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EC number: 218-577-4 | CAS number: 2186-92-7
- 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
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study; GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 992
- Report date:
- 1992
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- p-(dimethoxymethyl)anisole
- EC Number:
- 218-577-4
- EC Name:
- p-(dimethoxymethyl)anisole
- Cas Number:
- 2186-92-7
- Molecular formula:
- C10H14O3
- IUPAC Name:
- 1-(dimethoxymethyl)-4-methoxybenzene
- Details on test material:
- - Name of test material (as cited in study report): Anisaldehyddimethylacetal
- Purity: 94 %
- Substance No.: 90/645
- Physical state: Colorless to yellowish liquid
- Storage: +4°C to +6°C
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River GmbH, WIGA, D-W8741 Sulzfeld, FRG
- Weight at study initiation: mean ca. 28 g
- Assigned to test groups randomly: yes
- Housing: individually in Makrolon cages, type M I
- Diet (e.g. ad libitum): Standardized pelleted feed Kliba Haltungsdiät, Klingentalmühle AG, CH-4303 Kaiseraugst, Switzerland; ad libitum
- Water (e.g. ad libitum): drinking water; ad libitum
- Acclimation period: about one week in groups of 5 in Makrolon cages, type M III
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 30 - 70
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: olive oil
- Concentration of test material in vehicle: 3, 6, 12 g/100 ml
- Amount of vehicle (if gavage or dermal): 10 ml/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
All test substance formulations were prepared immediately before administration. - Duration of treatment / exposure:
- 16, 24, 48 h
- Frequency of treatment:
- single administration
- Post exposure period:
- not applicable
Doses / concentrations
- Remarks:
- Doses / Concentrations:
300, 600 and 1200 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide:
- Route of administration: intraperitoneal injection
- Doses / concentrations: 20 mg/kg bw
Vincristine:
- Route of administration: intraperitoneal injection
- Doses / concentrations: 0.15 mg/kg bw
Examinations
- Tissues and cell types examined:
- polychromatic erythrocytes from femur bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
In a pretest for the determination of the acute intraperitoneal toxicity ,deaths were observed down to a dose of 1500 mg/kg body weight. 1250 mg/kg body weight were survived by all animals but led to clinical signs of toxicity such as irregular respiration, abdominal and lateral position, staggering and piloerection about 15 - 60 minutes after test substance administration; the general state of the animals was poor.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
1200 mg/kg bw group: Sacrifice 16h, 24h, 48h after administration.
600 mg/kg bw group: Sacrifice 24h after administration.
300 mg/kg bw group: Sacrifice 24h after administration.
The animals of the negative control were sacrificed 24 hours after administration of the carrier. The control animals were treated at different times so that it was always possible to prepare control animals simultaneously for all the different sacrifice intervals of the test animals
DETAILS OF SLIDE PREPARATION:
The slides were stained in eosin and methylene blue solution for 5 minutes, rinsed in aqua dest. and then placed in fresh aqua dest. for 2 or 3 minutes. They were finally stained in Giemsa solution for 12 minutes. After being rinsed twice in aqua dest. and clarified in xylene, the preparations were embedded in Corbit-Balsam.
METHOD OF ANALYSIS:
In general, 1000 polychromatic erythrocytes from each of the male and female animals of every test group are evaluated and investigated for micronuclei. The normochromatic erythrocytes (= normocytes), which occur, are also scored. - Evaluation criteria:
- The increase in the number of micronuclei in polychromatic erythrocytes of treated animals as compared with the solvent control group provides an index of a chromosome-breaking (clastogenic) effect or of a spindle activity of the substance tested.
The number of micronuclei in normochromatic erythrocytes at the early sacrifice intervals represents the situation before test substance administration and may serve as a control value. A substance-induced increase in the number of micronuclei in normocytes may be found with an increase in the duration of the sacrifice intervals.
The ratio of polychromatic to normochromatic erythrocytes indicates an influence of the test substance specifically on the bone marrow .
