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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
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Referenceopen allclose all

Reference Type:
study report
Title:
Unnamed
Year:
2001
Report date:
2001
Reference Type:
publication
Title:
Developmental Toxicity Evaluation of Sodium Thioglycolate Administered Topically to Sprague-Dawley (CD) Rats and New Zealand White Rabbits
Author:
Tyl RW, Price CJ, Marr MC, Myers BB, van Birgelen APJM and Jahnke GD
Year:
2003
Bibliographic source:
Birth Defects Research (Part B) 68:144-161

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 414 (Prenatal Developmental Toxicity Study)
GLP compliance:
yes
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
Sodium mercaptoacetate
EC Number:
206-696-4
EC Name:
Sodium mercaptoacetate
Cas Number:
367-51-1
Molecular formula:
C2H4O2S.Na
IUPAC Name:
sodium sulfanylacetate
Details on test material:
Test substance: Sodium thioglycolate
CAS No.: 367-51-1
Source: Sigma Chemical Company by Midwest Research Institute (Kansas City, MO)
Batch: No. 88H1166
Purity: 99% (identity confirmed by infrared spectrometry) Solvent: 95% ethanol:distilled water (1:1).

Test animals

Species:
rat
Strain:
Sprague-Dawley
Details on test animals or test system and environmental conditions:
Test animals:         
- Source: Charles River Laboratories (Raleigh, NC).        
- Age: no data         
- Weight at dosing: ca. 250 g        
-  Acclimation period: no data        
- Diet: Purina Certified Rodent Chow (No. 5002), ad libitum        
-  Water: Tap water, ad libitum         
- Housing: singly housed in solid-bottom  polycarbonate cages with stainless steel wire lids with Sani-Chips certified hardwood bedding

Environmental conditions:         
- Temperature: 70.0-72.81 F         
- Humidity: 28.0-58 %         
- Air changes: no data         
- Photoperiod: Alternating 12-hour light and dark cycles

Administration / exposure

Route of administration:
dermal
Vehicle:
other: 95% ethanol:distilled water, 1:1
Details on exposure:
Treatment: 1.5 ml/kg of test material in vehicle or vehicle alone was applied  directly to a 3x3 inch shaved area on the dorsum of the rat with a glass  syringe fitted with a 16-gauge, stainless-steel, ball-tipped dosing  needle. The formulation was allowed to remain on the animal for a minimum  of 6 hr/treatment day. At the end of each 6-hr period, the application  site was wiped with warmwater-soaked gauze to remove residual vehicle or  sodium thioglycolate.
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Prepared weekly based on stability information and were verified to be  within 92.7-103.5 % of target.
Duration of treatment / exposure:
gestation days 6-19
Frequency of treatment:
daily
Duration of test:
necropsy on GD 20
Doses / concentrationsopen allclose all
Dose / conc.:
50 mg/kg bw/day (actual dose received)
Dose / conc.:
100 mg/kg bw/day (actual dose received)
Dose / conc.:
200 mg/kg bw/day (actual dose received)
No. of animals per sex per dose:
25
Control animals:
yes, concurrent vehicle
Details on study design:
Pregnant Sprague Dawley derived (CD.) rats were topically exposed to sodium thioglycolate in vehicle (50, 100, and 200 mg/kg/day) or vehicle  alone (95% ethanol:distilled water, 1:1) from gestational day (gd) 6  through 19.

Examinations

Maternal examinations:
Females were monitored at regular intervals throughout gestation for clinical signs (including dosing site condition), feed and water intake, and body weight. At necropsy on GD 20, the following were recorded: maternal clinical condition; body, liver and gravid uterine weights; and pregnancy status.
Ovaries and uterine content:
The number of ovarian corpora lutea and uterine implantations (resorbed,  dead, or live fetuses) was recorded.
Fetal examinations:
All live foetuses were counted, weighed, and examined for external alterations, including cleft palate. Approximately 50% of the live foetuses per litter were sexed internally  and examined for visceral alterations. These foetuses were decapitated  and the heads fixed, decalcified, and examined for soft tissue  craniofacial alterations. All foetal carcasses were eviscerated (and  foetuses not scheduled for a visceral examination were sexed internally),  macerated, and stained with alizarin red S and alcian blue. Intact  foetuses (those not decapitated) were examined for ossified and  cartilaginous skeletal alterations.
Statistics:
The unit for statistical measurement was the pregnant female or the  litter. Quantitative continuous data (e.g., maternal body weights, foetal  body weights, feed consumption, etc.) were compared among treatment  groups, per species, by parametric statistical tests whenever Bartlett  test for homogeneity of variance was not significant.  General linear models (GLM) procedures were applied to the ANOVA and the  tests for linear trend. Before GLM analysis, an arc sine-square root  transformation was carried out on all litter-derived percentage data  (e.g., % resorptions/litter, % malformations/litter, % variations/litter)  (Snedecor and Cochran, 1967). For litter-derived percentage data, the  ANOVA was weighted according to litter size. When a significant (p <  0.05) main effect for dose occurred, Dunnett's multiple comparison test  (Dunnett, 1955, 1964) was used to compare each treatment group to the  control group for that measure. A one-tailed (i.e., Dunnett's test) was used for all pairwise comparisons  to the vehicle control group, except that a two-tailed test was used for maternal body and organ weight  parameters, maternal feed consumption, fetal body weight, and percent  males per litter.

