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Administrative data

Key value for chemical safety assessment

Effects on fertility

Description of key information

In a key, K1 combined repeated dose toxicity study with the reproduction/developmental toxicity screening test, the test substance was administered daily to rats at dose levels up to 150 mg/kg bodyweight/day (OECD guideline 422; Betancourt 2014). The NOAEL was considered to be 10 mg/kg bw/day for systemic toxicity in both males and females. The NOEL for embryo-fetal toxicity was considered to be 75 mg/kg body weight/day.

Link to relevant study records
Reference
Endpoint:
screening for reproductive / developmental toxicity
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2012-07-19 - 2012-09-12
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study with acceptable restrictions
Remarks:
Dose formulations were not analyzed.
Qualifier:
according to guideline
Guideline:
OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Limit test:
no
Specific details on test material used for the study:
- Name of test material (as cited in study report): Jeffamine RFD-270 Amine
- Substance type: Colourless liquid
- Physical state: Liquid
- Lot/batch No.: 8802-8-9
- Analytical purity: 92%
- Composition of test material, percentage of components: 0.02 wt% water
- Purity test date: 2010-07-15
- Storage condition of test material: Sample stored in cool, well-ventilated storage area prior to testing
Species:
rat
Strain:
other: Wistar Hannover
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: BIOAGRI Laboratorios
- Age at study initiation: 11-12 weeks
- Weight at study initiation: 304-446 g (males) ; 179 to 267 g (females)
- Fasting period before study: not applicable
- Housing: Each animal was housed individually, except during cohabitation. After acclimation, one male was placed into females cages for pairing (up to 2 females:1 male). After pairing, females that presented vaginal smears with the presence of sperm were considered mated and housed individually. The rats were housed in polypropylene cages (41x34x19 cm) with wire mesh tops and bedding material (wood shavings). Clean cages were provided twice a week for all animals. The cages with the test animals were arranged on the racks in such a way that uniform experimental conditions (ventilation and light) were ensured.
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: A larger number of animals than necessary were ordered in order to permit the selection and/or replacement of individual animals before the start of treatment. Accordingly, a total of 70 males and 70 females were received for acclimation and were 10-11 weeks of age. Upon receipt from the supplier, animals were placed into cages (1 animal/cage/sex) examined and acclimated for 8 days. All animals were observed daily for morbidity and mortality and the estrous cycle was checked. At the end of this period, the animals were weighed and a detailed clinical examination was performed. Animals showing abnormal signs or irregular estrous cycle were not used in the study. Only animals with weights within ± 20 % from mean body weight were used in this study.

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19.2 - 24.5 °C
- Humidity (%): 40.5-69.9 %
- Air changes (per hr): 10-20
- Photoperiod (hrs dark / hrs light): 12h/12h
Route of administration:
oral: gavage
Vehicle:
water
Remarks:
deionized water
Details on exposure:
PREPARATION OF DOSING SOLUTIONS: For each dosage group, the appropriate amount of Jeffamine RFD 270 was weighed into a pre-calibrated beaker. The vehicle (deionized water) was added in sufficient quantity to achieve the desired concentration. Each solution was stirred and dispensed into individual containers properly identitified. A sufficient quantity of the vehicle was similarly dispensed for administration to control animals. The prepared solutions were stored at room temperature.
Test solutions were prepared daily at the testing facility and were administered within 2 hours after preparation. The test solutions were stirred continuously during the administration to maintain the homogeneity.

The volume administered each day was 4 mL/kg body weight.
Details on mating procedure:
Premating:
At the end of the acclimation period, animals were randomly assigned to the experimental groups, housed and the treatment started.

Mating:
After a premating period of 2 weeks, females were cohabited with an assigned male (1male: up to 2 females) from the same dose level until evidence of copulation was observed. Care was taken to avoid sibling mating. Vaginal smears were collected daily during mating period and examined for the presence of sperm. Day 0 of gestation was defined as the day a sperm is found in the vaginal smear. Males were euthanized after completing a dosing period of 39 days.

Gestation:
During gestation period all females were housed individually in the cages.

