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EC number: 284-395-7 | CAS number: 84870-65-5
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Density
- Particle size distribution (Granulometry)
- Vapour pressure
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- Oxidation reduction potential
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- Stability: thermal, sunlight, metals
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- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
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- Endpoint summary
- Stability
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- 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
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- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
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- 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:
- weight of evidence
- Study period:
- 20 November 1987 to 29 January 1988
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 988
- Report date:
- 1988
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- OECD Guidelines for Testing of Chemicals (1981) No. 474 "Genetic Toxicology: Micronucleus Test"
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- other: Micronucleus test
Test material
- Reference substance name:
- 2-[[4-(diethylamino)-2-methylphenyl]azo]-5-nitrobenzene-1,3-dicarbonitrile
- EC Number:
- 284-395-7
- EC Name:
- 2-[[4-(diethylamino)-2-methylphenyl]azo]-5-nitrobenzene-1,3-dicarbonitrile
- Cas Number:
- 84870-65-5
- Molecular formula:
- C19H18N6O2
- IUPAC Name:
- 2-[[4-(diethylamino)-2-methylphenyl]azo]-5-nitrobenzene-1,3-dicarbonitrile
- Test material form:
- solid
Constituent 1
- Specific details on test material used for the study:
- No further details specified in the study report.
Test animals
- Species:
- mouse
- Strain:
- other: albino CFLP
- Details on species / strain selection:
- Thirty-seven male and thirty-seven female albino CFLP strain mice were supplied by Interfauna (UK) Limited, Wyton, Huntingdon, Cambridgeshire.
The results of the test are believed to be of value in predicting the mutagenic potential of the test material to man. The test system was chosen because the mouse has been shown to be a suitable model for this type of study and is recommended in the test method . - Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Thirty-seven male and thirty-seven female albino CFLP strain mice were supplied by Interfauna (UK) Limited, Wyton, Huntingdon, Cambridgeshire. At the start of the main study the males weighed 26 – 29 g, and the females 25 – 29 g, and were approximately five to eight weeks old. After a minimum acclimatisation period of five days the animals were selected at random and given a unique number within the study by ear punching and a number written on a colour coded cage card.
The animals were housed in groups of up to five by sex in solid-floor polypropylene cages with sawdust bedding. With the exception of a 3-4 hour fast immediately before dosing and for approximately two hours after dosing, free access to mains drinking water and food (Rat and Mouse Expanded Diet No. 1, Special Diet Services Limited, Witham, Essex, U.K.) was allowed throughout the study.
The animal room was maintained at a temperature of 20 – 22 °C and relative humidity of 45 - 60%. The rate of air exchange was approximately 15 changes per hour and the lighting was controlled by a time switch to give 12 hours light and 12 hours darkness.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- For the purpose of this study the test material was freshly prepared as required as a suspension at the appropriate concentration in arachis oil B.P.
The vehicle was supplied by C.P. Pharmaceuticals Limited, as follows:
Description: clear, straw-coloured oily liquid
Container: plastic screw-top bottle
Supplier's identification: Oil Arachis B.P.
Batch number: 8611797
Storage conditions: room temperature
The identification and stability of the vehicle control were not determined. - Details on exposure:
- For the purpose of this study the test material was freshly prepared as required as a suspension at the appropriate concentration in arachis oil B.P.
- Duration of treatment / exposure:
- Single treatment/ 24, 48 & 72 hours
- Frequency of treatment:
- One treatment
- Post exposure period:
- Animals were killed 24, 48 or 72 hours after dosing.
Doses / concentrations
- Dose / conc.:
- 5 000 mg/kg bw/day (nominal)
- Remarks:
- maximum practical dose
- No. of animals per sex per dose:
- 30 animals (10 in each test group [5 male/5 female])
30 animals (10 in each vehicle control group [5 male/5 female])
10 animals (positive control [5 male/5 female]) - Control animals:
- yes
- yes, concurrent vehicle
- Positive control(s):
- The positive control material was supplied by Sigma Chemical Company, as follows:
Description: white powder
Container: brown glass screw-top bottle
Supplier's identification: Cyclophosphamide Monohydrate
Batch number: 85F-0054
Date of arrival: 26 June 1987
Storage conditions: + 4 °C in the dark
For the purpose of this study the positive control material was freshly prepared as required as a solution at the appropriate concentration in distilled water.
