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Diss Factsheets
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EC number: 915-623-1 | CAS number: -
- 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
Sediment toxicity
Administrative data
Link to relevant study record(s)
Description of key information
In a 28-day sediment spiked study (according to OECD guideline and GLP principles) with Chironomus riparius, the overall NOEC for emergence rate was 320 mg/kg sediment dw. This value will be used for the CSA.
The toxicity study has been performed with artificial sediment containing 2.1% organic carbon. As the concentration in freshly deposited sediment is taken as the PEClocal for sediment, the properties of suspended matter are used for deriving this PEC. Suspended matter contains 10% organic carbon. Therefore the NOEC from the study needs to be recalculated into a NOEC for a standard sediment, containing an organic carbon content of 10%:
NOEC (to use for the PNEC) = NOEC (from the study) x (10%/2.1%) = 320 x 4.762 = 1524 mg/kg sediment dw.
Then the PNEC derived from this value, can be compared with the PECs calculated in EUSES.
Key value for chemical safety assessment
- EC10, LC10 or NOEC for freshwater sediment:
- 1 524 mg/kg sediment dw
Additional information
Chironomid larvae (<48 hours old, 20 larvae/replicate, 4 replicates/concentration) were exposed to 2-amylanthraquinone at nominal concentrations of 10, 32, 100, 320 and 1000 mg/kg sediment dw in a sediment spiked system for 28 days. Exposure concentrations in sediment were analytically verified by HPLC-UV at the start of the test (103-113% of nominal) and after 28 days of exposure (78-93% of nominal). 2-Amylanthraquinone concentrations in overlying water and porewater were below the LOQ of 1.0 mg/L throughout the study. Concentrations of 10 until 320 mg/kg had no effect on the number of emerged animals but at a concentration of 1000 mg/kg the emergence was severely reduced. Less than 10 % of the animals emerged during the study at a concentration of 1000 mg/kg. No significant difference in sex ratio was found although the number of males was slightly reduced at concentrations of 320 and 1000 mg/kg. 2-Amylanthraquinone resulted in a delay in the emergence of the chironomids. The development rate was statistically significantly reduced at concentrations of 100, 320 and 1000 mg/kg. The reduction of the development rate at concentrations of 100 and 320 was only 4.0 and 4.9 % (the animals emerged about one day later). Because no effects on emergence rate were found at and below 320 mg/kg while effects on development rate were small (4.0 and 4.9% at 100 and 320 mg/kg), a concentration of 320 mg/kg will be considered as the overall No Oberved Adverse Effect Concentration.
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