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EC number: 904-153-2 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2020-01-13 to 2020-12-23
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 020
- Report date:
- 2020
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- 25 June 2018
- Deviations:
- yes
- Remarks:
- At arrival, the weight range for males was 331 to 335g instead of at least 340g as per the Study Protocol. This deviation was not considered to have affected the integrity or the purpose of the study. No other deviations occurred during the study.
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- (5-ethyl-1,3-dioxan-5-yl)methanol; 2-ethyl-2-(hydroxymethyl)propane-1,3-diol; 2-ethylpropane-1,3-diol
- EC Number:
- 904-153-2
- IUPAC Name:
- (5-ethyl-1,3-dioxan-5-yl)methanol; 2-ethyl-2-(hydroxymethyl)propane-1,3-diol; 2-ethylpropane-1,3-diol
- Details on test material:
- Polyol TD, batch no. 7350 was described as a clear liquid, and stored in sealed container under dryed gas (Nitrogen) blanket at ambient temperature in dry area protected from direct sunlight and the elements. The determination of the identity, strength, purity, composition and stability of the test item was the responsibility of the Sponsor.
1
- Specific details on test material used for the study:
- Identity: Polyol TD
Chemical name: Reaction mass of 2-ethylpropane-1,3-diol and 5-ethyl-1,3-dioxane-5-methanol and propylidynetrimethanol
Appearance: Clear, colourless liquid
Batch no: 7350
Inspection No: 890000050160
EC no: 904-153-2
Expiry date: 18 June 2020
Storage conditions: Store in sealed container under dry gas (Nitrogen, Argon or dried air) blanket, at ambient temperature, in dry area protected from direct sunlight and the elements
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Italia S.p.A., Calco (Lecco), Italy
- Age and weight at study initiation: females - 9 weeks old (200-225 g) and males at least 11 weeks old (at least of 331 g):
- Housing: The animals were housed in a limited access rodent facility. During the pairing period, the rats were housed on the basis of 1 male to 1 female in clear polysulfone cages measuring 42.5×26.6×18.5cm with a stainless steel mesh lid and floor Tecniplast Gazzada S.a.r.l., Buguggiate, Varese). Each cage tray held absorbent material which was inspected and changed daily.
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): Drinking water was supplied ad libitum to each cage via water bottles.
- Acclimation period: 15 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C ± 2°C
- Humidity (%): 55% ± 15%
- Air changes (per hr): approximately 15 to 20 air changes per hour
- Photoperiod (hrs dark / hrs light): rooms were lit by artificial light for 12 hours each day
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- The test item was administered orally by gavage at a dose volume of 10mL/kg body weight.
Control animals received the vehicle alone at the same dose volume. The dose was administered to each animal on the basis of the most recently recorded body weight and the volume administered was recorded for each animal. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Preparations of the test item were prepared as solutions in purified water. Concentration was assessed for all levels by taking two analytical aliquots (approximately 1 mL). Each analytical aliquot was analysed separately. Concentration was evaluated as the mean of the two determinations.
- Details on mating procedure:
- The females were paired with male rats. Females were paired one to one in the home cage of the male and left overnight. Vaginal smears were taken daily in themorning from the day after pairing until a positive identification of mating was made. The day of mating, as judged by the presence of spermin the vaginal smear or by the presence of a copulation plug, was considered as Day 0 of gestation (or Day 0 post coitum). Full mating records were maintained.
- Duration of treatment / exposure:
- All animals were dosed once a day from Day 3 through Day 19 post coitum.
- Frequency of treatment:
- All animals were dosed once a day from Day 3 through Day 19 post coitum.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Remarks:
- Vehicle - water
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 25 mated females/group
- Control animals:
- yes, concurrent vehicle
Examinations
- Maternal examinations:
- Mortality: Throughout the study, all animals were checked early in each working day and again in the afternoon. At weekends and Public Holidays a similar procedure was followed except that the final check was carried out at approximately mid-day.
Clinical Signs: All clinical signs were recorded for individual animals. Each animal was observed daily and any clinical signs recorded starting from allocation until sacrifice.
Body weight: All animals were weighed on Days 0, 3, 6, 9, 12, 15, 18 and 20 post coitum.
