Bismuth

    group 15 · period 6 · p-block · post-transition metal

    minorBismuth has no WHO, EU or US drinking water value and no effluent limit; the one health based guideline read is Australia's 10 mg/L, more than six orders of magnitude above anything found in tap water, because Bi(III) hydrolyses to insoluble oxychloride and oxide at neutral pH, sticks hard to sediment and is the least toxic heavy metal; it reaches water from lead free plumbing alloys, from bismuth pharmaceuticals in sewage and from lead, tungsten and zinc smelters, and it is coming into view only because its use is rising.

    Typical wastewaters

    • drinking water plumbing (bismuth copper lead free brass) Bi(III) dissolved from the alloy surface like lead, then hydrolysed to hydroxo complexes and BiOCl where chloride is present contamination arises after treatment, so there is no source water treatment for it; not detected below 0.005 µg/L in 172 Australian samples
    • lead, tungsten and zinc smelting and refining Bi(III), hydrolysed to oxide and oxychloride solids at neutral pH, in smelter and refinery effluents where bismuth is a by-product no effluent concentration was read

    1 · Identity

    Symbol, number
    Bi, 83
    Oxidation states in water
    +3 in all natural water chemistry, as hydroxo and chloro complexes and as the solids BiOCl and Bi₂O₃; +5 only in the strong oxidant sodium bismuthate, which is a laboratory reagent, not a water species.
    Note
    The element entry covers the metal, the lead substitute market, pigments and pharmaceuticals. This chapter is about Bi(III) hydrolysis and where the element appears in water.

    2 · Occurrence in water

    Natural sources
    Weathering of bismuthinite and of the sulfide ores of lead, tungsten, tin and copper that carry it (element entry); the hydrolysed ion partitions to particles at once, so dissolved bismuth in natural water is very low. In an Australian survey bismuth was not detected (below 0.005 µg/L) in 172 drinking water samples (NHMRC).
    Anthropogenic sources
    Bismuth copper alloys replacing lead in plumbing brass are the source NHMRC identifies for drinking water; bismuth subsalicylate and other bismuth medicines reach sewage after excretion; smelter and refinery effluents where bismuth is a by-product; cosmetics and pigment plants using bismuth oxychloride and vanadate (element entry). No effluent concentration was read.
    matrixtypical rangenote
    drinking waterbelow 0.005 µg/Lregion-dependent; one surveynot detected in 172 Western Australian samples
    seawater0.00002 mg/L
    compilation value, not a measured profile
    PubChem compilation figure carried in the element entry (0.02 µg/L)

    3 · Speciation

    Bi³⁺ hydrolyses strongly at any natural pH to hydroxo complexes and, with chloride, to bismuth oxychloride; the trihalides and nitrate hydrolyse in water to the oxyhalides and oxynitrate (element entry). Knight and Turner found linear sediment sorption isotherms up to 2000 µg/L with distribution coefficients that fell from 106,000 L/kg at pH 5.0 to 17,700 L/kg at pH 9.0 in river water, consistent with hydroxo complexes sorbing to the surface, and an order of magnitude higher sorption in seawater at pH 8.0 (1,530,000 L/kg) that they attribute to organic complexation and colloids; bismuth also binds to colloidal organic matter that flocculates on estuarine mixing, so catchment bismuth is retained in estuaries.

    conditiondominant speciesnote
    acid, below pH 2Bi³⁺, BiCl²⁺ and higher chloro complexesthe only range where the free ion persists; textbook, not sourced
    river water, pH 5 to 9hydroxo complexes sorbed to sediment; BiOCl (s) where chloride is presentKnight and Turner 2020; sorption strongest at low pH
    seawater and estuariesorganically complexed and colloidal bismuth, flocculating on mixingKnight and Turner 2020
    Solubility
    Bi₂O₃, BiOCl and Bi₂S₃ are insoluble; the nitrate and chloride dissolve only in acid and hydrolyse on dilution (element entry).
    Hydrolysis
    Strong; the trihalides hydrolyse to BiOX in water (element entry). No hydrolysis constants were read.
    Complexation
    Chloride in acid; organic and colloidal binding in estuaries (Knight and Turner 2020).
    Precipitates
    BiOCl, Bi(OH)₃ and Bi₂O₃ in neutral water; Bi₂S₃ under sulfide.
    BiClX3+HX2OBiOCl(s)+2HCl\ce{BiCl3 + H2O -> BiOCl (s) + 2 HCl}
    hydrolysis of the trichloride on dilution; the trihalides hydrolyse to the oxyhalides BiOX (element entry)
    BiX3++ClX+HX2OBiOCl(s)+2HX+\ce{Bi^3+ + Cl^- + H2O -> BiOCl (s) + 2 H+}
    the same reaction written for the dissolved ion in chloride bearing water; stoichiometry from the trichloride hydrolysis, constants not read

