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EC number: 246-805-2 | CAS number: 25306-75-6
- 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
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics, other
- Remarks:
- Assessment based on chemistry and data derived from key metabolites
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Justification for type of information:
- Assessment of existing data on the substance and key metabolites formed by hydrolysis.
- Reason / purpose for cross-reference:
- assessment report
- Objective of study:
- absorption
- distribution
- excretion
- metabolism
- other: Hydrolysis
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Assessment of gastric hydrolysis and potential adsorption, distribution and excretion of hydrolysis products based on published data for the metabolites
The approach taken is to consider the chemical structure and class of this substance and to look at the existing data set for the substance itself and for the well-defined hydrolysis products.
Searches for similar substances have been performed using commercial directories and the ECHA web-site to help provide a weight of evidence for metabolic processes of the parent substance and the hydrolysis products - GLP compliance:
- no
- Radiolabelling:
- no
- Species:
- other: Non-animal assessment
- Type:
- absorption
- Results:
- The substance is unlikely to be directly absorbed in view of the extremely rapid hydrolysis to carbon disulphide and corresponding aliphatic alcohol
- Type:
- absorption
- Results:
- Carbon disulphide and low molecular weight aliphatic alcohols are readily absorbed by inhalation.
- Type:
- distribution
- Results:
- Impart to spleen and liver, mainly through blood chemistry changes, demonstrate distribution of the hydrolysis products and their metabolites
- Type:
- metabolism
- Results:
- Low molecular weight aliphatic alcohols metabolise to carbon dioxide and water and used in metabolic processes associated with energy.
- Type:
- excretion
- Results:
- No evidence of significant excretion of parent substance or hydrolysis products through urine
- Type:
- clearance
- Results:
- Low molecular weight aliphatic alcohols can be excreted through air
Carbon disulphide shown to be excreted through air exchange - Details on absorption:
- • The substance is unlikely to be absorbed orally in view of the extremely rapid hydrolysis to carbon disulphide and corresponding aliphatic alcohol
• The substance is considered highly irritating to skin and there is no evidence of dermal absorption, although in the presence of moisture, hydrolysis is likely. It is possible that the reported local dermal reaction is directly linked to reactivity on the skin surface.
• Inhalation exposure to the parent substance is not considered significant, although exposure to the hydrolysis products cannot be ignored. - Details on distribution in tissues:
- • The metabolites are considered to be readily transported and metabolised further.
• Impact on organs including spleen and liver are consistent with carbon disulphide and alcohols. - Test no.:
- #1
- Transfer type:
- blood/placenta barrier
- Remarks:
- Research into carbon disulphide demonstrates transfer across the placenta following inhalation exposure.
- Observation:
- slight transfer
- Remarks:
- Not quantified
- Details on excretion:
- No evidence of excretion of the parent substance or immediate hydrolysis products. Kidneys and urine appear not to be affected in any studies performed on the parent or hydrolysis products.
- Metabolites identified:
- yes
- Remarks:
- Radiolabelled material was found to be excreted in urine in the form of complex sulphur-containing thiocarbonates
- Details on metabolites:
- Low molecular weight aliphatic alcohols metabolise to carbon dioxide and water and used in metabolic processes associated with energy.
- Enzymatic activity measured:
- Not specified
- Conclusions:
- Non accumulative
- Executive summary:
From evidence derived from direct testing and from information obtained on the hydrolysis products, it can be concluded that:
- The substance is unlikely to be absorbed orally in view of the extremely rapid hydrolysis to carbon disulphide and corresponding aliphatic alcohol
- The substance is considered highly irritating to skin and there is no evidence of dermal absorption, although in the presence of moisture, hydrolysis is likely. It is possible that the reported local dermal reaction is directly linked to reactivity on the skin surface.
- A human study shows that CS2 is absorbed through the skin from aqueous solutions.
- Inhalation exposure to the parent substance is not considered significant, although exposure to the hydrolysis products cannot be ignored.
- The metabolites are considered to be readily transported and metabolised further.
- Impact on organs including spleen and liver are consistent with carbon disulphide and alcohols.
- No evidence of excretion of the parent substance or immediate hydrolysis products. Kidneys and urine appear not to be affected in any studies performed on the parent or hydrolysis products.
- CS2 is eliminated via exhaled air. After termination of exposure, the elimination of unaltered CS2 via the exhaled air amounts roughly to 5 -50% of the absorbed amount.
- Unaltered CS2 is hardly excreted via the kidneys: less than 1%
- Radiolabelled material was found to be excreted in urine in the form of complex sulphur-containing thiocarbonates suggesting incorporation of carbon disulphide into other substances
- Low molecular weight aliphatic alcohols can be excreted through air, but typically metabolise to carbon dioxide and water and used in metabolic processes associated with energy.
- The substance and the hydrolysis products and biological metabolites are not considered accumulative
Reference
Description of key information
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
Xanthates are metabolized in the human or animal bodies to carbon disulfide(CAS# 75-15-0)due to presence of the CS2/cysteine (glutathione) conjugation product , 2-thiothiazolidine-4-carboxilic acid (TTCA) in urine of exposed workers or animals.
The lungs are the primary rout of excretion of unmetabolized carbon disulfide in humans and animals exposed by inhalation, whereas the kidneys are the primary route of excretion of carbon disulfide metabolites.
