Molybdenum, bis(N,N-dibutylcarbamodithioato-κS,κS')dioxodi-μ-thioxodi-, stereoisomer

Endpoint summary

Key value for chemical safety assessment

Effects on fertility

Link to relevant study records

Reference

Endpoint:

screening for reproductive / developmental toxicity

Type of information:

experimental study

Adequacy of study:

key study

Reliability:

1 (reliable without restriction)

Rationale for reliability incl. deficiencies:

guideline study

Reason / purpose for cross-reference:

reference to same study

Qualifier:

according to guideline

Guideline:

OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)

Version / remarks:

2016

Deviations:

yes

Remarks:

all were minor deviations not having an effect on study outcome

GLP compliance:

yes

Species:

rat

Strain:

Wistar

Sex:

male/female

Details on test animals or test system and environmental conditions:

TEST ANIMALS
- Source: Charles River Deutschland, Germany
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 10-12 weeks (males), 11-14 weeks (females)
- Weight at study initiation: 265-372 g (males), 194-238 g (females)
- Fasting period before study: no
- Housing: group housing up to 5 animals of the same sex and dosing group
; mated females were housed individually
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 6 days prior to start of dosing

DETAILS OF FOOD AND WATER QUALITY: pelleted rodent diet (SM R/M-Z from SNIFF Spezialdiäten GmbH, Germany), drinking water

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-22
- Humidity (%): 43-67
- Air changes (per hr): 10
- Photoperiod (hrs dark / hrs light):
12/12

Route of administration:

oral: gavage

Vehicle:

propylene glycol

Details on exposure:

PREPARATION OF DOSING SOLUTIONS:

DIET PREPARATION
- Rate of preparation of diet (frequency):
- Mixing appropriate amounts with (Type of food):
- Storage temperature of food:

VEHICLE
- Justification for use and choice of vehicle (if other than water): suitable vehicle
- Concentration in vehicle: 20, 60, 200 mg/ml
- Amount of vehicle (if gavage): 5 mg/kg body weight
- Lot/batch no. (if required):
- Purity:

Details on mating procedure:

- M/F ratio per cage: 1/1
- Length of cohabitation: max. 14 days
- Proof of pregnancy: vaginal plug / sperm in vaginal smear referred to as day 0 of pregnancy
- After ... days of unsuccessful pairing replacement of first male by another male with proven fertility. not applicable
- Further matings after two unsuccessful attempts: [no / yes (explain)]
- After successful mating each pregnant female was caged (how): indivually
- Any other deviations from standard protocol:

Analytical verification of doses or concentrations:

yes

Details on analytical verification of doses or concentrations:

the concentrations of the test substance analysed in the formulations by HPLC/UV were in agreement with target concentrations and were homogeneous.

Duration of treatment / exposure:

Males were dosed for 29 days. Females that delivered offspring were dosed for 50-62 days.

Frequency of treatment:

once daily

Dose / conc.:

100 mg/kg bw/day (actual dose received)

Dose / conc.:

300 mg/kg bw/day (actual dose received)

Dose / conc.:

1 000 mg/kg bw/day (actual dose received)

No. of animals per sex per dose:

10

Control animals:

yes, concurrent vehicle

Details on study design:

- Dose selection rationale: based on results of a dose range finding study
- Rationale for animal assignment (if not random): random
- Fasting period before blood sampling for clinical biochemistry: yes (overnight)
- Other: animals of satelite groups for a post-exposure recovery period were not mated

Positive control:

no

Parental animals: Observations and examinations:

CAGE SIDE OBSERVATIONS: Yes
- Time schedule:twice daily
- Cage side observations checked in table [No.?] were included.

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: once weekly

BODY WEIGHT: Yes
- Time schedule for examinations:
Animals were weighed individually on the first day of treatment (prior to dosing), and weekly thereafter. Mated females were weighed on Days 0, 4, 7, 11, 14, 17, and 20 post-coitum and during lactation on PND 1, 4, 7, and 13.

FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / Not specified

FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No

WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes / No / Not specified
- Time schedule for examinations:

Oestrous cyclicity (parental animals):

Estrous cycles were evaluated by examining the vaginal cytology of samples obtained by vaginal lavage.
Daily vaginal lavage was performed for all females (Main and Recovery) during 14 days prior to treatment (pretest period) and the first 14 days of treatment. For Main females, daily vaginal lavage was continued during mating until evidence of copulation was observed.

Sperm parameters (parental animals):

For the testes of all selected Main males of Groups 1 and 4 a detailed qualitative examination was made, taking into account the tubular stages of the spermatogenic cycle.

Litter observations:

STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: yes
- If yes, maximum of 8 pups/litter (4/sex/litter as nearly as possible); excess pups were used for blood sampling, killed and discarded.

PARAMETERS EXAMINED
The following parameters were examined in F1 offspring:
number and sex of pups, stillbirths, live births, postnatal mortality, presence of gross anomalies, weight gain, physical or behavioural abnormalities, anogenital distance (AGD), pup weight on the day of AGD, presence of nipples/areolae in male pups,

GROSS EXAMINATION OF DEAD PUPS: no

ASSESSMENT OF DEVELOPMENTAL NEUROTOXICITY: no

ASSESSMENT OF DEVELOPMENTAL IMMUNOTOXICITY: no

Postmortem examinations (parental animals):

SACRIFICE
- Male animals: All surviving animals after 28 days of dosing

- Maternal animals: All surviving animals on PND 14-16

GROSS NECROPSY
- Gross necropsy consisted of external and internal examinations including the cervical, thoracic, and abdominal viscera.

HISTOPATHOLOGY / ORGAN WEIGHTS
The tissues indicated in Table [#] were prepared for microscopic examination and weighed, respectively.

Postmortem examinations (offspring):

SACRIFICE
- The F1 offspring was sacrificed on PND 14-16
- These animals were subjected to postmortem examinations (macroscopic examination) as follows:
On PND 4, the surplus pups (> 8 pups per litter) were euthanized by decapitation. From two surplus pups per litter, blood was collected, if possible. All remaining pups were euthanized on PND 14-16. Sex was determined both externally and internally. Descriptions of all external abnormalities were recorded. Particular attention was paid to the external reproductive genitals to examine signs of altered development.
In addition, blood was collected from two pups per litter, and the thyroid from two pups per litter (one male and one female pup) was preserved in 10% buffered formalin. The pups selected for blood sampling were the same pups as selected for thyroid preservation.

GROSS NECROPSY
- Gross necropsy consisted of external examinations

HISTOPATHOLOGY / ORGAN WEIGTHS: not performed

Statistics:

All statistical tests were conducted at the 5% significance level. All pairwise comparisons were conducted using two sided tests and were reported at the 1% or 5% levels.
Numerical data collected on scheduled occasions for the listed variables were analyzed as indicated according to sex and occasion. Descriptive statistics number, mean and standard deviation (or %CV or SE when deemed appropriate) were reported whenever possible.
Parametric: Datasets with at least 3 groups (the designated control group and 2 other groups) were compared using Dunnett-test (many-to-one-t-test).
Non-Parametric: Datasets with at least 3 groups was compared using a Steel-test (many-to-one rank test). The motor activity data set was compared using an overall Kruskal-Wallis.
Incidence: An overall Fisher’s exact test was used to compare all groups at the 5% significance level. The above pairwise comparisons were conducted using Fisher’s exact test whenever the overall test is significant

Reproductive indices:

see Table on reproduction data attached as background material

Offspring viability indices:

see Table on reproduction and viability attached as background material

Clinical signs:

effects observed, treatment-related

Description (incidence and severity):

All males and females at 300 and 1000 mg/kg showed pale faeces starting at Treatment Day 27. In 1000 mg/kg males, the faeces appeared normal from Day 26 of the recovery period onwards. In 1000 mg/kg females, faeces were normal from Day 5 of the recovery period.

