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Diss Factsheets

Toxicological information

Toxicity to reproduction

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Administrative data

Endpoint:
reproductive toxicity, other
Remarks:
Subchronic reproductive study
Type of information:
experimental study
Adequacy of study:
weight of evidence
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
secondary literature
Justification for type of information:
Data from peer reviewed journal

Data source

Reference
Reference Type:
publication
Title:
Subchronic reproductive study of test material was conducted on female rats for 36 days
Author:
Maryanti et al
Year:
2014
Bibliographic source:
Cukurova Medical Journal 2014

Materials and methods

Test guideline
Qualifier:
equivalent or similar to guideline
Guideline:
other: As mentioned below
Principles of method if other than guideline:
Subchronic reproductive study of test material was conducted on female rats for 36 days
GLP compliance:
not specified
Limit test:
no
Justification for study design:
No data available

Test material

Constituent 1
Chemical structure
Reference substance name:
9-(2-carboxyphenyl)-3,6-bis(diethylamino)xanthylium chloride
EC Number:
201-383-9
EC Name:
9-(2-carboxyphenyl)-3,6-bis(diethylamino)xanthylium chloride
Cas Number:
81-88-9
Molecular formula:
C28H31N2O3.Cl
IUPAC Name:
9-(2-carboxyphenyl)-3,6-bis(diethylamino)xanthenium chloride
Details on test material:
- Name of test material (as cited in study report): Rhodamine B
- Molecular formula : C28H31N2O3Cl
- Molecular weight : 479.017 g/mole
- Substance type: Organic
- Physical state: Solid

Test animals

Species:
rat
Strain:
Wistar
Details on species / strain selection:
No data available
Sex:
female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Laboratory Pharmacology Brawijaya University.
- Weight at study initiation: (P) -150-200 g
- Diet : ad libitum
- Water: ad libitum
- Temperature (°C):22’C
- Photoperiod (hrs dark / hrs light): 12-h light/dark

Administration / exposure

Route of administration:
other: orally using probe.
Vehicle:
other: double distilled water
Details on exposure:
Test material was dissolved with double distilled water and administered orally using probe.
Details on mating procedure:
No data available
Analytical verification of doses or concentrations:
not specified
Duration of treatment / exposure:
36 days
Frequency of treatment:
No details
Details on study schedule:
No data available
Doses / concentrations
Remarks:
4.5, 9 ,and 18 mg/200gm body weight=22.5,45, 90 mg/kg
No. of animals per sex per dose:
28 rats
Control animals:
yes, concurrent vehicle
Details on study design:
No data available
Positive control:
No data available

Examinations

Parental animals: Observations and examinations:
OTHER: Cycle determination was started at the end of
the treatment. The cycle of each female rat was determined by observation of vaginal smears, which were taken using a plastic tip.
Oestrous cyclicity (parental animals):
Estrous cyclicity was observed
Sperm parameters (parental animals):
No data available
Litter observations:
No data available
Postmortem examinations (parental animals):
No data available
Postmortem examinations (offspring):
No data available
Statistics:
Data are presented as mean ± SD and differences between groups were analyzed using 1-way ANOVA with SPSS 19.0 statistical package. Post Hoc test was used if the ANOVA was significant. p < 0.05 was considered statistically significant.
Reproductive indices:
No data available
Offspring viability indices:
No data available

Results and discussion

Results: P0 (first parental generation)

General toxicity (P0)

Clinical signs:
not specified
Dermal irritation (if dermal study):
not specified
Mortality:
not specified
Body weight and weight changes:
not specified
Food consumption and compound intake (if feeding study):
not specified
Food efficiency:
not specified
Water consumption and compound intake (if drinking water study):
not specified
Ophthalmological findings:
not specified
Haematological findings:
not specified
Clinical biochemistry findings:
not specified
Urinalysis findings:
not specified
Behaviour (functional findings):
not specified
Immunological findings:
not specified
Organ weight findings including organ / body weight ratios:
not specified
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
The test material reduces thickness of endometrium significantly compared to the control (P < 0.05). The 22.5,45 mg/kg doses did not generate significant difference in the thickness of endometrium (P> 0.05)
Histopathological findings: neoplastic:
not specified
Other effects:
not specified

Reproductive function / performance (P0)

