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EC number: 237-696-2 | CAS number: 13927-77-0
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- Ecotoxicological Summary
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Endpoint summary
Administrative data
Description of key information
The NOAEL value for repeated dose oral toxicity was 0.2 mg/kg bw/day in rats.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 03 Aug 2018 to 15 Oct 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- 29 July 2016
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Wistar Han IGS rats (Crl:WI(Han))
- Details on species / strain selection:
- This rat strain was used because it is routinely used at the test facility for this type of studies.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland, Sulzfeld, Germany
- Age at study initiation: 11 to 12 weeks
- Weight at study initiation: Males: 308.1 to 370.5 g. Females: 207.4 to 246.3 g
- Housing: The rats were housed in Makrolon cages with a bedding of wood shavings and strips of paper and a wooden block as environmental enrichment. During the pre-treatment and pre-mating period the females were housed 3-4 to a cage and the males 4-5 to a cage. After allocation the animals were housed four rats to a cage (separated by sex). For mating, one male and one female were housed together. Males were transferred to their home cages after mating. Mated females were housed individually in Makrolon cages, which were placed in another cage rack.
- Diet: The rats received a cereal-based (closed formula) rodent diet (VRF1 (FG)) from a commercial supplier (SDS Special Diets Services, Witham, England) and were fed ad libitum.
- Water: Water was provided ad libitum
- Acclimation period: 9 days
DETAILS OF FOOD AND WATER QUALITY: Food and water was checked for contaminants.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22±2
- Humidity (%): 45-65
- Air changes (per hr): about 10
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: 03 Aug 2018 to 15 Oct 2018 - Route of administration:
- oral: gavage
- Details on route of administration:
- The oral route of administration was used because this is an anticipated route of human exposure.
- Vehicle:
- corn oil
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Dilutions of the test substance in the vehicle were prepared daily. During the daily administration all dilutions were continuously stirred on a magnetic stirrer.
VEHICLE
- Justification for use and choice of vehicle: Corn oil was selected as a vehicle for the preparation of test item formulations as the test item was not soluble in water.
- Concentration in vehicle: 0.04, 0.4 and 2.0 mg/mL corresponding to a dose of 0.2, 2.0 and 10.0 mg/kg bw, respectively.
- Amount of vehicle (if gavage): 5 mL/kg bw
- Lot/batch no. (if required): A1800663
- Purity: 100%
- The dosing volume was adjusted based on the latest recorded body weight for each individual animal to maintain a constant dose level in terms of the animal’s body weight. During the gestation period, dose volumes were not adjusted after GD 14. A fixed volume based on the body weight on gestation day 14 was used for females between gestation day 14 up to the end of pregnancy. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analyses to determine the homogeneity and content of the test substance in dosing dilutions were conducted using an ICP-MS method.
• The homogeneity (and content) of the test substance in the test dilutions was assessed in the batch prepared on 20 August 2018, by analysing three samples of each test dilution (taken at top-, mid- and bottom- of the vial).
• The content of the test substance in each test dilution was determined by analysing one sample of each test dilution prepared on 3, 10 and 17 September 2018.
• Because the test substance was determined by analysing the Nickel content, it was not possible to determine the stability of the test substance. Instead, fresh test dilutions were prepared daily. - Duration of treatment / exposure:
- Males: Male animals were dosed during a 2-week premating period, during mating and after mating up to and including the day prior to sacrifice (after 31 days of treatment).
Females: The female animals were dosed during a 2-week premating period, and during mating, gestation and lactation up to and including the day prior to sacrifice on day 14 of lactation, or soon thereafter (one female killed on day 15 of lactation). - Frequency of treatment:
- once daily
- Dose / conc.:
- 0.2 mg/kg bw/day (actual dose received)
- Remarks:
- Group 2: Low dose
- Dose / conc.:
- 2 mg/kg bw/day (actual dose received)
- Remarks:
- Group 3: Mid dose
- Dose / conc.:
- 10 mg/kg bw/day (actual dose received)
- Remarks:
- Group 4: High dose
- No. of animals per sex per dose:
- 12
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The dose levels were selected in consultation with the sponsor based on the results of an abandoned study (Triskelion Report V21099/02, September 2018) and a 2-week dose-range finding study in rats administered 0.2, 1.0 and 5.0 mg test substance/kg body weight/day (Triskelion Report V21099/03, September 2018).
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS:
- Time schedule: All the animals were observed once daily for clinical signs of toxicity and twice daily for mortality and morbidity.
DETAILED CLINICAL OBSERVATIONS:
- Time schedule: prior to the first exposure and then once weekly throughout the study. The latter observations were conducted a few hours after dosing. Arena testing was not performed during the last days of pregnancy and during the first days of lactation.
- Parameters checked: Signs noted included but were not limited to changes in skin and fur, piloerection, changes in the eyes, gait (including posture), and presence of clonic or tonic movements, stereotypies and bizarre behaviour.
BODY WEIGHT:
- Time schedule for examinations: The body weight of each adult animal was recorded once during the acclimatization period (on day -4) and at initiation of treatment (day 0). Females were weighed once per week during the premating and mating period. Mated females were weighed on days 0, 7, 14 and 20 during presumed gestation and on day 0, 4, 7 and 13 of lactation. Non-mated females were weighed once per week after the mating period. The adult animals were weighed on their scheduled necropsy date in order to calculate the correct organ to body weight ratios.
FOOD CONSUMPTION:
- The food consumption was measured per cage over the same periods as the body weight were measured. The results were expressed in g per animal per day. Food intake was not recorded during the mating period. Food intake of non-mated females was not recorded.
HAEMATOLOGY:
- Time schedule for collection of blood: On the day of scheduled sacrifice
- Anaesthetic used for blood collection: Yes (CO2/O2)
- Animals fasted: Yes, overnight (water was available)
- How many animals: The clinical pathology (haematological and clinical biochemistry) examinations were conducted in five males and five females randomly selected from each main group and from all recovery group animals.
- Parameters checked: Haemoglobin (Hb), Packed cell volume (PCV), Red blood cells (RBC), Reticulocytes, Total white blood cells (WBC), Differential white blood cells (neutrophils, lymphocytes, eosinophils, basophils, monocytes), Prothrombin time and Thrombocyte count. The following parameters were calculated: Mean corpuscular volume (MCV), Mean corpuscular haemoglobin (MCH) and Mean corpuscular haemoglobin concentration (MCHC).
CLINICAL CHEMISTRY:
- Time schedule for collection of blood: On the day of scheduled sacrifice
- Anaesthetic used for blood collection: Yes (CO2/O2)
- Animals fasted: Yes, overnight (water was available)
- How many animals: The clinical pathology (haematological and clinical biochemistry) examinations were conducted in five males and five females randomly selected from each main group and from all recovery group animals.
- Parameters checked: alkaline phosphatase activity (ALP), aspartate aminotransferase activity (ASAT), alanine aminotransferase activity (ALAT), gamma glutamyl transferase activity (GGT), total protein, albumin, ratio albumin to globulin (calculated), urea, creatinine, glucose (fasting), bilirubin (total), cholesterol (total), triglycerides, calcium (Ca), sodium (Na), potassium (K), chloride (Cl), inorganic phosphate (PO4) and bile acids.
NEUROBEHAVIOURAL EXAMINATION:
- Time schedule for examinations: Females on PN13 after sacrifice of their pups.
- Dose groups that were examined: All groups
- Battery of functions tested: See Table 2 in ‘Any other information on materials and methods incl. tables’. - Sacrifice and pathology:
- SACRIFICE:
The animals were sacrificed by exsanguination from the abdominal aorta whilst under CO2/O2 anaesthesia and then subjected to macroscopic examination for pathological changes. Adult male animals were sacrificed after 31 days of treatment. On the day of necropsy a vaginal smear was taken of all adult females. Dams were sacrificed on day 14 of lactation, except for one female that was killed on LD15.
GROSS NECROPSY/ ORGAN WEIGHTS: Table 3 in ‘Any other information on materials and methods incl. tables’.
At scheduled necropsy, the organs of the adult animals were weighed (paired organs together) as soon as possible after dissection to avoid drying. Samples of the tissues and organs (see Table 1) of the adult animals were preserved in a neutral aqueous phosphate-buffered 4% solution of formaldehyde. The reproductive organs, the thyroid, the parathymic lymph nodes and all gross lesions of all male and female animals were preserved. The number of implantation sites in the uterus was counted. The other organs/tissues were preserved of five adult animals/sex/group (surviving males with the lowest identification numbers in each cage; females with a litter were selected).
