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EC number: 304-990-8 | CAS number: 94313-91-4
- 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:
- March 2008
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP Guideline Study.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- Type: Activated sludge (domestic)
Source: municipal wastewater treatment plant Breisgauer Bucht
Concentration: 30 mg dry solids per litre
Dry solid of the activated sludge was determined as 535 g/L by weight measurements after 3 h drying at 105°e (mean of triplicate measurements) The activated sludge was washed twice by settling the sludge, decanting the supernatant and resuspending the sludge in aerated tap water. - Duration of test (contact time):
- 28 d
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 92.7
- Sampling time:
- 28 d
- Details on results:
- The mean degradation extent of the test item was 92.7% within 28 days after acidification (mean value of three test vessels). For finding the exact position of the 10-day window the degradation extents of the days without measurement were calculated by interpolation. On day 2 the calculated mean degradation extent of the test item was for the first time higher than 10% (mean value: 17.2%). Thus the end of the 10-day window was on day 12. The calculated degradation extent on day 12 was 81.6% (mean value). Therefore the test item reached the pass level for ready biodegradability (60% ThC02 and 10 d-window).
- Results with reference substance:
- The reference compound sodium benzoate reached the pass levels for ready biodegradability within 3 days.
The degradation in the toxicity control was 87.3% within 14 days and 99.5% within 28 days (after acidification), so there was no inhibition of the inoculum caused by the test item.
The highest mean COrevolution of the blank flasks in both test series was 22.1 mg/I within 28 days after acidification. - Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The mean degradation extent of the test item was 92.7% within 28 days after acidification (mean value of three test vessels). For finding the exact position of the 10-day window the degradation extents of the days without measurement were calculated by interpolation. On day 2 the calculated mean degradation extent of the test item was for the first time higher than 10% (mean value: 17.2%). Thus the end of the 10-day window was on day 12. The calculated degradation extent on day 12 was 81.6% (mean value). Therefore the test item reached the pass level for ready biodegradability (60% ThC02 and 10 d-window) and within the 10-day window.
- Executive summary:
In a reliable GLP OECD Guideline 301 B study (Ready Biodegradability: CO2 Evolution Test) the test substance KEU4587 was readily biodegradable and met the 10 -day window criterion. The mean degradation extent of the test item was 92.7% within 28 days after acidification (mean value of three test vessels).
- Endpoint:
- biodegradation in water: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline Study. Not GLP however, conducted in accordance with ISO/IEC 17025 (General requirements for the competence of testing and calibration laboratories).
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 311 (Anaerobic Biodegradability of Organic Compounds in Digested Sludge: Measurement of Gas Production)
- Deviations:
- no
- GLP compliance:
- yes
- Oxygen conditions:
- anaerobic
- Inoculum or test system:
- digested sludge
- Details on inoculum:
- Digested sludge from the digester of a municipal biological waste water treatment plant, not adapted, not pre-conditioned. 2.5 gil dry matter in the
final mixture Te - Duration of test (contact time):
- 68 d
- Parameter followed for biodegradation estimation:
- CH4 evolution
- Details on study design:
- Test unit: 1222 ml closed glass bottle containing a total volume of test solution of 800 ml; tightly closed with butyl rubber stoppers
Test medium: Anaerobic mineral salts medium (Table 3) prepared with double distilled water (conductivity: <1.5 ~S/cm; DOC: <03 mg/l)
Incubation: Temperature-controlled incubator (35 ± 2 °C)
Procedure:
The digested sludge was stored overnight at 35 ± 2 °C without adaptation. Prior to the test the sludge was washed twice with de-aerated tap water and once with de-aerated mineral medium. The test material was directly applied to give a final TOC concentration of about 100 mg/L.
For each test series the following number of test flasks was set up:
Test suspension (T) 3 replicates: containing digested sludge + test medium + test substance
Inoculum blank (B), 3 replicates: containing digested sludge + test medium
Procedure control (R), 2 replicates: containing digested sludge + test medium + diethyleneglycol as biodegradable reference compound known torapidly biodegrade under anaerobic conditions
The test vessels were incubated at 35 ± 2 °C for a test period of 69 days. The test vessels were not stirred, but agitated once per day (except weekends).