The size of micronuclei may give an indication on the possible mode of action of the test substance i.e. a clastogenic or a spindle poison effect. - Statistics:
- A statistical evaluation was not necessary to perform. The number of polychromatic micronucleated erythrocytes after test substance treatment was nearly the range of the actual control value and within the historical values.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not specified
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF DEFINITIVE STUDY
- Clinical signs of toxicity in test animals: The single intraperitoneal administration of the carrier in a volume of 10 ml/kg body weight was tolerated by all animals without any signs or symptoms.
Doses of 1200 mg/kg body weight led to irregular respiration, piloerection, abdominal position and staggering about 30 - 60 minutes after treatment and the general state of the animals was poor. The days after treatment only piloerection was observed in a few animals.
The administration of 600 mg/kg body weight led to irregular respiration, piloerection, staggering and squatting posture after about 30 - 60 minutes. The day after treatment only piloerection was found in few cases.
30 - 60 minutes after treatment of the animals with 300 mg/kg body weight only irregular respiration and piloerection was detected which were not observed any longer after two hours.
Neither the single administration of the positive control substance cyclophosphamide in a dose of 20 mg/kg body weight nor that of vincristine in a dose of 0.15 mg/kg body weight caused any evident signs of toxicity.
Any other information on results incl. tables
Results:
Test group | Interval: 16 h | |||
Polychromatic erythrocytes | Normocytes / total amount polychromatic erythrocytes | Cells with micronuclei (%o) | ||
Dose (mg/kg bw) | polychromatic | normochromatic | ||
vehicle control | ||||
1200 | 10000 | 7204 | 1.1 | 1 |
600 | ||||
300 | ||||
20, cyclophosphamide | ||||
0.15, vincristine | ||||
Test group | Interval: 24 h | |||
Polychromatic erythrocytes | Normocytes / total amount polychromatic erythrocytes | Cells with micronuclei ( %o) | ||
Dose (mg/kg bw) | polychromatic | normochromatic | ||
vehicle control | 10000 | 6501 | 0.7 | 1.7 |
1200 | 10000 | 6705 | 1.4 | 1.2 |
600 | 10000 | 5615 | 1.4 | 1.1 |
300 | 10000 | 5484 | 1.6 | 2.4 |
20, cyclophosphamide | 5000 | 2152 | 8.8 | 0.9 |
0.15, vincristine | 5000 | 4839 | 90.6 | 2.3 |
Test group | Interval: 48 h | |||
Polychromatic erythrocytes | Normocytes / total amount polychromatic erythrocytes | Cells with micronuclei ( %o) | ||
Dose (mg/kg bw) | polychromatic | normochromatic | ||
vehicle control | ||||
1200 | 10000 | 7326 | 1.3 | 1.1 |
600 | ||||
300 | ||||
20, cyclophosphamide | ||||
0.15, vincristine |
With
0.88 %, the positive control substance cyclophosphamide for
clastogenicity led to the expected increase in the number of
polychromatic erythrocytes containing exclusively small micronuclei at a
dose level of 20 mg/kg body weight.
With 9.06 % the positive control vincristine for spindle poison effects
also led to a clearly enhanced number of polychromatic erythrocytes
containing micronuclei with the expected amount of large micronuclei,
i.e. 1.34 %.
The number of normochromatic erythrocytes containing micronuclei did not
differ to any appreciable extent in the negative control or in the
various dose groups at any of the sacrifice intervals.
Thus, the test substance Anisaldehyddimethylacetal did not lead to any
increase in the rate of micronuclei.
The
number of normochromatic or polychromatic erythrocytes containing small
micronuclei (d < D/4) did not deviate from the solvent control value
at any of the sacrifice intervals. Nor were large micronuclei (d > D/4)
observed either in the negative control group or in the three dose
groups of Anisaldehyddimethylacetal.
No inhibition of erythropoiesis induced by the treatment of mice with
Anisaldehyddimethylacetal was detected; the ratio of polychromatic to
normochromatic erythrocytes was always in the same range as that of the
control values in all dose groups.
Applicant's summary and conclusion
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