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EC number: 201-122-9 | CAS number: 78-51-3
- 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
The acute toxicity of TBEP has been studied by all routes relevant to occupational exposure from which it can be concluded that the acute toxicity of TBEP is low. For oral toxicity, a GLP-compliant guideline study in rats (Rel. 1) by Roth (2000) has been chosen as key study. Supporting studies of Rel. 2 are Wolfe (1979), Picirillo (1981), Bullock (1972), Freeman (1991) and Gabriel (1980). The key study for dermal toxicity (Rel. 2) is Picirillo (1981)
For inhalation toxicity, a GLP-compliant guideline study in rats (assigned Rel. 2 because data on test substance purity are not available) by Hofmann (1990) has been chosen as key study. Supporting studies of Rel. 2 are Mount, 1991 and Pinkerton, 1981.
Key value for chemical safety assessment
Additional information
Oral Toxicity
Reported oral LD50 values range from >2000 to >13,000 mg/kg for rat, guinea pig and hen. Some, though not all, studies show females as more sensitive to the effects of TBEP than males. Inthe Reliability 1 key study by Roth (2000) the LD50 in rat was >2000 mg/kg (limit dose). Supporting studies of reliability 2 by Wolfe (1979), Piccirillo (1981), Bullock (1972), Gabriel (1980) and Freeman (1991) suggest that the LD50 is >5000 mg/kg for males and approximately 5000 mg/kg for females. Other reports of lower reliability and LD50 values from secondary literature are also consistent with the conclusion that TBEP is of low acute toxicity. All available data are summarised in Table 1
Table 1: Acute Oral Toxicity Studies on TBEP
Species |
LD50 |
Reference |
Rel. |
Rat |
>2000 |
Roth, 2000 |
1 |
Rat |
13,278 (m), 5,383 (f) |
Wolfe, 1979 |
2 |
Rat |
>5000 (m), <5000 (f) |
Piccirillo, 1981 |
2 |
Rat |
>5000 (m),500-5000(f) |
Freeman, 1991 |
2 |
Rat (m) |
>4640 |
Bullock, 1972 |
2 |
Rat |
>5000 |
Gabriel, 1980 |
2 |
Hen |
>5000 |
Carrington, 1989 |
2 |
Rat |
>5000 |
Moreno, 1978 |
3 |
Rat |
ca 10000 |
Heinemann, 1970 |
3 |
Rat (m) |
>5000 (m) |
Holsing, 1969 (EPA 1982) |
3 |
Rat |
10000 |
Holsing, 1969 |
3 |
Rat |
9490 |
FMC, 1976a |
4 |
Rat |
4700 |
Monsanto, 1984a |
4 |
Rat |
3000 |
Sax, 1988 |
4 |
Rat |
3000 |
Eldefrawi, 1977 |
4 |
Guinea pig |
3000 |
Sax |
4 |
Inhalation Toxicity
The Rel. 2 key study by Hofman (1990) gives inhalation LC50 >6.4 mg/l for a 4-hour exposure in rats. The values given in the Rel. 2 supporting studies by Mount (1991) and Pinkerton (1981) are consistent with this value. Studies of lower reliability give values which are consistent with those of the key and supporting studies, as shown in Table 2.
Table 2: Acute Inhalation Toxicity Studies on TBEP
Species |
LC50 (aerosol) |
Reference |
Rel. |
Rat |
>6.4 mg/l 4h |
Hofmann, 1990 |
2 |
Rat |
>4.43mg/l / 4h |
Mount, 1991 |
2 |
Rat |
>0.52 < 5.03 mg/L 4h |
Pinkerton, 1981 |
2 |
Rat |
21.08 / 1h nominal |
Wolfe, 1979 |
3 |
Rat |
21.1 / 1h nominal |
Gabriel, 1980 |
3 |
Rat |
30 / 1h nominal |
FMC, 1976 |
4 |
Mouse |
180 mg/kg |
Sax , 1988 |
4 |
Dermal Toxicity
Two Rel. 2 key studies conducted at limit doses give dermal LD50 as > 2000 mg/kg (Picirillo, 1981) or > 5000 mg/kg (Wolfe, 1979). Two supporting Rel. 2 studies (Bullock, 1973; Gabriel, 1980) confirm dermal LD50 values >5000 mg/kg, as do data from sources of lower reliability. All available data are summarised in Table 3.
Table 3: Acute Dermal Toxicity Studies on TBEP
Species |
LD50 |
Reference |
Rel. |
Rabbit |
> 2000 |
Picirillo, 1981 |
2 |
Rabbit |
> 5000 |
Wolfe, 1979 |
2 |
Rabbit |
> 5000 |
Doyle, 1979 |
2 |
Rabbit |
> 4640 |
Bullock, 1973 |
2 |
Rabbit |
>5000 |
Gabriel, 1980 |
2 |
Rabbit |
> 2000 |
Moreno, 1978 |
3 |
Rabbit |
>10000 |
FMC, 1976 |
4 |
Justification for classification or non-classification
Oral:
The limit value for classification of a substance as harmful on acute exposure by the oral route according to the criteria ofAnnex VI Directive 67/748/EEC (R22) and EU/GHS criteria (Acute toxicity Cat. 4) is oral LD50 2000 mg/kg. All the available studies on TBEP give LD50 > 2000 mg/kg.
TBEP is therefore not classified for acute oral toxicity according to the criteria of Annex VI Directive 67/748/EEC or EU GHS.
Dermal:
The limit value for classification of a substance as harmful on acute exposure by the dermal route according to the criteria ofAnnex VI Directive 67/748/EEC (R21) and EU/GHS criteria (Acute toxicity Cat. 4) is dermal LD50 2000 mg/kg. All the available studies on TBEP give LD50 > 2000 mg/kg.
TBEP is therefore not classified for acute dermal toxicity according to the criteria of Annex VI Directive 67/748/EEC or EU GHS.
Inhalation:
The limit value for classification of a substance as harmful on acute exposure by inhalation of an aerosol according to the criteria of Annex VI Directive 67/748/EEC (R21) and EU/GHS criteria (Acute toxicity Cat. 4) is inhalation LC50 5 mg/l (4-hour exposure). The key study and the majority of supporting studies on TBEP give LC50 > 5 mg/l.
TBEP is therefore not classified for acute inhalation toxicity according to the criteria of Annex VI Directive 67/748/EEC or EU GHS.
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