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Toxicological information

Developmental toxicity / teratogenicity

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Administrative data

Endpoint:
developmental toxicity
Type of information:
experimental study
Adequacy of study:
key study
Study period:
17 April 2013 to 19 November 2013
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Remarks:
Study was conducted according to an appropriate guideline and in compliance with GLP

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2014
Report date:
2014

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 414 (Prenatal Developmental Toxicity Study)
Version / remarks:
2001
Deviations:
no
Qualifier:
according to guideline
Guideline:
EPA OPPTS 870.3700 (Prenatal Developmental Toxicity Study)
Version / remarks:
1998
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
Hydroxytrimethylsilane
EC Number:
213-914-1
EC Name:
Hydroxytrimethylsilane
Cas Number:
1066-40-6
Molecular formula:
C3H10OSi
IUPAC Name:
Trimethylsilanol
Test material form:
other: liquid
Details on test material:
- Name of test material (as cited in study report): Trimethylsilanol

Test animals

Species:
rat
Strain:
Sprague-Dawley
Remarks:
Crl:CD IGS
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River Laboratories, Germany
- Age at study initiation: 12 weeks
- Weight at study initiation: 230 to 316g
- Fasting period before study: no
- Housing: In groups of three to five animals in Makrolon type-4 cages with wire mesh tops up to the day of mating and afterwards individually in Makrolon type-3 cages with wire mesh tops with sterilized standard softwood bedding (‘Lignocel’) with paper enrichment (ISO-BLOX).
- Diet (ad libitum): Pelleted standard Harlan Teklad 2018C
- Water (ad libitum): community tap water
- Acclimation period: 5 days

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18.2 - 23.5
- Humidity (%): 27.2 - 70.3
- Air changes (per hr): 10-15
- Photoperiod (hrs dark / hrs light): 12/12

IN-LIFE DATES: From: 22 April 2013 To: 23 May 2013

Administration / exposure

Route of administration:
oral: gavage
Vehicle:
corn oil
Details on exposure:
PREPARATION OF DOSING SOLUTIONS:
Trimethylsilanol was weighed into a glass beaker on a tared precision balance and the vehicle (corn oil) was added. Using an appropriate homogenizer, a homogeneous suspension was pre-pared. Separate formulations were prepared for each concentration
Dose formulations were devided into daily aliquots.
Homogeneity of the test item in the vehicle was maintained during the daily administration period using a magnetic stirrer.

VEHICLE
- Concentration in vehicle: 0, 10, 30, 90 mg/mL
- Amount of vehicle: 5 mL/kg
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
On the first treatment day samples from the control group as well as three samples (top, middle and bottom) of about 1 g of each concentration were taken prior to dosing for analysis of concentration and homogeneity. Samples of about 1 g of each concentration were taken from the middle only to confirm the stability (4 hrs at room temperature and 8 days in refrigerator). During the last week of the treatment, samples were taken from the middle to confirm concentration. The aliquots for analysis of dose formulations were frozen (-20 ± 5 °C) and delivered on dry ice to the person responsible for formulation analysis and stored there at -20 ± 5 °C until analysis.

The samples were analyzed by Headspace GC-Method The test item was used as the analytical standard.

Duplicates were taken of all samples and were stored.
Details on mating procedure:
- Impregnation procedure: cohoused
- M/F ratio per cage: 1:1
- Length of cohabitation: until evidence of copulation observed
- Verification of same strain and source of both sexes: yes
- Proof of pregnancy: vaginal plug or sperm in vaginal smear referred to as day 0 post coitum
- Any other deviations from standard protocol: no
Duration of treatment / exposure:
Day 6 to Day 20 post coitum
Frequency of treatment:
daily
Duration of test:
21 days
Doses / concentrationsopen allclose all
Dose / conc.:
0 mg/kg bw/day (actual dose received)
Remarks:
Group 1 - Control Group
Dose / conc.:
50 mg/kg bw/day (actual dose received)
Remarks:
Group 2
Dose / conc.:
150 mg/kg bw/day (actual dose received)
Remarks:
Group 3
Dose / conc.:
450 mg/kg bw/day (actual dose received)
Remarks:
Group 4
No. of animals per sex per dose:
22 female
Control animals:
yes, concurrent vehicle
Details on study design:
- Dose selection rationale: The dose levels were selected based on a previous dose range-finding toxicity study in Sprague Dawley rats using dose levels of 0, 50, 150 and 600/400 mg/kg bw/day.

