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EC number: 931-293-1 | CAS number: 1335202-78-2
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11 February 2015 - 26 March 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted according to OECD 414 Guideline and GLP conditions. Fully adequate for assessment.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in Section 13.
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- developmental toxicity
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 11 February 2015 - 26 March 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted according to OECD 414 Guideline and GLP conditions. Fully adequate for assessment.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- Deviation did not affect the purpose or integrity of the study.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3700 (Prenatal Developmental Toxicity Study)
- Qualifier:
- according to guideline
- Guideline:
- other: Japanese Ministry of Agriculture, Forestry and Fisheries Testing guidelines for Toxicology studies, 12 NohSan No 8147, (24 November 2000)
- Qualifier:
- according to guideline
- Guideline:
- other: Commission Regulation (EC) No 440/2008 of 30 May 2008 test methods pursuant to Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- - Test Material: Octadecene
- CAS Number: CAS 27070-58-2
- Physical State/Appearance : Clear colorless liquid
- Molecular Formula: C18 Isomerized Olefin
- Purity: 94.1%
- Batch Number: 747273
- Label: C18 Isomerised Olefin Lot 747273
- Date Received: 3 March 2014
- Storage Conditions: Room temperature, in the dark and under nitrogen (after opening the container)
- Expiry Date: 10 February 2016
Octadecene used in this study was a typical production sample, according to the details included in the boundary composition in IUCLID section 1.2. Octadecene was chosen in the Higher Olefins category testing strategy because it represents a substance with high di-sub content (category range 0.3 – 94%) and high tri-sub content (category range 1 - 65%). Please see the testing strategy attached in section 13 for further details. - Species:
- rat
- Strain:
- other: Sprague-Dawley Crl:CD (SD) IGS BR strain
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River (UK) Limited, Margate, Kent
- Age at study initiation: not specified
- Weight at study initiation: 180 to 284g.
- Housing: solid-floor polypropylene cages with stainless steel mesh lids furnished with softwood flakes
- Diet (e.g. ad libitum): A pelleted diet (Rodent 2018C Teklad Global Certified Diet, Harlan UK, Oxon, UK) - free access
- Water (e.g. ad libitum): freely available
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3 ºC
- Humidity (%): 50 ± 20%
- Air changes (per hr): 15 air changes per hr
- Photoperiod (hrs dark / hrs light): 12 hr light/12 hr dark
Experimental Starting Date: 11 February 2015
Experimental Completion Date: 26 March 2015
Justification for specie selection: the selected species is a readily available rodent species historically used in safety evaluation studies and is acceptable to appropriate regulatory authorities.
IN-LIFE DATES: From 11 February 2015 to 26 March 2015 - Route of administration:
- oral: gavage
- Vehicle:
- arachis oil
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): Formulations were prepared once.
- Mixing appropriate amounts with (Type of food): The appropriate concentrations were prepared in Arachis oil solutions.
- Storage temperature of food: Stored at approximately +4 °C in the dark. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The stability and homogeneity of the test item formulations were previously determined by Harlan Laboratories Ltd., Shardlow, UK Analytical Services (Project Number 41301656 - Octadecene CAS 27070-58-2: Ninety Day Repeated Dose Oral (Gavage) Toxicity Study in Rats). The results indicate that the prepared formulations were within 90-103% of the nominal concentration confirming the accuracy of the formulation procedure.
- Details on mating procedure:
- Female animals were delivered in two batches prior to Day 3 of gestation. The day that positive evidence of mating was observed was designated Day 0 of gestation.
- Duration of treatment / exposure:
- From Day 5 to Day 19 of gestation, by gavage
- Frequency of treatment:
- Daily
- Duration of test:
- From Day 5 to Day 19 of gestation
- Dose / conc.:
- 100 mg/kg bw/day
- Dose / conc.:
- 300 mg/kg bw/day
- Dose / conc.:
- 1 000 mg/kg bw/day
- No. of animals per sex per dose:
- 24 Females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Dose levels were selected based on available toxicity data including a dose range finding study (Harlan Laboratories Ltd report number 41403655)
- Maternal examinations:
- CAGE SIDE OBSERVATIONS:
Once daily during the gestation period. During the dosing period, observations were recorded immediately before and soon after dosing and one hour post dosing.
BODY WEIGHT:
Individual body weights were recorded on Day 3 (prior to dosing) and on Days 5, 6, 7, 8, 11, 14 and 17 of gestation of gestation, including for surviving animals at terminal kill (Day 20).