Lactation:
The day when delivery is completed was designated day 0 of lactation (postnatal day 0). On day 0 of lactation the number of alive and dead pups/sex were recorded. Dams with offspring were euthanized on day 4 postnatal. All pups were euthanized at day 4 postnatal.
Analytical verification of doses or concentrations:
no
Duration of treatment / exposure:
Parental animals (males and females) were treated, starting at 11-12 weeks old and ending when the animals were euthanized. Satellite animals (5 animals per sex of the control and 5 animals per sex of the high dose group) were kept for 14 days after the scheduled necropsy of parental animals without treatment, for observation of reversibility, persistence or delayed occurence of toxic effects. Satellite animals were not mated and, consequently, were not used for assessment of reproduction/developmental toxicity.

Frequency of treatment:
7-day per-week-basis
Dose / conc.:
0 mg/kg bw/day (nominal)
Remarks:
Group 1 (control)
Dose / conc.:
10 mg/kg bw/day (nominal)
Remarks:
Group 2
Dose / conc.:
75 mg/kg bw/day (nominal)
Remarks:
Group 3
Dose / conc.:
150 mg/kg bw/day (nominal)
Remarks:
Group 4
No. of animals per sex per dose:
12 animals in the main study
5 animals per sex of the control group and 5 animals per sex of the high dose group for the satellite groups
Control animals:
yes, concurrent vehicle
Details on study design:
- Dose selection rationale: The dosage levels were selected in agreement with the sponsor.
10 mg/kg bw/day as the expected dose which causes no signs;
75 mg/kg bw/day as the intermediate dose level;
150 mg/kg bw/day as the expected dose which causes signs of systemic toxicity, but no death or severe suffering.
Parental animals: Observations and examinations:
CAGE SIDE OBSERVATIONS/DETAILED CLINICAL OBSERVATIONS: Yes
All animals underwent a daily clinical observation for overt signs of ill health. These include, but are not limited to, changes in skin and fur, eye and mucous membranes, respiratory, circulatory, autonomic and central nervous system, motor activity and behavioural patterns.

BODY WEIGHT: Yes
Males were weighed on the first day of dosing and weekly thereafter (including mating and post-mating periods). Females were weighed on first day of dosing and once a week during premating and mating periods, on days 0, 7, 14 and 20 of gestation, and during lactation on the same days as the weighing of litters (on days 0 and 4 post natal).

FOOD CONSUMPTION :
Food consumption was determined on the same day of body weight determination during premating and lactation periods, except on day 0. During gestation period, food consumption was determined on days 3, 6, 9, 12, 15, 18 and 20. After mating period, food consumption of males was determined weekly. Food consumption was not determined during the mating period.

OTHER:
Organ weights: At scheduled necropsy, testes and epididymides of all males were weighed.
Organ weights were obtained for the following organs from 5 animals/sex/group: liver, kidneys, adrenals, thymus, spleen, brain, heart
Sperm parameters (parental animals):
testis weight, epididymides weight
Litter observations:
Live pups were counted, sexed and weighed on days 0 and 4 postnatal.

Postmortem examinations (parental animals):
GROSS PATHOLOGY: Yes
At termination, all parental animals were examined macroscopically for any abnormalities or pathological changes. The animals were euthanized in a carbon dioxide chamber. The number of implantation sites and corpora lutea were recorded. The animals were disposed in biological garbage and then incinerated. Animals found dead or euthanized moribund during the study were evaluated by gross examination as soon as possible after death. All pups were grossly examined for abnormalities of the oral, thoracic and abdominal cavities.

HISTOPATHOLOGY: Yes
At the scheduled necropsy, the following organs of all animals were preserved:
testes, epididymides, ovaries, prostate, semincal vesicle and coagulating gland, bulbourethral gland, organs showing alterations

The following organs and tissues of 5 animals/sex/group were preserved:
adrenals (right and left), bone marrow (femur), brain (cerebrum, cerebellum and pons), esophagus, heart, intestine (duodenum, jejunum, ileum - including Peyer's patches, cecum, colon, rectum/anus), kidneys (right and left), liver (3 lobes), lungs, lymph nodes (mesenteric and submaxillary), peripheral nerve (sciatic), salivary gland, spinal cord (cervical, midthoracic and lumbar sections), spleen, stomach (glandular and non-glandular), trachea, thymus, thyroid/parathyroid, urinary bladder, uterus, all gross lesions

