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EC number: 948-019-1 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Toxicity to reproduction
Administrative data
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 16 January 2017 to 06 September 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- 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
Test material
- Reference substance name:
- Bis(C11-14-branched and linear alkyl)dithiocarbamic acid
- Molecular formula:
- N/A
- IUPAC Name:
- Bis(C11-14-branched and linear alkyl)dithiocarbamic acid
- Reference substance name:
- Molybdenum, bis(C11-14 branched and linear alkyl)carbamodithioato-.kappa.S,.kappa.S')oxodi-thioxothioxodi-
- Molecular formula:
- N/A
- IUPAC Name:
- Molybdenum, bis(C11-14 branched and linear alkyl)carbamodithioato-.kappa.S,.kappa.S')oxodi-thioxothioxodi-
- Reference substance name:
- Molybdenum, bis(C11-14 branched and linear alkyl)carbamodithioato-.kappa.S,.kappa.S')dioxodi-thioxodi-
- Molecular formula:
- N/A
- IUPAC Name:
- Molybdenum, bis(C11-14 branched and linear alkyl)carbamodithioato-.kappa.S,.kappa.S')dioxodi-thioxodi-
- Reference substance name:
- Molybdenum, bis(N,N-di-C11-14 branched and linear alkyl)carbamodithioato-.kappa.S,.kappa.S')-oxodioxo-thioxodi-
- Molecular formula:
- N/A
- IUPAC Name:
- Molybdenum, bis(N,N-di-C11-14 branched and linear alkyl)carbamodithioato-.kappa.S,.kappa.S')-oxodioxo-thioxodi-
- Test material form:
- liquid
Constituent 1
Constituent 2
Constituent 3
Constituent 4
- Specific details on test material used for the study:
- - Purity: >90%
- Description: Brown viscous liquid
Test animals
- Species:
- rat
- Strain:
- other: Crl:CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Housing
Animals were housed in a limited access room in cages comprised of a polycarbonate body with a stainless steel mesh lid. Solid polycarbonate bottom cages were used during the acclimatization, pre-pairing, treatment, gestation, littering and lactation periods. Solid bottom cages contained softwood based bark-free fibre bedding, which was changed at appropriate intervals each week. Grid bottomed polypropylene cages that were suspended above absorbent paper, which was changed daily, were used during pairing. The cages were distributed on the racking to equalize, as far as possible, environmental influences amongst the groups.
Temperature and relative humidity were monitored and maintained within the range of 20-24ºC and 40-70%. The air supply was filtered fresh air, which was not recirculated. Artificial lighting was set to provide 12 hours light and 12 hours dark.
Number of animals per cage
Pre-pairing up to five animals of one sex
Pairing one male and one female
Males after mating up to five animals
Gestation one female
Lactation one female + litter
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- arachis oil
- Details on exposure:
- The Crl:CD(SD) rat strain was used because it is recognized by regulatory agencies as an appropriate model for conditions of possible human exposure and because of the historical control data available at the testing laboratory. The oral gavage route of administration, using a suitably graduated syringe and a rubber catheter inserted via the mouth, at doses of 0, 100, 330 and 1000 mg/kg/day in arachis oil BP, with a dose volume of 5 ml/kg, was chosen based upon results of a 14-day dose range finding oral gavagel toxicity study in the Crl:CD(SD) rat in which there were no mortalities and few signs of toxicity at the high dose of 1000 mg/kg bw.
A series of formulations at the required concentrations were prepared by dilution of individual weighings of the test item. - Details on mating procedure:
- -Pairing commenced: After a minimum of two weeks of treatment.
- Male/female ratio: 1:1 from within the same treatment groups.
- Duration of pairing: Up to two weeks.
- Daily checks for evidence of mating: Ejected copulation plugs in cage tray and sperm in the vaginal smear.
- Day 0 of gestation: When positive evidence of mating was detected.
- Male/female separation: Day when mating evidence was detected.
- Pre-coital interval: Calculated for each female as the time between first pairing and evidence of mating. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The mean concentrations of the test item in dose test formulations analyzed for the study were within ±12% of nominal concentrations, confirming accuracy of the dose formulations.
- Duration of treatment / exposure:
- Males: Two weeks before pairing up to necropsy after minimum of five weeks.
Females: Two weeks before pairing, then throughout pairing and gestation until Day 13 of lactation. - Frequency of treatment:
- Once daily
- Details on study schedule:
- Three groups of ten male and ten female rats received the test item at doses of 100, 330 or 1000 mg/kg/day in arachis oil by oral gavage administration. Males were treated daily for two weeks before pairing, up to necropsy after a minimum of five consecutive weeks. Females were treated daily for two weeks before pairing, throughout pairing, gestation and until Day 13 of lactation. Females were allowed to litter, rear their offspring and were killed on Day 14 of
lactation. The F1 generation received no direct administration of the test item; any exposure was in utero or via the milk. A similarly constituted Control group received the vehicle, arachis oil, at the same volume dose as the treated groups.