HISTOPATHOLOGY: Table 3 in ‘Any other information on materials and methods incl. tables’.
Tissues for microscopic examination were embedded in paraffin wax, sectioned, and stained with haematoxylin and eosin, except for sections of the testes which were stained with PAS haematoxylin. Microscopic examination (by light microscopy) was performed as follows:
Males:
• Microscopic examination was performed on the preserved organs of males of the control group (1) and the high-dose group (4). Organs marked with an asterisk (the levator ani plus bulbocavenosus muscle complex, Cowper’s glands and glans penis) were preserved after weighing but not further examined.
• Microscopic examination of the preserved adrenals, heart, liver, lungs and skeletal muscle was extended to males of the low-dose (2) and mid-dose (3) groups.
• Gross lesions and the parathymic lymph nodes were examined microscopically in males of all dose groups.
• Reproductive organs (testes, epididymides, seminal vesicles and prostate) of males that did not mate were examined microscopically.
Females:
Because the female high-dose group was terminated intercurrently, microscopic examination of organs and tissues was focussed on the next lower-dose group (3) which completed the entire study duration.
• Microscopic examination was performed on the preserved organs of all females of the control group (1) and mid-dose group (3).
• Microscopic examination of the preserved adrenals, heart, liver, lungs, and skeletal muscle was extended to females of the low-dose (2) group.
• Gross lesions and the parathymic lymph nodes were examined microscopically in females of all dose groups (including the high-dose females).
• Reproductive organs (ovaries and uterus) of females that were non-mated were examined microscopically. - Other examinations:
- Blood sampling for hormone determinations
During scheduled necropsy blood was taken from the aorta under CO2/O2 anaesthesia from all adult male and female animals and plasma was stored in a freezer at ≤-18° C.
Hormone determinations (T4)
Plasma samples were analysed for Thyroxin (T4) hormone levels in all adult males. - Statistics:
- The statistical procedures for analysis of data are described in Table 1 in ‘Any other information on materials and methods incl. tables’. Where applicable, high-dose females, and non-mated females were excluded from mean data tables presenting data from the gestation and lactation periods.
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- There were no treatment-related clinical signs in males or, until parturition, in females. Signs noted prior to the death of eight females of the high-dose group included respiratory distress, piloerection and soiled fur/perineum. Two other pregnant high-dose rats delivered, but had litters with mainly dead pups and showed paleness and piloerection after delivery. The females in the other dose-groups did not show treatment-related clinical signs.
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- At parturition, one high-dose rat was found dead and eight high-dose rats were humanely killed because of conditional decline.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- See Tables 1 to 8 in 'Any other information on results incl. tables'.
Mean body weights were statistically significantly reduced in high-dose males in the last two weeks of their treatment, and in high-dose females on day 7 and 20 of gestation. In addition, body weight gain was statistically significantly reduced in high-dose males at most stages, and in high-dose females during the first week of the premating period and the last week of gestation. There were no treatment-related differences in body weights or body weight gain in males or females of the low- and mid-dose groups.
Statistically significantly lower body weight gains noted in females prior to the start of the treatment, and in low-dose males in the last week of their treatment were not reflected in significant effects on body weights and are considered chance findings. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- See Tables 9 to 12 in 'Any other information on results incl. tables'.
Statistically significantly reductions in food consumption were noted in high-dose males, and in high-dose females during premating, gestation and (in two remaining rats only) lactation. Food consumption was also statistically significantly reduced in males of the mid-dose group in their last week of treatment. - Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- See Tables 13 to 16 in 'Any other information on results incl. tables'.
In mid- and high-dose males, red blood cell count, haemoglobin concentration and packed cell volume were statistically significantly decreased, and reticulocytes were increased compared to controls. Prothrombin time was statistically significantly increased in high-dose males. An incidental increase in thrombocyte count in mid-dose males was not confirmed in the high-dose group and was therefore considered a chance finding. In females treated up to 2 mg/kg bw/day there were no significant differences in red blood or coagulation parameters, apart from an incidental increase in haemoglobin concentration in mid-dose females. In high-dose males, total white blood cell count, absolute lymphocyte and eosinophil counts were statistically significantly lower, while the percentage of monocytes was statistically significantly higher than in controls. There were no statistically significant differences in white blood cell counts in males or females of the low- and mid-dose groups. - Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- See Tables 17 to 18 in 'Any other information on results incl. tables'.
In high-dose males, ASAT activity and urea, chloride and sodium concentrations were statistically significantly increased, while total protein, albumin, glucose and calcium concentrations were statistically significantly decreased compared to controls.
There were no treatment-related differences in clinical chemistry data in males or females of the low- and mid-dose groups. Results obtained in het high-dose female group are not discussed because the measurements were performed in one dam only. - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Description (incidence and severity):
- The results of the neurobehavioral observations and motor activity assessment did not indicate any neurotoxic potential of the test substance in rats.
Weak evidence of an effect of treatment on body temperature was, however, observed in the functional observation test: at the end of the treatment period, body temperature was statistically significantly decreased in the female high-dose group which included by then only two dams. - Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- See Tables 19 to 22 in 'Any other information on results incl. tables'.
The following statistically significant differences with the controls were noted in absolute organ weights and/or in organ to body weight ratio’s:
• The absolute and relative weights of the heart were increased in mid- and high-dose males. The absolute and relative weights of the heart were also considerably increased in the two surviving high-dose females (no statistics applied).
• The absolute and relative weights of the liver were increased in high-dose males.
• The absolute weights of the epididymides, prostate and seminal vesicles, and the relative weights of the prostate and seminal vesicles were decreased in high-dose males.
The following statistically significant differences were not ascribed to the test substance:
• The relative weight of the kidneys was decreased in low-dose males, but this finding was not confirmed at higher dose levels.
• The absolute weight of the kidneys was lower in high-dose males. Because the relative weight of this organ was not significantly affected, this finding is ascribed to the lower terminal body weights in this group.
There were no statistically significant changes in females of the low- and mid-dose groups. Results obtained in high-dose females are, due to the low number of remaining dams in this group, not further discussed. - Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- MACROSCOPY OF MORIBUND AND DEAD FEMALES:
Macroscopy showed enlarged parathymic lymphnodes in 6/9 females, a small cecum in 2/9 females, stomach ulcers in 4/9 females and pale lungs in 2/9 females. The remaining findings were considered unremarkable and part of the background pathology of rats of this strain and age.
MACROSCOPY AT SCHEDULED NECROPSY:
At necropsy, the parathymic lymphnodes were enlarged in 5/12 high-dose males and in 2/3 surviving high-dose females. Red discoloration was noted in 4/12 high-dose males (including three males also showing enlarged parathymic lympnodes). In the other groups, including the controls, these findings were observed only incidentally.
The heart was enlarged of 1/12 high-dose males. The remaining findings were considered unremarkable and part of the background pathology of rats of this strain and age. - Neuropathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- MICROSCOPY OF MORIBUND AND DEAD ANIMALS:
Mild to moderate histiocytosis was observed in the parathymic lymphnodes of 7/9 high-dose females which, in most cases, corresponded with the macroscopically observed enlarged parathymic lymphnodes (see above).
The macroscopically pale lungs (see above) of the two high-doses females showed minimal perivascular inflammation.
The remaining findings were considered unremarkable and part of the background pathology of rats of this strain and age.
MICROSCOPY AT SCHEDULED NECROPSY:
Parathymic lymphnode
In the control group 3/24 rats (3 males) showed minimal histiocytosis (including the male with the macroscopically observed enlargement of the parathymic lymphnodes). In the low-dose group, 4/24 rats (4 females) showed minimal histiocytosis. In the mid-dose group 5/21 rats (2 males and 3 females) showed minimal histiocytosis. In the high-dose group 14/15 rats (11 males and the three surviving females) showed mild to moderate histiocytosis of the parathymic lymphnodes. Adrenal gland
In 4/5 males of the mid-dose group and 5/5 males of the high-dose group, mild to moderate vacuolation was observed in the zona fasciculata of the adrenal gland. This finding was not observed in any other group.
Heart
Degeneration of heart muscle tissue, characterized by the presence of fibrotic areas, was observed in 4/5 mid-dose males at minimal to mild degree, and in 6/6 high-dose males at mild to moderate degree. This finding was not observed in any other group.
