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Diss Factsheets

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:
24.09.2001 to 06.09.2002
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: The study was conducted according to a test protocol that is similar to the appropriate OECD test guideline, and in compliance with GLP.
Cross-reference
Reason / purpose for cross-reference:
reference to same study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2002
Report date:
2002

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
other: OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
Deviations:
no
Principles of method if other than guideline:
Modified OECD 422 and USEPA Health Effects test guideline OPPTS 870.3650 (2000)
GLP compliance:
yes
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
N-(3-(trimethoxysilyl)propyl)ethylenediamine
EC Number:
217-164-6
EC Name:
N-(3-(trimethoxysilyl)propyl)ethylenediamine
Cas Number:
1760-24-3
Molecular formula:
C8H22N2O3Si
IUPAC Name:
N-(2-Aminoethyl)-3-aminopropyltrimethoxysilane

Test animals

Species:
rat
Strain:
Sprague-Dawley
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River Laboratories, Inc., Portage, MI, USA
- Age at study initiation: At least 8 weeks
- Weight at study initiation: Males: 253-301 g; Females: 181-229 g
- Fasting period before study: None
- Housing: Iindividually in suspended wire-mesh cages elevated over Bed-O'Cobs bedding; during cohabitation the females were pared 1 to 1 with a male in a suspended wire-mesh cage; pregnant females were moved into shoebox cages containing Enviro-dri and Bed-O'Cobs combination bedding (no later than three days prior to their expected delivery date until remainder of the study)
- Diet: PMI Certified Rodent Chow #5002 (PMI Nutritional International, St. Louis, MO, USA), ad libitum
- Water: Municipal water, further purified by reverse osmosis, ad libitum
- Acclimation period: Five days

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25
- Humidity (%): 30-70
- Air changes (per hr): 10-15
- Photoperiod (hrs dark / hrs light): 12/12

IN-LIFE DATES: From: 01.10.2001 To: 11.04.2002

Administration / exposure

Route of administration:
oral: gavage
Vehicle:
corn oil
Details on exposure:
PREPARATION OF DOSING SOLUTIONS: The dosing formulations were prepared daily by adding an appropriate amount of test substance to a measured amount of vehicle (dried and de-acidified) under nitrogen atmosphere.

VEHICLE
- Justification for use and choice of vehicle (if other than water): Corn oil was dried and de-acidified to removal residual water before use as test substance hydrolyses in contact with moisture.
- Lot/batch no. (if required): 070K0127
- Purity: 100 %
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Concentration, homogeneity and stability of the test substance in the vehicle were verified by gas chromatopgraphy with a flame ionisation detection (FID). Concentration verification was conducted on a weekly basis.
Details on mating procedure:
- Impregnation procedure: cohoused
- If cohoused:
- M/F ratio per cage: 1:1
- Length of cohabitation: Until evidence of copulation occurred or up to 2 weeks
- Proof of pregnancy: vaginal plug or sperm in vaginal smear referred to as day 0 of pregnancy
Duration of treatment / exposure:
Males: 28 days (beginning 2 weeks prior to mating)
Toxicity phase female: 29 days (beginning 2 week prior to mating)
Reproductive phase females: 39-44 days (2 weeks prior to mating, throughout mating and pregnancy until day 3 postpartum
Frequency of treatment:
Daily (seven days/week)
Duration of test:
Up to 44 days
Doses / concentrationsopen allclose all
Dose / conc.:
25 mg/kg bw/day (actual dose received)
Dose / conc.:
125 mg/kg bw/day (actual dose received)
Dose / conc.:
500 mg/kg bw/day (actual dose received)
No. of animals per sex per dose:
10/sex/dose (with females only used for toxicity and reproductive phase groups)
Control animals:
yes, concurrent vehicle
Details on study design:
- Dose selection rationale: The dose selection was based on a 7-day range finding study where 3 Sprague-Dawlex rats per sex were dosed per gavage with 125, 250, 500 or 1000 mg/kg bw/day. As a result one high dose female was found dead on study day 4. One high dose male was found moribund on study day 6 and was humanely sacrificed. All other animals survived until scheduled necropsy. Slight effects on body weight and food consumption have been observed in the treatment groups. Increased breathing sounds recorded as rales and soiling and wetness around the muzzle were the most common clinical findings related to treatment. Both findings were most common and most persistent in the 1000 mg/kg bw/day group. Some animals in the lower dose groups exhibited rales or wetness around the nose and/or mouth or soiling of the muzzle. However, these clinical findings were detectable for only one or two days of the study. At the highest dose, the majority of the clinical signs were associated with the two mortalities. However, one of the surviving females from the high dose group exhibited rales, hunched posture and muzzle soiling. Both of the animals that died before scheduled sacrifice had gaseous distension of the gastrointestinal tract and small dark livers. There were no adverse findings in the necropsy examination of the surviving animals.