During the study the following observations were made for the adult animals: clinical condition, detailed physical examination and arena observations, sensory reactivity observations, grip strength, motor activity, body weight, food consumption, haematology (peripheral blood), blood chemistry, serum thyroxine (T4) analysis, oestrous cycles, pre-coital interval, mating performance, fertility, gestation length, organ weight and macroscopic pathology and histopathology investigations were undertaken.
The clinical condition, litter size and survival, sex ratio, body weight, ano-genital distance and macropathology for all offspring were also recorded. The serum T4 analysis was performed for the Day 13 offspring. Nipple counts were performed on male offspring on Day 13 of age.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Dose / conc.:
- 330 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- The dose selection was based upon a range-finding study (please see RSS section 7.5.1 Supporting study, Envigo, 2018 (range-finding)).
Examinations
- Parental animals: Observations and examinations:
- Detailed observations were performed to establish and confirm a pattern of signs in association with dosing according to the following schedule:
F0 males Week 1 - daily
Week 2 onwards - once each week
F0 females Week 1 - daily
Week 2 - once
Gestation phase - Days 0, 7, 14 and 20
Lactation phase - Days 1, 6 and 12
Detailed observations were recorded at the following times in relation to dose administration:
Pre-dose observation
One to two hours after completion of dosing
As late as possible in the working day - Oestrous cyclicity (parental animals):
- Dry and wet smears were taken as follows:
- Dry smears: For 15 days before pairing using cotton swabs
- Wet smears: Using pipette lavage during the following phases:
> For 14 days before treatment (all females including spares); animals that failed to exhibit 4-5 day cycles were not allocated to study.
> After pairing until mating.
> For four days before scheduled termination (nominally Days 11 to 14 of lactation). - Sperm parameters (parental animals):
- For the assessment of the testes, a detailed qualitative examination was made, taking into account the tubular stages of the spermatogenic cycle. The examination was conducted in order to identify treatment related effects such as missing germ cell layers or types, retained spermatids, multinucleate or apoptotic germ cells and sloughing of spermatogenic cells in the lumen. Any cell- or stage-specificity of testicular findings was noted.
- Litter observations:
- - Clinical observations: Examined at approximately 24 hours after birth (Day 1 of age) and then daily thereafter for evidence of ill health or reaction to maternal treatment; these were on an individual offspring basis or for the litter as a whole, as appropriate.
- Litter size: Daily records were maintained of mortality and consequent changes in litter size from Days 1-13 of age.
- Sex ratio of each litter: Recorded on Days 1, 4, 7 and 13 of age.
- Individual offspring body weights: Days 1, 4, 7 and 13 of age.
- Ano-genital distance: Day 1 - all F1 offspring.
- Nipple/areolae count: Day 13 of age - male offspring. - Postmortem examinations (parental animals):
- Necropsy
- F0 males: After final investigations completed (after at least five weeks of treatment)
- F0 females failing to produce a viable litter: Day 25 after mating
- F0 females Day 14 of lactation (following terminal blood sampling)
Fixation
Tissues were routinely preserved in 10% Neutral Buffered Formalin with the exception of those detailed below:
- Testes: Initially in modified Davidson’s fluid.
- Eyes: In Davidson’s fluid.
Histology
- Processing: Tissue samples were dehydrated, embedded in paraffin wax and sectioned. For bilateral organs, sections of both organs were prepared. Sections were stained with hematoxylin and eosin; in addition samples of the testes were stained using a standard periodic acid/Schiff (PAS) method.
- Full List:
>All adult animals killed prematurely.
>At scheduled termination, the five lowest numbered surviving F0 males and females with a surviving litter in Groups 1 and 4.
- Abnormalities: All F0 animals.
Organ Weights
For bilateral organs, left and right organs were weighed together, unless specified.
Light Microscopy
Tissues preserved for examination were examined as follows:
- Premature deaths: F0 males and females from Groups 1 and 4 only.
- Scheduled kill: The first five F0 males and first five lactating F0 females in Groups 1 and 4 and All F0 animals from all groups. - Postmortem examinations (offspring):
- SACRIFICE
F1 offspring: Selected offspring for thyroid hormone analysis - Day 4 of age.
Scheduled Kill: Day 13 of age.
