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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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
For H2S toxicity, two key studies were identified. The key study for freshwater aquatic invertebrates is the study of Oseid and Smith (1974a) and that for marine aquatic invertebrates is the study of Gopakumar and Kuttyamma (1996). Oseid and Smith (1974a) obtained a 96-h LC50 of 0.02 mg H2S/L for mayfly larvae of the species Baetis vagans. Gopakumar and Kuttyamma (1996) reported a 96-h LC50 of 0.032 mg H2S/L for the penaeid prawn Penaeus indicus. For sulfate toxicity, the study of Mount et al. (1997) was identified as a key study. This study reports a 48-h LC50 of 3080 mg Na2SO4/L for Ceriodaphnia dubia. This value can be recalculated to an LC50 of 2083 mg SO4 2-/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.02 mg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 0.032 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 study of Oseid and Smith (1974a) yielded the lowest reliable 96-h LC50 for freshwater aquatic invertebrates (larvae of the mayfly Beatis vagans), whereas the study of Gopakumar and Kuttyamma (1996) reported the lowest reliable 96-h LC50 for marine invertebrates (the penaeid prawn Penaeus indicus). These values will be used for derivation of a PNECaquatic for H2S for 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 (Mount et al., 1997). This study reports a 48-h LC50 of 3080 mg Na2SO4/L for Ceriodaphnia dubia, yielding a 48-h LC50 of 2083 mg/L for sulfate. This LC50 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.
For NaOH and Na2CO3, one reliable (Klimisch 2) marine study were found for each. For Na2CO3, Warne and Schifko (1999) reported a 48 -h EC50 for Ceriodaphnia sp. between 200 and 227 mg/L. For NaOH, Warne (1999) reported a 48 -h EC50 for Ceriodaphnia sp. of ca. 40.4 mg/L. No freshwater data were found.
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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