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EC number: 909-082-0 | CAS number: 938065-79-3
- 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
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- Flash point
- Auto flammability
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- 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
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- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
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- Nanomaterial surface chemistry
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- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
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- 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
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- Genetic toxicity
- Carcinogenicity
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- Specific investigations
- Exposure related observations in humans
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- Additional toxicological data

Biodegradation in water: screening tests
Administrative data
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 7 June 2006 to 6 December 2006
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study followed OECD Guideline 301 F
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- GLP according to German "Chemikaliengesetz", EC and OECD Guideline principles
Test material
- Reference substance name:
- 5,12-dihydro-2,9-dimethylquino[2,3-b]acridine-7,14-dione
- EC Number:
- 213-561-3
- EC Name:
- 5,12-dihydro-2,9-dimethylquino[2,3-b]acridine-7,14-dione
- Cas Number:
- 980-26-7
- Molecular formula:
- C22H16N2O2
- IUPAC Name:
- 2,9-dimethyl-5,12-dihydroquino[2,3-b]acridine-7,14-dione
Constituent 1
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): Activated sludge from the sewage plant in Hildesheim, Germany, comprising mostly municipal sewage (industrial chemical waste: 30-33%, referring to BOD)
- Pretreatment: The activated sludge was washed twice with autoclaved tap water. After the second washing the settled sludge was filled up with mineral salts medium and was maintained in an aerobic condition by aeration with CO2-free air for 4 days. 10 mL/L were used to initiate inoculation.
- Concentration of sludge: 10 ml/L
- Initial cell/biomass concentration: Colony forming units in the test vessels: 10E07-10E08 CFU/L - Duration of test (contact time):
- 28 d
Initial test substance concentration
- Initial conc.:
- 40 mg/L
- Based on:
- ThOD/L
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Mineral salts medium according to OECD 301 F
- Test temperature: 19.5 - 22.0°C
- pH:
Start End
Inoculum Control 7.59 1) 7.56
2) 7.54
Functional Control 7.59 7.73
Test Item 1) 7.56 1) 7.51
2) 7.53 2) 7.53
Toxicity Control 7.50 7.72
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: brown glass bottles (volume 500 mL)
- Number of culture flasks/concentration: two replicates
- Measuring equipment: The oxygen consumption was determined continuously from the pressure in the incubation vessels by OxiTop(R) measuring system at 360 measuring points (every 112 minutes) during the 28 d incubation period.
- Test performed in closed vessels: closed with OxiTop(R) device (see above)
SAMPLING
The temperature in the incubator was documented continuously by a thermohygrograph.
At the beginning of the test the pH-values in the brown glass bottles (test item, toxicity control) and in the measuring flasks (inoculum control before dividing, functional control) were determined. At the end of the test the pH-values of the test solutions in the brown glass bottles were determined.
CONTROL AND BLANK SYSTEM
- Inoculum blank: mineral salts medium
- Toxicity control: test item and reference substance in test concentrations
- Functional control: benzoic acid, sodium salt
Reference substance
- Reference substance:
- benzoic acid, sodium salt
Results and discussion
% Degradation
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 28 d
- Remarks on result:
- other: 0% biodegradation after 7, 14, 21 and 28 d
- Details on results:
- Test item was tested in two replicates (see Table 1 below for detailed results)
pH at the end of all tests (test item, controls) was in the range of 6.0-8.5 (validity criterion), for detailed values, see above
Toxicity control showed 39% biodegradation after 14 d and 29% biodegradation after 28 d
Inoculum control showed oxygen depletion of 33.8 mg/l after 28 d
BOD5 / COD results
- Results with reference substance:
- Functional control (reference substance: 45 mg/l sodium benzoate) showed 94% biodegradation after 14 d and 92% biodegradation after 28 d
Any other information on results incl. tables
Table 1: Mean Biodegradation of the Test Item in Comparison to the Functional Control and Toxicity Control
|
Biodegradation [%] |
||||
|
[d] |
||||
|
Replicate |
7 |
14 |
21 |
28 |
Test Item 40 mg/L
|
1 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
|
Functional Control 45 mg/L |
1 |
82 |
94 |
90 |
92 |
Toxicity Control 40 + 45 mg/L |
1 |
36 |
39 |
36 |
29 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- see above for details
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Not readily biodegradable in the 10-d window and after 28 days
- Executive summary:
The ready biodegradability in the Manometric Respirometry Test was determined with a non adapted activated sludge for the test item over a period of 28 days. The study was conducted from 2006-06-20 to 2006-07-18 according to OECD guideline 301 F at DR.U.NOACK-LABORATORIEN, D-31157 Sarstedt. The test item concentration selected as appropriate was 40 mg/L, corresponding to a ThOD of 87.2 mgO2/L in the test vessel. The oxygen was depleted by the respiration of bacteria and the degradation was followed by measuring the oxygen concentration. The biodegradation is therefore expressed as the percentage BOD and was calculated for each study day.
The mean oxygen depletion in the inoculum control came to 33.8 mgO2/L after 28 days. In order to check the activity of the test system sodium benzoate was used as functional control. The pass level > 60 % was reached after 3 days. The biodegradation rate came to 92 % after 28 days.
In the toxicity control containing both test and reference item 39 % degradation occurred within 14 days. The degradation of the reference item was not inhibited by the test item.
The biodegradation of the test item is shown in Table 1 and graphically in Figure 1 in comparison to the readily degradable functional control. The 10 % level (beginning of biodegradation) was not reached until 28 days. The mean biodegradation remained at 0 %.
The validity criteria of the guideline are fulfilled.
The test item must be regarded as not readily biodegradable in the 10-d-window and after 28 days.
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