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EC number: 247-979-2 | CAS number: 26761-45-5
- 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
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- 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
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- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
No other data is available.
Additional information
An O.E.C.D. 443 Testing Guideline Extended One Generation Reproduction Toxicity Study in rats is proposed pending approval of the Stubstance Test Plan by the E.C.H.A.
A NOAEL of approximately 100 mg.kg/day was observed in the rat 90 -day oral study that did not demonstrate any histopthological evidence of adverse reproductive effects. This oral value is corrected to a human inhalation value of approximately 88.2 mg/m3 following ECHA Guidance (ECHA RIP 3.2, Chapter R.8: Characterization of dose [concentration]-response for human health. Fugure R. 8 -3, page 27). Following ECHA Guidance the Assessment Factors applied are: Interspecies = 2.5x; Intraspecies (worker) = 3x; Study Duration (subacute to chronic) = 2x. The total Assessment Factor applied to the 88.2 mg/m3 value is 15x. Therefore, the Interim TWA Reproductive Worker Inhalation DNEL = 5.88 mg/m3.
Short description of key information:
An O.E.C.D. 443 Testing Guideline Extended One-Generation
Reporductive Toxicity Study in rats by the oral route is proposed
pending approval of the Stubstance Test Plan by E.C.H.A.
Effects on developmental toxicity
Description of key information
The oral (gavage) administration of 2,3-epoxypropyl neodecanoate to pregnant rats from gestation Days 3 to 19, at dose levels of 100, 300 or 1000 mg/kg bw/day was associated with lower maternal body weight gain during gestation and an effect on food consumption at 300 and 1000 mg/kg bw/day. No similar effects were apparent at 100 mg/kg bw/day. Consequently, 100 mg/kg bw/day was considered to represent the No Observed Effect Level (NOEL) for the pregnant female.
In-utero survival of the developing conceptus was unaffected by maternal treatment with 1000 mg/kg bw/day There were also no changes in the measured fetal parameters or embryofetal development. The `No Observed Effect Level' (NOEL) for developmental toxicity was therefore considered to be 1000 mg/kg bw/day.
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Specific details on test material used for the study:
- Identification : 2,3-epoxypropyl neodecanoate
Physical State/Appearance : Colorless clear liquid
Purity : 100%
Batch Number : PV7G0064
Label : CARDURA (TM) E-10P, Lot Number: PV7G0064,
Date Received : 02 March 2018
Storage Conditions : Room temperature in the dark
Expiry Date : 02 March 2019 - Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- Animal Information
A total of ninety-six time-mated female Sprague-Dawley Crl:CD (SD) IGS BR strain rats were obtained from Charles River (UK) Limited, Margate, Kent. Animals were delivered in two batches containing females prior to Day 3 of gestation. The day that positive evidence of mating was observed was designated Day 0 of gestation. On arrival the females weighed 182 to 304 g.
Animal Care and Husbandry
The animals were housed individually in solid-floor polypropylene cages with stainless steel mesh lids furnished with softwood flakes (Datesand Ltd., Cheshire, UK). The animals were allowed free access to food and water. A pelleted diet (Rodent 2018C Teklad Global Certified Diet, EnvigoRMS(UK) Limited, Oxon, UK) was used. A certificate of analysis of the batch of diet used is given in Annex2. Mains drinking water was supplied from polycarbonate bottles attached to the cage. Environmental enrichment was provided in the form of wooden chew blocks and cardboard fun tunnels (Datesand Ltd., Cheshire, UK). The diet, drinking water, bedding and environmental enrichment was considered not to contain any contaminant at a level that might have affected the purpose or integrity of the study.
The animals were housed in a single air-conditioned room within the EnvigoResearch Limited, Shardlow, UK Barrier Maintained Rodent Facility. The rate of air exchange was at least fifteen air changes per hour and the low intensity fluorescent lighting was controlled to give twelve hours continuous light and twelve hours darkness. Environmental conditions were continuously monitored by a computerizedsystem, and print-outs of hourly mean temperatures and humidity are included in the study records. The Study Plan target ranges for temperature and relative humidity were 22 ± 3 ºC and 50 ± 20% respectively.Short term deviations from these targets were considered not to have affected the purpose or integrity of the study; see deviations from Study Plan.
The animals were randomly allocated to treatment groups using a randomization procedure based on stratified bodyweight to ensure similarity between the treatment groups. The animals were uniquely identified within the study by an ear punching system routinely used in these laboratories. - Route of administration:
- oral: gavage
- Vehicle:
- arachis oil
- Details on exposure:
- For the purpose of the study the test item was prepared at the appropriate concentrations as a solution in Arachis Oil. The stability and homogeneity of the test item formulations were determined by EnvigoResearch Limited, Shardlow, UK Analytical Services. Results are given in Annex 1 and show the formulations to be stable for at least 23 days when stored refrigerated. Formulations were therefore prepared once and stored at approximately +4 °C in the dark.
Samples were taken of each test item formulation and were analyzed for concentration of 2,3-epoxypropyl neodecanoate at Envigo Analytical Laboratory, Shardlow. The method used for analysis of formulations and the results obtained are given in Annex 1. The results indicate that the prepared formulations were within1% of the nominal concentration.
