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EC number: 276-696-7 | CAS number: 72490-01-8
- 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
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- 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:
- two-generation reproductive toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 8 Sep 1983 to 14 Dec 1984
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 986
- Report date:
- 1986
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 83-4 (Reproduction and Fertility Effects)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Ethyl [2-(4-phenoxyphenoxy)ethyl]carbamate
- EC Number:
- 276-696-7
- EC Name:
- Ethyl [2-(4-phenoxyphenoxy)ethyl]carbamate
- Cas Number:
- 72490-01-8
- Molecular formula:
- C17 H19 N O4
- IUPAC Name:
- ethyl [2-(4-phenoxyphenoxy)ethyl]carbamate
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Remarks:
- Albino (Crl:CD(SD)BR)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: (P) 6 weeks; (F1) 3.5 to 6.5 weeks
- Weight at study initiation: (P) Males: 200 to 285 g; Females: 144 to 201 g; (F1) Males: 132 to 226 g; Females: 106 to 178 g
- Housing: The animals were housed in groups or individually according to the phase of the study. Group housed animals were caged in stainless steel wire mesh cages suspended above aluminium trays with cardboard liners. Individually housed females and dames with litters were caged in solid floor polypropylene cages with stainless steel grid tops. Autoclaved sawdust was provided for bedding and, during parturition, shredded paper was provided as nesting material
- Diet: Powdered Rat and Mouse diet ad libitum
- Water: Ad libitum
- Acclimation period: 14 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 to 25
- Humidity (%): 40 to 70
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: 8 Sep 1983 to 14 Dec 1984
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- DIET PREPARATION
- Rate of preparation of diet: Separate batches of diet were prepared for each treatment group at weekly intervals throughout the study. Any diet remaining at the end of each week was discarded
- Storage temperature of food: Room temperature - Details on mating procedure:
- - M/F ratio per cage: 1/1
- Length of cohabitation: 21 days
- Proof of pregnancy: Sperm in vaginal smear referred to as day 0 of pregnancy
- After 10 days of unsuccessful pairing replacement of first male by another male with proven fertility.
- After successful mating each pregnant female was caged: The females were housed individually - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Batches of diet were prepared at concentrations corresponding to the proposed low and high dose levels. Quintuplicate samples (each from different levels of the mix) were taken from each batch and analysed in duplicate for their test substance content, to provide an indication of homogeneity.
The batches of diet were then stored at room temperature and triplicate samples were removed from each batch 7 and 14 days after preparation. The samples were then analysed to investigate the stability of the test article at room temperature.
The concentration of the test substance in was determined in duplicate samples of each experimental diet during weeks 1, 12, 25, 37, 49 and 61 to confirm the accuracy of the preparation - Duration of treatment / exposure:
- For the F0 animals, this was from initiation until the end of the F0-F1b mating period (F0 males) or until all the F1b litters were weaned (F0 females). For the selected F1b animals, this was from the time they began eating independently until the end of the F1-F2b mating period (F1 males) or until all the F2b litters were weaned (F1 females)
- Frequency of treatment:
- Continuously
- Details on study schedule:
- - Selection of parents from F1 generation when pups were 7 days of age.
- Age at mating of the mated animals in the study: F0: 80 days, F1: 100 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 200 ppm
- Remarks:
- Low dose: Dietary equivalent to 14 and 17 mg/kg bw/day for males and females, respectively
- Dose / conc.:
- 600 ppm
- Remarks:
- Mid dose: Dietary equivalent to 42 and 49 mg/kg bw/day for males and females, respectively
- Dose / conc.:
- 1 800 ppm
- Remarks:
- High dose: Dietary equivalent to 127 and 146 mg/kg bw/day for males and females, respectively
- No. of animals per sex per dose:
- F0: 30
F1: 25 - Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: The dietary concentrations were selected by the study sponsor after examination of data from a 6 week dose range-finding study in the rat.
Examinations
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS:
- Time schedule: At the beginning and end of each working day
GENERAL CLINICAL OBSERVATIONS:
- Time schedule: Daily. Towards the end of gestation, pregnant females were examined twice daily for signs of parturition
- Clinical observations: Signs of ill health, toxicity or behavioural change
BODY WEIGHT:
- Time schedule for examinations: Weekly until the confirmation of mating. Thereafter, body weights were recorded on days 0, 6, 12, 15 and 20 of gestation and on days 1,7, 14 and 21 of lactation. Following lactation, body weights were recorded weekly.