The identification and stability of the control material and the preparation was not determined.
Route of administration: Oral: gavage
Dose: 50 mg/kg bw
Concentration: 5 mg/mL
Dose volume: 10 mL/kg
Examinations
- Tissues and cell types examined:
- Polychromatic erythrocytes were scored for the presence of micronuclei.
- Details of tissue and slide preparation:
- Immediately following sacrifice (i.e. 24, 48 or 72 hours following dosing), one femur was dissected from each animal, aspirated with foetal calf serum (Flow Laboratories Ltd) and bone marrow smears prepared following centrifugation and re-suspension. The smears were air-dried, fixed in absolute methanol, defatted in xylene and stained in May-Gruenwald/Giemsa.
Evaluation of Slides
Stained bone marrow smears were examined at random using light microscopy at x 1000 magnification. The incidence of micronucleated cells per 1000 polychromatic erythrocytes (blue stained immature cells) per animal was scored. In addition, the number of normochromatic erythrocytes (pink stained mature cells) associated with 1000 polychromatic erythrocytes were counted; these cells were also scored for incidence of micronuclei.
The ratio of normochromatic to polychromatic erythrocytes was calculated together with appropriate group mean values for males and females separately and combined. - Evaluation criteria:
- A comparison was made between the number of micronucleated polychromatic erythrocytes occurring in each of the three test material groups and the number occurring in the corresponding vehicle control groups.
A positive mutagenic response is demonstrated when a statistically significant increase in the number of micronucleated polychromatic erythrocytes is observed for either the 24, 48 or 72 hour kill times.
If the above criteria is not demonstrated, the test material is considered to be non-mutagenic under the conditions of the test.
A positive response for bone marrow toxicity is demonstrated when the treatment group mean normochromatic to polychromatic ratio is twice the vehicle control value or when a treatment related increase is shown to be statistically significant. - Statistics:
- If necessary, and where possible, all data were statistically analysed using the Kruskal-Wallis one-way analysis of variance by ranks (Kruskal W.H. and Wallis W.A. 1952 J. Am. Statist. Soc. 47 583).
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RANGE-FINDING TOXICITY STUDY
Mice treated with Dispersionsblau F-60 768 at 5000 mg/kg, showed no signs of toxicity and therefore 5000 mg/kg was selected as the “maximum practical dose”. No deaths or abnormal clinical observations were recorded.
MICRONUCLEUS STUDY
Mortality Data and Clinical Observations
No deaths abnormal clinical observations were recorded.
Evaluation of Bone Marrow Slides
There were no significant differences between the test material treatment groups and their corresponding vehicle control groups, with regard to the number of micronucleated polychromatic erythrocytes and micronucleated normochromatic erythrocytes.
The positive control group showed a marked increase in the incidence of micronucleated polychromatic erythrocytes hence confirming the known mutagenic activity of cyclophosphamide monohydrate under the conditions of the test.
The test material did not induce an increase in micronucleated PCE’s that was consistent with a mutagenic effect. Dispersions-blau F-60 768 was, therefore, considered to be non-mutagenic under the conditions of the test in which no bone-marrow toxicity was observed.