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
Food consumption was recorded for each surviving individual animal at Day 3, 5, 8, 11, 14, 17 and 20 of gestation.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study):
Daily by visual inspection of the water bottles for any overt changes.
POST-MORTEM EXAMINATIONS: Yes
- Full external and internal examination ( any macroscopic abnormalities were recorded).
- Ovaries and uterine content:
- Ovaries and uteri examinations:
i) Number of corpora lutea
ii) Number, position and type of intrauterine implantation
iii) Fetal sex
iv) External fetal appearance
v) Fetal weight
vi) Placental weight
vii) Gravid uterus weight - Fetal examinations:
- - Fetal external findings
- Visceral findings
- Skeletal findings and skeletal development
- Number of implantations
- Embryofetal survival
- Litter size
- Sex ratio
- Mean fetal litter and placental weights - Statistics:
- The following parameters were analyzed statistically, where appropriate, using the test methods outlined below:
Body weight and body weight change (including adjustment for the contribution of the gravid uterus), food consumption, gravid uterus weight, litter data and fetal litter and placental weights.
Data were first analysed using Shapiro Wilk normality test and Bartlett’s test for homogeneity of variance. Where there was no significance, parametric methodology was applied using one way analysis of variance and, if significant, Dunnett’s multiple comparison test. Where statistical significance was observed, non parametric methodology was applied using Kruskal-Wallis nonparametric analysis of variance; and, if significant, pairwise analysis of control values against treated values using the Mann-Whitney ‘U’ test. Due to the preponderance of non-normal distributions for litter/fetal parameters, these data were routinely analyzed using non-parametric methodology.
Fetal morphology parameters, including skeletal or visceral findings were generally analysed by Kruskal- Wallis and, if significant, Mann-Whitney ‘U’ test.
Probability values (p) are presented as follows:
p<0.001 ***
p<0.01 **
p<0.05 *
p=0.05 (not significant) - Indices:
- Percentage pre-implantation loss
Percentage post-implantation loss
Sex ratio - Clinical signs:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No clinical signs of toxicity were detected.
One control female and one female treated with 300 mg/kg bw/day exhibited generalized fur loss. A further animal treated with 300 mg/kg bw/day also exhibited fur staining. In the absence of findings for high dose females, these observations were considered to be incidental and unrelated to treatment. - Mortality:
- no mortality observed
- Description (incidence):
- There were no unscheduled deaths.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Body weight and body weight gain, including adjustment for the contribution of the gravid uterus, were unaffected by treatment at 100, 300 or 1000 mg/kg bw/day.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Food consumption during gestation was unaffected by treatment at 100, 300 or 1000 mg/kg bw/day.
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Description (incidence and severity):
- Daily visual inspection of water bottles did not reveal any overt intergroup differences.
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry 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:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Findings observed at macroscopic necropsy did not indicate any effect of treatment. One control female exhibited generalized fur loss. In the absence of similar findings in high dose females this observation was considered to be incidental and unrelated to treatment.
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
- Other effects:
- no effects observed
- Description (incidence and severity):
- The number of implantations, subsequent embryofetal survival and litter size, sex ratio and mean fetal, litter and placental weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
No maternal toxicity - Key result
- Dose descriptor:
- NOEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: Systemic Toxicity
- Key result
- Abnormalities:
- no effects observed
- Fetal body weight changes:
- no effects observed
- Description (incidence and severity):
- Mean fetal, litter and placental weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
Migrated Data from removed field(s)
Field "Fetal/pup body weight changes" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.FetalPupBodyWeightChanges): no effects observed
Field "Description (incidence and severity)" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.DescriptionIncidenceAndSeverityFetalPupBodyWeightChanges): Mean fetal, litter and placental weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day. - Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- Sex ratio on Day 20 of gestation was unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- Changes in litter size and weights:
- no effects observed
- Description (incidence and severity):
- Litter size and weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- Changes in postnatal survival:
- no effects observed
- Description (incidence and severity):
- Embryofetal survival was unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- External malformations:
- no effects observed
- Description (incidence and severity):
- Neither the type, incidence or distribution of findings observed during external examination of the fetuses at necropsy on Day 20 of gestation indicated any adverse effect of maternal treatment on fetal development.
- Skeletal malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- Neither the type, incidence or distribution of findings observed during external examination of the fetuses at necropsy on Day 20 of gestation and subsequent detailed visceral and skeletal examination indicated any adverse effect of maternal treatment on fetal development.
