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EC number: 271-237-7 | CAS number: 68526-89-6 A complex combination of hydrocarbons produced by the distillation of products from the hydrogenation of isononanal from the hydroformylation of octene. It consists predominantly of C9-10 primary aliphatic alcohols, C10-20 dimer alcohols, C>18 acetals and esters and C>18 acid sodium salts and boils in the range of approximately 200°C to 400°C (392°F to 752°F).
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 07.04-16.12.2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 014
- Report date:
- 2014
Materials and methods
Test guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- yes
Test material
- Reference substance name:
- Octene, hydroformylation products, high-boiling
- EC Number:
- 271-237-7
- EC Name:
- Octene, hydroformylation products, high-boiling
- Cas Number:
- 68526-89-6
- Molecular formula:
- Unspecified
- IUPAC Name:
- Reaction products of octene, hydroformylation products of C8-alkenes, high boiling
- Details on test material:
- - Name of test material (as cited in study report): Oxooel 9N
- Physical state: liquid
- Analytical purity: 100% UVCB (The identity is confirmed by IR and NMR)
- Lot/batch No.: 93932509T0
- Expiration date of the lot/batch: 18 Sep 2015
- Stability under test conditions: The stability of the test substance under storage conditions over the test period was guaranteed by the sponsor
- Storage condition of test material: room temperature/under N2
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Research Models and Services, Germany GmbH
- Age at study initiation: 10-12 weeks
- Body weight at beginning: 140.3-190.3 g
- Fasting period before study: no
- Housing: rats were housed individually in Makrolon type M III cages supplied by BECKER & CO., Castrop-Rauxel, Germany
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: animals were paired by the breeder and supplied on GD 0 (= detection of vaginal plug/sperm); animals
were acclimated to the laboratory conditions between start of the study (beginning of the experimental phase) and first administration (GD 6).
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24°C
- Humidity (%): 30-70%
- Air changes (per hr): 15 times per hour
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
DIET PREPARATION
- Rate of preparation of diet (frequency): The oily test substance preparations were prepared at the beginning of the administration period and thereafter at intervals, which took into account the period of established stability. The preparations were kept at room temperature
- Diet preparation: the specific amount of test substance was weighed, topped up with corn oil in a graduated flask and intensely mixed by shaking until it is dissolved.
VEHICLE
- Concentration in vehicle: 0, 2500, 7500, 25000 mg/100 ml
- Amount of vehicle (if gavage): 4 ml/kg - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analytical verifications of the stability of the test substance in oil at room temperature over a period of 7 days had been verified prior to the start of the study in a similar batch.
Given that the test substance was completely miscible with corn oil, solutions were considered to be homogenous without further analysis. - Details on mating procedure:
- The animals were paired by the breeder (“time-mated”); the day of evidence of mating (= detection of vaginal plug/sperm) was referred to as GD 0. The animals arrived on the same day (GD 0) at the experimental laboratory. After 6 days acclimatization, treatment started on day 6
- Duration of treatment / exposure:
- gd6-19
- Frequency of treatment:
- once daily
- Duration of test:
- animals were sacrificed on day 20
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 100, 300, 1000 mg/kg/d
Basis:
actual ingested
- No. of animals per sex per dose:
- 25 females
- Control animals:
- yes, concurrent vehicle
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: once daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: once daily
BODY WEIGHT: Yes
- Time schedule for examinations: GD 0-1, 1-3, 3-6, 6-8, 8-10, 10-13, 13-15, 15-17, 17-19 and 19-20 - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yesa
- Number of late resorptions: Yes
- Number of dead fetuses: yes - Fetal examinations:
- - External examinations: Yes: [all per litter]
- Soft tissue examinations: Yes: [half per litter]
- Skeletal examinations: Yes: [half per litter] - Statistics:
- Dunnett test (Food consumptiona), body weight, body weight change, corrected body weight gain (net maternal body weight change), carcass weight, weight of unopened uterus, number of corpora lutea, number of implantations, number of resorptions, number of live fetuses, proportions of preimplantation loss,
proportions of postimplantation loss, proportions of resorptions, proportion of live fetuses in each litter, litter mean fetal body weight, litter mean placental weight)
Siegel test (Female mortality, females pregnant at terminal sacrifice, number of litters with fetal findings)
Nikenhuis/Wilf and Hettmansperger (Proportions of fetuses with malformations, variations and/or unclassified observations in each litter)
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
Two females of treatment group 2 (300 mg/kg/d) and one female assigned to treatment group 3 were not pregenant and hence not taken into account for further analyses.
