Registration Dossier
Registration Dossier
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: 203-404-7 | CAS number: 106-50-3
- 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
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: This study was selected as the key study because the information provided for the hazard endpoint is sufficient for the purpose of classification and labeling and/or risk assessment.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Remarks:
- The study was conducted according to the guideline in effect at the time of study conduct.
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Details on test material:
- - Purity: 99.8%
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 6 - 10 weeks
- Weight at study initiation at start of treatment:
males mean value 214.6 g (SD ± 10.48 g)
females mean value 172.3 g (SD ± 8.47 g)
- Fasting period before study: not reported
- Housing: singly in Makrolon Type II, with wire mesh top with granulated soft wood bedding
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: minimum 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3°C
- Humidity (%): 30-80 %
- Air changes (per hr): not reported
- Photoperiod (hrs dark / hrs light): artificial light 6.00 a.m. - 6.00 p.m.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle Control
- Name: deionised water
- Route and Frequency of Administration: orally, once
- Volume Administered: 10 mL/kg b.w. - Details on exposure:
- PREPARATION OF TEST SUBSTANCE FORMULATION:
-Solvent used: deionised water
-Preparation frequency: once
-Preparation details: Before preparation, the vehicle was degassed by sonication for at least 15 minutes and then saturated with nitrogen gas, and kept under nitrogen atmosphere for 15 minutes prior to dosing. The test substance dosage forms were prepared under nitrogen atmosphere and were stored prior touse protected from light and under nitrogen atmosphere until delivery, for a maximum period of 5 hours. - Duration of treatment / exposure:
- single oral dose
- Frequency of treatment:
- single oral dose
- Post exposure period:
- 24 and 48 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
25, 50, 100 mg/kg b.w.
Basis:
nominal in water
- No. of animals per sex per dose:
- 6 per sex at each dose level: negative control, low dose, medium dose, high dose and positive control
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - Positive Control
- Name: CPA; Cyclophosphamide
- Supplier: Sigma-Aldrich Vertriebs GmbH
- Catalogue no.: C 0768 (purity: > 98 %)
- Justification for choice of positive control(s): not reported
- Dissolved in: deionised water
- Dosing: 40 mg/kg b.w.
- Route and frequency of administration: orally, once
- Volume administered: 10 mL/kg b.w.
- Solution prepared on day of administration. The stability of CPA at room temperature is sufficient. At 25°C only 3.5 % of its potency is lost after 24 hours.
Examinations
- Tissues and cell types examined:
- PCEs and NCEs from rat bone marrow taken from the femur
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
It is generally recommended to use the maximum tolerated dose or the highest dose that can be formulated and administered reproducibly or 2000 mg/kg as the upper limit for non-toxic test items. The maximum tolerated dose level is determined to be the dose that causes toxic reactions without having major effects on survival within 48 hours. The volume to be administered should be compatible with physiological space available. Three adequate spaced dose levels spaced by a factor of 2 were applied at the central sampling interval 24 hours after treatment. For the highest dose level an additional sample was taken at 48 hours after treatment.
TREATMENT AND SAMPLING TIMES (in addition to information in specific fields):
At the beginning of the treatment the animals (including the controls) were weighed and the individual volume to be administered was adjusted to the animal’s body weight. The animals received the test item, the vehicle or the positive control substance once. Twelve animals, six males and six females, were treated per dose group and sampling time. The animals of all dose groups were examined for acute toxic symptoms at intervals of around 1, 2-4, 6, and 24 hours after administration of the test item. Sampling of the bone marrow was done 24 and 48 hours after treatment, respectively.
DETAILS OF SLIDE PREPARATION:
The nucleated cells were separated from the erythrocytes using the method of Romagna. Briefly, the cell suspensions were passed through a column consisting of α-Cellulose (Sigma) and Cellulose (Sigmacell type 50). The columns were then washed with Hank’s buffered saline. The cell suspension was centrifuged at 1500 rpm (390 x g) for 10 minutes and the supernatant was discarded. The pellet was resuspended in a small drop of FCS and spread on slides. The smear was air-dried and then one slide per animal was stained with May-Grünwald/Giemsa. Cover slips were mounted with EUKITT. At least one slide per animal was stained with acridine orange.
METHOD OF ANALYSIS:
Evaluation of the slides was performed using NIKON microscopes with 100x oil immersion objectives. At least 2000 polychromatic erythrocytes (PCE) were analysed per animal for micronuclei using May-Grünwald/Giemsa and acridine orange stained slides. 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. The analysis was performed with coded slides. Ten animals (5 males, 5 females) per test group were evaluated as described. The remaining 6th animal of each group and sex was evaluated in case an animal of that group died.
