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EC number: 246-807-3 | CAS number: 25307-17-9
- 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
LD50 = 1260 mg/kg bw. The only study available is an oral LD50 study on 2,2'-(Octadec-9-enylimino)bisethanol CAS No 25307-17-9, the study is reliability 1 GLP compliant to OECD Guideline 401.
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:
- November-December 1986
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Complete report according to guidelines/standards.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Sprague-Dawley CFY
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Interfauna (UK) Ltd., Wyton, UK
- Age at study initiation: 5-8 weeks
- Weight at study initiation: 123-152 g (males), 120-146 g (females)
- Fasting period before study: overnight prior to dosing until ca. 2 hours after dosing
- Housing: 5/sex in solid floor polypropylene cages with sawdust bedding
- Diet (e.g. ad libitum): ad lib
- Water (e.g. ad libitum): ad lib
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-23
- Humidity (%): 45-65
- Air changes (per hr): ca. 15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 7 November To: 10 December 1986 - Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: neat test compound was used
MAXIMUM DOSE VOLUME APPLIED: 2.20 ml/kg bw - Doses:
- 1000, 1260, 1587, 2000 mg/kg bw
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: observations were made 1 and 4 h after dosing and once daily thereafter. BW were
measured weekly and at death
- Necropsy of survivors performed: yes - Statistics:
- Method of Weil CS, Biometrics (1952), 8, 249
- Preliminary study:
- A preliminary study was carried out using 2 groups of one male and one female each. Dose levels were 500 and 2000 mg/kg bw.
At 500 mg/kg the 2 animals survived, whereas both animals died at 2000 mg/kg bw. - Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- 1 260 mg/kg bw
- 95% CL:
- 1 053 - 1 508
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 1 309 mg/kg bw
- 95% CL:
- 1 024 - 1 674
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 1 000 - < 1 587 mg/kg bw
- Mortality:
- All deaths occurred 2-3 days after treatment.
- Clinical signs:
- other: Major signs of toxicity noted in all dose groups during the day of dosing were hunched posture, pilo-erection, decreased respiratoryrate, increased salivation and ptosis. Surviving animals treated with 1000 mg/kg continued to show signs of toxicity on day
- Gross pathology:
- Common abnormalities noted at necropsy of decedents were congested or abnormally red lungs, dark livers, haemorrhage of the
gastric mucosa and congestion of the small intestines. Necropsy of animals killed at the end of the study revealed scattered
white thickened or raised areas on the non-glandular region of the stomach. The liver of two animals treated with 2000 mg/kg was adhering to the stomach. One decedent treated with 1000 mg/kg and two animals treated with 1587 mg/kg were cannabalised. No
necropsy was performed. - Other findings:
- No data
- Interpretation of results:
- Category 4 based on GHS criteria
- Remarks:
- Migrated information
- Conclusions:
- The LD50 value was calculated to be 1260 mg/kg bw with 95% confidence limits of 1053 and 1508 mg/kg bw. The test compound was classied in Category IV according to OECD-GHS.
- Executive summary:
A study was performed to determine the acute oral toxicity of the test material in the Sprague-Dawley CFY strain rat. The study was designed to comply with the recommendations of the OECD Guidelines for Testing of Chemicals (1981) No. 401 "Acute Oral Toxicity". Following a range-finding study, four groups, each of ten fasted animals (five males and five females) were given a single oral dose of undiluted test material, at dose levels of 1000 to 2000 mg/kg bodyweight. Deaths were noted two to three days after treatment. Major signs of toxicity noted during the day of dosing were hunched posture, pilo-erection, lethargy , decreased respiratory rate, increased salivation and ptosis. Less frequent signs of ataxia, pallor of the extremities, diarrhoea, diuresis, chromodacryorrhoea, tiptoe gait, emaciation, red/brown staining around the snout/eyes were also noted. Signs of reaction continued to be noted up to three to fourteen days after treatment. Surviving animals treated with 1000 mg/kg showed expected body weight gains over the study period. Effects on body weight were noted in other dose groups during the first week but all animals recovered to show expected body weight gains over the second week. Necropsy of decedents revealed congested or abnormally red lungs, dark livers , haemorrhage of the gastric mucosa with congestion of the small intestines. Necropsy of animals killed at the end of the study revealed thickened or raised white areas on the non-glandular region of the stomach. The acute oral median lethal dose (LDS0) and 95% confidence limits were found to be:
All animals: 1260 (1053 - 1508) mg/kg body weight
Males only: 1309 (1024 - 1674) mg/kg body weight
Females only: between 1000 and 1587 mg/kg body weight (best estimate).
Reference
Mortality data
Dose level (mg/kg bw) |
Deaths |
|||
Male |
Female |
Total |
% |
|
1000 |
0/5 |
1/5 |
1/10 |
10 |
1260 |
3/5 |
3/5 |
6/10 |
60 |
1587 |
4/5 |
4/5 |
8/10 |
80 |
2000 |
3/5 |
4/5 |
7/10 |
70 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 1 260 mg/kg bw
- Quality of whole database:
- Study of adequate quality, consistent with information within group of primary fatty amines with 2 EO.
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
The only study available is an oral LD50 study (According to OECD 401 and GLP compliant) on 2,2'-(Octadec-9-enylimino)bisethanol, CAS No. 25307-17-9, resulting to LD50 of 1260 (1053 - 1508) mg/kg body weight. Necropsy of the decedents showed haemorrhage of the gastric mucosa with congestion of the small intestines, and necropsy of animals killed at the end of the study revealed thickened or raised white areas on the non-glandular region of the stomach. This is indicative that the acute toxicity is mainly caused via local, corrosive, effects on the Gastro-intestinal system.
2,2'-(Octadec-9 -enylimino)bisethanol is corrosive to the skin. Testing for acute dermal toxicity is therefore not justified. Toxicity following dermal exposure is characterised by local tissue damage, rather than the result of percutaneously absorbed material. For corrosive substances, the use of protective gloves and other equipment, such as face shields, aprons and good work practices are mandatory. Consequently, the occurrence of substantial dermal exposure of amounts comparable to the levels for acute oral toxicity is unlikely.
2,2'-(Octadec-9-enylimino)bisethanol is a liquid with a low vapour pressure, and exposure to vapours would be negligible at ambient temperatures. Possible inhalation would have to involve aerosol (of large) droplets that will deposit mainly on upper airways. Due to the corrosive properties of the substance, local respiratory irritation can be expected to represent the first, and most prominent, effects following inhalation of aerosols.
Based on the viscosity being 147 mPa.s at 20ºC and a density of 0.907 g/cm3 the Kinematic viscosity would be 151 mm2/s. It is therefore unlikely the Kinematic viscosity would be less than 20.5 mm2/s at 40ºC, therefore an aspiration hazard is not expected.
Justification for classification or non-classification
The LD Value of 1260 mg/kg is considered correct and will lead to CLP Category 4 for acute oral toxicity.
Due to corrosive properties the actute toxicity has not been investigated via dermal and inhalation routes. Local effects are considered to take precedence over systemic toxicity.
An aspiration hazard is not expected.
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