Examinations

Maternal examinations:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: 3 times daily during treatment

BODY WEIGHT: Yes
- Time schedule for examinations: daily

FOOD CONSUMPTION: Yes
- Time schedule for examinations: recoreded at 3-day intervals, days 0-3, 3-6, 6-9, 9-12, 12-15, 15-18 and 18-21 post coitum
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/animal/day: Yes

WATER CONSUMPTION: No
- Time schedule for examinations:

POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 21
- liver weight recorded
Ovaries and uterine content:
The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
Fetal examinations:
- External examinations: Yes: all per litter
- Soft tissue examinations: Yes: half per litter
- Skeletal examinations: Yes: half per litter
- Head examinations: Yes: half per litter
Statistics:
The following statistical methods were used to analyze food consumption, body weights, reproduction and skeletal examination data:

• Means and standard deviations of various data were calculated and included in the report.

• The Dunnett-test (many to one t-test) based on a pooled variance estimate was applied if the variables could be assumed to follow a normal distribution for the comparison of the treated groups and the control groups for each sex.

• The Steel-test (many-one rank test) was applied instead of the Dunnett-test when the data could not be assumed to follow a normal distribution.

• Fisher's exact-test was applied if the variables could be dichotomized without loss of information.
Historical control data:
Data from test facility derived during 1992 to 2005 included

Results and discussion

Results: maternal animals

General toxicity (maternal animals)

Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
Clinical signs such as uncoordinated movement, decreased activity and/or prostrate appearance and/or ruffled fur occurred after dosing the animals with dose levels of 150 and/or 450 mg/kg bw/day during the treatment period. These were considered to be related to the treatment with the test item. Due to the full recovery of the animals, slight severity grade and frequency at 150 mg/kg bw/day, this dose level was considered to cause treatment-related but not adverse effects in pregnant rats. Due to the nature, frequency and severity of the findings and the observation that one animal did not fully recover from the symptoms, the dose level of 450 mg/kg bw/day was considered to cause treatment-related and adverse effects in pregnant rats.
Dermal irritation (if dermal study):
not examined
Mortality:
no mortality observed
Description (incidence):
All females survived until the scheduled necropsy.
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
At 450 and 150 mg/kg bw/day, mean absolute body weight and body weight gain were decreased statistically significantly and were considered to be related to the treatment with the test item. At 450 mg/kg bw/day, the corrected body weight gain was also affected by treatment with the test item.
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
At 450 and 150 mg/kg bw/day, test item-related statistically significant decreases were observed for mean food consumption.
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not specified
Ophthalmological findings:
not examined
Haematological findings:
not examined
Clinical biochemistry findings:
no effects observed
Urinalysis findings:
not examined
Behaviour (functional findings):
effects observed, treatment-related
Description (incidence and severity):
Uncoordinated movement, decreased activity with dose levels of 150 and/or 450 mg/kg bw/day during the treatment period. These were considered to be related to the treatment with the test item.
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Description (incidence and severity):
No effects on liver weights were noted.
Gross pathological findings:
no effects observed
Description (incidence and severity):
No findings were observed at any dose level during macroscopical examination.
Neuropathological findings:
not examined
Histopathological findings: non-neoplastic:
not examined
Histopathological findings: neoplastic:
no effects observed
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):
The relevant reproduction data (pre-and post-implantation loss and number of fetuses per dam) were not affected by treatment with the test item.
Mean numbers of corpora lutea and implantation sites were similar across all groups.
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
Other effects:
not specified
Details on maternal toxic effects:
Statistically significantly decreased mean food consumption, body weight, body weight gain and corrected body weight gain were affected by the treatment with the test
item and were considered to be adverse maternal toxic effects.

Effect levels (maternal animals)

Key result
Dose descriptor:
NOAEL
Remarks:
Maternal General Toxicity
Effect level:
ca. 150 mg/kg bw/day (nominal)
Based on:
test mat.
Basis for effect level:
body weight and weight gain
clinical signs
food consumption and compound intake

Maternal abnormalities

Key result
Abnormalities:
no effects observed

Results (fetuses)

