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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:
weight of evidence
Study period:
Unavailable - study report dated 1971
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
study well documented, meets generally accepted scientific principles, acceptable for assessment

Data source

Reference
Reference Type:
other:
Title:
Unnamed
Year:
1971

Materials and methods

Test guideline
Qualifier:
no guideline followed
Principles of method if other than guideline:
- Principle of test: Prenatal developmental toxicity assay in pregnant rats
- Short description of test conditions: After overnight mating, the rats were randomly allocated to five groups which included one control group and four different treatment groups.LAS was prepared daily as a series of graded aqueous solutions. Animals in all groups were dosed orally at the standard volume of 1.0 mL/100 g. Control animals were dosed in a similar manner with distilled water used as the vehicle. The dams were observed daily for signs of toxicity and weighed on days 1, 3, 6, 10, 14, 17 and 20 of pregnancy. On day 20, the rats were killed by CO2 euthanasia.
- Parameters analysed / observed:Ovaries and uterine contents were examined immediately for number of copora lutea, number of viable young, number of resorption sites, litter weight, and fetal abnormalities.
GLP compliance:
no
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
Benzenesulfonic acid, C10-13-alkyl derivs., sodium salts
EC Number:
270-115-0
EC Name:
Benzenesulfonic acid, C10-13-alkyl derivs., sodium salts
Cas Number:
68411-30-3
Molecular formula:
Not applicable for UVCB
IUPAC Name:
sodium 4-undecylbenzenesulfonate
Details on test material:
LAS (Na salt) as a slurry containing 64.0% w/v of active ingredient (Lion Oil and Fat Co., Ltd.); average alkyl chain length (based on LAS SIDS Consortium Survey, 2002) = C11.7-12.3.

Test animals

Species:
rat
Strain:
other: Charles River CD strain

Administration / exposure

Route of administration:
oral: drinking water
Vehicle:
not specified
Analytical verification of doses or concentrations:
not specified
Duration of treatment / exposure:
day 6 to day 15 of pregnancy
Frequency of treatment:
daily
Duration of test:
20 days
Doses / concentrationsopen allclose all
Dose / conc.:
0 other: mg/kg
Dose / conc.:
0.2 other: mg/kg
Dose / conc.:
2 other: mg/kg
Dose / conc.:
300 other: mg/kg
Dose / conc.:
600 other: mg/kg
No. of animals per sex per dose:
not specified
Control animals:
yes, concurrent no treatment
Details on study design:
After overnight mating, the rats were randomly allocated to five groups which included one control group and four different treatment groups. LAS was prepared daily as a series of graded aqueous solutions. Animals in all groups were dosed orally at the standard volume of 1.0 mL/100 g. Control animals were dosed in a similar manner with distilled water used as the vehicle. The dams were observed daily for signs of toxicity and weighed on days 1, 3, 6, 10, 14, 17 and 20 of pregnancy. On day 20, the rats were killed by CO2 euthanasia. Their ovaries and uterine contents were examined immediately for number of corpora lutea, number of viable young, number of resorption sites, litter weight, and fetal abnormalities.

Examinations

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

BODY WEIGHT: Yes
Ovaries and uterine content:
The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Number of corpora lutea: Yes
- Number of early resorptions: Yes / No / No data
- Number of late resorptions: Yes
Fetal examinations:
- External examinations: Yes

Results and discussion

Results: maternal animals

General toxicity (maternal animals)

Clinical signs:
not specified
Dermal irritation (if dermal study):
not examined
Mortality:
not specified
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
Change in bodyweight was not affected by treatment at 0.2, 2.0, and 300 mg/kg, but treatment at 600 mg/kg was associated with retarded weight gain and a transient diarrhea following initiation of treatment.
Food consumption and compound intake (if feeding study):
not examined
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:
not examined
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
not examined
Gross pathological findings:
not specified
Neuropathological findings:
not examined
Histopathological findings: non-neoplastic:
not specified
Details on results:
Parent animals were observed daily.Change in bodyweight was not affected by treatment at 0.2, 2.0, and 300 mg/kg, but treatment at 600 mg/kg was associated with retarded weight gain and a transient diarrhea following initiation of treatment

Maternal developmental toxicity

Number of abortions:
not specified
Pre- and post-implantation loss:
not examined
Total litter losses by resorption:
not examined
Early or late resorptions:
no effects observed
Dead fetuses:
not specified
Changes in pregnancy duration:
not specified
Changes in number of pregnant:
no effects observed
Details on maternal toxic effects:
The pregnancy rate was comparable at all dosages.