Skeletal muscle
Minimal to mild degeneration of the skeletal muscle was observed in 5/5 high-dose males. In addition 3/5 high-dose males showed minimal to mild necrosis and 4/5 high-dose males showed minimal to mild mononuclear inflammation. In the mid-dose group, one male showed minimal mononuclear inflammation and minimal necrosis. These findings were not observed in any other group.
Liver
Minimal to mild hyperemia was observed in in the liver of 5/6 high-dose males while minimal hyperemia was observed in the liver of 2/5 mid-dose females. This finding was not observed in any other group.
Lung
Minimal to mild perivascular inflammation was noted in 6/6 high-dose males, in 4/5 mid-dose males and in 5/5 mid-dose females. In addition, minimal to mild accumulation of alveolar macrophages was noted in 6/6 high-dose males, in 5/5 mid-dose males and in 4/5 mid-dose females. Further, the incidence of alveolitis was increased in high-dose males (5/6 high-dose males showed minimal to mild alveolitis). Apart from the incidental occurrence of alveolitis and alveolar macrophages, these findings were not observed in the control group or the low-dose group. Occasional occurrence of alveolar macrophages and alveolitis is in line with our historical control data.
The remaining findings were considered unremarkable and part of the background pathology of rats of this strain and age. - Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
- Description (incidence and severity):
- T4 LEVELS: No statistically significant effects in plasma T4 levels were noted between treatment groups and controls.
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 0.2 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- haematology
- histopathology: non-neoplastic
- organ weights and organ / body weight ratios
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 0.2 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- histopathology: non-neoplastic
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 10 mg/kg bw/day (actual dose received)
- System:
- musculoskeletal system
- Organ:
- heart
- other: skeletal muscle
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
- Conclusions:
- Based on the effects noted in the mid- and high-dose groups, the NOAEL for parental systemic effects was placed at 0.2 mg/kg body weight/day.
- Executive summary:
In this GLP compliant OECD 422 study, the effect of the test substance on general toxicity, reproductive performance and development of pups was examined in four groups of 12 male and 12 female Wistar rats. The test substance was suspended in corn oil and administered by oral gavage at 0, 0.2, 2 and 10 mg/kg body weight/day. The content, and homogeneity of the test substance in the vehicle were confirmed by analysis. The test substance was administered daily, during a pre-mating period of 2 weeks, during mating, gestation and lactation. Male animals were sacrificed after 31 days of treatment. Parental female animals were sacrificed at day 14 of lactation.
Most pregnant high-dose females, however, had to be sacrificed for humane reasons at parturition. There were no treatment-related clinical signs in males or, until parturition, in females. At parturition, one high-dose female was found dead and eight high-dose females were humanely killed because of conditional decline. Signs noted prior to their death included respiratory distress, piloerection and soiled fur/perineum. Two other pregnant high-dose rats delivered, but had litters with mainly dead pups, and showed paleness, piloerection and a lower body temperature. The results of the neurobehavioral observations and motor activity assessment did not indicate any neurotoxic potential of the test substance in rats. Mean body weights and body weight gain were reduced in high-dose males and in high-dose females during gestation. Reductions in food consumption were noted in the high-dose group in both sexes. Hematology and clinical chemistry was conducted at scheduled sacrifice in 5 males/group and in 5 dams in the control-, low- and mid-dose groups. In mid- and high-dose males, red blood cell count, hemoglobin concentration and packed cell volume were decreased, and reticulocytes were increased. Prothrombin time was increased in high-dose males. Total white blood cell, lymphocyte and eosinophil counts were decreased and the percentage of monocytes was increased in high-dose males. In high-dose males, ASAT activity and urea, chloride and sodium concentrations were increased, while total protein, albumin, glucose and calcium concentrations were decreased compared to controls. The absolute and relative weights of the heart were increased in mid- and high-dose males. The absolute and relative weights of the heart were also considerably increased in the two surviving high-dose dams. The absolute and relative weights of the liver were increased, and those of the prostate and seminal vesicles were decreased in high-dose males. In addition, the absolute weight of the epididymides was decreased in high-dose males. Macroscopic examination at scheduled necropsy showed enlarged parathymic lymphnodes in 5/12 high-dose males and in 2/3 remaining high-dose females. Enlarged parathymic lymphnodes were also noted in 6/9 high-dose females that died or were killed in moribund condition. Microscopic examination was performed on males of the high-dose group and the control group. Because the female high-dose group was terminated untimely, microscopic examination was focussed on the next lower-dose group (mid-dose females) and the controls. Organs showing treatment-related microscopic findings were also examined in the intermediate- dose group(s). The following findings were noted:
• A dose-dependent degeneration of the heart muscle in mid- and high-dose males, characterized by the presence of fibrotic areas.
• Degeneration of the skeletal muscle accompanied by necrosis and mononuclear inflammation in high-dose males. In the mid-dose group, 1/5 males showed necrosis and mononuclear inflammation of the skeletal muscle.
• Hyperemia in the liver of high-dose males and mid-dose females.
• Perivascular inflammation and accumulation of alveolar macrophages in the lungs of mid- and high-dose males and mid-dose females. In addition, the incidence of alveolitis was increased in high-dose males.
• Vacuolation in the zona fasciculata of the adrenal gland in mid- and high-dose males.
• Increased incidence of histiocytosis in the parathymic lymphnodes in males and females of the high-dose group.
Results of T4 hormone analysis in male adult animals did not show any significant effects between the groups.
Conclusions:
