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EC number: 700-012-2 | CAS number: 950919-28-5
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
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- Endpoint summary
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- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Description of key information
Repeated dose 28-day Oral toxicity study in rats: NOAEL = 300 mg/kg bw/day (OECD 407, GLP, rel. 1)
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:
- From July 30 to October 05, 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- Version / remarks:
- Adopted 03 October 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.7 (Repeated Dose (28 Days) Toxicity (Oral))
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- OECD GLP (inspected on November 05 to 09 and 26 to 30, 2007/ signed on November 12, 2008)
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories UK Limited, Oxon, UK.
- Age at study initiation: 6-8 weeks
- Weight at study initiation: Males: 208-237 g, females: 149-171 g
- Housing: Animals were housed in groups of 5/sex in solid floor polypropylene cages with stainless steel mesh lids and softwood flake bedding (Datesand Ltd., Cheshire, UK).
- Diet: Pelleted diet (Rodent 2014C Teklad Global Certified Diet, Harlan Laboratories UK Limited, Oxon, UK), ad libitum
- Water: Mains drinking water, ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature: 21 ± 2 ºC
- Humidity: 55 ± 15 %
- Air changes: 15 changes/ h
- Photoperiod: 12 h dark/ 12 h light
IN-LIFE DATES: From: July 30, 2009 To: October 05, 2009. - Route of administration:
- oral: gavage
- Vehicle:
- arachis oil
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Test material was prepared at the appropriate concentrations as a solution in Arachis oil BP. Test material formulations were stable for at least 8 days and therefore prepared weekly during the treatment period and stored at 4 ºC in the dark, under nitrogen.
VEHICLE
- Concentration in vehicle: 7.5, 75 and 150 mg/mL
- Amount of vehicle (if gavage): 4 mL/kg bw/day - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- - The concentration of test material in the formulations was determined by gas chromatography (GC) using an external standard technique. Test material formulations were sampled and analysed within three days of preparation for verification of concentration.
- The results indicate that the prepared formulations were within ± 9 % of the nominal concentration. - Duration of treatment / exposure:
- 28 days
- Frequency of treatment:
- Once daily
- Dose / conc.:
- 30 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 300 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 600 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Dose levels were chosen based on the results from previous toxicity work (Study Number 0161-0687).
- Rationale for animal assignment (if not random): Animals were randomly allocated to treatment groups using a stratified bodyweight randomisation procedure and the group mean bodyweights were then determined to ensure similarity between the treatment groups. - Positive control:
- None
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS / CLINICAL OBSERVATIONS: Yes
- Time schedule: Animals were observed immediately before dosing, up to 30 minutes post dosing and 1 and 5 h after dosing during the working week. At weekends, animals were observed immediately before and after dosing and 1 h after dosing.
BODY WEIGHT: Yes
- Time schedule for examinations: Individual bodyweights were recorded on Day 1 and at weekly intervals thereafter. Bodyweights were also recorded prior to terminal kill. Due to an increase in dose level for the high dose group, bodyweights were also recorded on Day 3.
FOOD CONSUMPTION: Yes
- Food consumption was recorded for each cage group at weekly intervals throughout the study.
FOOD EFFICIENCY: Yes
- Food efficiency (group mean bodyweight gain / group mean food consumption) was calculated.
WATER CONSUMPTION: Yes
- Water intake was measured and recorded daily for each cage group.
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: Haematological investigation was performed on all animals from each test and control group at the end of the study (Day 28).
- Anaesthetic used for blood collection: No data
- Animals fasted: No
- How many animals: 5 animals/sex/dose
- Parameters examined: Haemoglobin, erythrocyte count, haematocrit, erythrocyte indices (mean corpuscular haemoglobin, mean corpuscular volume, mean corpuscular haemoglobin concentration), total leucocyte count, differential leucocyte count (neutrophils, lymphocytes, monocytes, eosinophils, basophils), platelet count, reticulocyte count, prothrombin time.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: Clinical chemistry investigation was performed on all animals from each test and control group at the end of the study (Day 28).
- Animals fasted: No
- How many animals: 5 animals/sex/dose
- Parameters examined: Urea, glucose, total protein, albumin, albumin/Globulin ratio, sodium, potassium, chloride, calcium, inorganic phosphorus, aspartate aminotransferase, alanine aminotransferase, alkaline phosphatase, creatinine, total cholesterol, total bilirubin, bile acids.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations: Prior to the start of treatment and on Days 7, 14, 21 and 27 for signs of functional/behavioural toxicity. Functional performance tests were also performed on all animals during Week 4, together with an assessment of sensory reactivity to different stimuli. Observations were carried out from approximately 2 h after dosing on each occasion.
