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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
Description of key information
Additional information
TERRESTRIAL FATE:
Xanthates are dithiocarbonates which are used in the flotation processes for most sulfide minerals, the metallic elements such as copper,nickel, lead, zinc, silver and gold, and a number of oxidized minerals oflead and copper. Flotation is a physiochemical method of concentratingfinely ground ores. The process involves chemical treatment of an ore pulp to create conditions favorable for the attachment of certain mineral particles to air bubbles. The air bubbles carry the selected minerals tothe surface of the pulp and form a stabilized froth which is skimmed offwhile the other minerals remain submerged in the pulp. Xanthates fit in to this process by functioning as "collectors." Collectors aid in the attachmentof a mineral particle to an air bubble. Sodium isopropyl xanthate is one of the most commonly used xanthates.
Sodiumi sobutyl xanthate is hydrolytically unstable when exposed to acidic conditions, reverting rapidly to alcohol, carbon disulphide and caustic soda, andtherefore will not persist in the acidic environment of tailings dams. If discharged to waterways, the chemical would be likely to persist for at least some days,hydrolysing only slowly in this more neutral environment. However, it is not expected to bioaccumulate in view of its ionic character.Sodium isobutyl xanthate is not expected to contaminate the environment where ore tailings are confined to well constructed tailings dams. Most will be retained on sulphide minerals and destroyed when they are dried after flotation. Minor residues that remain associated with tailings will be destroyed by hydrolysis intailings dams.
Based on estimated Koc value of 11.7.L/kg, indicates that Sodium isobutyl xanthate is expected to have very high mobility in soil.
Volatilization of Sodium isobutyl xanthate from moist soil surfaces is not expected to be an important fate process given a estimated Henry's Law constant of 3.491E-016 atm-m3/mole (3.538E-011 Pa-m3/mole) . The estimated Henrys Law Constant (25 deg C) measured by calculation from EPI SuiteTM v4.1, HENRYWIN v3.20 Program was 3.491E-016 atm-m3/mole (3.538E-011 Pa-m3/mole) , which is almost zero.
Xanthates have not been subjected to regulatory action in any countryexceptAustralia. No further investigations were conducted as several xanthates were nolonger used inworld.Use of those that remained was not widespread, beingconfined to a few users in the mining industry.
Assuming a treatment rate of 500 gms sodiumIsobutylxanthate per tonne of feed, 1%loss to tailings and 30% solids content in the tailings slurry, the concentration ofsodiumIsobutylxanthate in the slurry will be in the order of 5 gms in 3.3 tonnes, orabout1.5 ppm. Concentrations of sodiumIsobutylxanthatelikely to be found in the tailings slurry may bemoderately toxic to aquatic fauna. Such wastestreams should therefore not be discharged to waterways.
When suitable precautions are taken to avoid entry of tailings to waterways, theenvironmental risk of sodiumIsobutylxanthate can be described as minimal in view ofthe low environmental exposure and limited persistence.
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