Full histopathology of the preserved organs and tissues listed above were performed in highest dose and control animals. TThe examination of the lung, liver, brain and kidneys was extended to animals of other dosage groups.
Postmortem examinations (offspring):
SACRIFICE
All pups were euthanized at day 4 postnatal

GROSS NECROPSY
All pups were grossly examined for abnormalities of the oral, thoracic and abdominal cavities.
Statistics:
Quantitative variables such as body weights, food consumption and organ weights were analyzed by One Way Analysis of Variance (ANOVA), followed by Dunnett's test if significance is detected, or by the non-parametric test of Kruskal-Willis, according to the results of tests for normaility and homogeneity of variance. For qualitative or non-parametric data such as clinical findings, macroscopic and microscopic findings and fetal findings, comparison between means were carried out using Fisher's Exact Test or the Chi-Square Test. The level of significance was set at 5%.
Reproductive indices:
The precentage of pre-implantation loss, post-implantation loss, mating index, fertility index, gestation index on day 4 post-partum were calculated (for each pregnant animal) according to the following:
% Pre-implantation loss = (Number of corpora lutea - Number of implantation sites x 100)/Number of corpora lutea
% Post-implantation loss = (Number of implantations - Number of live fetuses x 100)/Number of implantations
% Mating index = (Number of females mated x 100)/Number of females paired
% Fertility index = (Number of females pregnant x 100)/Number of mated pairs
% Gestation index = (Number of females with live pups at birth x 100)/Number of females pregnant
Offspring viability indices:
The percentage of live birth index and viability index on day 4 post-partum were calculated (for each pregnant animal) according to the following:
% Live birth index = (Number of live born pups x 100)/Number of delivered pups
% Viability index on day 4 post-partum = (Number of surviving pups on day 4 post-partum x 100)/Number of live born pups
Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
Most of male and female rats exposed to 150 mg/kg bw/day presented piloerection, apathy, respiratory sounds, dyspnea and rinocromodacryorrhea periodically from day 8 to day 44 of the test item administration. Males No 86, 93 and 108 at 150 mg/kg bw/day were found dead on days 12, 19 and 19 of treatment, respectively; while males rats No 84, 88, 89, 90 and 109 were sacrificed by animal welfare on days 12 and 13, after severe episodes of limited mobility and prostration. Females N° 96, 99, 101, 104, 105 and 115, at the same dose level were found dead on days 38, 12, 17, 25, 41 and 28 of treatment, respectively. These effects were dose related and could be attributed to treatment with the test item.
Dermal irritation (if dermal study):
not examined
Mortality:
mortality observed, treatment-related
Description (incidence):
Most of male and female rats exposed to 150 mg/kg bw/day presented piloerection, apathy, respiratory sounds, dyspnea and rinocromodacryorrhea periodically from day 8 to day 44 of the test item administration. Males No 86, 93 and 108 at 150 mg/kg bw/day were found dead on days 12, 19 and 19 of treatment, respectively; while males rats No 84, 88, 89, 90 and 109 were sacrificed by animal welfare on days 12 and 13, after severe episodes of limited mobility and prostration. Females N° 96, 99, 101, 104, 105 and 115, at the same dose level were found dead on days 38, 12, 17, 25, 41 and 28 of treatment, respectively. These effects were dose related and could be attributed to treatment with the test item.
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
Marked effects (decreases) on body weight, body weight gain and food consumption were observed in males and females in the high dose groups and in the high dose satellite male and female groups (150 mg/kg/day). Furthermore, even during the recovery period, a clear recovery in body weights was not observed in the satellite animals. Accordingly, changes observed in body weight, body weight gain and food consumption of males and females at 150 mg/kg/day, were considered to be treatment-related with toxicological difference.
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
Marked effects (decreases) on body weight, body weight gain and food consumption were observed in males and females in the high dose groups and in the high dose satellite male and female groups (150 mg/kg/day). Furthermore, even during the recovery period, a clear recovery in body weights was not observed in the satellite animals. Accordingly, changes observed in body weight, body weight gain and food consumption of males and females at 150 mg/kg/day, were considered to be treatment-related with toxicological difference.
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
not examined
Haematological findings:
effects observed, non-treatment-related
Description (incidence and severity):
Some changes in mean red blood cell count and mean corpuscular hemoglobin concentration, or mean platelets were statistically significant when compared to the control groups (males or females, different concentrations). However, these changes were not considered to be test item related because they were isolated findings or normal biological variations.