- Dose groups that were examined: 5 animals/sex/dose
- Battery of functions tested:
a) Behavioural assessments: Gait, tremors, twitches, convulsions, bizarre/abnormal/stereotypic behaviour, salivation, pilo-erection, exophthalmia, lachrymation, hyper/hypothermia, skin colour, respiration, palpebral closure, urination, defecation, transfer arousal and tail elevation.
b) Functional performance tests: Forelimb/hindlimb grip strength, motor activity.
c) Sensory reactivity: Sensory reactivity to auditory, visual and proprioceptive stimuli.
IMMUNOLOGY: No
OTHER:
- Organ weights: Adrenals, brain, epididymides, heart, kidneys, prostate and seminal vesicles (with coagulating glands and fluid), spleen, testes, thymus, liver, thyroid/parathyroid, ovaries, uterus, cervix and pituitary (post-fixation) were removed from animals that were killed at the end of the study and were dissected free from fat and weighed before fixation. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
On completion of the dosing period, all animals were killed by intravenous overdose of sodium pentobarbitone followed by exsanguination. Animals were subjected to a full external and internal examination, and any macroscopic abnormalities were recorded.
HISTOPATHOLOGY: Yes (see Table 7.5.1/1 )
Samples of the tissues mentioned in Table 7.5.1/1 were removed from all animals and preserved in buffered 10 % formalin for microscopic analysis. - Other examinations:
- - At the end of the study, plasma from each animal was stored frozen at approximately -20 °C for thyroid hormone assessment. No treatment related effects on the pituitary-thyroid axis were identified, therefore these samples were discarded.
- A vaginal smear was taken from all females and the stage of oestrus was recorded at the end of the study. - Statistics:
- - Mean values and standard deviations of data were calculated.
- Where appropriate, quantitative data were analysed by the Provantis™ Tables and Statistics Module.
- For each variable, the most suitable transformation of the data was found, the use of possible covariates checked and the homogeneity of means were assessed using ANOVA or ANCOVA and Bartlett’s test.
- Williams test was used for parametric data and the Shirley test for nonparametric data.
- If no dose response was found, but the data showed non-homogeneity of means, the data were analysed by a stepwise Dunnett (parametric) or Steel (nonparametric) test to determine significant differences from the control group.
- If required, pair-wise tests were performed using the Student t-test (parametric) or the Mann-Whitney U test (non-parametric).
- Probability values (P) are presented as follows:
P < 0.01 **
P < 0.05 *
p ≥ 0.05 (not significant) - Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- - Hunched posture, ataxia and tiptoe gait were observed in one female treated with highest dose level on the first day of dosing. A regression in symptoms was evident on Day 2 and the dose level was increased to 600 mg/kg bw/day on Day 3 of treatment. On Day 4, the previously observed clinical signs were evident for females until Day 18, and prostration was noted for one female on Days 15, 16 and 17. Similar clinical signs were evident for high dose males following dosing from Day 4, although these were incidental and only affected one male in each case.
- Increased salivation was detected soon after dosing and on occasion, prior to dosing, up to 1 h after dosing and up to 5 h after dosing for animals of either sex treated with 600 mg/kg bw/day from Day 6 for females and from Day 8 for males. These findings were not considered to represent systemic toxicity.
- Hunched posture, abnormal gait and increased salivation were also evident in the 300 mg/kg bw/day dose group, although the incidences were not of the extent observed at the highest dose level.
- No clinical observations were detected at 30 mg/kg bw/day.
CONCUSION: Adverse effects at 600 mg/kg bw in females (ataxia, prostration and lethargy) / reversible after 18 days - Mortality:
- no mortality observed
- Description (incidence):
- No unscheduled death occurred.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- - A slight reduction in bodyweight gains was evident for animals of either sex treated with 600 mg/kg bw/day when compared to controls, with the effect extending to the male 300 mg/kg bw/day dose group, although this was not considered to represent an adverse effect.
- No adverse effects on bodyweight change were evident for females treated with 300 mg/kg bw/day or for animals of either sex treated with 30 mg/kg bw/day.
CONCUSION: Non-adverse effects - Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- CLINICAL CHEMISTRY
- Male: Males treated with 300 mg/kg bw/day showed increases in alanine aminotransferase and alkaline phosphatase levels in comparison to controls. No significant effects were detected for animals of either sex treated with the highest or
lowest dose levels. These findings were not considered to represent an adverse effect.
