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EC number: 209-132-5 | CAS number: 556-61-6
- 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 soil
Administrative data
- Endpoint:
- biodegradation in soil
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: 3 a, b, c: Documentation insufficient for assessment; Significant methodological deficiencies (in comparison with standard and guideline methods)
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- No information
- Author:
- Tomlinson TG et al
- Year:
- 1 966
- Bibliographic source:
- J Appl Bact 29: 266-91
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 989
- Reference Type:
- publication
- Title:
- No information
- Author:
- Verhagen C et al
- Year:
- 1 996
- Bibliographic source:
- Soil Biol Biochem 12: 1753-56
Materials and methods
Test material
- Reference substance name:
- Methyl isothiocyanate
- EC Number:
- 209-132-5
- EC Name:
- Methyl isothiocyanate
- Cas Number:
- 556-61-6
- Molecular formula:
- C2H3NS
- IUPAC Name:
- isothiocyanatomethane
Constituent 1
Results and discussion
Applicant's summary and conclusion
- Executive summary:
In a soil biodegradation study, the biodegradation ofmethyl isothiocyanategenerally followed first order kinetics in soils previously untreated with the compound(1). In soils previously exposed tomethyl isothiocyanate,the biodegradation was generally much faster and the biodegradation did not follow first order kinetics(1). Even in soils that were previously untreated withmethyl isothiocyanate,an accelerated transformation (which did follow first order kinetics) was observed after an initial period (8-15 days) of first order transformation(1). Using the first order kinetics, the biodegradation half-life was estimated to range from 0.5 to 50 days(2). Generally, the transformation was appreciably faster in soils that have been previously treated with the chemical frequently(2). At or above concns of 0.8 mg/l,methyl isothiocyanateinhibited nitrification in the activated sludge process of sewage disposal(2).Methyl isothiocyanatewas confirmed to be biodegradable according to a Netherlands study that employed 10 soils under field conditions(3). Soil core samples from Dutch agricultural fields with a 4 year history ofmethyl isothiocyanatetreatment were incubated with the test compound for 1 to 14 days at 20 deg C; 50% degradation times ranged from 0.5 to 9 days(3).
[(1) Tomlinson TG et al; J Appl Bact 29: 266-91 (1966) (2) Smelt JH et al; J Environ Sci Health B24: 437-55 (1989) (3) Verhagen C et al; Soil Biol Biochem 12: 1753-56 (1996)]
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