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Diss Factsheets

Administrative data

Description of key information

NOEL > 300 mg/kg bw/day (rat) male/female, Maurissen et. al. (2004)

Key value for chemical safety assessment

Effect on neurotoxicity: via oral route

Link to relevant study records
Reference
Endpoint:
neurotoxicity: chronic oral
Type of information:
experimental study
Adequacy of study:
key study
Study period:
02 February 2002 - 20 February 2004
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Reason / purpose for cross-reference:
reference to same study
Qualifier:
according to guideline
Guideline:
other: EPA OPPTS 870.6200 (Neurotoxicity Screening Battery) and EPA OPPTS 870.4300 (Combined Chronic Toxicity / Carcinogenicity)
Deviations:
no
Qualifier:
according to guideline
Guideline:
other: OECD Guideline 424 (Neurotoxicity Study in Rodents) and OECD Guideline 453 (Combined Chronic Toxicity / Carcinogenicity Studies)
Deviations:
no
Qualifier:
according to guideline
Guideline:
other: EU Method Part B. (Combined Chronic Toxicity / Carcinogenicity Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
other: JMAFF, Combined Chronic Toxicity/Oncogenicity Study and Subchronic Oral Toxicity Study) 1985
Deviations:
no
GLP compliance:
yes
Limit test:
no
Species:
rat
Strain:
Fischer 344
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Age at study initiation: 6 weeks
- Housing: The animals were housed 2-3 per cage during acclimatisation and two per cage during the main study in stainless steel cages.
- Diet: Certified canine diet in meal form, provided ad libitum.
- Water: Municipal water, provided ad libitum.
- Acclimation period: Animals were acclimated to the laboratory for one week prior to the start of the study.

ENVIRONMENTAL CONDITIONS
- Temperature (° C): 22 ± 1 °C (with a maximum permissible excursion range of ± 3°C)
- Humidity (%): 40 to 70 %
- Air changes (per hr): approximately 12-15 times/hour
- Photoperiod (hrs dark / hrs light): A 12-hour light/dark photocycle was maintained for all animal rooms with lights on at 6:00 a.m. and off at 6:00 p.m.
Route of administration:
oral: feed
Vehicle:
unchanged (no vehicle)
Details on exposure:
DIET PREPARATION
Diets were prepared by serially diluting a concentrated test material- feed mixture (premix) with ground feed. Premixes were mixed periodically throughout the study based on stability data. Initial concentrations of test material in the diet were calculated from historical body weights and feed consumption data. Subsequently, the concentrations of the test material in the feed were adjusted weekly for the first 13-weeks of the study and at 4-week intervals thereafter, based upon the most recent body weight and feed consumption data.
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
- Homogeneity: The homogeneity of the low-dose female and high-dose male test material- feed mixtures were determined prior to the start of dosing and at approximately 1.5, 3, 8, 12, 18, and 24 months. Additional analytical analyses were conducted at approximately 8, 9, 14, and 20 months to verify homogeneity of the diet mixes.
- Stability: Previous 90-day toxicity study in rats (Yano and Dryzga, 2002) demonstrated that the test material was stable for at least 42 days in rodent chow at concentrations ranging from 0.005 % to 5 %. In this study, an additional stability evaluation was conducted at 0.0001 % to cover the concentration ranges of the administered diets.
- Concentration Verification: Analyses of the premix, all dose levels and the 0 (control) mg/kg bw/day diets were determined prior to the start of exposure and at approximately 1.5, 3, 8, 12, 18, and 24 months. Additional concentration analyses were also conducted at approximately 14, 18, and 20 months. The method for analysing the test material in feed was a solvent extraction method followed by analyses using liquid chromatography- mass spectrometry (LC-MS) and solvent standards incorporating an internal standard.
- Retainer Samples: Reference samples (one/sex/dose/mix) were retained and stored in sealed vials in a manner consistent with the sample retention policy of the laboratory.
Duration of treatment / exposure:
One year.
Frequency of treatment:
Daily.
Dose / conc.:
0 mg/kg bw/day
Remarks:
Basis:
nominal in diet
Dose / conc.:
0.1 mg/kg bw/day
Remarks:
Basis:
nominal in diet
Dose / conc.:
1 mg/kg bw/day
Remarks:
Basis:
nominal in diet
Dose / conc.:
75 mg/kg bw/day
Remarks:
Basis:
nominal in diet
Dose / conc.:
300 mg/kg bw/day
Remarks:
Basis:
nominal in diet
No. of animals per sex per dose:
Ten per sex per dose.
Control animals:
yes, plain diet
Details on study design:
- Dose selection rationale: Selected dose levels for the combined chronic toxicity/oncogenicity/neurotoxicity study were 0, 0.1, 1.0, 75, and 300 mg/kg bw/day, and these dose levels were approved by the USEPA. The high dose was selected based on the data from the 90-day dietary toxicity study and the limited pharmacokinetic study. Data from these studies indicated that GI absorption was saturated at an actual dose of 78-86 mg/kg bw (targeted concentration of 100 mg/kg bw) and this conclusion was supported by numerous toxicology data points, especially liver weights. The highest-dose level was selected at 300 mg/kg bw/day rather than 100 mg/kg bw/day because, although the dose was not proportional to toxicity or the AUCs, additional test material was absorbed at doses higher than 100 mg/kg bw/day.
Therefore, a conservative approach to dose level selection was to challenge the rats to this higher dose level. Treatment-related effects induced in rats given 300 mg/kg bw/day were expected to be as follows: 1) slight reduction in body weight, 2) increased liver weights, and 3) possible alterations in clinical pathology parameters. Similar effects of a lesser magnitude were expected to occur in rats given 75 mg/kg bw/day.
- Dosing route rationale: Probable routes of human exposure to the test material are via accidental ingestion during application or manufacture. Thus, administration of the test material via the diet represents an appropriate means of exposure.
- Rationale for animal assignment: Animals were stratified by pre-exposure body weight and then randomly assigned to treatment groups using a computer program.
Observations and clinical examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: A cage-side (general) clinical examination was conducted at least once a day, typically at the same time each day (usually in the morning). Moribund animals not expected to survive until the next observation periods were humanely euthanized that day. In addition, all animals were observed for morbidity, mortality, and the availability of feed and water at least twice daily.
- Cage side observations included, but not limited to: Decreased/increased activity, repetitive behaviour, vocalization, incoordination/limping, injury, neuromuscular function (convulsion, fasciculation, tremor, twitches), altered respiration, blue/pale skin and mucous membranes, severe eye injury (rupture), alterations in faecal consistency, and faecal/urinary quantity.

