Gallium

    group 13 · period 4 · p-block · post-transition metal

    minorGallium has no drinking water or effluent limit anywhere read and no treatment role; its water story is trace hydroxo-complexed Ga(III) at picomoles per kilogram in the sea, a wastewater-impacted Taiwanese stream a thousand times higher, and compound-semiconductor (GaAs) fab effluent from which the metal is now worth recovering.

    Typical wastewaters

    • semiconductor and photovoltaic manufacture (GaAs and GaN wafer fabrication) dissolved Ga(III) with arsenic in rinse and etch water; Ga³⁺ and its first hydroxo complexes in acid process water at pH 2 to 3 the arsenic, not the gallium, is the regulated parameter; the gallium is recovered by siderophore complexation; no concentration given in the abstract read
    • municipal sewage (urban wastewater reaching a coastal stream, Taiwan) hydroxo-complexed Ga(III), Ga(OH)₃^0 and Ga(OH)₄⁻, 11,000 to 19,000 pmol/L in the receiving stream the review quotes the wastewater impacted stream, not the effluent itself

    1 · Identity

    Symbol, number
    Ga, 31
    Oxidation states in water
    +3 only; hydrolysed to Ga(OH)₃^0 and Ga(OH)₄⁻ in natural water (the review's thermodynamic statement for Ga and In)
    Note
    The element entry covers the amphoteric metal and its hydroxide. In water gallium behaves as a smaller, more hydrolysed aluminium: no redox chemistry, solubility controlled by hydroxide.

    2 · Occurrence in water

    Natural sources
    Weathering of aluminium minerals in which gallium substitutes for Al (bauxite, sphalerite in the element entry); scavenged in the ocean, with elevated surface and deep concentrations and a minimum at intermediate depth.
    Anthropogenic sources
    Semiconductor and optoelectronic manufacture (GaAs, GaN wafers); wafer fabrication process water; urban wastewater in Taiwan raised a coastal stream to 11,000 to 19,000 pM.
    matrixtypical rangenote
    seawater2 to 40 pmol/kgNorth East Pacific 2 to 30, South and Central Atlantic 6 to 40, North West Pacific 3 to 30, surface to about 5000 m
    coastal stream, wastewater impacted11,000 to 19,000 pmol/Lone siteTaiwan; the only strongly anthropogenic water value in the review
    industrial wastewaternot quoted as a number
    abstract only, no concentration given
    two wafer fabrication process waters described as low gallium concentration; 100 percent of the Ga was complexed by desferrioxamine siderophores and recovered at 69.8 and 92.9 percent purity

    3 · Speciation

    Dissolved inorganic gallium is the neutral trihydroxide and the gallate anion Ga(OH)₄⁻; the free ion matters only in acid water. Because hydrolysis is so strong, gallium is scavenged onto particles and its ocean profile is that of a scavenged element.

    conditiondominant speciesnote
    seawater and neutral to alkaline fresh waterGa(OH)₃^0, Ga(OH)₄⁻from thermodynamic calculation quoted in the review
    acid process water, pH 2 to 3Ga³⁺ and the first hydroxo complexesthe pH at which biosorption and siderophore recovery were run
    Solubility
    Controlled by gallium hydroxide, amphoteric like aluminium hydroxide; no solubility product was read this session.
    Hydrolysis
    Ga³⁺ hydrolyses at lower pH than Al³⁺ and passes to the tetrahydroxo anion in neutral water (qualitative, from the review's species list).
    Complexation
    Hydroxamate siderophores (desferrioxamine B and E) bind Ga³⁺ so strongly that 100 percent complexation was reached in fab process water; EDTA in six fold excess at pH 3.5 strips it again.
    Precipitates
    Ga(OH)₃ or GaOOH on neutralising acid gallium solutions; amphoteric, so it redissolves as gallate in strong alkali. None forms in natural water at natural concentrations.
    GaX3++4HX2OGa(OH)X4X+4HX+\ce{Ga^3+ + 4 H2O -> Ga(OH)4^- + 4 H+}
    overall hydrolysis to the gallate anion, the dominant species in seawater; a stoichiometric statement of the species named in the review, no constant read

    4 · Role in treatment

    as a problem
    gallium in compound semiconductor effluent
    GaAs wafer processing leaves dissolved gallium with arsenic in rinse and etch water; the arsenic, not the gallium, is the regulated parameter
    the gallium is a resource, not a pollutant: recovery from fab water is the research theme