Animals were allocated to treatment groups as follows:
Treatment Dose Level Treatment Concentration Animal Numbers
Group (mg/kg bw/day) Volume (mL/kg) (mg/mL)
Control 0 4 0 24 (1-24)
Low 100 4 25 24 (25-48)
Intermediate 300 4 75 24 (49-72)
High 1000 4 250 24 (73-96)
The numbers in parentheses ( ) show the individual animal numbers allocated to each treatment group.
The test item was administered daily, from Day 3 to Day 19 of gestation, by gavage. Control animals were treated in an identical manner with the vehicle alone. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples were taken of each test item formulation and were analyzed for concentration of 2,3-epoxypropyl neodecanoate at Envigo Analytical Laboratory, Shardlow. The method used for analysis of formulations and the results obtained are given in Annex 1. The results indicate that the prepared formulations were within 1% of the nominal concentration.
- Duration of treatment / exposure:
- The test item was administered daily, from Day 3 to Day 19 of gestation, by gavage. Control animals were treated in an identical manner with the vehicle alone.
- Frequency of treatment:
- Once per day
- Duration of test:
- 20 days
- Dose / conc.:
- 0 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 100 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 300 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 24
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- The study was performed to investigate the effects of the test item on embryonic and fetal development, following repeated administration by gavage atdose levels 100, 300 and 1000 mg/kg bw/day to the Sprague-Dawley Crl:CD® (SD) IGS BR strain rat during gestation, including the period of organogenesis.
The dose levels were selected in collaboration with the Sponsor Representative and were based on available toxicity data including preliminary data from a Preliminary Oral (Gavage) Pre-Natal Development Toxicity Study in the Rat (Envigo Study Number: BT01NH). In the preliminary study, a dose level of 1000 mg/kg bw/day caused initial reductions in body weight gains and food consumptions. However, these effects were considered not to be sufficient enough to preclude the use of this as the high dose level for further investigation.
The oral route was selected as the most appropriate route of exposure, based on the physical properties of the test item, and the results of the study are believed to be of value in predicting the likely toxicity of the test item to man.
The study was performed between 12 June 2018 and 03 September 2018. The in-life phase of the study was conducted between 15 June 2018 (first day of treatment) and 04 July 2018 (final day of necropsy). - Maternal examinations:
- General Observations/Measurements
Clinical Observations
Following arrival, all animals were examined for overt signs of toxicity, ill-health or behavioral changes once daily during the gestation period. Additionally, during the dosing period, observations were recorded immediately before and soon after dosing and one hour post dosing. All observations were recorded.
Body Weight
Individual body weights were recorded on Day 3 (before the start of treatment) and on Days 4, 5, 8, 11, 14 and 17 of gestation. Bodyweights were also recorded for animals at terminal kill (Day 20).
Food Consumption
Food consumption was recorded for each individual animal at Day 3, 5, 8, 11, 14, 17 and 20 of gestation.
Water Consumption
Water intake was observed daily by visual inspection of the water bottles for any overt changes. - Ovaries and uterine content:
- Terminal Investigation
Necropsy
All animals were killed by carbon dioxide asphyxiation followed by cervical dislocation on Day 20 of gestation. All animals were subjected to a full external and internal examination and any macroscopic abnormalities were recorded. The ovaries and uteri of pregnant females were removed, examined and the following data recorded:
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
The uteri of any apparently non-pregnant females were immersed in 0.5% ammonium polysulphide solution to reveal evidence of implantation.
Implantation types were divided into:
Early Death: No visible distinction between placental/decidual tissue and embryonic tissue
Late Death: Separate embryonic/fetal and placental tissue visible
Dead Fetus: A fetus that had died shortly before necropsy. These were included as late deaths for reporting purposes
All implantations and viable fetuses were numbered according to their intrauterine position as follows (as an example):
Left Horn Cervix Right Horn
L1 L2 L3 L4 L5 L6 L7 L8 R1 R2 R3 R4 R5 R6 R7 R8
V1 V2 V3 V4 V5 V6 V7 V8 V9 V10 V11 V12 V13 V14 V15 V16
V = viable fetus
The fetuses were killed by subcutaneous injection of sodium pentobarbitone. Fetuses from each litter were divided into two groups and examined for skeletal alterations and soft tissue alterations. Alternate fetuses were identified using an indelible marker and placed in Bouin’s fixative. Fetuses were subsequently transferred to distilled water and examined for visceral anomalies under a low power binocular microscope and then stored in 10% Buffered Formalin. The remaining fetuses were identified using cardboardtags marked with chinagraph pencil andplacedinto70% IMS in distilled water. The fetuses were subsequently eviscerated, processed and the skeletons stained with alizarin redSbefore being transferred to 50% glycerol for examination of skeletal development and anomalies and storage. - Fetal examinations:
- Pre and Post Implantation Loss
Percentage pre-implantation loss was calculated as:
(number of corpora lutea - number of implantations) x 100/number of corpora lutea
Percentage post-implantation loss was calculated as:
(number of implantations - number of live fetuses) x 100/number of implantations
Sex Ratio
Sex ratio was calculated as:
% male fetuses (sex ratio) = (Number of male fetuses x 100)/Total number of fetuses - Statistics:
- Where considered appropriate, quantitative data was subjected to statistical analysis to detect the significance of intergroup differences from control; statistical significance was achieved at a level of p<0.05. Statistical analysis was performed on the following parameters:
Female body weight, female body weight change, food consumption, gravid uterus weight, all caesarean necropsy parameters and fetal parameters, fetal evaluation parameters, including skeletal or visceral findings.
