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EC number: 268-612-2 | CAS number: 68131-30-6 A solution obtained by dissolving the chemicals recovered in the alkaline pulping process in water.
- 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)
Description of key information
Key value for chemical safety assessment
Additional information
The evaluation of toxicokinetics of green liquor applies constituent/ion based approach. Therefore, toxicokinetics of these different ions is discussed separately in the chapters dealing with toxicokinetics. Sodium and potassium hydroxides, sulfides, oxidised sulfur constituents and carbonates, in the GL are dissociated in the body fluids. The true speciation of these ions in the human body is determined mainly by the nature of the ion, pH and ionic composition of the physiological fluids.
Sodium and potassium hydroxides and carbonates in GL are rapidly dissolved in the body. Resulted sodium and potassium ions are normal and essential constituents of the blood and other body fluids and their concentration in the blood is controlled by renal excretion . Carbonate and hydroxide ions in GL could potentially affect the acid-base balance of the body. However, they are usually neutralized by gastric acid and the pH regulation mechanisms of the blood.Therefore they are not expected to be systemically available in the body under normal handling conditions. However, due to their corrosive properties in high concentrations the alkalis might cause burns to the skin and therefore facilitate the exposure of GL to the body.
Soluble sulfide salts dissociate into sulfide ions that are oxidated to sulfates (major metabolic excretory pathway) or methylated (minor detoxification pathway) and excreted by the kidney. Similarly, tiosulfate in GL is excreted by the kidney. Sulfide ions also can react with the hydrogen ions in water to form the hydrosulfide ion (HS¯) or hydrogen sulfide (H2S). The relative concentrations of these species are a function of the pH of the water; hydrogen sulfide concentrations increase with decreasing pH. After ingestion there can be formation of H2S in the stomach due to acidity.The formed H2S can be absorbed through the gastrointestinal tract, bound by plasma albumin and distributed to different organs causing toxic effects. Direct toxic effects to lung tissues are also possible if volatile H2S is formed and inhaled. It is doubtful whether skin absorbs enough sulfides to cause systemic poisoning. Hydrogen sulfide is excreted primarily as sulfate (free sulfate or thiosulfate) in the urine. It is also excreted unchanged in exhaled air and in feces and flatus.
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