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EC number: 205-288-3 | CAS number: 137-30-4
- 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
Zinc bis dimethyldithiocarbamate (CAS No. 137-30-4) is not readily biodegradable (7.7% biodegradation in 28 d). Simulation tests on biodegradation in water, sediment and soil are available. Mineralization rates of the substance were carefully investigated in the different systems.
In the water system mineralization rate reached 31.5% (high dose system) to 56.9% (low dose system) after 30 days. Test item DT50 resulted into half-lives of 1.53 - 2.47 days (3.7 - 5.8 days, recalculated to 12 °C). In the sediment system, test item DT50 were 0.2 - 0.3 days (0.4 - 0.6 days, recalculated to 12 °C), while mineralization rate of 48.6% (pond system) to 84.2% (river system) after 101 d were measured. In soil a test item half-life of 0.6 days (1.4 days, recalculated to 12 °C) was determined under aerobic conditions. Mineralization rate of 53.2% after 28 days was determined. Therefore, based on these simulation tests, zinc bis dimethyldithiocarbamate can be considered as biodegradable.
Furthermore, zinc bis dimethyldithiocarbamate degrades in the environment through abiotic processes. It is susceptible to photolysis in air (half-life = 2.8 hours, calculated), water and soil (half-lives < 10 hours) and once released into the water, hydrolysis plays an important role in the degradation of this substance, especially under acidic and neutral conditions (half-lives of 10.4 minutes at pH 4 and 17.7 hours at pH 7). Based on the estimated Henry’s Law constant (0.0057 Pa m3/mol), the parent substance is not expected to evaporate from the water surface.
The substance shows a high potential for adsorption to soil and sediment particles (log Koc of 2.89 – 4.54) and incorporation of the test material to organic matter contributes significantly to its elimination from the aquatic system. In view of the estimated octanol-water partition coefficient (1.65) and the fact that the substance is not ionizable or surface active, the bioaccumulation potential in biota is assumed to be low.
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