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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 terrestrial plants
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to terrestrial plants: short-term
- 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
- Qualifier:
- according to guideline
- Guideline:
- other: ISO 11269-2 (1995)
- GLP compliance:
- no
- Remarks:
- Test were performed to fulfill the requirements of 2000/532/EG and Dir 91/689/EEC, GLP was not required for that purpose
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on preparation and application of test substrate:
- - for each dilution step in total 7200 g of mixture containing the corresponding amount of ash and soil was prepared
- each testing vessel was filled with 900 g (± 10 g) of this mixture - Species:
- Avena sativa
- Plant group:
- Monocotyledonae (monocots)
- Details on test organisms:
- - Common name: oat
- Variety: ARAGON
- Source of seed: Saat-Union GmbH, Iserhagen - Species:
- Brassica napus
- Plant group:
- Dicotyledonae (dicots)
- Details on test organisms:
- - Common name: rape
- Variety: LIFORUM
- Source of seed: LUFA, Speyer - Test type:
- early seedling growth toxicity test
- Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 14 d
- Remarks:
- starting after emergence of 50% of control plants
- Test temperature:
- 23 ± 3 °C
- Moisture:
- soil/substrate mixture in test vessels was moisturised with 100 mL per 900 g
- Details on test conditions:
- TEST SYSTEM
- Testing facility: ECT Oekotoxikologie GmbH, Flörsheim am Main, Germany
- Test container (type, material, size): plastic cups (Göttinger Pflanztöpfe) , 120x120x120 mm
- Amount of soil: 900 ± 10 g (fresh weight)
- Method of seeding: seeds were sown with tweezers in a depth of 1 cm
- No. of seeds per container: 10
- No. of plants (retained after thinning): 5
- No. of replicates per treatment group: 4
- No. of replicates per control: 4
SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
- Composition (if artificial substrate): no data
- Artificial soil: LUFA Standardboden 2.3 (standard soil)
NUTRIENT MEDIUM (if used)
- Description: Substral plant nutrition (Scotts Celaflor GmbH und Co KG, Ingelheim)
- Dilution: 70 mL of fertiliser/10 L deionised water
- Application: once
GROWTH CONDITIONS
- Photoperiod: 16 h light / 8 h dark
- Light intensity and quality: 13000 ± 2000 lx
- Relative humidity (%): 40 - 50
- Watering regime and schedules:
- Water source/type: deionised water
- Volume applied: 100 mL
- Interval of applications: once
- Method of application: test vessel was placed in a water reservoir
EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
- fresh weight, shoot length (above-ground), visual toxic effects (chlorosis, necrosis, deformation) - Nominal and measured concentrations:
- see table 1 in "any other information on materials and methods incl. tables"
- Reference substance (positive control):
- no
- Species:
- Avena sativa
- Duration:
- 14 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 g/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth
- Remarks on result:
- other: dilution: > 1/2
- Species:
- Brassica napus
- Duration:
- 14 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 g/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth
- Remarks on result:
- other: dilution: > 1/2
- Conclusions:
- EC50 could not be determined as even at the highest test concentration growth rate was not reduced by 50%. For both test species Avena sativa and Brassica napus EC50 is beyond 1000 g/kg soil d.w..
- Endpoint:
- toxicity to terrestrial plants: long-term
- Data waiving:
- other justification
- Justification for data waiving:
- other:
Referenceopen allclose all
Table 2: Reduction of fresh weight of Avena sativa and Brassica napus after 14 days
dilution |
|
1/64 |
1/32 |
1/16 |
1/8 |
1/6 |
1/4 |
1/3 |
1/2 |
100% ash |
reduction of weight [%] |
Avena sativa |
- |
- |
- |
- |
- |
5 |
7.3 |
34.6 |
65.3* |
Brassica napus |
- |
- |
- |
-18.9 |
- |
- |
-3.02 |
40.2 |
- |
* instead of pure ash (100% ash) a mixture of 71% ash and 29% soil was tested
Description of key information
EC50 could not be determined as even at the highest test concentration growth rate was not reduced by 50%. For both test species Avena sativa and Brassica napus EC50 is beyond 1000 g/kg soil d.w..
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 ISO 11269-2 (1995). During an exposure period of 14 days the plant species Avena sativa and Brassica napus were exposed to different concentrations of fly ash in soil.
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.
Fly ashes showed no or only slight growth reduction at concentration of greater than 1000 g/kg soil d. w. EC50 could not be determined as even at the highest test concentration growth rate was not reduced by 50%. For both test species Avena sativa and Brassica napus EC50 is beyond 1000 g/kg soil d. w.
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