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EC number: 289-348-4 | CAS number: 87788-32-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Description of key information
The acute oral median lethal dose (LD50) of the test item in the female Wistar strain rat was estimated to be in the range of 300 to 2000 mg/kg body weight (Globally Harmonized Classification System Category 4).
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Experimental start date 08 November 2016 Experimental completion date 14 December 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 420 (Acute Oral Toxicity - Fixed Dose Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 bis (Acute Oral Toxicity - Fixed Dose Procedure)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- fixed dose procedure
- Limit test:
- yes
- Specific details on test material used for the study:
- Identification: (μ(5-amino-1,3,3-trimethylcyclohexylamine-N,N')hexafluorodiboron
Batch: AEF0009100
Purity: 100% UVCB
Physical state/Appearance: clear colorless liquid
Expiry Date: 29 August 2017
Storage Conditions: room temperature in the dark - Species:
- rat
- Strain:
- Wistar
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- Animal Information
Female Wistar (RccHan™:WIST) strain rats were supplied by Envigo RMS (UK) Limited, Oxon, UK. On receipt the animals were randomly allocated to cages. The females were nulliparous and non pregnant. After an acclimatization period of at least 5 days the animals were selected at random and given a number unique within the study by indelible ink marking on the tail and a number written on a cage card. At the start of the study the animals were 8 to 12 weeks of age. The body weight variation did not exceed ±20% of the mean body weight at the start of treatment.
Animal Care and Husbandry
The animals were housed in groups of up to four in suspended solid floor polypropylene cages furnished with woodflakes. With the exception of an overnight fast immediately before dosing and for approximately 3 to 4 hours after dosing, free access to mains drinking water and food (2014C Teklad Global Rodent diet supplied by Envigo RMS (UK) Limited, Oxon, UK) was allowed throughout the study. The diet, drinking water and bedding were routinely analyzed and were considered not to contain any contaminants that would reasonably be expected to affect the purpose or integrity of the study.
The temperature and relative humidity were set to achieve limits of 19 to 25 °C and 30 to 70% respectively. The rate of air exchange was at least fifteen changes per hour and the lighting was controlled by a time switch to give 12 hours continuous light and 12 hours darkness.
The animals were provided with environmental enrichment items which were considered not to contain any contaminant of a level that might have affected the purpose or integrity of the study. - Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- Using available information on the toxicity of the test item, 2000 mg/kg was chosen as the starting dose. A single animal was treated with a dose volume of 1.94 mL/kg to one rat.
- Doses:
- Due to mortality at a dose level of 2000 mg/kg, an additional animal was treated as follows: 300 mg/kg, with the dose volume being 10 mL/kg, to one rat.
- No. of animals per sex per dose:
- In the absence of toxicity at a dose level of 300 mg/kg, an additional group of animals was treated as follows: 4 rats.
- Control animals:
- no
- Details on study design:
- All animals were dosed once only by gavage, using a metal cannula attached to a graduated syringe. The volume administered to each animal was calculated according to the fasted body weight at the time of dosing. Treatment of animals was sequential. Sufficient time was allowed between each dose group to confirm the survival of the previously dosed animals.
Clinical observations were made 30 minutes, 1, 2, and 4 hours after dosing and then daily for up to 14 days. Morbidity and mortality checks were made twice daily, early and late during normal working days, and once daily at weekends and public holidays.
Individual body weights were recorded on Day 0 (the day of dosing) and on Days 7 and 14 or at death.
At the end of the observation period the surviving animals were killed by cervical dislocation. All animals were subjected to gross necropsy. This consisted of an external examination and opening of the abdominal and thoracic cavities. The appearance of any macroscopic abnormalities was recorded. No tissues were retained. - Preliminary study:
- mortality at a dose level of 2000 mg/kg
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 300 - < 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- Dose level 2000 mg/kg: The animal was killed for humane reasons, 1 day after dosing, due to the occurrence of clinical signs of toxicity that exceeded the severity limit set forth in the UK Home Office Project Licence.
Dose level 300 mg/kg: There were no deaths. - Clinical signs:
- Dose level 2000 mg/kg: Signs of systemic toxicity noted were hunched posture, pilo erection, lethargy, ataxia, hypothermia, decreased respiratory rate and dehydration.
Dose level: 300 mg/kg: No signs of systemic toxicity were noted during the observation period. - Body weight:
- Dose level 300 mg/kg: All animals showed expected gains in body weight over the observation period.
- Gross pathology:
- Dose level 2000 mg/kg: Abnormalities noted at necropsy were dark liver, dark kidneys, clear liquid present in the stomach and hemorrhagic gastric mucosa.
