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EC number: 923-511-9 | CAS number: -
- 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
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- discriminating dose
- Value:
- 5 000 mg/kg bw
Acute toxicity: via dermal route
Endpoint conclusion
- Dose descriptor:
- discriminating dose
- Value:
- 2 000 mg/kg bw
Additional information
Green liquor sludge contains several alkaline metal compounds/salts such as hydroxides, oxidised sulfur constituents (sulfates, thiosulfate and sulfites) and carbonates. Acute toxicity values for all of these compounds have been earlier characterized extensively in animal studies and reviewed in CSR report to Green liquor sludge. A lot of human data for these substances can be also found, because these compounds have been in the industrial use during decades. From the GLS compounds carbonates and hydroxides are rapidly dissolved and resulted nontoxic metabolites, which are removed from the body mainly via kidneys. Because of their rapid inactivation, these compounds are not believed to result in systemic toxicity and they have relatively low acute toxicity levels according the earlier animal experiments. However, due to their alkaline properties an irritation and corrosiveness to skin, respiratory tract and trachea is noticed depending on their concentrations.
Acute inhalation toxicity for sulfides and oxidised sulfur constituents seem to be very low when pH is maintained on alkaline side. However, hydrogen sulfide gases (H2S) are toxic, lethal if inhaled in high concentrations. H2S may evaporated from GLS in contact with acids. If H2S gas is evolved it will be the most toxic compound in GLS and lethal concentrations in animal experiments are: LC50 335 ppm 6 hours for rats and LC100 722 ppm 50 minutes for mice. The lowest lethal dose evaluated for humans in accidental case reports was only 76 ppm of hydrogen sulfide. However, no sulfides were detected in the GLS samples determined in the studies for this report.The pH of GLS is over 12 and it is unlikely that hydrogen sulfide is released in gaseous form under normal handling conditions.
Acute oral and dermal toxicity experiments with rats verified low acute toxicity values for GLS. The LD50,oralwas determined to be > 2000 mg/kg body weight. Based on the guidance given in OECD guideline 423 (annex 2c), the LD50,oral can be assessed to be > 5000 mg/kg body weight. According to the decision trees of the OECD Guideline and the EC Directive the LD50,dermal of GLS is higher than 2000 mg/kg body weight in rats.
No test results are available for inhalation route. GLS is a non volatile solid substance. However, it may form inhalable dusts like any other solid powders when dry. Particle size distribution study indicate (468 µm (50%), 9 µm (10 percentile)) that only a small fraction might enter the small alveoli. The acute inhalation of GLS dust may cause discomfort and stress as well as sign of local irritation to nasal, bronchiolar and ocular mucous membranes. Highly alkaline mists are acutely toxic if inhaled. However, GLS is a solid paste that contains >50% water before drying and therefore it is unlikely that alkaline mists can be formed. The alkality is also rapidly reduced by the influence of CO2 in the air. We can hypothesize that GLS's acute inhalation toxicity caused by OH- ions reduces rapidly with time and distance. Acute inhalation toxicity for sulfides and oxidised sulfur constituent seem to be very low when pH is maintained in alkaline side. In conclusion, GLS dusts are expected to be acutely non-toxic via inhalation route.
Justification for classification or non-classification
Acute oral and dermal toxicity experiments with rats verified low acute toxicity for Green liquor sludge.
The LD50,oral was > 2000 mg/kg (wet wt. test material) body weight in rats.
The LD50,dermal was > 2000 mg/kg (wet wt. test material) body weight in rats.
Acute toxicity for inhalation route is expected to be low, based on route-to-route extrapolation from the oral and dermal test results.
As a conclusion, the acute systemic toxicity for the tested patch of GLS is very low and overall classification for acute toxicity for GLS is not needed.
Classification for Acute toxicity:
No classification
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