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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
Biological effects monitoring
Administrative data
- Endpoint:
- biological effects monitoring
- Type of information:
- other: published data
- Adequacy of study:
- supporting study
- 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.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 002
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- An integrated model stream ecosystem fate and effects study of a C12LAS homologue, with a high content (35.7%) of its most hydrophobic and toxic 2-phenyl isomer, was performed in the summer and fall of 1996 in Procter and Gamble’s Experimental Stream facility. The study addressed responses of periphytic microbes, immature benthic fauna including abundance and drift, and emergence of adult insects in a 56-day exposure.
- GLP compliance:
- not specified
- Type of study / information:
- Type of test:out-door experimental streams.
Test material
- Reference substance name:
- Sodium dodecylbenzenesulfonate
- EC Number:
- 246-680-4
- EC Name:
- Sodium dodecylbenzenesulfonate
- Cas Number:
- 25155-30-0
- Molecular formula:
- C18H30NaO3S
- IUPAC Name:
- sodium dodecylbenzenesulfonate
- Test material form:
- solid: compact
- Details on test material:
- Dodecyl linear alkylbenzene sulfonate (C12LAS) (CAS# 25155-30-0).
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.
Constituent 1
Results and discussion
Any other information on results incl. tables
Microbial heterotrophs acclimated to C12LAS exposure quickly (14 days) and biodegraded C12LAS at all concentrations. Blue-green algae responded by increasing in abundance with increasing C12LAS concentration. Invertebrates responded by increased drift and reduced benthic abundances at concentrations exceeding 293 μg/LL. Emergence at 927 μg/L also declined relative to the control. Adverse responses for mayflies and chironomids were indicated using univariant statistical techniques. Multivariant techniques indicated these taxa plus molluscs, aquatic worms, caddisflies, and stoneflies were impaired at some concentrations. Bioavailability of C12LAS was investigated in streams as a function of the total suspended solids load in the water column driven by local weather and watershed patterns. A continuous bioavailability model indicated exposure was reduced by an average of 8.5 ± 8.9%. A model ecosystem NOEC (no-observed-effect-concentration) was concluded to be 293 μg/L based on measured water column exposure and adjusted to 268 μg/LL by the bioavailability model. A summary of selected population and community responses at 8 weeks from the current study is shown in the table below.
Community/Measure |
Dose Response |
Temporal |
NOEC (µg/L) |
Heterotrophic microbial Biomass (total lipid phosphate/mm2) Amino acid uptake (3H dpm/mm2/min) Phospholipid fatty acid (PLFA) distr. Surfactant mineralization (% CO2) |
NS NS |
Shift at >293 µg/L Acclimation at all conc. |
|
Autotrophic microbial Bicarbonate uptake (14C dpm/mm2/min) Algal density (cells/mm2) Algal biovolume (µm3/mm2) Blue-green algal density (cells/mm2) Green algal density (cells/mm2) Diatom algal density (cells/mm2) Algal richness Dominant taxa (cells/mm2) Cocconeis placentula Melosira varians Chrococcus sp. Nitzschia dissipata Navicula salinarum v. intermedia Pleurosira (= Biddulphia) laevis Nitzschia inconspicua Nitzschia palea Diatoma vulgare Gyrosigma acuminatum |
+ NS NS ++ NS NS - - NS + NS NS NS ++ + -- - |
+ ++ - - + ++ + -- - |
927 927 927 927 |
Invertebrates Richness Diversity (Shannon-Weaver) Total abundance (No./m2) Insect abundance (No./m2) EPT abundance (No./m2) Mayfly abundance (No./m2) Caddisfly abundance (No./m2) True fly abundance (No./m2) Chironomid abundance (No./m2) Mollusk abundance (No./m2) Oligochaete abundance (No./m2) Dominant populations (No./m2) Baetis sp. (mayfly) Isonychia sp. (mayfly) Stenonema sp. (mayfly) Thienemannimyla sp. (chironomid) Tanytarsus sp. (chironomid) Cricotopus sp. (chironomid) Polypedilum sp. (chironomid) Reotanytarsus sp. (chironomid) Naididae (aquatic worm) |
NS NS -- NS - NS NS NS NS NS -- b --- NS --- ++ + + NS NS |
-- - -- --- --- ++ + + |
293 927 293 927 293 |
a Plus (+) and minus (-) signs indicate whether the response significantly increased or decreased from the control condition (± = 0.05). The strength to the response was graded as slight (+/-), moderate (++/--), or great (+++/---) based on statistical analyses. NS indicates not significant. bTaxon too low in abundance, emerged.
Applicant's summary and conclusion
- Conclusions:
- A model ecosystem NOEC (no-observed-effect-concentration) was concluded to be 293 μg/L based on measured water column exposure and adjusted to 268 μg/L by the bioavailability model.
- Executive summary:
An integrated model stream ecosystem fate and effects study of a C12LAS homologue, with a high content (35.7%) of its most hydrophobic and toxic 2-phenyl isomer, was performed in the summer and fall of 1996 in Procter and Gambles Experimental Stream facility. The study addressed responses of periphytic microbes, immature benthic fauna including abundance and drift, and emergence of adult insects in a 56-day exposure. A model ecosystem NOEC (no-observed-effect-concentration) was concluded to be 293 microgram/L based on measured water column exposure and adjusted to 268 microgram/L by the bioavailability model.
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