• Based on the effects noted in the mid- and high-dose groups, the NOAEL for parental systemic effects was placed at 0.2 mg/kg body weight/day.
Reference
Table 1. Body weight males during the study - Day(s) Relative to Start Date
Sex: Male |
|
Bodyweights |
|||||
Bodywt day -x (g) [G] |
Bodywt [G] |
Bodywt (g) [G] |
Bodywt (g) [G] |
Bodywt (g) [G] |
Bodywt (g) [G] |
||
-4 |
0 |
7 |
14 |
21 |
28 |
||
0.0 mg/kg |
Mean |
332.25 |
339.20 |
349.24 |
360.44 |
364.82 |
377.88 |
|
SD |
14.42 |
16.02 |
16.17 |
17.21 |
15.37 |
14.27 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
330.89 |
338.01 |
346.78 |
357.60 |
361.08 |
368.26 |
|
SD |
12.48 |
12.55 |
13.83 |
13.92 |
15.38 |
17.69 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
2.0 mg/kg |
Mean |
330.38 |
339.37 |
346.56 |
358.48 |
362.31 |
372.29 |
|
SD |
12.58 |
13.26 |
13.00 |
14.23 |
14.99 |
16.79 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
331.36 |
336.26 |
337.01 |
346.16 |
343.83** |
349.34** |
|
SD |
14.80 |
14.44 |
14.55 |
17.78 |
15.84 |
19.15 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
[G] - Ancova/Anova & Dunnett: ** = p < 0.01
Table 2. Body weight females premating -Day(s) Relative to Start Date
Sex: Female |
|
Bodyweights |
|||
Bodywt (g) [G] |
Bodywt [G] |
Bodywt [G] |
Bodywt [G] |
||
-4 |
0 |
7 |
14 |
||
0.0 mg/kg |
Mean |
220.88 |
227.02 |
227.25 |
232.16 |
|
SD |
10.23 |
9.64 |
8.57 |
12.38 |
|
N |
12 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
221.58 |
225.08 |
225.74 |
232.08 |
|
SD |
10.67 |
10.81 |
10.50 |
9.43 |
|
N |
12 |
12 |
12 |
12 |
2.0 mg/kg |
Mean |
221.50 |
226.14 |
225.57 |
231.78 |
|
SD |
9.72 |
10.83 |
12.34 |
10.36 |
|
N |
12 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
221.63 |
225.31 |
218.46 |
223.95 |
|
SD |
12.02 |
11.42 |
11.87 |
13.84 |
|
N |
12 |
12 |
12 |
12 |
[G] - Ancova/Anova & Dunnett
Table 3. Body weight females gestation - Day(s) Relative to Mating (Litter: A)
Sex: Female |
Bodyweights |
||||
Bodywt [G] |
Bodywt [G] |
Bodywt [G] |
Bodywt [G] |
||
0 |
7 |
14 |
20 |
||
0.0 mg/kg |
Mean |
232.50 |
253.30 |
272.04 |
335.07 |
|
SD |
11.11 |
9.41 |
15.61 |
10.99 |
|
N |
12 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
229.98 |
251.06 |
271.20 |
334.12 |
|
SD |
11.09 |
10.20 |
11.56 |
14.81 |
|
N |
10 |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
228.88 |
253.80 |
275.38 |
338.78 |
|
SD |
8.65 |
12.96 |
14.20 |
19.49 |
|
N |
12 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
224.24 |
240.39* |
258.06 |
301.00** |
|
SD |
14.04 |
15.67 |
18.39 |
24.59 |
|
N |
11 |
11 |
11 |
11 |
[G]
- Ancova/Anova & Dunnett: * = p < 0.05; ** = p < 0.01
Litter: A = First litter
Table 4. Body weight females lactation - Day(s) Relative to Mating (Litter: A)
Sex: Female |
Bodyweights |
||||
Bodywt [G] |
Bodywt [G1] |
Bodywt [G] |
Bodywt [G] |
||
0 |
4 |
7 |
13 |
||
0.0 mg/kg |
Mean |
259.67 |
266.33 |
270.13 |
278.13 |
|
SD |
13.44 |
13.83 |
13.53 |
12.55 |
|
N |
12 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
254.92 |
262.06 |
268.41 |
274.79 |
|
SD |
11.13 |
5.75 |
10.47 |
9.30 |
|
N |
10 |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
258.28 |
267.38 |
273.63 |
275.38 |
|
SD |
13.68 |
14.75 |
14.28 |
11.73 |
|
N |
12 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
245.05n |
249.20n |
253.95n |
260.35n |
|
SD |
3.75 |
5.37 |
1.34 |
14.64 |
|
N |
2 |
2 |
2 |
2 |
[G] - Ancova/Anova & Dunnett: n - Inappropriate for statistics
[G1] - Kruskal-Wallis & Dunnett on Ranks: n - Inappropriate for statistics
Litter: A = First litter
Table 5. Body weight changes males during the study - Day(s) Relative to Start Date
Sex: Male |
|
|
||||
Wgt change (g) [G] |
Body wt (g) [G] |
Body wt (g) [G] |
Body wt (g) [G1] |
Body wt (g) [G] |
||
-4 - 0 |
0 - 7 |
7 - 14 |
14 - 21 |
21 - 28 |
||
0.0 mg/kg |
Mean |
6.95 |
10.04 |
11.20 |
4.38 |
13.07 |
|
SD |
3.89 |
4.01 |
2.39 |
3.71 |
5.10 |
|
N |
12 |
12 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
7.12 |
8.77 |
10.83 |
3.48 |
7.18* |
|
SD |
2.44 |
3.38 |
4.72 |
4.01 |
4.24 |
|
N |
12 |
12 |
12 |
12 |
12 |
2.0 mg/kg |
Mean |
8.99 |
7.19 |
11.92 |
3.83 |
9.98 |
|
SD |
3.05 |
2.82 |
3.36 |
2.15 |
4.32 |
|
N |
12 |
12 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
4.90 |
0.75** |
9.15 |
-2.33** |
5.52** |
|
SD |
2.96 |
3.42 |
5.02 |
6.35 |
6.63 |
|
N |
12 |
12 |
12 |
12 |
12 |
[G]
- Ancova/Anova & Dunnett: * = p < 0.05; ** = p < 0.01
[G1] - Kruskal-Wallis & Dunnett on Ranks: ** = p < 0.01
Table 6. Body weight changes females premating - Day(s) Relative to Start Date
Sex: Female |
|
|
||
Wgt change (g) [G] |
Body wt (g) [G] |
Body wt (g) [G] |
||
-4 - 0 |
0 - 7 |
7 - 14 |
||
0.0 mg/kg |
Mean |
6.14 |
0.23 |
4.91 |
|
SD |
1.29 |
6.90 |
8.48 |
|
N |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
3.50* |
0.66 |
6.34 |
|
SD |
2.44 |
5.54 |
5.99 |
|
N |
12 |
12 |
12 |
2.0 mg/kg |
Mean |
4.64 |
-0.58 |
6.21 |
|
SD |
2.77 |
6.23 |
3.99 |
|
N |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
3.68* |
-6.85* |
5.49 |
|
SD |
2.05 |
4.63 |
6.43 |
|
N |
12 |
12 |
12 |
[G] - Ancova/Anova & Dunnett: * = p < 0.05
Table 7. Body weight changes females gestation - Day(s) Relative to Mating (Litter: A)
Sex: Female |
|
|||
Body wt (g) [G] |
Body wt (g) [G1] |
Body wt (g) [G1] |
||
0 - 7 |
7 - 14 |
14 - 20 |
||
0.0 mg/kg |
Mean |
20.80 |
18.74 |
63.03 |
|
SD |
7.47 |
11.18 |
9.84 |
|
N |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
21.08 |
20.14 |
62.92 |
|
SD |
6.35 |
5.57 |
8.97 |
|
N |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
24.93 |
21.58 |
63.41 |
|
SD |
5.65 |
3.54 |
9.02 |
|
N |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
16.15 |
17.67 |
42.94* |
|
SD |
4.04 |
5.96 |
16.33 |
|
N |
11 |
11 |
11 |
[G] - Ancova/Anova & Dunnett
[G1] - Kruskal-Wallis & Dunnett on Ranks: * = p < 0.05
Litter: A = First litter
Table 8. Body weight changes females lactation - Day(s) Relative to Littering (Litter: A)
Sex: Female |
|
|||
Body wt (g) [G] |
Body wt (g) [G] |
Body wt (g) [G] |
||
0 - 4 |
4 - 7 |
7 - 13 |
||
0.0 mg/kg |
Mean |
6.67 |
3.79 |
8.01 |
|
SD |
10.27 |
8.08 |
11.00 |
|
N |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
7.14 |
6.35 |
6.38 |
|
SD |
7.93 |
6.88 |
11.65 |
|
N |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
9.11 |
6.24 |
1.76 |
|
SD |
10.42 |
4.65 |
8.72 |
|
N |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
4.15n |
4.75n |
6.40n |
|
SD |
1.63 |
4.03 |
13.29 |
|
N |
2 |
2 |
2 |
[G]
- Ancova/Anova & Dunnett: n - Inappropriate for statistics
Litter: A = First litter
Table 9. Food consumption males during the study - Daily Food Cons Per Animal (Gram)
Sex: Male |
Day(s) Relative to |
|||
0 - 7 |
7 - 14 |
21 - 28 |
||
0.0 mg/kg |
Mean |
16.7 |
15.0 |
14.8 |
|
SD |
0.5 |
0.5 |
1.1 |
|
N |
3 |
3 |
3 |
0.2 mg/kg |
