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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 water and sediment: simulation tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: sewage treatment 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:
- no guideline followed
- Principles of method if other than guideline:
- Radiolabeled LAS was dosed at an environmentally relevant concentration into biotic and abiotic activated sludge. Activated sludge mixed liquor was used from two STP (Polk Run and Sycamore) near Cincinnati. Standard methods were used and the test flasks (reactors) were maintained at 20+/-2oC.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- 14C-[uniform ring] C12 LAS; radiochemical purity exceeded 98% based upon TLC.14C-[uniform ring] C12 LAS was obtained from New England Nuclear(Boston, MA) an had a specific activity of 68 mCi/mg.
- Radiolabelling:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, non-adapted
- Details on source and properties of sediment:
- Test medium :Activated sludge mixed liquor was collected from Pol Run Sewage Treatment (STP) and Sycamore Sewage Treatmnet (STP) which are located near on 1995. Both treatment plants receive mainly domestic wastewater and are located near Cincinnati, OH.
- Duration of test (contact time):
- 52 h
- Initial conc.:
- 1 mg/L
- Based on:
- test mat.
- Details on study design:
- 14C-ring C12 LAS homologs is dosed at an environmentally relevant concentration into biotic and abiotic activated sludge.Activated sludge mixed liquor was collected from Pol Run Sewage Treatment(STP) and Sycamore Sewage Treatmnet(STP)Periodically, samples are removed, acidified, and analyzed by LSC(Liquid Scintillation Counting) to determine 14 CO2 evolution. And then the 14C-ring C12 LAS homologs are flahfrozen, lyophilized, and extracted to recover the parent and metabolites, which are analyzed by Rad-TLC.
- Compartment:
- other: water / sediment, material (mass) balance
- Remarks on result:
- other: PolK Run Sewage Treatment(STP) and Sycamore Sewage Treatmnet(STP)
- % Degr.:
- > 96
- Parameter:
- test mat. analysis
- Sampling time:
- 6 h
- Compartment:
- entire system
- DT50:
- 1.3 h
- Type:
- (pseudo-)first order (= half-life)
- Remarks on result:
- other: Polk Run STP
- Compartment:
- entire system
- DT50:
- 1.38 h
- Type:
- (pseudo-)first order (= half-life)
- Remarks on result:
- other: Sycamore STP
- Transformation products:
- yes
- Details on results:
- -Within 8h, 41-44% was evolved as 14CO2 , 1-2% remained as parent, 24-33% was incorporated into biomass, and 10-15% was present as intermediates, primarily sulfophenylcarboxylates.- Primary and complete biodegradation were described by a first-order model,with rate constants of 0.96-1.10/h (t 1/2 = 0.63–0.72 h) for primaryloss and 0.50-0.53/h (t 1/2 = 1.30–1.38 h) for complete degradation.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Primary and complete biodegradation were described by a first-order model, with rate constants of 0.96-1.10/h (t½ = 0.63–0.72 h) for primary loss and 0.50-0.53/h (t½ = 1.30–1.38 h) for complete degradation.
- Endpoint:
- biodegradation in water: sewage treatment 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:
- 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 303 A (Simulation Test - Aerobic Sewage Treatment. A: Activated Sludge Units)
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- Dodecylbenzenesulfonate 14C(DBS-14C)
- Radiolabelling:
- yes
- Oxygen conditions:
- anaerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Duration of test (contact time):
- 120 h
- Initial conc.:
- 76 other: ppm
- Based on:
- test mat.
- Details on study design:
- This study showed the biodegradation of LAS (DBS-14C) and the decomposition products of DBS-14C. The composition products of DBS-14C were identified by GLC and GC-MS spectrometry.(GLC column ; 0.3 cm×1.7 m, stationary phase; PEG-20M, temp; 200 deg C). And The biodegradation values of DBS-14C was obtained by methlene blue method.
- % Degr.:
- > 90
- Parameter:
- test mat. analysis
- Sampling time:
- 90 h
- Transformation products:
- yes
- No.:
- #1
- No.:
- #2
- No.:
- #3
- No.:
- #4
- Details on transformation products:
- 1-Tetralone, 1-indanone, 4-methyl-1-tetralone, naphthalene were the decomposition products.