OTHER:
The analysis of the test item concentration in blood serum was performed at RCC-ECP under the phase number A26774. For this purpose 3 animals per sex and sampling time were treated at RCC Ltd with radiolabelled test item using the dose corresponding to the high dose of the mutagenicity experiment, i.e. 100 mg/kg. The test item was formulated in degassed deionised water. The volume was as for the mutagenicity experiment 10 mL/kg b.w. 0.5 and 2 hours after the treatment approx. 2 mL of blood was collected via the jugular vein into glass tubes and stored at –60 to -80 °C. Radioactivity in blood was determined by liquid scintillation counting (LSC). - Evaluation criteria:
- A test item is classified as mutagenic if it induced either a dose-related increase or a clear increase in the number of micronucleated polychromatic erythrocytes in a single dose group. However, the primary point of consideration is the biological relevance of the results. A test item that failed to produce a biological relevant increase in the number of micronucleated polychromatic erythrocytes was considered non-mutagenic in this system.
- Statistics:
- Statistical methods (nonparametric Mann-Whitney test) were used as an aid in evaluating the results.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 4 animals (2 males, 2 females) received orally a single dose of 100 mg/kg b.w. test substance formulated in deionised water. The volume administered was 10 ml/kg b.w..
- Clinical signs of toxicity in test animals: reductions of spontaneous activity = 2/2 for all observation times; ruffled fur = 0/0 for all observation times except 2/2 at 6 h; Urine = orange at 2-4 h and 6 h.
- Rationale for exposure: In a GLP study (RCC-CCR study number 902402) performed parallel to this study the toxicity of the test item in Wistar rats after oral (gavage) application was analyzed. The data showed that one out of 4 animals died 24 h after treatment with 150 mg/kg b.w. Thus, the starting dose for the pre-experiment was set at 100 mg/kg b.w.
RESULTS OF DEFINITIVE STUDY
- Clinical signs of toxicity in test animals: See Table 1.
- Summary of Micronucleus Test: See Table 2
- Statistical Significance Data: Biometry: See Table 3
Any other information on results incl. tables
Table 1. Clinical signs of toxicity in test animals |
||||||
Toxic Reactions |
Hours post-treatment (male/female) |
|||||
1 hr |
2-4 hr |
6 h |
24 h
|
48* h |
||
100 mg/kg b.w. (vol administered is 10 ml/kg b.w.) |
Reduction of spontaneous activity |
7/7 |
10/10 |
12/12 |
12/12 |
1/1 |
Ruffled fur |
0/0 |
0/0 |
12/12 |
12/12 |
0/1 |
|
Urine |
– |
orange |
orange |
dark yellow |
– |
|
50 mg/kg b.w. (vol administered is 10 ml/kg b.w.) |
Reduction of spontaneous activity |
0/0 |
3/3 |
3/4 |
0/0 |
N.O. |
Ruffled fur |
0/0 |
0/0 |
4/4 |
3/3 |
N.O. |
|
Urine |
– |
orange |
orange |
dark yellow |
N.O. |
|
25 mg/kg b.w. (vol administered is 10 ml/kg b.w.) |
Reduction of spontaneous activity |
0/0 |
2/3 |
3/3 |
0/0 |
N.O. |
Ruffled fur |
N.O. |
N.O. |
N.O. |
N.O. |
N.O. |
|
Urine |
– |
light orange |
light orange |
– |
N.O. |
|
* = only 6 animals per sex were used N.O. = not observed |
Table 2. Summary of Micronucleus Test Results |
|||||
Test Group |
Dose (mg/kg b.w.) |
Samling Time (h) |
PCEs with micronuclei (%) |
Range |
PCE per 2000 erythocytes |
A. Stained with Giemsa/May-Grünwald |
|||||
Vehicle |
0 |
24 |
0.190 |
1-6 |
1088 |
Test Item |
25 |
24 |
0.115 |
0-4 |
1079 |
Test Item |
50 |
24 |
0.200 |
0-8 |
1081 |
Test Item |
100 |
24 |
0.245 |
1-10 |
983 |
Positive Control |
40 |
24 |
1.145 |
13-35 |
879 |
Vehicle |
0 |
48 |
0.110 |
0-6 |
1035 |
Test Item |
100 |
48 |
0.180 |
0-6 |
1053 |
B. Stained with Acridine |
|||||
Vehicle |
0 |
24 |
0.155 |
1-4 |
1134 |
Test Item |
25 |
24 |
0.230 |
2-7 |
1237 |
Test Item |
50 |
24 |
0.210 |
1-7 |
1107 |
Test Item |
100 |
24 |
0.190 |
0-7 |
1076 |
Positive Control |
40 |
24 |
1.990 |
15-66 |
784 |
Vehicle |
0 |
48 |
0.150 |
0-5 |
1216 |
Test Item |
100 |
48 |
0.145 |
1-6 |
