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EC number: 700-327-5 | CAS number: 1061328-86-6
- 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: screening test, other
- Remarks:
- inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study, basic information available by the test report
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 302 B (Inherent biodegradability: Zahn-Wellens/EMPA Test)
- Deviations:
- no
- GLP compliance:
- no
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
No surrogate or analogue material was used. - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, adapted
- Details on inoculum:
- - Source of activated sludge: aeration tank of the sewage treatment plant "Aquanet S.A., Centralna Oczyszczalnia, Scieków ul. Gdynska 1, Kozieglowy
- Date of collection: 2010-03-15
- Pretreatment: Washing twice, centrifugation for separation of the sludge
- Concentration of activated sludge in reaction mixture: 0.3 g ss/L - Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- DOC
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Test temperature: 20 - 25 °C
- Aeration of dilution water: yes
- Suspended solids concentration: 0.3 g ss/L medium
- Continuous darkness: yes
TEST SYSTEM
- Test suspension: mineral medium, test substance and inoculum
- Procedure control: mineral medium, reference substance and inoculum
- Inoculum blank: mineral medium and inoculum
- Toxicity control: mineral medium, test substance, reference substance and inoculum
- Test volume: 1000 mL
- Chemical analysis: Determination of dissolved total organic carbon (DOC)
- Test apparatus: Spectrophotometer CADAS Dr. Lange
SAMPLING
- Sampling frequency: daily - Reference substance:
- other: Sodium benzoate
- Preliminary study:
- Not applicable.
- Test performance:
- Neither unusual observations during test nor any other information affecting results are reported.
- Parameter:
- % degradation (DOC removal)
- Value:
- 1.5
- Sampling time:
- 7 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 3.2
- Sampling time:
- 14 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 5.3
- Sampling time:
- 21 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 7.1
- Sampling time:
- 27 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 8.2
- Sampling time:
- 28 d
- Details on results:
- No toxic effects to bacteria were observed.
- Results with reference substance:
- The reference compound reached the level of greater or equal to 70 % degradation within 14 days, since at this time point, 98 % degradation has had occurred.
- Validity criteria fulfilled:
- yes
- Remarks:
- Validity criteria of the applied guideline were met.
- Interpretation of results:
- not inherently biodegradable
- Conclusions:
- The study report describes about a valid biodegradation study according to OECD Guideline 302 B (Zahn-Wellens/EMPA Test). According to the obtained degradation of 8.2 % after 28 days, the test substance is considered as not inherently biodegradable.
- Executive summary:
The biodegradation potential of Fe(III)HBED was investigated according to OECD Guideline 302 B (Chojnacka, 2010). Activated sludge was used as inoculum and mixed with the test substance and mineral medium in 2 parallels. Further flasks were the procedure control (with the reference substance sodium benzoate), the inoculum blanks (each in 2 parallels) and one toxicity control (containing mineral medium, test substance, reference substance and inoculum). The suspended solid concentration was 0.3 g ss/L in each flask. The mixtures were agitated and aerated at 20 - 25 °C in the dark for a period of 28 days. The biodegradation process is monitored by determination of dissolved total organic carbon (DOC) with a spectrophotometer in filtered samples taken in daily intervals. The ratio of eliminated DOC, corrected for blank after each time interval, to the initial DOC value is expressed as the % biodegradation at the sampling time. The reference item attained 98 % degradation already after 14 days incubation, thereby fulfilling the validity criteria of the applied guideline, concluding that more or equal to 70 % degradation should have been occurred after 14 days. The test substance showed no toxic effects towards the used bacteria, since the toxicity control attained 55 % degradation after 28 days. The DOC content of the blank was below 10 mg/L at the start of the experiment. The test substance attained 3.2 % degradation after 14 days and 8.2 % degradation after 28 days, respectively. The test substance cannot be regarded as inherently biodegradable.
Reference
Description of key information
OECD 302B, Zahn-Wellens Test: 8.2 % degradation after 28 days - not inherently biodegradable
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
The biodegradation potential of Fe(Na)HBED was investigated according to OECD Guideline 302 B (Chojnacka, 2010). Activated sludge was used as inoculum and mixed with the test substance and mineral medium in 2 parallels. Further flasks were the procedure control (with the reference substance sodium benzoate), the inoculum blanks (each in 2 parallels) and one toxicity control (containing mineral medium, test substance, reference substance and inoculum). The suspended solid concentration was 0.3 g ss/L in each flask. The mixtures were agitated and aerated at 20 - 25 °C in the dark for a period of 28 days. The biodegradation process is monitored by determination of dissolved total organic carbon (DOC) with a spectrophotometer in filtered samples taken in daily intervals. The ratio of eliminated DOC, corrected for blank after each time interval, to the initial DOC value is expressed as the % biodegradation at the sampling time. The reference item attained 98 % degradation already after 14 days incubation, thereby fulfilling the validity criteria of the applied guideline, concluding that more or equal to 70 % degradation should have been occurred after 14 days. The test substance showed no toxic effects towards the used bacteria, since the toxicity control attained 55 % degradation after 28 days. The DOC content of the blank was below 10 mg/L at the start of the experiment. The test substance attained 3.2 % degradation after 14 days and 8.2 % degradation after 28 days, respectively. The test substance cannot be regarded as inherently biodegradable.
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