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EC number: 247-426-5 | CAS number: 26040-51-7
- 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: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 302 C (Inherent Biodegradability: Modified MITI Test (II))
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: activated sludge (domestic and industrial)
- Details on inoculum:
- Activated sludge from an aeration tank of two different wastewater treatment plants treating predominantly domestic wastewater (Wupper area water authority, WWTP Odenthal and WWTP Cologne-Stammheim).
Activated sludge from the aeration tanks of a wastewater treatment plant treating predominantly wastewater of industrial origin (WWTP Leverkusen Bürrig).
The three sludge types were mixed taking 2 parts from each of the two domestic WWTPS plus 1 part from the industrial WWTP.
Pre-treatment of inoculum:
-The three sludges of two different origins were mixed as described before.
-The combined sludge was washed twice by adding mineral medium and centrifuging for 10 min at 2000 rpm and 20 °C and decanting off the supernatant.
-An aliquot of the wet sludge was dried in order to determine the wet weight / dry weight ratio of the sludge and to prepare a stock suspension with a defined concentration of suspended solids.
-The calculated amount of sludge, needed to achieve 300 mL of this stock suspension of 5 g dw/L, was dissolved in mineral medium and then filled up to a defined end volume.
-Before use, the inoculum was stored for one day at room temperature under continuous shaking with aeration. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 30 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Pre-treatment of the test item
7.5 mg of the test item were added to the test flasks, filled with 200 mL of mineral medium. Afterwards the volume was made up to 250 mL with mineral medium plus inoculum to give a final concentration of 30 mg test item/L and a final concentration of suspended solids of 100 mg/L.
A measured volume of inoculated mineral medium, containing a known concentration of 30 mg/L of the test item was stirred in a closed flask at a constant temperature (25 ± 2 °C) under aerobic conditions in the dark.
The consumption of oxygen (BOD) was determined by measuring the drop in pressure in the automated respirometer flasks. Evolved carbon dioxide was absorbed in sodium hydroxide. The amount of oxygen taken up by the test item (corrected for uptake by blank inoculum, run in parallel) was expressed as a percentage of the theoretical oxygen demand (ThOD).
The test lasted for 28 days.
The endogenous activity of the inoculum was checked running parallel blanks with inoculum but without test item. A reference compound (sodium benzoate) was run in parallel to check the operation of the procedures.
A toxicity control (test item and reference compound mixed) was not run in parallel, because the chosen concentration of the test item was not inhibitory to microorganisms (see study 2012/0061/07).
Because of the nature of biodegradation and of the mixed bacterial populations used as inoculum, determinations of test item and for the inoculum blank were carried out in triplicate and for the reference compound in duplicate.
The oxygen uptake was calculated from the readings taken at regular and frequent intervals, using the method given by the manufacturer of the equipment. At the end of incubation, the pH was measured in the flasks. - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- Purity: 99.7 %
- Parameter:
- % degradation (O2 consumption)
- Value:
- 7
- Sampling time:
- 28 d
- Details on results:
- 6 % degradation after 7 days
7 % degradation after 14 days
6 % degradation after 21 days
7 % degradation after 28 days
pH after 28 days: 7.0 - 8.2 - Parameter:
- COD
- Value:
- 1.337 other: mg O2/mg test mat.
- Results with reference substance:
- The per cent degradation of the reference compound sodium benzoate reached the level of ≥ 40 % after 7 days, but remained 2 % below the level of ≥ 65 % after 14 days, caused by high activity of the sludge in the blank control. As the degradation was above 40 % after 7 days (65% degradation on day 7) and the test item showed only 7 % biodegradation after 28 days, the test was regarded to be valid.
- Validity criteria fulfilled:
- yes
- Remarks:
- The degradation of the reference compound reached the level of ≥ 40 % after 7 days, but remained 2 % below the level of ≥ 65 % after 14 days.As the test item showed only 7 % biodegradation after 28 days, the test was regarded to be valid.
- Interpretation of results:
- not inherently biodegradable
- Conclusions:
- Within 28 days a degradation of 7 % was determined according to the OECD Guideline 302 C. Therefore the substance is considered to be "Not Inherently Biodegradable".
- Executive summary:
To test for its inherent biodegradability potential, the substance was incubated for 28 days in continuously stirred 250 ml closed flask (three replicates) in the dark with an inoculum of mixed population of aquatic microorganisms (activated sludge) partially from domestic wastewater treatment plant and partially from industrial origin. In this assay, biodegradation was estimated by biological oxygen demand (BOD) over time. BOD was determined daily measuring the drop in pressure in the automated respirometer flasks. The incubation temperature was 25 ± 2 °C, pH was 7.0 - 8.2. The concentration of inoculum was 100 mg /L and the one of test substance was 30 mg/L. Degradation was calculated by subtracting the amount BOD in the negative (inoculum only) control from that in the test material or positive control at any given time point and divided by the chemical oxygen demand (COD) or theoretical oxygen demand (ThOD). The per cent degradation of the reference compound sodium benzoate reached the level of ≥ 40 % after 7 days, but remained 2 % below the level of ≥ 65 % after 14 days, caused by high activity of the sludge in the blank control. As the degradation was above 40 % after 7 days (65% degradation on day 7) and the test item showed only 7 % biodegradation after 28 days, the test was regarded to be valid. The test item is considered to be "Not Inherently Biodegradable".
Reference
Description of key information
Within 28 days a degradation of 7 % was determined in a study for inherent
biodegradability. Therefore the substance is considered to be "Not Inherently Biodegradable". As a conclusion, the substance is considered as not readily biodegradable as well, because there is no indication that ready biodegradability will be observed in a ready biodegradability test after the poor inherent biodegradability ratio of the substance in the present study.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
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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