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EC number: 205-788-1 | CAS number: 151-21-3
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
72h-EC50 > 120 mg/L (nominal concentration) for growth rate of Desmodesmus subspicatus (DIN 38412, part 9)
72h-EC10 = 30 mg/L (nominal concentration) for yield of Desmodesmus subspicatus (DIN 38412, part 9)
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 120 mg/L
- EC10 or NOEC for freshwater algae:
- 30 mg/L
Additional information
Several studies are available investigating the toxicity of sodium dodecyl sulfate (SDS) algae (see table 1), since SDS is an economically important surfactant and was frequently used as reference substance in toxicity tests. The data set is comprised of several publications with acceptable quality and validity focusing on standard and non-standard freshwater and marine species as well as one study report investigating the toxicity to the standard species Desmodesmus subspicatus (BASF 1994). The GLP study was performed according to OECD guideline 201 testing concentrations between 15 and 120 mg/L. The test substance concentrations were measured and showed to be stable throughout the test. The 72h-EC50 value is determined to be above the highest tested concentration of 120 mg/L based on growth rate and nominal concentrations. A 72h-NOEC value of 30 mg/L was recorded based on yield and nominal concentrations. Although this effect value is not the lowest observed in the data set it was used for hazard assessment since (i) this study is rated as the most comprehensive and reliable one and (ii) the remaining data set is biased because several effect values are existing in the literature for some of the additional (standard) species tested but always the lowest obtained value per species is listed and no averaging was performed. This was done because the data set is primarily presented to statistically assess the general susceptibility ofalgaeto SDS in comparison to fish and aquatic invertebrates using a conservative approach. To use the effect value from BASF (1994) is considered to be acceptable for hazard assessment since classification and labeling as well as PNEC derivation is not based on algal toxicity and since this value adequately represents the toxicity (= harmful) of SDS to algae (see table 1).
In general algae show to be less susceptible to SDS than fish and aquatic invertebrates. The data set is not robust enough to conclude on differences in susceptibility between freshwater and marine species.
Table 1: Acute toxicity of SDS to different freshwater and marine algae. Publications showing the lowest obtained effect values for a single species are listed.
Species | Exposure time | EC/LC50 [mg/L] | marine/freshwater | Reference |
Tetraselmis chuii | 96h | 30.2 | m |
Nunes et al. 2005 |
Chlamydomonas reinhardtii | 72h | 18.8 | fw | Brack & Rottler 1994 |
Lemna minor |
7d | 18 | fw | Bishop 1979 |
Desmodesmus subspicatus | 72h | > 100 | fw | BPCN, unpublished data |
Pseudokirchneriella subcapitata | 96h | 117 | fw | Nyholm & Damgaard |
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