Food consumption: Food consumption was measured on Days 3, 6, 9, 12, 15, 18 and 20 post coitum starting from Day 0 post coitum.
Clinical pathology investigations: Blood collection was performed, for hormone determination, from all females at termination on Day 20 post coitum. Blood samples (approximately 0.5 mL) were withdrawn from the sublingual vein under light isoflurane anaesthesia. This procedure was performed within a short timeframe (e.g. two hours, as possible) on the morning of the day of necropsy. Samples were assayed to determine the serum levels of Total triiodothyronine (total T3), Total thyroxine (total T4) and Thyroid stimulating hormone (TSH).
All animals were subjected to necropsy, supervised by a pathologist. From all females, the organs that were found to be abnormal and the thyroid were dissected free of fat and weighed. The ratios of organ weight to body weight were calculated for each animal. These organs were subject to histpathological examination. - Ovaries and uterine content:
- The ovaries and uteri were examined to determine:
– Gravid uterine weight, including the cervix;
– number of corpora lutea;
– number of implantation sites;
– number, sex and weight of all live foetuses;
– internal foetal sex determination in each foetus allocated to the skeletal examination; internal foetal sex determination for the remaining foetuses performed during the fixed-visceral examination;
– number and sex of dead foetuses (foetuses at termwithout spontaneous movements and breathing);
– anogenital distance (AGD) in all live foetuses;
– number of intra-uterine deaths;
– gross evaluation of placentae.
Intra-uterine deaths were classified as:
– Early resorptions: only placental remnants visible.
– Late resorptions: placental and foetal remnants visible. - Blood sampling:
- Clinical pathology investigations: Blood collection was performed, for hormone determination, from all females at termination on Day 20 post coitum. Blood samples (approximately 0.5 mL) were withdrawn from the sublingual vein under light isoflurane anaesthesia. This procedure was performed within a short timeframe (e.g. two hours, as possible) on the morning of the day of necropsy. Samples were assayed to determine the serum levels of Total triiodothyronine (total T3), Total thyroxine (total T4) and Thyroid stimulating hormone (TSH).
- Fetal examinations:
- All foetuseswere examined externally. Approximately one-half of the foetuses (i.e., routinely, every second live foetus) in each litter was preserved in Bouin’s solution for subsequent fixed visceral examination.
Sex determination performed during post mortem examination was confirmed by internal gonads inspection, during the fixed-visceral examination. Internal foetal sex determination in each foetus allocated to the skeletal examination was performed during the post mortem examination. Indication of incomplete testicular descent/cryptorchidism was noted in male foetuses.
The remaining foetuses were eviscerated after which the carcasses were fixed in 95% (v/v) ethanol for subsequent skeletal examination (single staining). Skeletal and fixed-visceral examinations were performed in all groups. Structural deviation were classified as follows:
Malformations: Major abnormalities that are rare and/or affect the survival or health of the species under investigation.
Anomalies: Minor abnormalities that are detected relatively frequently.
Variants: A change that occurs within the normal population under investigation and is unlikely to adversely affect survival or health. This might include a delay in growth or morphogenesis that would have otherwise followed a normal pattern of development.
Pre-implantation loss
Anogenital distance - Statistics:
- For continuous variables the significance of the differences amongst group means was assessed by Dunnett’s test or a modified t test, depending on the homogeneity of data. Statistical analysis of non-continuous variables was carried out by means of the Kruskal-Wallis test and intergroup differences between the control and treated groups assessed by a non-parametric version of the Williams test.
- Historical control data:
- Historical control data was used for thyroid hormone determination, for comparison with foetal examinations, sex ratio and litter data and for pregnancy information.
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- No adverse clinical signs were observed throughout the study both in control and treated females.
Four control and one receiving 300 mg/kg bw/day showed scab on neck or head. In addition, two control females and two receiving 300 mg/kg/day showed hairloss on head. These signs were in general observed during the middle or last gestation period. - Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Description (incidence):
- No animals died during the study.
One female receiving 1000 mg/kg bw/day was found not pregnant at necropsy.
One control female had unilateral implantation in the left horn and was not pregnant in the right one.