BODY WEIGHT: Yes
- Time schedule for examinations: Body weights were recorded prior to each FOB session.

FOOD CONSUMPTION AND COMPOUND INTAKE: Yes
- Food consumption: Feed consumption data were collected weekly during the first 13 weeks of the study and then at approximately monthly intervals thereafter for all animals. Feed containers were weighed at the start and end of a measurement cycle and consumption was calculated using the following equation:
Feed consumption (g/day) = (initial weight of feed containers - final weight of feed containers) / [(No. of days in measurement cycle)(No. of animals per cage)]
- Test material intake (TMI): TMI was calculated using test material concentrations in the feed, actual body weights (BW) and feed consumption using the following equation:
TMI = [(feed consumption) * (1000) * (% of test material in feed/100)] / {[(current BW + previous BW) / 2] / 1000}

FOOD EFFICIENCY:
Feed efficiency was calculated using body weight gain and feed consumption data from the first 13 weeks of the study using the following equation:
Feed efficiency = (g feed consumed/day) / (g body weight gain/day)

OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: The eyes of all animals were examined by a veterinarian pre-exposure and prior to the scheduled necropsy using indirect ophthalmoscopy.
- Dose groups that were examined: All dose groups were examined.
- Method: One drop of 0.5 % tropicamide ophthalmic solution was instilled in each eye to produce mydriasis prior to the indirect ophthalmic examinations. Eyes were also examined by a prosector during necropsy using a moistened glass slide pressed to the cornea.
Neurobehavioural examinations performed and frequency:
FUNCTIONAL OBSERVATIONAL BATTERY: Yes
- Parameters checked: The functional observational battery (FOB) included hand-held and open-field observations, measurements of hind- and forelimb grip performance, hind limb landing, foot splay, and rectal temperature.
> Hand-Held and Open-Field Observations:
Hand-held and open-field observations included a careful physical examination and sensory evaluation according to an established format. Open-field observations and sensory evaluations were made in a clear plastic box (50 cm x 50 cm). Observations were dictionary based, and contained most of the common physical and neurologic abnormalities seen in toxicity studies. Because not all potential observations are contained in the dictionary, free- field descriptions were also allowed.
Cage-side evaluation included: Unusual body movements (e.g. tremors, convulsions), abnormal behaviour (e.g. circling, stereotypy) and posture, and resistance to removal (a ranked observation).
> Grip Performance:
Hind limb grip performance was tested according to the procedure described by Mattsson et al. (1986). Briefly, the observer placed the animal’s forelegs on a plastic bench and the hind feet were set on a horizontal screen attached to an electronic strain gauge (Cha tillon, Greensboro, North Carolina). The observer then smoothly but firmly pulled backward on the tail until the animal’s grip on the screen was broken. An electronic strain gauge reading was used to record the animal’s resistance to the pull in grams. The average of three trials was used for statistical analysis. Forelimb grip performance was similarly tested, except that a bench was not used. The animal was placed so that the forefeet were on the screen and the hind feet were suspended approximately 10 cm above the smooth horizontal plastic surface.
Instrument Calibration: A standard 500 g weight attached to a fine gauge wire was suspended from the load cell and the resulting mass was recorded in grams. A 1 % tolerance (i.e., 500 ± 5 g) was acceptable and was checked just before and just after testing.
> Landing Foot Splay:
The landing foot splay procedure was similar to that published by Edwards and Parker (1977). A form containing the study, animal identification, and date was used to capture the data. The outer-most toe of each hind foot was marked with ink. The animal was then dropped from a height of 30 cm onto the recording sheet. This procedure was repeated three times, and the toes were re-inked as necessary before each trial. The distance from centre-to-centre of the ink marks for each trial was measured (cm), and the average of the three splay values were used for statistical analysis.
> Rectal Temperature:
Rectal temperature was measured with a rectal thermistor that was calibrated at 37 °C before and after the study. The instrument was recalibrated if the temperature recordings differed from the reference thermometer by more than ± 0.5 °C. The thermistor was placed approximately 4 cm into the rectum for about 10-15 seconds. Temperature was then recorded.