FOOD CONSUMPTION AND COMPOUND INTAKE:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes, at weekly intervals during the pre-mating periods only
OTHER:
- In the event of a delay between discovery of a dead animal and its necropsy, the carcass was stored at approximately 4 °C to minimise tissue autolysis
- The following data were recorded: date of mating, date of parturition and duration of gestation. - Oestrous cyclicity (parental animals):
- Not examined
- Sperm parameters (parental animals):
- Not examined
- Litter observations:
- PARAMETERS EXAMINED
The following data were recorded for each litter:
- Number of pups born (live and dead)
- Number of pups alive on days 1, 4, 7, 14 and 21 post-partum
- Individual pup weights on days 1, 4, 7, 14 and 21 post-partum
- Sexes of pups alive on days 1, 4, 7 and 21 post-partum general condition of pups throughout the pre-weaning period (birth to day 21 post-partum).
On day 4 post-partum litters were culled to a maximum of eight pups (4 male+ 4 female, where possible). Pups were selected by random card draw. Any pup dying during lactation was necropsied, where possible, to investigate the cause of death. Culled pups were also necropsied.
The following developmental parameters were measured for each litter:
- Pinna unfolding,
- Fur and hair growth,
- Tooth eruption
- Eye opening.
For each parameter, the number of pups in each litter showing the observation on each day was recorded until all the pups in the litter had shown the observation. In addition, on day 21 post-partum (weaning), 2 male and 2 female pups per litter (where possible) were selected for the following functional tests:
- Grip strength
- Pupillary reflex (both eyes)
- Visual placing response
- Auditory response. - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: All surviving animals after the second mating
- Maternal animals: All surviving animals after 21 days of weaning.
GROSS NECROPSY
Females: The following tissues and organs were taken from each animal and preserved in 10% neutral buffered formalin: uterus vagina*, ovaries*, target organ (liver)*.
Males: The following tissues were prepared for macroscopic examination and weighed: Testes*, epididymides, seminal vesicles, prostate and target organ (liver)*.
(*) organs were weighed prior to fixation
HISTOPATHOLOGY / ORGAN WEIGHTS
- Histopathological examinations were performed on the tissues and organs of all control and high dose males.
- Histopathological examination was performed on the tissues and organs of all control and high dose females. The uteri of pregnant females, killed or found dead, were examined. Implantations were subdivided into: Normal for date foetuses and resorbed foetuses
OTHER:
Twenty five days after the second pairing period in each generation, females that failed to litter were killed and necropsied. The uterus was examined for evidence of implantation before fixation. - Postmortem examinations (offspring):
- SACRIFICE
- The F1 offspring not selected as parental animals and all F2 offspring were sacrificed at 21 days of age.
GROSS NECROPSY
- All F1a, F2a and the non-selected F1b pups were subjected to macroscopic examination. The following tissues and organs were taken from one male and one female pup per litter (where possible) and preserved in 10% neutral buffered formalin: *adrenals, *brain (fore-, mid-, hind-), caecum, colon duodenum, +eyes (both), femur (including bone marrow), *heart, ileum, jejunum, *kidneys, *liver (2 lobes), lung (2 sections, coronal cut), mesenteric lymph node, ovaries/uterus testes/epididymides/prostate/seminal vesicles pancreas, pituitary, salivary glands (mandibular), spinal cord (cervical and lumbar), spleen, stomach, thymus, thyroids, trachea, urinary bladder, vagina and all gross lesions
(*) organs weighed before fixation
- All F2b offspring were subject to macroscopic examination. From one male and one female pup per litter (where possible), the following tissues and organs were taken and preserved in 10% neutral buffered formalin: #*adrenals, #*brain, caecum, colon, #duodenum, #+eyes (both), femur (including bone marrow), *heart, ileum, jejunum, #*kidneys, #*liver (2 lobes), #lung (2 sections, coronal cut), #mesenteric lymph node, #ovaries/uterus, #testes/epididymides/prostate/seminal vesicles, #pancreas, #pituitary, salivary glands (mandibular), spinal cord, (cervical and lumbar), #spleen, #stomach, #thymus, #thyroids, trachea, #urinary bladder, #vagina and all gross lesions (*) organs weighed before fixation
(+) preserved in Davidson's fluid.
(#) Histopathological examination of all organs was performed on the control and high dose pups.
HISTOPATHOLOGY / ORGAN WEIGTHS
Organs and tissues for histopathological examination were embedded in paraffin wax BP (mp 56°C), sectioned at a nominal thickness of 5 microns and stained with haematoxylin and eosin.
