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EC number: 432-080-1 | 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 16 December 1998 to 13 January 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Deviations:
- no
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- Type: mixed population of aquatic microorganisms (activated sludge)
Origin: secondary effluent of a domestic sewage treatment plant
Date of collection: 11.12.1998
Pre-treatment: none - Duration of test (contact time):
- 28 d
- Initial conc.:
- 4.8 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- The test substance is suspended in a mineral medium, inoculated with a mixed population of aquatic microorganisms and incubated for 28 days under aerobic conditions in the dark at 20 ±1°C. During this period, the biodegradation of the test substance is determined on the basis of the reduction of dissolved oxygen.
Test substance: Reaktiv-Orange DYPR 1410
Concentration of the stock solution: 1.0gl test substance
Remarks: none
Initial concentration: 4.8mg/l test substance
Reference substance
Name of reference substance: Aniline
Purity: at least 99.5%
Initial concentration: 2.0mg/l reference substance
Inoculum
Source of sewage effluent: secondary effluent of a domestic sewage treatment plant
Treatment given: separation of coarse particles by filtration
Concentration of effluents in reaction mixture: 5 ml/l
Preconditioning: aeration for 5 days
Study conditions
Duration: 28 days
Test temperature20 ± 1°C - Reference substance:
- aniline
- Test performance:
- The test performed in accordance with the recommendations of the test method.
- Parameter:
- % degradation (O2 consumption)
- Value:
- 1
- Sampling time:
- 28 d
- Details on results:
- In parallel preparations with the reference substance aniline a degradation of 85 % was achieved within 14 days.
Previously a Modified OECD Screening Test has been carried out with the test substance. Further experiments showed that the DOC of the test substance decreases by adsorption. Therefore the Modified OECD Screening Test is an inappropriate test method. - Results with reference substance:
- Dissolved oxygen of reference substance: (mg O2/l after x days)
Bottle No. 0 days Bottle No. 7 days Bottle No. 14 days Bottle No. 21 days Bottle No. 28 days
11 9.66 13 5.86 15 5.14 17 4.26 19 4.21
12 9.68 14 6.08 16 4.69 18 4.28 20 4.26
Mean 9.67 5.97 4.92 4.27 4.24
Reference substance
Test concentration: 2.0 mg/l
ThOD: 2409 mg/g
COD: --- mg/g DO depletion after n days [mg/l]
7d 14d 21d 28d
No.1: (mt0 – mtx) – (mb0 – mbx) 3.19 3.84 4.53 4.60
No.2: (mt0 – mtx) – (mb0 – mbx) 2.99 4.31 4.53 4.57
D1: % Degradation 66 80 94 95
D2: % Degradation 62 89 94 95
D, Mean 64 85 94 95 - Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Within the test period of 28 days, a degradation of 1 % was determined for Realktiv-Orange DYPR 1410.
- Executive summary:
Study conducted to procedure: Biodegradability - Closed Bottle Test Method according to Council Directive 92/69 EEC, Method C.4-E, in compliance with GLP.
The test substance is suspended in a mineral medium, inoculated with a mixed population of aquatic microorganisms and incubated for 28 days under aerobic conditions in the dark at 20±1°C. During this period, the biodegradation of the test substanceisdetermined on the basis of the reduction of dissolved oxygen.
In parallel preparations with the reference substance aniline a degradation of 85 % was achieved within 14 days.
Previously a Modified OECD Screening Test has been carried out with the test substance. Further experiments showed that the DOC of the test substance decreases by adsorption. Therefore the Modified OECD Screening Test is an inappropriate test method.
Within the test period of 28 days, a degradation of 1 % was determined for Realktiv-Orange DYPR 1410.
Hence, Reaktiv-Orange DYPR 1410 is not readily biodegradable.
Reference
Oxygen measurement
Dissolved oxygen of blank inoculum: (mg O2/l after x days)
Bottle No. |
0 days |
Bottle No. |
7 days |
Bottle No. |
14 days |
Bottle No. |
21 days |
Bottle No. |
28 days |
1 |
9.68 |
3 |
9.02 |
5 |
9.01 |
7 |
8.81 |
9 |
8.89 |
2 |
9.66 |
4 |
9.09 |
6 |
8.96 |
8 |
8.78 |
10 |
8.75 |
Mean |
9.67 |
|
9.06 |
|
8.99 |
|
8.80 |
|
8.82 |
Dissolved oxygen of test substance: (mg O2/l after x days)
Bottle No. |
0 days |
Bottle No. |
7 days |
Bottle No. |
14 days |
Bottle No. |
21 days |
Bottle No. |
28 days |
21 |
9.61 |
23 |
9.13 |
25 |
8.98 |
27 |
8.76 |
29 |
8.81 |
22 |
9.68 |
24 |
9.07 |
26 |
9.10 |
28 |
8.79 |
30 |
8.73 |
Mean |
9.65 |
|
9.10 |
|
9.04 |
|
8.78 |
|
8.77 |
Dissolved oxygen of toxicity control: (mf O2/l after x days)
Bottle No. |
0 days |
Bottle No. |
7 days |
Bottle No. |
14 days |
Bottle No. |
21 days |
Bottle No. |
28 days |
31 |
9.63 |
33 |
6.06 |
35 |
5.00 |
37 |
4.68 |
39 |
4.21 |
32 |
9.63 |
34 |
6.16 |
36 |
5.10 |
38 |
4.43 |
40 |
4.39 |
Mean |
9.63 |
|
6.11 |
|
5.05 |
|
4.56 |
|
4.30 |
Results – DO depletion: % Degradation
Test substance Test concentration: 4.8mg/l ThOD: 1241 mg/g COD: --- mg/g |
DO depletion after n days [mg/l] |
|||
7d |
14d |
21d |
28d |
|
No.1: (mt0 – mtx) – (mb0 – mbx) |
0.00 |
0.00 |
0.00 |
0.00 |
No.2: (mt0 – mtx) – (mb0 – mbx) |
0.00 |
0.00 |
0.02 |
0.10 |
D1: % Degradation |
0 |
0 |
0 |
0 |
D2: % Degradation |
0 |
0 |
0 |
2 |
D, Mean |
0 |
0 |
0 |
1 |
* Toxicity control |
DO depletion after n days [mg/l] |
|||
7d |
14d |
21d |
28d |
|
No.1: (mt0 – mtx) – (mb0 – mbx) |
2.96 |
3.95 |
4.08 |
4.57 |
No.2: (mt0 – mtx) – (mb0 – mbx) |
2.86 |
3.85 |
4.33 |
4.39 |
D1: % Degradation |
27 |
37 |
38 |
42 |
D2: % Degradation |
27 |
36 |
40 |
41 |
D, Mean |
27 |
37 |
39 |
42 |
Comments: * In the toxicity control 4.8 mg/l test substance and 2.0 mg/l reference substance were used. The ThOD values respectively COD values of these substances are shown in the table above.
Description of key information
Within the test period of 28 days, a degradation of 1 % was determined for Reaktiv-Orange DYPR 1410. Hence, Reaktiv-Orange DYPR 1410 is not readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
- Type of water:
- freshwater
Additional information
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.
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