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EC number: 213-563-4 | CAS number: 981-34-0
- 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

Oxidising properties
Administrative data
- Endpoint:
- oxidising solids
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.17 (Oxidising Properties (Solids))
- GLP compliance:
- no
Test material
- Reference substance name:
- 9β,11β-epoxy-17,21-dihydroxy-16β-methylpregna-1,4-diene-3,20-dione
- EC Number:
- 213-563-4
- EC Name:
- 9β,11β-epoxy-17,21-dihydroxy-16β-methylpregna-1,4-diene-3,20-dione
- Cas Number:
- 981-34-0
- Molecular formula:
- C22H28O5
- IUPAC Name:
- 17,21-dihydroxy-16-methyl-9,11-epoxypregna-1,4-diene-3,20-dione
- Test material form:
- solid: particulate/powder
Constituent 1
Results and discussion
Test results (Oxidising solids)
- Sample tested:
- 1:1 sample-to-cellulose ratio
- Parameter:
- burning time of reaction over a distance of 200 mm
- Result:
- 84 s
- Remarks on result:
- other: see tables below
Any other information on results incl. tables
The barium nitrate reference substance was mixed with dried cellulose in various ratios and
tested as described in the experimental section above.
Data and results of the different mixtures are reported in Table 1.
The maximum burning rate of the reference substance mixture was achieved with barium
nitrate mixed with dried cellulose in the proportion 40 to 60 (w/w).
TABLE 1 Test conducted on reference substance mixtures
Barium nitrate/cellulose (%w/w) | Burning time over 200 mm (sec) | Burning rate (mm/sec) |
60/40 | 382 | 0.52 |
50/50 | 330 | 0.61 |
40/60 | 302 | 0.66 |
0/100 | 315 | 0.63 |
The test item was mixed with dried cellulose in various ratios and tested as described in the
experimental section.
Data and results of the different mixtures are reported in Table 2.
TABLE 2 Test conducted on test item mixtures
Mixture | Test item/cellulose (5 w7w) | Burning time over 200 mm (sec) | Burning rate (mm/sec) |
A | 10/90 | 329 | 0.61 |
B | 20/80 | 285 | 0.70 |
C | 30/70 | 239 | 0.84 |
D | 40/60 | 287 | 0.70 |
E | 50/50 | 236 | 0.85 |
F | 60/40 | 293 | 0.68 |
G | 70/30 | 552 | 0.36 |
H | 80/20 | burning does not propagate | - |
I | 90/10 | burning does not propagate | - |
In order to investigate the possible false positive hypothesis, the tests with the four fastest
mixtures (from C to F) were repeated using kieselguhr (diatomaceous earth) as an inert
support instead of the combustible cellulose.
If the test item is a true oxidizing substance, the burning rate would be slower as the test item
has no material to oxidize.
The results obtained for the mixtures with kieselguhr are reported in Table 3.
TABLE 3 Test conducted using kieselguhr on the fastest mixtures
Mixture | Tet item/Kieselguhr (% w/w) | Burning time over 200 mm (sec) | Burning rate (mm/sec) |
C | 30/70 | burning does not propagate | - |
D | 40/60 | burning does not propagate | - |
E | 50/50 | 84 | 2.38 |
F | 60/40 | 87 | 2.30 |
The test showed burning rates for mixtures E and F definitely faster than those observed
using the combustible cellulose while for mixture C and D the burning did not propagate.
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- The test item was therefore not acting as an oxidizer but the “wick effect” was observed; i.e.
the test item melted when the ignition source was applied and became flammable in the presence of the solid carrier.
For mixtures C and D the test item ratios were too low to burn.
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