MOTOR ACTIVITY: Yes
Twenty-four motor activity chambers (also referred to as cages), visually isolated from each other, were located in a quiet, dimly lit room. Each motor activity cage consisted of a clear plastic circular alley similar to the one developed by Richelle et al. (1967) and Fontaine et al. (1966). An infrared photobeam bisected the cage so that the beam crossed the alley in two locations. Each animal was tested individually and no entry into the MA test room was allowed during the testing period. Each test session consisted of six 8 minute epochs, totalling 48 minutes of testing per animal per test session. This duration was chosen based on the results of validation studies indicating that activity counts of control animals approached asymptote within 30-40 minutes in Fischer 344 rats (Marable and Andrus, 2001). Activity counts for each epoch were recorded. Each beam break lasting more than 100 msec constituted an activity count. This minimum duration was set to discount activities such as tail-flicking, rearing, head-bobbing, etc. A positive control report for motor activity was used.
> Motor Activity Cage Calibration: Cages used for testing were calibrated prior to testing each day. Calibration was performed with a rod attached to a rotary motor that broke the infrared beam at a constant speed. The duration of each beam break was calculated to ensure equivalence across chambers.
> Motor Activity Cage Allocation: Rats were allocated to the motor activity cages such that counterbalancing of treatment groups and sexes across cages and test times was maximized.
Sacrifice and (histo)pathology:
NECROPSY/GROSS PATHOLOGY
Five randomly pre-selected rats/sex/group were evaluated for neuropathologic effects. Rats fasted and submitted alive for necropsy were given an intraperitoneal injection of 0.2 mL heparin (10,000 USP/mL) per 100 grams body weight approximately 10 minutes prior to perfusion. Rats were anesthetised by inhalation of isoflurane vapours. While under deep anaesthesia, the heart was exposed, the left ventricle cannulated, and the right atrium was incised. Rats were perfused by gravity pressure with 0.05 M phosphate buffer containing sodium nitrite followed by a phosphate-buffered fixative solution of 1.5 % glutaraldehyde – 4 % formaldehyde (c. 540 mOs).
Tissues were examined for gross pathologic alterations by a veterinary pathologist assisted by a team of trained individuals. The brain, head, spinal column with spinal cord, fore- and hind limbs, and tail were trimmed to remove excessive skin and muscle; muscles from the hind limbs were reflected to further expose the nerves. All tissues were immersed in the glutaraldehyde/formaldehyde fixative. Transponders were removed and placed in jars with tissues.
In addition, thoracic and abdominal viscera were collected and preserved in the glutaraldehyde/formaldehyde fixative. These tissues were disposed of after the issuance of this report as it was determined that their retention or further examination were not warranted.