Mean |
16.5 |
14.4 |
13.2 |
|
SD |
1.1 |
0.6 |
0.5 |
|
N |
3 |
3 |
3 |
2.0 mg/kg |
Mean |
16.7 |
14.0 |
12.8* |
|
SD |
0.8 |
0.3 |
0.4 |
|
N |
3 |
3 |
3 |
10.0 mg/kg |
Mean |
15.2 |
12.2** |
11.3** |
|
SD |
1.0 |
0.7 |
0.6 |
|
N |
3 |
3 |
3 |
Dunnett: * = p < 0.05; ** = p < 0.01
N=Number of cages
Consumption was measured per cage over the periods shown and expressed as g/animal/day
Table 10. Food consumption females premating - Daily Food Cons Per Animal (Gram)
Sex: Female |
Day(s) Relative to |
||
0 - 7 |
7 -14 |
||
0.0 mg/kg |
Mean |
12.3 |
12.2 |
|
SD |
0.9 |
0.5 |
|
N |
3 |
3 |
0.2 mg/kg |
Mean |
12.1 |
11.5 |
|
SD |
0.7 |
0.7 |
|
N |
3 |
3 |
2.0 mg/kg |
Mean |
12.6 |
11.3 |
|
SD |
0.3 |
0.3 |
|
N |
3 |
3 |
10.0 mg/kg |
Mean |
10.9 |
9.5** |
|
SD |
0.3 |
0.3 |
|
N |
3 |
3 |
Dunnett: ** = p < 0.01
N=Number of cages
Consumption was measured per cage over the periods shown and expressed as g/animal/day
Table 11. Food consumption females gestation - Daily Food Cons Per Animal
Sex: Female |
Day(s) Relative |
|||
0 - 7 |
7 - 14 |
14 - 20 |
||
0.0 mg/kg |
Mean |
13.66 |
14.24 |
16.45 |
|
SD |
1.42 |
2.35 |
2.00 |
|
N |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
13.20 |
13.95 |
14.93 |
|
SD |
1.18 |
1.41 |
1.13 |
|
N |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
13.42 |
14.57 |
16.04 |
|
SD |
1.61 |
1.49 |
1.41 |
|
N |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
11.25** |
12.57 |
12.90** |
|
SD |
1.30 |
1.06 |
2.23 |
|
N |
11 |
11 |
11 |
Dunnett: ** = p < 0.01
Litter: A = First litter
N=Number of cages
Consumption was measured per cage over the periods shown and expressed as g/animal/day
Table 12. Food consumption females lactation - Daily Food Cons Per Animal
Sex: Female |
Day(s) Relative |
|||
0 - 4 |
4 - 7 |
7 - 13 |
||
0.0 mg/kg |
Mean |
24.05 |
34.72 |
41.50 |
|
SD |
2.87 |
4.11 |
4.46 |
|
N |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
23.37 |
33.23 |
41.86 |
|
SD |
3.17 |
3.19 |
5.87 |
|
N |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
22.59 |
33.17 |
39.91 |
|
SD |
4.37 |
4.41 |
4.42 |
|
N |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
10.09** |
16.00** |
14.23** |
|
SD |
0.19 |
1.98 |
5.63 |
|
N |
2 |
2 |
2 |
Dunnett: ** = p < 0.01
Litter: A = First litter
N=Number of cages
Consumption was measured per cage over the periods shown and expressed as g/animal/day
Table 13. Red blood cell and coagulation parameters -Day: 31 Relative to Start Date
Sex: Male |
|
|
|
|
|
|
|
|
|
|
RBC (10E12/L) [G] |
Hb (mmol/L) [G] |
PCV [G] |
MCV [G] |
MCH [G] |
MCHC (mmol/L) [G] |
Reticulo (%) [G] |
Thrombo (10E9/L) [G1] |
Prothrom Time (s) [G1] |
||
0.0 mg/kg |
Mean |
8.962 |
9.76 |
0.4788 |
53.44 |
1.089 |
20.39 |
2.228 |
754.2 |
17.74 |
|
SD |
0.251 |
0.30 |
0.0116 |
1.03 |
0.031 |
0.42 |
0.148 |
55.6 |
0.48 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
0.2 mg/kg |
Mean |
8.702 |
9.52 |
0.4672 |
53.70 |
1.094 |
20.38 |
2.086 |
778.6 |
17.92 |
|
SD |
0.210 |
0.24 |
0.0111 |
1.15 |
0.017 |
0.31 |
0.199 |
24.8 |
0.47 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
2.0 mg/kg |
Mean |
8.480* |
9.20** |
0.4534* |
53.48 |
1.086 |
20.30 |
3.054* |
865.8** |
18.12 |
|
SD |
0.308 |
0.14 |
0.0123 |
0.80 |
0.026 |
0.35 |
0.559 |
39.5 |
0.19 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
10.0 mg/kg |
Mean |
8.270** |
8.80** |
0.4410** |
53.35 |
1.065 |
19.96 |
3.224** |
738.8 |
19.46** |
|
SD |
0.316 |
0.32 |
0.0144 |
1.43 |
0.032 |
0.42 |
0.550 |
131.8 |
0.89 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
[G]
- Ancova/Anova & Dunnett: * = p < 0.05; ** = p < 0.01
[G1] - Kruskal-Wallis & Dunnett on Ranks: ** = p < 0.01
Table 14 Red blood cell and coagulation parameters -Day: 14 Relative to Littering (Litter: A)
Sex: Female |
|
|
|
|
|
|
|
|
|
|
RBC (10E12/L) [G] |
Hb (mmol/L) [G] |
PCV [G] |
MCV [G] |
MCH [G] |
MCHC (mmol/L) [G] |
Reticulo (%) [G] |
Thrombo (10E9/L) [G] |
Prothrom Time (s) [G1] |
||
0.0 mg/kg |
Mean |
7.872 |
9.20 |
0.4544 |
57.81 |
1.170 |
20.25 |
2.570 |
961.8 |
19.44 |
|
SD |
0.454 |
0.41 |
0.0238 |
3.31 |
0.057 |
0.21 |
1.367 |
73.3 |
0.71 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
0.2 mg/kg |
Mean |
7.505 |
9.03 |
0.4440 |
59.16 |
1.203 |
20.33 |
3.230 |
830.5 |
19.80 |
|
SD |
0.147 |
0.22 |
0.0146 |
1.34 |
0.021 |
0.26 |
0.478 |
122.9 |
0.22 |
|
N |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
2.0 mg/kg |
Mean |
8.310 |
9.80* |
0.4804 |
57.81 |
1.180 |
20.41 |
2.856 |
856.0 |
19.30 |
|
SD |
0.267 |
0.20 |
0.0191 |
1.32 |
0.022 |
0.40 |
0.371 |
90.3 |
1.13 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
10.0 mg/kg |
Mean |
7.255n |
9.45n |
0.4840n |
66.80n |
1.306n |
19.55n |
3.310n |
701.5n |
19.65n |
|
SD |
0.983 |
0.92 |
0.0566 |
1.25 |
0.050 |
0.39 |
0.311 |
4.9 |
1.63 |
|
N |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
[G]
- Ancova/Anova & Dunnett: * = p < 0.05; n - Inappropriate for statistics
[G1] - Kruskal-Wallis & Dunnett on Ranks: n - Inappropriate for
statistics
Table 15. Total and differential white blood cell counts -Day: 31 Relative to Start Date
Sex: Male |
|
|
|
|
|
|
|
|
|
|
|
|
WBC [G] |
Lympho (10E9/L) [G] |
Neutro Absolute (10E9/L) [G] |
Eosino (10E9/L) [G] |
Baso (10E9/L) [G1] |
Mono Absolute (10E9/L) [G2] |
Lympho (%) [G] |
Neutro phils (%) [G] |
Eosino phils (%) [G] |
Baso phils (%) [G1] |
Mono cytes (%) [G] |
||
0.0 mg/kg |
Mean |
6.54 |
5.00 |
1.25 |
0.115 |
0.015 |
0.125 |
76.36 |
19.40 |
1.70 |
0.22 |
1.90 |
|
SD |
1.97 |
1.63 |
0.44 |
0.053 |
0.009 |
0.047 |
6.81 |
6.33 |
0.52 |
0.08 |
0.22 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
0.2 mg/kg |
Mean |
6.22 |
4.74 |
1.22 |
0.098 |
0.014 |
0.111 |
76.24 |
19.60 |
1.62 |
0.22 |
1.78 |
|
SD |
1.33 |
1.00 |
0.31 |
0.031 |
0.004 |
0.033 |
2.04 |
1.50 |
0.58 |
0.04 |
0.40 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
2.0 mg/kg |
Mean |
6.28 |
4.79 |
1.22 |
0.114 |
0.013 |
0.108 |
76.06 |
19.84 |
1.80 |
0.20 |
1.66 |
|
SD |
2.11 |
1.70 |
0.36 |
0.043 |
0.009 |
0.056 |
4.05 |
3.89 |
0.31 |
0.07 |
0.27 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
10.0 mg/kg |
Mean |
3.42* |
2.29* |
0.96 |
0.042* |
0.010 |
0.107 |
68.12 |
26.78 |
1.32 |
0.24 |
3.12** |
|
SD |
1.26 |
0.72 |
0.59 |
0.012 |
0.012 |
0.043 |
8.83 |
8.71 |
0.43 |
0.22 |
0.19 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
[G] - Ancova/Anova & Dunnett: * = p < 0.05; ** = p < 0.01
[G1 ]- Kruskal-Wallis & Dunnett on Ranks
[G2] -Ancova/Anova & Dunnett(Log)
Table 16. Total and differential white blood cell counts - Day: 14 Relative to Littering (Litter: A)
Sex: Female |
|
|
|
|
|
|
|
|
|
|
|
|
WBC [G] |
Lympho (10E9/L) [G] |
Neutro Absolute (10E9/L) [G] |
Eosino (10E9/L) [G] |
Baso (10E9/L) [G1] |
Mono Absolute (10E9/L) [G] |