Fetal body weight changes:
effects observed, treatment-related
Description (incidence and severity):
At 450 mg/kg bw/day, there were statistically significantly decreased fetal body weights both on litter and individual basis and this was related to the treatment with the test item.
Reduction in number of live offspring:
no effects observed
Changes in sex ratio:
no effects observed
Description (incidence and severity):
No test item-related effects on the sex ratio of the fetuses were noted in any group.
Changes in litter size and weights:
effects observed, treatment-related
Description (incidence and severity):
At 450 mg/kg bw/day, there were statistically significantly decreased fetal body weights both on litter and individual basis and this was related to the treatment with the test item.
Changes in postnatal survival:
no effects observed
External malformations:
no effects observed
Skeletal malformations:
no effects observed
Description (incidence and severity):
No test item-related findings were noted during skeletal examination of the fetuses. Non-ossified cervical vertebral bodies (1 - 7), some non-ossified caudal vertebrae, incompletely ossified sternebra 5, non-ossified metatarsalia 1 and non-ossified digits on fore and hind limbs were seen in fetuses at 450 mg/kg bw/day. These findings indicated a slight delay in ossification at 450 mg/kg bw/day which correlated with the lower fetal body weight in this dose group and this was related to the treatment with the test item.
At 450 mg/kg bw/day, statistically significantly increased incidence of supernumerary rudimentary ribs, long ventral plate and long or interrupted costal cartilage occurred both on an individual
and litter basis and these indicated a slight disturbance in development.
These observations were only variations with high spontaneous incidence of this strain.
Visceral malformations:
no effects observed
Other effects:
not specified
Details on embryotoxic / teratogenic effects:
The mean fetal body weight was statistically significantly lower at 450 mg/kg bw/day and was considered to be related to the treatment with the test item. In correlation with the lower fetal weights a slight delay in ossification was noted in the high dose group (450 mg/kg bw/day). An increased incidence of long or interrupted costal cartilages or long ventral plate indicated a slight disturbance in development at this dose level.

Effect levels (fetuses)

Key result
Dose descriptor:
NOEL
Effect level:
ca. 150 mg/kg bw/day (actual dose received)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
fetal/pup body weight changes
other:
Remarks on result:
other: Effects seen are considered secondary to maternal toxicity or variations only

Fetal abnormalities

Key result
Abnormalities:
effects observed, treatment-related
Localisation:
skeletal: forelimb
skeletal: rib
skeletal: vertebra
skeletal: hindlimb
Description (incidence and severity):
An increased incidence of long or interrupted costal cartilages or long ventral plate indicated a slight disturbance in development at this dose level. However these observations are variations only, and not reported as malformations.

Overall developmental toxicity

Key result
Developmental effects observed:
yes
Lowest effective dose / conc.:
450 mg/kg bw/day (actual dose received)
Treatment related:
yes
Relation to maternal toxicity:
developmental effects as a secondary non-specific consequence of maternal toxicity effects
Dose response relationship:
yes
Relevant for humans:
not specified

Any other information on results incl. tables

Table 1: Results for Formulation Analysis

Dose Group

Sample taken from

Nominal Conc (mg/mL)

Actual Conc
(mg/mL)

Relative to Nominal
(%)

Mean
(%)

Control

vehicle

0.0

ND

-

-

2

top
middle
bottom

10.0
10.0
10.0

9.273
9.830
9.721

92.7
98.3
97.2


96.1

3

top
middle
bottom

30.0
30.0
30.0

31.61
29.51
29.25

105.4
98.4
97.5


100.4

4

top
middle
bottom

90.0
90.0
90.0

89.91
90.59
90.59

99.9
100.7
100.7


100.4

ND = not detected

In addition, the test item was found to be stable in application formulations when kept four hours at room temperature and eight days at in the refrigerator (5 ± 3 °C) due to recoveries which met the variation limit of 10% from the time-zero (homogeneity) mean value.

Table 2 - Summary of Performance of Mated Females

Group
Dose (mg/kg bw/day)

1
(0)

2
(50)

3
(150)

4
(450)

Female numbers

1 - 22

23 - 44

45 - 66

67 - 88

Number of mated females

22

22

22

22

Non-pregnant females (A)

1

0

1

1

Number of pregnant females

21

22

21

21

Number of females with live fetuses at termination*

21

22

21

21

*    Only dams with at least one live fetus at caesarean section were used for the calculations of food consumption, body weight gain and corrected body weight gain data.

(A) Female no. 10 from group 1 (control), female no. 57 from group 3 and female no. 79 from group 4 were not pregnant.

Applicant's summary and conclusion

Conclusions:
In the pre-natal developmental toxicity study conducted according to OECD Test Guideline 414 and in compliance with GLP, administration of trimethylsilanol (CAS 1066-40-6) by oral gavage to Sprague-Dawley rats from Day 6 to 20 of pregnancy at 0, 50, 150 or 450 mg/kg/day resulted in clinical signs and reduced food consumption and body weight gain in dams at 150 and 450 mg/kg bw/day. The effects on food consumption and body weight were considered to be adverse at 450 mg/kg/day, therefore the maternal NOAEL for general toxicity was considered to be 150 mg/kg/day. There was no maternal developmental effects observed but reduced foetal weight, delayed ossification and increased incidence of some cartilaginous variations were noted in foetuses at 450 mg/kg/day. The skeletal findings are reported to be variations only and are not considered to be adverse effects as such. The reduced foetal weight is considered secondary to maternal toxicity. Therefore the developmental NOEL is considered to be 150 mg/kg bw/day based on findings observed in the pups.