The number of females with live foetuses on Day 20 post coitum was: 25 in the control, 25 in the low (100 mg/kg bw/day - Group 2), 25 in the medium (300 mg/kg bw/day - Group 3) and 24 in the high dose groups (1000 mg/kg bw/day - Group 4). - Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- No relevant differences in body weight were noted between control and treated groups. A very slight statistically significant decrease in mean body weight (-4%) was noted on Day 6 post coitum, in females receiving 300 and 1000 mg/kg bw/day, when compared to the control mean values. On Day 6 post coitum, body weight gain was decreased (-8%, -22%, -38% in order of ascending dose levels) at all dose levels, reaching a statistically significance at 1000 mg/kg bw/day, compared to the control group. This change was considered related to treatment but not adverse since occurred as isolated case and afterwards, a regular increment was noted in all treated groups compared to the control.
No significant differences in terminal body weight were observed in treated groups compared to the control group. A slight decrease (-9%) in absolute weight gain (terminal body weight minus body weight at Day 0 post coitum minus gravid uterus), was noted in females receiving 1000 mg/kg bw/day, when compared to control group. Due to the limited entity of this change it was considered to be without toxicological relevance.
Please see results table below. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- A reduction (-16%) in food consumption, statistically significant on Day 6 post coitum, was noted in females receiving 1000 mg/kg bw/day, compared to the control group. This was considered treatment-related, but not adverse.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Endocrine findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No dose-related changes were recorded.
Compared with controls, females dosed at 1000 mg/kg bw/day showed a statistically significant increase of thyroxine (16%). Looking at individual data, only four animals showed thyroxine data outside the historical range and simultaneous change of the other parameters (decrease of TSH and increase of T3) was recorded in one animal only. Since the simultaneous changes of the three hormones were sporadic, and no histopathological changes were recorded, the above findings were considered to be incidental.
T3 and TSH values were outside the range of historical data in some control and treated animals, therefore these findings were considered to be unrelated to treatment. - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- No effects on the thyroid weight (absolute and relative) was noted at any dose levels, compared to the control group.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- Females that completed the treatment period did not show relevant macroscopic changes that could be considered treatment-related
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- No treatment-related changes were noted.
The sporadic lesions, reported in control and treated animals were considered to be an expression of spontaneous and/or incidental pathology, commonly seen in this species. - Histopathological findings: neoplastic:
- not examined
- Other effects:
- not specified
Maternal developmental toxicity
- Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- no effects observed
- Description (incidence and severity):
- Please see data presented below.
- 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:
- effects observed, non-treatment-related
- Description (incidence and severity):
- One female receiving 1000 mg/kg bw/day was found not pregnant at necropsy.
Please see details below. - Other effects:
- not specified
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: no adverse effects observed
Maternal abnormalities
- Key result
- Abnormalities:
- no effects observed
- Description (incidence and severity):
- While effects were observed these effects were not considered adverse.
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Description (incidence and severity):
- Litter weight and mean foetal weight (for each sexes, as well as for both sexes combined) of treatment groups were comparable to the control group.
- Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Description (incidence and severity):
- Sex ratios of the foetuses, calculated as the percentage of males per litter, did not show differences between control and treated groups and ranged between 49% and 53%.
Please refer to table below for details. - Changes in litter size and weights:
- no effects observed
- Description (incidence and severity):
- Litter weight and mean foetal weight (for each sexes, as well as for both sexes combined) of treatment groups were comparable to the control group.
- Anogenital distance of all rodent fetuses:
- no effects observed
- Description (incidence and severity):
- No relevant differences were noted in the mean values of the AGD (anogenital distance normalised for the cube root of the body weight performed on Day 20 post coitum) of foetuses of both sexes maternally exposed at all dose levels compared to the control group.
A statistically significant increase was noted in males at the dose level of 1000 mg/kg bw/day compared to the control group. However, the difference was very slight, +3% compared to controls.
No such effect was observed in females.