Intergroup differences for some skeletal parametersoccasionally attained statistical significance but these isolated differences were considered incidental and did not indicate any disturbance of fetal development. - Visceral malformations:
- no effects observed
- Description (incidence and severity):
- Neither the type, incidence or distribution of findings observed during external examination of the fetuses at necropsy on Day 20 of gestation and subsequent detailed visceral and skeletal examination indicated any adverse effect of maternal treatment on fetal development.
- Other effects:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
No embryotoxic/teratogenic effects - Key result
- Dose descriptor:
- NOEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Developmental Toxicity
- Key result
- Abnormalities:
- no effects observed
- Key result
- Developmental effects observed:
- no
- Conclusions:
- Based on the result of the study, the ‘No Observed Effect Level' (NOEL) for the pregnant female and the ‘No Observed Effect Level' (NOEL) for developmental toxicity is considered to be 1000 mg/kg bw/day.
- Executive summary:
In a key Guideline (OECD 414) pre-natal developmental toxicity study, the test material (Octadecene; CAS# 27070-58-2) was administered by gavage to three groups each of twenty-four time mated Sprague-Dawley Crl:CD® (SD) IGS BR strain rats, between Days 5 and 19 of gestation inclusive at dose levels 100, 300, and 1000 mg/Kg bw/day. A further group of twenty-four time mated females was exposed to the vehicle only (Arachis Oil BP) to serve as a control over the same treatment period.
Clinical signs, body weight change, food and water consumptions were monitored during the study. All females were terminated on Day 20 of gestation and subjected to gross necropsy including examination of the uterine contents. The number of
corpora lutea, number, position and type of implantation, placental weights, fetal weight, sex and external and internal macroscopic appearance were recorded. Half of each litter were examined for detailed skeletal development and the remaining half were subjected to detailed visceral examination.
No mortality was observed through the study period and oral administration of the test material to pregnant rats by oral gavage during gestation at dose levels of 100, 300 and 1000 mg/Kg bw/day did not result in any treatment related effects. The No
Observed Effect Level' (NOEL) for the pregnant female was considered to be 1000 mg/Kg bw/day.
No treatment-related changes were detected in the offspring parameters measured. The ‘No Observed Effect Level’ (NOEL) for developmental toxicity was therefore considered to be 1000 mg/Kg bw/day.
Table 2. Summary of Female Performance |
||||
Category |
Number of Females at Dose Level (mg/kg bw/day) |
|||
0 (control) |
100 |
300 |
1000 |
|
Initial Group Size |
24 |
24 |
24 |
24 |
Pregnant |
24 |
24 |
24 |
24 |
Table 3. Group Mean Gravid Uterus Weight and Adjusted Body Weight and Body Weight Change Values |
|||||||
Dose Level (mg/Kg bw/day) |
|
Body Weight (g) on Days of Gestation |
Body Weight Change (g) during Days of Gestation |
Gravid Uterus Weight (g) |
Adjusted Body Weight (g) Day 20 |
Adjusted Body Weight (g) Change
|
|
5 |
20 |
5-20 |
Day 20 |
5-20 |
|||
0 (control) |
Mean |
255.7 |
374.5 |
118.8 |
83.667 |
290.8 |
35.1 |
Sd |
30.7 |
48.6 |
21.4 |
12.753 |
39.0 |
12.5 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
|||||||
100 |
Mean |
256.7 |
381.8 |
125.0 |