Mortality:

no mortality observed

Body weight and weight changes:

no effects observed

Description (incidence and severity):

see respective Table in endpoint study record of repeated dose toxicity study attached as background material

Food consumption and compound intake (if feeding study):

no effects observed

Description (incidence and severity):

see respective Table in endpoint study record of repeated dose toxicity study attached as background material

Food efficiency:

not examined

Water consumption and compound intake (if drinking water study):

no effects observed

Ophthalmological findings:

not examined

Haematological findings:

effects observed, non-treatment-related

Description (incidence and severity):

see respective Table in endpoint study record of repeated dose toxicity study attached as background material

Clinical biochemistry findings:

effects observed, non-treatment-related

Description (incidence and severity):

see respective Table in endpoint study record of repeated dose toxicity study attached as background material

Urinalysis findings:

not examined

Behaviour (functional findings):

no effects observed

Immunological findings:

not examined

Organ weight findings including organ / body weight ratios:

no effects observed

Histopathological findings: non-neoplastic:

effects observed, non-treatment-related

Description (incidence and severity):

Any finding was within normal background values.

Histopathological findings: neoplastic:

not examined

Other effects:

no effects observed

Reproductive function: oestrous cycle:

no effects observed

Description (incidence and severity):

see Table on estrous cycles attached as background material

Reproductive function: sperm measures:

no effects observed

Reproductive performance:

no effects observed

Description (incidence and severity):

see Tables on reproduction data attached as background material

Key result

Dose descriptor:

NOAEL

Effect level:

>= 1 000 mg/kg bw/day (actual dose received)

Based on:

test mat.

Sex:

male/female

Remarks on result:

other: no effects at highest dose tested

Key result

Dose descriptor:

NOAEL

Remarks:

for reproductive function

Effect level:

>= 1 000 mg/kg bw/day (actual dose received)

Based on:

test mat.

Sex:

male/female

Remarks on result:

other: no effects at highest dose tested

Key result

Critical effects observed:

no

Clinical signs:

no effects observed

Mortality / viability:

mortality observed, non-treatment-related

Description (incidence and severity):

Viability index (number of live offspring on PND 4 before culling as percentage of number of live offspring on PND 1) was considered not to be affected by treatment. Viability indices were 98, 95, 97 and 96% for the control, 100, 300, and 1000 mg/kg groups, respectively. Two pups of the control group, five pups at 100 mg/kg, four pups at 300 mg/kg, and four pups at 1000 mg/kg were found dead or missing (most likely cannibalised) on PND 2, 3 or 4. This post-natal loss was regarded as unrelated to treatment due to the incidental occurrence (within the range considered normal for pups of this age).

Body weight and weight changes:

no effects observed

Description (incidence and severity):

see Table on body weights of pups attached as background material

Food consumption and compound intake (if feeding study):

not examined

Description (incidence and severity):

pups were killed on PND 14-16

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:

no effects observed

Description (incidence and severity):

Serum levels of T4 in PND 14-16 pups were considered not to be affected by treatment.

see Table on T4 levels of PND 14-16 pups attached as background material

Urinalysis findings:

not examined

Sexual maturation:

not examined

Anogenital distance (AGD):

no effects observed

Description (incidence and severity):

see Table on anogenital distance and nipple retention of pups attached as background material

Nipple retention in male pups:

no effects observed

Description (incidence and severity):

see Table on anogenital distance and nipple retention of pups attached as background material

Organ weight findings including organ / body weight ratios:

not examined

Gross pathological findings:

no effects observed

Histopathological findings:

not examined

Other effects:

no effects observed

Behaviour (functional findings):

not examined

Developmental immunotoxicity:

not examined

Key result

Dose descriptor:

NOAEL

Generation:

F1

Effect level:

>= 1 000 mg/kg bw/day (actual dose received)

Based on:

test mat.

Remarks:

dams were dosed

Sex:

male/female

Remarks on result:

other: no effects at highest dose tested

Key result

Critical effects observed:

no

Key result

Reproductive effects observed:

no

Conclusions:

Up to and including the highest dose level of 1000 mg/kg body weight/d no effects on reproductive function and on development of offspring until PND 14-16 were observed.

Effect on fertility: via oral route

Endpoint conclusion:

no adverse effect observed

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

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

No effects on reproductive function and on development of offspring until PND 14-16 was observed at the highest dose level. Accordingly, no classification for toxicity to reproduction is necessary according to Regulation 1272/2008.