg/kg
- Clinical signs of toxicity in test animals: Mice dosed at all dose levels showed neurotoxic signs (hyperactive) and deaths at high dose of 500 mg/kg.
Any other information on results incl. tables
Summary data from micronuleus assay for RDX in bone marrow of CD-l mouse
*Significantly greater than the corresponding vehicle control,P =0.01 CP = cyclophosphamide. PCE = polychromatic erythrocyte. NCE = normochromatic erythrocyte. |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
RDX was found to be negative in the in vivo mouse bone marrow micronucleus assay.
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