86.848 |
294.9 |
38.2 |
Sd |
22.4 |
31.2 |
18.5 |
11.060 |
26.7 |
13.2 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
|||||||
300 |
Mean |
258.8 |
380.0 |
121.2 |
87.820 |
292.2 |
33.4 |
Sd |
20.4 |
24.7 |
14.1 |
8.848 |
22.8 |
10.6 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
|||||||
1000 |
Mean |
257.8 |
374.1 |
116.3 |
81.928 |
292.2 |
34.3 |
Sd |
24.6 |
39.6 |
19.9 |
15.792 |
31.6 |
13.0 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
Table 4. Group Mean Litter Data Values |
||||||||||||||||||
Dose Level (mg/Kg bw/day) |
|
Number of Corpora Lutea |
Number of Implants |
Number of Embryonic/Fetal Deaths |
Implantation Loss % |
Number of Live Implants |
% Male Fetuses |
Mean Male Fetal Weight (g) |
Mean Female Fetal Weight (g) |
Mean Fetal Weight (g) |
Mean Placental Weight (g) |
Litter Weight (g) |
Total Placental Weight (g) |
|||||
Early |
Late |
Total |
Pre |
Post |
Male |
Female |
Total |
|||||||||||
0 (control) |
Mean |
13.9 |
13.5 |
0.2 |
0.2 |
0.4 |
2.3 |
2.9 |
7.3 |
5.8 |
13.2 |
55.3 |
4.185 |
3.981 |
4.092 |
0.569 |
53.555 |
7.478 |
Sd |
2.0 |
1.9 |
0.5 |
0.7 |
1.1 |
3.9 |
8.1 |
2.0 |
1.5 |
2.3 |
9.7 |
0.255 |
0.273 |
0.253 |
0.057 |
7.966 |
1.392 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
||||||||||||||||||
100 |
Mean |
14.3 |
14.0 |
0.2 |
0.0 |
0.2 |
2.4 |
1.6 |
6.5 |
7.3 |
13.8 |
47.2 |
4.122 |
3.917 |
4.012 |
0.559 |
55.012 |
7.656 |
Sd |
1.9 |
1.9 |
0.5 |
0.2 |
0.7 |
5.4 |
5.0 |
2.2 |
2.1 |
2.0 |
13.7 |
0.218 |
0.196 |
0.196 |
0.048 |
7.555 |
1.166 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
||||||||||||||||||
300 |
Mean |
14.7 |
14.3 |
0.1 |
0.0 |
0.1 |
2.2 |
2.1 |
7.5 |
6.5 |
14.0 |
53.4 |
4.126 |
3.909 |
4.027 |
0.563 |
56.340 |
7.873 |
Sd |
1.4 |
1.5 |
0.4 |
0.0 |
0.4 |
4.3 |
6.7 |
1.9 |
2.0 |
1.5 |
13.6 |
0.194 |
0.181 |
0.177 |
0.061 |
6.343 |
1.098 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
||||||||||||||||||
1000 |
Mean |
13.9 |
13.5 |
0.4 |
0.0 |
0.5 |
3.4 |
3.6 |
6.3 |
6.7 |
13.0 |
49.0 |
4.127 |
3.925 |
4.023 |
0.557 |
52.280 |
7.200 |
Sd |
1.7 |
2.4 |
0.8 |
0.2 |
0.8 |
11.2 |
6.6 |
1.9 |
2.1 |
2.6 |
11.4 |
0.250 |
0.214 |
0.232 |
0.059 |
10.888 |
1.550 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
Table 5. Summary Incidence of Fetal Skeletal Findings |
||||||||||||
Skeletal Findings |
Dose Level (mg/kg bw/day) |
|||||||||||
0 (control) |
100 |
300 |
1000 |
|||||||||
Number of Fetuses (litters) Examined |
||||||||||||
150 (24) |
160 (24) |
162 (24) |
150 (24) |
|||||||||
NF |
NL |
%† |
NF |
NL |
%† |
NF |
NL |
%† |
NF |
NL |
%† |
|
Skull |
|
|||||||||||
Hyoid - incomplete ossification |
21 |
13 |
14.0 |
22 |
13 |
13.8 |
12 |
8 |
7.2 |
6 |
6 |
3.8* |
Vertebral Column |
|
|||||||||||
Number of pre-sacral vertebrae = 25/27 |
0 |
0 |
0.0 |
0 |
0 |
0.0 |
4 |
4 |
2.7* |
0 |
0 |
0.0 |
* Significantly different from control group p<0.05
Table 6. Historical Data - Charles River (UK) Limited - Normal Ranges for Pre-Natal Study Skeletal Fetal Findings in the Sprague-Dawley Crl:CD®(SD) IGS BR Rat |
||
Skeletal findings |
Range ** Group mean % of fetuses affected |
No. of Litters {fetuses} examined |
Hyoid - incomplete ossification |
5 (11.5) - 18.4 [4.0] |
255 {1605} |
|
||
Number of pre-sacral vertebrae = 25/27 |
0 (0.4) – 2.7 [0.8] |
255 {1605} |
** Range = minimum to maximum value ( ) = group mean [ ] = 1 standard deviation
Where the range exceeds the minimum or maximum possible physiological values, the minimum or maximum physiological values are presented.