    4 · Role in treatment

    as a problem
    leaching from lead free brass
    bismuth copper alloys stand in for lead in plumbing fittings; bismuth dissolves from the alloy surface like lead does, then hydrolyses
    NHMRC names this as the pathway to drinking water and says there is no source water treatment because the contamination arises after treatment

    5 · Removal and control

    coagulation, sedimentation and filtration (generic particulate metal removal)
    bismuth is a hydrolysed, strongly sorbed solid at neutral pH and leaves with the solids; the very high sediment distribution coefficients of Knight and Turner imply near complete partitioning to any floc
    no bismuth specific treatment study read; NHMRC found no treatment information
    Efficiency
    not read
    Interferences
    low pH and strong chloride keep bismuth dissolved as chloro complexes

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MSEPA 6020 and ICP-OES EPA 6010 (NHMRC); bismuth is listed as a stock standard in EPA 200.8 but is not one of its analyteslimit of reporting 0.001 to 0.01 µg/L (NHMRC)mass 209 is monoisotopic and free of common isobaric interference
    Sampling pitfalls
    Bismuth hydrolyses and sorbs to bottle walls within minutes at neutral pH; acidify at collection and filter first if dissolved bismuth is wanted. Do not store in chloride free acid and expect the same answer as in chloride bearing samples.

    7 · Regulatory limits

    Limits change, and many are set locally. Treat these as the published values to start from, not as your compliance target: check the standard in force at your site and the numbers written into your own permit.

    drinking water
    bodylimitnote
    NHMRC Australian Drinking Water Guidelines (bismuth fact sheet, evidence review 2023)10 mg/Lhealth based, from a 28 day rat study with bismuth metal powder (NOAEL 1000 mg/kg bw per day) and a 300 fold safety factor; reticulated water is far below it
    WHO GDWQno guideline bismuth does not appear in the Annex 3 chemical summary tables
    US EPA NPDWRnot regulated no entry in the table of regulated contaminants
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set BAT 12 metals are Cr, Cu, Ni and Zn only

    8 · Health and environmental effects

    Toxicity
    Very low: bismuth is swallowed as a stomach medicine (element entry); NHMRC reports nephrotoxicity and mortality in animals at high doses and human neurotoxicity and kidney damage from medication overdose, with bioavailability strongly dependent on the chemical form.
    Bioaccumulation
    Both duckweed and the amphipod Echinogammarus veneris accumulated bismuth strongly from bismuth nitrate solutions (Iannilli 2025).
    Ecotoxicity
    Species specific: Lemna minor showed no effect on growth or photosynthesis over 7 days at 0 to 242 mg/L bismuth nitrate, whereas the amphipod showed DNA damage in the comet assay even at the lowest concentration tested in 24 hours (Iannilli 2025); no water quality criterion exists.

    Flags

    • The 10 mg/L value is Australian and is the only numeric guideline read; it is region-dependent.
    • The seawater figure is a compilation value from the element entry.
    • The distribution coefficients are laboratory spikes into one estuarine sediment; the field concentrations at which they apply are far below the spike range.
    • The lowest amphipod concentration with DNA damage is not stated in the abstract read.

    Gaps

    • No source read gives bismuth in rivers, groundwater, municipal wastewater or smelter effluent as numbers.
    • No hydrolysis constants or solubility products for Bi(III) were read; the speciation is qualitative.
    • EU DWD 2020/2184 Annex I was not read this session.
    • Excretion and sewage fate of bismuth pharmaceuticals were not sourced.
    • No GCC discharge standard was read.

    Sources

    Conventions

    Valence electrons are counted by the usual convention: the outer shell for s- and p-block elements, ns and (n-1)d for the d-block, ns, (n-1)d and (n-2)f for the f-block. Lanthanides and actinides are placed in the f-block with no group number. Electrical conductivity is the reciprocal of the printed resistivity. Ionic radii are Shannon effective radii, six-coordinate unless noted. Where a field reads “not in sources” the value was not found; it is a gap, not a zero. Regulatory limits are the published values and change often, so check the standard in force at your site and the numbers written into your own permit before you design to them.

    Data

    Element records, isotopes, radii and the descriptive text come from PubChem (NCBI), the Los Alamos National Laboratory periodic table, IUPAC CIAAW and the IAEA Atomic Mass Data Center. Appearance, thermal conductivity, electrical resistivity, crystal structure, discovery and the origin of each name come from Wikipedia and Periodic-Table-JSON, used under CC BY-SA 4.0. Hazard classifications come from the ECHA C&L inventory via PubChem. Ionic radii follow R. D. Shannon (1976). The water chapters cite their own sources at the foot of each entry, and are written to the level of Snoeyink and Jenkins, Stumm and Morgan, MWH's Water Treatment and Metcalf and Eddy.