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EC number: 215-136-8 | CAS number: 1304-85-4
- 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
Bioaccumulation: terrestrial
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation: terrestrial
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: No experimental details available
- Justification for type of information:
- See attached read-across justification
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Analyis of Bi concentrations in soils and mushrooms in Germany.
- GLP compliance:
- not specified
- Radiolabelling:
- no
- Vehicle:
- no
- Test organisms (species):
- other: Clitocybe odora
- Test temperature:
- not reported
- pH:
- not reported
- TOC:
- not reported
- Moisture:
- not reported
- Details on test conditions:
- not reported
- Nominal and measured concentrations:
- not reported
- Type:
- BSAF
- Value:
- 0.047 dimensionless
- Details on results:
- Bi concentration in soil: 5.6 mg Bi/kg dw
Bi concentration in fungi: 0-0.26 mg Bi/kg dw - Reported statistics:
- not reported
- Validity criteria fulfilled:
- not specified
- Conclusions:
- No experimental details are available; study is used as weight of evidence for the absence of Bi accumulation in plants.
- Endpoint:
- bioaccumulation: terrestrial
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: No paired observations of Bi concentrations in soil and plants, only concentration ranges reported, no individual data.
- Justification for type of information:
- See read-across justification attached below.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Determination of Bismuth contamination in plants and soil near a mine in Korea.
- GLP compliance:
- not specified
- Radiolabelling:
- no
- Details on sampling:
- Various crop plants including corn grain (Zea mays), jujube grain (Zizyphus jujuba), perilla leaves (P. frutescens var. japonica), red pepper (Capsicum annuum), soybean leaves (Glycine max) and spring (Welsh) onions (Allium cepa) were sampled in and around the mine. Similar materials were also collected at a nearby control area. The samples were thoroughly washed in deionized water and dried in a clean room at room temperature (20 °C) for 5 days.
- Vehicle:
- no
- Test organisms (species):
- other: Zea mays, Capsicum annuum, Glycine max, Allium cepa, Zizyphus jujuba, P. frutescens var. Japonica
- Test temperature:
- not reported
- pH:
- 4.9-6.6
- TOC:
- organic matter: 3.1-5.4%
- Moisture:
- not reported
- Details on test conditions:
- unpolluted soil, Clay%: 2-16, CEC: 13-53 cmolc/kg.
- Nominal and measured concentrations:
- not reported
- Type:
- BSAF
- Value:
- 0.021 dimensionless
- Basis:
- other: grains
- Calculation basis:
- steady state
- Remarks on result:
- other: for Zea mays
- Type:
- BSAF
- Value:
- 0.014 dimensionless
- Basis:
- other: peppers
- Calculation basis:
- steady state
- Remarks on result:
- other: for Capsicum annuum
- Type:
- BSAF
- Value:
- 0.029 dimensionless
- Basis:
- other: leaves
- Calculation basis:
- steady state
- Remarks on result:
- other: for Glycine max
- Type:
- BSAF
- Value:
- 0.114 dimensionless
- Basis:
- other: onion
- Calculation basis:
- steady state
- Remarks on result:
- other: for Allium cepa
- Type:
- BSAF
- Value:
- 0.007 dimensionless
- Basis:
- other: grain
- Calculation basis:
- steady state
- Remarks on result:
- other: for Zizyphus jujuba
- Type:
- BSAF
- Value:
- 0.036 dimensionless
- Basis:
- other: leaves
- Calculation basis:
- steady state
- Remarks on result:
- other: for perilla
- Details on results:
- Bi concentration in soil: 0.9-1.8 mg Bi/kg dw
Bi concentration in plants:
- maize grains: 0.03 mg Bi/kg dw
- pepper: 0.01-0.04 mg Bi/kg dw
- soybean leaves: 0.02-0.08 mg Bi/kg dw
- spring onions: 0.06-0.25 mg Bi/kg dw
- jujube grain: 0.01-0.02 mg Bi/kg dw
- perilla leaves: 0.05 mg Bi/kg dw - Reported statistics:
- not reported
- Validity criteria fulfilled:
- not specified
- Conclusions:
- No paired observations of Bi concentrations in soil and plants, only concentration ranges reported, no individual data; study is used as weight of evidence for the absence of Bi accumulation in plants.
