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EC number: 203-716-3 | CAS number: 109-89-7
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
The test substance is acutely harmful to aquatic invertebrates.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 58 mg/L
Additional information
Under supervision of the Japanese Ministry of the Environment, a Daphnia magna immobilisation test according to OECD 202 was conducted under GLP and published in 2000. The daphnids were exposed for 48 hours under static conditions to nominal test concentrations of 0.79 to 15.0 mg/L diethylamine. In addition, in a supplemental test, test concentrations of 27.0 to 157.5 mg/L were tested. The test concentrations were analytically verified and deviated more than 20% from the nominal test concentrations. Therefore, measured geomean concentrations were used to assess the effect values. A 48 -h EC50 was determined to be 58 mg/L (95% CL: 49.9 - 68.1 mg/L,based on measured geomean concentrations; NITE 2000).
In addition, supporting information is available.
The toxicity of diethylamine towards Ceriodaphnia dubia was assessed according to ASTM guideline (1993). The test duration was 48 hours, the test solutions were renewed daily. The test concentrations were analytically verified and deviated less than 20% from the nominal values. Nevertheless, the results are based on the mean measured test concentrations. The pH values were not adjusted and ranged from 7.6 to 8.6 throughout the test. The 48 -h LC50 was assessed to be 4.6 mg/L (95% CL: 3.1 - 6.7 mg/L, based on measured test concentrations). The 48 -h NOAEL (No-Observed-Acute Effects Level) is 3.1 mg/L (based on measured test concentrations, Arkema, 1994, report no.: 94 -6 -5329). The results demonstrate that the aquatic invertebrate Ceriodaphnia dubia is considerably more sensitive to diethylamine than Daphnia magna (>= factor 10). However, the study does not fulfill the requirements of the OECD 202 guideline, therefore it is not considered for the environmental risk assessment.
In addition, in an OECD 202 guideline study van Leeuwen and co-workers (1985) determined an EC50 of 56 mg/L (95% CL: 32.0 - 100 mg/L, nominal) for the mobility of Daphnia magna after a 48 -hour exposure to the test substance. This result is in accordance with a publication which also demonstrate, that diethylamine is acutely harmful to aquatic invertebrates. Not following a specific guideline, a nominal 48 -h EC50 of 100 mg/L for Daphnia magna and diethylamine was found (Bringmann & Kuehn, 1959).
Two studies with 24 -h values for Daphnia magna are available, ranging from 41 mg/L to 77 mg/L (Trenel & Kuehn, 1982, IRCHA ED, 1993). In addition, Trenel and Kuehn, 1982, observed an 24 -h EC50 of 288 mg/L when using neutralised test substance solutions.
In conclusion, diethylamine is acutely harmful to aquatic invertebrates.
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