Data was assessed separately using the R Environment for Statistical Computing. Initially, the distribution of the data was assessed by the Shapiro-Wilk normality test, followed by assessment of the homogeneity of the data using Bartlett's test. Where considered appropriate, parametric analysis of the data was applied incorporating analysis of variance (ANOVA), which if significant, was followed by pair-wise comparisons using Dunnett's test. Where parametric analysis of the data was considered to be unsuitable, non-parametric analysis of the data was performed incorporating the Kruskal- Wallis test which if significant was followed by the Mann-Whitney "U" test. Dose response relationships were also investigated by linear regression.
Probability values (p) are presented as follows:
p<0.001 ***
p<0.01 **
p<0.05 *
p≥0.05 (not significant) - Clinical signs:
- no effects observed
- Description (incidence and severity):
- There were no clinical observations of toxicological significance at any dose level.
Sporadic incidences of increased salivation were evident in the majority of animals treated with 1000 mg/kg bw/day from Day 5 until Day 19 of gestation. Isolated instances of increased salivation were noted in seven animals treated with 300 mg/kg bw/day from Day 8 until Day 17 of gestation but to a much lesser extent than animals treated with 1000 mg/kg bw/day. Such findings are commonly observed in this type of study and usually reflect unpalatability and/or an irritant nature of the test item formulation and are generally deemed to be of no toxicological importance.
No clinical signs were apparent in any animal treated with 100 mg/kg bw/day. - Mortality:
- no mortality observed
- Description (incidence):
- There were no unscheduled deaths during the study.
- Description (incidence and severity):
- Animals treated with 300 and 1000 mg/kg bw/day showed marginal reductions in body weight gains during the majority of the treatment period with a dose relationship being apparent, however, statistical significance was not achieved. The reductions in body weight gains throughout the treatment period ultimately resulted in cumulative body weight gains being statistically significantly reduced (p<0.05) from Day 14 to Day 17 in animals treated with 300 mg/kg bw/day and from Day 8 until the end of the treatment period at 1000 mg/kg bw/day (p<0.05-p<0.01). This resulted in overall body weight gains for these animals being 9% and 12% lower than control for animals treated with 300 and 1000 mg/kg bw/day respectively. When adjustment was made for the gravid uterus, statistically significant reductions of 20% (p<0.05) and 36% (p<0.001) were noted in animals treated with 300 and 1000 mg/kg bw/day respectively.
No effects were detected on body weight development in females treated with 100 mg/kg bw/day. - Description (incidence and severity):
- Animals treated with 1000 mg/kg bw/day showed reductions in food consumption throughout the treatment period which achieved statistical significance from Days 3 to 5, 5 to 8, 11 to 14 and 17 to 20 (p<0.05 to p<0.001).
Animals treated with 300 mg/kg bw/day showed reductions in food consumption throughout the treatment period which achieved statistical significance from Day 5 until the end of the treatment period (p<0.05 to p<0.001).
No effect was detected on food consumption in females treated with 100 mg/kg bw/day. - Description (incidence and severity):
- Daily visual inspection of water bottles did not reveal any overt intergroup differences.
- Details on results:
- No toxicologically significant macroscopic abnormalities were detected at necropsy.
One animal treated with 300 mg/kg bw/day exhibited generalized fur loss, however, due to the isolated nature of this finding it was considered not to be related to treatment with the test item. - Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- no effects observed
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Changes in pregnancy duration:
- no effects observed
- Changes in number of pregnant:
- no effects observed
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Basis for effect level:
- other: no effects
- Description (incidence and severity):
- The following assessment is based on the 23, 23, 23 and 20 females with live young on Day 20 of gestation at 0 (control), 100, 300 and 1000 mg/kg bw/day, respectively.
There was no effect of maternal treatment on litter data as assessed by the mean number of implantations, in-utero offspring survival (as assessed by the mean number of early or late resorptions), live litter size and post-implantation losses at 100, 300 or 1000 mg/kg bw/day.
Pre-implantation losses and sex ratios across all test item-treated dose groups were also similar to controls.
There was no obvious effect of maternal treatment on litters as assessed by litter, fetal or placental weights.
For litters from dams treated with 300 and 1000 mg/kg bw/day, mean male and/or female fetal and combined fetal weights were statistically significantly lower (p<0.05 - p<0.01 and p<0.05 respectively) than control. However, the differences at each dosage were slight and an association with treatment is considered equivocal, especially as a true dose relationship was not apparent. The slightly lower fetal weights were considered to be a reflection of the slightly larger litter sizes apparent at these dosages when compared to control and as such, this apparent effect was consideredto be due to normal biological variation. Placental weights, total placental weights and litter weights were similar to control.
There was no effect of maternal treatment at 100 mg/kg bw/day on litters as assessed by litter, fetal or placental weights. - Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- no effects observed
- External malformations:
- no effects observed
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Neither the type, incidence nor distribution of external findings apparent for fetuses at Day 20 of gestation indicated an effect of maternal treatment on fetal development at 100, 300 or 1000 mg/kg bw/day.
Visceral examinations of fetuses on Day 20 of gestation did not indicate any obvious effect of maternal treatment on fetal development at 100, 300 or 1000 mg/kg bw/day.
At 1000 mg/kg bw/day statistically significant increases in the incidence of increased renal pelvic cavitation (p<0.05) was noted. The percentage incidence was found to be within the historical control data ranges. As a dose-related response was not evident, this finding is considered to be due to normal biological variation and therefore, un-related to treatment with the test item.