- Males treated with 600 mg/kg/day showed an increase in albumin/globulin ratio when compared to controls. The significance achieved was minimal (P<0.05) and in isolation, these findings were most probably attributed to one or two lower than expected control values, and were not considered to represent true effects of treatment.
- Females treated with 600 mg/kg/day showed a reduction in urea levels when compared to their concurrent controls. The significance achieved was minimal (P<0.05) and in isolation, these findings were most probably attributed to one or two lower than expected control values, and were not considered to represent true effects of treatment.
- Males treated with 300 mg/kg/day showed a reduction in blood sodium levels when compared to controls. Three males showed values lower than the normally expected ranges and one value was higher than expected. Furthermore, two control values were also higher than the normally expected ranges for this parameter. In the absence of an electrolyte imbalance, this finding was considered to have arisen incidentally and was not considered to be related to treatment.
CONCLUSION: Non-adverse effect - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- effects observed, treatment-related
- Description (incidence and severity):
- - Female: Weekly open field arena observations confirmed the clinical signs of increased salivation for one female treated with 300 mg/kg bw/day and one female treated with 600 mg/kg bw/day during Weeks 3 and 4. One female treated with 600 mg/kg bw/day also showed tiptoe gait during Week 4. These findings were not considered to represent systemic toxicity.
- No treatment-related effects were detected for males from all treatment groups or for animals of either sex treated with 30 mg/kg bw/day.
- Overall activity was reduced for animals of either sex treated with 600 mg/kg bw/day and for males treated with 300 mg/kg bw/day when compared to controls. In the absence of a similar effect observed during the asymptotic period, these reductions were considered to be attributed to a slight decline in physical health and unrelated to neurotoxicity. No such effects were evident for females treated with 300 mg/kg bw/day or for animals of either sex treated with 30 mg/kg bw/day.
- No treatment-related effects were detected in grip strength for treated animals when compared to controls.
- No treatment-related effects were detected on sensory reactivity.
CONCLUSION: non-adverse effects /reversible - Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- - Increases in absolute and relative liver weights were evident for animals of either sex treated with 600 mg/kg bw/day when compared to controls, with the effect extending into the male 300 mg/kg bw/day dose group. Hepatocyte enlargement is commonly seen in the rodent liver following the ingestion of xenobiotics and, in the absence of associated degenerative or inflammatory changes, is generally considered to be adaptive in nature.
- Females treated with 600 mg/kg/day showed an increase in absolute and relative adrenal weights when compared to controls (P<0.05), with one absolute weight value higher than the normally expected range. Females treated with 300 and 30 mg/kg/day also showed statistically significant increases in absolute and relative adrenal weights, however, a convincing dose-related response was not observed. In the absence of any histopathological adrenal changes, the increases in adrenal weights in females from all the treatment levels were not considered to be of any toxicological importance.
- Kidney weights, both absolute and relative to terminal bodyweight were higher for females treated with 600 mg/kg/day when compared to controls (P<0.05). Review of the individual data revealed two higher than expected values for absolute kidney weight in the treated group, although one value from the control group was also higher than expected. All individual values for relative kidney weights were within the normally expected ranges, and in the absence of any histopathological correlates, these increases were not considered to represent a toxicologically significant effect of treatment.
- Males treated with 30 mg/kg/day showed lower than expected kidney weights, both absolute and bodyweight relative. In the absence of a dose-related response, this finding was considered to have arisen incidentally.
- Absolute and relative thymus weights were higher for females treated with 300 or 30 mg/kg/day when compared to controls. The significance in each case was minimal and in the absence of an histopathological correlates, these effects were not considered to be of any toxicological significance.
CONCLUSION: Non-adverse effect - Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Macroscopic findings were confined to the presence of enlarged cervical lymph nodes for one female treated with 300 mg/kg bw/day. In isolation, this finding was considered to be unrelated to treatment.
CONCLUSION: non-adverse effect - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- Centrilobular hepatocyte enlargement in high dose group. These findings were considered to be adaptive effects
- Histopathological findings: neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Centrilobular hepatocyte enlargement was seen in relation to treatment for animals of either sex treated with 600 mg/kg bw/day, and for males treated with 300 mg/kg bw/day. Hepatocyte enlargement is commonly seen in the rodent liver following
the ingestion of xenobiotics and, in the absence of associated degenerative or inflammatory changes, is generally considered to be adaptive in nature.
CONCLUSION: non-adverse effects - Other effects:
- no effects observed
- Description (incidence and severity):
- No differences in stage of oestrus were detected for females from treated groups when compared to controls.