Reproductive function: oestrous cycle:
effects observed, treatment-related
Description (incidence and severity):
In the 90mg/kg dose group increase ovarian MDA levels significantly than the control (P < 0.05). There was no significant difference in the
In 22.5 and 45 mg/kg dose group compared to the third dose (P > 0.05).Administration of test material in 45 and 90mg/kg dose group in female rats can reduce thenumber of primary, secondary, and De Graaf follicles significantly compared to the control (P < 0.05). For primary follicles, there were no significant differences among the three doses group(P> 0.05) Administration of test material in 45 and 90mg/kg dose group in female rats can reduce 17β-estradiol level significantly compared to the control (P < 0.05).
Reproductive function: sperm measures:
not specified
Reproductive performance:
not specified

Effect levels (P0)

Dose descriptor:
NOAEL
Effect level:
22.5 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
female
Basis for effect level:
histopathology: non-neoplastic
reproductive function (oestrous cycle)
Remarks on result:
other: overall no effects on estrous cycle

Target system / organ toxicity (P0)

Critical effects observed:
not specified
System:
other: not specified
Organ:
not specified
Treatment related:
not specified
Dose response relationship:
not specified
Relevant for humans:
not specified

Results: F1 generation

General toxicity (F1)

Clinical signs:
not examined
Dermal irritation (if dermal study):
not examined
Mortality / viability:
not examined
Body weight and weight changes:
not examined
Food consumption and compound intake (if feeding study):
not examined
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
Urinalysis findings:
not examined
Sexual maturation:
not examined
Organ weight findings including organ / body weight ratios:
not examined
Gross pathological findings:
not examined
Histopathological findings:
not examined
Other effects:
not examined

Developmental neurotoxicity (F1)

Behaviour (functional findings):
not examined

Developmental immunotoxicity (F1)

Developmental immunotoxicity:
not examined

Effect levels (F1)

Dose descriptor:
other: not specified
Generation:
F1
Based on:
not specified
Sex:
not specified
Basis for effect level:
other: not specified
Remarks on result:
not measured/tested

Target system / organ toxicity (F1)

Critical effects observed:
not specified
System:
other: not specified
Organ:
not specified
Treatment related:
not specified
Dose response relationship:
not specified
Relevant for humans:
not specified

Overall reproductive toxicity

Reproductive effects observed:
not specified
Treatment related:
not specified
Relation to other toxic effects:
not specified
Dose response relationship:
not specified
Relevant for humans:
not specified

Applicant's summary and conclusion

Conclusions:
NOAEL was considered to be 22.5 mg/kg base on ovarian toxicity through oxidative stress, a decrease in the number of follicles, and decreased level of 17β-estradiol which ultimately lowered the thickness of endometrium, When female rats were treated with test chemical.
Executive summary:

The subchronic reproductive study conducted on Wister female rats for 36 days. The test material wasdissolved with double distilled water and administeredat concentrations of 22.5 ,45 and 90mg/kg bw orally using probe.28Female rats were randomly divided into the following four groups: the control group and three treatment group Malondialdehyde level in ovary was measured thiobarbituric acid method using TBARS Assay Kit (R&D system, Catalog Series KGE013, USA). The numbers of primary, secondary, tertiary and de Graaf follicles were calculated from the right ovary cut transversely and then preparation was made and stained histologically with HE and the follicles were calculated using Dotslide Olympus Camera XC 10. The entire cross-section was analyzed and further identified with magnification of 100 X. The cycle of each female rat was determined by observation of vaginal smears, which were taken using a plastic tip. Saline was placed on the vaginal opening, aspirated, and then placed on a microscopic slide.After the sample had dried, it was stained with hematoxylin-eosin. When the dye was removed, the slide was washed in de-ionized water and examined under a binocular microscope. Animals in the diestrus phase were used. The remainder of the animals continued to have their estrous cycles checked daily, being sacrificed always when in diestrus.

 

The test material reduces thickness of endometrium significantly compared to the control (P < 0.05). The22.5,45 mg/kgdoses did not generate significant difference in the thickness of endometrium (P> 0.05).In the 90mg/kg dose group increase ovarian MDA levels significantly than the control (P < 0.05). There was no significant difference in the 22.5 and 45 mg/kg dose group compared to the 90mg/kg dose group(P > 0.05).Administration of test material in 45 and 90mg/kg dose group in female rats can reduce thenumber of primary, secondary, and De Graaf follicles significantly compared to the control (P < 0.05). For primary follicles, there were no significant differences among the three doses group(P> 0.05) Administration of test material in 45 and 90mg/kg dose group in female rats can reduce 17β-estradiol level significantly compared to the control (P < 0.05).Hence NOAEL was considered to be 22.5 mg/kg based onovarian toxicity through oxidative stress, a decrease in the number of follicles, and decreased level of 17β-estradiol which ultimately lowered the thickness of endometrium, When female rats were treated with test material orally.