Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 271-807-5 | CAS number: 68608-88-8 This substance is identified by SDA Substance Name: C11-C13 branched alkyl benzene sulfonic acid and SDA Reporting Number: 25-096-00.
- 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

Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
In a 96 h acute toxicity study, Bluegill (Lepomis macrochirus) were exposed to C11.8 LAS (linear alkylbenzene sulfonate, an anionic surfactant) under static conditions. Nominal concentrations were not specified in the report. Measured concentrations were 79 % of nominal concentrations.
The 96 h LC50 value, based on measured concentration, was 1.67 mg a.i./L, with 95% CL 1.58 to 1.77 mg/L. This toxicity study is classified as acceptable and satisfies the guideline requirement for the current USEPA OPPTS 850.1075 (1996) acute fish toxicity study.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 1.67 mg/L
Additional information
In the key study, a 96 h acute toxicity study, Bluegill (Lepomis macrochirus) were exposed to C11.8 LAS (linear alkylbenzene sulfonate, an anionic surfactant) under static conditions. Nominal concentrations were not specified in the report. Measured concentrations were 79 % of nominal concentrations. The 96 h LC50 value, based on measured concentration, was 1.67 mg a.i./L, with 95% CL 1.58 to 1.77 mg/L. This toxicity study is classified as acceptable and satisfies the guideline requirement for the current USEPA OPPTS 850.1075 (1996) acute fish toxicity study.
In the first supporting study, groups of 10 carp or rainbow trout fry were exposed to various concentrations of LAS or BABS Na salt for 15 days in a semi-static experiment. The TLm value for fish for LAS was 1-2 mg/L. The TLm value for fish for BABS Na salt was 4-6 mg/L. BABS Na salt is two to three times less toxic to fish than LAS supporting the use of LAS data as worst case read across for BAB Acid.
In the second supporting study, the TLm values of BABS Na salt were tested against 11 species of fish. Two replicates of 10 fish were exposed to various concentrations from 0 -20 mg/L BABS Na salt for 4 days. The TLm values ranged from 7.4 - 22 mg/L.
In the third supporting study, six concentrations of LAS were tested in a 4-day flow-through study. Analytical monitoring was performed 4 times daily. 2 replicates of 10 fish from 5 different species were tested. Results show that BABS Na salt is two to four times less toxic to fish than LAS.
In the fourth supporting study, eight samples of sewage water were collected, and the bacteria that made up the inoculum was determined. Two test substances, LAS and BABS Na salt were then added, and the biodegradation of the substances followed for 168 hrs. At the times 0, 16, 24, 40, 48, 72, and 168 hrs, samples from the biodegradation tests were taken, and these samples were used in 24 -hr zebra fish acute toxicity experiments. Results of the toxicity tests show that LAS is more toxic than BABS.
In the fifth supporting study, a flow-through study, fathead minnow eggs were exposed to six to seven concerntrations of either LAS or BABS Na salt for 9 days. Results show that LAS is two to three times more toxic than BABS.
In the sixth supporting study, rainbow trout were exposed to various concentrations BABS Na salt for a period of 5 days. After exposure, some of the fish were sacrificed, and various blood parameters measured. Results show that the 96 -hr LC50 for fish was 2.58 mg/L, with death due to gill destruction.
Based on the data for linear and branched alkylbenzene sulfonates, linear structures are more toxic than branched structures. Therefore, data on linear materials, e.g., the chronic aquatic studies using LAS, are considered to be a worst case scenario.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.