Lympho (%) [G] |
Neutro phils (%) [G] |
Eosino phils (%) [G2] |
Baso phils (%) [G1] |
Mono cytes (%) [G] |
||
0.0 mg/kg |
Mean |
8.46 |
3.79 |
4.22 |
0.073 |
0.012 |
0.325 |
44.16 |
50.46 |
0.86 |
0.14 |
3.84 |
|
SD |
0.98 |
1.01 |
0.40 |
0.014 |
0.008 |
0.056 |
7.64 |
7.50 |
0.13 |
0.09 |
0.53 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
0.2 mg/kg |
Mean |
6.43 |
2.81 |
3.30 |
0.059 |
0.009 |
0.212 |
44.28 |
50.65 |
0.98 |
0.13 |
3.38 |
|
SD |
2.31 |
1.04 |
1.28 |
0.044 |
0.007 |
0.097 |
6.77 |
7.62 |
0.78 |
0.05 |
1.16 |
|
N |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
2.0 mg/kg |
Mean |
5.76 |
2.32 |
3.07 |
0.071 |
0.006 |
0.245 |
39.84 |
53.70 |
1.24 |
0.10 |
4.26 |
|
SD |
2.37 |
1.00 |
1.24 |
0.029 |
0.004 |
0.125 |
3.35 |
4.03 |
0.34 |
0.07 |
1.00 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
10.0 mg/kg |
Mean |
4.60n |
1.89n |
2.33n |
0.205n |
0.006n |
0.140n |
35.30n |
54.85n |
5.85n |
0.15n |
3.30n |
|
SD |
2.40 |
1.87 |
0.59 |
0.103 |
0.000 |
0.034 |
22.20 |
15.77 |
5.30 |
0.07 |
0.99 |
|
N |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
[G] - Ancova/Anova & Dunnett: n - Inappropriate for statistics
[G1] - Kruskal-Wallis & Dunnett on Ranks: n - Inappropriate for statistic
[G2] - Ancova/Anova & Dunnett(Log): n - Inappropriate for statistics
Table 17. Clinical chemistry -Day: 31 Relative to Start Date
Sex: Male |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ALP [G] |
ASAT [G1] |
ALAT [G] |
GGT [G] |
Bilirub (umol/L) [G] |
Creatin (umol/L) [G1] |
Bile (umol/L) [G] |
Total (g/L) [G] |
Albumin [G1] |
Albumin/ [G] |
Glucose (mmol/L) [G] |
Cholest (mmol/L) [G] |
Triglyc (mmol/L) [G2] |
Urea (mmol/L) [G] |
PO4 (mmol/L) [G] |
Ca (mmol/L) [G] |
Cl (mmol/L) [G] |
K (mmol/L) [G] |
Na (mmol/L) [G] |
T4 [G] |
||
0.0 mg/kg |
Mean |
79.2 |
63.0 |
51.8 |
9.20 |
1.14 |
42.6 |
12.28 |
65.8 |
12.6 |
0.237 |
7.682 |
1.812 |
0.600 |
5.32 |
2.744 |
2.850 |
105.4 |
5.76 |
142.8 |
451.03 |
|
SD |
9.5 |
7.2 |
9.6 |
2.17 |
0.32 |
0.9 |
8.46 |
1.3 |
0.9 |
0.023 |
1.360 |
0.287 |
0.199 |
0.94 |
0.358 |
0.093 |
1.1 |
0.84 |
1.3 |
147.38 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
0.2 mg/kg |
Mean |
103.2 |
68.2 |
51.8 |
11.40 |
1.04 |
41.2 |
18.22 |
64.6 |
12.4 |
0.238 |
7.290 |
1.600 |
0.824 |
5.08 |
2.384 |
2.762 |
105.4 |
5.54 |
142.8 |
451.59 |
|
SD |
23.0 |
9.7 |
12.0 |
1.95 |
0.40 |
1.5 |
24.05 |
1.5 |
1.3 |
0.028 |
0.904 |
0.060 |
0.487 |
0.43 |
0.235 |
0.026 |
1.1 |
0.33 |
1.3 |
164.97 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
2.0 mg/kg |
Mean |
88.6 |
73.8 |
46.6 |
9.80 |
1.34 |
41.2 |
30.42 |
65.4 |
12.6 |
0.239 |
7.346 |
1.476 |
0.658 |
6.00 |
2.580 |
2.868 |
105.6 |
5.84 |
143.2 |
356.25 |
|
SD |
12.7 |
6.9 |
12.2 |
3.27 |
0.57 |
4.0 |
15.78 |
3.7 |
0.9 |
0.010 |
0.817 |
0.287 |
0.098 |
0.54 |
0.174 |
0.069 |
0.5 |
0.53 |
1.6 |
112.48 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
10.0 mg/kg |
Mean |
81.0 |
215.6** |
61.0 |
8.40 |
0.98 |
46.8 |
10.04 |
60.2** |
10.6* |
0.214 |
5.252** |
1.482 |
0.346 |
8.06** |
2.396 |
2.716* |
110.6** |
5.44 |
145.0* |
380.35 |
|
SD |
16.2 |
67.9 |
25.4 |
2.07 |
0.35 |
6.0 |
9.49 |
0.8 |
0.5 |
0.013 |
0.730 |
0.225 |
0.096 |
1.18 |
0.318 |
0.062 |
1.5 |
0.38 |
0.7 |
109.83 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
10 |
The bromocresol polychromatic endpoint kit, used by the Siemens Dimension Clinical Chemistry system for the detection of albumin, has a lower response for rat albumin than for human albumin. Calibration curves in the physiological range for rat albumin showed that the signal for rat albumin was approximately one third of the signal obtained with human QC samples (Triskelion validation report V 21229/10, 2018). Hence, the true plasma albumin concentrations in this rat study were about three times higher than the values shown in this table, and the A/G ratio reported is lower than the actual value.
[G] - Ancova/Anova & Dunnett: * = p < 0.05; ** = p < 0.01
[G1] - Kruskal-Wallis & Dunnett on Ranks: * = p < 0.05; ** = p < 0.01
[G2] - Ancova/Anova & Dunnett(Log)
Table 18. Clinical chemistry -Day: 14 Relative to Littering (Litter: A)
Sex: Female |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
ALP [G] |
ASAT [G1] |
ALAT [G] |
GGT [G] |
Bilirub (umol/L) [G] |
Creatin (umol/L) [G2] |
Bile (umol/L) [G] |
Total (g/L) [G] |
Albumin [G] |
Albumin/ [G] |
Glucose (mmol/L) [G] |
Cholest (mmol/L) [G] |
Triglyc (mmol/L) [G2] |
Urea (mmol/L) [G] |
PO4 (mmol/L) [G] |
Ca (mmol/L) [G] |
Cl (mmol/L) [G] |
K (mmol/L) [G] |
Na (mmol/L) [G] |
||
0.0 mg/kg |
Mean |
97.2 |
95.6 |
52.8 |
13.60 |
0.92 |
45.0 |
36.03 |
61.6 |
10.8 |
0.213 |
7.454 |
2.084 |
1.766 |
8.48 |
3.792 |
2.754 |
99.4 |
4.98 |
143.8 |
|
SD |
30.6 |
7.3 |
11.5 |
2.51 |
0.41 |
3.3 |
23.07 |
2.1 |
1.3 |
0.025 |
0.516 |
0.407 |
0.925 |
1.38 |
0.496 |
0.101 |
1.5 |
0.25 |
1.3 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
4 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
0.2 mg/kg |
Mean |
97.2 |
102.2 |
57.2 |
13.20 |
1.60 |
47.2 |
24.18 |
58.4 |
11.0 |
0.231 |
7.560 |
1.938 |
1.266 |
9.26 |
3.750 |
2.676 |
99.4 |
4.90 |
143.8 |
|
SD |
13.4 |
18.2 |
15.1 |
2.17 |
0.81 |
1.3 |
26.71 |
3.5 |
1.6 |
0.024 |
0.812 |
0.280 |
0.277 |
0.77 |
0.422 |
0.059 |
1.8 |
0.19 |
2.5 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
4 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
4 |
5 |
5 |
5 |
5 |
2.0 mg/kg |
Mean |
92.0 |
133.5 |
67.5 |
12.50 |
1.38 |
52.0 |
17.58 |
61.5 |
11.0 |
0.218 |
7.225 |
1.958 |
1.648 |
9.43 |
3.443 |
2.740 |
99.3 |
5.05 |
142.0 |
|
SD |
31.7 |
35.2 |
12.7 |
1.29 |
0.65 |
7.2 |
14.66 |
2.1 |
0.8 |
0.016 |
1.260 |
0.494 |
0.523 |
1.48 |
0.101 |
0.056 |
1.0 |
0.37 |
2.7 |
|
N |
4 |
4 |
4 |
4 |
4 |
3 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
4 |
3 |
4 |
4 |
4 |
10.0 mg/kg |
Mean |
57.0n |
239.0n |
39.0n |
12.00n |
1.40n |
48.0n |
1.80n |
62.0n |
11.0n |
0.216n |
5.650n |
1.900n |
0.630n |
13.30n |
3.460n |
2.870n |
107.0n |
5.70n |
147.0n |
|
|
SD- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
SD- |
- |
- |
- |
- |
- |
- |
- |
- |
|
N |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
The bromocresol polychromatic endpoint kit, used by the Siemens Dimension Clinical Chemistry system for the detection of albumin, has a lower response for rat albumin than for human albumin. Calibration curves in the physiological range for rat albumin showed that the signal for rat albumin was approximately one third of the signal obtained with human QC samples (Triskelion validation report V 21229/10, 2018). Hence, the true plasma albumin concentrations in this rat study were about three times higher than the values shown in this table, and the A/G ratio reported is lower than the actual value.
