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EC number: 238-270-9 | CAS number: 14324-55-1
- 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 oral toxicity of zinc bis(diethyldithiocarbamate) (ZDEC) has been investigated in several studies with rats, all predating GLP and OECD guidelines. The lowest obtained LD50 value was 1960 mg/kg bw in male rats. Acute dermal toxicity study with rabbits resulted in LD50 > 2000 mg/kg bw. No data on acute inhalation toxicity were available; however, as sufficient data are available on the other two routes of exposure, the study is not warranted in accordance with Column 2 of REACH Annex VIII.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 1 960 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:
- discriminating dose
- Value:
- 2 000 mg/kg bw
Additional information
Several acute oral toxicity studies with zinc bis(diethyldithiocarbamate) (ZDEC) were available for assessment, all predating GLP and OECD Guidelines. Most of them (TNO, 1976a; Pharmacology Research Inc., 1977; Younger Laboratories, 1976) reported LD50 values in rats ranging from 2450 to 3530 mg/kg bw; however, the study of Sumimoto Chemical Co., Ltd., 1977 reported lower values of 2280 mg/kw bw for female and of 1960 mg/kg bw for male rats, respectively. Two studies (TNO, 1976a; Pharmacology Research Inc., 1977) reported possible renal pathology, with necrotic spots on the kidneys of several animals (TNO, 1976a). No significant changes at necropsy were noted in the study of Sumimoto Chemical Co., Ltd., 1977. Clinical signs included mostly diarrhea, reduced appetite and activity and weight losses. Using the precautionary principle, the lowest LD50 value shall be used for risk assessment.
In the available acute dermal toxicity study with rabbits (Pharmacology Research, Inc., 1977) a single dose of 2000 mg/kg bw of ZDEC was applied to pre-moistened hair-clipped skin of each of the 6 rabbits under occlusive dressing. The patch was removed 24 hours post-dosing and animals were observed for 7 days. No mortalities were observed and the animals remained asymptomatic during the observation period. Based on the result of the study, dermal LD50 in rabbits was established to exceed 2000 mg/kg bw.
No data on acute inhalation toxicity of zinc bis(diethyldithiocarbamate) (ZDEC) were available for assessment. However, in accordance with Column 2 of REACH Annex VIII the study does not need to be conducted, as sufficient data are available on the other two routes of exposure.
Justification for classification or non-classification
Based on the acute oral LD50 value of 1960 mg/kg, zinc bis(diethyldithiocarbamate) (ZDEC) should be classified as harmful if swallowed (Xn, R22) and Category 4, H302 (harmful if swallowed) according to the EU Directive 67/548/EEC and EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008, respectively. Based on the acute dermal LD50 value of > 2000 mg/kg, classification for acute dermal toxicity is not warranted according to the EU Directive 67/548/EEC and EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
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