Please attached document for details. - Changes in postnatal survival:
- not examined
- External malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- One control foetus showed some alterations recorded at the external examination classified as malformation on the jaw (micromaxilla), or anomalies on the tail (bent), on the head (domed shape), on the hindlimb (swollen with flexure in the left one and hyperextension in the right one). In addition, one control foetus showed a subcutaneous hematoma on the right side of the head (anomaly). One foetus of dam maternally exposed at 1000 mg/kg bw/day had an imperforate anus (malformation) and rudimentary tail (anomaly).
A total of 5 small foetuses (< 2.7 g) were detected, 1 out of 377 in the control group, 1 out of 371 in the low dose group and 3 out of 372 in the medium group.
Please refer to the attachment on external examination of foetuses data. - Skeletal malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Major alterations were distributed along the treated groups without dose relationship, in terms of foetuses/litters affected. Please see table below for details.
Regarding the other alterations (anomalies and variations), unossified or incomplete ossification of various part of the skeleton were noted in control and treated groups without differences. These findings involved the forepaw (no ossification of the 4th metacarpal), sternebrae elements (incomplete ossification or no ossification of the 5th and/or 6th), bones of the skull (incomplete ossification of the supraoccipital, interparietal and temporal segments, no ossification or incomplete ossification of the hyoid), sacral vertebrae (incomplete ossification of the arch(es)). The type and distribution of the above mentioned findings, both for major and minor alterations, did not show any association with treatment with the test item. - Visceral malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- The major alterations (malformations) noted, at visceral examination of foetuses, were on the brain/head. These included the extreme enlargement of the lateral ventricles of the brain, at dose levels of 100 and 300 mg/kg bw/day and a cerebral hypoplasia associated to the absence of the third ventricle at the dose level of 1000 mg/kg bw/day. One foetus maternally exposed at 300 mg/kg bw/day showed cleft palate. Although an increase in malformation rate was noted in all treated groups, the alterations were quantitatively similar between doses, occurred in foetuses without growth retardation and with an absence of doses-related response when compared to the control group. However, the brain alteration is present in the background control data (see attached document), even if with a severity between slight to moderate. Please refer to table below for details.
One foetus maternally exposed at 100 mg/kg bw/day showed a small opened area in olfactory bulb (classified as anomaly). In addition, alterations recorded in the ureters (enlarged and kinked), testis (displaced) and kidneys (ectopic), classified as variations and anomalies, were observed in control and treated groups with similar incidence in terms of litter and foetuses affected. - Other effects:
- not specified
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No treatment-related adverse effects observed
Fetal abnormalities
- Key result
- Abnormalities:
- effects observed, non-treatment-related
Overall developmental toxicity
- Key result
- Developmental effects observed:
- no
Any other information on results incl. tables
Implantation Loss Data (%):
Group | Pre-implantation loss (%) | Post-implantation loss (%) | Total (%) | |
1 | Mean | 3.61 | 2.06 | 5.66 |
SD | 10.73 | 3.91 | 10.72 | |
(n) | 25 | 25 | 25 | |
2 | Mean | 3.21 | 0.98 | 4.14 |
SD | 5.89 | 2.88 | 6.56 | |
(n) | 25 | 25 | 25 | |
3 | Mean | 1.89 | 4.00 | 5.84 |
SD | 3.56 | 9.92 | 10.10 | |
(n) | 25 | 25 | 25 | |
4 | Mean | 5.03 | 2.51 | 7.38 |
SD | 9.03 | 6.38 | 11.05 | |
(n) | 24 | 24 | 24 |
Fate of Females
Group 1 (control) | Group 2 | Group 3 | Group 4 | |
Initial group size | 25 | 25 | 25 | 25 |
Unilateral implantation | 1 | 0 | 0 | 0 |
Not pregnant | 0 | 0 | 0 | 1 |
With live foetuses at gestation Day 20 | 25 | 25 | 25 | 24 |
