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EC number: 273-224-1 | CAS number: 68953-70-8 The complex combination of alkanolamines from the distillation of reaction products of ammonia and oxirane. It consists predominantly of triethanolamine, diethanolamine and higher amines from the reaction of triethanolamine and oxirane.
- 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
Since Amix TE (CAS 68953-70-8) is composed of at least 75 % of TEA (CAS 102-71-6) and the available data for Amix TE are limited, a read-across to TEA was conducted. Acute toxicity data indicate low toxicity: in rats the oral LD50 was 6400 mg/kg bw (for TEA) and >2000 mg/kg bw (for Amix TE); in rabbits the dermal LD50 was > 2000 mg/kg (TEA). Inhalation exposure for 8 hours to vapour saturated with TEA failed to cause any deaths in rats (LC50 was not determined).
Key value for chemical safety assessment
Additional information
Since Amix TE (CAS 68953-70-8) is composed of at least 75 % of TEA (CAS 102-71-6) and the available data for Amix TE are limited, a read-across to TEA was conducted. In addition to the acute toxicity studies for TEA mentioned below, another acute oral toxicity study with Amix TE was performed: in rats the oral LD 50 was >2000 mg/kg bw, no mortality and no abnormal clinical signs were observed (BASF AG 10A0444/951087).
Oral toxicity
In an acute oral toxicity study (BASF AG, 1966), 5 Sprague-Dawley rats/sex/dose were exposed to 200 - 6400 mg/kg bw TEA by gavage and observed for 7 days. The LD50 was determined to be 6400 mg/kg bw for males and females. No deaths occured at doses of 5000 mg/kg bw or below. At 200 mg/kg bw, slight agitation was observed up to 4 hours after exposure; at higher doses unsteady, elevated respiration, anancasm to chew, apathy, and reduced grooming was noticed. Two days after exposure, no clinical signs were observed. Gross pathology did not reveal any abnormalities.
Dermal toxicity
In a dermal limit test, rabbits were treated with 2000 mg/kg bw TEA on the intact or abraded skin and subsequently observed for a 14 -day period (TSCATS, 1989). The test substance was either derived from NH3 (92% TEA) or DEA (88% TEA), both containing approximately 6.5% DEA. Mild erythema was observed following exposure to TEA derived from NH3 on the intact or abraded skin, returning to normal on day 6. Moderate erythema was observed following exposure to TEA derived from DEA on the intact or abraded skin, returning to normal on day 10. No mortality was observed, hence the LD50 was > 2000 mg/kg bw.
Inhalation toxicity
Due to its extremely low volatility, there is a lack of data documenting the acute inhalation toxicity. One report stated that whole-body exposure of rats to a saturated TEA atmosphere (approximately 1.8 mg/m3) at 20°C for 8 hours failed to cause any deaths. Therefore no LC50 value has been determined for this compound (BASF AG, 1966).
Justification for classification or non-classification
Based on the results of acute oral, inhalation and dermal toxicity studies, Amix TE does not need to be classified according to Directive 67/548/EEC and according to the EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
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