HISTOPATHOLOGY
Tissues for neuropathologic evaluation were prepared from all rats in the control and high-dose groups. Nine cross-sections of the brain were prepared to include the following regions: olfactory bulb, cerebrum (frontal, parietal, temporal and occipital areas), thalamus/hypothalamus, midbrain, pons, cerebellum, and medulla oblongata. In addition, sections were prepared from the trigeminal ganglion and nerve, pituitary gland, eyes with optic nerves, spinal cord (cervical and lumbar), olfactory epithelium, and skeletal muscles (gastrocnemius and anterior tibial). These tissues were processed by standard histologic procedures, embedded in paraffin, sectioned approximately six µm thick and stained with hematoxylin and eosin. Spinal nerve roots (cervical and lumbar), dorsal root ganglia (cervical and lumbar), and peripheral nerves (sciatic, tibial [proximal and distal - at the knee and calf muscle branches] and sural) were osmicated, embedded in epoxy resin, sectioned approximately 2-3 µm thick and stained with toluidine blue.
Tissues were evaluated by a veterinary pathologist using a light microscope. Histopathologic findings were subjectively graded as appropriate to assess the potential effects of treatment with the test material with regard to the contribution of a specific lesion to the health status of an animal. Very slight and slight grades were used for conditions present in excess of the normal textbook appearance of an organ/tissue, but were of minimal severity and were not expected to significantly affect the function of the specific organ/tissue involved nor have a significant effect on the overall health of the animal. Lesions of these severities involved only a minor portion of the affected organ and the two grades were differentiated based upon the frequency that the change was noted.
Lesions of moderate severity involved up to 30 % of the parenchyma and may have had an effect upon the function of the organ but not to the extent that it was considered likely to result in clinical manifestations of disease. Categories of severe or very severe were available for potential use for lesions of greater severity.
Statistics:
Data interpretation was guided by the following statement of the ICH Harmonized Tripartite Guideline (European Community, Japan, U.S.A.): "Significance tests (inferential statistics) can be used only as a support for the interpretation of results. The interpretation itself must be based on biological plausibility. It is unwise to assume that a difference from control values is not biologically relevant simply because it is not ‘statistically significant.’ To a lesser extent it can be unwise to assume that a ‘statistically significant’ difference must be biologically relevant" (ICH, 1993).
See "Any other information on materials and methods incl. tables" for details on the statistical analysis employed in this study.
Clinical signs:
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Mortality:
no mortality observed
Description (incidence):
No treatment related effects in the neurotoxicity subgroup.
Body weight and weight changes:
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Food consumption and compound intake (if feeding study):
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Food efficiency:
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Clinical biochemistry findings:
not examined
Behaviour (functional findings):
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Gross pathological findings:
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Neuropathological findings:
no effects observed
Description (incidence and severity):
No treatment related effects in the neurotoxicity subgroup.
Other effects:
not examined
Details on results:
BODY WEIGHT AND WEIGHT GAIN
The analysis revealed a statistically significant Treatment x Time interaction (p = 0.0304), i.e., with male and female data considered together, treatment affected body weight across time points. The Treatment x Time x Sex interaction was also significant (p = 0.0406), i.e. there was a statistically significant difference in body weights across time points and/or sexes. The analysis was then conducted separately for males and females. The Treatment x Time interaction was not significant for males (p = 0.1010), but was significant for females (p = 0.0221), which suggests that the difference among treatment groups for the females was what caused the significant Treatment x Time x Sex interaction. The results of the subsequent linear contrasts for females across all time points were as follows: control vs. 0.1 mg/kg bw/day (p = 0.0524), control vs. 1 mg/kg bw/day (p = 0.0810), control vs. 75 mg/kg bw/day (p = 0.2108), and control vs. 300 mg/kg bw/day (p = 0.6210). None of the comparisons were significant at alpha = 0.02, which indicated that treated females at all dose levels did not differ from control females at any time point. Upon inspection of the data, the greatest difference in body weight compared to control values was an increase in body weight of females given 1 mg/kg bw/day after 12 months of exposure, which does not suggest a dose response relationship. Furthermore, the p values for the linear contrasts suggested that the majority of the significance in the Treatment x Time interaction for the females came from the lowest two dose groups.
The analysis and the data do not suggest a treatment effect in either sex for the neurotoxicity subgroup. However, statistically significant differences in body weights were seen in rats treated with 75 or 300 mg/kg bw/day after 12 months of exposure to the test material (males: 3.5 and 3.7 %; and females: 4.0 and 6.0 % less than control; respectively) when all study animals were considered (n = 65/sex/group; Yano et al., 2004).

FOOD CONSUMPTION AND COMPOUND INTAKE (IF FEEDING STUDY)
- Test Material Intake: Test material intake (TMI) data are found in Yano et al. (2004). The TMI was consistent with the targeted concentrations for all dose levels over the course of the study. The actual calculated TMI over the first year of the study, for all 65 animals/sex/group (75 animals/sex for the first 90 days at 1.0 mg/kg bw/day), was 0.102, 1.02, 76.6, and 307 mg/kg bw/day and was 0.100, 1.00, 75.4, and 302 mg/kg bw/day for males and females, respectively.

