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EC number: 202-844-7 | CAS number: 100-36-7
- 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
Additional information
Short-term toxicity to fish
2 -Aminoethyldiethylamine is with high probability acutely not harmful to fish.
Key study: Leuciscus idus, DIN 38 412 -L15 (equivalent to OECD 203), non-GLP, no analytical verification (BASF AG, 1987, report no.: 10F0143/875047): 96 -h LC50 = 100 to 215 mg/L (nominal, CL not determined, non-neutralized test solutions); 96 -h LC50 > 464 mg/L (nominal, CL not determined, neutralized test solutions)
Supporting study: Leuciscus idus, DIN 38 412 -L15 (equivalent to OECD 203), non-GLP, no analytical verification, read-across to CAS 104 -78 -9 (BASF AG 1988, report no.: 10F0561/875051): 96 -h LC50 = 146.6 mg/L (geomentric mean, nominal, CL not determined, non-neutralized test solutions); 96 -h LC50 > 464 mg/L (nominal, CL not determined, neutralized test solutions)
Short-term toxicity to aquatic invertebrates
2 -Aminoethyldiethylamine is acutely harmful to aquatic invertebrates.
Key study: Daphnia magna, ISO 6341, non-GLP, no analytical verification, read-across to CAS 104 -78 -9 (Arkema, 1991, report no.: 1944/91): 48 -h EC50 = 30.16 mg/L (nominal, CL not determined)
Supporting study: Daphnia magna, EU Directive 79/831/EEC Annex V, part C (equivalent to OECD 202), non-GLP, no analytical verification, read-across to CAS 104 -78 -9 (BASF AG 1989, report no.: 1/0020/2/89 -0020/89): 48 -h EC50 = 51.8 mg/L (nominal, 95% CL: 43.08 - 62.2, based on not neutralised test solutions)
Toxicity to aquatic algae and cyanobacteria
2 -Aminoethyldiethylamine is acutely harmful to aquatic algae.
Key study: Pseudokirchneriella subcapitata, OECD 201, GLP, analytically verified test concentrations, read-across to CAS 104 -78 -9 (Arkema, 2000, report no.: 57/99/A): 72 -h ErC50 = 34 mg/L, 72 -h NOEC = 19.53 mg/L, 72 -h ErC10 = 26 mg/L
Supporting studies:
- Desmodesmus subspicatus, DIN 38 412/9, non-GLP, no analytical verification, read-across to CAS 104 -78 -9 (BASF AG 1990, report no.: 02/90/134): 72 -h ErC50 > 100 - <150 mg/L (nominal, not neutralised test solutions)
- Desmodesmus subspicatus, DIN 38 412/9, non-GLP, no analytical verification, read-across to CAS 104 -78 -9 (BASF AG 1990, report no.: 02/90/134): 72 -h ErC50 = 7.12 g/L (nominal, neutralised test solutions), 72 -h ErC10 = 3.45 g/L (nominal, neutralised test solutions)
Toxicity to microorganisms
The inhibition of the degradation activity of activated sludge is not anticipated when introduced in appropriately low concentrations.
Key study: Pseudomonas putida, DIN 38412 Part 8, non-GLP, no analytical verification (BASF AG 1988, report no.: 9/1244/87): 17 -h EC10 = 111.7 mg/L, 17 -h EC50 = 203.4 mg/L (nominal)
Supporting studies:
- activated sludge (industrial), ISO 8192, non-GLP, no analytical verification (BASF AG 1983, report no.: 347): 30 -min EC20 > 1995 mg/L (nominal)
- activated sludge (municipal), OECD 209, GLP, no analytical verification, read-aross to CAS 104 -78 -9 (BASF SE 2005, report no.: 08G0264/053084): 30 -min EC20 > 1000 mg/L, 30 -min EC50 > 1000 mg/L (nominal)
- Pseudomonas putida, DIN 38412 Part 8, no analytical verification, read-across to CAS 104 -78 -9 (BASF AG 1987, report no.: 9/0784/87): 17 -h EC10 = 76.1 mg/L, 17 -h EC50 = 100.5 mg/L (nominal)
- activated sludge (industrial), ISO 8192, non-GLP, no analytical verification, read-across to CAS 104 -78 -9 (BASF AG 1983, report no.: 344): 30 -min EC20 > 1995 mg/L, 30 -min EC50 > 1995 mg/L (nominal)
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