Data shown are recorded for presentation purposes, therefore it is not always possible to calculate the range exactly from the mean and SD presented.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 015
- Report date:
- 2015
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- Deviation did not affect the purpose or integrity of the study.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3700 (Prenatal Developmental Toxicity Study)
- Qualifier:
- according to guideline
- Guideline:
- other: Japanese Ministry of Agriculture, Forestry and Fisheries Testing guidelines for Toxicology studies, 12 NohSan No 8147, (24 November 2000)
- Qualifier:
- according to guideline
- Guideline:
- other: Commission Regulation (EC) No 440/2008 of 30 May 2008 test methods pursuant to Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Octadecene
- EC Number:
- 248-205-6
- EC Name:
- Octadecene
- Cas Number:
- 27070-58-2
- Molecular formula:
- C18H36
- IUPAC Name:
- octadecene
- Test material form:
- other: Clear colorless liquid
- Details on test material:
- - Test Material: Octadecene
- CAS Number: CAS 27070-58-2
- Physical State/Appearance : Clear colorless liquid
- Molecular Formula: C18 Isomerized Olefin
- Purity: 94.1%
- Batch Number: 747273
- Label: C18 Isomerised Olefin Lot 747273
- Date Received: 3 March 2014
- Storage Conditions: Room temperature, in the dark and under nitrogen (after opening the container)
- Expiry Date: 10 February 2016
Constituent 1
- Specific details on test material used for the study:
- - Test Material: Octadecene
- CAS Number: CAS 27070-58-2
- Physical State/Appearance : Clear colorless liquid
- Molecular Formula: C18 Isomerized Olefin
- Purity: 94.1%
- Batch Number: 747273
- Label: C18 Isomerised Olefin Lot 747273
- Date Received: 3 March 2014
- Storage Conditions: Room temperature, in the dark and under nitrogen (after opening the container)
- Expiry Date: 10 February 2016
Octadecene used in this study was a typical production sample, according to the details included in the boundary composition in IUCLID section 1.2. Octadecene was chosen in the Higher Olefins category testing strategy because it represents a substance with high di-sub content (category range 0.3 – 94%) and high tri-sub content (category range 1 - 65%). Please see the testing strategy attached in section 13 for further details.
Test animals
- Species:
- rat
- Strain:
- other: Sprague-Dawley Crl:CD (SD) IGS BR strain
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River (UK) Limited, Margate, Kent
- Age at study initiation: not specified
- Weight at study initiation: 180 to 284g.
- Housing: solid-floor polypropylene cages with stainless steel mesh lids furnished with softwood flakes
- Diet (e.g. ad libitum): A pelleted diet (Rodent 2018C Teklad Global Certified Diet, Harlan UK, Oxon, UK) - free access
- Water (e.g. ad libitum): freely available
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3 ºC
- Humidity (%): 50 ± 20%
- Air changes (per hr): 15 air changes per hr
- Photoperiod (hrs dark / hrs light): 12 hr light/12 hr dark
Experimental Starting Date: 11 February 2015
Experimental Completion Date: 26 March 2015
Justification for specie selection: the selected species is a readily available rodent species historically used in safety evaluation studies and is acceptable to appropriate regulatory authorities.
IN-LIFE DATES: From 11 February 2015 to 26 March 2015
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- arachis oil
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): Formulations were prepared once.
- Mixing appropriate amounts with (Type of food): The appropriate concentrations were prepared in Arachis oil solutions.
- Storage temperature of food: Stored at approximately +4 °C in the dark. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The stability and homogeneity of the test item formulations were previously determined by Harlan Laboratories Ltd., Shardlow, UK Analytical Services (Project Number 41301656 - Octadecene CAS 27070-58-2: Ninety Day Repeated Dose Oral (Gavage) Toxicity Study in Rats). The results indicate that the prepared formulations were within 90-103% of the nominal concentration confirming the accuracy of the formulation procedure.
- Details on mating procedure:
- Female animals were delivered in two batches prior to Day 3 of gestation. The day that positive evidence of mating was observed was designated Day 0 of gestation.
- Duration of treatment / exposure:
- From Day 5 to Day 19 of gestation, by gavage
- Frequency of treatment:
- Daily
- Duration of test:
- From Day 5 to Day 19 of gestation
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day
- Dose / conc.:
- 300 mg/kg bw/day
- Dose / conc.:
- 1 000 mg/kg bw/day
- No. of animals per sex per dose:
- 24 Females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Dose levels were selected based on available toxicity data including a dose range finding study (Harlan Laboratories Ltd report number 41403655)
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS:
Once daily during the gestation period. During the dosing period, observations were recorded immediately before and soon after dosing and one hour post dosing.
BODY WEIGHT:
Individual body weights were recorded on Day 3 (prior to dosing) and on Days 5, 6, 7, 8, 11, 14 and 17 of gestation of gestation, including for surviving animals at terminal kill (Day 20).