Results and discussion

Results: maternal animals

General toxicity (maternal animals)

Clinical signs:
no effects observed
Dermal irritation (if dermal study):
effects observed, treatment-related
Description (incidence and severity):
see below
Mortality:
mortality observed, treatment-related
Description (incidence):
see below
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
see below
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
see below
Food efficiency:
not specified
Water consumption and compound intake (if drinking water study):
effects observed, treatment-related
Description (incidence and severity):
see below
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:
no effects observed
Gross pathological findings:
no effects observed
Neuropathological findings:
not examined
Histopathological findings: non-neoplastic:
not examined
Histopathological findings: neoplastic:
not examined
Other effects:
not specified
Details on results:
Sodium thioglycolate treatment was associated with one maternal death at 200 mg/kg/day (only clinical observations at the dosing site preceded death). Other effects, dependent on dose and exposure duration, included body weight and weight gain reductions, changes in relative feed and water intake, and discolouration and slight erythema at the application site. Feed consumption in g/kg/day was significantly increased above the control at 50 (5.4%) and 100 (6.1%) mg/kg/day, but not at 200 mg/kg/day (2.2%). Maternal water consumption in g/kg/day was significantly increased at 200 mg/kg/day, (12.7%) and slightly (but not statistically significantly) increased at 50 (3.2%) and 100 (5.1%) mg/kg/day. Maternal body weights and body weight changes were decreased only at 200 mg/kg/day. At scheduled necropsy, there were no macroscopic indications of organ toxicity. In addition, organ weights and gravid uterine weights were equivalent across groups; maternal body weight was significantly reduced at 200 mg/kg/day.

Maternal developmental toxicity

Number of abortions:
no effects observed
Pre- and post-implantation loss:
no effects observed
Total litter losses by resorption:
no effects observed

Effect levels (maternal animals)

open allclose all
Key result
Dose descriptor:
NOAEL
Effect level:
< 50 mg/kg bw/day (actual dose received)
Based on:
test mat.
Basis for effect level:
clinical signs
food consumption and compound intake
Key result
Dose descriptor:
LOAEL
Effect level:
<= 50 mg/kg bw/day (actual dose received)
Based on:
test mat.
Basis for effect level:
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):
see below
Reduction in number of live offspring:
effects observed, treatment-related
Description (incidence and severity):
see below
Changes in sex ratio:
no effects observed
Changes in litter size and weights:
effects observed, treatment-related
Changes in postnatal survival:
not examined
External malformations:
no effects observed
Skeletal malformations:
no effects observed
Visceral malformations:
no effects observed
Other effects:
not specified
Details on embryotoxic / teratogenic effects:
Details on embryotoxic / teratogenic effects:
Prenatal viability was unaffected by maternal exposure to sodium  thioglycolate. The incidences of foetal external, visceral, and skeletal  alterations were also unaffected. A significant, dose-related, upward  trend was present for % foetuses with skeletal variations per litter, but  there were no significant pairwise comparisons to the vehicle control  group value. The historical data presented in the study report shown a  range of 0.58 to 25.65 % for this parameter, with 9 out of 21 studies  (43%) with a % higher than 15.1% (the highest value observed at 200 mg/kg  bw/d). Accordingly, this effect was not considered as treatment-related.  Body weights of male and female foetuses per litter at 200 mg/kg/day were  significantly lower than control values.

Effect levels (fetuses)

open allclose all
Key result
Dose descriptor:
NOAEL
Effect level:
100 mg/kg bw/day (actual dose received)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
reduction in number of live offspring
fetal/pup body weight changes
changes in litter size and weights
Key result
Dose descriptor:
LOAEL
Effect level:
200 mg/kg bw/day (actual dose received)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
reduction in number of live offspring
fetal/pup body weight changes
changes in litter size and weights

Fetal abnormalities

Key result
Abnormalities:
no effects observed

Overall developmental toxicity

Key result
Developmental effects observed:
no

Any other information on results incl. tables

Maternal Toxicity in CD Rats Exposed to Sodium Thioglycolate by Topical Application on Gestational Days 6 Through 19

                                              

Sodium thioglycolate (mg/kg/day, dermal)