Assessment of the toxicokinetics behavior of the substance to the extent that can be derived from the relevant available information..(Donoghue A.M., Occup. Med. Vol. 48, 469-470,1998)
The expired CS2in the exhaled air was monitored in the study of the metabolism of xanthates with humans and guinea pigs. After injection of 50 or 100mg/kg of sodium ethyl xanthate in guinea pigs up to 7% was expired as CS2during 8 hours. The rate of elimination was dose-related, however the total percentage recovered was independent of dose after administration of sodium or
potassium xanthate. Co injection of ethyl alcohol with sodium ethyl xanthate increased rate of CS2elimination and greater total recovery.
Study of CS2elimination in breath after oral intake in human volunteers of 150 and 250 mg of sodium ethyl xanthate showed a maximum rate 13-57 µm/m3/h between 1-2h, complete elimination by 6h.
Sodium ethyl xanthate is metabolized to CS2(CAS# 75-15-0) due to presence in urine of exposed workers, of the CS2/cysteine conjugated product, 2-thiothiazolidine-4-carboxylic acid (TTCA).
The metabolite was detected in urine of a worker exposed to extensive skin contamination with the xanthate powder
and solution during the reagent mixing. An illness consisting of predominantly gastrointestinal symptoms began 20h after the exposure.
Carbon disulphide is readily absorbed by inhalation.6 Studies also indicate that carbon disulphide as a liquid, such as a solvent or aqueous solution, is absorbed through the skin. Studies in humans have shown that approximately 70–90% of carbon disulphide absorbed into the body is metabolised, with 1% excreted unchanged and the remainder exhaled. Due to its affinity for lipid-rich tissues and organs, carbon disulphide rapidly disappears from the bloodstream. In humans, carbon disulphide is metabolised to give organo-sulphur compounds such as thiourea in the urine. Studies in rats and guinea pigs have indicated that carbon disulphide is initially accumulated in the liver, brain, blood and adrenals.
Carbon disulfide is metabolized by cytochrome P-450 to an unstable oxygen intermediate which may either degrade to atomic sulfur and carbonyl sulfide or hydrolyze to form atomic sulfur and monothiocarbonate. The atomic sulfur may either bind to macromolecules or be oxidized to sulfate. The carbonyl sulfide may be converted to monothiocarbonate by carbonic anhydrase. Dithiocarbamates are the products of the reaction of CS2with amino acids. In vitro studies found that carbon disulfide reacts with amino acids in human blood, the half time of this reaction was 6,5h. Thiocarbamide has been found in the urine of exposed workers. After inhalation exposure of male human , up to 90% of the retained carbon disulfide was metabolized , the remainder was excreted by the lungs (6-10%) and in urine (about 1%) Carbon disulfide is oxidized by the liver mixed-function oxidase system to carbonyl sulfide and then undergoes further desulfurizatioin releasing elemental sulfur.
Metabolism of xanthates:
Sodium ethyl xanthate is metabolized to CS2(CAS# 75-15-0)due to presence in urine of exposed workers, of the CS2/cysteine conjugated product, 2-thiothiazolidine-4-carboxylic acid (TTCA). The metabolite was detected in urine of a worker exposed to extensive skin contamination with the xanthate powder and solution during the reagent mixing. An illness consisting of predominantly gastrointestinal symptoms began 20h after the exposure.(Donoghue A.M., Occup. Med. Vol. 48, 469-470,1998)
Study of CS2elimination in breath after oral intake in human volunteers of 150 and 250 mg of sodium ethyl xanthate showed a maximum rate 13-57 µm/m3/h between 1-2h, complete elimination by 6h(Merlevede E., Peters J., 1965, Archives of the Belgian Medical Society, 23(8): 513-551).
Metabolism of carbon disulfide(CAS# 75-15-0)
Carbon disulfide is metabolized by cytochrome P-450 to an unstable oxygen intermediate which may either degrade to atomic sulfur and carbonyl sulfide or hydrolyze to form atomic sulfur and monothiocarbonate. The atomic sulfur may either bind to macromolecules or be oxidized to sulfate. The carbonyl sulfide may be converted to monothiocarbonate by carbonic anhydrase(Beauchamp R.D., et all, 1983, CRC Critical Reviews in Toxicology 11: 169-278)
Dithiocarbamates are the products of the reaction of CS2with amino acids. In vitro studies found that carbon disulfide reacts with amino acids in human blood, the half time of this reaction was 6,5h. Thiocarbamide has been found in the urine of exposed workers(Pergal M.,et all , 1972, Arch. Environ Health 25:42-44). After inhalation exposure of male human , up to 90% of the retained carbon disulfide was metabolized , the remainder was excreted by the lungs (6-10%) and in urine (about 1%)(McKee R.W., et all, JAMA 122:217-222).
Carbon disulfide is oxidized by the liver mixed-function oxidase system to carbonyl sulfide and then undergoes further desulfurizatioin releasing elemental sulfur(Dalvi R.R. , et all, 1974, Life Sci. 14:1785-1796).
Conjugation of carbon disulfide or carbonyl sulfide with endogenous glutathione yields thiazolidine-2-thione-4-carboxylic acid (TTCA) and 2-oxythiazolidine-4-carboxylic acid, respectively(Van Doorn R., et all,1981, Arch. Environ. Health 36:289-2970). High concentration about 320mM of TTCA were detected in the urine of women exposed to approximately 32 ppm (100 mg/m3) CS2through inhalation.
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