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EC number: 215-113-2 | CAS number: 1302-93-8
- 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
Additional toxicological data
Administrative data
- Endpoint:
- additional toxicological information
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2009-12-07 - 2010-03-18
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
- Type of study / information:
- Determination of the resorption in the digestive tract of White Fused Mullite according to DIN 19738 to determine the bioavailable parts.
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: DIN 19738
- Deviations:
- yes
- Remarks:
- Temperature in some conducts was outside the range of 37 ± 1 °C. The samples were stored in closed vessels at 2 - 8°C. The solutions were centrifuged at 4779 g, instead of 7000 g.
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Mullite
- EC Number:
- 215-113-2
- EC Name:
- Mullite
- Cas Number:
- 1302-93-8
- Molecular formula:
- Al6O13Si2
- IUPAC Name:
- Mullite; Al6O13Si2
Constituent 1
Results and discussion
Any other information on results incl. tables
Composition of Test Item
This was calculated from the data of X-ray analysis as presented in the following table:
Parameter |
Mrin g/mol |
% in Oxide |
% in Test Item |
µg/g Test Item |
Al2O3 |
101.9613 |
100% |
78.2% |
- |
Al |
26.98 |
52.92% |
41.39% |
413862.936 |
Calculation of Mobilised Mass
The mobilised masses of the elements were calculated as
wi,mob = (ci * V)/mE
with
wi,mob = mobilised part in µg/g test item per element
Ci = measured element concentration in µg/L
V = total volume in L of the aqueous phase (standard is 200 ml)
mE = weight of used test item (standard is 2.0 g)
Calculation of Bioaccessibility
Bioaccessibility was calculated as
Ri = (wi,mob * 100%)/wi,fest
with
Ri = bioaccessible part in %
wi,mob = mobilised part in µg/g test item per element
wi,fest = part of the element in the test item in µg/g
Results
The concentrations of Al in the tests are higher than in the blanks, calculation of a limit bio-accessibility for Al was based on the LOQ and compared to the values which were found in the blanks because calculation of effective concentrations was not reasonable.
Samples without addition of milk powder:
Parameter |
Mean |
Standard Deviation |
Relative Standard Deviation (%) |
Mobilised mass of test item in µg/g |
34.50 |
4.61 |
13.4% |
Bioavailability in % |
0.0083% |
0.0001 |
13.36% |
Samples with addition of milk powder:
Parameter |
Mean |
Standard Deviation |
Relative Standard Deviation (%) |
Mobilised mass of test item in µg/g |
1276.60 |
147.84 |
11.6% |
Bioavailability in % |
0.3085% |
0.0004 |
11.58% |
Applicant's summary and conclusion
- Conclusions:
- All values in the samples were marginally above the values of the blanks. The values in the samples with addition of milk powder were higher than the values in the samples without milk powder. Bio-accessibility in the samples with addition of milk powder was 0.3085 % with RSD of 11.58 %.
Bio-accessibility was doubtlessly low, though, as no values lying significantly above the blanks were found. - Executive summary:
All values in the samples were marginally above the values of the blanks. The values in the samples with addition of milk powder were higher than the values in the samples without milk powder. Bio-accessibility in the samples with addition of milk powder was 0.3085 % with RSD of 11.58 %.
Bio-accessibility was doubtlessly low, though, as no values lying significantly above the blanks were found.
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