Examinations

Maternal examinations:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily for morbidity, moribundity and mortality. General clinical observations were made at least once per day, approximately one hour after dosing.

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Once before the first dosing and weekly thereafter.

BODY WEIGHT: Yes
- Time schedule for examinations: Individual body weights were recorded weekly beginning approximately one week prior to test substance administration, on the first day of dosing and just prior to scheduled necropsy.

FOOD CONSUMPTION: Individual food consumption was recorded weekly for female animals in the toxicity group for four weeks. Individual food consumption for the male animals and the reproductive group females were recorded during the first two weeks of treatment. Food consumption was not measured during the cohabitation period. Food consumption was measured for the reproductive group females throughout gestation until terminal sacrifice.

HAEMATOLOGY: Yes
- Time schedule for collection of blood: On the day of scheduled sacrifice
- Anaesthetic used for blood collection: Yes, ketamine HCl/Xylazine
- Animals fasted: Yes, overnight
- How many animals: All male and toxicity group females
- Parameters checked in table 1 were examined.

CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: On the day of scheduled sacrifice
- Animals fasted: Yes
- How many animals: All male and toxicity group females
- Parameters checked in table 1 were examined.

FUNCTIONAL OBSERVATIONAL BATTERY (FOB): Yes
- Time schedule for examinations: Prior to the start of dosing and during the fourth week of the treatment. The assessments were conducted following the daily dose administration.
- Dose groups that were examined: All male and toxicity group females.
- Battery of functions tested: cageside observations, hand-held observations, open field observations, categorical observations, measurements/counts, motor activity.
Ovaries and uterine content:
The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: No
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: No
- Number of late resorptions: No
Fetal examinations:
SACRIFICE
- Postpartum day 3

GROSS NECROPSY
- Gross necropsy consisted of external and internal examinations including the cervical, thoracic, and abdominal viscera.

HISTOPATHOLOGY / ORGAN WEIGHTS
Not conducted.
Statistics:
All data analysis was carried out using SAS. In all comparisons, the family wise error rate was held at 5% (alpha=0.05). Prior to this analysis, an exploratory analysis was carried out on all variables tested. Bartlett's test was used to check for heterogeneity of variances and a Kolmogorov-smirnov test was used to test normality of the data. Parametric data was then tested using one-way Analysis of Variance (ANOVA) followed by Dunnett's Test (if significant). Non-parametric data were tested by Kruskal Wallis Test followed by Wilcoxon (if significant). For variables that had multiple measurements across time Repeated Measurement ANOVA was used to analyse the data. Categorical data were tested for equal proportions using the Fisher's Exact Test.

Statistically significant probabilities are reported at either the p≤0.05 or p≤0.01 levels.
Indices:
Viability and fertility

Results and discussion

Results: maternal animals

Maternal developmental toxicity

Details on maternal toxic effects:
Maternal toxic effects:no effects

Details on maternal toxic effects:
No significant adverse systemic effects in maternal animals.

Effect levels (maternal animals)

Dose descriptor:
NOAEL
Remarks:
maternal
Effect level:
>= 500 mg/kg bw/day (actual dose received)
Based on:
test mat.
Basis for effect level:
other: No significant adverse systemic effects in maternal animals.

Results (fetuses)

Details on embryotoxic / teratogenic effects:
Embryotoxic / teratogenic effects:no effects

Details on embryotoxic / teratogenic effects:
No abnormal behaviour or effects, including teratogenic, were observed in offspring.

Effect levels (fetuses)

Dose descriptor:
NOAEL
Remarks:
developmental
Effect level:
>= 500 mg/kg bw/day (actual dose received)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: No abnormal behaviour or effects, including teratogenic, were observed in offspring.

Fetal abnormalities

Abnormalities:
not specified

Overall developmental toxicity

Developmental effects observed:
not specified

Applicant's summary and conclusion

Conclusions:
In an oral gavage study conducted to OECD 422 and to GLP (reliability score 1) the NOAEL for the test material relating to repeated dose (systemic) effects and to developmental toxicity was at least 500 mg/kg bw/day, as no significant adverse effects were observed up to the highest dose of 500 mg/kg bw/day tested in rats.