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EC number: 943-728-2 | CAS number: -
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Remarks:
- DRF for OECD 414 study
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 18-11-2021 to Pending final QA report issue
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- DRF for OECD 414 study
Data source
Reference
- Title:
- Unnamed
- Year:
- 2 022
Materials and methods
Test guideline
- Qualifier:
- no guideline required
- GLP compliance:
- no
- Remarks:
- DRF study, GLP not required
Test material
- Reference substance name:
- Reaction mass of 3,5-dimethylcyclohex-3-ene-1-carbaldehyde and 2,4-dimethylcyclohex-3-ene-1-carbaldehyde
- EC Number:
- 943-728-2
- Molecular formula:
- C9H14O
- IUPAC Name:
- Reaction mass of 3,5-dimethylcyclohex-3-ene-1-carbaldehyde and 2,4-dimethylcyclohex-3-ene-1-carbaldehyde
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source (i.e. manufacturer or supplier) and lot/batch number of test material: Sponsor; SHT036
- Purity, including information on contaminants, isomers, etc.: 99.48% (sum of isomers)
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Store at laboratory conditions, protected from heat and light
Test animals
- Species:
- rat
- Strain:
- Wistar
- Remarks:
- Wistar Crl
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: SPF breeding, VELAZ s.r.o., Dědinská 893/29, 161 00 Prague 6 - Ruzyně, Czech Republic, RČH CZ 11760500
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 12 weeks
- Housing: IVC TOUCH animal house of CETA; sterilized shavings of soft wood or Lignocel
- Diet: Maintenance pelleted diet for rats and mice - Altromin for rats/mice, Manufacturer: Altromin Spezialfutter GmbH & Co. KG, Germany
- Water: drinking water ad libitum, quality corresponding to the Regulation No. 252/2004 of Czech Coll. of Law
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3 °C
- Humidity (%): 30-70 %
- Photoperiod (hrs dark / hrs light): 12 hours light, 12 hours dark
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- olive oil
- Analytical verification of doses or concentrations:
- no
- Remarks:
- Stability and homogeneity were confirmed in a separate analytical study (refer to Key study record)
- Details on mating procedure:
- After acclimatization females were mated with males (1 male and 2 females). Vaginal smears were carried out daily in the morning to control fertilization (first time: 24 hours after placing the male to the females). Presence of sperm was examined. Day 0 of pregnancy was the day on which sperm in vaginal smears were observed. Pregnant females were randomly distributed to experimental groups.
- Duration of treatment / exposure:
- Test item administration lasted from implantation (the 5th day after fertilization) to one day prior to the day of scheduled euthanasia (the 19th day after fertilization).
- Frequency of treatment:
- Daily
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 6 females
- Control animals:
- yes, concurrent vehicle
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
Mortality/viability:twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: twice a day (except weekend, when clinical observation was performed once a day)
BODY WEIGHT: Yes
- Time schedule for examinations: 1st, 5th, 8th, 11th, 14th, 17th and 20th day of pregnancy
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day # 20
- Organs examined: On the 20th day of pregnancy the females were euthanized. The revision of the external surface of the body was performed. During macroscopy, all orifices, the cranial, thoracic and abdominal cavities were examined and uterus (incl. the cervix) was removed and weighed. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included: In gravid uteri, the number of viable foetuses, number of dead foetuses, number of early resorption (implantation without recognizable embryo/foetus) and number of late resorption (dead embryo or foetus with external degenerative changes) were recorded. The numbers of corpora lutea of both ovaries were recorded.
- Blood sampling:
- Before necropsy of animals the blood samples were collected from the orbital plexus by glass micropipette under the light diethyl ether narcosis into the PVC test tubes containing anticoagulation systems. Basic blood parameters (total erythrocyte count, total leucocyte count, mean corpuscule volume, haematocrit, haemoglobin concentration, total platelet count) was determined on haematology analyser.
- Fetal examinations:
- Sex, individual and body weights of foetuses were recorded. Each foetus was examined for external alterations and soft tissue alterations.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- No changes of animal health status or clinical symptoms of intoxication were observed in animals at the dose level 100 mg/kg bw/day. Piloerection was observed in one female at 500 mg/kg bw/day from the 1st to the 3rd day of application. Generally, piloerection and decreased reaction to stimuli (auditory, visual and proprioceptive) were recorded after application of the test item in females at the dose level 1000 mg/kg bw/day. The symptom of intoxication – decreased reaction to stimuli disappeared by the next day in females at 1000 mg/kg bw/day.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- The body weights of pregnant females at all dose levels were comparable to the control group during the whole study period. The body weight increment was reduced at the dose level 1000 mg/kg bw/day.
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- The total leucocyte counts were increased at the dose levels 500 and 1000 mg/kg bw/day in comparison with the control. The haematocrit was slightly increased in all treated groups compared to the control group. Other haematological parameters did not show significant differences between dosed and control group.
- Clinical biochemistry findings:
- not examined
- Endocrine findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- Macroscopic examination was performed in all females (including females without foetuses, except non-paired female No. 106). No finding related with treatment was noted at necropsy in all treated females.
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- effects observed, treatment-related
- Description (incidence and severity):
- The number of implantations was slightly decreased at the dose level 100 mg/kg bw/day in comparison with the control group. The numbers of corpora lutea were comparable in all treated groups with the control group.