- F1b pups: histological examination was performed only on the livers of 5 male and 5 female F1b pups form each of groups 1 and 4.
- F2b pups: histopathological examination of all organs marked with an # in the list above was performed on the control and high dose pups. - Statistics:
- Continuous or semi-continuous responses and some discrete responses: Statistical evaluation was made using an analysis of variance technique for normally distributed errors on by non-parametric techniques for non-normally distributed errors. Analysis of variance established the significance of 'the variability between all groups to determine a treatment-related response. The standard deviation obtained from this analysis was used for 't'-tests between the control and treatment groups. Where necessary, the data were suitably transformed before analysis. Non-parametric testing was carried out using the Kruskal-Wallis test to determine a treatment-related response. Significant differences between control and treatment groups were determined using the Wilcoxon rank sum test. All tests were carried out at li and 5% significance levels for a two sided risk.
Discrete responses: Statistical analysis was carried out using Fisher's two-sum randomisation (permutation) test with a Monte Carlo simulation for computation of significance levels. The litter was the experimental unit and a square root transformation was used for weighting the number of incidences and adjusting the
different litter sizes. Each treatment group was tested against the control at 1% and 5% significance levels for a one-sided risk. In the interpretation of statistical analyses p values greater than 0.05 were considered to be not significant - Reproductive indices:
- Mating index, fertility index and the fecundity index
- Offspring viability indices:
- Gestation index, live birth index, viability index 1 (day 1 to 4), viability index 2 (day 4 to 7), viability index 3 (day 7 to 14), viability index 4 (day 14 to 21) and pre-weaning loss (day 0 to 21).
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- There were no abnormalities of clinical condition considered to be related to treatment. Non-specific changes of the type commonly seen in reproduction studies with this strain of rat occurred with similar frequency across all groups.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One group 4 male, died during week 17. One group 2 female was killed in extremis on day 7 of gestation in the F1a littering phase of the study.
During the second mating phase, at the time of parturition, a number of females exhibited dystocia - often with languor and tremors. Some animals died, some were killed in extremis and some were able to litter, but the pups were born dead or died shortly after birth. Five group 1 females died or were killed on days 21 or 22 of gestation, two group 2 females and one group 4 female were killed on day 21. In addition, one female from each of groups 2 and 4 died on day 1 of lactation. The pups died on day 1 from 2 further litters, one from group 2 and one from group 4. The problem at parturition appeared to be associated with severe stress as a consequence of unusually large litter sizes. All the females that died or were killed had litter sizes larger than the norm. The incidence of affected females was not dose-related.
All mortalities were considered to be incidental to treatment. - Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- During the pre-mating period, the mean body weight gain for the treated males and females was comparable to or higher than the control in groups 2 and 3 and marginally lower in group 4. The group 4 weight gain was significantly lower than controls in females for weeks 0 to 4 only.
For the remainder of the study, including (for females) both gestation and lactation phases, weight gains were comparable to or higher than controls for both sexes in all groups. - Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- During the pre-mating period the food consumption of the parental animals was generally comparable between all groups, and although marginally lower values were observed for group 4 females, no statistically significant intergroup differences were observed.
- Food efficiency:
- no effects observed
- 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, treatment-related
- Description (incidence and severity):
- - Microscopically, treatment-related changes were seen in the liver of some of the group 4 parental animals, minimal to slight hypertrophy was recorded in 19 out of 30 parental· males and 13 out of 30 females; moderate periportal hypertrophy was seen in 1 male. In addition, minimal to slight focal necrosis was seen in 5 out of 30 group 4 males and one female compared to 2 out of 30 control males. The severity was moderate to marked for the control animals. A further group 4 male had severe lobar necrosis. Two group 4 females had moderate to marked centrilobular necrosis, which was the same incidence and similar severity to the control females. There was no evidence of a treatment-related effect on any other tissue. examined.
- No treatment-related changes were seen at necropsy for the selected F1 a or F1 b pups. Histological examination of the livers of the group 4 F1 b pups revealed no abnormalities. - Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- effects observed, treatment-related
- Reproductive function: sperm measures:
- no effects observed
- Reproductive performance:
- no effects observed
- Description (incidence and severity):
- - All males mated during the F0-F1a mating period and only 2 males (one from each of groups 2 and 4) failed to mate during the F0-F1b mating period.