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 300 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- clinical signs
- Dose descriptor:
- NOEL
- Effect level:
- 30 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No treatment-related effects were detected for animals of either sex treated with 30 mg/kg bw/day.
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 600 mg/kg bw/day (actual dose received)
- System:
- central nervous system
- Organ:
- other: not applicable
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
- Conclusions:
- Based on the results of the study, NOAEL and NOEL were considered to be 300 and 30 mg/kg bw/day, respectively.
- Executive summary:
In a repeated dose toxicity study performed in accordance with OECD test guideline No. 407 and in compliance with GLP, test material solution in arachis oil was administered by gavage to three groups of Wistar Han™:HsdRccHan™:WIST strain rats (5/sex/dose) at dose levels of 30, 300 and 600 mg/kg bw/day for 28 consecutive days. Control rats were given the vehicle alone. The highest dose group was initially treated at a lower dose level (300 mg/kg bw/day) for the first two days of the treatment to allow animals in this dose group to acclimatise to the test material at a lower dosage before exposure to the full dosage of 600 mg/kg bw/day. This action was undertaken to reduce the risk of treatment-related deaths at the highest dose level following the effects observed in a previous study undertaken with this test material. Clinical signs, functional observations, bodyweight development, dietary intake and water consumption were monitored during the study. Haematology and blood chemistry were evaluated for all animals at the end of the study. All animals were subjected to gross necropsy examination and histopathological evaluation of selected tissues was performed.
Although no deaths were evident in this study, clinical signs were evident for one female from the highest dose group on the first day of treatment. Regression was evident on Day 2 and the dose level was increased to 600 mg/kg bw/day on Day 3. Clinical signs appeared in one male and two females on Day 4 (the second day of treatment at 600 mg/kg bw/day) and incidental clinical signs were evident during the treatment period. Incidents of hunched posture, and abnormal gait were also evident for two females treated with the intermediate dose on the first day of treatment however complete regression was evident thereafter. The clinical signs observed during the daily clinical observations were confirmed during the weekly arena observations. Furthermore, motor activity assessments revealed lower overall motor activity for animals of either sex treated with 600 mg/kg bw/day, extending into the male 300 mg/kg/day dose group. No significant reductions were evident during the final 20% of the assessment period, known as the asymptotic period, which would suggest that the reduced activity observed was most probably attributed to a slight decline in the physical health of the animals, and did not represent a neurotoxic effect of treatment. Remaining clinical signs consisted of increased salivation following dose, which was observed in both the high and intermediate dose groups. This observation is commonly observed following administration of a slightly unpalatable or irritant test material formulation. There were no toxicologically significant differences in dietary or water intake for treated animals when compared to control values and histopathological examinations did not reveal any effects of the gastro-intestinal tract which may be suggestive of irritancy. In the absence of any changes to suggest neurotoxicity the increased salivation detected in this study was not considered to represent an adverse effect of treatment and is most likely to be attributed to the poor taste of the test substance. A slight reduction in overall bodyweight change was observed for animals of either sex treated with the highest dose level in comparison to controls, with the effect extending into the intermediate male dose group. No adverse effects on dietary intake or food conversion efficiency were detected, therefore, the slightly reduced bodyweight gain was not considered to represent an adverse effect. Blood chemical analysis did not reveal any significant differences in the highest dose level, however, significantly elevated alanine aminotransferase levels were observed for males treated with 300 mg/kg bw/day, together with an increase in alkaline phosphate. Furthermore, liver weights were elevated for animals of either sex treated with 600 mg/kg bw/day with the effect extending into the intermediate male dose group. Finally, histopathological examination revealed centrilobular hepatocyte enlargement in the highest dose group, with the effect extending into the male 300 mg/kg bw/day dose group. The increases in enzyme activity, elevated liver weights and microscopic hepatic changes are commonly observed following the administration of a xenobiotics, resulting in induction of metabolising enzymes. In the absence of any inflammatory or degeneration changes, these findings were not considered to represent an adverse effect of treatment.
Due to the nature of the clinical signs observed at the highest dose level, consisting of ataxia, prostration and lethargy, together with the remaining treatment-related effects, a ‘No Observed Adverse Effect Level’ (NOAEL) could not be established at the highest dose level. The treatment-related effects detected at 300 mg/kg bw/day were not considered to represent an adverse health effect, therefore a NOAEL was established at 300 mg/kg bw/day. No treatment-related effects were detected at 30 mg/kg/day, therefore a No Observed Effect Level (NOEL) was established at 30 mg/kg bw/day.
