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Registration Dossier
Diss Factsheets
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EC number: 238-953-1 | CAS number: 14882-18-9
- 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
- Type of information:
- calculation (if not (Q)SAR)
- Remarks:
- Migrated phrase: estimated by calculation
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- A written assessment of toxicokinetic behaviour is considered appropriate for the substance. The substance displays only minor toxicological effects in any of the studies proposed, and is deemed to be be not harmful for health effects. As such, it is deemed inappropriate in terms of animal welfare to conduct a toxicokinetic assessment when no harmful effects are predicted based on known toxicology. A written assessment has therefore been prepared to address this endpoint.
- Principles of method if other than guideline:
- A written assessment based on the toxicological profile of the substance.
- Species:
- other: not applicable
- Details on test animals or test system and environmental conditions:
- Not applicable
- Route of administration:
- other: not applicable
- Details on exposure:
- Not applicable
- Duration and frequency of treatment / exposure:
- Not applicable
- Remarks:
- Doses / Concentrations:
Not applicable - No. of animals per sex per dose / concentration:
- Not applicable
- Positive control reference chemical:
- Not applicable
- Details on study design:
- Not applicable
- Details on dosing and sampling:
- Not applicable
- Preliminary studies:
- Not applicable
- Details on absorption:
- Not applicable
- Details on distribution in tissues:
- Not applicable
- Details on excretion:
- Not applicable
- Details on metabolites:
- Not applicable
- Conclusions:
- Interpretation of results (migrated information): other: low bioaccumulation potential based on review of study results
Bismuth subsalicylate in pharmaceutical preparations is converted to bismuth carbonate and sodium salicylate in the small intestine. The bismuth portion of bismuth subsalicylate is poorly absorbed from the gastrointestinal tract with an oral bioavailability reported to be < 0.005%. There are very few data on the dermal absorption of bismuth, however, absorption via this route is expected to be low. In contrast, the salicylate portion of bismuth subsalicylate is well absorbed via the oral route with a bioavailability > 90%. Salicylates are also absorbed percutaneously. Based on particle size distribution data and modelling of deposition in the respiratory tract, it is estimated that between 2.9% to 9.2% of bismuth subsalicylate is absorbed via inhalation.
The small amount of bismuth that is absorbed is distributed to various organs with the highest concentration expected to be in the kidney. Bismuth can cross the blood-brain barrier. The results of a study in guinea pigs with radiobismuth suggest poor placental transfer of bismuth (< 1%). Excretion of absorbed bismuth is via the urinary and faecal routes. The distribution half-life of bismuth is 1 to 4 hours, the plasma half-life is 5 to 11 days and the urinary excretion half-life lasts between 21 to 72 days. Unabsorbed bismuth is excreted in the faeces. Salicylates are widely distributed through the body with an elimination half-life that is dependent on level of exposure; half-life may be prolonged to 22 hours with ingestion of toxic doses. Elimination is via metabolism in the liver with urinary excretion of conjugated metabolites and free salicylic acid. The elimination of salicylates at therapeutic doses follows first order kinetics, which may change to zero order kinetics with toxic doses due to saturation of 2 of the 5 possible pathways of elimination. Alkalinisation of the urine increases the urinary excretion rate of salicylates. - Executive summary:
A toxicokinetics assessment was conducted for bismuth subsalicylate using available data including data from the published literature.
Absorption: The bismuth portion of bismuth subsalicylate is poorly absorbed from the gastrointestinal tract with an oral bioavailability reported to be < 0.005%. There are very few data on the dermal absorption of bismuth, however, absorption via this route is expected to be low. In contrast, the salicylate portion of bismuth subsalicylate is well absorbed via the oral route with a bioavailability of > 90%. Salicylates are also absorbed percutaneously. Based on particle size distribution data and modelling of deposition in the respiratory tract, it is estimated that between 2.9% and 9.2% of bismuth subsalicylate may be absorbed via inhalation.
Distribution: The small amount of bismuth that is absorbed is distributed to various organs with the highest concentration expected to be in the kidney. The results of a study in guinea pigs with radiobismuth indicate poor placental transfer of bismuth (<1%), however, bismuth can cross the blood-brain barrier. The distribution half-life of bismuth is 1 to 4 hours and the plasma half-life is 5 to 11 days. Salicylates are widely distributed through the body with an elimination half-life that is dependent on level of exposure; the half-life may be prolonged to 22 hours with ingestion of toxic doses.
Elimination: Excretion of absorbed bismuth is via the urinary and faecal routes and the urinary excretion half-life lasts between 21 to 72 days. Unabsorbed bismuth is excreted in the faeces.Elimination of salicylate is via metabolism in the liver with urinary excretion of conjugated metabolites and free salicylic acid. The elimination of salicylates at therapeutic doses follows first order kinetics, which may change to zero order kinetics with toxic doses due to saturation of 2 of the 5 possible pathways of elimination. Alkalinisation of the urine increases the urinary excretion rate of salicylates.
Reference
Description of key information
A toxicokinetics assessment was conducted for bismuth subsalicylate using available data including data from the published literature. Based on the results of this assessment, the substance is considered to have low bioaccumulation potential. As the salicylate component of bismuth subsalicylate is expected to be well absorbed by the dermal and oral routes, a default absorption rate of 100% has been assumed for these two routes as a worst case even though the bismuth component is very poorly absorbed. The inhalation absorption rate is based on particle size distribution data and modelling of deposition in the respiratory tract.
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
- Absorption rate - oral (%):
- 100
- Absorption rate - dermal (%):
- 100
- Absorption rate - inhalation (%):
- 9.2
Additional information
A toxicokinetics assessment was conducted for bismuth subsalicylate using available data including data from the published literature.
Absorption: The bismuth portion of bismuth subsalicylate is poorly absorbed from the gastrointestinal tract with an oral bioavailability reported to be < 0.005%. There are very few data on the dermal absorption of bismuth, however, absorption via this route is expected to be low. In contrast, the salicylate portion of bismuth subsalicylate is well absorbed via the oral route with a bioavailability of > 90%. Salicylates are also absorbed percutaneously. Based on particle size distribution data and modelling of deposition in the respiratory tract, it is estimated that between 2.9% and 9.2% of bismuth subsalicylate may be absorbed via inhalation.
Distribution: The small amount of bismuth that is absorbed is distributed to various organs with the highest concentration expected to be in the kidney. The results of a study in guinea pigs with radiobismuth indicate poor placental transfer of bismuth (<1%), however, bismuth can cross the blood-brain barrier. The distribution half-life of bismuth is 1 to 4 hours and the plasma half-life is 5 to 11 days. Salicylates are widely distributed through the body with an elimination half-life that is dependent on level of exposure; the half-life may be prolonged to 22 hours with ingestion of toxic doses.
Elimination: Excretion of absorbed bismuth is via the urinary and faecal routes and the urinary excretion half-life lasts between 21 to 72 days. Unabsorbed bismuth is excreted in the faeces.Elimination of salicylate is via metabolism in the liver with urinary excretion of conjugated metabolites and free salicylic acid. The elimination of salicylates at therapeutic doses follows first order kinetics, which may change to zero order kinetics with toxic doses due to saturation of 2 of the 5 possible pathways of elimination. Alkalinisation of the urine increases the urinary excretion rate of salicylates.
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