- All females mated, at both pairings, generally within one oestrous cycle. After the first pairing (F1a) only 2 animals, one group 1 and one group 3 were not pregnant. After the second pairing (F1b) 7 animals were not pregnant, 2 from each of groups 1, 2 and 3 and one from group 4. Only one group 3 animal failed to conceive after both pairings.
- There was no effect of treatment on litter size for either the F1a or F1b litters. The mean number of pups born per dam in the treated groups was similar to or larger than the control mean and there was little intergroup variation in sex ratio
Effect levels (P0)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Systemic toxicity
- Effect level:
- 200 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- food consumption and compound intake
- organ weights and organ / body weight ratios
- histopathology: non-neoplastic
- Remarks on result:
- other: Dietary equivalent to 14 and 17 mg/kg bw/day for males and females, respectively
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Reproductive toxicity
- Effect level:
- > 1 800 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Remarks:
- Dietary equivalent to 127 and 146 mg/kg bw/day for males and females, respectively
Target system / organ toxicity (P0)
- Key result
- Critical effects observed:
- no
Results: P1 (second parental generation)
General toxicity (P1)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- There were no abnormalities of clinical condition considered to be related to treatment.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One group 3 male was killed in extremis during week 24. There were no deaths in the females on the F2a littering phase of the study. As was seen in the first (F0) generation a number of females showed dystocia at the second (F2 b) littering phase and died or were killed. Four group 1 females died between day 22 of gestation and day 1 of lactation; 2 group 2 females died on day 22 of gestation; one group 3 female was killed on day 21 of gestation and one group 4 female died on day 1 of lactation. It was considered that the F1 females were past their peak of reproductive performance at the time of the second littering phase and probably this contributed to the observed difficulties in parturition.
All mortalities were considered to be incidental to treatment. - Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- - The group 4 parental animals were slightly lower in body weight than the controls at the start of the F1 generation. The mean weight of the males was 9% lower than the control weight and the female weight was 5% lower. The rate of body weight gain for group 4 was generally similar to the controls, although a significantly lower weight gain was observed in females from weeks 8 to 12. The initial body weights and the weight gain in groups 2 and 3 were similar to the controls.
- The initial body weights and the weight gain in groups 2 and 3 were similar to the controls.
- The body weight gain for treated females during the gestation and lactation periods of both the F2a and F2b pregnancies were comparable to the control gain. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- During the pre-mating period the food consumption of the parental animals was similar in groups 1, 2 and 3 and marginally lower in group 4. The reduction was statistically significant in group 4 females for weeks 1 to 5 only.
- Food efficiency:
- no effects observed
- 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
- Description (incidence and severity):
- - The mean relative liver weights of group 3 females and group 4 parental males and females were significantly increased when compared to the control (increase: group 3 female 19%; group 4 male 15%, female 36%). The mean relative weight for other parental animals was similar to the control.
- There was no treatment-related change in the relative weights of the other weighed organs from the parental animals. - Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Microscopically, treatment-related changes were seen in the liver of some of the group 4 parental animals. Minimal to moderate hypertrophy was seen in 14 out of 25 group 4 females. In addition, minimal to slight focal necrosis was seen in 14 out of 25 group 4 males; the incidence of focal necrosis for the females was similar to that of the controls. There was no evidence of a treatment-related effect on any other tissue examined.
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
Reproductive function / performance (P1)
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- no effects observed
- Description (incidence and severity):
- - There was no effect of treatment at any dose level on mating performance or fertility.
- Compared to the F0 generation, there was an increase in the number of males that did not mate twice in the F1 generation. However, there was no conclusive association with treatment as the incidence was 5, 3, 5 and 4 in groups 1 to 4, respectively. Also, only three of these animals (2 group 3 and 1 group 4 ) failed to mate on both occasions.
- All females mated at both pairings, generally within 1 oestrous cycle. The pregnancy incidence in the treated groups was higher than the control group at both pairings.
- The mean duration of gestation was comparable to controls in group 2, marginally shorter in group 3 and significantly reduced in group 4. In the F2b littering phase significant reductions in the duration of gestation were observed in groups 3 and 4. Several animals also showed difficulties in parturition, but the incidence of affected females was not dose-related.
- Only 2 females, one from each of groups 1 and 2 failed to conceive after both pairings.