Clinical biochemistry findings:
effects observed, treatment-related
Description (incidence and severity):
Markedly higher mean aspartate aminotransferase levels were observed in male and females rats exposed to 75 and 150 mg/kg bw/day. No other alterations were found in the hemogram, leukogram and clotting parameters. However, these chemistry effects in the mid and high dose males and females, while not statistically significant, were observed in treated satellite males and females. Furthermore, these findings were supported by other observations from macroscopic and microscopic pathology examinations and are considered to be biologically relevant. Moreover, male rats at high dose level had a decrease in cholesterol levels, which were outside the historical control range and are considered to be dose related. Also this finding was observed in treated satellite males, confirming it as a treatment related effect.
Urinalysis findings:
not examined
Behaviour (functional findings):
effects observed, treatment-related
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Mild congestion in brain, liver, lung and kidney were the most common histopathological findings in both male and female rats exposed to 150 mg/kg bw/day, being statistically significant to the control group. These effects were dose related and should be considered treatment related.
Histopathological findings: neoplastic:
not examined
Other effects:
not specified
Reproductive function: oestrous cycle:
not examined
Reproductive function: sperm measures:
not examined
Reproductive performance:
effects observed, treatment-related
Description (incidence and severity):
Decreases in mating and fertility indices were observed in females at the high dose group. In addition, the high dose dams had a reduction in the number of corpora lutea implantations and the number of total pups at postnatal days 0 and 4. Also, the live birth index and viability index on day 4 were moderately lower than control and considered to be treatment related with toxicological relevance.
Key result
Dose descriptor:
NOAEL
Remarks:
systemic toxicity
Effect level:
10 mg/kg bw/day
Based on:
test mat.
Sex:
male/female
Basis for effect level:
mortality
body weight and weight gain
clinical biochemistry
gross pathology
histopathology: non-neoplastic
Key result
Critical effects observed:
no
Clinical signs:
no effects observed
Dermal irritation (if dermal study):
not examined
Mortality / viability:
mortality observed, treatment-related
Description (incidence and severity):
Markedly higher mortality occurred in pups from dams exposed to 150 mg/kg/day at postnatal day 0 (33.9%) and day 4 (16.2%), being statistically significant when compared to the control group. This effect was considered to be related to the treatment with the test item. No other signs or mortality treatment related were observed in the other dose levels.
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
Statistically significant lower body weight was observed in pups from dams exposed to 150 mg/kg bw/day compared to the control group on postnatal day 4 (-20%). Mean body weight on postnatal day 0, although without statistical significance, was moderately lower than control (-16.4%). These differences were dose related and therefore considered to treatment related.
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
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:
effects observed, treatment-related
Description (incidence and severity):
Body trauma (67.7%), cyanosis (41.9%) and cannibalized pups (12.9%) were findings statistically higher at the highest dose level and dose-related. These effects were associated with maternal toxicity observed at this highest dose and should be attributed to treatment with the test item.
Histopathological findings:
not examined
Other effects:
not specified
Behaviour (functional findings):
not examined
Developmental immunotoxicity:
not examined
Key result
Dose descriptor:
NOAEL
Remarks:
reproductive toxicity
Generation:
F1
Effect level:
75 mg/kg bw/day
Based on:
test mat.
Sex:
male/female
Basis for effect level:
viability
Key result
Dose descriptor:
NOAEL
Remarks:
developmental toxicity
Generation:
F1
Effect level:
75 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
viability
body weight and weight gain
gross pathology
Key result
Critical effects observed:
no
Key result
Reproductive effects observed:
yes
Lowest effective dose / conc.:
150 mg/kg bw/day (nominal)
Treatment related:
yes
Relation to other toxic effects:
not specified
Dose response relationship:
yes
Relevant for humans:
not specified
Conclusions:
Under the experimental conditions of this study, the NOAEL of the test substance in Wistar rats was 10 mg/kg/day for male systemic toxicity and maternal systemic toxicity, and 75 mg/kg bw/day for embryo-fetal toxicity.
Effect on fertility: via oral route
Endpoint conclusion:
adverse effect observed
Dose descriptor:
NOAEL
75 mg/kg bw/day
Study duration:
subacute
Species:
rat
Effect on fertility: via inhalation route
Endpoint conclusion:
no study available
Effect on fertility: via dermal route
Endpoint conclusion:
no study available
Additional information