Any other information on results incl. tables
RANGE-FINDING TOXICITY STUDY
The mortality data are summarised as follows:
DOSE LEVEL mg/kg |
SEX |
DEATHS ON DAY |
TOTAL DEATHS |
|||
0 |
1 |
2 |
3 |
|||
5000 |
MALE |
0 |
0 |
0 |
0 |
0/4 |
FEMALE |
0 |
0 |
0 |
0 |
MICRONUCLEUS STUDY
SUMMARY OF GROUP MEAN DATA (MALES AND FEMALES COMBINED)
TREATMENT GROUP |
NUMBER OF PCE WITH MICRONUCLEI |
NUMBER OF NCE WITH MICRONUCLEIa |
NCE RATIO PCE |
|||
PER 1000 PCE |
PER 1000 NCE |
|||||
GROUP MEAN |
SD |
GROUP MEAN |
SD |
GROUP MEAN |
SD |
|
1. DISPERSIONSBLAU 5000 mg/kg 24-hour sampling time |
2.2 |
1.0 |
1.9 |
1.3 |
0.81 |
0.14 |
2. DISPERSIONSBALU 5000 mg/kg 49-hour sampling time |
2.0 |
1.2 |
0.7 |
1.0 |
0.75 |
0.15 |
3. DISPERSIONBALU 5000 mg/kg 72-hour sampling time |
2.5 |
1.9 |
1.9 |
1.3 |
0.57 |
0.13 |
4. VEHICLE CONTROL 24-hour sampling time |
2.4 |
1.3 |
1.3 |
1.1 |
0.78 |
0.31 |
5. VEHICLE CONTROL 48-hour sampling time |
1.9 |
1.2 |
0.9 |
0.7 |
0.93 |
0.22 |
6. VEHICLE CONTROL 72-hour sampling time |
1.7 |
1.2 |
0.9 |
0.8 |
0.71 |
0.18 |
7. POSITIVE CONTROL 24-hour sampling time |
44.9 |
6.2 |
3.3 |
0.9 |
1.39 |
0.38 |
Key:
PCE = polychromatic erythrocytes
NCE = normochromatic erythrocytes
SD = standard deviation
a= calculated data
MICRONUCLEUS STUDY – INDIVIDUAL AND GROUP MEAN DATA
TREATMENT GROUP |
ANIMAL NUMBER & SEX |
TOTAL CELLS SCORED (PCE+NCE) |
POLYCHROMATIC ERYTHROCYTES (PCE) |
NORMOCHROMATIC ERYTHROCYTES (NCE) |
NCE PCE RATIO |
|||
NUMBER SCORED |
PCE+MN |
NUMBER SCORED |
NCE+MN |
NCE+MN PER 103NCE |
||||
DISPERSIONSBLAU 5000 mg/kg 24-hour sampling time |
1 M 2 M 3 M 4 M 5 M |
1699 1754 1745 1610 1857 |
1000 1000 1000 1000 1000 |
3.0 2.0 3.0 1.0 3.0 |
699 754 745 610 857 |
1.0 2.0 2.0 1.0 3.0 |
1.43 2.65 2.68 1.64 3.50 |
0.70 0.75 0.75 0.61 0.86 |
MALE MEANS S.D. |
1733 90 |
1000 0 |
2.4 0.9 |
733 90 |
1.8 0.8 |
2.38 0.85 |
0.73 0.09 |
|
6 F 7 F 8 F 9 F 10 F |
1888 1797 2119 1835 1752 |
1000 1000 1000 1000 1000 |
2.0 4.0 1.0 1.0 2.0 |
888 797 1119 836 752 |
0.0 3.0 0.0 2.0 1.0 |
0.00 3.76 0.00 2.40 1.33 |
0.89 0.80 1.12 0.84 0.75 |
|
FEMALE MEANS S.D. |
1878 144 |
1000 0 |
2.0 1.2 |
878 144 |
1.2 1.3 |
1.50 1.62 |
0.88 0.14 |
|
GROUP MEANS S.D. |
1806 136 |
1000 0 |
2.2 1.0 |
806 136 |
1.5 1.1 |
1.94 1.30 |
0.81 0.14 |
S.D. = standard deviation
TREATMENT GROUP |
ANIMAL NUMBER & SEX |
TOTAL CELLS SCORED (PCE+NCE) |
POLYCHROMATIC ERYTHROCYTES (PCE) |
NORMOCHROMATIC ERYTHROCYTES (NCE) |
NCE PCE RATIO |
|||
NUMBER SCORED |
PCE+MN |
NUMBER SCORED |
NCE+MN |
NCE+MN PER 103NCE |
||||