OPHTHALMOLOGY
No observations were made on any animal at pre-exposure, except for one male assigned to the 300 mg/kg bw/day group that had incomplete dilation of the pupil. Pre-terminal observations included a variety of non-specific, iatrogenic, and common spontaneous lesions that were not dose-dependent. Overall, there were no changes in ophthalmic parameters that could be attributed to treatment.

NEUROBEHAVIOUR
- Functional Observation Battery (FOB)
> Hand-Held and Open-Field Observations
Within the scored FOB observations, sixteen average ranks differed from controls by 0.5 or greater. These sixteen values occurred at the 300, 75, 1, and 0.1 mg/kg bw/day groups, and three observations were significantly different from control (p < 0.02). Additionally, one observation was statistically identified, but did not differ from control based on the criterion for the average ranks.
Overall, the scored observations identified by either statistical significance and/or meeting the 0.5 average rank criterion were more concentrated in males than females (14/17). During the open-field activity, decreases in the level of defecation, and increases and decreases in the level of urination were observed primarily for the males and occurred sporadically across time points and dose levels.The fluctuation in the amount of urine and faeces voided during the open-field activity was not attributed to treatment, but rather the high variability of the measurement between animals. Additionally, an increased level of open-field activity was statistically identified in males given 1 mg/kg bw/day at months 1 and 3. This finding could not be attributed to treatment as it was exclusive to one dose group and was not dose-responsive. Also, an increase in the level of activity in middle-low dose males (or any other dose group) was not supported by the motor activity data collected at any time point (see the following section: “Motor Activity”).
For categorical (non-scored) observations, incidences of red periocular soiling were observed randomly across all dose groups for females following 3 months of exposure. The incidence of these observations was slightly higher following 9 months and throughout the remainder of the study, but it occurred randomly across dose groups and was not attributed to treatment. Additionally, sporadic incidences of perineal urine soiling were present for both sexes at months 3 and 6. A slight increase in perineal urine soiling occurred in males at month 9 and females at month 12 in the 75 mg/kg bw/day dose level only. Due to the lack of a dose response, this slight increase in urine soiling was not attributed to treatment. Other categorical observations were sporadic and not considered treatment-related.

> Summary of Hand-Held and Open-Field Observations
For scored FOB observations, there were no observations that could be reliably attributed to treatment. Similarly, for categorical FOB observations, there were no findings related to treatment.

> Grip Performance
The Treatment x Time x Sex interaction was not significant (p = 0.1649 and p = 0.7617 for hind limb and forelimb grip performance, respectively), i.e., there was no statistically significant difference in grip performance across time points and/or sexes. Furthermore, the analysis also revealed no statistically significant Treatment x Time interaction (p = 0.0831 and p = 0.5574 for hind- and forelimb, respectively), i.e., with male and female data considered together, treatment did not affect grip performance across time points. Upon examination of the data, hind limb grip performance in females given the test material at 0.1 mg/kg bw/day appears to be decreased at the 12- month time-point. This was interpreted to be a spurious finding, as there was no dose- response relationship.

> Landing Foot Splay
The analysis revealed no statistically significant Treatment x Time interaction (p = 0.9402), i.e., with male and female data considered together, treatment did not affect landing foot splay across time points. However, the Treatment x Time x Sex interaction was significant (p = 0.0047), i.e., there was a statistically significant difference in landing foot splay across time points and/or sexes with treatment. This significant interaction was thought to be due to the sex difference in the pattern of landing foot splay data across time points. The trend for the males appears to be linear with an increase in splay over time. For females, however, there was a biphasic trend resulting in a decrease after baseline followed by an increase across the remaining time points. The analysis was then conducted separately for males and females. The Treatment x Time interaction was not significant for males (p = 0.2921), but was significant for females (p = 0.0468), which suggests that the difference among treatment groups for the females was what caused the significant Treatment x Time x Sex interaction.
The results of the subsequent linear contrasts for females across all time points are as follows: control vs. 0.1 mg/kg bw/day (p = 0.1345), control vs. 1 mg/kg bw/day (p = 0.5248), control vs. 75 mg/kg bw/day (p = 0.0601), and control vs. 300 mg/kg bw/day (p = 0.0430).
None of the comparisons were significant at alpha = 0.02, which indicated that treated females at all dose levels did not differ from control females at any time point. Upon inspection of the data, however, landing foot splay of the high-dose females was 9.9 % less compared to the control females after 12 months of treatment. The following arguments provide support for and against a treatment-related effect on hind limb grip performance in high-dose females.
Evidence supporting a treatment-related effect:
1. Prior to treatment, the average landing foot splay for the high-dose females was 6 % greater than the average of the control group. Following treatment, the average landing foot splay for the high-dose females was 9.9 % less than the average of the control group.
2. The decrease for landing foot splay for females at month 12 appears to be dose-dependent (however, an apparent dose-response could also be seen under baseline conditions).
3. The historical control data of three studies (including the present one) show average control values of 6.1, 6.38 and 6.28 cm in females, whereas the mean splay (5.66 cm) in high-dose females from this study falls below these average historical control values.
Evidence against a treatment-related effect:
1. Under baseline conditions (i.e., before treatment), the between-group variation for females reached 10.7 % when the different groups were compared pre-treatment. The 9.9 % difference seen between females of the control and high-dose groups after 12 months of treatment falls below the normal biological variation seen before treatment.
2. The ratio between female low-dose group and control at month 9 (0.88) was of the same order as the ratio between female high-dose group and control at month 12 (0.90).
3. The mean high-dose landing foot splay at 12 months was 5.66 cm in the present study. The historical control data of three studies (including the present one) show that 5.66 falls within the range of the minimum and maximum values (4.9 and 7.6 cm) recorded for landing foot splay.
4. There were no differences in the FOB either for extensor thrust or gait that would support the presence of an effect in the hind limbs.
5. There were no histopathologic alterations in either the
- central nervous, or
- peripheral nervous, or
- musculoskeletal systems
that were attributable to treatment or that would suggest the presence of an effect on hind limbs.
6. Landing foot splay was less than control in females only (at one time point for high-dose females) whereas no convincing evidence of differential neurotoxic response has been encountered.
7. The difference between the control and high-dose groups was not statistically significant at the alpha predefined in the protocol.
Based on the evidence provided, the decrease in hind limb landing foot splay seen for females given 300 mg/kg bw/day for 12 months does not appear to be a treatment effect.

