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EC number: 241-620-3 | CAS number: 17636-10-1
- 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
Stability
No experimental data are available for 1-Propanesulfonic acid, 3 -mercapto-, monosodium salt (CAS 17636-10-1). The phototransformation in air can be determined with the help of the computer program AOPWIN v1.92 (EPIWIN software) of US-EPA (Chemservice S.A., 2011). An atmospheric half-life of 0.243 days (around 2.913 hours) was calculated. Neither an ozone reaction nor any nitrate radical reaction is important for the target chemical. This modelling is a scientifically accepted calculation method and is therefore reliable with restrictions and can be used for the chemical safety assessment.
The hydrolytical half-life at pH 9 at a temperature of 25 °C was experimentally determined as 52.3 days (Tarran, 2012). At pH 4 and 7, the substance is considered as stable, since the half-lives are greater than 1 year.
Biodegradation
For 1-Propanesulfonic acid, 3-mercapto-, monosodium salt (CAS 17636-10-1) the biodegradability can be predicted by the computer program BIOWIN v4.10 (EPIWIN software) of US-EPA (Chemservice S.A., 2011). The program calculates with seven different models. According to Biowin 1 and 2 the substance is biodegrading fast. The Ultimate Biodegradation Timeframe is "weeks", whereas the Primary Biodegradation Timeframe reveals "days" as result. Both MITI Models predict that the substance is not readily biodegradable. Overall Ready Biodegradability Prediction: No.
Further prediction can be made using the modelling tool Toxtree (v.2.5.0), which uses the START (Structural Alerts for Reactivity in Toxtree) plug-in. This is a developed rulebase, which estimates the biodegradability potential of a chemical compound based on structural alerts compiled from the Canadian EPA (START2008). The chemical was assigned to the class III - unknown biodegradability.
Bioaccumulation
1-Propanesulfonic acid, 3 -mercapto-, monosodium salt (CAS 17636-10-1) was not investigated for its aquatic bioaccumulation potential so far. The computer program BCFBAFWIN v3.00 was used to predict the bioconcentration factor (BCF) of the substance (Chemservice S.A., 2011). Using the regression-based estimate (traditional method) a BCF of 3.16 L/kg wet-wt was calculated. Using the Arnot-Gobas method, based on the mechanistic first principles, the BCF results in a value of 0.90 L/kg wet-wt. The metal compounds (Na, K, Li) were removed for its calculation procedure. Hence, bioaccumulation in aquatic organisms is not to be expected.
Transport and distribution
The adsorption potential to soil of 1 -Propanesulfonic acid, 3 -mercapto-, monosodium salt (CAS 17636-10-1) was determined by the scientifically accepted calculation method with KOCWIN v2.00 (Chemservice S.A., 2011) Two different models are used, whereby the MCI method is taken more seriously into account, due to the fact that is includes improved correction factors. For this chemical compound, the metal compound (Na) has been removed by the program to allow the estimation via the MCI method, resulting in a Koc value of 2.857 L/kg. The traditional method gives a value of 0.086 L/kg. It is noted that these results represent a best-fit to the majority of experimental values, due to the fact that the Koc of this structure may be sensitive to the surrounding pH.
Additionally, the Henry´s Law constant was predicted by the EPIWIN software HENRYWIN v3.20 (Chemservice S.A., 2011). The Bond Method resulted in a value of 0.0000801 Pa*m³/mol (8.01 E-5 Pa*m³/mol) at an ambient temperature of 25 °C.
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