At 100 mg/kg bw/day statistically significant increases in the incidences of kinked ureter (p<0.01), increased renal pelvic cavitation (p<0.001) and absence of the renal papilla (p<0.05) were noted. All findings were found to be higher than historical control data ranges. However, as a dose relationship was not apparent, these findings are considered to be incidental and un-related to treatment with the test item.
Skeletal examinations of fetuses on Day 20 of gestation did not indicate any obvious effect of maternal treatment on fetal development at 100, 300 or 1000 mg/kg bw/day.
At 1000 mg/kg bw/day a statistically significant increase (p<0.05) in the incidence of fetuses/litters exhibiting incomplete ossification (nasal) was apparent. A higher percentage of each litter showing this effect was noted in seven litters at this dose level when compared with the historical control data range, however, the overall percentage of litters affected was within the historical control data range. There was no true dose related response and this variation was seen in the absence of other delays in ossification and any adverse effects on mean fetal weight. This was considered to be an isolated finding which was not regarded as evidence of an effect of embryofetal developmental toxicity. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: no effects
- Key result
- Abnormalities:
- no effects observed
- Key result
- Developmental effects observed:
- no
- Conclusions:
- The oral (gavage) administration of 2,3-epoxypropyl neodecanoate to pregnant rats from gestation Days 3 to 19, at dose levels of 100, 300 or 1000 mg/kg bw/day was associated with lower maternal body weight gain during gestation and an effect on food consumption at 300 and 1000 mg/kg bw/day. No similar effects were apparent at 100 mg/kg bw/day. Consequently, 100 mg/kg bw/day was considered to represent the No Observed Effect Level (NOEL) for the pregnant female.
In-utero survival of the developing conceptus was unaffected by maternal treatment with 1000 mg/kg bw/day There were also no changes in the measured fetal parameters or embryofetal development. The `No Observed Effect Level' (NOEL) for developmental toxicity was therefore considered to be 1000 mg/kg bw/day. - Executive summary:
Introduction
The study was performed to investigate the effects of the test item on embryonic and fetal development following repeated administration by gavage to the pregnant female during gestation including the period of organogenesis.
The study was designed to comply with the following guidelines:
US EPA Health Effects Test Guideline OPPTS 870.3700, ‘Prenatal Developmental Toxicity Study’ (August 1998)
Japanese Ministry of Agriculture, Forestry and Fisheries Testing guidelines for Toxicology studies, 12 Nousan No 8147, (24 November 2000)
OECD Guidelines for Testing of Chemicals, No 414, ‘Prenatal Developmental Toxicity Study’ (adopted 22 January 2001)
Commission Regulation (EC) No 440/2008 of 30 May 2008 test methods pursuant to Regulations (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH)
Methods
The test item was administered by gavage to three groups each of twenty-four time mated Sprague-Dawley Crl:CD® (SD) IGS BR strain rats, between Days 3 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) to serve as a control.
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.
Results
Mortality
There were no unscheduled deaths during the study.
Clinical Observations
There were no clinical observations of any toxicological significance at any dose level.
Body Weight
Animals treated with 300 and 1000 mg/kg bw/day showed marginal reductions in body weight gains during the majority of the treatment period with a dose relationship being apparent. This resulted in reductions in cumulative body weight gains from Day 14 to Day 17 in animals treated with 300 mg/kg bw/day and from Day 8 until the end of the treatment period at 1000 mg/kg bw/day. This resulted in lower overall body weight gains for these animals when compared to control animals. When adjustment was made for the gravid uterus these reductions were more pronounced.
No effects were detected on body weight development in females treated with 100 mg/kg bw/day.
Food Consumption
Animals treated with 300 and 1000 mg/kg bw/day showed general reductions in food consumption throughout the treatment period.
No effect was detected on food consumption in females treated with 100 mg/kg bw/day.
Water Consumption
No effect on water consumption was detected.
Post Mortem Studies
No toxicologically significant macroscopic abnormalities were detected at necropsy.
Litter Data and Litter Placental and Fetal Weights
There was no effect of maternal treatment on litter data as assessed by the mean number of implantations, in-utero offspring survival (as assessed by the mean number of early or late resorptions), live litter size and post-implantation losses at 100, 300 or 1000 mg/kg bw/day. Pre-implantation losses and sex ratios across all test item-treated dose groups were also similar to controls.
There was no obvious effect of maternal treatment on litters as assessed by litter, fetal or placental weights.
Fetal Examination
Skeletal and visceral examinations of fetuses on Day 20 of gestation did not indicate any obvious effect of maternal treatment on fetal development at 100, 300 or 1000 mg/kg/day.
Conclusion
The oral (gavage) administration of 2,3-epoxypropyl neodecanoate to pregnant rats from gestation Days 3 to 19, at dose levels of 100, 300 or 1000 mg/kg bw/day was associated with lower maternal body weight gain during gestation and an effect on food consumption at 300 and 1000 mg/kg bw/day. No similar effects were apparent at 100 mg/kg bw/day. Consequently, 100 mg/kg bw/day was considered to represent the No Observed Effect Level (NOEL) for the pregnant female.
In-utero survival of the developing conceptus was unaffected by maternal treatment with 1000 mg/kg bw/day. There were also no changes in the measured fetal parameters or embryofetal development. The `No Observed Effect Level' (NOEL) for developmental toxicity was therefore considered to be 1000 mg/kg bw/day.
