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Diss Factsheets
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EC number: 800-353-8 | CAS number: 1379524-06-7
- 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
Aquatic ecotoxicity tests of Amides, C18-unsatd., N-[3-(dimethylamine)propyl] on fish, daphnia and algae have been performed in natural river water. This approach is considered to be conservative but more environmentally realistic than the standard method. Indeed, the substance has a strong tendency to adsorb to negatively charged surfaces (suspended matter, algae, test vessels or organic material). Ecotoxicity tests performed in river water using the bulk approach reduce the bioavailability of the test substance as it occurs in the environment with such substances.
Toxicity to fish:
The study from Kean, 2012 (OECD 203) has a Klimisch rating of 1 and is identified as the key study.
The 96-hour LC50 to Danio rerio under semi-static conditions was 0.94 mg/L.
Therefore, the substance is considered as very toxic to fish.
Toxicity to invertebrates:
An acute toxicity test is available but was identified with a Klimish rating of 3 because the test concentrations were not checked during the test.Nevertheless, a long-term aquatic toxicity study on Daphnia magna (OECD 211) performed with a bulk approach is available (Kean, 2010). The 28d-EC10 based on reproduction
under semi-static conditions was 0.07 mg/L.
Toxicity to aquatic algae:
Toxicity to green algae was evaluated in the study from Kean (2013) identified as the key study with a Klimish rating of 1.
This study was carried out in general accordance with OECD Guideline 201 using some specific modifications (natural surface water supplemented with nutrients and NaHCO3). The bulk approach was applied to the test methodology allowing the use of total aquatic concentrations for calculation of endpoints. The 72 hour ErC10 was calculated as 0.32 mg/L and the ErC50 > 0.96 mg/L (extrapolated value = 1.17 mg/L), expressed as measured initial values. Thus the substance is considered as toxic to algae.
Toxicity to microorganisms:
The toxicity to activated sludge was determined in accordance with OECD 209 in a study from Geerts (2010) identified with a Klimish rating of 1 and as the key study. The EC50 for activated sludge after 3 hours contact time is 192 mg/L.
Therefore, the substance is considered not harmful to activated sludge.
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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