DISPERSIONSBLAU 5000 mg/kg 48-hour sampling time |
11 M 12 M 13 M 14 M 15 M |
1720 1772 1620 1841 1531 |
1000 1000 1000 1000 1000 |
0.0 2.0 4.0 2.0 3.0 |
720 772 620 841 531 |
1.0 2.0 0.0 0.0 0.0 |
1.39 2.59 0.00 0.00 0.00 |
0.72 0.77 0.62 0.84 0.53 |
MALE MEANS S.D. |
1697 123 |
1000 0 |
2.2 1.5 |
697 123 |
0.6 0.9 |
0.80 1.17 |
0.70 0.12 |
|
16 F 17 F 18 F 19 F 20 F |
1634 1897 2037 1644 1843 |
1000 1000 1000 1000 1000 |
2.0 2.0 1.0 3.0 1.0 |
634 897 1037 644 843 |
1.0 0.0 0.0 1.0 0.0 |
1.58 0.00 0.00 1.55 0.00 |
0.63 0.90 1.04 0.64 0.84 |
|
FEMALE MEANS S.D. |
1811 172 |
1000 0 |
1.8 0.8 |
811 172 |
0.4 0.5 |
0.63 0.86 |
0.81 0.17 |
|
GROUP MEANS S.D. |
1754 153 |
1000 0 |
2.0 1.2 |
754 153 |
0.5 0.7 |
0.71 0.97 |
0.75 0.15 |
S.D. = standard deviation
TREATMENT GROUP |
ANIMAL NUMBER & SEX |
TOTAL CELLS SCORED (PCE+NCE) |
POLYCHROMATIC ERYTHROCYTES (PCE) |
NORMOCHROMATIC ERYTHROCYTES (NCE) |
NCE PCE RATIO |
|||
NUMBER SCORED |
PCE+MN |
NUMBER SCORED |
NCE+MN |
NCE+MN PER 103NCE |
||||
DISPERSIONSBLAU 5000 mg/kg 72-hour sampling time |
21 M 22 M 23 M 24 M 25 M |
1529 1336 1595 1820 1614 |
1000 1000 1000 1000 1000 |
4.0 6.0 4.0 2.0 4.0 |
529 336 595 820 614 |
1.0 1.0 2.0 3.0 1.0 |
1.89 2.98 3.36 3.66 1.63 |
0.53 0.34 0.60 0.82 0.61 |
MALE MEANS S.D. |
1579 174 |
1000 0 |
4.0 1.4 |
579 174 |
1.6 0.9 |
2.70 0.90 |
0.58 0.17 |
|
26 F 27 F 28 F 29 F 30 F |
1672 1488 1432 1603 1602 |
1000 1000 1000 1000 1000 |
0.0 1.0 1.0 1.0 2.0 |
672 488 432 603 602 |
1.0 0.0 1.0 1.0 0.0 |
1.49 0.00 2.31 1.66 0.00 |
0.67 0.49 0.43 0.60 0.60 |
|
FEMALE MEANS S.D. |
1559 97 |
1000 0 |
1.0 0.7 |
559 97 |
0.6 0.5 |
1.09 1.04 |
0.56 0.10 |
|
GROUP MEANS S.D. |
1569 133 |
1000 0 |
2.5 1.9 |
569 133 |
1.1 0.9 |
1.90 1.25 |
0.57 0.13 |
S.D. = standard deviation
TREATMENT GROUP |
ANIMAL NUMBER & SEX |
TOTAL CELLS SCORED (PCE+NCE) |
POLYCHROMATIC ERYTHROCYTES (PCE) |
NORMOCHROMATIC ERYTHROCYTES (NCE) |
NCE PCE RATIO |
|||
NUMBER SCORED |
PCE+MN |
NUMBER SCORED |
NCE+MN |
NCE+MN PER 103NCE |
||||
VEHICLE CONTROL 24-hour sampling time |
31 M 32 M 33 M 34 M 35 M |
1459 1839 1600 1485 1593 |
1000 1000 1000 1000 1000 |
4.0 5.0 3.0 2.0 2.0 |
459 839 600 485 593 |
0.0 2.0 2.0 1.0 1.0 |
0.00 2.38 3.33 20.6 1.69 |
0.46 0.84 0.60 0.49 0.59 |
MALE MEANS S.D. |
1595 150 |
1000 0 |
3.2 1.3 |
594 150 |
1.2 0.8 |
1.89 1.22 |
0.60 0.15 |
|
36 F 37 F 38 F 39 F 40 F |
1907 1623 1703 2246 2381 |
1000 1000 1000 1000 1000 |
2.0 2.0 1.0 1.0 2.0 |
907 623 703 1246 1381 |
1.0 0.0 0.0 2.0 1.0 |
1.10 0.00 0.00 1.61 0.72 |
0.91 0.62 0.70 1.25 1.38 |
