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EC number: 205-440-9 | CAS number: 140-90-9
- 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
Toxicity to soil microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
The test item at the concentrations ranging from 125 to 2000 mg/kg dry weight of soil statistically significantly inhibited the process of nitrogen transformation to nitrate.
The concentration of the test item causing a 50% inhibition of nitrogen transformation to nitrate (EC50) is 553.9 mg/kg dry weight of soil.
The concentration of the test item causing a 25% inhibition of nitrogen transformation to nitrate (EC25) is 126.0 mg/kg dry weight of soil.
The concentration of the test item causing a 10% inhibition of nitrogen transformation to nitrate (EC10) is <125.0 mg/kg dry weight of soil.
Key value for chemical safety assessment
- Long-term EC10 or NOEC for soil microorganisms:
- 125 mg/kg soil dw
Additional information
Antimicrobial activity of xanthates was evident from median inhibitory limit on amonia oxidation in Nitrosomonas of 12 ppm(Bremner J. M. and Yeomans J. C., 1986, Biol. Fertil. Soils 173-179)
Potassium ethyl xanthate(CAS# 140-89-6) is a nitrification microbial inhibitor and was observed to inhibit soil denitrification at concentration about 50 ppm (US EPA, Washington DC, Full Public Report, Sodium Ethyl Xanthate, Priority Existing Chemical No.5, Canberra, May 1995).
Sodium ethyl(CAS# 140-90-9):The test item at the concentrations ranging from 125 to 2000 mg/kg dry weight of soil statistically significantly inhibited the process of nitrogen transformation to nitrate.
The concentration of the test item causing a 50% inhibition of nitrogen transformation to nitrate (EC50) is 553.9 mg/kg dry weight of soil.
The concentration of the test item causing a 25%inhibition of nitrogen transformation to nitrate(EC25) is 126.0 mg/kg dry weight of soil.
The concentration of the test item causing a 10%inhibition of nitrogen transformation to nitrate(EC10) is <125.0 mg/kg dry weight of soil.(Anna Arendarczyk, Institute of Industrial Organic Chemistry Branch Pszczyna, Department of Ecotoxicology,43-200 Pszczyna Poland)
Sodium ethyl(CAS# 140-90-9) or sodium isopropyl xanthates(CAS# 140-93-2) depending on concentration inhibit or activate mushroom tyrosinase (enzyme). The thiol compounds can act as inhibitors of tyrosinase due to their ability to chelate Cu+2. Tyrosinase also known as polyphenol oxidase, is a copper containing mixed - function oxidase widly distributed in microorganisms, animals and plants. The investigated xanthates act as activators at concentration about 11.5µM but as inhibitors at 20 - 50 µM(Saboury A. A., et all, J. Chinese Chem. Soc. 2008,55,937-942)
The inhibitory effect of n-alkyl xanthates on mushroom tyrosinase depend on alkyl chain length. Shorter alkyl radical gives a more potent inhibitor(Saboury A. A., et all, 2007, Acta Biochimica Polonica 54, 183-192)
Toxicity of Carbon disulfide(CAS# 75-15-0) to soil dwelling microorganisms:
Test conditions: natural soil,
Endpoint: inhibition
Result: NOEC: 15 kg of CS2per 100 m2.
(UCLID Dataset, Carbon disulfide, 2000 European Chemicals Bureau)
Carbon disulfide (CAS# 75-15-0) is a soil disinfectant and toxic to bacteria(EPA, 1986, Health and environmental effects profile for carbon disulfide, EPA/600/X-86/155,129).
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