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EC number: 309-886-6 | CAS number: 101316-84-1 A tar obtained from low temperature carbonization and low temperature gasification of brown coal. Composed primarily of aliphatic, naphthenic and cyclic aromatic hydrocarbons, heteroaromatic hydrocarbons and cyclic phenols.
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The substance was tested for growth inhibition on algae Desmodesmus subspicatus.
The test was performed according to method C.3. - Freshwater Algae and Cyanobacteria, Growth Inhibition Test, Commission Regulation (EC) No. 761/2009, Annex IV.
Since the test substance is multi-component poorly soluble substance the water-accommodated fractions (WAFs) were prepared by adding measured amounts of the test substance to the test medium and then were stirred for a period of 72 hours. After period of stirring the WAFs were filtered through 0.45 μm filter and these solutions were used for testing. The WAFs were prepared for preliminary and main test.
The preliminary test was performed in range of test substance loading rates 10 – 100 mg/L. The highest inhibition of growth rate was 1.7 % and the highest inhibition of yield was 9.4 % in the preliminary test. Therefore the main test was performed in appropriate concentration range. The main test was performed in range of test substance loading rates 62 – 100 mg/L.
The study was performed without the analytical determination of the test substance concentrations. Only the concentrations of metals in the highest loading rate 100 mg/L were analysed in the main test. For all evaluations and results the loading rates of the test substance were used.
Test results:
72 hour - ErL50 > 100 mg/L (loading rate)
72 hour - EyL50 > 100 mg/L (loading rate)
72 hour - NOELRr = 100 mg/L (loading rate)
72 hour - NOELRy = 100 mg/L (loading rate)
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 19.9 mg/L
- EC10 or NOEC for freshwater algae:
- 12 mg/L
Additional information
Since the test substance is multi-component poorly soluble substance the water-accommodated fractions (WAFs) were prepared by adding measured amounts of the test substance to the test medium and then were stirred for a period of 72 hours. After period of stirring the WAFs were filtered through 0.45 μm filter and these solutions were used for testing. The WAFs were prepared for preliminary and full test.
The preliminary test was performed in range of test substance loading rates 10 – 100 mg/L. Based on the toxicity of the test substance found in preliminary test, the full test was performed in appropriate loading rates.
The full test was performed in range of test substance loading rates 12 – 90 mg/L.
The study was performed without the analytical determination of the test substance concentrations. For the analytical determination of the test substance concentration was not available suitable analytical method.
For all evaluations and results the loading rates of the test substance were used.
Test results:
72 hour – ErL50 = 50.5 mg/L (loading rate) (95% confidence limit: 47.0 – 54.0 mg/L)
72 hour – EyL50 = 19.9 mg/L (loading rate) (95% confidence limit: 18.4 – 21.4 mg/L)
72 hour – NOELRr = 24 mg/L (loading rate)
72 hour – NOELRy < 12 mg/L (loading rate)
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