GROSS NECROPSY and HISTOPATHOLOGY
> Blood samples were collected as follows:
- Day 4 of age: F1 offspring, two females per litter
- Day 13 of age: F1 offspring, two males and two females per litter (where possible).
- All surviving F0 adult males and females (except the female which failed to litter) at termination. - Statistics:
- Statistical analyses were performed on the majority of data presented and results of these tests, whether significant or non-significant. For some parameters, including estrous cycles before treatment, stage of estrous cycle at termination and gestation index the similarity of the data was such that analyses were not considered to be necessary. Statistical analyses were carried out separately for males and females using the individual animal as the experimental unit for litter/foetal findings, the litter was taken as the treated unit.
- Reproductive indices:
- The following were calculated for each litter:
Post-implantation survival index (%) = (Total number of offspring born / Total number of uterine implantation sites) x 100
Post-implantation survival index was expressed as 100% where the number of offspring exceeded the number of implantation sites recorded.
Group mean values were calculated from individual litter values. - Offspring viability indices:
- The following were calculated for each litter:
Post-implantation survival index (%) = (Total number of offspring born / Total number of uterine implantation sites) x 100
Post-implantation survival index was expressed as 100% where the number of offspring exceeded the number of implantation sites recorded.
Live birth index (%) = (Number of live offspring on Day 1 after littering / Total number of offspring born) x 100
Viability index (%) = (Number of live offspring on Day 4 (before blood sampling) / Number live offspring on Day 1 after littering) x 100
Lactation index (%) = (Number of live offspring on Day 13 after littering / Number of live offspring on Day 4 (after blood sampling)) x 100
Group mean values were calculated from individual litter values.
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Description (incidence):
- One non-pregnant, non-litter producing female receiving 330 mg/kg/day was sacrificed on gestation day 25, as specified in the study plan.
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- effects observed, non-treatment-related
- Description (incidence and severity):
- For females treated at 1000 mg/kg/day, mean food consumption was slight high when compared with controls prior to pairing (Weeks 1-2) but these variations were marginal and considered incidental.
During gestation, food consumption was comparable to controls in females treated at 100, 330 or 1000 mg/kg/day.
During Days 4-7 and 7 -13 of lactation, mean food consumption was slightly high in females treated at 330 or 1000 mg/kg/day when compared with controls but these variations were marginal with no statistical significance and considered incidental. - 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):
- Hematological evaluation in males of the 330 or 1000 mg/kg/day groups revealed statistically significant decreases of mean prothrombin time (PT) and activated partial prothrombin time (APTT) compared to the concurrent control group.
In addition, for males of the 1000 mg/kg/day group, mean large unstained cells (LUC) and platelet counts were marginally higher than the concurrent control group. These differences were within the historical control data ranges and considered normal biological variations, not treatment related.
Hematological evaluation in females revealed no treatment-related effects. - Clinical biochemistry findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Potassium concentration in males treated at 100, 330 or 1000 mg/kg/day were slightly high when compared with controls and phosphorus concentration in males and females treated at 100, 330 or 1000 mg/kg/day were also slightly high however these differences were slight and there was no evidence of a dose response.
Furthermore, these changes were within the histrorical control data ranges and are considered incidental.
Triglycerides were low in females treated at 100, 330 or 1000 mg/kg/day however, these values were within the HCD ranges and considered incidental. - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- effects observed, non-treatment-related
- Description (incidence and severity):
- Sensory reactivity and grip strength were unaffected by treatment.
Group mean high and low beam activity scores for all groups of treated males were low compared with Controls, with statistical significance attained at the 12-minute interval (100 mg/kg/day; high and low beams), the 42-minute interval (1000 mg/kg/day; low beam only) and the total scores (all treated groups, high beams only). However, the majority of these scores were within the historical control data ranges, including some of the scores that have attained statistical significance.
The majority of group mean high and low beam activity scores for all groups of treated females were slightly high compared with Controls with an isolated statistical significance attained at the 42-minute interval for low beams but the differences in the total scores did not attain statistical significance and no effect of treatment is inferred. - Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Microscopic examination revealed accumulations of macrophages which were present in the mesenteric lymph nodes of males and females of animals given 330 or 1000 mg/kg/day.
Vacuolation was present in the adrenal cortex (zona reticularis and zona fasciculata) of two males given 1000 mg/kg/day; as this was only present in two males and the severity of this finding was slight this finding could not be directly attributed to treatment.
A single incidence of nephroblastoma was observed in a male given 1000 mg/kg/day. These tumours do occasionally occur as spontaneous lesions in younger animals such as this in short term studies (Ikezaki et al, 2011). Given the short term nature of this study and the absence of similar lesions in other animals, it is considered that this is an incidental finding and not related to administration of the test item.
