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EC number: 919-979-9 | 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:
- Study initiation date 18 January 2019
Experimental starting date 22 January 2019
Experimental completion date 19 February 2019 - Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, non-adapted
- Details on inoculum:
- The activated sludge used was sampled from the aeration tank of the ARA Werdhölzli (CH-8048
Zürich), a municipal biological waste water treatment plant on 17 January 2019, 8:30 am.
In accordance with the guideline, this sludge was not pre-adapted to the test item but pre-conditioned to reduce the amount of CO2 produced in the blank controls. In the pre-conditioning procedure, the sludge was washed twice with tap water and once with test medium right after sampling from the waste water treatment plant. After centrifugation, the sludge was suspended in test medium at about 2 g/l dry matter and kept under constant aeration and stirring without feeding for five days until test start.
On the day of test start, this sludge suspension was diluted down to 300 mg/l dry matter, i.e. ten-fold the final concentration, and an appropriate amount of this suspension was added to the flasks (except to the abiotic sterile control). - Duration of test (contact time):
- 28 d
- Initial conc.:
- 28.3 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- inorg. C analysis
- Details on study design:
- The gas-absorption bottles were filled with the 0.13 M KOH solution. The test vessels were connected to the air supply (CO2-free, synthetic) and the gas-absorption bottles were connected to the test vessels, so that the air leaving the individual vessels was passed through the KOH solution and the CO2 produced by mineralisation of the test item trapped therein.
All test vessels were stirred thoroughly and aerated with the aforementioned air supply for the whole test period.
The CO2 trapped in the KOH solutions was determined as inorganic carbon at frequent time intervals to allow for the assessment of the 10-day window for biodegradation in the vessels.
The temperature was measured several times per day with a datalogger.
At the end of the test, the pH and the IC concentration in each test vessel was determined. - Reference substance:
- benzoic acid, sodium salt
- Key result
- Parameter:
- % degradation (TOC removal)
- Value:
- 68
- Sampling time:
- 28 d
- Key result
- Parameter:
- % degradation (TOC removal)
- Value:
- 41
- Sampling time:
- 10 d
- Details on results:
- Reaction products of olive oil and ozone (NOVOX) (EC no. 919–979–9) did not reach the pass level of 60% for ready biodegradability in the CO2 Evolution Test within the 10-d window, and therefore, cannot be termed as readily biodegradable. However, the pass level of 60% was reached within 28 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- inherently biodegradable, fulfilling specific criteria
- Conclusions:
- According to OECD guideline 301, a substance is considered "readily biodegradable in the CO2 evolution test" if at least 60% biodegradation, based on IC measurements, is achieved within 10 days after the attainment of 10% biodegradation (10 day-window), and within a total of 28 days.
If the results of the test indicate that the pass level criterion is almost fulfilled (i.e. degradation slightly below 60%) such results can be used to indicate inherent biodegradability. This is also the case when the pass level criterion is fulfilled but the 10-day window criterion is not.
The substance reach thedegradation level of 68% at 28 days and can be considered "inherent biodegradable". - Executive summary:
The biodegradability of Reaction products of olive oil and ozone (NOVOX) (EC no. 919–979–9) exposed to microorganisms derived from the activated sludge of a municipal sewage treatment plant was investigated under aerobic static exposure conditions according to the test OECD guideline 301 B.
The biodegradability of Reaction products of olive oil and ozone (NOVOX), based on CO2 evolution and expressed as % of the total organic carbon (TOC) applied, was calculated to be 68% after an incubation time of 28 days.
At the end of the 10-d window, the biodegradation of Reaction products of olive oil and ozone (NOVOX) reached 49%.
Significant biodegradation of the test item was observed after a lag phase of about 4.5 days.
The positive control, sodium benzoate, reached 73% biodegradation after 14 days, thus confirming suitability of inoculum and test conditions.
Reaction products of olive oil and ozone (NOVOX) (EC no. 919–979–9) did not reach the pass level of 60% for ready biodegradability in the CO2 Evolution Test within the 10-d window, and therefore, cannot be termed readily biodegradable. However, the pass level of 60% was reached within 28 days.
Reference
Description of key information
The biodegradability of Reaction products of olive oil and ozone (NOVOX), based on CO2 evolution and expressed as % of the total organic carbon (TOC) applied, was calculated to be 68% after an incubation time of 28 days.
At the end of the 10-d window, the biodegradation of Reaction products of olive oil and ozone (NOVOX) reached 41%.
Significant biodegradation of the test item was observed after a lag phase of about 4.5 days.
The positive control, sodium benzoate, reached 73% biodegradation after 14 days, thus confirming suitability of inoculum and test conditions.
Reaction products of olive oil and ozone (NOVOX) (EC no. 919–979–9) did not reach the pass level of 60% for ready biodegradability in the CO2 Evolution Test within the 10-d window, and therefore, cannot be termed as readily biodegradable. However, the pass level of 60% was reached within 28 days.
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable, fulfilling specific criteria
- Type of water:
- other: Tap water
Additional information
inherently biodegradable, fulfilling specific criteria
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