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EC number: 300-212-6 | CAS number: 93924-19-7 Hollow ceramic spheres formed as a part of the ash in power stations burning pulverized coal. Composed primarily of the oxides of aluminium, iron and silicon and contain carbon dioxide and nitrogen within the sphere.
- 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 soil microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil microorganisms
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with acceptable restrictions, Basic data given
- Qualifier:
- according to guideline
- Guideline:
- other: DIN 38412-L48 (2002); German standard methods for the examination of water, waste water and sludge - Bio-assays (group L) - Part 48: Toxicity test with Arthrobacter globiformis for contaminated solids (L 48)
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on preparation and application of test substrate:
- AMENDMENT OF SOIL
- Type of organic substrate: LUFA - standard soil 2.2 - Test organisms (inoculum):
- other: Arthrobacter globiformis
- Total exposure duration:
- 3 h
- Test temperature:
- 30 °C
- Moisture:
- 0.6 g of ash-soil-mixture was moisturised with 0.6 mL of water
- Details on test conditions:
- TEST SYSTEM
- Testing facility: ECT Oekotoxikologie GmbH, Flörsheim am Main, Germany
- Test container: 24-well plates
- Amount of soil: 0.6 g of ash-soil-mixture
- No. of replicates per concentration: 4
- No. of replicates per control: number not reported (controll was siliceous sand)
DETAILS OF PREINCUBATION OF SOIL (if any):
- prior to testing soil (in 24-well plates) was heated twice to inhibit soil inherent dehydrogenase activity
TEST PERFORMANCE
- after the soil (in 24-well plates) was cooled down the inoculum was added and incubated for 2 hours on a shaker
- subsequent 0.8 mL of resazurin were added and fluorescence was measured over a period of 1 hour
- Photoperiod: continuously darkness
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- activity of dehydrogenase was assessed by photometric measurements of fluorescence - Nominal and measured concentrations:
- see table 1 in "any other information on materials and methods incl. tables"
- Reference substance (positive control):
- yes
- Remarks:
- BAC and zinc
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 1 000 g/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: dehydrogenase activity
- Conclusions:
- Under the conditions of this study no EC50 could be determined. Based on raw data (without statistical analysis) the test substance seems to have no significant effect on the dehydrogenase activity of Arthrobacter globiformis.
Reference
Under the conditions of this study no EC50 could be determined. Based on raw data (without statistical analysis) the test substance seems to have no significant effect on the dehydrogenase activity of Arthrobacter globiformis.
Table 2: Inhibition of dehydrogenase activity of Arthrobacter globiformis
Dilution |
1/128 |
1/64 |
1/32 |
1/16 |
1/8 |
1/4 |
1/2 |
100% ash |
inhibition of dehydrogenase activity [%] |
- |
- |
-0.6 |
-2.6 |
2.1 |
-1.9 |
-2.3 |
-1.6 |
Description of key information
No harmful effect could be observed, he test substance has no significant effect on the dehydrogenase activity of Arthrobacter globiformis.
Key value for chemical safety assessment
Additional information
On behalf of the VGB PowerTech e. V. the toxicity of ashes to plants was assessed by Roembke (2008) according to the DIN 38412-L48 (2002); German standard methods for the examination of water, waste water and sludge - Bio-assays (group L) - Part 48: Toxicity test with Arthrobacter globiformis for contaminated solids (L 48). The tested fly ash (FA1) was structural related to ash (residues), cenospheres and as cenospheres are a component of fly ash, these results can be used as read across.
During an exposure period of 3h, Arthrobacter globiformis was exposed to different concentrations of fly ash. Under the conditions of this study no EC50 could be determined. The test substance has no significant effect on the dehydrogenase activity of Arthrobacter globiformis.
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