Terminal Body Weight, Gravid Uterus Weight and Absolute Weight Gain Data
Terminal body weight (g) | Gravid uterus weight (g) | Absolute weight gain (g) | ||
1 | Mean | 410.18 | 88.50 | 63.44 |
SD | 28.88 | 19.52 | 12.24 | |
(n) | 25 | 25 | 25 | |
2 | Mean | 413.86 | 88.47 | 69.08 |
SD | 31.31 | 11.02 | 13.88 | |
(n) | 25 | 25 | 25 | |
3 | Mean | 399.78 | 88.91 | 60.23 |
SD | 26.50 | 12.92 | 14.98 | |
(n) | 25 | 25 | 25 | |
4 | Mean | 396.29 | 85.57 | 57.43 |
SD | 32.29 | 16.09 | 14.69 | |
(n) | 24 | 25 | 24 |
Skeletal examination of foetuses
Groups (mg/kg bw/day) | 1 (0) | 2 (100) | 3 (300) | 4 (1000) |
Malformations | ||||
Forelimb(s): Humerus misshapen | 2 (2) | 0 | 0 | 0 |
Pectoral girdle: Clavicle malpositioned | 1 (1) | 0 | 0 | 0 |
Pectoral girdle: Scapula misshaped | 0 | 0 | 2(1) | 0 |
Pelvic girdle: Pubis no ossification | 4 (3) | 3 (3) | 4 (4) | 3 (2) |
Pelvic girdle: Ilium no ossification | 0 | 0 | 1(1) | 0 |
Skull: Tympanic annulus malposition | 1(1) | 0 | 0 | 0 |
Skull: Zygomatic malpositioned | 2 (2) | 0 | 1(1) | 2(2) |
Thoracic vertebrae: Arch(es) fused | 0 | 0 | 3(1) | 0 |
foetal incidence; ( ) litter incidence |
Visceral examination of foetuses Data
Group (mg/kg bw/day) | 1 (0) | 2 (100) | 3 (300) | 4 (1000) |
Malformations | ||||
Brain: Ventricles enlarged extreme | 0 | 1(1) | 1(1) | 0 |
Brain: Cerebral hypoplasia and third ventricle absent | 0 | 0 | 0 | 1(1) |
Head: Cleft palate | 0 | 0 | 1(1) | 0 |
foetal incidence; ( ) litter incidence |
Applicant's summary and conclusion
- Conclusions:
- Based on the findings from this study, the NOAEL (No Observed Adverse Effect Level) for both maternal and developmental toxicity could be set at 1000 mg/kg bw/day.
- Executive summary:
In a developmental toxicity study performed according to OECD TG 414, Polyol TD (in water) was administered to 25 mated female Sprague Dawley rats/dose by oral gavage at dose levels of 0, 100, 300 and 1000 mg/kg bw/day from days 3 through 19 of gestation.
No mortality in the maternal animals occurred during the study and animals did not show treatment-related clinical signs. Maternal body weight gain was reduced in treated groups on occasion (Day 6 post coitum). In addition food consumption was also decreased in females receiving 1000 mg/kg bw/day. These parameters tended to recover, were comparable between control and treated groups during the last gestation period and did not affect the pregnancy outcome. Therefore, these effects were considered treatment-related but not adverse. No relevant treatment-related change were observed at microscopic and macroscopic observations and for thyroid weight. The sporadic changes of the three hormones (T3, T4 and TSH) determined in the parental females were considered to be unrelated to treatment.
No relevant differences were noted in the mean values of the anogenital distance of foetuses of both sexes compared to the control group. No differences were observed between control and treated groups in the number of implantation sites, corpora lutea, implantation losses, uterine deaths, viable foetuses, mean foetal weight (for each sex as well as for both sexes combined) and sex ratios. One foetus maternally exposed at 1000 mg/kg bw/day showed, at external examination, an imperforate anus (malformation) and rudimentary tail (anomaly). At skeletal examinations, the type and distribution of the findings observed, both for major and minor alterations, did not show any association with treatment with the substance. Although an increase in malformation rate was noted, at visceral examination, in all treated groups, the alterations were quantitatively similar between doses, occurred in foetuses without growth retardation and with an absence of doses-related response when compared to the control group.
Based on the findings from this study, the NOAEL (No Observed Adverse Effect Level) for both maternal and developmental toxicity is set at 1000 mg/kg bw/day, this being hte highest dose tested.
The developmental toxicity study in the rat is classified acceptable and satisfies the guideline requirement for a developmental toxicity study (OECD 414) in rats.
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