[G] - Ancova/Anova & Dunnett: n - Inappropriate for statistics
[G1] - Kruskal-Wallis & Dunnett on Ranks: n - Inappropriate for statistics
[G2] - Ancova/Anova & Dunnett(Log): n - Inappropriate for statistics
Table 19. Absolute organ weights -Day(s): 31 Relative to Start Date
Sex: Male |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Terminal bw (g) [G] |
Brain [G] |
Heart [G1] |
Adrenals [G] |
Kidneys [G] |
Liver [G] |
Spleen [G] |
Thymus [G] |
Thyroid [G1] |
Testes [G] |
Epididy (g) [G] |
Prostate [G] |
Seminal (g) [G] |
LABC (g) [G] |
Cowpers (g) [G] |
Glans Penis (g) [G2] |
||
0.0 mg/kg |
Mean |
365.67 |
2.080 |
1.002 |
0.0586 |
2.160 |
8.242 |
0.5774 |
0.2568 |
0.0160 |
3.648 |
1.218 |
1.054 |
1.283 |
1.0848 |
0.1086 |
0.1268 |
|
SD |
16.21 |
0.089 |
0.058 |
0.0088 |
0.142 |
0.619 |
0.0854 |
0.0326 |
0.0051 |
0.269 |
0.136 |
0.147 |
0.230 |
0.1339 |
0.0228 |
0.0251 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
357.54 |
2.068 |
1.014 |
0.0532 |
2.012 |
8.368 |
0.5824 |
0.2870 |
0.0168 |
3.488 |
1.170 |
0.990 |
1.412 |
1.0198 |
0.1128 |
0.1168 |
|
SD |
16.20 |
0.061 |
0.084 |
0.0052 |
0.094 |
0.688 |
0.0272 |
0.0753 |
0.0034 |
0.282 |
0.090 |
0.190 |
0.225 |
0.0914 |
0.0157 |
0.0167 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
2.0 mg/kg |
Mean |
361.52 |
2.104 |
1.206** |
0.0600 |
2.204 |
8.744 |
0.6282 |
0.2856 |
0.0176 |
3.567 |
1.203 |
0.963 |
1.323 |
1.0993 |
0.1161 |
0.1203 |
|
SD |
15.79 |
0.080 |
0.068 |
0.0115 |
0.059 |
0.765 |
0.0581 |
0.0477 |
0.0069 |
0.242 |
0.098 |
0.167 |
0.211 |
0.1526 |
0.0221 |
0.0290 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
336.98** |
2.028 |
1.410** |
0.0560 |
1.938* |
9.626* |
0.5778 |
0.2760 |
0.0162 |
3.514 |
1.073** |
0.655** |
0.886** |
0.9769 |
0.1039 |
0.1207 |
|
SD |
19.59 |
0.044 |
0.173 |
0.0070 |
0.131 |
0.936 |
0.0880 |
0.1033 |
0.0036 |
0.251 |
0.064 |
0.098 |
0.187 |
0.1106 |
0.0319 |
0.0287 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
[G]
- Ancova/Anova & Dunnett: * = p < 0.05; ** = p < 0.01
[G1] - Ancova/Anova & Dunnett(Log): ** = p < 0.01
[G2] - Kruskal-Wallis & Dunnett on Ranks
Table 20. Absolute organ weights -Day(s): 14 Relative to Littering (Litter: A)
Sex: Female |
|
|
|
|
|
|
|
|
|
|
|
|
Terminal bw (g) [G] |
Brain [G] |
Heart [G] |
Adrenals [G1] |
Kidneys [G1] |
Liver [G] |
Spleen [G1] |
Thymus [G2] |
Thyroid [G] |
Ovaries [G] |
Uterus [G] |
||
0.0 mg/kg |
Mean |
255.28 |
1.962 |
0.882 |
0.0736 |
1.588 |
8.788 |
0.5362 |
0.1724 |
0.0168 |
0.0806 |
0.4788 |
|
SD |
12.94 |
0.087 |
0.046 |
0.0073 |
0.107 |
0.952 |
0.0247 |
0.0262 |
0.0045 |
0.0107 |
0.0564 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
252.33 |
1.952 |
0.814 |
0.0726 |
1.628 |
8.718 |
0.5348 |
0.1606 |
0.0146 |
0.0822 |
0.5472 |
|
SD |
8.49 |
0.101 |
0.090 |
0.0062 |
0.083 |
0.255 |
0.0514 |
0.0155 |
0.0021 |
0.0095 |
0.0931 |
|
N |
10 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
254.19 |
1.944 |
0.936 |
0.0956 |
1.634 |
9.294 |
0.5200 |
0.2192 |
0.0159 |
0.0863 |
0.5176 |
|
SD |
12.10 |
0.102 |
0.112 |
0.0264 |
0.231 |
1.214 |
0.1234 |
0.0853 |
0.0035 |
0.0147 |
0.0888 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
244.65n |
1.905n |
1.810n |
0.0925n |
1.755n |
9.845n |
0.4515n |
0.2920n |
0.0150n |
0.1225n |
0.7050n |
|
SD |
9.40 |
0.064 |
0.099 |
0.0007 |
0.049 |
0.163 |
0.0375 |
0.0537 |
0.0071 |
0.0290 |
0.3196 |
|
N |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
[[G] - Ancova/Anova & Dunnett: n - Inappropriate for statistics
[G1] - Kruskal-Wallis & Dunnett on Ranks: n - Inappropriate for statistics
[G2]
- Ancova/Anova & Dunnett(Log): n - Inappropriate for statistics
Litter: A = First litter
Table 21. Relative organ weights -Day(s): 31 Relative to Start Date
Sex: Male |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Terminal bw (g) [G] |
Brain (g/kg bw) |
Heart rel.wgt (g/kg bw) [G] |
Adrenals (g/kg bw) [G] |
Kidneys (g/kg bw) [G] |
Liver (g/kg bw) [G] |
Spleen (g/kg bw) [G] |
Thymus (g/kg bw) [G] |
Thyroid (g/kg bw) [G1] |
Testes (g/kg bw) |
Epididy rel.wgt (g/kg bw) [G] |
Prostate (g/kg bw) [G] |
Sem ves (g/kg bw) [G] |
LABC Muscle rel.wgt (g/kg bw) [G] |
Cowpers Gl. rel.wgt (g/kg bw) [G1] |
Glans Penis rel.wgt (g/kg bw) [G2] |
||
0.0 mg/kg |
Mean |
365.67 |
5.847 |
2.813 |
0.1654 |
6.073 |
23.14 |
1.622 |
0.722 |
0.0441 |
9.988 |
3.333 |
2.897 |
3.516 |
2.9661 |
0.2970 |
0.3474 |
|
SD |
16.21 |
0.291 |
0.086 |
0.0297 |
0.450 |
1.30 |
0.229 |
0.090 |
0.0153 |
0.767 |
0.375 |
0.490 |
0.637 |
0.3304 |
0.0603 |
0.0689 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
357.54 |
5.650 |
2.765 |
0.1454 |
5.491* |
22.81 |
1.590 |
0.786 |
0.0471 |
9.765 |
3.276 |
2.767 |
3.939 |
2.8568 |
0.3153 |
0.3269 |
|
SD |
16.20 |
0.301 |
0.179 |
0.0159 |
0.200 |
1.22 |
0.075 |
0.212 |
0.0103 |
0.795 |
0.267 |
0.508 |
0.542 |
0.2732 |
0.0410 |
0.0440 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
2.0 mg/kg |
Mean |
361.52 |
5.769 |
3.308* |
0.1642 |
6.044 |
24.00 |
1.722 |
0.782 |
0.0485 |
9.886 |
3.329 |
2.658 |
3.655 |
3.0330 |
0.3212 |
0.3317 |
|
SD |
15.79 |
0.185 |
0.199 |
0.0289 |
0.141 |
2.38 |
0.143 |
0.124 |
0.0180 |
0.834 |
0.232 |
0.395 |
0.521 |
0.3288 |
0.0592 |
0.0688 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
336.98** |
6.102 |
4.226** |
0.1680 |
5.814 |
28.84** |
1.728 |
0.821 |
0.0483 |
10.477 |
3.192 |
1.950** |
2.642** |
2.9071 |
0.3089 |
0.3616 |
|
SD |
19.59 |
0.429 |
0.402 |
0.0191 |
0.226 |
1.48 |
0.199 |
0.275 |
0.0126 |
1.185 |
0.222 |
0.321 |
0.600 |
0.3562 |
0.0956 |
0.0991 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
[G]
- Ancova/Anova & Dunnett: * = p < 0.05; ** = p < 0.01
[G1] - Ancova/Anova & Dunnett(Log)
[G2] - Kruskal-Wallis & Dunnett on Ranks
Table 22. Relative organ weights -Day(s): 14 Relative to Littering (Litter: A)
Sex: Female |
|
|
|
|
|
|
|
|
|
|
|
|
Terminal bw (g) [G] |
Brain (g/kg bw) |
Heart rel.wgt (g/kg bw) [G1] |
Adrenals (g/kg bw) [G1] |
Kidneys (g/kg bw) [G1] |
Liver (g/kg bw) [G1] |
Spleen (g/kg bw) [G1] |
Thymus (g/kg bw) [G] |
Thyroid (g/kg bw) [G] |
Ovaries (g/kg bw) [G] |
Uterus (g/kg bw) [G] |
||
0.0 mg/kg |
Mean |
255.28 |
7.747 |
3.487 |
0.2909 |
6.264 |
34.65 |
2.119 |
0.680 |
0.0658 |
0.3148 |
1.874 |
|
SD |
12.94 |
0.225 |
0.240 |
0.0312 |
0.189 |
2.84 |
0.111 |
0.095 |
0.0175 |
0.0308 |
0.178 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
