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EC number: 233-593-1 | CAS number: 10254-57-6
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Acute toxicity to fish:
In an OECD 203 study, conducted to GLP, based on the mean measured test concentrations of the centrifuged test media the acute toxicity of the test material to rainbow trout, methylene bis(dibutyldithiocarbamate) gave a 96-Hour LC50 value of greater than 0.060 mg /L. The NOEC was 0.060 mg/L (Safepharm Laboratories, 2004).
No mortality was observed during the test. The test was conducted using dimethylforamide to pre-dissolve the test material before dilution in test media. When analysed test concentrations were far lower than what was theoretically created, indicating that there were difficulties stemming from water solubility of the test material. The test material is known to possess low water solubility (0.243 mg/l at 20 ± 5 ºC). In the absence of any evidence of toxicity, and taking into consideration the difficulties in water solubility, it is considered that no evidence of toxicity is seen at the limit of solubility.
Chronic toxicity to fish:
In on OECD210 study, no mortalities or sub-lethal effects were observed following exposure of fathead minnow (Pimephales promelas) larvae to the test material for 33 days (28 days post-hatch). Based on the geometric mean measured concentration, the E(L)C10 and E(L)C50 values were determined to be greater than 0.20 mg/L for hatching, post-hatch survival, body length and wet weight. The No Observed Effect Concentration (NOEC) based on survival or growth was 0.20 mg/L.
Acute toxicity to daphnia:
In an OECD 204 study, conducted to GLP, the 48-HourEC50 of methylenbis(dibutyldithiocarbamate) (centrifuged test media) todaphnia magna is greater than 0.052 mg/L (mean measured) and correspondingly the NOEC was 0.052 mg/L (Safepharm Laboratories, 2004).
No mortality was observed during the test. The test was conducted using dimethylforamide to pre-dissolve the test material before dilution in test media. When analysed test concentrations were far lower than what was theoretically created, indicating that there were difficulties stemming from water solubility of the test material. methylenbis(dibutyldithiocarbamate) is known to possess a low water solubility (0.243 mg/l at 20 ± 5 ºC). In the absence of any evidence of toxicity, and taking into consideration the difficulties in water solubility, it is considered that no evidence of toxicity is seen at the limit of solubility.
Chronic toxicity to daphnia:
In an OECD 211 study, conducted to GLP, the 21-day toxicity toDaphnia Magna NOEC and MATC of 4,4'-methylene bis(dibutyldithiocarbamate) was determined to be greater than 247 μg/L.
As the NOEC was 0.247 mg/l at 21 days, it is considered that there is no toxicity at the limit of water solubility (water solubility; 0.247 mg/l at 20 ± 5 ºC) (Harlan Laboratories, 2009).
Acute toxicity to algae:
In an OECD 201 study, conducted to GLP, the 72-Hour EC50 of methylenbis(dibutyldithiocarbamate) (centrifuged test media) toScenedesmus subspicatus is greater than 0.0325 mg/L (mean measured) and correspondingly the NOEC was 0.0325 mg/L (Safepharm Laboratories, 2004).
No mortality was observed during the test. The test was conducted using dimethylforamide to pre-dissolve the test material before delusion in test media. When analysed test concentrations were far lower than what was theoretically created, indicating that there were difficulties stemming from water solubility of the test material. The test material is known to possess a low water solubility (0.243 mg/l at 20 ± 5 ºC). In the absence of any evidence of toxicity, and taking into consideration the difficulties in water solubility, it is considered that no evidence of toxicity is seen at the limit of solubility.
Activated Sludge Respiration Inhibition:
In an OECD 209 study, conducted to GLP, methylenbis(dibutyldithiocarbamate) was not toxic to waste water (activated sludge) bacteria at or below a loading rate of 1000 mg/L (NOEC). The EC50 exceeded a loading rate of 1000 mg/L (WIL Research Europe, 2013).
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