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
Food consumption was recorded for each surviving individual animal at Day 3, 5, 8, 11, 14, 17 and 20 of gestation.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study):
Daily by visual inspection of the water bottles for any overt changes.
POST-MORTEM EXAMINATIONS: Yes
- Full external and internal examination ( any macroscopic abnormalities were recorded).
- Ovaries and uterine content:
- Ovaries and uteri examinations:
i) Number of corpora lutea
ii) Number, position and type of intrauterine implantation
iii) Fetal sex
iv) External fetal appearance
v) Fetal weight
vi) Placental weight
vii) Gravid uterus weight - Fetal examinations:
- - Fetal external findings
- Visceral findings
- Skeletal findings and skeletal development
- Number of implantations
- Embryofetal survival
- Litter size
- Sex ratio
- Mean fetal litter and placental weights - Statistics:
- The following parameters were analyzed statistically, where appropriate, using the test methods outlined below:
Body weight and body weight change (including adjustment for the contribution of the gravid uterus), food consumption, gravid uterus weight, litter data and fetal litter and placental weights.
Data were first analysed using Shapiro Wilk normality test and Bartlett’s test for homogeneity of variance. Where there was no significance, parametric methodology was applied using one way analysis of variance and, if significant, Dunnett’s multiple comparison test. Where statistical significance was observed, non parametric methodology was applied using Kruskal-Wallis nonparametric analysis of variance; and, if significant, pairwise analysis of control values against treated values using the Mann-Whitney ‘U’ test. Due to the preponderance of non-normal distributions for litter/fetal parameters, these data were routinely analyzed using non-parametric methodology.
Fetal morphology parameters, including skeletal or visceral findings were generally analysed by Kruskal- Wallis and, if significant, Mann-Whitney ‘U’ test.
Probability values (p) are presented as follows:
p<0.001 ***
p<0.01 **
p<0.05 *
p=0.05 (not significant) - Indices:
- Percentage pre-implantation loss
Percentage post-implantation loss
Sex ratio
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No clinical signs of toxicity were detected.
One control female and one female treated with 300 mg/kg bw/day exhibited generalized fur loss. A further animal treated with 300 mg/kg bw/day also exhibited fur staining. In the absence of findings for high dose females, these observations were considered to be incidental and unrelated to treatment. - Mortality:
- no mortality observed
- Description (incidence):
- There were no unscheduled deaths.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Body weight and body weight gain, including adjustment for the contribution of the gravid uterus, were unaffected by treatment at 100, 300 or 1000 mg/kg bw/day.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Food consumption during gestation was unaffected by treatment at 100, 300 or 1000 mg/kg bw/day.
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Description (incidence and severity):
- Daily visual inspection of water bottles did not reveal any overt intergroup differences.
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry 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:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Findings observed at macroscopic necropsy did not indicate any effect of treatment. One control female exhibited generalized fur loss. In the absence of similar findings in high dose females this observation was considered to be incidental and unrelated to treatment.
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
Maternal developmental toxicity
- Other effects:
- no effects observed
- Description (incidence and severity):
- The number of implantations, subsequent embryofetal survival and litter size, sex ratio and mean fetal, litter and placental weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
No maternal toxicity
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: Systemic Toxicity
Maternal abnormalities
- Key result
- Abnormalities:
- no effects observed
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Description (incidence and severity):
- Mean fetal, litter and placental weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
Migrated Data from removed field(s)
Field "Fetal/pup body weight changes" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.FetalPupBodyWeightChanges): no effects observed
Field "Description (incidence and severity)" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.DescriptionIncidenceAndSeverityFetalPupBodyWeightChanges): Mean fetal, litter and placental weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day. - Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- Sex ratio on Day 20 of gestation was unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- Changes in litter size and weights:
- no effects observed
- Description (incidence and severity):
- Litter size and weights on Day 20 of gestation were unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- Changes in postnatal survival:
- no effects observed
- Description (incidence and severity):
- Embryofetal survival was unaffected by maternal treatment at 100, 300 and 1000 mg/kg bw/day.
- External malformations:
- no effects observed
- Description (incidence and severity):
- Neither the type, incidence or distribution of findings observed during external examination of the fetuses at necropsy on Day 20 of gestation indicated any adverse effect of maternal treatment on fetal development.
