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Diss Factsheets
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EC number: 203-542-8 | CAS number: 108-01-0
- 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 aquatic toxicity tests are available for three trophic levels (fish, invertebrates, and algae). No chronic experimental data are available regarding possible effects of the test substance.
Regarding short-term toxicity to fish, Leuciscus idus was used in two different experiments. In the key study performed according to German Industrial Standard DIN 38412 (part 15), a LC50 value (96 h) of 146.63 mg/L is reported (BASF AG, 1990). Referring to the supporting study (toxicity screening study), a LC50 (48h) range of 1500 - 2500 mg/L was determined (BASF AG, 1977).
For assessing the acute toxicity towards invertebrates, the effects on Daphnia magna according to Directive 79/831/EEC, Annex V, C2 (1984) have been determined. As final result, an EC50 (48h) of 98.37 mg/L is reported (BASF AG, 1988).
The aquatic toxicity towards algae was investigated by fluorimetric determination of algae growth exposed to dimethylethanolamine (DMAE) for 72 hours. The following results were obtained: EC50 (72h) = 66.08 mg/L, EC10 (72h) = 24.49 mg/L, and EC20 (72h) = 34.47 mg/L (BASF AG, 1989).
Referring to the toxicity of dimethylaminoethanol (DMAE) towards aquatic microorganisms, no experimental data are available. However, read-across to the substance 2,2´-(methylimino)diethanol (MDEA) was performed due to the structural similarities of both the target and the read-across substance. For the read-across substance, three valid studies are available.
In the key study, domestic activated sludge was used for an experiment conducted similar to OECD 209 (BASF AG, 1993). As final result, an EC20 (30min) greater than 1000 mg/L is reported which is based on the respiration rate. Referring to supporting information, Pseudomonas putida was used in a test conducted according to DIN 38412, part 8 (BASF AG, 1988). A photometric determination at 436 nm was used to indicate growth inhibition. The results are given as follows: EC10 (17h) = 273.8 mg/L, EC50 (17h) = 413.8 mg/L, and EC90 (17h) = 820.2 mg/L. In another supporting study, an oxygen consumption inhibition test was performed with activated sludge from BASF wastewater treatment plant (BASF AG, 1988). 1000 mg/L was the highest test concentration with less than 20 % respiration inhibition during 30 minutes exposure time. Therefore, EC20 (30 min) > 1000 mg/L is reported as effect concentration result.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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