- Details on results:
- DBS decreased from 76.0 ppm to less than 0.6 ppmat 90h(Readily degradation).The biodegradation of DBS-14C has three periods of rapid adsorption period, acclimation period, and degradation process. 1-Tetralone, 1-indanone, 4-methyl-1-tetralone, naphthalene were the decomposition products
- Validity criteria fulfilled:
- yes
- Conclusions:
- DBS decreased from 76.0 ppm to less than 0.6 ppmat 90h(Readily degradation).The biodegradation of DBS-14C has three periods of rapid adsorption period, acclimation period, and degradation process. 1-Tetralone, 1-indanone, 4-methyl-1-tetralone, naphthalene were the decomposition products
- Endpoint:
- biodegradation in water: sediment simulation testing
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the substance is readily biodegradable
Referenceopen allclose all
Description of key information
Biodegradation in water and sediment: simulation tests
In the study of Federle TW and Itrich NR 1997, Linear alkylbenzene sulfonate (14C-ring C12LAS) was tested as model compounds in two sludges.
- Within 8 h, 41−44% was evolved as 14CO2,
- 1−2% remained as parent,
- 24−33% was incorporated into biomass,
- and 10−15% was present as intermediates, primarily sulfophenylcarboxylates.
Primary and complete biodegradation were best described by a first-order model. First-order rate constants for LAS were 0.96−1.10 h-1 for primary loss and 0.50−0.53 h-1 for complete degradation. This approach provides an accurate and comprehensive kinetic picture of biodegradation under realistic conditions as well as information on the mechanism of biodegradation.
Biodegradation of Linear alkylbenzene sulfonate (14C-ring C12LAS), at 1 mg/l was measured >96% after 6 hours and test temperature was maintained at 20 deg C.
In the study of Kubodera T, Muto T and Yamamoto T 1978 Dodecylbenzenesulfonate 14C (DBS-14C) was tested as model compound.
Biodegradation of Dodecylbenzenesulfonate 14C(DBS-14C) at 76 ppm was measured >90% after 90 hours and test temperature was maintained at 24 deg C.
DBS decreased from 76.0 ppm to less than 0.6 ppm at 90h (Readily degradation).The biodegradation of DBS-14C has three periods of rapid adsorption period, acclimation period, and degradation process. 1-Tetralone, 1-indanone, 4-methyl-1-tetralone, naphthalene were the decomposition products
Key value for chemical safety assessment
Additional information
Biodegradation in water and sediment: simulation tests
In the study of Federle TW and Itrich NR 1997, Linear alkylbenzene sulfonate (14C-ring C12LAS) was tested as model compounds in two sludges.
- Within 8 h, 41−44% was evolved as 14CO2,
- 1−2% remained as parent,
- 24−33% was incorporated into biomass,
- and 10−15% was present as intermediates, primarily sulfophenylcarboxylates.
Primary and complete biodegradation were best described by a first-order model. First-order rate constants for LAS were 0.96−1.10 h-1 for primary loss and 0.50−0.53 h-1 for complete degradation. This approach provides an accurate and comprehensive kinetic picture of biodegradation under realistic conditions as well as information on the mechanism of biodegradation.
Biodegradation ofLinear alkylbenzene sulfonate (14C-ring C12LAS), at 1mg/lwas measured>96% after6hoursand test temperature was maintained at 20 deg C.
In the study of Kubodera T, Muto T and Yamamoto T 1978 Dodecylbenzenesulfonate 14C (DBS-14C) was tested as model compound.
Biodegradation of Dodecylbenzenesulfonate 14C(DBS-14C)at76ppmwas measured>90% after90hoursand test temperature was maintained at 24deg C.
DBS decreased from 76.0 ppm to less than 0.6 ppm at 90h (Readily degradation).The biodegradation of DBS-14C has three periods of rapid adsorption period, acclimation period, and degradation process. 1-Tetralone, 1-indanone, 4-methyl-1-tetralone, naphthalene were the decomposition products
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