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EC number: 946-134-1 | CAS number: 164651-56-3
- 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:
- other: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- From November 28 to January 23, 2003
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- The test was conducted by means of Read Across approach. The reliability of the source study report is 1. Further information was attached at section 13
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
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:
- micronucleus assay
Test material
- Reference substance name:
- Acid Green 073:2 - Similar Substance 02
- IUPAC Name:
- Acid Green 073:2 - Similar Substance 02
- Test material form:
- not specified
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- 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: Approximately 6 weeks
- Weight at study initiation: Male animals-mean = 181.4 g (= 100 %) (min = 173 g, max = 191 g); female animals- mean = 146.5 g (=100 %) (min = 140 g, max = 154 g)
- Assigned to test groups randomly: Yes
- Housing: Five animals per cage in transparent macrolon cages (type IV) on soft wood granulate in an air conditioned room.
- Diet (e.g. ad libitum): Rat/mice diet ssniff R/M-H (V 1534), ad libitum, ssniff® GmbH, Postbox 2039, 59480 Soest
- Water (e.g. ad libitum): Tap water in plastic bottles, ad libitum
- Acclimation period: 5 d under study conditions
- Animal identification: Fur marking with KMnO4 and cage numbering
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C (except short lasting deviations due to disturbances of air condition)
- Humidity (%): 50% (except short lasting deviations due to disturbances of air condition)
- Photoperiod (hrs dark / hrs light): 12 h light/dark cycle
IN-LIFE DATES: From December 03, 2002 to December 05, 2002
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: deionised water
- Concentration of test material in vehicle: 200 mg/mL
- Amount of vehicle (if gavage or dermal): 10 mL/kg bw - Details on exposure:
- PREPARATION OF DOSING SUSPENSION: On the day of first administration the test substance was dissolved in deionized water at an appropriate concentration.
A magnetic stirrer was used to keep the preparation homogeneous until dosing had been completed.
Stability and homogeneity in the vehicle : guaranteed for 96 hours in deionized water by the sponsor (archived with the raw data) - 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
- No. of animals per sex per dose:
- 5 per sex per group.
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Positive control: Cyclophosphamide
Dissolved in: distilled water
Dose: 40 mg/kg bw
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 normochromatic 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 2000 counted erythrocytes. - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: No preliminary experiments were performed, as corresponding toxicological information was available. Since 5000 mg per kg body weight resulted in no lethality in acute oral toxicity testing a limit test with 2000 mg per kg body weight was performed.
.
-Extraction of the bone marrow: Animals were killed by carbon dioxide asphyxiation 24 h after dosing. One femora was removed and the bone freed of muscle tissue. The proximal end of the femora was opened, the bone marrow flushed into a centrifuge tube containing about 3 mL of fetal bovine serum and a suspension was prepared. The mixture was then centrifuged for 5 minutes at approximately 1200 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 slides were stained as follows:-
-5 minutes in methanol
-5 minutes in May-Grunwald'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 as positive if there is a significant dose- related increase in the number of micronucleated polychromatic erythrocytes compared with the concurrent negative control group. A test substance producing no significant dose-related increase in the number of micronucleated polychromatic erythrocytes is considered non-clastogenic in this system.
- Statistics:
- Assuming the study is valid based on a monotone-dose-relationship, one-sided Wilcoxon tests were performed initially comparing control values with those of the highest dose group. A significance level of 5% is adopted for all tests.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Remarks:
- Exposure was assured by the presence of light grey coloured tissues at necropsy
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- All animals survived after treatment. No signs of toxicity were detected. All dosed animals showed black discoloured faeces and Body surface showed grey discolorations which were noted on hairless areas 24 hours after the first administration up to the end of study.
The dissection of the animals revealed a nearly black coloured content of the gastro-intestinal tract and light grey coloured tissues.
The bone marrow smears were examined for the occurrence of micronuclei in red blood cells. The incidence of micronucleated polychromatic erythrocytes in the test tem-treated groups was within the normal range of the negative control groups (mean of micronucleated polychromatic erythrocytes per 2000 cells: 1.7 — 4.9). No statistically significant increase in micronucleated polychromatic erythrocytes was observed. The ratio of polychromatic erythrocytes to total erythrocytes remained essentially unaffected by the test compound and differed less than 20% from the control values.
Cyclophosphamide (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:
- Not clastogenic
- Executive summary:
Method
The study was conducted to investigate the potential of the test substance to induce micronuclei in polychromatic erythrocytes (PCE) in the bone marrow of the rat according to OECD Guideline 474, EPA OPPTS 870.5395 and EU Method B.12, in compliance with GLP.
The test compound was dissolved in deionized water and was given twice at an interval of 24 hours as oral doses of 2000 mg per kg body weight to male and female rats (Hsd:Sprague Dawley). At study start the animals were 6 weeks of age and had mean body weights of 181.4 g (M) and 146.5 g (F). According to the test procedure the animals were killed 24 hours after the last administration.
Endoxan® was used as positive control substance and was administered once orally at a dose of 40 mg per kg body weight.
Observations
The number of polychromatic erythrocytes containing micronuclei was not significantly increased compared with the control. The ratio of polychromatic erythrocytes to total erythrocytes in both male and female animals remained unaffected by the treatment with the test substance and differed less than 20 % from the control value.
Endoxan®induced a marked statistically significant increase in the number of polychromatic cells with micronuclei, indicating the sensitivity of the test system. The ratio of polychromatic erythrocytes to total erythrocytes was not changed to a significant extent.
Conclusions
Under the conditions of the present study the results indicate that the test substance is not clastogenic in the micronucleus testin vivo.
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