- Endpoint:
- bioaccumulation: terrestrial
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: Only averages and standard error of 5 root and soil samples were reported. No relevant exposure: only top 4 cm of the soil samples, not representative for the whole soil
- Justification for type of information:
- See read-across justification attached below.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Determination of ambiet Bismuth concentration in soil and plants from an unpolluted area.
- GLP compliance:
- not specified
- Radiolabelling:
- no
- Details on sampling:
- The site studied was a beech forest stand in North-central Scania (568059N; 138389E), South Sweden. Sampling was carried out in early November 2002, just after leaf-fall. Five square sampling areas, each 50=50 cm, were selected along a 40 m line in the middle of the forest (ca. 0.5 km from any forest margin), each 10 m apart and ) 2 m from the nearest beech trunk. Litter, mainly consisting of entire and little decomposed beech leaves, was removed and the upper 4 cm of the
mor with numerous fine beech roots was sampled quantitatively using metal-free plastic tools and HCl yaq washed, powder-free plastic gloves (as throughout subsequent sampling and pre-treatments). The material was passed through a 6 mm HCl yaq washed nylon screen mounted on a wooden frame, all mor material passing the screen collected as soil sample. The <1 mm diameter roots were cut and collected from the material remaining on the screen and carefully washed with demin. water in a laboratory, where no chemicals were allowed. The root tips were morphologically ectomycorrhizal. Each sample was carefully mixed and all materials dried at 40 8C to constant weight. - Vehicle:
- no
- Test organisms (species):
- other: Fagus sylvatica
- Details on test organisms:
- The beech stand was closed, dominating trunks being 100 – 130-year-old and developed from former semi-natural, never-fertilized wooded pastures.
- Test temperature:
- not reported
- pH:
- 3.2-3.6
- TOC:
- not reported
- Moisture:
- not reported
- Details on test conditions:
- The materials studied were ectomycorrhizal beech (Fagus sylvatica L.) roots and their almost purely organic soil substrate, the O-horizon (mor;
raw humus) of a Podzol in South Sweden, developed in a site which has been untouched by forestry or other mechanical disturbance since at least 50 years and located in an area with no local sources of pollution - Nominal and measured concentrations:
- field concentrations are measured.
- Type:
- BSAF
- Value:
- 0.13 dimensionless
- Basis:
- other: fine roots (<1 mm diameter)
- Calculation basis:
- steady state
- Details on results:
- Bi concentration soil: 0.092 mg Bi/kg dw
Bi concentration plant: 0.012 mg Bi/kg dw - Reported statistics:
- not reported
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Only averages and standard error of 5 root and soil samples were reported. No relevant exposure: only top 4 cm of the soil samples, not representative for the whole soil.; study is used as weight of evidence for the absence of Bi accumulation in plants.
Referenceopen allclose all
Description of key information
No reliable data are available for the bioaccumulation of bismuth subnitrate in terrestrial organisms. The data available for uptake of read-across substance, bismuth, in plants and fungi indicate BSAF values between 0.007 and 0.13, indicating the absence of bismuth accumulation from soil to plants or fungi. No data were identified for bioaccumulation of bismuth subnitrate or bismuth in terrestrial invertebrates.
Key value for chemical safety assessment
- BCF (terrestrial species):
- 0.13 dimensionless
Additional information
No reliable data are available for the bioaccumulation of bismuth subnitrate or bismuth in terrestrial organisms. There are data available for uptake of read-across substance, bismuth, in plants and fungi with a range in plant bismuth concentrations between 0.01 and 0.26 mg bismuth/kg dry weight for soil concentrations between 0.09 and 5.6 mg bismuth/kg dry weight. This results in BSAF values between 0.007 and 0.13, indicating the absence of bismuth accumulation from soil to plants or fungi. No data were identified for bioaccumulation of bismuth subnitrate or bismuth in terrestrial invertebrates.
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