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Reaction products of diazotised 2-amino-5-{[2-(sulfooxy)ethyl]sulfonyl}benzenesulfonic acid coupled with 4-amino-5-hydroxynaphthalene-2,7-disulfonic acid under acidic conditions, further coupled with diazotised reaction products of 2,4,6-trifluoro-1,3,5-triazine with 2-[(2-anilinoethyl)sulfonyl]ethyl hydrogen sulfate and 2,4-diaminobenzenesulfonic acid (1:1:1) under alkaline conditions, potassium sodium salts
EC number: 948-562-4 | CAS number: -
- 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
Link to relevant study record(s)
- Endpoint:
- oxidising solids
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- September 27, 2018 - October 04, 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.17 (Oxidising Properties (Solids))
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Contact with:
- powdered cellulose
- Key result
- Sample tested:
- test mixture as specified
- Remarks:
- 2:1 mixture test item : cellulose
- Parameter:
- preliminary test
- Result:
- 0 s
- Remarks on result:
- mixture does not ignite and burn
- Key result
- Sample tested:
- test mixture as specified
- Remarks:
- 1:9 mixture test item : cellulose
- Parameter:
- burning rate
- Result:
- 0.62 mm/s
- Key result
- Sample tested:
- reference mixture as specified
- Parameter:
- burning rate
- Result:
- 1.61 mm/s
- Interpretation of results:
- GHS criteria not met
- Executive summary:
The test item had no oxidizing properties in the sense of the European Commission Regulation (EC) No. 440/2008, Method A.17.
Reference
Preliminary test
Grinding, sieving and drying of the test item, barium nitrate, cellulose
The cellulose was driedby treating the sample at 105 °C ± 5 °C until the weight was constant. Due to the particle size of the cellulose grinding and sieving was not necessary. The barium nitrate was ground, sieved < 0.12 mm and dried by treating the sample at 105 °C ± 5 °C until the weight was constant. The test item wasdriedby treating the sample at 30 °C ± 5 °C under vacuum until the weight was constant. Grounding and sieving was not successful, as the test item agglomerated. Thus the test item was tested as delivered.
Preliminary test
Three test mixtures with the test item and cellulose 2:1 stopped burning after removing the flame. The mixtures coaled partially. Three test mixtures with barium nitrate/cellulose 2:1 burned down completely in 58 s, 61 s and 59 s, respectively. Due to the results of the preliminary test the main test had to be performed.
Main test
Four tests were performed for the reference mixture (barium nitrate and cellulose) with 50, 55, 60 and 70 wt. % oxidizer (barium nitrate). The results are shown in Table1.
Table1: Burning times and rates of reference mixtures
Barium nitrate [wt.%] |
Burning time over 200 mm [s] |
Burning rate [mm/s] |
50 |
152 |
1.32 |
55 |
141 |
1.42 |
60 |
124 |
1.61 |
70 |
164 |
1.22 |
The highest burning rate of 1.61 mm/s was found for the mixture with 60 wt. % oxidizer.
Mixtures of the test item with cellulose were prepared in between 10 and 90 wt. % of the test item and tested. Table2 shows the results.
Table2: Burning times and rates of test item mixtures
Test item[%] |
Burning time over 200 mm [s] |
Burning rate [mm/s] |
10 |
328 |
0.61 |
20 |
Flame distinguished after 25 seconds in the start zone. |
--- |
30 |
Flame distinguished in the start zone. |
--- |
40 |
Flame distinguished in the start zone. |
--- |
60 |
Flame distinguished in the start zone. |
--- |
90 |
The mixture could not be ignited. |
--- |
Due to the fact that the maximum burning rate of the mixtures of the test item with cellulose is lower than the maximum burning rate of the reference mixture, six tests were performed only with three mixtures (10 wt.%, 20 wt.% and 30 wt.% of the test item) with the highest burning rate to verify these values (see Table3).
Table3: Burning times and rates of the fastest test item mixtures
Test: |
t [s] |
V[mm/s] |
t [s] |
V[mm/s] |
t[s] |
V[mm/s] |
t [s] |
V[mm/s] |
t [s] |
V[mm/s] |
t [s] |
V[mm/s] |
10 % |
328 |
0.61 |
346 |
0.58 |
339 |
0.59 |
324 |
0.62 |
349 |
0.57 |
341 |
0.59 |
20 % |
1) |
- |
2) |
- |
2) |
- |
2) |
- |
3) |
- |
4) |
- |
30 % |
2) |
- |
2) |
- |
2) |
- |
2) |
- |
2) |
- |
2) |
- |
Remarks: 1) After 25 s and 4 mm the flame distinguished.
2) The flame distinguished in the start zone.
3) After 68 s and 28 mm the flame distinguished.
4) After 32 s and 2 mm the flame distinguished
The mixtures were measured 6 times. The mean burning rate for the mixture with the highest burning rate (10 %) was 0.62 mm/s. The difference between the mean burning rate and the maximum burning rate was ≤ 10 % for this mixture. The maximum burning rate of the mixtures of the test item and cellulose (0.62 mm/s) was lower than the maximum burning rate of the reference mixture of cellulose and barium nitrate (1.61 mm/s).
Due to the fact that the mixture of the test item with cellulose burned slower compared to the reference mixture it was concluded thatthe test item has no oxidizing properties.
Description of key information
The test item had no oxidizing properties in the sense of the European Commission Regulation (EC) No. 440/2008, Method A.17.
Key value for chemical safety assessment
- Oxidising properties:
- non oxidising
Additional information
Justification for classification or non-classification
Due to the fact that the mixture of the test item with cellulose burned slower compared to the reference mixture it was concluded that the test item has no oxidizing properties.
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