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EC number: 221-242-5 | CAS number: 3039-83-6
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
According to the key study (OECD 301 B) the test item can be considered as inherently biodegradable.
The degradation of the test item at the end of the test was 67.4% of ThCO₂ (42 d with considering the IC in the liquid phase, mean of three replicates. After 28 days, the mean degradation was 31.8% of ThCO₂ with individual values varying widely (6.9% — 68.3%).
Therefore, the test item did not reach the criteria for ready biodegradability (60% of ThCO₂ within 28 days and within a 10-day window). However, the test item reached the criterion to be considered non-persistent (60% of ThCO₂ within 60 days).
The pH in the test vessels was 7.0 — 7.5 after 28 days and 7.1 at the end of the test.
The test guideline pass level for ready biodegradability (60 % CO₂ formation) was not reached within 28 days.
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable
- Type of water:
- freshwater
Additional information
Key study
The degradation of the test item at the end of an OECD 301 B test was 67.4% of ThCO₂ (42 d with considering the IC in the liquid phase, mean of three replicates. After 28 days, the mean degradation was 31.8% of ThCO₂ with individual values varying widely (6.9% — 68.3%).
Therefore, the test item did not reach the criteria for ready biodegradability (60% of ThCO₂ within 28 days and within a 10-day window) and the test duration was extended to 42 days. The test item reached the criterion to be considered non-persistent (60% of ThCO₂ within 60 days). The pH in the test vessels was 7.0 — 7.5 after 28 days and 7.1 at the end of the test.
Supporting studies
The purpose of an OECD 301 E study was to determine the ready biodegradability of sodium vinylsulphonate, but the study report had some deficiencies in documentation. The test item was exposed to activated sludge from the aeration tank of a domestic waste water treatment plant for 28 days. The biodegradation was followed by dissolved organic carbon (DOC) during exposure. Under the test conditions the percentage biodegradation of the test item reached a mean of 56 % after 28 days based on DOC. Therefore, the test item can be considered as inherently biodegradable.
In another supporting study, performed prior to OECD guideline release, sodium vinylsulphonate was assessed for its biodegradability using non-adapted and adapted sludge. The biodegradation was followed by chemical oxygen demand (COD) in a Sapromat. In this study sodium vinylsulphonate was practically non-biodegradable without adaption of the sludge. However, with adapted sludge 90 % biodegradability was observed. Therefore, the test item was considered as inherently biodegradable in this study.
Assessment
In summary, it can be concluded that the substance sodium vinyl sulphonate is biologically degraded but shows a significant lag time before biodegradation begins, thereby exceeding the 28-day window, typically applied in biodegradation studies. The results of the key study however show clearly that with an extended observation period, a high level of biodegradation can be observed (67.4% of ThCO₂ within 42 d). Thus, the substance is considered inherently biodegradable and non-persistent.
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