Dose level: 300 mg/kg: No abnormalities were noted at necropsy. - Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- The acute oral median lethal dose (LD50) of the test item in the female Wistar strain rat was estimated to be in the range of 300 2000 mg/kg body weight (Globally Harmonized Classification System Category 4).
- Executive summary:
Introduction
The study was performed to assess the acute oral toxicity of the test item in the Wistar strain rat.
Methods
Following a sighting test at dose levels of2000 mg/kg and300 mg/kg, a further group of four fasted females was given a single oral dose of test item, as asolutionindistilled water, at a dose level of300 mg/kg body weight. Clinical signs and body weight development were monitored during the study. All animals were subjected to gross necropsy.
Results
Mortality. Theanimal treated at a dose level of 2000 mg/kg was killed for humane reasons, 1 day after dosing, due to the occurrence of clinical signs of toxicity that exceeded the severity limit set forth in the UK Home Office Project Licence. There were no deaths at a dose level of 300 mg/kg.
Clinical Observations. Signs of systemic toxicity noted in the animal treated at a dose level of 2000 mg/kg were hunched posture, pilo‑erection, lethargy, ataxia, hypothermia, decreased respiratory rate and dehydration. There were no signs of systemic toxicity noted at a dose level of 300 mg/kg.
Body Weight. Surviving animals showed expected gains in body weight.
Necropsy. Abnormalities noted at necropsy of the animal treated at a dose level of 2000 mg/kg were dark liver, dark kidneys, clear liquid present in the stomach and hemorrhagic gastric mucosa. No abnormalities were noted at necropsy of animals treated at a dose level of 300 mg/kg.
Conclusion
The acute oral median lethal dose (LD50) of the test item in the female Wistar strain rat was estimated to be in the range of300 ‑ 2000 mg/kg body weight (Globally Harmonized Classification System-Category 4).
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 300 mg/kg bw
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- This study was conducted between 23 August 2017 and 06 September 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Version / remarks:
- 24 February 1987
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.3 (Acute Toxicity (Dermal))
- Version / remarks:
- EC No. 440/2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- fixed dose procedure
- Limit test:
- yes
- Specific details on test material used for the study:
- Information as provided by the Sponsor.
Identification: (μ(5-amino-1,3,3-trimethylcyclohexylamine-N,N')hexafluorodiboron
Batch: AEF0009100
Purity: 100% UVCB
Physical state / Appearance: clear colorless liquid
Expiry Date: 29 August 2017
Storage Conditions: room temperature in the dark - Species:
- rat
- Strain:
- Wistar
- Remarks:
- RccHan:WIST strain
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Five male and five female Wistar (RccHan:WIST) strain rats were supplied by Envigo RMS (UK) Limited, Oxon, UK. On receipt the animals were randomly allocated to cages. The females were nulliparous and non pregnant. After an acclimatization period of at least 5 days the animals were selected at random and given a number unique within the study by indelible ink marking on the tail and a number written on a cage card. At the start of the study the animals weighed at least 200 g, and were 8 to 12 weeks of age. The weight variation did not exceed ±20% of the mean weight for each sex.
Animal Care and Husbandry
The animals were housed in suspended solid floor polypropylene cages furnished with woodflakes. The animals were housed individually during the 24 Hour exposure period and in groups of five, by sex, for the remainder of the study. Free access to mains drinking water and food (2014C Teklad Global Rodent diet supplied by Envigo RMS (UK) Limited, Oxon, UK) was allowed throughout the study. The diet, drinking water and bedding were routinely analyzed and were considered not to contain any contaminants that could reasonably be expected to affect the purpose or integrity of the study.
The temperature and relative humidity were set to achieve limits of 19 to 25 C and 30 to 70% respectively. The rate of air exchange was at least fifteen changes per hour and the lighting was controlled by a time switch to give 12 hours continuous light and 12 hours darkness.
The animals were provided with environmental enrichment items which were considered not to contain any contaminant of a level that might have affected the purpose or integrity of the study. - Type of coverage:
- semiocclusive
- Vehicle:
- unchanged (no vehicle)
- Details on dermal exposure:
- On the day before treatment the back and flanks of each animal were clipped free of hair.
Using available information on the toxicity of the test item, a single group of animals was treated as follows:
Dose Level (mg/kg) Specific Gravity Dose Volume (mL/kg) Number of Rats
Male Female
2000 1.035 1.94 5 5
The appropriate amount of test item was applied as evenly as possible to an area of shorn skin (approximately 10% of the total body surface area). A piece of surgical gauze was placed over the treatment area and semi occluded with a piece of self adhesive bandage. The animals were caged individually for the 24 Hour exposure period. Shortly after dosing the dressings were examined to ensure that they were securely in place.