0.2 mg/kg |
Mean |
252.33 |
7.911 |
3.303 |
0.2935 |
6.590 |
35.30 |
2.166 |
0.651 |
0.0579 |
0.3259 |
2.165 |
|
SD |
8.49 |
0.588 |
0.449 |
0.0184 |
0.316 |
1.15 |
0.217 |
0.070 |
0.0086 |
0.0379 |
0.333 |
|
N |
10 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
10 |
10 |
10 |
2.0 mg/kg |
Mean |
254.19 |
7.629 |
3.664 |
0.3740 |
6.407 |
36.58 |
2.032 |
0.847 |
0.0624 |
0.3386 |
2.033 |
|
SD |
12.10 |
0.468 |
0.344 |
0.0997 |
0.900 |
5.99 |
0.436 |
0.275 |
0.0122 |
0.0500 |
0.325 |
|
N |
12 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
12 |
12 |
12 |
10.0 mg/kg |
Mean |
244.65n |
7.797n |
7.396n |
0.3784n |
7.175n |
40.26n |
1.850n |
1.190n |
0.0619n |
0.5034n |
2.909n |
|
SD |
9.40 |
0.560 |
0.120 |
0.0174 |
0.073 |
0.88 |
0.224 |
0.174 |
0.0313 |
0.1379 |
1.418 |
|
N |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
[G] - Ancova/Anova & Dunnett: n - Inappropriate for statistics
[G1] - Kruskal-Wallis & Dunnett on Ranks: n - Inappropriate for statistics
Litter: A = First litter
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 0.2 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- System:
- musculoskeletal system
- Organ:
- heart
- other: skeletal muscle
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Combined repeated dose toxicity study with the reproduction / developmental toxicity screening test:
In this GLP compliant OECD 422 study, the effect of the test substance on general toxicity, reproductive performance and development of pups was examined in four groups of 12 male and 12 female Wistar rats. The test substance was suspended in corn oil and administered by oral gavage at 0, 0.2, 2 and 10 mg/kg body weight/day. The content, and homogeneity of the test substance in the vehicle were confirmed by analysis. The test substance was administered daily, during a pre-mating period of 2 weeks, during mating, gestation and lactation. Male animals were sacrificed after 31 days of treatment. Parental female animals were sacrificed at day 14 of lactation.
Most pregnant high-dose females, however, had to be sacrificed for humane reasons at parturition. There were no treatment-related clinical signs in males or, until parturition, in females. At parturition, one high-dose female was found dead and eight high-dose females were humanely killed because of conditional decline. Signs noted prior to their death included respiratory distress, piloerection and soiled fur/perineum. Two other pregnant high-dose rats delivered, but had litters with mainly dead pups, and showed paleness, piloerection and a lower body temperature. The results of the neurobehavioral observations and motor activity assessment did not indicate any neurotoxic potential of the test substance in rats. Mean body weights and body weight gain were reduced in high-dose males and in high-dose females during gestation. Reductions in food consumption were noted in the high-dose group in both sexes. Hematology and clinical chemistry was conducted at scheduled sacrifice in 5 males/group and in 5 dams in the control-, low- and mid-dose groups. In mid- and high-dose males, red blood cell count, haemoglobin concentration and packed cell volume were decreased, and reticulocytes were increased. Prothrombin time was increased in high-dose males. Total white blood cell, lymphocyte and eosinophil counts were decreased and the percentage of monocytes was increased in high-dose males. In high-dose males, ASAT activity and urea, chloride and sodium concentrations were increased, while total protein, albumin, glucose and calcium concentrations were decreased compared to controls. The absolute and relative weights of the heart were increased in mid- and high-dose males. The absolute and relative weights of the heart were also considerably increased in the two surviving high-dose dams. The absolute and relative weights of the liver were increased, and those of the prostate and seminal vesicles were decreased in high-dose males. In addition, the absolute weight of the epididymides was decreased in high-dose males. Macroscopic examination at scheduled necropsy showed enlarged parathymic lymphnodes in 5/12 high-dose males and in 2/3 remaining high-dose females. Enlarged parathymic lymphnodes were also noted in 6/9 high-dose females that died or were killed in moribund condition. Microscopic examination was performed on males of the high-dose group and the control group. Because the female high-dose group was terminated untimely, microscopic examination was focussed on the next lower-dose group (mid-dose females) and the controls. Organs showing treatment-related microscopic findings were also examined in the intermediate- dose group(s). The following findings were noted:
• A dose-dependent degeneration of the heart muscle in mid- and high-dose males, characterized by the presence of fibrotic areas.
• Degeneration of the skeletal muscle accompanied by necrosis and mononuclear inflammation in high-dose males. In the mid-dose group, 1/5 males showed necrosis and mononuclear inflammation of the skeletal muscle.
• Hyperemia in the liver of high-dose males and mid-dose females.
• Perivascular inflammation and accumulation of alveolar macrophages in the lungs of mid- and high-dose males and mid-dose females. In addition, the incidence of alveolitis was increased in high-dose males.
• Vacuolation in the zona fasciculata of the adrenal gland in mid- and high-dose males.
• Increased incidence of histiocytosis in the parathymic lymphnodes in males and females of the high-dose group.
Results of T4 hormone analysis in male adult animals did not show any significant effects between the groups.
Conclusions:
• Based on the effects noted in the mid- and high-dose groups, the NOAEL for parental systemic effects was placed at 0.2 mg/kg body weight/day.
Justification for classification or non-classification
The available data for subacute oral toxicity are reliable and suitable for classification purposes under Regulation 1272/2008. Based on the result of the available studies, classification for repeated oral toxicity is not warranted in accordance with EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation No. (EC) 1272/2008.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

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