The biodegradation of the test material was followed by a pressure-measuring device at regular intervals. - Reference substance:
- diethylene glycol
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 68
- Sampling time:
- 68 d
- Remarks on result:
- other: A steady state (plateau) was reached after about 61 days of incubation
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 77
- Sampling time:
- 68 d
- Remarks on result:
- other: Including the produced inorganic carbon in the liquid phase
- Details on results:
- Based on the data of a pressure-measuring device Servo Q 8040 reached a biodegradability of 68% after 68 days of incubation, calculated with respect to the inorganic carbon production in the headspace.
A steady state (plateau) was reached after about 61 days of incubation.
Including the produced inorganic carbon in the liquid phase, measured at the end of the incubation period, a total biodegradability of Servo Q 8040 of 77% was attained within the incubation period of 68 days.
An adaptation period (lag phase) of about 2 -3 days was observed. - Results with reference substance:
- The positive control, diethylenegiycol, reached a steady state value (plateau) of 69% biodegradation after about 26 days of incubation (based on the inorganic carbon production in the headspace).
Including the produced inorganic carbon in the liquid phase, measured at the end of the incubation period, a total biodegradability of the reference compound of 78% was attained. The test was considered valid, since a plateau of more than 60% was reached within 60 days of incubation. - Validity criteria fulfilled:
- yes
- Interpretation of results:
- other: ultimately biodegradable
- Conclusions:
- Servo Q 8040 reached a steady state value of 60% or more under the conditions of the OECD guideline no. 311 within 60 days and, therefore, can be termed to be ultimately biodegradable under anaerobic conditions.
- Executive summary:
The ultimate biodegradability of the test substance exposed to microorganisms derived from activated sludge obtained from a municipal wastewater treatment plant was investigated under anaerobic static exposure conditions following OECD 311 methods. After 68 days the test substance showed 68% degradation, based on CO2 evolution. An adaptation period (lag phase) of about 2 -3 days was observed. The study concluded that the test substance can be considered to be ultimately biodegradable.
Referenceopen allclose all
The biodegradability of KEU4587 exposed to microorganisms derived from activated sludge obtained from a municipal wastewater treatment plant was investigated under aerobic static exposure conditions following OECD 301B methods. After 28 days the test substance showed 92.7% degradation, after acidification, based on measured CO2. The substance degraded 81.6% by the end of the 10-day window, meeting passing requirements. The study concluded that KEU4587 can be considered to be readily biodegradable and passing the 10-day window.
Description of key information
Two reliable biodegradation studies are available and both demonstrate biodegradability. The key study by Elementis Specialities (2008) determined that the test substance is readily biodegradable and meets the 10-day window criterion.
Elementis Specialities (2008) conducted a reliable (Klimisch 1) GLP compliant study according to OECD 301 B methods. The biodegradability of the substance exposed to microorganisms derived from activated sludge obtained from a municipal wastewater treatment plant was investigated under aerobic static exposure conditions. After 28 days the test substance showed 92.7% degradation, after acidification, based on measured CO2. The substance degraded 81.6% by the end of the 10-day window meeting the criterion. The study concluded that the substance can be considered to be readily biodegradable, passing the 10-day window.
Vendico Chemical (2010) conducted a reliable (Klimisch 1) study according to OECD 311 methods. The ultimate biodegradability of the substance exposed to microorganisms derived from activated sludge obtained from a municipal wastewater treatment plant was investigated under anaerobic static exposure conditions. After 28 days the test substance showed 68% degradation, based on CO2 evolution. An adaptation period (lag phase) of about 2 -3 days was observed. The study concluded that the substance can be considered to be ultimately biodegradable.
These studies demonstrate the ready and ultimate biodegradability of the substance and the key study by Elementis Specialities (2008) is taken for the biodegradation in water endpoint.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
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