Reference
KEY TO TABLES AND APPENDICES
M Male
F Female
sd Standard deviation
n Number of animals/litters
NF Number of fetuses
NL Number of litters
%† Group mean percent
N/A Not applicable
NP Not pregnant
V Viable fetuses+
FWT Fetal weight
PWT Placental weight
C Cervix
DF Dead fetus
ED Early death
LD Late death
Statistical Footnotes:
* Significantly different from control group p<0.05
** Significantly different from control group p<0.01
*** Significantly different from control group p<0.001
TABLES
Table 1 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 23 23 23 20
Non-Pregnant 1 1 1 4
Table 2 Summary Incidence of Daily Clinical Observations
Dose Level (mg/kg bw/day) Number of Animals Clinical Observations Number Showing Effect
(Days post coitum affected)
0 (Control) 24 No abnormalities detected
100 24 No abnormalities detected
300 24 Increased salivation 7 (8, 14, 15, 17)
1000 24 Increased salivation 23 (5, 6, 8-19)
Table 3 Group Mean Body Weight Values
Dose Level (mg/kg bw/day) Body Weight (g) on Day of Gestation
3 4 5 8 11 14 17 20
0 (Control) mean 266.0 270.7 276.0 291.1 309.1 327.2 358.6 403.4
sd 30.7 33.0 31.8 32.7 33.8 34.7 37.6 42.1
n 23 23 23 23 23 23 23 23
100 mean 268.0 272.2 276.4 291.7 309.2 327.9 358.9 402.8
sd 23.4 24.4 23.9 24.1 24.4 27.6 27.8 34.0
n 23 23 23 23 23 23 23 23
300 mean 263.8 266.9 271.0 284.3 301.1 316.0 345.6 388.7
sd 25.6 25.7 25.0 24.0 23.6 22.2 22.8 26.4
n 23 23 23 23 23 23 23 23
1000 mean 262.4 264.6 267.4 281.5 298.4 315.4 343.3 382.8
sd 26.4 29.7 27.0 26.4 27.6 27.3 28.8 33.2
n 20 20 20 20 20 20 20 20
Table 4 Group Mean Body Weight Change Values
Dose Level (mg/kg bw/day) Body Weight Change (g) during Days of Gestation
3 to 4 4 to 5 5 to 8 8 to 11 11 to 14 14 to 17 17 to 20
0 (Control) mean 4.7 5.3 15.0 18.0 18.1 31.3 44.8
sd 4.0 5.3 4.5 5.0 4.7 5.7 9.2
n 23 23 23 23 23 23 23
100 mean 4.2 4.2 15.3 17.5 18.7 31.0 43.9
sd 5.9 4.8 5.6 3.2 5.0 5.9 8.0
n 23 23 23 23 23 23 23
300 mean 3.1 4.1 13.3 16.8 14.8 29.7 43.1
sd 4.5 4.8 6.0 3.6 4.7 5.3 7.2
n 23 23 23 23 23 23 23
1000 mean 2.2 2.8 14.1 17.0 17.0 27.9 39.6
sd 5.8 6.1 5.0 3.8 4.8 5.7 12.9
n 20 20 20 20 20 20 20
Dose Level (mg/kg bw/day) Cumulative Body Weight Change (g) from Day 3 of Gestation
4 5 8 11 14 17 20
0 (Control) mean 4.7 10.0 25.0 43.0 61.2 92.5 137.3
sd 4.0 5.1 6.8 9.4 12.3 16.2 23.4
n 23 23 23 23 23 23 23
100 mean 4.2 8.4 23.7 41.2 59.9 90.9 134.8
sd 5.9 7.6 8.0 8.5 11.3 11.7 17.0
n 23 23 23 23 23 23 23
300 mean 3.1 7.2 20.6 37.3 52.2* 81.8* 124.9
sd 4.5 4.7 6.5 6.9 9.6 12.1 14.6
n 23 23 23 23 23 23 23
1000 mean 2.2 5.0 19.1* 36.0* 53.0* 80.9* 120.4**
sd 5.8 6.5 6.8 7.2 10.0 9.9 17.2
n 20 20 20 20 20 20 20
Table 5 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 Change (g)
3-20
3 20 3-20
0 (Control) mean 266.0 403.4 137.3 83.517 319.9 53.8
sd 30.7 42.1 23.4 18.520 36.8 13.8
n 23 23 23 23 23 23
100 mean 268.0 402.8 134.8 83.682 319.1 51.1
sd 23.4 34.0 17.0 16.383 29.8 15.4
n 23 23 23 23 23 23
300 mean 263.8 388.7 124.9 82.086 306.6 42.8*
sd 25.6 26.4 14.6 9.296 23.5 11.3
n 23 23 23 23 23 23
1000 mean 262.4 382.8 120.4* 85.787 297.0 34.6***
sd 26.4 33.2 17.2 9.915 34.1 18.9
n 20 20 20 20 20 20
Table 6 Group Mean Food Consumption Values
Dose Level (mg/kg bw/day) Food Consumption (g/rat/day) between Days of Gestation
3 - 5 5 - 8 8 - 11 11 - 14 14 - 17 17 - 20
0 (Control) mean 21.4 23.2 25.4 25.3 25.8 27.1
sd 3.0 2.8 2.6 2.9 3.3 3.1
n 23 23 23 23 23 23
100 mean 21.4 22.3 24.8 24.8 25.5 26.5
sd 3.1 2.1 2.5 3.1 2.7 3.2
n 23 23 23 23 23 23
300 mean 20.0 20.5*** 23.2** 22.3*** 23.5* 25.0*
sd 1.9 1.8 2.0 2.0 2.1 1.9
n 23 23 23 23 23 23
1000 mean 18.9* 20.1*** 23.7 23.2* 24.3 24.7*
sd 4.1 2.5 2.5 1.8 2.1 2.9
n 20 20 20 20 20 20
Table 7 Summary Incidence of Necropsy Findings
Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
TERMINAL DEATH