- Skeletal malformations:
- effects observed, treatment-related
- Description (incidence and severity):
- Neither the type, incidence or distribution of findings observed during external examination of the fetuses at necropsy on Day 20 of gestation and subsequent detailed visceral and skeletal examination indicated any adverse effect of maternal treatment on fetal development.
Intergroup differences for some skeletal parametersoccasionally attained statistical significance but these isolated differences were considered incidental and did not indicate any disturbance of fetal development. - Visceral malformations:
- no effects observed
- Description (incidence and severity):
- Neither the type, incidence or distribution of findings observed during external examination of the fetuses at necropsy on Day 20 of gestation and subsequent detailed visceral and skeletal examination indicated any adverse effect of maternal treatment on fetal development.
- Other effects:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
No embryotoxic/teratogenic effects
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Developmental Toxicity
Fetal abnormalities
- Key result
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Key result
- Developmental effects observed:
- no
Any other information on results incl. tables
Table 2. Summary of Female Performance |
||||
Category |
Number of Females at Dose Level (mg/kg bw/day) |
|||
0 (control) |
100 |
300 |
1000 |
|
Initial Group Size |
24 |
24 |
24 |
24 |
Pregnant |
24 |
24 |
24 |
24 |
Table 3. Group Mean Gravid Uterus Weight and Adjusted Body Weight and Body Weight Change Values |
|||||||
Dose Level (mg/Kg bw/day) |
|
Body Weight (g) on Days of Gestation |
Body Weight Change (g) during Days of Gestation |
Gravid Uterus Weight (g) |
Adjusted Body Weight (g) Day 20 |
Adjusted Body Weight (g) Change
|
|
5 |
20 |
5-20 |
Day 20 |
5-20 |
|||
0 (control) |
Mean |
255.7 |
374.5 |
118.8 |
83.667 |
290.8 |
35.1 |
Sd |
30.7 |
48.6 |
21.4 |
12.753 |
39.0 |
12.5 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
|||||||
100 |
Mean |
256.7 |
381.8 |
125.0 |
86.848 |
294.9 |
38.2 |
Sd |
22.4 |
31.2 |
18.5 |
11.060 |
26.7 |
13.2 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
|||||||
300 |
Mean |
258.8 |
380.0 |
121.2 |
87.820 |
292.2 |
33.4 |
Sd |
20.4 |
24.7 |
14.1 |
8.848 |
22.8 |
10.6 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
|||||||
1000 |
Mean |
257.8 |
374.1 |
116.3 |
81.928 |
292.2 |
34.3 |
Sd |
24.6 |
39.6 |
19.9 |
15.792 |
31.6 |
13.0 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
Table 4. Group Mean Litter Data Values |
||||||||||||||||||
Dose Level (mg/Kg bw/day) |
|
Number of Corpora Lutea |
Number of Implants |
Number of Embryonic/Fetal Deaths |
Implantation Loss % |
Number of Live Implants |
% Male Fetuses |
Mean Male Fetal Weight (g) |
Mean Female Fetal Weight (g) |
Mean Fetal Weight (g) |
Mean Placental Weight (g) |
Litter Weight (g) |
Total Placental Weight (g) |
|||||
Early |
Late |
Total |
Pre |
Post |
Male |
Female |
Total |
|||||||||||
0 (control) |
Mean |
13.9 |
13.5 |
0.2 |
0.2 |
0.4 |
2.3 |
2.9 |
7.3 |
5.8 |
13.2 |
55.3 |
4.185 |
3.981 |
4.092 |
0.569 |
53.555 |
7.478 |
Sd |
2.0 |
1.9 |
0.5 |
0.7 |
1.1 |
3.9 |
8.1 |
2.0 |
1.5 |
2.3 |
9.7 |
0.255 |
0.273 |
0.253 |
0.057 |
7.966 |
1.392 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
||||||||||||||||||
100 |
Mean |
14.3 |
14.0 |
0.2 |
0.0 |
0.2 |
2.4 |
1.6 |
6.5 |
7.3 |
13.8 |
47.2 |
4.122 |
3.917 |
4.012 |
0.559 |
55.012 |
7.656 |
Sd |
1.9 |
1.9 |
0.5 |
0.2 |
0.7 |
5.4 |
5.0 |
2.2 |
2.1 |
2.0 |
13.7 |
0.218 |
0.196 |
0.196 |
0.048 |
7.555 |
1.166 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
||||||||||||||||||
300 |
Mean |
14.7 |
14.3 |
0.1 |
0.0 |
0.1 |
2.2 |
2.1 |
7.5 |
6.5 |
14.0 |
53.4 |
4.126 |
3.909 |
4.027 |
0.563 |
56.340 |
7.873 |