- There was no effect of treatment on litter size. The mean number of pups born per dam in the treated groups was similar to or higher than in the control group. Sex ratios were within the normal range in all groups
Effect levels (P1)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Systemic toxicity
- Effect level:
- 200 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- food consumption and compound intake
- organ weights and organ / body weight ratios
- histopathology: non-neoplastic
- Remarks on result:
- other: Dietary equivalent to 14 and 17 mg/kg bw/day for males and females, respectively
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Reproductive toxicity
- Effect level:
- > 1 800 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Remarks:
- Dietary equivalent to 127 and 146 mg/kg bw/day for males and females, respectively
Target system / organ toxicity (P1)
- Key result
- Critical effects observed:
- no
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- There was no effect of treatment of the clinical condition.
- Dermal irritation (if dermal study):
- not examined
- Mortality / viability:
- mortality observed, non-treatment-related
- Description (incidence and severity):
- Survival of the offspring was unaffected by treatment. However, the pre-weaning loss for group 2 in the F1b littering phase was higher than normal. This was due to 3 females showing total litter loss during the first 2 days post-partum.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- - For the F1 a litters the mean pup weight at day 1 post-partum was similar in all groups. However, subsequently the mean weight of the control pups increased at a marginally greater rate than in the treated groups. The difference in weight was significant in all groups by day 14 and at weaning on day 21 post-partum the mean pup weight increase for groups 2, 3 and 4 was 92, 93 and 89% of the control weight increase, respectively.
- For the F1 b litter the mean pup weight at day 1 post-partum was similar in all groups. Subsequently the mean weight of groups 2 and 3 pups increased at a similar rate to the controls. The mean weight of the group 4 pups was again significantly lower than the control by day 14. At weaning on day 21 post-partum the mean weight increases for group 2, 3 and 4 were 98.1, 95.6 and 89.1% of the control weight increase, respectively. - 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:
- effects observed, treatment-related
- Description (incidence and severity):
- - The mean relative liver weight of the group 4 F1a female pups killed on day 21 post-partum was marginally increased, by 5%, when compared to the control.
- At the F1b kill the mean relative liver weight for group 4 male and female and group 3 female pups were significantly increased, compared to the control (increase: group 3 female 10%; group 4 male 19%; female 19%). Group 3 male relative liver weight were also slightly increased (5% compared to control) but the difference was not statistically significant. - Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- No necropsy findings were found on the offspring, dead or culled pups from either of the F1 litters.
- Histopathological findings:
- no effects observed
- Description (incidence and severity):
- Histological examination of the livers of the group 4 F1b pups revealed no abnormalities.
- Other effects:
- no effects observed
- Description (incidence and severity):
- There was very little intergroup difference in the physical development of the offspring, in either of the F1 litters, as assessed by the intra litter onset and duration of pinna unfolding, hair growth, tooth eruption and eye opening. Functional development of the offspring of both F1 litters was unaffected by treatment.
Developmental neurotoxicity (F1)
- Behaviour (functional findings):
- not examined
Developmental immunotoxicity (F1)
- Developmental immunotoxicity:
- not examined
Effect levels (F1)
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Developmental
- Generation:
- F1
- Effect level:
- 600 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- Remarks on result:
- other: Dietary equivalent to 42 and 49 mg/kg bw/day for males and females, respectively
Target system / organ toxicity (F1)
- Key result
- Critical effects observed:
- no
Results: F2 generation
General toxicity (F2)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- There was no effect of treatment on the clinical condition of the offspring.
- Dermal irritation (if dermal study):
- not examined
- Mortality / viability:
- mortality observed, non-treatment-related
- Description (incidence and severity):
- Survival of the offspring was unaffected by treatment. Pre-weaning losses in the treated groups were similar to or lower than in the control group.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- - In both littering phases (F2 a and b) the mean pup weights at day 1 and day 4 post-partum were slightly lower in the treated groups than the control weights. However, the control litter size was slightly smaller than in the treated groups and it was considered that the slightly heavier control pups were due to reduced intra-litter competition resulting from the smaller litter size. When this bias was eliminated (by standardisation of litter size at day 4) weight gain in groups 2 and 3 was comparable to controls and only marginal reductions were observed in group 4.
- Significant differences in pup weight were, however, observed in the treated groups as weight gain after day 4 did not compensate for the early retardation. - 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:
- effects observed, treatment-related
- Description (incidence and severity):
- - The mean relative liver weights of the group 4 F2a pups killed on day 21 post-partum was significantly increased (by 5 to 6%) when compared to the control. The mean relative weight for other pups and F2a pups was similar to the control. At the F2 b kill the mean relative liver weight of the group 4 females was only marginally increased (by 4%) when compared to the control. The mean relative liver weights of the other F2b pups were comparable to the control weight, although some significant differences were observed in absolute weights.