Number of animals examined 24 24 24 24
External:
Generalized fur loss 0 0 1 0
No abnormalities detected 24 24 23 24
Table 8 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 15.9 13.7 0.3 0.0 0.4 14.7 2.6 6.5 6.8 13.3 50.8 4.150 3.915 4.046 0.550 53.385 7.181
sd 3.3 3.2 0.6 0.2 0.8 14.7 4.9 2.1 2.4 3.1 15.3 0.300 0.278 0.295 0.055 12.723 1.571
n 23 23 23 23 23 23 23 23 23 23 23 23 22 23 23 23 23
100 mean 16.2 14.5 0.7 0.1 0.7 10.7 5.8 6.9 6.8 13.7 50.6 3.998 3.784 3.876 0.539 53.276 7.334
sd 2.2 2.4 1.2 0.3 1.2 10.6 10.8 3.0 3.1 3.0 18.8 0.248 0.216 0.218 0.045 11.514 1.452
n 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23
300 mean 16.0 14.1 0.3 0.1 0.3 11.7 2.5 6.9 6.9 13.8 50.3 3.915* 3.707* 3.810** 0.530 52.317 7.261
sd 1.8 1.9 0.5 0.3 0.6 10.2 4.6 2.2 2.4 2.0 14.9 0.270 0.217 0.230 0.050 6.988 1.010
n 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23
1000 mean 16.5 14.9 0.4 0.3 0.7 9.4 4.3 6.6 7.6 14.2 46.1 3.967 3.709* 3.827* 0.570 54.337 7.969
sd 2.1 1.9 0.5 0.4 0.7 7.1 5.0 2.1 1.8 1.9 11.3 0.321 0.300 0.302 0.149 8.218 1.649
n 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20
Table 9 Summary Incidence of Fetal External Findings
External Findings Dose level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of fetuses (litters) examined
305 (23) 316 (23) 317 (23) 284 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
Total Number Affected 8 5 2.5 6 5 2.2 14 10 4.3 21 6 8.3
Hematoma - Right Side of Face 1 1 0.3 1 1 0.3 0 0 0.0 0 0 0.0
Small Fetus 4 2 1.4 4 3 1.6 9 8 2.9 6 4 2.4
Large Placenta 0 0 0.0 1 1 0.3 1 1 0.3 12 2 5.0
Hematoma - Left Hind Limb 0 0 0.0 0 0 0.0 0 0 0.0 1 1 0.4
Small Placenta 2 2 0.6 0 0 0.0 7 6 2.1 4 2 1.4
Four Hind Limbs 1 1 0.3 0 0 0.0 0 0 0.0 0 0 0.0
Hematoma - Right Ear 1 1 0.3 0 0 0.0 0 0 0.0 0 0 0.0
Table 10 Summary Incidence of Fetal Visceral Findings
Visceral Findings Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of Fetuses (litters) Examined
157 (23) 165 (23) 164 (23) 147 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
EXTERNAL
Hemorrhage 0 0 0.0 1 1 0.5 0 0 0.0 0 0 0.0
HEAD
Tongue - short 0 0 0.0 0 0 0.0 0 0 0.0 1 1 0.6
Rugae - non-uniform patterning 10 7 6.3 7 5 3.8 13 6 7.7 7 6 4.5
Micropthalmia 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Brain - olfactory ventricle - enlarged 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Brain - lateral ventricle - enlarged 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Brain - third ventricle - enlarged 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Brain - fourth ventricle - enlarged 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
ABDOMEN
Liver - additional lobe between right and left median 0 0 0.0 1 1 0.5 0 0 0.0 5 3 3.2
Liver - lobes thickened throughout 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Liver - papillary process - reduced in size 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Spleen - reduced in size 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Umbilical artery - left-sided 0 0 0.0 0 0 0.0 0 0 0.0 2 2 1.4
Testis - partially undescended 1 1 0.6 1 1 0.5 0 0 0.0 0 0 0.0
Ureter - kinked 4 3 2.6 26 11 15.0** 5 4 3.4 11 8 7.5
Ureter - dilated - Slight/Severe 3 2 2.1 11 7 6.9 3 2 2.2 5 4 3.6
Kidney - malpositioned - Cranially/Caudally 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Kidney - reduced in size 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Renal pelvic cavitation - increased - Slight/Severe 1 1 0.7 23 12 14.5*** 7 6 4.2 8 6 5.5*
Table 10 (continued) Summary Incidence of Fetal Visceral Findings
Visceral Findings Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of Fetuses (litters) Examined
157 (23) 165 (23) 164 (23) 147 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
ABDOMEN (continued)
Renal papilla - absent 0 0 0.0 5 4 3.8* 0 0 0.0 1 1 0.6