|
FEMALE MEANS S.D. |
1972 332 |
1000 0 |
1.6 0.5 |
972 332 |
0.8 0.8 |
0.69 0.70 |
0.97 0.33 |
|
GROUP MEANS S.D. |
1784 314 |
1000 0 |
2.4 1.3 |
784 314 |
1.0 0.8 |
1.29 1.13 |
0.78 0.31 |
S.D. = standard deviation
TREATMENT GROUP |
ANIMAL NUMBER & SEX |
TOTAL CELLS SCORED (PCE+NCE) |
POLYCHROMATIC ERYTHROCYTES (PCE) |
NORMOCHROMATIC ERYTHROCYTES (NCE) |
NCE PCE RATIO |
|||
NUMBER SCORED |
PCE+MN |
NUMBER SCORED |
NCE+MN |
NCE+MN PER 103NCE |
||||
VEHICLE CONTROL 48-hour sampling time |
41 M 42 M 43 M 44 M 45 M |
1963 1789 1915 1799 2053 |
1000 1000 1000 1000 1000 |
0.0 1.0 1.0 3.0 2.0 |
963 789 915 799 1053 |
0.0 0.0 1.0 1.0 1.0 |
0.00 0.00 1.09 1.25 0.95 |
0.96 0.79 0.92 0.80 1.05 |
MALE MEANS S.D. |
1904 112 |
1000 0 |
1.4 1.1 |
904 112 |
0.6 0.5 |
0.66 0.61 |
0.90 0.11 |
|
46 F 47 F 48 F 49 F 50 F |
1507 2019 2336 2050 1878 |
1000 1000 1000 1000 1000 |
4.0 1.0 3.0 2.0 2.0 |
507 1019 1336 1050 878 |
1.0 1.0 2.0 1.0 0.0 |
1.97 0.98 1.50 0.95 0.00 |
0.51 1.02 1.34 1.05 0.88 |
|
FEMALE MEANS S.D. |
1958 302 |
1000 0 |
2.4 1.1 |
958 302 |
1.0 0.7 |
1.08 0.74 |
0.96 0.30 |
|
GROUP MEANS S.D. |
1931 217 |
1000 0 |
1.9 1.2 |
931 217 |
0.8 0.6 |
0.87 0.67 |
0.93 0.22 |
S.D. = standard deviation
TREATMENT GROUP |
ANIMAL NUMBER & SEX |
TOTAL CELLS SCORED (PCE+NCE) |
POLYCHROMATIC ERYTHROCYTES (PCE) |
NORMOCHROMATIC ERYTHROCYTES (NCE) |
NCE PCE RATIO |
|||
NUMBER SCORED |
PCE+MN |
NUMBER SCORED |
NCE+MN |
NCE+MN PER 103NCE |
||||
VEHICLE CONTROL 72-hour sampling time |
51 M 52 M 53 M 54 M 55 M |
1598 1783 1608 1544 1861 |
1000 1000 1000 1000 1000 |
2.0 1.0 4.0 3.0 1.0 |
598 783 608 544 861 |
1.0 1.0 1.0 0.0 0.0 |
1.67 1.28 1.64 0.00 0.00 |
0.60 0.78 0.61 0.54 0.86 |
MALE MEANS S.D. |
1679 136 |
1000 0 |
2.2 1.3 |
679 136 |
0.6 0.5 |
0.92 0.85 |
0.68 0.14 |
|
56 F 57 F 58 F 59 F 60 F |
1548 1895 2047 1545 1631 |
1000 1000 1000 1000 1000 |
2.0 1.0 0.0 2.0 1.0 |
548 895 1047 545 631 |
0.0 1.0 0.0 1.0 1.0 |
0.00 1.12 0.00 1.83 1.58 |
0.55 0.90 1.05 0.55 0.63 |
|
FEMALE MEANS S.D. |
1733 226 |
1000 0 |
1.2 0.8 |
733 226 |
0.6 0.5 |
0.91 0.87 |
0.73 0.23 |
|
GROUP MEANS S.D. |
1706 178 |
1000 0 |
1.7 1.2 |
706 178 |
0.6 0.5 |
0.91 0.81 |
0.71 0.18 |
S.D. = standard deviation
TREATMENT GROUP |
ANIMAL NUMBER & SEX |
TOTAL CELLS SCORED (PCE+NCE) |
POLYCHROMATIC ERYTHROCYTES (PCE) |
NORMOCHROMATIC ERYTHROCYTES (NCE) |
NCE PCE RATIO |
|||
NUMBER SCORED |
PCE+MN |
NUMBER SCORED |
NCE+MN |
NCE+MN PER 103NCE |
||||
POSITIVE CONTROL 50 mg/kg 24-hour sampling time |
61 M 62 M 63 M 64 M 65 M |