After the 24 Hour contact period the bandage was carefully removed and the treated skin and surrounding hair wiped with cotton wool moistened with distilled water to remove any residual test item. The animals were returned to group housing for the remainder of the study period. - Duration of exposure:
- 24 h
- Doses:
- 2000 mg/kg
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- Study Design
On the day before treatment the back and flanks of each animal were clipped free of hair.
Using available information on the toxicity of the test item, a single group of animals was treated as follows:
Dose Level (mg/kg) Specific Gravity Dose Volume (mL/kg) Number of Rats
Male Female
2000 1.035 1.94 5 5
The appropriate amount of test item was applied as evenly as possible to an area of shorn skin (approximately 10% of the total body surface area). A piece of surgical gauze was placed over the treatment area and semi occluded with a piece of self adhesive bandage. The animals were caged individually for the 24 Hour exposure period. Shortly after dosing the dressings were examined to ensure that they were securely in place.
After the 24 Hour contact period the bandage was carefully removed and the treated skin and surrounding hair wiped with cotton wool moistened with distilled water to remove any residual test item. The animals were returned to group housing for the remainder of the study period.
The animals were observed for deaths or overt signs of toxicity 30 minutes, 1, 2 and 4 hours after dosing and subsequently once daily for 14 days.
After removal of the dressings and subsequently once daily for 14 days, the test sites were examined for evidence of primary irritation and scored according to the following scale:
EVALUATION OF SKIN REACTIONS
Erythema and Eschar Formation Value
No erythema 0
Very slight erythema (barely perceptible) 1
Well-defined erythema 2
Moderate to severe erythema 3
Severe erythema (beef redness) to
slight eschar formation (injuries in depth) 4
Edema Formation Value
No edema 0
Very slight edema (barely perceptible) 1
Slight edema (edges of area well-defined by definite raising) 2
Moderate edema (raised approximately 1 millimeter) 3
Severe edema (raised more than 1 millimeter
and extending beyond the area of exposure) 4
Any other skin reactions, if present were also recorded.
Individual body weights were recorded prior to application of the test item on Day 0 and on Days 7 and 14.
At the end of the study the animals were killed by cervical dislocation. All animals were subjected to gross necropsy. This consisted of an external examination and opening of the abdominal and thoracic cavities. The appearance of any macroscopic abnormalities was recorded. No tissues were retained.
Data Evaluation
Data evaluations included the relationship, if any, between the exposure of the animal to the test item and the incidence and severity of all abnormalities including behavioral and clinical observations, gross lesions, body weight changes, mortality and any other toxicological effects.
Using the mortality data obtained, an estimate of the acute dermal median lethal dose (LD50) of the test item was made.
The results were also evaluated according to the Globally Harmonized System of Classification and Labelling of Chemicals. - Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- no indication of skin irritation up to the relevant limit dose level
- Mortality:
- There were no deaths.
- Clinical signs:
- No signs of systemic toxicity were noted during the observation period.
- Body weight:
- All animals showed expected gains in body weight over the observation period.
- Gross pathology:
- No abnormalities were noted at necropsy
- Other findings:
- Dermal Reactions
Very slight erythema was noted at the treated skin sites of three females and one male up to 3 days after dosing. Small superficial scattered scabs were noted at the treated skin site of one male on Days 1 to 4. - Interpretation of results:
- GHS criteria not met
- Conclusions:
- The acute dermal median lethal dose (LD50) of the test item in the Wistar strain rat was found to be greater than 2000 mg/kg body weight.
The test item does not meet the criteria for classification according to the Globally Harmonized System of Classification and Labelling of Chemicals. - Executive summary:
The study was performed to assess the acute dermal toxicity of the test item in the Wistar strain rat.
Methods
A group of ten animals (five males and five females) was given a single, 24 hour, semi‑occluded dermal application of the undiluted test item to intact skin at a dose level of 2000 mg/kg body weight. Clinical signs and body weight development were monitored during the study. All animals were subjected to gross necropsy.
Results
Mortality. There were no deaths.
Clinical Observations. There were no signs of systemic toxicity.
Dermal Irritation. Very slight erythema was noted at the treated skin sites of three females and one male up to 3 days after dosing. Small superficial scattered scabs were noted at the treated skin site of one male on Days 1 to 4.
Body Weight. All animals showed expected gains in body weight.
Necropsy. No abnormalities were noted at necropsy.
Conclusion
The acute dermal median lethal dose (LD50) of the test item in the Wistar strain rat was found to be greater than 2000 mg/kg body weight.
The test item does not meet the criteria for classification according to theGlobally Harmonized Systemof Classification and Labelling of Chemicals.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
Additional information
Justification for classification or non-classification
The acute oral median lethal dose (LD50) of the test item in the female Wistar strain rat was estimated to be in the range of 300 2000 mg/kg body weight (Globally Harmonized Classification SystemCategory 4).
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