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EC number: 303-085-5 | CAS number: 94158-14-2
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
Test material
- Reference substance name:
- 2-(1,3-benzodioxol-5-ylamino)ethanol hydrochloride
- EC Number:
- 303-085-5
- EC Name:
- 2-(1,3-benzodioxol-5-ylamino)ethanol hydrochloride
- Cas Number:
- 94158-14-2
- Molecular formula:
- C9H11NO3.ClH
- IUPAC Name:
- 2-(1,3-benzodioxol-5-ylamino)ethanol hydrochloride
- Test material form:
- solid: crystalline
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- Distilled water
- Duration of treatment / exposure:
- Single administration 24 and 48 hours (high dose only) before sacrifice
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day
- Remarks:
- control group
- Dose / conc.:
- 25 mg/kg bw/day
- Dose / conc.:
- 125 mg/kg bw/day
- Dose / conc.:
- 250 mg/kg bw/day
- No. of animals per sex per dose:
- 5
- Control animals:
- yes
- Positive control(s):
- positive control groups received 40 mg/kg bw cyclophosphamide (CPA), dissolved in deionised water
Examinations
- Details of tissue and slide preparation:
- Femoral bone marrow was sampled from mice after sacrifice (24 hours after dosing) for all dose groups except for the high dose group (48 h after dosing). Bone marrow of the negative and positive control animals were sampled 24 h after administration. Slides were prepared from the bone marrow preparations, stained with May-Grünwald/Giemsa, and evaluated (without knowledge of the dose group) for the number of polychromatic erythrocytes (PCE) with micronuclei. At least 2000 PCEs per animal were analysed. In addition, the ratio between polychromatic and total erythrocytes per animal was determined. Five animals per sex and test group were evaluated as described above.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- but only in the high dose group. toxic signs noted: palpebral closure and lethargy within the first hour after administration and lethargy for up to 6 hours after start of treatment.
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
Applicant's summary and conclusion
- Conclusions:
- HYDROXYETHYL-3,4-METHYLENEDIOXYANILINE HCL was not mutagenic in the in vivo micronucleus test using NMRI mice after a single intraperitoneal administration at doses up to the maximum tolerated dose of 250 mg/kg bw.
- Executive summary:
HYDROXYETHYL-3,4-METHYLENEDIOXYANILINE HCL,dissolved in distilled water, was administered intraperitoneally to groups of 5 male and 5 female NMRI mice (supplied by HARLAN WINKELMANN, Germany; 7-12 weeks old at start of the treatment, mean bw 25.2±1.2 g (males) and 22.2±1.3 g (females)) at doses of 25, 125 and 250 mg/kg bw. For the high dose, two groups were treated to allow sampling after 24 and 48 hours. Single doses were administered in a total volume of 10 ml/kg bw to animals. Dose selection was based on findings in the pre-experiment in which doses of 250 and 1000 mg/kg bw were administered to three female and three male mice under the same treatment procedure. Negative control groups received distilled water and positive control groups received 40 mg/kg bw cyclophosphamide (CPA), dissolved in deionised water. Femoral bone marrow was sampled from mice after sacrifice (24 hours after dosing) for all dose groups except for the high dose group (48 h after dosing). Bone marrow of the negative and positive control animals were sampled 24 h after administration. Slides were prepared from the bone marrow preparations, stained with May-Grünwald/Giemsa, and evaluated (without knowledge of the dose group) for the number of polychromatic erythrocytes (PCE) with micronuclei. At least 2000 PCEs per animal were analysed. In addition, the ratio between polychromatic and total erythrocytes per animal was determined. Five animals per sex and test group were evaluated as described above. The animals were examined for acute toxic signs three times within the first 24 hours after treatment and the high dose group additionally 48 hours after administration. Stability and homogeneity data are not provided in the study. However, the test solution was prepared freshly prior to administration. In addition, a sufficient stability and solubility of HYDROXYETHYL-3,4-METHYLENEDIOXYANILINE HCL in water was analytically confirmed. In the pre-experiment, at 1000 mg/kg bw all animals (3 male and 3 female mice) died within 24 hours. At 250 mg/kg bw toxic signs noted were palpebral closure and lethargy within the first hour after administration and lethargy for up to 6 hours after start of treatment. No mortality occurred. Based on these findings, doses of 25, 100 and 250 mg/kg bw were chosen for the main study. In the main study, toxic signs like those described in the pre-experiment (250 mg/kg bw) were noted in all animals of the high dose group within the first hour after substance administration. The ratio between PCEs and total erythrocytes was not affected by the test item at any test concentration or sampling time as compared to the ratio observed in the vehicle control. However, the observed signs of systemic toxicity indicate that the test item was systemically distributed and bio-available. This assumption is further supported byin vivoandin vitrokinetic studies, in which a very good bioavailability after oral administration of aqueous formulations of HYDROXYETHYL-3,4-METHYLENE-DIOXYANILINE HCLwas demonstrated. There was no statistically significant or biologically relevant increase in the number of micronuclei per 2000 PCEs in the mice of any of the HYDROXYETHYL-3,4-METHYLENE-DIOXYANILINE HCL treated groups compared to the respective vehicle control groups. The positive control (CPA) induced a statistically significant increase in micronucleated PCEs and the values from the vehicle control groups were well within the range of historical control data of the performing laboratory. This demonstrates the validity and sensitivity of the used test system.
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