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EC number: 203-442-4 | CAS number: 106-92-3
- 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
Allyl Glycidyl Ether (AGE) is harmful if swallowed and toxic if inhaled. AGE may be harmful in contact with skin according to GHS-UN (Cat 5) standards.
LD50 Oral (rat) = 830 mg/kg bw (male) and 1164 mg/kg bw (female)
LD50 Dermal = 2550 mg/kg bw (rat)
LC50 Inhalation-vapor (rat- 4h) = 2.56mg/l (male)
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 830 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- LC50
- Value:
- 2 560 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 2 550 mg/kg bw
Additional information
Oral exposure route:
Two studies were considered as key. In one study (Hine et al. 1956), male rats (n = 6) were dosed at 1300, 1600, 1900 and 2300 mg/kg bw allyl glycidyl ether (AGE) by intragastric intubation once. Mortality was observed at 1600, 1900 and 2300 mg/kg bw: 3/6, 5/6 and 5/6, respectively, and LD50 was established to be 1600 mg/kg bw. Treated rats showed signs of distress such as slight lacrimation, mussed fur, restlessness, slight unsteadiness, slight to moderate depression and dyspnea. Most survivors recovered overnight. Lethargy or coma was observed prior to death. At necropsy, rats that died showed diffuse inflammation of the lungs, slight to moderate irritation of the gastroenteric tract with fluid distention and petechial haemorrhages in the stomach. Spleen and kidneys were pale and discolored. Rats at scheduled sacrifice showed hypotonicity of the enteric tract and extensive adhesions of the stomach wall to adjacent tissues. One animal showed focal areas of necrosis in the liver during macroscopically examination. In the other key study (DOW 1978) performed similar to OECD guideline 401, six groups of rats were dosed by gavage at dose levels of 500, 1000, 1120, 1260, 1580 and 2000 mg/kg bw. Mortality occurred at 1000 mg/kg bw onwards, and LD50 was considered to be 830 mg/kg bw (females) and 1164 mg/kg bw (males). Prior to death, both male and female rats were lethargic, had piloerection, and had diarrhea. Gross pathological examination of male and female rats of the 500 mg/kg bw dose group (the least amount dosed) at 14 days after dosing revealed irritation of the nonglandular portion of the stomach, including hyperkeratosis, erosion, and ulcerations.
These findings were supported by further acute oral studies in which LD50 values of ca. 1746 mg/kg bw in males and female rats (BASFAG XVIII 219, 1968), and 260-340 mg/kg bw in male mice (Hine et al. 1956) were reported.
Taking all the presented data into consideration, AGE is classified as R22 according to EU standards and in Cat 4 according to GHS and CLP standards.
Inhalation exposure route:
Two studies were considered as key. In one study (DOW 1978), male rats (n=6) per dose group were exposed to the nominal vapor concentrations of 0.47, 1.18, 1.42, 1.78, 2.37, 3.32, 5.57 and 12.31 mg/l for 7 h. Mortalities occurred at 1.42 mg/l onwards and the LC50 was established to be 1.46 mg/l (ca. 2.56 mg/l for 4 h exposure). During exposure to the top 3 exposed groups, the rats showed gasping and had exudates around the nose and mouth. Slight nasal irritation and slight gasping were observed in rats of the 0.47 mg/l group during exposure. These signs of toxicity occurred with increasing severity as the exposure level increased. In the other key study (Hine et al. 1956), groups of 6 male rats were exposed to the vapor generated from the test substance at the nominal concentrations of 1.4, 2.1, 3.12 and 4.66 mg/l for 8 hours.Mortality was observed at 1.4, 2.1, 3.12 and 4.66 mg/l and LC50 was established to be between 3.12 and 4.66 mg/l (6.24 - 9.32 mg/l for 4 h exposure). Considerable lacrimation, nasal and salivary discharge, dyspnea, gasping and corneal opacity were noted. Rats dying during the study showed moderate to severe diffuse inflammation and hemorrhage of the lungs, pleural effusion, emphysema, bronchophenumonia, severe gaseous distension of the G.I. tract, pale and mottled liver and kidneys, engorged and enlarged adrenals as well as hypertrophy of the spleen. Rats from scheduled sacrifice showed slight diffuse inflammation of the lungs, emphysema, bronchopneumonia and mottled discoloured kidneys. Microscopically, 2 rats showed pneumonia.
The above findings were supported by another study in male mice where LC50 was reported to be 1.26 mg/l (Hine et al. 1956).
Taking all the presented data into consideration (the lowest LD50 value), AGE should be classified as R20 according to EU standards and in Cat 3 according to GHS / CLP standards.
Dermal exposure route:
In the key study (Hine et al, 1956), three male rabbits were exposed to 730, 1450, 2900 and 5800 mg/kg bw AGE by skin application under occlusive conditions for 7 h. Mortality was observed at 2900 and 5800 mg/kg bw, 2/3 and 3/3, respectively, and LD50 was established to be 2550 mg/kg bw. Mortality occurred within 7 hours after prior observed increasing depression. At necropsy constricted kidneys and spleens were observed. Microscopically, no abnormalities were noted. In another study, 4 groups of 4 rabbits each were subjected to an acute percutaneous absorption test resulting in mortality of 0/4, 1/4, 3/4 and 4/4 in the 252, 500, 1000 and 2000 mg/kg bw dose groups, respectively. The volume of administration, type of coverage and duration of exposure were not mentioned. Topical responses observed when the cuffs were removed included an application site which was purple in color, had moderate to severe swelling, and was necrotic. Prior to death, rabbits were lethargic and had labored breathing. Surviving rabbits behaved in a normal fashion, but had hard, leathery patches over the entire application site. The mortalities and necrosis of the skin observed in rabbits might be due to very longer exposure period or type of coverage used or other reasons, which are not documented in the present study. Due to lack of documentation (reliability 4), the results can not be used for assessment.
Based on the results, AGE is classified in Cat 5 according to GHS (UN) standards. No classification is required according to EU standards.
Justification for classification or non-classification
EU classification according to Annex I of Directive 67/548/EEC: Xn, R20/22
CLP Regulation (EC No 1272/2008)
- Oral route: Acute Category 4
- Dermal route: Not classified
- Inhalation route (vapour): Acute Category 3
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