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EC number: 416-600-4 | CAS number: -
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2008-09-02 to 2009-05-11
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 1997
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- -
- EC Number:
- 416-600-4
- EC Name:
- -
- Cas Number:
- 77703-56-1
- Molecular formula:
- C23H32N4O2
- IUPAC Name:
- 3-butyl-1-[4-({4-[(butylcarbamoyl)amino]phenyl}methyl)phenyl]urea
Constituent 1
- Specific details on test material used for the study:
- Analytical purity: >= 99.4 %
Lot/batch No.: 05-12-06
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River; Saint-Germain-sur-l'Arbresle, France;
- Age at study initiation: 5 to 6 weeks;
- Weight at study initiation: males: 150 to 180 g; females: 150 to 187 g;
- Assigned to test groups randomly: yes;
- Fasting period before study: animals were not fasted before study begin;
- Housing: in polypropylene cages, in groups of 2 or 3; by random distribution;
- Diet: No. A04C10 irradiated rat/mouse feed; Supplier: SAFE;
- Water: drinking water softened, treated by osmosis and filtered over 0.2 µm membrane filter; ad libitum;
- Acclimation period: at least 5 days;
ENVIRONMENTAL CONDITIONS
- Temperature: 22 +/- 3 °C;
- Humidity: 55 +/- 15 % R.H.;
- Air changes: 20 air changes per hour;
- Photoperiod: 12 hours light/12 hours dark from 8:00 a.m. to 8:00 p.m.;
Administration / exposure
- Route of administration:
- subcutaneous
- Vehicle:
- corn oil
- Details on exposure:
- Limit test: N
- Duration of treatment / exposure:
- 2 successive administrations at 24-hour intervals;
- Frequency of treatment:
- 2 times;
- Post exposure period:
- 24 hours
Doses / concentrationsopen allclose all
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 2000 mg/kg bw: 5 males, 5 females;
1000 mg/kg bw: 5 males, 5 females;
500 mg/kg bw: 5 males, 5 females; - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide;
25 mg/kg bw/day;
Examinations
- Tissues and cell types examined:
- Bone marrow;
immature (polychromated) erythrocytes;
micronucleated immature erythrocytes;
immature among total erythrocytes; - Details of tissue and slide preparation:
- Bone marrow was extracted with foetal calf serum. Cell supensions were centrifugated for 5 minutes at 1000 rpm. Centrifugate was spread on slides. Smears were stained to make possible to distinguish between polychromatic (PCE) and normochromatic (NCE) erythrocytes. PCE are purple whereas NCE are red.
- Evaluation criteria:
- The mean number of micronuclei observed in the negative control animals must be within the range of the historical values for control animals. The mean number of micronuclei observed in the positive control animals treated with cyclophosphamide must show a statistically significant increase from the negative control animals and higher than the minimal historical value for positive animals. If deaths are observed at the tested dose, the mortality rate must be less than 20 % per group. The dead animals are replaced by those in parallel treatment.
- Statistics:
- The statistical comparison for the proportion of polychromatic among total erythrocytes and for the weight homogeneity within the sex of each group was performed using the Student's test. Statistical analysis was performed for micronucleus number using a non-parametric test, the Mann Whitney U rank test. An analysis of a large number of control results has shown that the distribution of the numbers of micronuclei does not correspond to a Gaussian distribution, but to a Poisson-type distribution.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- GENOTOXICITY ASSAY
Number of sampling times :
one: for negative control and treated groups: 24 hours after the second treatment
one: for positive control group: 24 hours after single treatment
Reference substance :
cyclophosphamide, 25 mg/kg bw, intraperitoneal administration;
Number of polychromatic erythrocytes observed for each animal :
2000 for micronuclei ;
1000 for fraction of PCE among total erythrocytes (PCE+NCE).
No statistically significant decrease in the fraction of PCE among total erythrocytes (PCE+NCE) was observed (this finding provides no evidence that bone marrow cell exposure has occurred). No statistically significant increase in the number of micronuclei was noted at the doses of 2000, 1000 or 500 mg/kg bw/day (x2) in male or in female rats.
Any other information on results incl. tables
SAMPLING TIME |
TEST ITEM
DOSES in mg/kg bw/day (x2) |
SEX |
Fraction of PCE* (%) |
MICRONUCLEI FOR 1000 PCE |
||
Mean |
Student’s t Test (p) |
Mean |
Mann Whitney (p) |
|||
Negative control Group |
VEHICLE 10 mL/kg bw |
M F M + F |
62.9 54.2 58.5 |
|
0.70 0.60 0.65 |
|
Positive control Group |
Cyclosphosphamide 25 mg/kg bw/day (x1) |
M F M + F |
44.4 37.8 41.1 |
<0.01 <0.001 <0.001 |
9.60 8.90 9.25 |
P<0.01 P<0.01 P<0.001 |
HAT ISO
TREATED
GROUPS |
2000 |
M F M + F |
63.3 48.0 55.7 |
N.S. N.S. N.S. |
0.40 0.80 0.60 |
N.S. N.S. N.S. |
1000 |
M F M + F |
58.7 53.8 56.3 |
N.S. N.S. N.S. |
0.70 0.60 0.65 |
N.S. N.S. N.S. |
|
500 |
M F M + F |
55.1 53.7 54.4 |
N.S. N.S. N.S. |
0.60 0.50 0.55 |
N.S. N.S. N.S. |
N.S.: Non significant at the threshold of p=0.05
PCE: Polychromatic erythocytes
NCE: Normochromatic erythocytes
*Fraction of PCE among total erythrocytes = 100xPCE /(PCE+NCE)
Applicant's summary and conclusion
- Conclusions:
- HAT ISO was tested for mutagenic activity in the in vivo Micronucleus test in rats. Under the experimental conditions of this test, HAT ISO induced no genotoxic activity. No classification and labelling for mutagenic activity is required according to Regulation 1272/2008/EC (CLP).
- Executive summary:
HAT-ISO was investigated by means of the in vivo micronucleus test, in male and female OFA Sprague Dawley rats. Animals were treated by subcutaneous route twice with 2000, 1000 or 500 mg/kg bw/day (x2). Treatment was followed by one sampling time 24 hours after the last treatment. In conclusion, HAT-ISO induced no genotoxic activity under these experimental conditions.
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