- Statistically significant differences in relative brain weight were observed in group 4 male F2a pups and all treated female F2b selected pups, but were considered to be associated with the retardation of body weight seen in these pups rather than a direct effect of treatment.
- Significant increases in relative kidney weight were observed in treated male F2b selected pups only and were considered incidental to treatment as there was no effect of the F2b female selected pups or the F2a selected pups.
- There was no treatment-related change in the relative weights of the other weighed organs from the selected F2a or F2b offspring. - Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- No treatment related changes were seen at necropsy for the selected F2a and F2b pups.
- Histopathological findings:
- no effects observed
- Description (incidence and severity):
- Histological examinations of the livers of the group 4 F2b pups revealed no abnormalities.
- Other effects:
- no effects observed
- Description (incidence and severity):
- The physical and functional development of the offspring of both F2 litters was unaffected by treatment.
Developmental neurotoxicity (F2)
- Behaviour (functional findings):
- not examined
Developmental immunotoxicity (F2)
- Developmental immunotoxicity:
- not examined
Effect levels (F2)
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- Developmental
- Generation:
- F2
- Effect level:
- 600 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- organ weights and organ / body weight ratios
- Remarks on result:
- other: Dietary equivalent to 42 and 49 mg/kg bw/day for males and females, respectively
Target system / organ toxicity (F2)
- Key result
- Critical effects observed:
- no
Overall reproductive toxicity
- Key result
- Reproductive effects observed:
- no
Any other information on results incl. tables
Results analysis of test diet formulations:
The homogeneity of the test substance in the low dose and the high dose diet mixes was considered to be acceptable (mean values of 101.0 and 100.2% of nominal). In addition, the stability of the test substance in the diet was also considered to be acceptable (7% loss/week at 250 µg/g). The homogeneity and stability tests were completed before dosing started.
The concentration of the test substance in diets analysed during the F0 generation phase of the study were close to the nominal concentrations (95.5 - 102.5% of nominal) and were considered to be acceptable.
The concentration of the test article in diets analysed during the F1 generation phase of the study were close to the nominal concentrations (97.5 to 105% of nominal) and were considered to be acceptable.
Table 1. Group reproduction indices F0 -F1a
Parameter | Group 1 | Group 2 | Group 3 | Group 4 |
Total number of females | 30 | 30 | 30 | 30 |
Total number of mated females | 30 | 30 | 30 | 30 |
% females mating | 100 | 100 | 100 | 100 |
Mating index % | 87.9 | 90.9 | 100 | 93,8 |
Total number of pregnant females | 29 | 30 | 29 | 30 |
Fertility index % | 96.7 | 100 | 96.7 | 100 |
Fecundity index % | 96.7 | 100 | 96,7 | 100 |
Gestation index % | 100 | 96.7 | 100 | 100 |
Live birth index % | 96.4 | 95.5 | 96.6 | 97.6 |
Viability index 1 % | 90.8 | 86.8 | 90.2 | 93.5 |
Viability index 2 % | 99.7 | 99.1 | 100 | 100 |
Viability index 3 % | 100 | 99.7 | 100 | 99.5 |
Viability index 4 % | 100 | 100 | 99.7 | 100 |
Pre- weaning loss % | 12.6 | 18.1 | 13.1 | 9.2 |
Table 2. Group reproduction indices F0 -F1b
Parameter | Group 1 | Group 2 | Group 3 | Group 4 |
