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EC number: 240-210-1 | CAS number: 16066-35-6
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Algae are the most sensitive aquatic species with a 72-hr EC50 value of 73 mg/L a.i., and NOEC of 44.8 mg/L a.i.. Fish, invertebrates and bacteria appear much less sensitive. It may well be the acidity of the test substances that are the cause of the observed algal toxicity. The pH of the test medium was between 3 and 5 in the replicates at the end of the test. The pH in the fish, invertebrate and bacteria tests remained in the normal aquatic environment range. Toxicity in the sediment compartment is not considered a particularly relevant endpoint for these acids given their low partitioning coefficients.
A single, good quality (non-GLP) fish acute toxicity study (Hoechst, 1981), is available for p-toluenesulfonic acid (CAS No. 104-15-4). There were no mortalities and the 96 hr LC50 is >325 mg active ingredient/L.
There are 3 acute studies with the invertebrate Daphnia magna. The key study is an OECD 202 Guideline, GLP-compliant study (p-TA Coalition, 2005) with benzenesulfonic acid (CAS No. 98-11-3). It is a well documented limit test with analytical confirmation. There was no mortality or immobility observed at 100 mg/L (nominal) / 103 mg/L (measured). The test conditions were confirmed to be valid and the reference substance produced expected results. The 48h-EC50 is reported as >100 mg active ingredient/L. A second study with 98-11-3 (Huntsman, 1995) and a study with toluene-4-sulphonic acid (CAS No. 104-15-4) (Hoechst, 1983) confirm the lack of toxicity at 100 mg/L.
There is one algal toxicity study. It is an OECD 201 Guideline, GLP compliant study for benzenesulphonic acid (CAS 98 -11 -3) (pTA-Coalition, 2005) using analytical confirmation and a reference substance. The 72h-EC50 for Selenastrum capricornutum was 70 mg/L active ingredient based on biomass inhibition and 73 mg/L a.i. for growth rate inhibition. The reported 72h-NOEC was 44.8 mg/L. The report indicates that the observed toxicity may very well have been due to the acidity of the test substance. The pH of the test medium at the two highest test concentrations (100 and 220 mg/L) was in the range of 5 and 3, respectively. Comparable tests with the salt form (hydrotropes - calcium xylene sulphonate - Ruetgers Nease, 1994; and sodium xylene sulphonate - Stepan, 1993) indicate much higher EC50 values, >758 mg/L a.i. and >230 mg/L a.i., respectively.
There is a single study of aquatic microbial toxicity (Hoechst, 1989). The OECD 209 guideline study with activated sludge microbes exposed to toluene-4-sulphonic acid (CAS. 104-15-4) reports a 3-hour NOEC for growth inhibition is 580 mg/L.
The aromatic sulphonic acids have low logPow values and are therefore not expected to be sorbed onto sediments. These substances are readily biodegraded and therefore will not accumulate. A significant distribution into the sediment compartment is not predicted and exposures to sediment dwelling organisms is expected to be comparable to pelagic species.
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