Effect levels (maternal animals)

Key result
Dose descriptor:
NOAEL
Effect level:
300 other: mg/kg
Based on:
test mat.
Basis for effect level:
body weight and weight gain
Remarks on result:
other: maternal toxicity
Remarks:
retarded weight gain and a transient diarrhea observed at high dose level

Maternal abnormalities

Abnormalities:
no effects observed

Results (fetuses)

Fetal body weight changes:
effects observed, non-treatment-related
Description (incidence and severity):
Mean pup weights were statistically higher at 0.2, 2.0 and 300 mg/kg.
Reduction in number of live offspring:
no effects observed
Changes in sex ratio:
not examined
Changes in litter size and weights:
no effects observed
Changes in postnatal survival:
not examined
External malformations:
no effects observed
Skeletal malformations:
effects observed, treatment-related
Description (incidence and severity):
The distribution of skeletal variants were not statistically significant with the exception of a marginal retardation of sternebral ossification at 600 mg/kg.
Visceral malformations:
no effects observed
Description (incidence and severity):
The incidence of minor visceral anomalies was unaffected by treatment at any dosage.
Details on embryotoxic / teratogenic effects:
- Pregnancy/litter data: The litter parameters assessed included litter size, fetal loss and litter weight. These parameters were not significantly affected by any dosage. Mean pup weights were statistically higher at 0.2, 2.0 and 300 mg/kg.
- Embryonic and fetal development were assessed by the incidence of major malformations. The incidence of minor visceral anomalies was unaffected by treatment at any dosage. The distribution of skeletal variants were not statistically significant with the exception of a marginal retardation of sternebral ossification at 600 mg/kg.

Effect levels (fetuses)

Key result
Dose descriptor:
NOAEL
Effect level:
300 other: mg/kg
Based on:
test mat.
Sex:
male/female
Basis for effect level:
skeletal malformations
Remarks on result:
other: teratogenicity
Remarks:
marginal retardation of sternebral ossification

Fetal abnormalities

Abnormalities:
no effects observed

Overall developmental toxicity

Developmental effects observed:
no

Applicant's summary and conclusion

Conclusions:
Female rats were given LAS orally in distilled water from gestation days 6 to 15 during pregnancy. Some effects such as decreased weight gain and transient diarrhea occurred at the highest dose. Pregnancy rates were comparable at all doses. Litter parameters were not significantly affected at any dose. No significant differences were observed in visceral anomalies or skeletal variants, with the exception of a marginal retardation of sternabral ossification at the highest dose. Based on these results the maternal and developmental NOAELs were therefore determined to 300 mg/kg.
Executive summary:

In a developmental toxicity study LAS was administrated pregnant Charles River CD rats/does in water at dose levels of 0, 0.2, 2, 300 or 600 mg/kg from days 6 through 15 of gestation. The number of animals tested was not specified in the study.

The parent animals were observed daily. Body weight change was not affected by treatment at 0.2, 2.0 and 300 mg/kg, but treatment at 600 mg/kg was associated with delayed weight gain and transient diarrhoea after the start of treatment. Pregnancy rates were comparable at all doses. Litter parameters evaluated were litter size, fetal loss and litter weight. These parameters were not significantly affected by any of the doses. Mean pup weights were statistically higher at 0.2, 2.0 and 300 mg/kg. In addition, embryonic and fetal development was assessed by the incidence of major malformations. The incidence of minor visceral anomalies was not affected by the treatment at any dose. The distribution of skeletal variants was not statistically significant except for a marginal delay in sternal ossification at 600 mg/kg. Based on these observations the maternal and the developmental NOAELs are therefore determined to be 300 mg/kg.