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EC number: 267-051-0 | CAS number: 67774-74-7
- 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
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:
- 5 Jun 1989 to 8 Jun 1989
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 989
- Report date:
- 1990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Benzene, C10-13-alkyl derivs.
- EC Number:
- 267-051-0
- EC Name:
- Benzene, C10-13-alkyl derivs.
- Cas Number:
- 67774-74-7
- Molecular formula:
- C6 H5 Cn H2n+1; n= 10 to 13
- IUPAC Name:
- Benzene, C10-C13 Alkyl derivs.
- Reference substance name:
- Undecylbenzene
- EC Number:
- 229-806-2
- EC Name:
- Undecylbenzene
- Cas Number:
- 6742-54-7
- Molecular formula:
- C17H28
- IUPAC Name:
- 4-[undecan-(2 to 6)-yl] benzene
Constituent 1
Constituent 2
Test animals
- Species:
- mouse
- Strain:
- other: BRO:NMRI (SPF Han.)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: FA. Winkelmann
- Age at study initiation: young adult
- Weight at study initiation: about 26 g
- Fasting period before study: 18 hours
- Housing: 5 animals per cage in Makrolon Type III cages, identified by cage signs
- Diet: Ssniff R 10 - Alleindiat fur Ratten
- Water: Tap water, ad libitum
- Acclimation period: 6 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 ± 1
- Humidity (%): 60 ± 10
- Photoperiod (hrs dark / hrs light): 12
Administration / exposure
- Route of administration:
- oral: gavage
- Duration of treatment / exposure:
- Single oral gavage exposure
- Frequency of treatment:
- Once
- Post exposure period:
- Animals were sacrificed at 24, 48, and 72 hours after exposure.
Doses / concentrations
- Dose / conc.:
- 5 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 15 including negative controls and 5 in positive control group
- Control animals:
- yes
- Positive control(s):
- Positive control animals were given a single dose of 100 mg/kg cyclophosphamide. Negative control animals were given water instead of test substance.
Examinations
- Tissues and cell types examined:
- After sacrifice, the marrow from the thighs of each animal were removed and 2 mL fetal bovine serum was added. This suspension was centrifuged for 5 minutes. Marrow from each animals was divided into 3 slides, dried, and stained.
- Details of tissue and slide preparation:
- TREATMENT AND SAMPLING TIMES:
Animals were given a single oral dose, and 5 animals of each sex per dose were sacrificed at 24, 48, and 72 hours after exposure.
DETAILS OF SLIDE PREPARATION:
Marrow from each animals was divided into 3 slides, dried, and stained.
METHOD OF ANALYSIS:
Cells were analysed by microscope ,1000 cells were analyzed per sample (3000/animal).
- Evaluation criteria:
- The nucleus of each cell was examined for size (micronucleus, which was considered 1/20th of the largest nucleus), and the number of polychromatid erythrocytes (PCE) to normochromatid erythrocytes (NCE).
- Statistics:
- F-test, t-test, and U-test were used to analyze the data.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- diarrhea and diuresis was seen in test group animals
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Animals in the treatment group exhibited diarrhea and diuresis during the treatment period. There was a significant increase in the PCE/NCE ratio and PCE cells with micronucleus in the positive control group. There was no significant increase in either of these parameters in the treatment group.
Any other information on results incl. tables
Table 1: Results of Mouse Micronucleus Assay
Dose (mg/kg) |
Hours after application |
% PCE with micronucleus |
PCE/NCE |
|
Positive control |
100 |
24 |
3.34 ± 0.97 |
0.97 ± 0.07 |
Negative control |
- |
24 |
0.18 ± 0.06 |
1.15 ± 0.10 |
- |
48 |
0.25 ± 0.12 |
1.31 ± 0.09 |
|
- |
72 |
0.28 ± 0.10 |
1.20 ± 0.33 |
|
Treatment group |
5000 |
24 |
0.20 ± 0.07 |
1.07 ± 0.10 |
5000 |
48 |
0.18 ± 0.08 |
1.26 ± 0.16 |
|
5000 |
72 |
0.18 ± 0.11 |
1.38 ± 0.20 |
Applicant's summary and conclusion
- Conclusions:
- Under the conditions described for this Mammalian Erythrocyte Micronucleus assay the tested substance did not reveal mutagenic properties.
- Executive summary:
This study in accordance with OECD 474 and in compliance with GLP was performed to examine the mutagenic potential of the test substance in vivo. A groups of 15 female and 15 male mice were given a single dose of test substance to determine the effect on bone marrow. 5 animals of each sex were sacrificed at 24, 48, and 72 hours after exposure. Similar groups were exposed to cyclophosphamide (positive control), and water (negative control). All animals in the positive control group were sacrificed at 24 hours. Analysis of the bone marrow showed no significant increase in either micronucleus or polychromatid erythrocytes in the treatment group as compared to negative controls. The test substance is not mutagenic.
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