THORAX
Thymus - lobe partially undescended 5 5 3.3 5 3 3.0 6 5 3.8 3 3 2.0
Thymus - lobe - irregular surface 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Lungs - irregular surface throughout 1 1 0.6 0 0 0.0 0 0 0.0 0 0 0.0
Atrium - enlarged 0 0 0.0 0 0 0.0 0 0 0.0 1 1 0.6
Total 19 14 12.2 41 16 25.6 28 13 17.2 28 12 18.2
Table 11 Summary Incidence of Fetal Skeletal Findings
Skeletal Findings Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of Fetuses (litters) Examined
148 (23) 151 (23) 153 (23) 137 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
SKULL
Fontanelle (anterior) - large 0 0 0.0 1 1 2.2 1 1 0.6 2 2 1.3
Nasal - incomplete ossification 6 3 3.7 21 9 13.0 10 8 6.7 25 9 19.0*
Frontal - incomplete ossification 2 2 1.2 4 4 2.8 0 0 0.0 3 3 2.1
Frontal - unossified area 1 1 0.6 3 2 2.0 1 1 0.9 2 2 1.7
Parietal - incomplete ossification 10 8 6.3 9 6 5.9 8 6 5.1 9 5 7.0
Parietal - unossified area(s) 1 1 0.6 1 1 0.5 0 0 0.0 0 0 0.0
Interparietal - incomplete ossification 26 13 17.0 38 13 24.4 37 14 23.9 43 16 32.3
Interparietal - unossified area(s) 1 1 0.5 0 0 0.0 0 0 0.0 1 1 1.0
Occipital (Supra-occipital) - incomplete ossification 17 10 10.7 21 13 14.9 20 11 13.1 25 12 20.0
Occipital (Supra-occipital) - unossified area(s) 17 13 11.1 18 13 15.3 10 8 6.6 7 5 6.1
Squamosal - incomplete ossification 19 9 12.3 20 13 12.8 15 11 9.2 23 9 16.8
Squamosal - unossified area(s) 1 1 0.6 1 1 0.5 0 0 0.0 0 0 0.0
Jugal - incomplete ossification 5 3 3.5 5 3 3.2 6 5 4.4 5 3 3.8
Table 11 (continued) Summary Incidence of Fetal Skeletal Findings
Skeletal Findings Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of Fetuses (litters) Examined
148 (23) 151 (23) 153 (23) 137 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
SKULL (continued)
Zygomatic process of maxilla - incomplete ossification 11 5 7.5 14 9 8.1 15 7 9.7 14 8 9.1
Zygomatic process of squamosal - incomplete ossification 0 0 0.0 1 1 0.7 1 1 0.9 1 1 0.6
Zygomatic process of squamosal - fused to jugal 0 0 0.0 0 0 0.0 1 1 0.6 0 0 0.0
Hyoid - incomplete ossification 16 8 10.9 24 14 14.8 17 10 11.9 22 11 16.8
Hyoid - not ossified 5 4 2.9 12 7 6.7 6 3 3.7 6 5 4.1
Presphenoid - incomplete ossification 1 1 0.6 0 0 0.0 1 1 0.6 2 2 1.3
Basisphenoid - incomplete ossification 0 0 0.0 0 0 0.0 0 0 0.0 1 1 0.7
Basioccipital - misshapen 0 0 0.0 0 0 0.0 0 0 0.0 1 1 1.0
VERTEBRAL COLOUMN
Odontoid - ossification present 2 2 1.6 0 0 0.0 1 1 0.6 0 0 0.0
Ventral arch of vertebra 1 - ossification present 47 17 34.3 50 13 31.3 39 16 27.1 42 12 30.7
Cervical (neural) arch - incomplete ossification 3 2 1.8 7 7 6.2 10 6 6.5 6 4 4.7
Thoracic centrum - incomplete ossification 5 5 3.0 4 4 4.1 15 5 8.9 10 6 7.7
Thoracic centrum - not ossified 0 0 0.0 0 0 0.0 2 2 1.2 2 1 1.4
Thoracic centrum - bipartite ossification 1 1 0.5 0 0 0.0 2 1 1.2 2 2 1.3
Thoracic centrum - dumb-bell-shaped 10 6 6.3 20 8 15.4 17 11 11.2 17 10 12.5
Table 11 (continued) Summary Incidence of Fetal Skeletal Findings
Skeletal Findings Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of Fetuses (litters) Examined
148 (23) 151 (23) 153 (23) 137 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
VERTEBRAL COLOUMN
Thoracic centrum - asymmetrically ossified 1 1 0.5 0 0 0.0 2 2 1.5 1 1 0.6
Lumbar centrum - bipartite ossification 0 0 0.0 0 0 0.0 1 1 0.6 1 1 0.7
Lumbar centrum - dumb-bell-shaped 0 0 0.0 0 0 0.0 1 1 0.6 0 0 0.0
Sacral (neural) arch - incomplete ossification 20 9 12.7 28 13 17.3 28 14 18.5 27 13 21.8
Sacral (neural) arch - not ossified 0 0 0.0 0 0 0.0 0 0 0.0 1 1 1.0
Caudal vertebrae - less than 4 ossified 23 13 14.3 34 15 24.8 39 16 24.4 45 15 33.6
Number of pre-sacral vertebrae = 25/27 (add “D” for pelvic displacement, or comment) 4 4 2.4 0 0 0.0 1 1 0.6 1 1 0.7
RIBS