Mortality: There were no test substance-related or spontaneous mortalities in female animals of any test group (0, 100, 300 or 1000 mg/kg bw/d).
Clinical Observations: Nearly all females (24 out of 25) of the high-dose group (1000 mg/kg bw/d) and some females (11 out of 25) of the mid-dose group (300 mg/kg bw/d) showed transient salivation during the treatment period. Salivation persisted in the respective animals only for some minutes after daily gavage dosing (i.e. up to 10 minutes) and was initially observed on GD 9. From the temporary, short appearance immediately after dosing it was concluded that salivation was induced by a bad taste of the test substance or local affection of the upper digestive tract. This finding was not considered to be an adverse and toxicologically relevant effect. No further clinical signs or changes of general behavior, which may be attributed to the test substance, were detected in any female at dose levels of 100, 300 or 1000 mg/kg bw/d during the entire study period.
Food concumption: The mean food consumption of the high-dose dams (1000 mg/kg bw/d) was significantly increased from GD 13 onwards until scheduled sacrifice on GD 20. However, if calculated for the entire treatment period or the entire study period, the high-dose dams did not consume significantly more food than the concurrent control group. Therefore, the changes were assessed to be incidental and not related to treatment.
Body weight: The mean body weights and the average body weight gains of the low-, mid- and high-dose groups (100, 300 and 1000 mg/kg bw/d) were in general comparable to the controls throughout the entire study period. This includes the significantly increased body weight change value in test group 1 (100 mg/kg bw/d) between GD 13-15. The corrected body weight gain of test groups 1-3 (100, 300 and 1000 mg/kg bw/d) revealed no difference of any biological relevance to the corresponding control group. Moreover, mean carcass weights remained also unaffected by the treatment.
Uterus weight: The mean gravid uterus weights of the animals of test group 1-3 (100, 300 and 1000 mg/kg bw/d) were not influenced by the test substance. The differences between these groups and the control group revealed no dose-dependency and were assessed to be without biological relevance.
Necroscopy: No necropsy findings which could be attributed to the test substance were observed in any dam of the test groups 1, 2 or 3 (100, 300 or 1000 mg/kg bw/d). Two spontaneous findings occurred, i.e. dilated renal pelvis in two females of test group 2 and a diaphragmatic hernia in one female of the same test group. These findings were detected in single animals and were not assessed to be treatment-related.
Reproduction data: The conception rate was 92% in test group 2 (300 mg/kg bw/d), 96% in test group 3 (1000 mg/kg bw/d) and 100% in test groups 0 and 1 (0 and 100 mg/kg bw/d). With these rates, a sufficient number of pregnant females were available for the purpose of the study (according to the test guidelines listed in chapter 2.3.). No test substance-related and/or biologically relevant differences between the test groups 0, 1, 2 and 3 (0, 100, 300 and 1000 mg/kg bw/d) were observed with regard to conception rate, mean number of corpora lutea and implantation sites or the values calculated for the postimplantation loss, the number of resorptions and viable fetuses. All observed differences were considered to reflect the normal range of fluctuations for animals of this strain and age
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day
- Basis for effect level:
- other: no effects observed
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
Sex distribution: The sex distribution of the fetuses in test groups 1-3 (100, 300 and 1000 mg/kg bw/d) was comparable to the control fetuses.
Weight of plancentae: The mean placental weights of the low-, mid- and high-dose groups (100, 300 and 1000 mg/kg bw/d) were comparable to the corresponding control group.
Weight of fetuses: The mean fetal weights of test groups 1, 2 and 3 (100, 300 and 1000 mg/kg bw/d) were not influenced by the test substance and did not show any biologically relevant differences in comparison to the control group.
Fetal external malformations: External malformations were recorded for one fetus of the high-dose group (1000 mg/kg bw/d). Male fetus No. 83-03 had more than one malformation affecting the fetal head, i.e. domed head, anophthalmia, retarded development of right side of head (asymmetric face) and upturned nose. The total incidence of external malformations in treated animals did not differ significantly from the control group and was comparable to the historical control data.
Fetal external variations: One external variation, i.e. limb hyperextension, was detected in test group 1 (100 mg/kg bw/d). This single case was considered to be incidental and not related to treatment.
Fetal external unclassified observations: One unclassified external observation, i.e. placentae fused, was recorded in one fetus of the mid-dose group (300 mg/kg bw/d). This finding was not considered to be biologically relevant.