0

50

100

200

Maternal pregnancy status

Treated, n

25

25

25

25

Removed, n

0

0

0

0

Dead or euthanized, n

0

0

0

1a

Pregnant at sacrifice, n(%)

25(100)

23(92)

23(92)

21(88)b

Maternal body weight changes (g)c,d

Pretreatment wt. gain (GD 0–6)

32.2±1.3h

29.21±1

28.4±2.1

26.5±1.6

Gestation weight gain (GD 0–20)

135.6±3.3i

129.7±4.4

127.0±5.0

112.5±5.9k

Treatment weight gain (GD 6–20)

110.1±3.1i

106.5±4.0

104.8±3.8

92.7±5.7j

Corrected weight gaine

49.6±1.8i

45.6±2.4

43.9±3.3

34.8±2.8k

Gravid uterine wt.

86.0±3.2

84.1±3.1

83.0±3.1

77.6±4.9

Maternal organ weightsc,f

Liver Absolute (g)

17.78±0.23

17.64±0.40

17.69v0.29

17.02±0.27

Relative (% sacrifice wt.)f

4.53±0.04

4.56±0.07

4.62±0.05

4.65±0.08

Kidney Absolute (g)

2.22±0.04

2.19±0.05

2.26±0.05

2.20±0.04

Relative (% sacrifice wt.)f

0.57±0.01h

0.57±0.01

0.59±0.01

0.60±70.01

Maternal feed consumptionc,g

Pretreatment period (gd 0–6)

Absolute (g/day)

23.4±0.5

23.2±0.6

22.6±0.6

22.5±0.4

Relative (g/kg/day)

85.0±1.4

84.6±1.7

83.3±2.0

83.6±1.3

Treatment period (GD 6–20)

Absolute (g/day)

26.3±0.3

27.5±0.4

27.3±0.5

25.5±0.4

Relative (g/kg/day)

77.1±0.5

81.3±0.9k

81.8±0.8k

78.8±0.8

Maternal water consumptionc,g

Pretreatment period (gd 0–6)

Absolute (g/day)

35.7±1.2

34.2±0.9

32.4±1.1

34.1±0.9

Relative (g/kg/day)

129.8v4.3

125.2v2.9

119.0±3.5

126.9±3.1

Treatment period (gd 6–20)

Absolute (g/day)

43.6±1.3

44.1±1.3

44.4±1.1

46.2±1.2

Relative (g/kg/day)

127.1±3.2i

131.2±3.3

133.6±2.6

143.3v3.9k

aDam 4 was found dead on the morning of gd 18.

bDam 31 had only one implantation site, and no live fetuses on gd 20.

cIncludes all dams pregnant at sacrifice; mean 7 SEM; gd, gestational day.

dBody weights were recorded in the morning of each designated gestational day.

eWeight change during gestation minus gravid uterine weight.

fCalculated using body weight at the time of sacrifice on gd 20.

gRelative feed and water consumption (g/kg/day) were calculated using appropriate body weights.

hp<0.05; Test for linear trend.

ip<0.01; Test for linear trend.

jp<0.05; Dunnett’s test

k p<0.01; Dunnett’s test.

Developmental Toxicity in CDsRat Fetuses Following Maternal Exposure to Sodium Thioglycolate by Topical. Application on Gestational Days 6 Through 19

Sodium Thioglycolate (mg/kg/day, dermal)

0

50

100

200

All littersa,b

25

23

23

21

No. corpora lutea/dam

17.5±0.4

16.7±0.5

16.4±0.5

16.8±0.7

No. implantation sites/litter

15.6±0.5

15.1±0.6

14.7±0.7

15.4±v0.8

% preimplantation loss/litter

11.2±2.7

10.3±2.4

11.6±3.6

10.5±4.1

% resorptions/litter

3.9±1.3

4.6±1.4

3.0±0.9

11.2±5.1

% litters with resorptions

40

48

35

52

% late fetal deaths/litter

0.0±0.0

0.3±0.3

0.0±0.0

0.0±0.0

% litters with late fetal deaths

0

4

0

0

Live littersb,c

25

23

23

20d

No. live fetuses/litter

15.0±0.6

14.4±0.6

14.2±0.6

15.1±0.6

Avg. male fetal body wt./litter (g)

3.73±0.06f

3.70±0.05

3.75±0.08

3.42±0.08g

Avg. female fetal body wt./litter (g)

