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Administrative data

Key value for chemical safety assessment

Toxic effect type:
dose-dependent

Effects on fertility

Description of key information

NOAEL fertiliy and development ≥ 750 mg/kg bw/day (highest dose tested) (OECD 421, GLP, Key, Rel.1)

Link to relevant study records
Reference
Endpoint:
screening for reproductive / developmental toxicity
Type of information:
experimental study
Adequacy of study:
key study
Study period:
05 Jun - 24 Aug 2005
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 421 (Reproduction / Developmental Toxicity Screening Test)
Version / remarks:
1995
Deviations:
yes
Remarks:
gross pathological findings were not examined in the F1 generation
GLP compliance:
yes (incl. QA statement)
Limit test:
no
Specific details on test material used for the study:
- Date of receipt: 29 Apr 2005
- Color: amber
- Form: liquid
- Storage conditions: room temperature (approx. 22 ± 3°C), protected from light
Species:
rat
Strain:
Sprague-Dawley
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Taconic Farms, Germantown, USA
- Females nulliparous and non-pregnant: yes
- Age at study initiation: (P) x 8 wks
- Weight at study initiation: (P) Males: 190-214 g; Females: 161-173 g
- Housing: individually in stainless steel cages; one male and one female in polycarbonate shoebox with corncob bedding during mating period.
- Diet: Harlan Teklad Certified Rodent Diet 8728C ad libitum
- Water: tap water from the city of Chicago ad libitum
- Acclimation period: 1 week

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18-26
- Humidity (%): 30-70
- Air changes (per hr): 10
- Photoperiod (hrs dark / hrs light): 12/12

IN-LIFE DATES: From: 05 Jun 2005 To: 24 Aug 2005
Route of administration:
oral: gavage
Vehicle:
water
Remarks:
deionized
Details on exposure:
PREPARATION OF DOSING SOLUTIONS:

DIET PREPARATION
- Rate of preparation of diet: every week
- Mixing appropriate amounts with: water
- Storage temperature of food: room temperature (approx. 22 ± 3°C)

VEHICLE
- Concentration in vehicle: 10, 50 and 150 mg/mL
- Amount of vehicle: 5 mL/kg bw
Details on mating procedure:
- M/F ratio per cage: 1/1
- Length of cohabitation: up to 2 weeks
- Proof of pregnancy: vaginal plug or sperm in vaginal smear referred to as day 0 of pregnancy
- After successful mating each pregnant female was caged: individually shoebox cage with corncob bedding
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Samples of the dosing formulations taken from the 1st, 2nd and 7th week preparations were analyzed for homogeneity via HPLC-UV prior to using. The analytically determined concentrations were within 10% of the target concentrations.
Duration of treatment / exposure:
(P) Males: 2 weeks before mating, 1 week during mating, 2 weeks after mating (minimum of 35 days)
(P) Females: 2 weeks before mating, 1 week during mating, during gestation and lactation until post-partum day 4 (minimum of 46 days)
Frequency of treatment:
7 days/week
Dose / conc.:
50 mg/kg bw/day (actual dose received)
Dose / conc.:
250 mg/kg bw/day (actual dose received)
Dose / conc.:
750 mg/kg bw/day (actual dose received)
No. of animals per sex per dose:
12 P males and 12 P females per tested concentration and per control
Control animals:
yes, concurrent vehicle
Details on study design:
- Dose selection rationale: Doses were selected by the sponsor based on the results of previous toxicity studies with the test material.
Parental animals: Observations and examinations:
CAGE SIDE OBSERVATIONS: Yes

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly

BODY WEIGHT: Yes
- Time schedule for examinations: 1 day prior to treatment initiation and weekly thereafter

FOOD CONSUMPTION AND COMPOUND INTAKE: Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as gfood/kg body weight/day: No
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No



Oestrous cyclicity (parental animals):
The stage of the estrous cycle was determined with daily vaginal smears taken during mating period until evidence for mating was found.
Sperm parameters (parental animals):
Parameters examined in P male parental generations:
testis weight and epididymis weight, stages of spermatogenesis and interstitial testicular cell structure
Litter observations:
STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: no

PARAMETERS EXAMINED
The following parameters were examined in F1 offspring:
number and sex of pups, stillbirths, live births

GROSS EXAMINATION OF DEAD PUPS:
yes, for external abnormalities; possible cause of death was not determined for pups born or found dead.