Fetal soft tissue malformations: Soft tissue malformations were recorded for one low-dose fetus. Female fetus No. 27-12 had more than one malformation affecting the urinary tract, i.e. hydronephrosis and hydroureter. The finding was assessed to be incidental and not related to treatment. There were no further soft tissue malformations in any of the other test groups
Fetal soft tissue variations: Three soft tissue variations were detected, i.e. short innominate, dilated renal pelvis and dilated ureter. These variations were neither significantly different from the control nor dosedependently altered. Therefore, they were not considered to be biologically relevant
Fetal soft tissue unclassified observations: No unclassified soft tissue observations were recorded.
Fetal skeletal malformations: One high-dose male fetus (No. 83-03 – 1000 mg/kg bw/d) showed multiple malformations. In correlation to the external malformations, some skull bones were small on the right side (nasal, frontal and zygomatic bones, zygomatic process). Furthermore, this fetus had malformations affecting the cervical vertebrae and sternebrae. This single case of multiple malformations is considered to be an incidental finding. There were no further skeletal malformations recorded in any fetuses of the test groups 0-3 (0, 100, 300 and 1000 mg/kg bw/d)
Fetal skeletal variations: For all test groups, skeletal variations of different bone structures were observed with or without effects on corresponding cartilages. The observed skeletal variations were related to several parts of fetal skeleton and their incidences were neither significantly different from control nor dose-dependent. Therefore, they were not considered to be biologically relevant. The overall incidences of skeletal variations were comparable to the historical control data. The increased incidences of skeletal variations were neither related to the dose nor were they outside the historical control range. They were in any case not considered as adverse events.
Fetal skeletal unclassified cartilage observations: Additionally, some isolated cartilage findings without impact on the respective bony structures, which were designated as unclassified cartilage observations, occurred in all test groups (table 4.3.4.3.1.). The observed unclassified cartilage findings were related to the skull, the sternum and ribs and did not show any relation to dosing. However, the incidence of bipartite processus xiphoideus was significantly increased in test groups 1 and 3 (100 and 1000 mg/kg bw/d). As a consequence of this occasional increase, also the incidence of total skeletal unclassified cartilage observations was significantly increased in these test groups. However, this finding showed no dose-dependency and was therefore assessed to be without biological relevance.
Assessment of all fetal external, soft tissue and skeletal observations: There were noted external, soft tissue and skeletal malformations in test groups 1 and 3 (100 and 1000 mg/kg bw/d). The distribution of total malformations to the test groups was not related to the doses. Two fetuses were multiple malformed: low-dose female fetus No. 27-12 (100 mg/kg bw/d) had more than one visceral malformation affecting the urinary tract, i.e. hydronephrosis and hydroureter, while the findings in high-dose male fetus No. 83-03 (1000 mg/kg bw/d) consisted of multiple external malformations affecting the fetal head (domed head, anophthalmia, development of right side of head retarded [asymmetric face] and upturned nose) and multiple skeletal malformations affecting the skull, cervical vertebrae and sternebrae (small nasal, frontal and zygomatic bones, small zygomatic process, cervical hemivertebra, malpositioned and bipartite sternebrae). No ontogenetic pattern was recognizable for the individual malformations nor was there any cluster of any of these individual malformations seen in the other offspring of these test groups. One external variation, three soft tissue variations and a broad range of skeletal variations occurred in all test groups including the controls. None of the incidences showed a relation to dosing. The majority of the skeletal variations were equally distributed among the different test groups, if normal biological variation is taken into account, and can be found in the historical control data at a comparable frequency
Total fetal variations: No unclassified soft tissue observations were recorded for any of the fetuses in this study. A spontaneous origin was assumed for the unclassified external observation, which was observed in one fetus of test group 2 (300 mg/kg bw/d). This isolated finding did not suggest any relation to treatment. Several unclassified skeletal cartilage observations were observed in several fetuses of test groups 0-3 (0, 100, 300 and 1000 mg/kg bw/d). Although the total incidences in test groups 1 and 3 were significantly increased, a relation to treatment was not assumed, because these findings were not related to the dose and can be found in the historical control data. Finally, fetal examinations revealed that there was no effect of the compound on the respective morphological structures up to the highest dose tested (1000 mg/kg bw/d).
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day
- Basis for effect level:
- other: no effects observed
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of this prenatal developmental toxicity study, the oral administration of Oxooel 9N to pregnant Wistar rats from implantation to one day prior to the expected day of parturition (GD 6-19) at a dose of 1000 mg/kg bw/d caused no evidence of maternal toxicity.
In addition, no toxicologically relevant adverse fetal findings were evident. In conclusion, the no observed adverse effect level (NOAEL) for maternal toxicity was 1000 mg/kg bw/d, the highest dose tested. The no observed adverse effect level (NOAEL) for prenatal developmental toxicity was also 1000 mg/kg bw/d.
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