Registration Dossier
Registration Dossier
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: 944-092-9 | 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:
- from 1991-04-17 to 1991-05-22
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.6 (Degradation: Chemical Oxygen Demand)
- Version / remarks:
- 1984
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Type of inoculum: Activated sludge bacteria.
- Source of inoculum: The aeration stage of the Severn Trent PLc Sewage treatment plant at Belper, Derbyshire (U.K), treating predominantly domestic sewage.
- Data of collection: 1991-04-17
- Preparation: The sample was allowed to settle and the supernatant filtered through Whatman GFA filter paper (first 200 mL discarded) - Duration of test (contact time):
- > 0 - <= 28 d
- Initial conc.:
- ca. 2 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- DOC removal
- Remarks:
- (DOC for each medium were determined, in duplicate at 0.5, 15 and 28 days by means of a yellow Springs 800 probe).
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Standard nutrient medium according to OECD guideline
- Additional substrate: No
- Solubilising agent: No
- Test temperature: 21 °C
- pH adjusted: no
- Aeration of dilution water: yes
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: 250-300 mL BOD bottles (darkened glass) with ground glass stoppers
- Number of culture flasks/concentration: 2 flasks/concentration
Test concentrations:
(a) Non-inoculated dilution water: 2 flasks
(b) Inoculated dilution water: 2 flasks
(c) 2 mg/L test material: 2 flasks
(d) 3 mg/L sodium benzoate: 2 flasks
Test media b, c and d were inoculated with activated sludge filtrate at the rate of 1 drop of Inoculum per litre.
Procedure: BOD bottles were filled, by siphon and firmly stoppered to exclude all air bubbles. Sufficient bottles were prepared to allow single oxygen determination per bottle to be made at 0, 5, 15 and 28 days for each test medium (duplicate bottles at each sampling time).
Bottles were incubated in a water bath at 21°C for 0, 5, 15 or 28 days as appropriate.
- Measuring equipment: Dissolved oxygen concentration for each test medium were determined, in duplicate, at 0, 5, 15 and 28 days by mean of a yellow Springs 800 Probe (Model 800)
- Test performed in open system: no
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes
- Abiotic sterile control: no
- Toxicity control: no
- Positive control: Performed with the reference substance sodium benzoate - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- 3 mg/L sodium benzoate
- Preliminary study:
- Not performed.
- Test performance:
- The validity criteria were fulfilled.
- Key result
- Parameter:
- % degradation (DOC removal)
- Remarks:
- only 6% degradation with 28 days
- Value:
- ca. 6
- Sampling time:
- 28 d
- Remarks on result:
- other: Observations: Dissolved oxygen concentrations for each test medium were determined, in duplicate, at 0, 5, 15 and 28 days by means of a Yellow Springs BOD Probe.
- Details on results:
- Kayarus Supra Rubine BLN attained only 6% degradation with 28 days therefore is considered to be not readily biodegradable.
- Results with reference substance:
- Sodium benzoate attained 103% degradation within 28 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- Kayarus Supra Rubine BLN attained only 6% degradation with 28 days therefore is considered to be not readily biodegradable.
- Executive summary:
A study on biodegradation was performed according to OECD 301 D under GLP conditions. Dissolved oxygen measurements for the test and standard material solutions, together with the inoculated and non-inoculated blank controls, at 0, 5, 15 and 28 days were assessed. Sodium benzoate attained 103% degradation within 28 days. The validity criteria were met. Kayarus Supra Rubine BLN attained only 6% degradation with 28 days therefore is considered to be not readily biodegradable.
Reference
Table 1: Mean Oxygen Depletion and percentage Biodegradation Values.
Test Series |
Day |
||
|
5 |
15 |
28 |
(a) Dilution water without inoculum O2 depletion in (mg O2/L) % degradation |
0.025 |
0.075 |
0.175 |
(b) Dilution water with inoculum O2 depletion in (mg O2/L) % degradation |
0.075 |
0.175 |
0.200 |
(c) Kayarus Supra Rubine BLN (2mg/L) with inoculum O2 depletion in (mg O2/L) % degradation |
0.125 4 |
0.100 4 |
0.175 6 |
|
|
|
|
(d) Standard material, Sodium benzoate (3mg/L) with inoculum O2 depletion in (mg O2/L) % degradation |
4.575 |
4.750 |
5.150 |
|
91 |
95 |
103 |
Closed bottle test according to OECD Guideline No. 301 referenced as Method C.6 of Commission Directive 84/449/EEC
Duration: 28 days
Temperature: 21°C
Test concentration: 2 mg/L
Oxygen depletion (28 days): 0.175 mg O2/L
Theoretical oxygen demand (ThOD): 1.40 mg O2/L
Percentage Biodegradation (28 days): 6 %
Method of Preparation: direct dispersion in culture medium
Results:
Kayarus Supra Rubine BLN attained only 6% degradation with 28 days and so cannot, therefore, be considered as ready biodegradable.
Sodium benzoate attained 103% degradation within 28 days.
Oxygen depletions in the inoculated and non-Inoculated control series were within the prescribed limits*.
* Non-inoculated control:
< 0.3 mg O2/L after 5 days
<
0.4 mg O2/L after 28 days
Inoculated control:
<
0.5 mg O2/L after 5 days
< 0.6 mg O2/L after 28 days
Description of key information
The read across substance Kayarus Supra Rubine BLN attained only 6% degradation with 28 days, therefore the test substance is considered to be as not readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
A study on biodegradation was performed according to OECD 301 D under GLP conditions. Dissolved oxygen measurements for the test and standard material solutions, together with the inoculated and non-inoculated blank controls, at 0, 5, 15 and 28 days were assessed. Sodium benzoate attained 103% degradation within 28 days. The validity criteria were met. The read across substance Kayarus Supra Rubine BLN attained only 6% degradation with 28 days therefore is considered to be not readily biodegradable.
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.