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Diss Factsheets
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EC number: 205-232-8 | CAS number: 136-23-2
- 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
Acute toxicity of zinc bis(dibutyldithiocarbamate) (ZDBC) by oral and dermal exposure routes is low. Several acute oral toxicity studies give oral LD50 value over 5000 mg/kg bw for rats, while two acute dermal toxicity studies with rabbits give LD50 > 2000 mg/kg bw/day. No data on acute inhalation toxicity were available; however, in accordance with REACH Annex VIII, the study does not need to be conducted, as data on two other routes of exposure are available.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 5 000 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
Additional information
Four acute oral toxicity studies with zinc bis(dibutyldithiocarbamate) (ZDBC) were available for assessment, all reporting LD50 values well above 2000 mg/kg bw. Out of these studies, the most recent one (Monsanto Company, 1982a), performed under GLP, was chosen as a key study. Five Sprague-Dawley rats of each sex were administered a single oral dose of 5000 mg/kg bw of the test substance as a 434 mg/ml suspension in corn oil. No mortalities occurred and no abnormal findings were noted at necropsy. Diarrhoea occurred in three males and five female rats on the day of dosing, but this effect was probably induced by the corn oil used as the dosing vehicle.
Two acute dermal toxicity studies with rabbits were available for assessment, one with very limited reporting. Respectively, the other one, more recent GLP-compliant study (Monsanto Company, 1982b) was chosen as a key study. The test material moistured with physiological saline was administered to abraded skin of a dorsal surface of five New Zealand White rabbits of each sex in the amount of 2000 mg/kg bw under occlusive conditions. After 24 hours the patch was removed, the excessive test material wiped off, and the animals were observed for 14 days and necropsied afterwards. There were no mortalities. Erytherna was observed in the exposed area of three male animals and one female rabbit on the first day after exposure. No other clinical abnormalities were noted. At necropsy, pale renal coloration was observed in one male animal, but this was not considered to be related to exposure to the test material. No abnormalities were observed in the remaining nine rabbits.
No data on acute inhalation toxicity of zinc bis(dibutyldithiocarbamate) were available. However, in accordance with REACH Annex VIII, the study does not need to be conducted, as the data on two other routes of exposure are available.
Justification for classification or non-classification
Based on the acute oral LD50 of > 5000 mg/kg and the acute dermal LD50 of > 2000 mg/kg, ZDBC should not be classified as hazardous to health after acute exposure, according to the EU Directive 67/548/EEC and EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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