Mineralisation was present in the tubules of the renal cortex in females from all groups, including controls. Similar renal changes were not identified in males. The finding is not considered to be related to treatment.
Foci of mucosal congestion and epithelial necrosis were present in the glandular region of the stomach in females from all groups, including controls. These changes are not considered to be related to treatment. The cause of the lesions is unclear. - Histopathological findings: neoplastic:
- not examined
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- no effects observed
- Reproductive function: sperm measures:
- no effects observed
- Reproductive performance:
- no effects observed
Effect levels (P0)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- reproductive function (oestrous cycle)
- reproductive function (sperm measures)
- reproductive performance
- Remarks on result:
- not determinable due to absence of adverse toxic effects
Target system / organ toxicity (P0)
- Key result
- Critical effects observed:
- no
Results: F1 generation
Effect levels (F1)
- Remarks on result:
- not measured/tested
Overall reproductive toxicity
- Key result
- Reproductive effects observed:
- no
Applicant's summary and conclusion
- Conclusions:
- Reproductive performance, fertility and offspring survival were unaffected by parental treatment. The No-observed-adverse-effect-level (NOAEL) of the test item for systemic toxicity and for reproductive/developmental effects was considered to be 1000 mg/kg/day.
- Executive summary:
The study was designed to assess the general systemic toxic potential in rats, including a screen for reproductive/developmental effects and assessment of endocrine disruptor relevant endpoints, with administration of the test item by oral gavage administration for at least five weeks. The study has been performed to the standardized guidelines OECD 422, under GLP conditions.
Three groups of ten male and ten female rats received the test item at doses of 100, 330 or 1000 mg/kg/day in arachis oil by oral gavage administration. Males were treated daily for two weeks before pairing, up to necropsy after a minimum of five consecutive weeks. Females were treated daily for two weeks before pairing, throughout pairing, gestation and until Day 13 of lactation. Females were allowed to litter, rear their offspring and were killed on Day 14 of lactation. The F1 generation received no direct administration of the test item; any exposure was in utero or via the milk. A similarly constituted Control group received the vehicle, arachis oil, at the same volume dose as the treated groups.
During the study the following observations were made for the adult animals: clinical observations, body weight, food consumption, hematology (peripheral blood), blood chemistry, serum thyroxine (T4) analysis, estrous cycles, pre-coital interval, mating performance, fertility, gestation length, organ weight and macroscopic pathology and histopathology investigations were undertaken.
The clinical condition, litter size and survival, sex ratio, body weight, ano-genital distance and macropathology for all offspring were also recorded. The serum T4 analysis was performed for the Day 13 offspring. Nipple counts were performed on male offspring on Day 13 of age.
There were no treatment related deaths and no adverse effects on clinical condition, sensory reactivity, grip strength, motor activity, body weight gain, food intake, haematology, and blood chemistry measurements in males and females. In addition, the reproductive endpoints assessed which were unaffected by treatment included estrus cycles, pre-coital interval, gestation length, mating performance, fertility, litter size, offspring survival or offspring sex ratio.
Offspring clinical condition, body weight, body weight gain, ano-genital distance and external development were also unaffected by treatment.
There was notreatment relatedeffect on the serum T4 levels in all analysed samples from adult male rats and offspring on Day 13 of age.
Group mean absolute and adjusted organ weights in males were unaffected by treatment. A trend of decrease in thymus weights was observed in females treated at 100, 330 or 1000 mg/kg/day with the difference from controls demonstrating a dose-relationship, but the decrease in thymus weights did not attain statistical significance and was considered as non-adverse.
The gross pathology examination performed on males after 5 weeks of treatment or females on Day 14 of lactation revealed no test item-related lesions.
The histopathology examination of a full list of tissues revealed one change that was considered treatment related but non-adverse: accumulations of macrophages in the mesenteric lymph nodes of males and females given 330 or 1000 mg/kg/day.
In conclusion, oral administration of the test item to parental Sprague Dawley (Crl:CD(SD)) rats at dose levels of 100, 330 or 1000 mg/kg/day for five weeks to males and for two weeks before pairing, throughout gestation and up to Day 13 of lactation in females was well-tolerated with no adverse effect observed.
Reproductive performance, fertility and offspring survival were unaffected by parental treatment. There was no effect of treatment on the number of implantations, litter size or the growth of the offspring.
In the context of this study, the test item showed no evidence of being an endocrine disruptor.
The No-observed-adverse-effect-level (NOAEL) of the test item for systemic toxicity and for reproductive/developmental effects was considered to be 1000 mg/kg/day.
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