1190 |
Table 3. Statistical Significance Data: Biometry |
||
Vehicle Control vs. Test Group |
Significance |
p |
A. Stained with Giemsa/May- Grünwald |
||
25 mg test substance/kg b.w.; 24 h |
n.t. |
– |
50 mg test substance/kg b.w.; 24 h |
– |
0.5 |
100 mg test substance/kg b.w.; 24 h |
– |
0.2147 |
40 mg CPA/kg b.w.; 24 h |
+ |
< 0.0001 |
100 mg test substance/kg b.w.; 48 h |
– |
0.0627 |
B. Stained with Acridine |
||
25 mg test substance/kg b.w.; 24 h |
+ |
0.0286 |
50 mg test substance/kg b.w.; 24 h |
– |
0.0784 |
100 mg test substance/kg b.w.; 24 h |
– |
0.2719 |
40 mg CPA/kg b.w.; 24 h |
+ |
< 0.0001 |
100 mg test substance/kg b.w.; 48 h |
n.t. |
– |
Notes: Statistical significance at the five per cent level (p < 0.05) was evaluated by means of the non-parametric Mann-Whitney test. – = not significant + = significant; n.t. = not tested, as the mean micronucleus frequency was not above the vehicle control value |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
This study and the conclusions which are drawn from it fulfill the quality criteria (validity, reliability, repeatability). Under the conditions of the study, the test substance did not induce cytogenetic damage leading to micronucleus formation in the bone marrow of rats treated orally up to the maximal tolerated dose of 100 mg/kg, with clear demonstration that treated animals were exposed systemically. Therefore, the test substance was considered to be non-gentoxic in this micronucleus assay. - Executive summary:
This study was performed to investigate the potential of the test substance to induce micronuclei in polychromatic erythrocytes (PCE) in the bone marrow of the rat. The test substance was formulated in degassed deionised water, which was also used as vehicle control. Two vehicle controls (one for 24 h and one for 48 h evaluation) were used. The volume administered orally was 10 mL/kg b.w. 24 h and 48 h after a single administration of the test item the bone marrow cells were collected for micronuclei analysis.
Ten animals (5 males, 5 females) per test group were evaluated for the occurrence of micronuclei. At least 2000 polychromatic erythrocytes (PCEs) per animal were scored for micronuclei. To describe a cytotoxic effect due to the treatment with the test item the ratio between polychromatic and total erythrocytes was determined in the same sample and reported as the number of PCEs per 2000 erythrocytes.
The following dose levels of the test item were investigated: 1) 24 h preparation interval: 25, 50, and 100 mg/kg b.w., 2) 48 h preparation interval: 100 mg/kg b.w. The highest dose (100 mg/kg) was estimated by a pre-experiment to be the maximum tolerated dose.
After treatment with the test item the number of PCEs was not substantially decreased as compared to the mean value of PCEs of the vehicle control thus indicating that the test substance did not exert any cytotoxic effects in the bone marrow. However urine colour of the treated animals was orange to dark yellow indicating the systemic distribution of the test item, thus, confirming its bioavailbility. In addition, rats given 100 mg/kg 14C-test substance with the same regimen showed significant plasma levels 0.5 and 2 hours after compound administration (> 20 μg eg 14C-test substance/g of plasma). In comparison to the corresponding vehicle controls there was no biologically relevant enhancement in the frequency of the detected micronuclei at any preparation interval after administration of the test item and with any dose level used. 40 mg/kg b.w. cyclophosphamide administered orally as positive control showed a substantial increase of induced micronucleus frequency.
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.

Welcome to the ECHA website. This site is not fully supported in Internet Explorer 7 (and earlier versions). Please upgrade your Internet Explorer to a newer version.
This website uses cookies to ensure you get the best experience on our websites.
Find out more on how we use cookies.