Indium

    group 13 · period 5 · p-block · post-transition metal

    minorIndium has no drinking water or effluent limit anywhere read and no treatment role; it is one of the least abundant dissolved metals (sub-picomolar in the Pacific), hydrolysed and particle bound, with a coastal anthropogenic signal near Japanese electronics manufacture and a medical one as the indium-111 DTPA complex.

    Typical wastewaters

    • flat panel display and semiconductor manufacture (indium tin oxide, indium phosphide) hydrolysed In(III), In(OH)₃^0 and In(OH)₄⁻, particle bound; the industrial signal is 2 to 300 pmol/L in Japanese coastal water the review quotes the receiving coastal water, not the effluent
    • hospital effluent and sewage (radiopharmaceuticals) indium-111 as the In(DTPA)²⁻ chelate, which keeps it in solution the review's interpretation of evidence, not a measurement

    1 · Identity

    Symbol, number
    In, 49
    Oxidation states in water
    +3 only; hydrolysed to In(OH)₃^0 and In(OH)₄⁻ (the review's thermodynamic statement for Ga and In); anthropogenic In(DTPA)²⁻ from medical use
    Note
    The element entry covers the metal, In₂O₃ and ITO. In water indium is a strongly hydrolysed trivalent cation with even lower solubility than gallium.

    2 · Occurrence in water

    Natural sources
    Trace substitution in sphalerite and other sulfides (element entry); weathering releases very little and hydrolysis keeps it on particles.
    Anthropogenic sources
    Indium tin oxide for flat panel displays (more than half of use), indium phosphide and semiconductor manufacture, ITO sputtering scrap recycling; medical indium-111 DTPA; Japanese coastal water carries the industrial signal.
    matrixtypical rangenote
    seawater0.047 to 4.7 pmol/kgWestern North Pacific 0.047 to 0.101; North Atlantic 0.59 to 1.62; Mediterranean 3.2 to 4.7
    estuaries0.03 to 14.7 pmol/LChao Phraya (Thailand) 0.03 to 0.42; Japanese estuaries 1.0 to 14.7
    coastal water, Japan2 to 300 pmol/Llarge scatteraverage 25 plus or minus 55; the anthropogenic end of the range

    3 · Speciation

    Dissolved indium is the neutral trihydroxide with some In(OH)₄⁻; the free In³⁺ ion exists only in acid solution. Anthropogenic indium from medical imaging travels as the In(DTPA)²⁻ chelate, which keeps it in solution.

    conditiondominant speciesnote
    seawater and neutral fresh waterIn(OH)₃^0, In(OH)₄⁻thermodynamic calculation quoted in the review
    sewage and receiving water below hospitalsIn(DTPA)²⁻evidence cited in the review for medical indium
    Solubility
    Very low, controlled by In(OH)₃; no solubility product read.
    Hydrolysis
    Complete in neutral water (qualitative).
    Complexation
    Strong aminopolycarboxylate (DTPA) chelation from medical use; no natural ligand data read.
    Precipitates
    In(OH)₃ on neutralisation of acid indium solutions.
    InX3++3HX2OIn(OH)X3+3HX+\ce{In^3+ + 3 H2O -> In(OH)3 + 3 H+}
    hydrolysis to the neutral trihydroxide, the dominant species in the review; a stoichiometric statement, no constant read

    4 · Role in treatment

    Not relevant or not given for this element.

    5 · Removal and control

    Not relevant or not given for this element.

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after preconcentrationresearch methods behind the review's ocean data; no standard method readsub-pmol/kg in the open ocean dataonly one certified reference value exists for indium in a marine organism (24 plus or minus 5 ng/g)
    Sampling pitfalls
    Sub-picomolar seawater levels demand trace-metal clean sampling; indium contamination from tin solder and ITO coated laboratory glass is a plausible blank (writer's caution, not sourced).

    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
    WHO GDWQ Table A₆.1 (radionuclides)1000 Bq/Lindium-111, the medical isotope; guidance level for drinking water at 0.1 mSv per year
    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 for stable indium in water anywhere read; no ingestion toxicology was read this session.
    Bioaccumulation
    No published concentration data for marine organisms other than one reference material value (review). Medaka accumulated In dose dependently with sublethal growth and behaviour effects.
    Ecotoxicity
    96 h LC₅₀ for the freshwater shrimp Macrobrachium nipponense 6.89 mg/L In(III), the least toxic of the five semiconductor metals tested (Ga 2.77, Sb 1.96, Cd 0.054, Cu 0.031 mg/L). In acidic paddy soil above 4 mmol/kg In, medaka died mainly from released aluminium.

    Flags

    • The In(DTPA)²⁻ statement is the review's interpretation of evidence, not a measurement quoted here.
    • Japanese coastal average 25 plus or minus 55 pmol/L has a standard deviation larger than the mean; treat as a range.

    Gaps

    • No river, groundwater, municipal or industrial wastewater concentration was read.
    • No hydrolysis constants or solubility product were read.
    • No removal process for indium from water was read; ITO etching effluent treatment was not found in a readable source.
    • No GCC discharge standard 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)
    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
    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), Annex 6 Table A6.1 guidance levels for radionuclides in drinking-water (individual dose criterion 0.1 mSv per year, levels rounded to the nearest order of magnitude)
    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 In (metal, In2O3 and ITO, sphalerite source) (data/elements/In.json, data/reference/text/In.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.