Ossification centre - associated with 7th cervical vertebra 0 0 0.0 0 0 0.0 0 0 0.0 1 1 0.8
14th rib - extra - associated with 1st lumbar vertebra 1 1 0.5 1 1 0.9 0 0 0.0 0 0 0.0
Ossification centre - associated with 1st lumbar vertebra 16 11 11.0 7 5 4.8 7 6 5.0 13 7 9.0
One or more ribs - thickened 0 0 0.0 0 0 0.0 0 0 0.0 2 2 1.8
Rib - short 2 1 1.1 0 0 0.0 1 1 0.6 0 0 0.0
Rib - rudimentary 0 0 0.0 1 1 0.5 1 1 0.7 1 1 1.0
Rib - fused 0 0 0.0 0 0 0.0 0 0 0.0 1 1 0.7
Rib - not ossified 1 1 0.5 0 0 0.0 0 0 0.0 0 0 0.0
Table 11 (continued) Summary Incidence of Fetal Skeletal Findings
Skeletal Findings Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of Fetuses (litters) Examined
148 (23) 151 (23) 153 (23) 137 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
RIBS (continued)
Costal cartilage - misaligned 5 4 2.9 3 3 3.5 6 4 4.5 3 3 2.3
Costal cartilage - not fused to sternebra 9 7 6.3 13 9 9.9 14 10 9.0 7 5 5.0
STERENBRAE
Sternebra - incomplete ossification 2 1 1.1 4 4 2.9 4 3 2.4 3 3 2.3
Sternebra - not ossified 0 0 0.0 0 0 0.0 1 1 0.7 0 0 0.0
Sternebra - bipartite ossification 1 1 0.5 1 1 2.2 1 1 0.7 0 0 0.0
Sternebra - misaligned 7 5 4.4 5 5 3.8 12 10 8.4 3 3 2.3
Sternebra - fused 0 0 0.0 1 1 0.7 0 0 0.0 0 0 0.0
Sternebra - misshapen 1 1 0.5 0 0 0.0 0 0 0.0 0 0 0.0
Xiphoid cartilage - partially split 8 6 4.4 8 8 5.2 3 3 1.9 6 6 4.2
PECTORAL GIRDLE
Scapula - bent 0 0 0.0 0 0 0.0 0 0 0.0 1 1 1.0
Scapula - misshapen (comment on region) 2 2 1.1 5 4 3.1 2 2 1.2 4 3 2.7
FORELIMBS
Metacarpal - not ossified 37 14 23.0 51 16 33.3 64 19 41.6 64 17 47.4
Metacarpal - incomplete ossification 1 1 0.6 1 1 0.6 1 1 0.7 0 0 0.0
Forepaw phalanges - 1 or more - ossified 28 11 19.3 18 11 12.4 10 6 6.6 15 6 11.6
Humerus - incomplete ossification 1 1 0.6 6 4 5.0 1 1 0.6 5 3 3.7
Table 11 (continued) Summary Incidence of Fetal Skeletal Findings
Skeletal Findings Dose Level (mg/kg bw/day)
0 (Control) 100 300 1000
Number of Fetuses (litters) Examined
148 (23) 151 (23) 153 (23) 137 (20)
NF NL %† NF NL %† NF NL %† NF NL %†
FORELIMBS (continued)
Polymelia - forelimb (State details) 1 1 0.5 0 0 0.0 0 0 0.0 0 0 0.0
PELVIC GIRDLE
Ischium - incomplete ossification 0 0 0.0 2 2 1.1 1 1 0.6 0 0 0.0
Pubis - not ossified 0 0 0.0 3 2 2.3 0 0 0.0 0 0 0.0
Pubis - incomplete ossification 3 2 2.1 11 7 7.0 3 2 2.1 7 5 5.3
HINDLIMBS
Metatarsal - 1st - ossified 0 0 0.0 1 1 0.7 0 0 0.0 3 1 2.5
Metatarsal - incomplete ossification 0 0 0.0 0 0 0.0 0 0 0.0 3 2 2.6
Femur - incomplete ossification 9 7 9.8 14 10 12.3 6 6 4.2 10 5 8.3
Polymelia - hindlimb (State details) 1 1 0.5 0 0 0.0 0 0 0.0 0 0 0.0
Total 131 23 88.5 135 23 89.9 133 23 87.7 128 20 93.9
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Species:
- rat
Additional information
The oral (gavage) administration of 2,3-epoxypropyl neodecanoate to pregnant rats from gestation Days 3 to 19, at dose levels of 100, 300 or 1000 mg/kg bw/day was associated with lower maternal body weight gain during gestation and an effect on food consumption at 300 and 1000 mg/kg bw/day. No similar effects were apparent at 100 mg/kg bw/day. Consequently, 100 mg/kg bw/day was considered to represent the No Observed Effect Level (NOEL) for the pregnant female.
In-utero survival of the developing conceptus was unaffected by maternal treatment with 1000 mg/kg bw/day There were also no changes in the measured fetal parameters or embryofetal development. The `No Observed Effect Level' (NOEL) for developmental toxicity was therefore considered to be 1000 mg/kg bw/day.
Justification for classification or non-classification
An OECD 414 in rat is available upon which to base a Classification and Labeling decision regarding reproductive and developmental effects. The evidence is conclusive and not sufficient for classification.
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