A combined repeated dose toxicity study with the reproduction/developmental toxicity screening test is performed in rats, in which male and female rats are exposed to 0 (vehicle), 10, 75 and 150 mg/kg bw/day via gavage (OECD 422).

The test substance caused clinical signs of toxicity from day 8 to 44 of the test item administration; in addition, a marked total mortality of 50% in males and 50% in females occurred in the high dose group (150 mg/kg bw/day) during the study. These effects were dose related and therefore, attributed to treatment with the test item.

Decreases on body weight, body weight gain and food consumption were observed in males and females in the high dose group and in the high dose satellite male and female groups (150 mg/kg bw/day). Furthermore, even during the recovery period, a complete recovery in the bodyweights was not observed in the satellite animals. Accordingly, changes observed in body weight, body weight gain and food consumption of males and females at 150 mg/kg bw/day were considered to be treatment-related with toxicological significance.

Other than the cage side observations noted, there were no test article effects on reaction to stimuli and motor activity assessment in the functional observational battery study.

Markedly higher mean aspartate aminotransferase levels were observed in male and female rats exposed to 75 and 150 mg/kg bw/day. These findings were supported by other macroscopic and microscopic pathology findings and were considered to be treatment related. No other alterations were found in the hemogram, leukogram and clotting parameters. However, these chemistry effects in the mid and high dose males and females, while not statistically significant, were observed in treated satellite males and females. Furthermore, these findings are considered to be treatment related at the high dose level males and females and satellite males and females. Moreover, male rats at the high dose level and the satellite male groups had decreased cholesterol levels which fell outside of the Bioagri historical control value range. This finding was considered to be a treatment related effect.

The mean number of days of pairing before mating and the length of the gestation period were comparable between the control group and treated groups and within the physiological range of this species and strain, according Bioagri’s historical data base. For the control group, 2/12 females were not pregnant, compared to 0/12, 0/12 and 6/12 at 10, 75 and 150 mg/kg/day groups, respectively. The mating and fertility indices were similar in all groups, except in females at 150 mg/kg/day were they were lower than control (75% and 81.8%, respectively); though, the gestation index was not affected. No biologically or statistically significant changes were observed when the percentages of pre and post implantation loss were compared to the control group. However, the live birth index (-33.1%), viability index on day 4 (-15.4%), corpora lutea number (-26.1%), implantation number (-21.8%), number of total pups at day 0 (-21.8%) and postnatal day 4 (-47.5%) were lower in dams exposed to 150 mg/kg/day compared to the control group. Although all these findings were without statistical significance, they should be considered test item related, because were markedly higher and occurred at the high dose level.

In pups from dams at the high dose level, markedly higher mortality occurred at postnatal days 0 and 4. Furthermore, decreases in body weight were noted with related macroscopic findings such as body trauma, cyanosis and cannibalized pups. These effects were associated with maternal toxicity observed at this highest dose and should be attributed to treatment with the test item.

Accordingly, in the experimental conditions of this study, the NOAEL of the test item in Wistar rats was 10 mg/kg/day for male systemic toxicity and maternal systemic toxicity, and 75 mg/kg/day for embryo-fetal toxicity.

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

The results of the combined repeated dose toxicity study with the reproduction/developmental toxicity screening test

showed adverse effects in the embryo/foetus associated with strong evidence of maternal toxicity, that may influence development via non-specific secondary mechanisms. As the adverse effects on fertility and reproductive performance were only seen at levels causing marked systemic toxicity, it is considered that the pup findings are secondary to maternal toxicity and the substance should not be classified for reproductive toxicity according to the CLP Regulation.

Additional information