    5 · Removal and control

    biosorption on dead algal biomass
    surface charge interaction between biomass and Ga species; desorbed by acid washing
    pH 2.3 to 2.8, simulated semiconductor wastewater
    Efficiency
    14.1 mg/g at pH 2.3 rising to 38.5 mg/g at pH 2.8
    siderophore complexation and reversed-phase chromatography
    desferrioxamine B or E binds Ga³⁺ through hydroxamate groups; the complex is caught on a C₁₈ column and Ga released with EDTA
    wafer fabrication process water; decomplexation above 90 percent with six fold EDTA at pH 3.5
    Efficiency
    100 percent complexation; above 95 percent recovery of the complex at 69.8 (DFOB) and 92.9 percent (DFOE) purity
    Interferences
    other metals in the process water lower the purity

    6 · Analytics

    methodstandarddetection limitnote
    HR-ICP-MS after automated chelating resin preconcentrationresearch method, no standard method readpmol/kg level (seawater values in the review are 2 to 40 pmol/kg)the ocean data in the review come from preconcentration methods
    Sampling pitfalls
    Gallium is scavenged: filter at once and acidify, and use trace-metal clean handling, since pmol/kg levels are far below any laboratory blank from glass or aluminium contact.

    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
    WHO GDWQ 4th ed. with addenda (2022)no guideline not in Table A₃.3 (guideline values) nor in Table A₃.2 (chemicals considered but not given a value)
    EU DWD 2020/2184not set not an Annex I parameter
    US EPA NPDWRnot regulated no MCL
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902), BAT 12not set Tables 1 to 3 carry TOC, COD, TSS, TN, Ninorg, TP, AOX, Cr, Cu, Ni and Zn only

    8 · Health and environmental effects

    Toxicity
    No human health guideline anywhere read. Gallium salts are used therapeutically and diagnostically; no drinking water toxicology was read.
    Bioaccumulation
    Not biomagnified or biodiluted through the food web in Arctic pelagic systems, distributed proportionally in tissues (review). Medaka in a soil-water-fish system accumulated Ga dose dependently with growth inhibition and altered swimming at sublethal levels.
    Ecotoxicity
    96 h LC₅₀ for the freshwater shrimp Macrobrachium nipponense 2.77 mg/L Ga(III) (indium 6.89, cadmium 0.054, copper 0.031 mg/L in the same tests). In acidic aluminium rich paddy soil, gallium above 1 mmol/kg killed medaka largely by displacing aluminium into the water.

    Flags

    • The wafer fabrication process water gallium concentration is not given in the abstract read.
    • The Taiwan stream value is a single wastewater impacted site quoted in the review.
    • The equation is a stoichiometric statement of the species named in the review; no hydrolysis constant was read.

    Gaps

    • No river, groundwater or municipal wastewater concentration for gallium was read; the review covers marine and coastal water only.
    • No hydrolysis constants or solubility product were read; speciation is qualitative.
    • Arsenic removal from GaAs fab wastewater is the arsenic entry's story and is not repeated here.
    • No GCC discharge standard was read; no GCC row is written.
    • No standard analytical method text for gallium was read.

    Sources

    Less-Studied Technology-Critical Elements (Nb, Ta, Ga, In, Ge, Te) in the Marine Environment: Review on Their Concentrations in Water and Organisms, Frontiers in Marine Science 6 (2019) 532 (open access)
    Algae-based sorbents for removal of gallium from semiconductor manufacturing wastewater, Clean Technologies and Environmental Policy (2018) (abstract via OSTI 1580750)
    Recovery of gallium from wafer fabrication industry wastewaters by desferrioxamine B and E using reversed-phase chromatography approach, Water Research (2019), doi 10.1016/j.watres.2019.04.005 (abstract, PubMed 31035197)
    Comparative acute toxicity of gallium(III), antimony(III), indium(III), cadmium(II), and copper(II) on freshwater swamp shrimp (Macrobrachium nipponense), Biological Research 47 (2014) 13 (open access, PMC4107944)
    Differential effects of gallium and indium addition on metal bioavailability and toxicity in paddy soils: insights from a soil-water-fish exposure system, Environmental Pollution (2026) (abstract, PubMed 41643983)
    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), Annex 3 chemical summary tables: Table A3.2 chemicals for which guideline values have not been established and Table A3.3 guideline values for chemicals of health significance
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B, C and D (annexes read on legislation.gov.uk)
    US EPA, National Primary Drinking Water Regulations (table of MCLs; inorganic chemicals and radionuclides; beta particle and photon emitters 4 millirem per year)
    Commission Implementing Decision (EU) 2016/902 establishing BAT conclusions for common waste water and waste gas treatment/management systems in the chemical sector (CWW), BAT 12 Tables 1 to 3 (TOC, COD, TSS, TN, Ninorg, TP, AOX, Cr, Cu, Ni, Zn) (annex read on legislation.gov.uk)
    The Element Book, element entry and reference text for Ga (amphoteric metal, hydroxide, GaAs and GaN uses) (data/elements/Ga.json, data/reference/text/Ga.json)

    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.