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EC number: 217-614-1 | CAS number: 1908-87-8
- 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

Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
EPIWIN software by US-EPA
2. MODEL (incl. version number)
KOCWIN v2.00
3. SMILES
CN1CCSC1=S
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
- Defined endpoint: log Koc – soil adsorption coefficient of organic compounds
- Unambiguous algorithm: log Koc = 0.5213 MCI + 0.60 + ΣPfN
MCI – molecular connectivity index, ΣPfN - summation of the products of all applicable correction factor coefficients available in the data set multiplied by the number of times (N) that factor is counted for the structure.
- Defined domain of applicability: Currently, there is no universally accepted definition of model domain. The training set of the model contains diverse molecules, so that the fragment library is abundant. It is however possible that a compound has functional groups or other structural features that are not represented in the training set and for which no fragment coefficients were developed. Additionally, there can be more instances of a given fragment than the maximum for all training set compounds. These points should be taken into consideration while interpreting test results.
Molecular weight limits of the training set: 32 - 665 g/mol
Log Kow limits: -2.11-9.10
- Appropriate measures of goodness-of-fit and robustness and predictivity: for the statistics, training data set has been split up into two subsets: the one containing non-polar substances with no fragments subjected to corrections (i.e. those with ΣPfN = 0) and the one containing the remaining ones. For the non-polar set: N = 69 compounds, correlation coefficient R2 = 0.967, standard deviation sd = 0.247 and average deviation ad = 0.199. For the second set: N = 447 compounds, correlation coefficient R2 = 0.9, standard deviation sd = 0.34 and average deviation ad = 0.273. For the external validation data set: N = 158 compounds, correlation coefficient R2 = 0.85, standard deviation sd = 0.583 and average deviation ad = 0.459. For the 516 compounds in the training set, 93% are within 0.6 log units and 100% within 1 log unit.
- Mechanistic interpretation: The methodology and relationship between the forst order molecular connectivity index (MCI) and adsorption coefficient is outlined in the reference paper: Meylan, W., P.H. Howard and R.S. Boethling, "Molecular Topology/Fragment Contribution Method for Predicting Soil Sorption Coefficients", Environ. Sci. Technol. 26: 1560-7 (1992). MCI was initially successfully used to predict soil sorption coefficients for non-polar organics, and the developed new estimation method based on MCIand series of statistically derived fragment contribution factors made it useful also for the polar ones.
5. APPLICABILITY DOMAIN
Molecular weight of ca. 133.24 in molecular weight limits of the training set: 32 - 665 g/mol; log Kow of 0.59 in log Kow limits: -2.11-9.10; applicability domain fulfilled
6. ADEQUACY OF THE RESULT
The organic substance 3-methylthiazolidine-2-thione lies within the applicability domain with a molecular weight of 133.24 and a log Kow of 0.59; the result seems reasonable and considering the low log kow (0.59) and the quite low log koc as calculated in this QSAR, it is considered as adequate and acceptable to use this result for risk assessment purposes.
Data source
Reference
- Title:
- EPI Suite Version 4.10
- Year:
- 2 012
- Bibliographic source:
- KOCWIN - Meylan and Howard (1992)
Materials and methods
Test guideline
- Guideline:
- other: REACH guidance on QSARs Chapter R.6
- Version / remarks:
- May 2008
- Principles of method if other than guideline:
- Meylan, W., P.H. Howard and R.S. Boethling, "Molecular Topology/Fragment Contribution Method for Predicting Soil Sorption Coefficients", Environ. Sci. Technol. 26: 1560-7 (1992).
- GLP compliance:
- no
- Type of method:
- other: calculation method
- Media:
- soil
Test material
- Reference substance name:
- 3-methylthiazolidine-2-thione
- EC Number:
- 217-614-1
- EC Name:
- 3-methylthiazolidine-2-thione
- Cas Number:
- 1908-87-8
- Molecular formula:
- C4H7NS2
- IUPAC Name:
- 3-methyl-1,3-thiazolidine-2-thione
Constituent 1
- Specific details on test material used for the study:
- SMILES: CN1CCSC1=S
Results and discussion
Adsorption coefficientopen allclose all
- Type:
- Koc
- Value:
- 124.4 L/kg
- Temp.:
- 25 °C
- Remarks on result:
- other: MCI based estimate
- Type:
- log Koc
- Value:
- 2.09 dimensionless
- Temp.:
- 25 °C
- Remarks on result:
- other: MCI based estimate
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The study report describes a scientifically accepted calculation method for the soil adsorption coefficient using the US-EPA software KOCWIN v2.00. No GLP criteria are applicable for the usage of this tool and the QSAR estimation is easily repeatable. The result (Koc = 124.4 L/kg; log Koc = 2.09) is adequate for the regulatory purpose.
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