Based on the results of this study, test material is not classified for damage to organs through 28 days oral repeated exposure according to the criteria of the Annex VI of the Regulation (EC) No. 1272/2008 (CLP) and to the GHS.
This study is considered as acceptable and satisfies the requirement for sub-acute oral toxicity endpoint.
Reference
None
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 300 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- The key study is GLP-compliant and of high quality (Klimish score = 1)
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
Repeated dose toxicity: oral
In a repeated dose toxicity study (Harlan, 2010, rel. 1) performed in accordance with OECD test guideline No. 407 and in compliance with GLP, test material solution in arachis oil was administered by gavage to three groups of rats (5/sex/dose) at dose levels of 30, 300 and 600 mg/kg bw/day for 28 consecutive days. Control rats were given the vehicle alone. The highest dose group was initially treated at a lower dose level (300 mg/kg bw/day) for the first two days of the treatment to allow animals in this dose group to acclimatise to the test material at a lower dosage before exposure to the full dosage of 600 mg/kg bw/day. This action was undertaken to reduce the risk of treatment-related deaths at the highest dose level following the effects observed in a previous study undertaken with this test material (Harlan range-finder, 2010).
Although no deaths were evident in this study, clinical signs were evident for one female from the highest dose group on the first day of treatment. Regression was evident on Day 2 and the dose level was increased to 600 mg/kg bw/day on Day 3. Clinical signs appeared in one male and two females on Day 4 (the second day of treatment at 600 mg/kg bw/day) and incidental clinical signs were evident during the treatment period. Incidents of hunched posture, and abnormal gait were also evident for two females treated with the intermediate dose on the first day of treatment however complete regression was evident thereafter. The clinical signs observed during the daily clinical observations were confirmed during the weekly arena observations. Furthermore, motor activity assessments revealed lower overall motor activity for animals of either sex treated with 600 mg/kg bw/day, extending into the male 300 mg/kg/day dose group. No significant reductions were evident during the final 20% of the assessment period, known as the asymptotic period, which would suggest that the reduced activity observed was most probably attributed to a slight decline in the physical health of the animals, and did not represent a neurotoxic effect of treatment. Remaining clinical signs consisted of increased salivation following dose, which was observed in both the high and intermediate dose groups. This observation is commonly observed following administration of a slightly unpalatable or irritant test material formulation.
There were no toxicologically significant differences in dietary or water intake for treated animals when compared to control values and histopathological examinations did not reveal any effects of the gastro-intestinal tract which may be suggestive of irritancy. In the absence of any changes to suggest neurotoxicity the increased salivation detected in this study was not considered to represent an adverse effect of treatment and is most likely to be attributed to the poor taste of the test substance.
A slight reduction in overall bodyweight change was observed for animals of either sex treated with the highest dose level in comparison to controls, with the effect extending into the intermediate male dose group. No adverse effects on dietary intake or food conversion efficiency were detected, therefore, the slightly reduced bodyweight gain was not considered to represent an adverse effect. Blood chemical analysis did not reveal any significant differences in the highest dose level, however, significantly elevated alanine aminotransferase levels were observed for males treated with 300 mg/kg bw/day, together with an increase in alkaline phosphate. Furthermore, liver weights were elevated for animals of either sex treated with 600 mg/kg bw/day with the effect extending into the intermediate male dose group. Finally, histopathological examination revealed centrilobular hepatocyte enlargement in the highest dose group, with the effect extending into the male 300 mg/kg bw/day dose group. The increases in enzyme activity, elevated liver weights and microscopic hepatic changes are commonly observed following the administration of a xenobiotics, resulting in induction of metabolising enzymes. In the absence of any inflammatory or degeneration changes, these findings were not considered to represent an adverse effect of treatment.
Due to the nature of the clinical signs observed at the highest dose level, consisting of ataxia, prostration and lethargy, together with the remaining treatment-related effects, a ‘No Observed Adverse Effect Level’ (NOAEL) could not be established at the highest dose level. The treatment-related effects detected at 300 mg/kg bw/day were not considered to represent an adverse health effect, therefore a NOAEL was established at 300 mg/kg bw/day. No treatment-related effects were detected at 30 mg/kg/day, therefore a No Observed Effect Level (NOEL) was established at 30 mg/kg bw/day.
Justification for classification or non-classification
Harmonized classification:
The substance has no harmonized classification according to the Regulation (EC) No 1272/2008.
Self-classification:
Based on the available data, no additional classification is proposed regarding the specific target organ toxicity after oral dose-repeated exposure according to the Regulation (EC) No 1272/2008 and to the GHS.
There were no data regarding the dermal and inhalation routes.
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