Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- 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:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: as the test substance is a complex mixture of individual substances water accommodate fractions (WAFs) were prepared
=> Stock solution: 100 mg/L (saturated solution), volume 10 L
=> stock solution was stirred on a shaft stirrer throughout two days, ultrasonicated for 10 minutes and filtered through 0.45 micron filter.
The concentrations of solutions used in the preliminary and limit test were obtained by dilution of the stock saturated solution with dilution water.
- Differential loading: no
- Controls: yes - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Source: own laboratory breeding
- Age at study initiation: < 24 hours
- Method of breeding: aperiodic parthenogenesis
- Feeding during test: no
- Lighting: natural variation of daylight and darkness
- Number of test animals: 20 animals/test concentration and control (in preliminary test and limit test)
- Aeration: without aeration
ACCLIMATION
- Acclimation period: not specified (Adult gravid females are separated into dilution water. Young daphnia less than 24 hours are segregated to the handling container from which they entered the experiment.)
- Acclimation conditions: same as test
- Type and amount of food: a mixture of algae - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Hardness:
- Preliminary test: content of (Ca+Mg) ions 2.61 mmol/L
Limit test: content of (Ca+Mg) ions 2.59 mmol/L - Test temperature:
- Preliminary test: 19.6 °C - 19.8 °C
Limit test: 19.6 °C - 19.7 °C - pH:
- Preliminary test: 7.8 - 8.0 (based on 100 mg/L and control)
Limit test: 7.4 - 8.0 (based on 100 mg/L and control) - Dissolved oxygen:
- Preliminary test: 4.6 - 9.2 mg O2/L (based on 100 mg/L and control)
Limit test: 7.6 - 9.1 mg O2/L (based on 100 mg/L and control) - Nominal and measured concentrations:
- Preliminary test: 100%, 50%, 10%, 5%, and 1% of stock solution (100 mg/L)
Limit test: 100%, 91%, 83%, 75%, 68%, and 62% of stock solution (100 mg/L) - Details on test conditions:
- all informations reported in this field refer to the limit test
TEST SYSTEM
- Test vessel:
- Type: open
- Material, fill volume: glass beakers, 50 mL of test solution
- Aeration: no
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 2
- Biomass loading rate: 1 daphnia / 5 mL
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: standard dilution water according to ISO 6341-1982 (OECD 202, Annex 2)
- Conductivity: 0.135 µS/m
- Intervals of water quality measurement: only once before the test
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: natural variation of daylight and darkness
- Light intensity: natural variation of daylight and darkness
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- The acute toxicity is monitored by immobilisation of Daphnia magna after 24 and 48 hours.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.1
- Range finding study
- Test concentrations: 100%, 50%, 10%, 5%, and 1% of stock solution (100 mg/L) - Reference substance (positive control):
- yes
- Remarks:
- (pottasium dichromate)
- Duration:
- 48 h
- Dose descriptor:
- NOELR
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- LL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: not observed
- Observations on body length and weight: not observed
- Other biological observations: not observed
- Mortality of control: none
- Other adverse effects control: not observed - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Mortality: yes
- EC50: EC50 (24 h) = 1.15 mg/L, EC50 (48 h) = 0.8 mg/L - Validity criteria fulfilled:
- yes
- Conclusions:
- No immobilisation was observed in the limit test, concluding that the test substance is not acute toxic to Daphnia magna at a concentration of 100 mg/L.
Reference
Limit test
Table 1.Immobilisation of daphnia – limit test
Nominal concentration |
mg·L-1 |
100 |
91 |
83 |
75 |
68 |
62 |
C |
Saturated solution dosing |
mL·L-1 |
1000 |
910 |
830 |
750 |
680 |
620 |
C |
Number of live animals |
24 hours/1stseries |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
Number of live animals |
24 hours/2ndseries |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
Number of live animals |
24 hours/total |
20 |
20 |
20 |
20 |
20 |
20 |
20 |
Immobilisation % |
24 hours |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Number of live animals |
48 hours/1stseries |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
Number of live animals |
48 hours/2ndseries |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
Number of live animals |
48 hours/total |
20 |
20 |
20 |
20 |
20 |
20 |
20 |
Immobilisation % |
48 hours |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Table 2.Concentration of dissolved oxygen and test temperature – limit test
Nominal concentration |
mg·L-1 |
100 |
91 |
83 |
75 |
68 |
62 |
C |
t°C |
O2(mg·L-1) |
0 hour |
7.6 |
8.0 |
8.2 |
8.3 |
8.4 |
8.6 |
9.1 |
19.7 |
O2(mg·L-1) |
48 hours |
8.9 |
8.9 |
9.0 |
9.2 |
9.1 |
9.1 |
8.9 |
19.6 |
Table 3.pH of solutions – limit test
Nominal concentration |
mg·L-1 |
100 |
91 |
83 |
75 |
68 |
62 |
C |
pH |
0 hour |
7.4 |
7.5 |
7.5 |
7.5 |
7.5 |
7.8 |
8.0 |
pH |
48 hours |
7.9 |
7.9 |
7.9 |
8.0 |
8.0 |
8.0 |
8.0 |
Description of key information
The test substance is not harmful to aquatic invertebrates and it can be regarded that cenospheres has no harmful effects on invertebrates.
Key value for chemical safety assessment
Additional information
One limit tests according to OECD TG 202 water accommodate fractions (WAFs) of fly ash was prepared. The toxicity of the soluble fractions of the ash contained in the WAFs was assessed by observations on the mobility of Daphnia magna. After a testing period of 48 hours no adverse effects could be determined up to the loading rate of 100 mg/L. The tested fly ash was structural related to ash (residues), cenospheres and as cenospheres are a component of fly ash, these results can be used as read across. The EL50 could not be determined as they were beyond the range tested, exceeding a loading rate of 100 mg/L. NOEL for ash equalled a loading rate of >= 100 mg/L. Based on these findings the substance is not to be harmful to Daphnia magna and it can be concluded that cenospheres are also not harmful to aquatic invertebrates.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.