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EC number: 247-557-8 | CAS number: 26264-06-2
- 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 soil
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in soil: simulation testing
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Justification for type of information:
- Sodium dodecylbenzenesulfonate (CAS# 25155-30-0 , EC Number; 246-680-4 ) is a very close analogue of Calcium dodecylbenzenesulfonate (CAS No 26264-06-2, EC Number; 247-557-8) ) and read-across is valid.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 307 (Aerobic and Anaerobic Transformation in Soil)
- GLP compliance:
- not specified
- Test type:
- laboratory
- Radiolabelling:
- yes
- Oxygen conditions:
- aerobic/anaerobic
- Soil classification:
- other: Alfisol
- Details on soil characteristics:
- - Soil : Air-dried and sifted to a particle size of 0.125 mmparticle size distribution ; Clay(<2 μm) 17%, silt(2-63 μm) 75%, sand(0.63-2 mm) 8%, organic matter 2.45%- Soil pH : 7.3
- Initial conc.:
- 15 other: μg
- Based on:
- test mat.
- Details on experimental conditions:
- - Experience vessels; 1 litre wide-mouth bottles- Incubation mixture; 50g soil and 150ml water were equilibrated for 7 days at 35 deg C in oxygen or nitrogen. Then 15μg of 14C-labelled chemical was added in aqueous solution ot suspension.- Mechnical mixing; continuous shaking in a water bath (35 deg C)
- % Degr.:
- 40.6 - 51.9
- Parameter:
- CO2 evolution
- Sampling time:
- 42 d
- Transformation products:
- yes
- Conclusions:
- n-Dodecylbenzenesulphonate was readily biodegradable. And the degradation (mineralization) values in anaerobic environment was faster than those in aerobic environment.
- Endpoint:
- biodegradation in soil: simulation testing
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Justification for type of information:
- C12 LAS; Linear Alkylbenzene Sulfonate (LAS)) is a very close analogue of Calcium dodecylbenzenesulfonate (CAS No 26264-06-2, EC Number; 247-557-8) ) and read-across is valid.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 307 (Aerobic and Anaerobic Transformation in Soil)
- GLP compliance:
- not specified
- Test type:
- laboratory
- Radiolabelling:
- yes
- Soil classification:
- other: : Soil type in Rapid city is the sandy loam and soil type in Harleysville is the loamy sand.
- Details on soil characteristics:
- Soils were obtained from sludge-amended agricultural fields in Rapid city and Harleysville. Soil type in Rapid city is the sandy loam and soil type in Harleysville is the loamy sand.
- Initial conc.:
- 250 mg/kg soil d.w.
- Based on:
- test mat.
- Soil No.:
- #1
- Temp.:
- 20℃
- Humidity:
- 35% moisture level
- Details on experimental conditions:
- Tesk flasks were continuously flushed with CO2-free air at >>50ml/min and incubated 20 +/- 2 deg C. Half-lives ofr mineralization(t 1/2) were calculated from the relationship t 1/2=ln2/k1(k1=first-order rate conctant).
- DT50:
- 23.1 d
- Type:
- (pseudo-)first order (= half-life)
- Temp.:
- 20 °C
- Transformation products:
- yes
- Details on results:
- Half-lives for mineralization of the C12-LAS homolog is 23.1 days.
- Conclusions:
- Half-lives for mineralization of the C12-LAS homolog is 23.1 days.
Referenceopen allclose all
Description of key information
Biodegradation in soil
Ward and Larson (1989) conducted a laboratory study and observed the biodegradation rate constant and half-life for C12-LAS in sludge-amended soil. The biodegradation rate constant for C12-LAS is 0.030 day-1and half-life for C12-LAS is 23.1 days. Scheunertet al., (1987) measured the biomineralization rate of dodecylbenzenesulfonate in soil/water suspension under anaerobic and aerobic conditions for 42 days. The results (40.6%14CO2: aerobic, 51.9%14CO2: anaerobic) showed that the substance was readily biodegradable by the micro-organisms present in soil.
Key value for chemical safety assessment
- Half-life in soil:
- 23.1 d
- at the temperature of:
- 20 °C
Additional information
Biodegradation in soil
Ward and Larson (1989) conducted a laboratory study and observed the biodegradation rate constant and half-life for C12-LAS in sludge-amended soil. The biodegradation rate constant for C12-LAS is 0.030 day-1and half-life for C12-LAS is 23.1 days. Scheunertet al., (1987) measured the biomineralization rate of dodecylbenzenesulfonate in soil/water suspension under anaerobic and aerobic conditions for 42 days. The results (40.6%14CO2: aerobic, 51.9%14CO2: anaerobic) showed that the substance was readily biodegradable by the micro-organisms present in soil.
Table Summary of Biodegradationin soil
Type/ Method |
Test material |
Degradation |
Duration |
References |
Aerobic/ Other |
C12-LAS |
50% |
23.1 days |
Ward and Larson, 1989 |
Aerobic and Anaerobic/ Other |
Dodecylbenzenesulfonate |
40.6%14CO2of mineralization (aerobic), 51.9%14CO2of mineralization (anaerobic) |
42 days |
Scheunertet al., 1987 |
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