2508 2366 1938 2817 2906 |
1000 1000 1000 1000 1000 |
43.0 44.0 42.0 41.0 54.0 |
1508 1366 938 1817 1906 |
5.0 4.0 4.0 2.0 7.0 |
3.32 2.93 4.26 1.10 3.67 |
1.51 1.37 0.94 1.82 1.91 |
MALE MEANS S.D. |
2507 387 |
1000 0 |
44.8 5.3 |
1507 387 |
4.4 1.8 |
3.06 1.20 |
1.51 0.39 |
|
66 F 67 F 68 F 69 F 70 F |
2404 2226 2840 1963 1905 |
1000 1000 1000 1000 1000 |
47.0 36.0 56.0 46.0 40.0 |
1404 1226 1840 963 905 |
6.0 4.0 6.0 3.0 3.0 |
4.27 3.26 3.26 3.12 3.31 |
1.40 1.23 1.84 0.96 0.91 |
|
FEMALE MEANS S.D. |
2268 378 |
1000 0 |
45.0 7.6 |
1268 378 |
4.4 1.5 |
3.45 0.47 |
1.27 0.38 |
|
GROUP MEANS S.D. |
2387 383 |
1000 0 |
44.9 6.2 |
1387 382 |
4.4 1.6 |
3.25 0.88 |
1.39 0.38 |
S.D. = standard deviation
Applicant's summary and conclusion
- Conclusions:
- The test material, Dispersionsblau F 60 768, was found not to produce micronuclei in polychromatic erythrocytes of mice under the conditions of the test.
The test substance is not classifiable according to CLP critera. - Executive summary:
A study was performed to assess the potential of Dispersionsblau F60 768 to produce damage to chromosomes or the mitotic apparatus of mice when administered by the oral route. The method used followed that described in the OECD Guidelines for Testing of Chemicals (1981) No. 474 “Genetic Toxicology: Micronucleus Test”.
Following a preliminary range-finding study to confirm the oral toxicity of the test material, the micronucleus study was conducted using Dispersionsblau F-60 768 at the maximum practical dose level (MPD).
In the micronucleus study, groups of ten mice (five males and five females) were given a single oral dose of Dispersionsblau F-60 768 at the maximum practical dose (5000 mg/kg). Animals were killed 24, 48 or 72 hours later. Polychromatic erythrocytes were scored for the presence of micronuclei.
Further groups of ten mice were treated with arachis oil B.P. or cyclophosphamide, to serve as vehicle and positive controls respectively.
There was no evidence of an increase in the incidence of micronucleated polychromatic erythrocytes in mice treated with Dispersionsblau F-60 768 when compared to the vehicle control groups. No statistical analysis was necessary.
The positive control material produced a very marked increase in the number of micronucleated polychromatic erythrocytes.
The test material, Dispersionsblau F-60 768, was considered to be non-mutagenic under the conditions of the test.
The test substance is not classified according to CLP criteria.
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