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EC number: 603-923-2 | CAS number: 135590-91-9
- 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
- Year:
- 1 990
- Report date:
- 1990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- diethyl 1-(2,4-dichlorophenyl)-5-methyl-4,5-dihydro-1H-pyrazole-3,5-dicarboxylate
- EC Number:
- 603-923-2
- Cas Number:
- 135590-91-9
- Molecular formula:
- C16H18Cl2N2O4
- IUPAC Name:
- diethyl 1-(2,4-dichlorophenyl)-5-methyl-4,5-dihydro-1H-pyrazole-3,5-dicarboxylate
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: HOECHST AG, Kastengrund, SPF breeding colony
- Age at study initiation: 7 weeks
- Weight at study initiation: mean males = 29.7 g (27 - 35g), females = 24.8 g (20 - 29 g)
- Housing: in fully air-conditioned rooms in Macrolon cages (Type 3), on softwood granulate in groups of 5 animals
- Diet (e.g. ad libitum): rat/mice diet Altromin 1324 (Altromin-GmbH, Lage/Lippe), ad libitum
- Water (e.g. ad libitum): tap water in plastic bottles, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22±2
- Humidity (%): 55±10
- Air changes (per hr):
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: starch mucilage
- Concentration of test material in vehicle: 250 mg/ml (25 % w/v)
- Amount of vehicle (if gavage or dermal): The test compound was given in two equal parts of 10 ml/kg bw each within two hours - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test compound dilutions were prepared fresh each day. The test compound was mortared, 6250 mg Hoe 107892 - substance, technical were weighed in a beaker, mixed with starch mucilage, washed out in a 25 ml flask and topped up to the calibration mark. A suspension was formed. - Duration of treatment / exposure:
- 2 oral applications of half of the dose within 2 h
- Frequency of treatment:
- once
- Post exposure period:
- 24, 48, 72 h
Doses / concentrations
- Dose / conc.:
- 5 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide (Endoxan)
- Route of administration: oral gavage
- Doses / concentrations: 50 mg/kg bw
Examinations
- Tissues and cell types examined:
- bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
According to a preliminary study to test the acute toxicity, a dose of 5000 mg Hoe 107892 - substance, technical per kg bodyweight was the maximum applicable dose level.
DETAILS OF SLIDE PREPARATION:
The animals were killed by carbon dioxide asphyxiation 24, 48 or 72 hours after application. For each animal, about 3 ml foetal bovine serum was poured into a centrifuge tube. Both femora were removed and the bones freed of muscle tissue. The proximal ends of the femora were opened and the bone marrow flushed into the centrifuge tube. A suspension was formed. The mixture was then centrifuged for 5 minutes at 1200 rpm and almost all the supernatant discarded. One drop of the thoroughly mixed sediment was smeared on a cleaned slide, identified by project code and animal number and air-dried for about 24 hours.
Staining procedure:
- 5 minutes in methanol
- 3 minutes in May-Gruenwalds solution
- 2 minutes in May-Gruenwalds solution diluted 1:1 with distilled water
- brief rinsing twice in distilled water
- 10 minutes staining in 1 part Giemsa solution to 6 parts buffer solution, pH 7.2 (Weise)
- rinsing in distilled water
- drying
- coating with Entellan
METHOD OF ANALYSIS:
1000 polychromatic erythrocytes were counted for each animal. The number of cells with micronuclei was recorded, not the number of individual micronuclei. As a control measure 1000 mature erythrocytes were also counted and examined for micronuclei. In addition, the ratio of polychromatic to normochromatic erythrocytes was determined. All bone marrow smears for evaluation were coded to ensure that the group which they belonged to remained unknown to the investigator. The number of polychromatic erythrocytes with micronuclei occurring in the 1000 polychromatic erythrocytes counted, and the number of normocytes with micronuclei occurring in the 1000 normocytes counted, were evaluated statistically. - Statistics:
- Comparison of dose groups with the simultaneous control group was performed according to Wilcoxon (paired, one-sided, increase). The results of the treatment groups (test substance) in the micronucleus test at each dose and killing time were compared with corresponding control values. The ratio of polychromatic to normochromatic erythrocytes was also evaluated statistically by the method of Wilcoxon (paired, two sided). The statistical evaluations were performed using the "Diamant" computer program Version 2.0, supplied by the Department of Information and Communication Hoechst AG. All statistical results are based on a 95 % level of significance. Actual data were also compared with historical controls.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 5000 mg/kg bw
- Clinical signs of toxicity in test animals: reduced spontaneous activity and uncoordinated gait
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): The incidence of micronucleated polychromatic and normochromatic erythrocytes in the dose groups of Hoe 107892 - substance, technical was within the normal range of the negative control groups. The number of normochromatic erythrocytes with micronuclei did not differ from the values of the simultaneous control animals for each of the three killing times investigated.
- Ratio of PCE/NCE (for Micronucleus assay): The ratio of polychromatic erythrocytes to normocytes remained essentially unaffected by the test compound
- Statistical evaluation: No statistically significant increase of micronucleated polychromatic erythrocytes has been observed.
Any other information on results incl. tables
All animals survived after application of 5000 mg Hoe 107892 - substance, technical per kg bodyweight. No signs of toxicity were observed.
Summarizing it can be stated that, under the conditions described, administration of Hoe 107892 - substance, technical did not lead to a substantial increase of micronucleated polychromatic erythrocytes. It is concluded that Hoe 107892 - substance, technical is not mutagenic in the micronucleus test.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: negative
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