Sd |
1.4 |
1.5 |
0.4 |
0.0 |
0.4 |
4.3 |
6.7 |
1.9 |
2.0 |
1.5 |
13.6 |
0.194 |
0.181 |
0.177 |
0.061 |
6.343 |
1.098 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
|
|
||||||||||||||||||
1000 |
Mean |
13.9 |
13.5 |
0.4 |
0.0 |
0.5 |
3.4 |
3.6 |
6.3 |
6.7 |
13.0 |
49.0 |
4.127 |
3.925 |
4.023 |
0.557 |
52.280 |
7.200 |
Sd |
1.7 |
2.4 |
0.8 |
0.2 |
0.8 |
11.2 |
6.6 |
1.9 |
2.1 |
2.6 |
11.4 |
0.250 |
0.214 |
0.232 |
0.059 |
10.888 |
1.550 |
|
n |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
24 |
Table 5. Summary Incidence of Fetal Skeletal Findings |
||||||||||||
Skeletal Findings |
Dose Level (mg/kg bw/day) |
|||||||||||
0 (control) |
100 |
300 |
1000 |
|||||||||
Number of Fetuses (litters) Examined |
||||||||||||
150 (24) |
160 (24) |
162 (24) |
150 (24) |
|||||||||
NF |
NL |
%† |
NF |
NL |
%† |
NF |
NL |
%† |
NF |
NL |
%† |
|
Skull |
|
|||||||||||
Hyoid - incomplete ossification |
21 |
13 |
14.0 |
22 |
13 |
13.8 |
12 |
8 |
7.2 |
6 |
6 |
3.8* |
Vertebral Column |
|
|||||||||||
Number of pre-sacral vertebrae = 25/27 |
0 |
0 |
0.0 |
0 |
0 |
0.0 |
4 |
4 |
2.7* |
0 |
0 |
0.0 |
* Significantly different from control group p<0.05
Table 6. Historical Data - Charles River (UK) Limited - Normal Ranges for Pre-Natal Study Skeletal Fetal Findings in the Sprague-Dawley Crl:CD®(SD) IGS BR Rat |
||
Skeletal findings |
Range ** Group mean % of fetuses affected |
No. of Litters {fetuses} examined |
Hyoid - incomplete ossification |
5 (11.5) - 18.4 [4.0] |
255 {1605} |
|
||
Number of pre-sacral vertebrae = 25/27 |
0 (0.4) – 2.7 [0.8] |
255 {1605} |
** Range = minimum to maximum value ( ) = group mean [ ] = 1 standard deviation
Where the range exceeds the minimum or maximum possible physiological values, the minimum or maximum physiological values are presented.
Data shown are recorded for presentation purposes, therefore it is not always possible to calculate the range exactly from the mean and SD presented.
Applicant's summary and conclusion
- Conclusions:
- Based on the result of the study, the ‘No Observed Effect Level' (NOEL) for the pregnant female and the ‘No Observed Effect Level' (NOEL) for developmental toxicity is considered to be 1000 mg/kg bw/day.
- Executive summary:
In a key Guideline (OECD 414) pre-natal developmental toxicity study, the test material (Octadecene; CAS# 27070-58-2) was administered by gavage to three groups each of twenty-four time mated Sprague-Dawley Crl:CD® (SD) IGS BR strain rats, between Days 5 and 19 of gestation inclusive at dose levels 100, 300, and 1000 mg/Kg bw/day. A further group of twenty-four time mated females was exposed to the vehicle only (Arachis Oil BP) to serve as a control over the same treatment period.
Clinical signs, body weight change, food and water consumptions were monitored during the study. All females were terminated on Day 20 of gestation and subjected to gross necropsy including examination of the uterine contents. The number of
corpora lutea, number, position and type of implantation, placental weights, fetal weight, sex and external and internal macroscopic appearance were recorded. Half of each litter were examined for detailed skeletal development and the remaining half were subjected to detailed visceral examination.
No mortality was observed through the study period and oral administration of the test material to pregnant rats by oral gavage during gestation at dose levels of 100, 300 and 1000 mg/Kg bw/day did not result in any treatment related effects. The No
Observed Effect Level' (NOEL) for the pregnant female was considered to be 1000 mg/Kg bw/day.
No treatment-related changes were detected in the offspring parameters measured. The ‘No Observed Effect Level’ (NOEL) for developmental toxicity was therefore considered to be 1000 mg/Kg bw/day.
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