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EC number: 934-716-8 | CAS number: -
- 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
Two studies were considered to yield reliable information on sulfide/H2S toxicity. The first study (Admiraal and Peletier, 1979) was an atypical study in which several pennate benthic and centric planktonic diatom species were exposed for 48 h to a series of sulfide concentrations in the absence of oxygen and light (not affecting control populations). In this study, the lowest 48-h NOEC values were < 30 mg S2-/L. The second study (Breteler et al., 1991) investigated the effects of sulfide on photosynthesis of the planktonic diatom Skeletonema costatum by exposing the diatoms for 4 h to a series of sulfide concentrations in the presence of a 14C-labeled carbon source and measuring 14C photoincorporation. The NOEC was determined to be 0.77 mg S2-/L, which corresponds to a H2S concentration of 0.041 mg H2S/L. The study of Breteler et al. (1991) was considered as a key study. The available studies only reported reliable results for marine algae. No reliable information was identified for freshwater algae. For sulfate toxicity, the study of Patrick et al. (1968) was identified as a key study. The 120-h EC50 (based on reduction in number of cells produced compared to the control) of Na2SO4 for the freshwater diatom Nitzschia linearis was reported to be 1900 mg/L. Recalculation to SO4 2- yields an EC50 of 1285 mg/L.
Key value for chemical safety assessment
- EC50 for marine water algae:
- 0.104 mg/L
- EC10 or NOEC for marine water algae:
- 0.041 mg/L
Additional information
Toxicity studies investigating the toxicity of Na2S or NaHS to aquatic organisms have focused in most cases on the toxicity of H2S, which is the most toxic sulfur species that can be formed upon dissolution of Na2S and NaHS. Among the available studies using either Na2S, NaHS (or its respective hydrates) or H2S as test substance, the studies of Breteler et al. (1991) and Admiraal and Peletier (1979) yielded reliable information on sulfide toxicity, but only for marine diatoms. The study of Breteler et al. (1991) delivered the key NOEC of 0.041 mg H2S/L for the marine diatom Skeletonema costatum, which will be used for derivation of a PNECaquatic for H2S for both the freshwater and marine environment. In oxic environments, released sulfides will be oxidized to - eventually - sulfate. In these cases, the risks entailed by the released sulfur should be evaluated using toxicity data for sulfate. Na2SO4 was identified as the most relevant substance for this purpose. From the OECD SIDS for Na2SO4, one reliable (Klimisch 2) study was selected for inclusion in this dossier. The study of Patrick et al. (1968) was considered as the key study. This study reports a 120-h EC50 of 1900 mg Na2SO4/L for the freshwater diatom Nitzschia linearis, yielding a 120-h EC50 of 1285 mg/L for sulfate. This EC50 most likely represents a worst case value since the overall observed toxicity of Na2SO4 is also affected by the presence of sodium ions and not only by the presence of sulfate ions.
No reliable data were found for NaOH or Na2CO3.
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.
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