- Total litter losses by resorption:
- effects observed, treatment-related
- Description (incidence and severity):
- The number of resorptions was increased at the dose level 1000 mg/kg bw/day in comparison with the control group.
- Early or late resorptions:
- effects observed, treatment-related
- Description (incidence and severity):
At 1000 mg/kg bw/day, there was 1 early resorption in 1 female, 16 early resorptions in 1 female, and 6 early resorptions in 1 female.- Dead fetuses:
- effects observed, treatment-related
- Description (incidence and severity):
- Four dead foetuses were recorded at the dose level 1000 mg/kg bw/day.
- Changes in pregnancy duration:
- not examined
- Changes in number of pregnant:
- effects observed, treatment-related
- Description (incidence and severity):
- One female at the dose level 1000 mg/kg bw/day became pregnant and then all implanted conceptuses in the uterus were totally resorbed (females without foetuses but with implantations and resorptions). The number of non-pregnant females was as follows: 2 – 0 – 0 – 0, respectively for the dose levels 0 – 100 – 500 – 1000 mg/kg bw/day.
Effect levels (maternal animals)
- Dose descriptor:
- other: No NOAEL; doses selected for main study
Results (fetuses)
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- The mean body weight of all foetuses was decreased at the dose level 1000 mg/kg bw/day compared to the control foetuses. Male foetuses were heavier than females in all groups.
- Reduction in number of live offspring:
- not examined
- Changes in sex ratio:
- effects observed, non-treatment-related
- Description (incidence and severity):
- The mean number of foetuses per litter was slightly decreased at dose levels 100 mg/kg bw/day compared to the control group. Also the mean number of female foetuses was markedly decreased at this dose level.
- Changes in litter size and weights:
- not examined
- Anogenital distance of all rodent fetuses:
- not examined
- Changes in postnatal survival:
- not examined
- External malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Cranial meningocele, lip cleft and exophthalmos were recorded in one foetus at the dose level 100 mg/kg bw/day. This was considered as a sporadic finding and probably not related to the test item treatment. No other macroscopic changes of soft tissues and external alteration were found during the pathological examination of the foetuses at all dose levels.
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- no effects observed
Effect levels (fetuses)
- Dose descriptor:
- other: No NOAEL; doses selected for main study
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Any other information on results incl. tables
Refer to Tables 3 - 9 attached.
Applicant's summary and conclusion
- Conclusions:
- After evaluation of the results of the DRF, the following dose levels – 0, 100, 300 and 1000 mg/kg bw/day will be used for the main Prenatal Developmental Toxicity Study.
- Executive summary:
In a dose range finding study (no guideline) for a prenatal developmental toxicity in rats (OECD 414/GLP), the test item (99.48% (sum of isomers)) was administered to pregnant Wistar Crl rats (6/dose) by oral gavage in olive oil at dose levels of 0, 100, 500 and 1000 mg/kg bw/day daily from GD 5-19.
Twenty-four females (6 for each group) were mated in the study. The number of confirmed pregnant evaluated dams was 4 in the Control and 6 in all test item dose groups. No unscheduled death of maternal animals was recorded during the DRF.No changes of animal health status or clinical symptoms of intoxication were observed in animals at the dose level 100 mg/kg bw/day. Piloerection was observed in one female at 500 mg/kg bw/day from the 1st to the 3rd day of application. Generally, piloerection and decreased reaction to stimuli (auditory, visual and proprioceptive) were recorded after application of the test item in females at the dose level 1000 mg/kg bw/day with the latter resolving the next day.The body weights of pregnant females at all dose levels were comparable to the control group during the whole study period. The body weight increment was reduced at the dose level 1000 mg/kg bw/day.
The total leucocyte counts were increased at the dose levels 500 and 1000 mg/kg bw/day in comparison with the control. The haematocrit was slightly increased in all treated groups compared to the control group. Other haematological parameters did not show significant differences between dosed and control group.
Macroscopic examination was performed in all females (including females without foetuses). No finding related with treatment was noted at necropsy in all treated females.
During necropsy on the 20th day of pregnancy, foetuses and implantations were not found in all females. One female at the dose level 1000 mg/kg bw/day became pregnant and then all implanted conceptuses in the uterus were totally resorbed (females without foetuses but with implantations and resorptions). The number of implantations was slightly decreased at the dose level 100 mg/kg bw/day in comparison with the control group. The numbers of corpora lutea were comparable in all treated groups with the control group. At 1000 mg/kg bw/day, there was 1 early resorption in 1 female, 16 early resorptions in 1 female, and 6 early resorptions in 1 female.
The mean body weight of all foetuses was decreased at the dose level 1000 mg/kg bw/day compared to the control foetuses. Male foetuses were heavier than females in all groups. The mean number of foetuses per litter was slightly decreased at dose levels 100 mg/kg bw/day compared to the control group. Also the mean number of female foetuses was markedly decreased at this dose level. Four dead foetuses were recorded at the dose level 1000 mg/kg bw/day. Cranial meningocele, lip cleft and exophthalmos were recorded in one foetus at the dose level 100 mg/kg bw/day. This was considered as a sporadic finding and probably not related to the test item treatment. No other macroscopic changes of soft tissues and external alteration were found during the pathological examination of the foetuses at all dose levels.Based on the results of the DRF, the following doses were selected for the main study: 0, 100, 300 and 1000 mg/kg bw/day.
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