3.50±0.05e

3.56±0.05

3.61±0.10

3.2570.08g

% male fetuses/litter

45.173.6

52.373.5

50.673.2

52.5±2.3

% externally malformed fetuses/litter

0.0±0.0

0.0±0.0

0.9±0.7

0.3±0.3

% viscerally malformed fetuses/litter

0.0±0.0

0.5±0.5

0.0±0.0

2.2±1.7

% skeletally malformed fetuses/litter

2.3±1.8

2.2±1.0

1.2±0.8

4.5±2.6

% malformed fetuses/litter

1.1±0.9

1.4±0.6

1.5±0.7

3.4±2.2

% fetuses with external variations/litter

0.5±0.5

0.5±0.4

0.0±0.0

0.3±0.3

% fetuses with visceral variations/litter

3.3±1.3

5.0±1.5

3.7±1.7

3.7±2.2

% fetuses with skeletal variations/litter

3.9±1.3f

6.4±2.3

11.2±3.0

15.1±4.2

% fetuses with variations/litter

4.1±1.0

6.3±1.4

7.3±1.7

9.9±2.6

aIncludes all dams pregnant at sacrifice; litter size¼no. implantation sites per dam.

bReported as the mean 7 SEM.

cIncludes only dams with live fetuses; litter size¼no. live fetuses per dam.

dOne female at 200 mg/kg/day had a fully resorbed litter at scheduled necropsy.

ep<0.05; Test for linear trend.

fp<0.01; Test for linear trend.

gp<0.05; Dunnett’s test.

Applicant's summary and conclusion

Conclusions:
Topically applied sodium thioglycolate resulted in toxicity to the dam at 200 mg/kg/day (expressed as reduced body weights and weight gain, increased relative water consumption, observations at the dosing site and one death). Treatment-related increases in feed consumption (and observations at the application site) were also present at 50 and 100 mg/kg/day, in the absence of increased body weights or body weight change. This is an uncommon finding and has been previously observed in rats exposed to sodium thioglycolate, attributed to a block in fatty acid metabolism. Sodium thioglycolate at 200 mg/kg/day also resulted in significantly decreased male and female foetal body weights per litter, with no other evidence of embryofoetal toxicity and no evidence of treatment-related teratogenicity. Based on the study findings, a no observed adverse effect level (NOAEL) could not be identified for maternal toxicity while for developmental toxicity, 100 mg/kg/day was the NOAEL.
Executive summary:

The developmental toxicity of sodium thioglycolate was evaluated in pregnant rats in a study performed according to a method comparable to the OECD guideline # 414. Pregnant Sprague-Dawley rats were exposed topically, 6 hr/day, to sodium thioglycolate (99% pure) in vehicle (95% ethanol:distilled water, 1:1) from gestational day (gd) 6 through 19 at dose levels of 0, 50, 100, and 200 mg/kg bw/d. Twenty-five timed-mated female rats were assigned to each group and monitored at regular intervals throughout gestation for clinical signs (including dosing site condition), feed and water intake, and body weight. At necropsy on gestational day 20; the following were recorded: maternal clinical condition; body, liver and gravid uterine weights; and pregnancy status. The number of ovarian corpora lutea and uterine implantations (resorbed, dead, or live foetuses) was recorded. All live foetuses were counted, weighed, and examined for external alterations, including cleft palate. Approximately 50% of the live rat foetuses per litter were sexed internally and examined for visceral alterations. These foetuses were decapitated and the heads fixed, decalcified, and examined for soft tissue craniofacial alterations. All foetal carcasses were eviscerated (and rat foetuses not scheduled for a visceral examination were sexed internally), macerated, and stained with alizarin red S and alcian blue. Intact rat foetuses (those not decapitated) were examined for ossified and cartilaginous skeletal alterations.

Sodium thioglycolate treatment was associated with one maternal death at 200 mg/kg/d (only clinical observations at the dosing site preceded death). Other effects, dependent on dose and exposure duration, included body weight and weight gain reductions, changes in relative feed and water intake, and discoloration and slight erythema at the application site. Feed consumption was significantly increased above the control at 50 (5.4%) and 100 (6.1%) mg/kg bw/d, but not at 200 mg/kg bw/d (2.2%). Maternal water consumption was significantly increased at 200 mg/kg bw/d (12.7%) and slightly (but not statistically significantly) increased at 50 (3.2%) and 100 (5.1%) mg/kg bw/d. Maternal body weights and body weight changes were decreased only at 200 mg/kg bw/d. At scheduled necropsy, there were no macroscopic indications of organ toxicity. In addition, organ weights and gravid uterine weights were equivalent across groups; maternal body weight was significantly reduced at 200 mg/kg/d. Prenatal viability was unaffected by maternal exposure to sodium thioglycolate. The incidences of foetal external, visceral, and skeletal alterations were also unaffected. A significant, dose-related, upward trend was present for % foetuses with skeletal variations per litter, but there were no significant pairwise comparisons to the vehicle control group value and the % were in the range of the historical control data . Body weights of male and female foetuses per litter at 200 mg/kg bw/d were significantly lower than control values. The maternal NOAEL could not be identified.