> Rectal Temperature
The Treatment x Time x Sex interaction was not significant (p = 0.9834), i.e., there was no statistically significant difference in rectal temperature across time points and/or sexes with treatment. Furthermore, the analysis also revealed no statistically significant Treatment x Time interaction (p = 0.7753), i.e., with male and female data considered together, treatment did not affect rectal temperature across time points.

- Motor Activity
The Treatment x Time x Sex interaction was not significant (p = 0.4870), i.e., there was no statistically significant difference in motor activity across time points and/or sexes with treatment. Furthermore, the analysis also revealed no statistically significant Treatment x Time interaction (p = 0.0711), i.e., with male and female data considered together, treatment did not affect motor activity across time points. The triple interaction of Treatment x Time x Epoch was not statistically significant (p = 0.4405), indicating that the distribution of motor activity counts within each session was not significantly affected by treatment.
Following one month of treatment, however, there appeared to be a decrease in motor activity for males in a dose responsive manner. In response to these data, an additional motor activity session was conducted at approximately two months of exposure for males only. An analysis (repeated-measure ANOVA) of the month two male motor activity session was conducted. There was no significant main effect of Treatment (p = 0.2041), i.e., treatment did not affect motor activity in males after two months of treatment. Furthermore, the interaction of Treatment x Epoch was not statistically significant (p = 0.9753), indicating that the distribution of motor activity counts within each session was not significantly affected by treatment. The apparent dose responsive decrease in male motor activity was no longer present, and the decrease seen at month one was determined not to be treatment related, but due to random variation between the groups.

GROSS PATHOLOGY
There were no observations made at necropsy that were attributed to the ingestion of the test material. All visible lesions involved only a single rat from a dose group or the control group (and often only a single rat from the entire study) and there was no apparent tendency for rats given the high-dose level to have these isolated observations. All were interpreted to be spontaneous findings unassociated with dietary exposure to the test material and were considered typical of spontaneous changes commonly found in Fischer 344 rats of this age and husbandry conditions.