Postmortem examinations (parental animals):
SACRIFICE
- Male animals: All surviving animals, including those found dead or euthanized moribund
- Maternal animals: All surviving animals, including those found dead or euthanized moribund

GROSS NECROPSY
- Gross necropsy consisted of examination of the external body surface, all orifices, the cranial, thoracic, and peritoneal cavities and their contents.

HISTOPATHOLOGY / ORGAN WEIGHTS
- The tissues of livers, ovaries, testes and epididymides were prepared for microscopic examination and weighed, respectively.
Postmortem examinations (offspring):
The F1 animals were not subjected to postmortem examinations.

Statistics:
Calculation of means and standard deviations using Microsoft Excel; Systat 10 used for remaining statistical analysis. Analysis of data for homogeneity of variance using Levene's test. In case of homogeneous data, the data were further analyzed by one-way analysis of variance (ANOVA); in case of non-homogeneous data, Dunnett's test was performed for post-hoc comparisons. Mating and absolute pup-survival were analyzed using the Chi-Square test.
Reproductive indices:
Successful Mating: (# Successful Parturation / # Selected for Littering) x 100
% Pre-implantation loss = [(Total Corpora Lutea - Total Corpora Implants) / Total Corpora Lutea] x 100
% Post-implantation loss = [(Total Implants - Total Born) / Total Implants] x 100
Offspring viability indices:
% alive on day 0 = [(Total number of pups born - number of stillborn fetuses) / Total number of pups born] x 100
% alive on day 4 = (number alive on day 4 / number alive on day 0) x 100
% surviving = (number alive on day 4 / number alive on day 0) x 100
Clinical signs:
effects observed, non-treatment-related
Description (incidence and severity):
All signs observed (i.e. alopecia, red material around nose/eyes, forelimbs/gead scab, and ventral mass) were sporadically distributed among the groups and low in incidence.
Dermal irritation (if dermal study):
not examined
Mortality:
mortality observed, non-treatment-related
Description (incidence):
One control female (animal number 62) died during the first week of the study due to gavage trauma.
Body weight and weight changes:
no effects observed
Description (incidence and severity):
Body weight and body weight gain were similar across all groups with no observed treatment-related trends.
Food consumption and compound intake (if feeding study):
no effects observed
Description (incidence and severity):
Food consumption was not affected by treatment.
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
Endocrine findings:
not examined
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
effects observed, treatment-related
Histopathological findings: non-neoplastic:
effects observed, non-treatment-related
Description (incidence and severity):
Histopathological findings (i.e. degeneration of germinal epithelium in the testes and interstitial infiltration with mixed cells in the epididymides) were considered incidental and non-treatment related.
Histopathological findings: neoplastic:
no effects observed
Other effects:
no effects observed
Reproductive function: oestrous cycle:
no effects observed
Reproductive function: sperm measures:
no effects observed
Reproductive performance:
no effects observed
Key result
Dose descriptor:
NOAEL
Remarks:
reproductive
Effect level:
>= 750 mg/kg bw/day
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: no adverse effects observed up to highest dose tested
Remarks on result:
not determinable due to absence of adverse toxic effects
Key result
Critical effects observed:
no
Clinical signs:
not examined
Dermal irritation (if dermal study):
not examined
Mortality / viability:
no mortality observed
Body weight and weight changes:
no effects observed
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
Anogenital distance (AGD):
not examined
Nipple retention in male pups:
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
Behaviour (functional findings):
not examined
Developmental immunotoxicity:
not examined
Key result
Dose descriptor:
NOAEL
Generation:
F1
Effect level:
>= 750 mg/kg bw/day
Based on:
test mat.
Sex:
not specified
Basis for effect level:
other: no adverse effects were observed up to the highest concentration
Remarks on result:
not determinable due to absence of adverse toxic effects
Key result
Critical effects observed:
no
Key result
Reproductive effects observed:
no
Conclusions:
Based on these findings, the no-observed-adverse-effect level (NOAEL) for systemic and reproductive toxicity is equal to or greater than the highest dose tested 750 mg/kg bw/day.
Executive summary:

Test Item was formulated in deionized water (vehicle) and was administered as a solution by oral gavage at dose levels of 0 (vehicle control), 50, 250 or 750 mg/kg bw/day to 12 Sprague­ Dawley rats/sex/group for the assessment of reproductive and developmental toxicity. Doses were administered at a constant volume of 5 mL/kg bw for 2 weeks prior to mating, during the approximately 1-week mating period, through gestation and lactation until sacrifice, for a total of 5 weeks of dosing for males and approximately 7 weeks for females. Parental food consumption, body weights, body weight gain, reproductive performance, organ weights and histopathology were evaluated during the study, along with offspring body weight and survival.


 


No treatment-related clinical signs or deaths occurred during the study. Parental body weight, body weight gain and food consumption were unaffected by treatment.


 


No statistically significant differences in mean corpora lutea, implantation sites, litter size, total pups born or pups born alive on postnatal days 0 were detected among the groups. Pup survival was unaffected by treatment on postnatal day 0 and 4. Offspring body weight and growth were similar across all groups and unaffected by treatment.


 


Parental reproductive organ weights (ovaries, testes or epididymides) failed to reveal any treatment-related effect. Male liver weights and liver-to-body weight ratios were increased in a dose-related manner; however, statistical significance was not achieved. No evidence of histological changes was observed in the ovaries, testes or epididymides.


 


Based on these findings, the no-observed-adverse-effect level (NOAEL) for systemic and reproductive toxicity is equal to or greater than the highest dose tested 750 mg/kg bw/day.

Effect on fertility: via oral route
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
750 mg/kg bw/day
Study duration:
subacute
Species:
rat
Quality of whole database:
The key study is GLP-compliant and of high quality (Klimisch score = 1).
Effect on fertility: via inhalation route
Endpoint conclusion:
no study available
Effect on fertility: via dermal route
Endpoint conclusion:
no study available
Additional information

Test Item was formulated in deionized water (vehicle) and was administered as a solution by oral gavage at dose levels of 0 (vehicle control), 50, 250 or 750 mg/kg bw/day to 12 Sprague­ Dawley rats/sex/group for the assessment of reproductive and developmental toxicity in a study similar to OECD TG 421. Doses were administered at a constant volume of 5 mL/kg bw for 2 weeks prior to mating, during the approximately 1-week mating period, through gestation and lactation until sacrifice, for a total of 5 weeks of dosing for males and approximately 7 weeks for females. Parental food consumption, body weights, body weight gain, reproductive performance, organ weights and histopathology were evaluated during the study, along with offspring body weight and survival.


 


No treatment-related clinical signs or deaths occurred during the study. Parental body weight, body weight gain and food consumption were unaffected by treatment.


 


No statistically significant differences in mean corpora lutea, implantation sites, litter size, total pups born or pups born alive on postnatal days 0 were detected among the groups. Pup survival was unaffected by treatment on postnatal day 0 and 4. Offspring body weight and growth were similar across all groups and unaffected by treatment.


 


Parental reproductive organ weights (ovaries, testes or epididymides) failed to reveal any treatment-related effect. Male liver weights and liver-to-body weight ratios were increased in a dose-related manner; however, statistical significance was not achieved. No evidence of histological changes was observed in the ovaries, testes or epididymides.


 


Based on these findings, the no-observed-adverse-effect level (NOAEL) for systemic and reproductive toxicity is equal to or greater than the highest dose tested 750 mg/kg bw/day.

Effects on developmental toxicity

Effect on developmental toxicity: via oral route
Endpoint conclusion:
no study available
Effect on developmental toxicity: via inhalation route
Endpoint conclusion:
no study available
Effect on developmental toxicity: via dermal route
Endpoint conclusion:
no study available

Justification for classification or non-classification

Harmonised classification:


The substance has no harmonised classification for toxicity to reproduction according to the Regulation (EC) No. 1272/2008 (CLP). 


 


Self-classification:


Based on the available information, no self-classification is proposed according to the CLP or GHS.

Additional information