Total number of females | 30 | 29 | 30 | 30 |
Total number of mated females | 30 | 29 | 30 | 30 |
% females mating | 100.0 | 100.0 | 100.0 | 100.0 |
Mating index % | 96.6 | 93.1 | 100.6 | 100.0 |
Total number of pregnant females | 28 | 27 | 28 | 29 |
Fertility index % | 93.3 | 93.1 | 93.3 | 96.7 |
Fecundity index % | 93.3 |
93.1 |
93.3 |
96.7 |
Gestation index % | 82.1 | 88.9 | 100 | 93.1 |
Live birth index % | 96.5 | 89.l | 97.4 | 92.2 |
Viability index 1 % | 91.3 | 90.0 | 90.S | 95.2 |
Viability index 2 % | 99.3 | 99.3 | 99.4 | 100.0 |
Viability index 3 % | 99.6 | 99.3 | 99.4 | 98,7 |
Viability index 4 % | 100.0 | 100.0 | 100.0 | 100.0 |
Pre- weaning loss % | 12.9 | 21.0. | 12.9 | 13.3 |
Table 3. Group mean litter data, pup number F1a
Parameter | Group 1 | Group 2 | Group 3 | Group 4 |
Number of pregnancies | 29/30 | 30/30 | 29/30 | 30/30 |
% of pregnancies | 96.7 | 100.0 | 96.7 | 100.0 |
Mean duration of gestation (days) | 21.s | 21.4 | 21.3 | 21.3- |
Number of pups born | 419 | 419 | 413 | 424 |
Mean number per dam |
14.4 |
14.4 |
14.2 |
14.1 |
Sex ratio males : females | 1:1.14 | 1:0.91 | 1:1.00 | 1:1.03 |
Number of pups alive day 1 | 404 |
400 |
399 |
414 |
Mean number per dam | 13.9 | 13.8 | 13.8 | 13.8 |
Number of pups alive day 4 |
367 |
347 |
360 |
387 |
Mean number per dam | 12.7 | 12 | 12.4 | 12.9 |
Number of pups culled day 4 | 143 | 131 | 136 | 147 |
Mean number per dam |
4.9 |
4.5 |
4.7 |
4.9 |
Number of pups alive day 7 | 223 | 213 | 224 | 240 |
Mean number per dam | 7.7 | 7.3 | 7.7 | 8 |
Number of pups alive day 14 | 223 | 212 | 224 | 238 |
Mean number per dam | 7.7 | 7.3 | 7.7 | 7.9 |
Number of pups alive day 21 | 223 | 212 | 223 | 238 |
Mean number per dam |
7.7 |
7.3 |
7.7 |
7.9 |
% pre-weaning loss | 12.6 | 18.1 | 13.1 | 9.2 |
Table 4. Group mean litter data, pup number F1b
Parameter | Group 1 | Group 2 | Group 3 | Group 4 |
Number of pregnancies | 28/30 | 27/29 | 28/30 | 29/30 |
% of pregnancies | 93.3 | 93.1 | 93.3 | 96.7 |
Mean duration of gestation (days) | 23 | 24 | 28 | 27 |
Mean duration of gestation (days) | 21.7 | 21.3 | 21.3* | 21.2** |
Number of pups born | 311· | 338 | 389 | 361 |
Mean number per dam |
13.5 | 14.1 | 13.9 | 13.4 |
Sex ratio males : females | 1:1.19 | 1:0.99 | 1:0.95 | 1:1.02 |
Number of pups alive day 1 | 300 | 301 | 379 | 333 |
Mean number per dam | 13.0 | 12.5 | 13.5 | 12.3 |
Number of pups alive day 4 |
274 | 271 | 343 | 317 |
Mean number per dam | 11.9 | 11.3 | 12.3 | 11.7 |
Number of pups culled day 4 | 97 | 114 | 134 | 118 |
Mean number per dam |
4.2 | 4,8 | 4.8 | 4,4 |
Number of pups alive day 7 | 175 | 155 | 207 | 199 |
Mean number per dam | 7.6 | 6,S | 7.4 | 7.4 |
Number of pups alive day 14 | 174 | 153 | 20S | 19S |
Mean number per dam | 7.6 | 6,4 | 7.3 | 7.2 |
Number of pups alive day 21 | 174 | 153 | 205 | 195 |
Mean number per dam |
7.6 | 6.4 | 7.3 | 7.2 |
% pre-weaning loss | 12.9 | 21.0 | 12,9 | 13.3 |
Statistical analysis: Intergroup differences from control group duration of gestation statistically significant: p<0,05* p<0.01**
Applicant's summary and conclusion
- Conclusions:
- The NOAEL is set at 200 ppm for systemic parental toxicity (mean dietary equivalent to 14 and 17 mg/kg bw/day for males and females, respectively, the NOAEL for reproductive toxicity is set at 1800 ppm (mean dietary equivalent to 127 and 146 mg/kg bw/day, respectively and the NOAEL for developmental toxicity is set at 600 ppm (mean dietary equivalent to 42 and 49 mg/kg bw/day for males and females.