HISTOPATHOLOGY
There were no treatment-related histopathologic observations in the central or peripheral nervous systems, and in the muculoskeletal system of rats administered the test material. Although diagnoses were made in one or more sites for all rats, including controls, all primary neuropathologic lesions were of minor severity and were generally graded as very slight in degree, with a few graded as slight or moderate. All histopathologic observations were interpreted to be spontaneous findings, unassociated with dietary administration of the test material.
The most common nervous system lesions consisted of 1) degeneration of individual nerve fibers and 2) axonal swellings. Degeneration of individual nerve fibers was noted at various sites in the central and peripheral nervous systems in variable numbers of rats from the control and treatment groups. This was characterized by myelin ovoid formation, disruption of axons and the presence of phagocytes. In the central nervous system, a low number of glial cells were occasionally present adjacent the degenerate nerve fibers. At times, only a single fiber was affected and the lesion was termed focal, while at other times several fibers or sites were affected and the lesion was termed multifocal. These lesions were graded as very slight.
Nerve fiber degeneration was most frequently diagnosed in the trapezoid body of the medulla oblongata, tibial peripheral nerves and the cervical section of spinal cord. It was also infrequently noted in the lumbar spinal cord, cervical and lumbar spinal nerve roots or spinal nerve, and the sciatic and sural peripheral nerves. Degeneration of individual nerve fibers was also found in the trigeminal nerve. Axonal swellings were found in the nucleus gracilis of all rats. They were graded as very slight or moderate severity.
All neural lesions are considered to be spontaneous lesions that are typical of those found in Fischer 344 rats of this age (Cotard-Bartley et al., 1981; Eisenbrandt et al., 1990; Eisenbrandt and Stebbins, 1999; Fujisawa and Shiraki, 1978 and 1980; Mitsumori and Boorman, 1990; Sharma et al., 1980; Weisse, 1994).
Proliferative lesions were noted in the pars distalis or intermedia of the pituitary gland of several rats. Very slight hyperplasia was diagnosed for two control males, one given 1000 mg/kg bw/day and one control female. Adenoma of the pars distalis occurred in two control females and one female given 300 mg/kg bw/day.
Several other lesions of a non-neuropathologic nature, all of minimal severity, occurred in other organs. The most frequent of these were small foci of mineralisation, particularly of the eye, where they were found in the cornea and blood vessels in close proximity to the optic nerve, and olfactory mucosa. Other lesions noted sporadically included sinusoidal dilatation within the pars distalis of the pituitary gland and a cyst with keratinous debris in the lumbar spinal cord. These lesions were not associated with ingestion of the test material and were considered typical of spontaneous lesions found in Fischer 344 rats of this age and husbandry conditions.
In summary, there were no gross or histopathologic alterations observed in the central or peripheral nervous system tissues which were attributable to treatment with the test material at the highest-dose level.
Key result
Dose descriptor:
NOEL
Effect level:
> 300 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: No effects to suggest neurotoxic effects were observed up to the maximum dose level.
Remarks on result:
other:

Environmental Conditions

Room temperature and relative humidity were recorded daily for the duration of the study. However, on one occasion the relative humidity and temperature were not recorded. This one time occurrence did not affect the integrity of the study. The monthly average temperature and humidity of the rooms ranged from 21.8 °C to 21.9 °C and 44.4 to 51.5 % respectively. The daily temperature and relative humidity values were within the range for rats as outlined in the Guide for the Care and Use of Laboratory Animals (National Research Council, 1996).

Conclusion

Twelve months of dietary exposure up to 300 mg/kg bw/day did not affect body weight in either the male or female Fischer 344 rats assigned to the neurotoxicity subgroup (n = 10/sex/dose). However, statistically significant decreases in body weights were seen in rats treated with 75 or 300 mg/kg bw/day (males: 3.5 and 3.7 %; and females: 4.0 and 6.0 % less than control; respectively) when all study animals were considered (n = 65/sex/group; Yano et al., 2004).

For the FOB, in both scored and non-scored observations, there were no observations that were attributed to treatment. Treatment did not affect grip performance, rectal temperature, motor activity, or ophthalmic observations in either male or female rats, at any point during the study. Landing foot splay seen in females given 300 mg/kg bw/day after 12 months of exposure was 9.9 % less than control; however, this difference was not statistically significant. Furthermore, examination of the present and historical control data, the absence of any evidence of related effects (e.g., in extensor thrust, gait, and grip test) or of any neuropathological effects (central, peripheral, musculoskeletal), suggested that this difference was not a treatment effect.

There were no treatment-related gross or histopathologic observations in the central or peripheral nervous systems of rats administered the test material, and the NOEL for neuropathology was at least 300 mg/kg bw/day for both male and female Fischer 344 rats.

Conclusions:
Given the absence of neuropathologic findings in the central and peripheral nervous system, and the lack of effect on all other parameters suggestive of neurotoxicity, the chronic dietary NOEL for the test material neurotoxicity in male and female Fischer 344 rats was greater than 300 mg/kg bw/day.
Executive summary:

A one-year chronic neurotoxicity study was conducted as part of a two-year chronic toxicity/oncogenicity study to assess the effects of dietary exposure to the test material at levels of 0, 0.1, 1, 75, and 300 mg/kg bw/day in male and female Fischer 344 rats. The neurotoxicity subgroup contained 10 rats/sex/dose, and was evaluated pre-exposure, and at 1, 3, 6, 9, and 12 months of exposure using a functional observational battery (FOB), determinations of grip performance, rectal temperature, landing foot splay, and an automated test of motor activity (also conducted at 2 months for males). Following 12 months of exposure, 5 rats/sex from the control and high-dose groups were perfused, and tissues from the central and peripheral nervous system were submitted for neuropathologic examination.

