Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 432-550-6 | CAS number: 243858-01-7
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
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 September 27, 1999 to November 26, 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- -
- EC Number:
- 432-550-6
- EC Name:
- -
- Cas Number:
- 243858-01-7
- Molecular formula:
- Hill formula: C25H22FN7Na4O16S5 CAS formula: C25H26FN7O16S5.4Na
- IUPAC Name:
- tetrasodium 2-({4-fluoro-6-[methyl({2-[2-(sulfonatooxy)ethanesulfonyl]ethyl})amino]-1,3,5-triazin-2-yl}amino)-5-hydroxy-6-[2-(4-methyl-2-sulfonatophenyl)diazen-1-yl]naphthalene-1,7-disulfonate
- Test material form:
- solid: particulate/powder
- Details on test material:
- - Name of test material (as cited in study report): Reaktiv Orange F97-0318
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Winkelmann GmbH, Gartenstrasse 27, 33178 Borchen
- Age at study initiation: Male/female animals approximately 8 weeks
- Body weight range at treatment: Males: 32-40 g; Females: 27-32 g
- Housing: In fully air-conditioned rooms in makrolon cages type 3 (five animals/cage) on soft wood granulate
- Diet: Rat/mice diet ssnif R/M-H (V 1534), ad libitum
- Water: Tap water in plastic bottles, ad libitum
- Acclimation period: 5 d under study conditions
- Animal identification: Fur marking with KMn04 and cage numbering
- Randomization procedure: Randomization schemes 1999.0432 and 1999.0433
ENVIRONMENTAL CONDITIONS
- Temperature: 22±3°C
- Humidity: 50±20%
- Photoperiod: 12 h light/dark cycle
IN-LIFE DATES: From: To: September 27, 1999 to November 26, 1999
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: Deionized water
- Concentration of test material in vehicle: 20% (w/v)
- Amount of vehicle (if gavage or dermal): 10 mL/kg bw - Details on exposure:
- PREPARATION OF DOSING SUSPENSION: On the days of administration the test substance was dissolved in deionized water at the appropriate concentration. A magnetic stirrer was used to keep the preparation homogeneous until dosing had been completed.
- Duration of treatment / exposure:
- 2 d
- Frequency of treatment:
- twice at an interval of 24 h
Doses / concentrations
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 5/sex/group
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Positive control: Endoxan® containing cyclophosphamide
Dissolved in: Distilled water
Dose: 50 mg/kg bw
Concentration: 0.5% (w/v)
Route and frequency of administration: Oral (gavage), once
Volume Administered: 10 mL/kg bw
Examinations
- Tissues and cell types examined:
- - 2,000 polychromatic erythrocytes were counted for each animal.
- The number of cells with micronuclei was recorded, not the number of individual micronuclei.
- The ratio of polychromatic erythrocytes to 200 total erythrocytes was determined.
- Main parameter for the statistical analysis, i.e. validity assessment of the study and mutagenicity of the test substance, was the proportion of polychromatic erythrocytes with micronuclei out of the 2,000 counted erythrocytes. - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Based on the results of preliminary dose range finding study the dose of 2,000 mg/kg bw which did not cause any toxic effects in male and female mice over an observation period of 7 d, was selected as the highest dose, for the main study. This selected dose level also represents the limit dose according to the regulations.
-Preparation and Staining: Animals were killed by carbon dioxide asphyxiation 24 h after dosing. For each animal, about 3 mr fetal bovine serum was poured into a centrifuge tube. Both femora were removed and the bones freed of muscle tissue. The proximal ends of the femora were opened and the bone marrow flushed into the centrifuge tube. A suspension was formed. The mixture was then centrifuged for 5 minutes at approximately 1,200 rpm, after which almost all the supernatant was discarded. One drop of the thoroughly mixed sediment was smeared onto a cleaned slide, identified by project code and animal number and air-dried for about 12 h.
-Staining procedure: The staining was performed as follows:
-5 minutes in methanol
-5 minutes in May-Gronwald's solution
-Brief rinsing twice in distilled water
-10 minutes staining in 1 part Giemsa solution to 6 parts buffer solution, pH 7.2 (Weise)
-Rinsing in distilled water
-Drying
-Coating with Entellan - Evaluation criteria:
- Both biological and statistical significances were considered together for evaluation purposes. A test substance is considered positive if there is a significant increase in the number of micronucleated polychromatic erythrocytes compared with the concurrent negative control group. A test substance producing no significant increase in the number of micronucleated polychromatic erythrocytes is considered non-mutagenic in this system.
- Statistics:
- After confirming the validity of the study the following sequential test procedure for the examination of the mutagenicity was applied: Based on a monotone-dose-relationship, one-sided Wilcoxon tests were performed starting with the highest dose group. These tests were performed with a multiple level of significance of 5%.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- orange discolored urine and red discolored feces were observed as clinical signs after administration of test substance
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- - All animals survived after treatment. Orange discolored urine and red discolored feces were observed as clinical signs. 24 h after the applications all animals were free of clinical signs.
- The dissection of the animals revealed no test substance related macroscopic findings.
- The bone marrow smears were examined for the occurrence of micronuclei in red blood cells. The incidence of micronucleated polychromatic erythrocytes in the dose group of test substance was within the normal range of the negative control groups. No statistically significant increase of micronucleated polychromatic erythrocytes was observed. The ratio of polychromatic erythrocytes to total erythrocytes remained essentially unaffected by the test substance and was not less than 20% of the control values.
- Cyclophosphamide (i.e., endoxan) induced a marked and statistically significant increase in the number of polychromatic erythrocytes with micronuclei, thus indicating the sensitivity of the test system
Applicant's summary and conclusion
- Conclusions:
- The test substance did not induce micronuclei in bone marrow cells of mice. Therefore, the test substance was not considered to be mutagenic in this micronucleus assay.
- Executive summary:
A study was conducted to investigate the potential of the test substance to induce micronuclei in polychromatic erythrocytes (PCE) in the bone marrow of HsdWin:NMRI mice according to OECD Guideline 474, EPA OPPTS 870.5395 and EU Method B.12, in compliance with GLP.
The test substance was dissolved in deionized water and given twice at an interval of 24 h as an oral dose of 2,000 mg/kg bw/day to male and female mice. The dose was selected based on the results of a previous dose range finding study. The animals were sacrificed 24 h after the last administration and bone marrow cells were collected for micronuclei analysis.
The positive control (endoxan) induced a marked statistically significant increase in the number of polychromatic cells with micronuclei, indicating the sensitivity of the test system. After treatment with the test substance, the number of polychromatic erythrocytes containing micronuclei was not increased. The ratio of polychromatic erythrocytes to total erythrocytes in both male and female animals remained unaffected and was not less than 20% of the control value.
Under the study conditions, the test substance did not induce micronuclei in bone marrow cells of mice. Therefore, the test substance was not considered to be mutagenic in this micronucleus assay.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
![ECHA](/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/echa_logo.png)