- Executive summary:
A two-generation reproduction study of the test substance was conducted in the Sprague Dawley-derived rat of the Crl:CD(SD)BR strain according to EPA 83.2 and GLP principles. Groups of 30 male and 30 female (F0 generation) or 25 male and 25 female (F1 generation) rats were given the test substance orally, in the diet, at concentrations of 200, 600 or 1800 ppm (groups 2, 3 and 4, respectively). Similar groups of rats given untreated diet acted as controls (group 1). For males the dietary equivalent were 14, 42 and 127 mg/kg bw/day and for females 17, 49 and 146 mg/kg bw/day for males and females, respectively. For 600 ppm, the dietary intakes were equivalent to mg/kg bw/day. After a period of maturation (F0: 80 days, F1: 100 days) the parental animals were mated (1M:1F) and the females were allowed to rear their offspring to weaning (F0-F1a; F1-F2a). One week after weaning was completed, the parental animals were paired and allowed to rear their offspring to weaning for a second time (F0-F1b; F1-F2b). The animals which formed the F1 generation were randomly selected from the F1b litters. In each generation, the parental animals were evaluated for treatment-related effects on survival, clinical condition, body weight gain, food consumption, reproductive performance and pathological changes. The offspring were evaluated for effects on viability, growth, clinical condition, physical and functional development and pathological changes. The concentration of test article in the formulated diets which were analysed during weeks 1, 12, 25, 37, 49 and 61 was close to the nominal concentration and was considered acceptable for the purpose of this study. The homogeneity and stability of the test substance in the diet were assessed and considered acceptable before the start of the study.
Results showed that there were no treatment-related mortalities of the parental animals in either the F0 or F1 generations. In both generations, several females died during or shortly after parturition of the second litters. These deaths were attributed to the animals being past their peak of reproductive performance and to their unusually large litter sizes and were considered incidental to treatment. There were no abnormalities of clinical condition in the parental animals of either generation which could be considered treatment-related. During the pre-mating period, body weight gain of the F0 parental animals was comparable to controls in groups 2 and 3 but marginally lower in group 4. For the remainder of the F0 treatment period, body weight gain was comparable to controls in all groups. There was no effect of treatment at any dose level on body weight gain of the F1 parental animals although the group 4 animals were slightly lighter at the start of treatment. Food consumption during the pre-mating period was marginally lower than controls in group 4 females during the F0 generation and in group 4 males and females during the F1 generation. There was no effect of treatment in groups 2 and 3 on food consumption during either the F0 or F1 generation. Mating performance and fertility were unaffected by treatment at any of the dose levels investigated at either the first or second mating in each generation. Slight reductions in the duration of gestation were observed in groups 3 and 4 in the second mating of the first generation and both matings in the second generation. There was no effect of treatment in either generation on the number of pups born, neonatal viability, or clinical condition or necropsy findings of the offspring arising from either mating phase. A marginal reduction in the rate of weight gain was observed in both group 4 litters in each of the F0 and F1 generations. Neonatal growth in groups 2 and 3 was comparable to controls in each littering phase. The physical and functional development of the offspring of all treated animals was similar to controls in both litters of each generation. All group 4 parental animals showed a statistically significant increase in both absolute and relative liver weight, with marginal increases also noted in group 3 females. In general, group 4 offspring also showed increased liver weight relative to body weight, although the effect was less distinct than in the adults. Gonad weights were slightly increased in group 4 F0 adults only, although there were no adverse effects on reproductive performance. Treatment-related liver changes (hypertrophy/focal necrosis) were observed in the majority of the group 4 F0 or F1 parental animals. When compared to controls, both the incidence and severity of these findings were increased at this dose level. There was no evidence of a treatment-related effect on any other tissue examined, or on the livers of the selected F1b or F2b pups.
In conclusion, treatment at 1800 ppm elicited slight toxicity in the parental animals, characterised by marginal, temporary effects on weight gain, food intake and on gonad weight, liver weight and liver pathology. There were no adverse effects at this dose level on clinical condition, reproductive performance, or on neonatal viability, condition, development or pathology. However, minimal effects on pup growth and lover weight were observed in each generation. At 600 ppm, slight increases in liver weight were observed only in the parental females (F1) and female F1b pups. A slight reduction in the duration of gestation was also observed in each generation. No other adverse effects were observed at this dose level. There was no effect of treatment at 200 ppm on either the parental animals or their offspring. Therefore the NOAEL is set at 200 ppm for systemic parental toxicity (mean dietary equivalent to 14 and 17 mg/kg bw/day for males and females, respectively, the NOAEL for reproductive toxicity is set at 1800 ppm (mean dietary equivalent to 127 and 146 mg/kg bw/day, respectively and the NOAEL for developmental toxicity is set at 600 ppm (mean dietary equivalent to 42 and 49 mg/kg bw/day for males and females.
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