No treatment related effects were seen on grip performance, rectal temperature, or motor activity at any time during the study. After 12 months of exposure to the test material, landing foot splay seen in females given 300 mg/kg bw/day was 9.9 % less than control; however, this difference was not statistically significant. Furthermore, examination of the present and historical control data, and the absence of any evidence of related effects (e.g., in extensor thrust, gait, and grip test) or of any neuropathological effects (central, peripheral, musculoskeletal), suggested that this difference was not a treatment effect.

Within the neurotoxicity subgroup, no statistically significant treatment effects were seen on body weight, though statistically significant body weight effects were seen in rats treated with 75 or 300 mg/kg bw/day (males: 3.5 and 3.7 %; and females: 4.0 and 6.0 % less than control; respectively) when all study animals (n = 65/sex/group; chronic neurotoxicity/chronic toxicity/oncogenicity) were considered after 12 months of exposure to the test material. For the scored and categorical FOB, there were no observations that could be attributed to treatment. There were no treatment-related gross or histopathologic findings in either the central or peripheral nervous system following one year of dietary exposure.

Under the conditions of the test, there were no treatment related effects on any parameter that would suggest a neurotoxic effect, and the chronic dietary NOEL for neurotoxicity in male and female Fischer 344 rats is greater than 300 mg/kg bw/day.

Endpoint conclusion
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
300 mg/kg bw/day
Study duration:
chronic
Species:
rat
Quality of whole database:
The study was conducted under GLP conditions as part of a guideline two-year chronic toxicity/oncogenicity study; the study was awarded a reliability score of 1 in line with the criteria outlined by Klimisch et al. (1997). The quality of the database is therefore considered to be high.

Effect on neurotoxicity: via inhalation route

Endpoint conclusion
Endpoint conclusion:
no study available

Effect on neurotoxicity: via dermal route

Endpoint conclusion
Endpoint conclusion:
no study available

Additional information

The study was conducted in accordance with the standardised guidelines US EPA OPPTS 870.4300, OPPTS 870.3100, OECD 453, OECD 408, EEC, Part B, 87/302/EEC, EU Method B.26 and JMAFF, Combined Chronic Toxicity/Oncogenicity Study and Subchronic Oral Toxicity Study under GLP conditions.

A one-year chronic neurotoxicity study was conducted as part of a two-year chronic toxicity/oncogenicity study to assess the effects of dietary exposure to the test material at levels of 0, 0.1, 1, 75, and 300 mg/kg bw/day in male and female Fischer 344 rats. The neurotoxicity subgroup contained 10 rats/sex/dose, and was evaluated pre-exposure, and at 1, 3, 6, 9, and 12 months of exposure using a functional observational battery (FOB), determinations of grip performance, rectal temperature, landing foot splay, and an automated test of motor activity (also conducted at 2 months for males). Following 12 months of exposure, 5 rats/sex from the control and high-dose groups were perfused, and tissues from the central and peripheral nervous system were submitted for neuropathologic examination.

No treatment related effects were seen on grip performance, rectal temperature, or motor activity at any time during the study. After 12 months of exposure to the test material, landing foot splay seen in females given 300 mg/kg bw/day was 9.9 % less than control; however, this difference was not statistically significant. Furthermore, examination of the present and historical control data, and the absence of any evidence of related effects (e.g., in extensor thrust, gait, and grip test) or of any neuropathological effects (central, peripheral, musculoskeletal), suggested that this difference was not a treatment related effect.

Within the neurotoxicity subgroup, no statistically significant treatment effects were seen on body weight, though statistically significant body weight effects were seen in rats treated with 75 or 300 mg/kg bw/day (males: 3.5 and 3.7 %; and females: 4.0 and 6.0 % less than control; respectively) when all study animals (n = 65/sex/group; chronic neurotoxicity/chronic toxicity/oncogenicity) were considered after 12 months of exposure to the test material. For the scored and categorical FOB, there were no observations that could be attributed to treatment. There were no treatment-related gross or histopathologic findings in either the central or peripheral nervous system following one year of dietary exposure.

Under the conditions of the test, there were no treatment related effects on any parameter that would suggest a neurotoxic effect, and the chronic dietary NOEL for neurotoxicity in male and female Fischer 344 rats is greater than 300 mg/kg bw/day.

Justification for selection of effect on neurotoxicity via oral route endpoint:

Only one study is available.

Justification for classification or non-classification

In accordance with the criteria for classification as defined in Annex I (Classification and Labelling Requirements for Hazardous Substances and Mixtures), Regulation (EC) No. 1272/2008 (CLP), the substance does not require classification with respect to neurotoxicity.