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EC number: 604-636-5 | CAS number: 148477-71-8
- 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
Neurotoxicity
Administrative data
- Endpoint:
- neurotoxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.6300 (Developmental Neurotoxicity Study)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 3-(2,4-Dichlorophenyl)-2-oxo-1-oxaspiro[4.5]dec-3-en-4-yl 2,2-dimethylbutanoate
- Cas Number:
- 148477-71-8
- Molecular formula:
- C21H24Cl2O4
- IUPAC Name:
- 3-(2,4-Dichlorophenyl)-2-oxo-1-oxaspiro[4.5]dec-3-en-4-yl 2,2-dimethylbutanoate
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Remarks:
- Wistar Hannover Crl:WI (Glx/BRL/Han) IGS BR rats
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Approximately 120 male and 120 female (nulliparous and nonpregnant) were placed on study to provide a minimum of 20 acceptable litters per dietary level. Animals had not been previously treated and were at least 15 weeks (males) or 12 weeks (females) of age at co-housing. The adult males served only as "breeders" and, as such, were not exposed to the test substance or included in any tests. The Wistar rat was selected as the test system due to its general acceptance and suitability for toxicological testing of this type as well as the availability of a historical database.
Administration / exposure
- Route of administration:
- oral: feed
Results and discussion
Results of examinations
- Details on results:
- This developmental neurotoxicity study was performed at dietary concentrations of 0, 70, 350 and 1500 ppm. There was no evidence of developmental neurotoxicity in this study.
Applicant's summary and conclusion
- Conclusions:
- This developmental neurotoxicity study was performed at dietary concentrations of 0, 70, 350 and 1500 ppm. There was no evidence of developmental neurotoxicity in this study.
General
There were no effects on reproduction parameters at any dietary level.
Based on analytical results, the average concentrations of spirodiclofen in the diet were 0,
71.9, 357 and 1452 ppm. The average daily intake of active ingredient was as follows for
nominal concentrations of 0, 70, 350 and 1500 ppm:
Gestation: 0, 6.5, 32.1 and 135.9 mg/kg/day, respectively; and
Lactation: 0, 14.0, 69.7 and 273.8 mg/kg/day, respectively.
Maternal
Compound-related effects consisted of the following:
70 ppm - There were no compound-related effects (NOAEL).
350 ppm - There were no compound-related effects (NOAEL).
1500 ppm - Decreased body weight and food consumption during lactation.
Offspring
Compound-related effects were limited to the following:
70 ppm - There were no compound-related effects (NOAEL).
350 ppm - There were no compound-related effects (NOAEL).
1500 ppm - Decreased body weight and weight gain during lactation, with complete
recovery after weaning. - Executive summary:
Technical-grade spirodiclofen was administered via the diet from gestation day (GD) 0 through lactation day (LD) 21 to mated female Wistar rats, at nominal concentrations of 0, 70, 350 and 1500 ppm. The offspring were evaluated using a functional observational battery, body weight, food consumption, developmental landmarks for sexual maturation, automated measures of activity (figure-eight maze), acoustic startle habituation, learning and memory (passive avoidance and a water maze task), and an ophthalmic examination. Serum cholesterol was measured in the dams and offspring and tissues were collected from the offspring for morphometry (brain) and microscopic examination on PND 21 (brain) and at study termination (brain, an assortment of additional neural tissues and skeletal muscle). In summary, the following observations were noted.
General- There were no effects on reproduction parameters at any dietary level.
Based on analytical results, the average concentrations of spirodiclofen in the diet were 0, 71.9, 357 and 1452 ppm. The average daily intake of active ingredient was as follows for nominal concentrations of 0, 70, 350 and 1500 ppm:
Gestation: 0, 6.5, 32.1 and 135.9 mg/kg/day, respectively; and
Lactation: 0, 14.0, 69.7 and 273.8 mg/kg/day, respectively.
Maternal
Compound-related effects consisted of the following:
70 ppm - There were no compound-related effects (NOAEL).
350 ppm - There were no compound-related effects (NOAEL).
1500 ppm - Decreased body weight and food consumption during lactation.
Offspring
Compound-related effects were limited to the following:
70 ppm - There were no compound-related effects (NOAEL).
350 ppm - There were no compound-related effects (NOAEL).
1500 ppm - Decreased body weight and weight gain during lactation, with complete
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