Germanium

    group 14 · period 4 · p-block · metalloid

    minorGermanium is not regulated in drinking water or effluent anywhere read and has no treatment role; in water it is a trace silicon analogue, germanic acid at picomoles per kilogram with a biological methylgermanium pool that makes up most of the dissolved total in the sea, and its health story is renal failure from ingested germanium supplements, not from water.

    Typical wastewaters

    • optical fibre industry wastewater low concentration germanium in fibre optics industry wastewater, complexed by desferrioxamine B at low pH over 80 percent recovered at 84.5 percent purity from real fibre optics wastewater
    • lead smelter slag washing wastewater germanium with Zn and Fe(II) in acidic slag washing water; precipitated selectively with tannic acid at pH 3 to 6 96.6 percent Ge precipitation in 2 minutes; treated water reused
    • solar panel manufacturing wastewater germanium ion together with silicate ion; adsorbed as a catechol anion complex on a quaternary ammonium membrane at pH 3

    1 · Identity

    Symbol, number
    Ge, 32
    Oxidation states in water
    +4 as germanic acid Ge(OH)₄ and its anion, plus the methylated Ge(IV) species monomethylgermanium and dimethylgermanium
    Note
    The element entry covers the metalloid and GeO₂. In water germanium follows silicon: germanic acid is taken up with silicic acid and cycles with biogenic silica in the ocean (the review's statement; the Ge/Si ratio literature was not read).

    2 · Occurrence in water

    Natural sources
    Weathering of silicate rock releases germanic acid with silicic acid; siliceous organisms take it up and it cycles with silica in the ocean. Methylgermanium species are a separate, unreactive dissolved pool.
    Anthropogenic sources
    Fibre optic, infrared optic, semiconductor and solar manufacture (element entry); coal combustion residues (germanium rich lignites in the element entry). No effluent concentration was read.
    matrixtypical rangenote
    seawater, inorganic Gebelow 4 to 117 pmol/kgNorth Atlantic below 4 to 37; Western Indian 2 to 99; South Pacific 5 to 97; North West Pacific 5 to 117; nutrient type profile rising with depth like silica
    seawater, methylgermaniumabout 330 (monomethyl) and 120 (dimethyl) pmol/Lglobal averages; the methylated species make up more than 70 percent of total dissolved germanium

    3 · Speciation

    Inorganic germanium is the neutral tetrahydroxide Ge(OH)₄ (germanic acid) in neutral water, deprotonating to the anion in alkaline water; the methylated species CH₃Ge(OH)₃ and (CH₃)₂Ge(OH)₂ are stable, unreactive and dominate the total in seawater. Ge(IV) is not reduced in natural water.

    conditiondominant speciesnote
    fresh and seawater, pH 6 to 9Ge(OH)₄^0 (germanic acid), a small share of GeO(OH)₃⁻the silicon analogue; taken up by diatoms with silicic acid
    seawater, all depthsmonomethylgermanium and dimethylgermaniumbiological origin, conservative, more than 70 percent of total dissolved Ge
    Solubility
    GeO₂ dissolves to germanic acid; no solubility figure was read.
    Hydrolysis
    Germanic acid is a weak acid like silicic acid; the first deprotonation matters only in alkaline water (no pKa read this session).
    Complexation
    No complexation data read; the methyl species are covalent, not complexes.
    Precipitates
    None in natural water; germanium leaves solution inside biogenic opal and with iron oxides.
    Ge(OH)X4GeO(OH)X3X+HX+\ce{Ge(OH)4 -> GeO(OH)3^- + H+}
    first deprotonation of germanic acid, alkaline water; 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
    hydride generation, cryotrapping, ICP-MS/MS speciationresearch method (Talanta 2021)0.015 ng/L inorganic Ge, 0.005 ng/L monomethylgermanium, 0.003 ng/L dimethylgermanium1 mL of water without pretreatment; external calibration; validated on river water (SLRS) and seawater (CASS, NASS) reference materials
    ICP-MSno standard method read for germaniumnot readgermanium is not a listed analyte in the water methods read this session
    Sampling pitfalls
    Blank control decides the result at ng/L: the speciation method reports a procedure to minimise inorganic Ge blanks from reagents and water. Methylgermanium does not demethylate during hydride generation in the Tris-cysteine medium, so speciation survives the analysis.

    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 drinking water guideline. Germanium is not an essential element and its acute toxicity is low, but at least 31 human cases linked prolonged intake of germanium supplements (dioxide, carboxyethyl germanium sesquioxide, lactate citrate; total doses 15 to over 300 g over 2 to 36 months) with renal failure and death, with kidney tubular degeneration, anaemia, muscle weakness and peripheral neuropathy; recovery of renal function was slow and incomplete. A lifetime drinking water study in animals at 5 ppm germanium gave tissue accumulation and impaired kidney and liver function.
    Bioaccumulation
    Fish and seafood 1 to 5 ng/g (mean 2 ng/g); mussel reference material 68 ng/g (review).
    Ecotoxicity
    No aquatic ecotoxicity value was read.

    Flags

    • The 5 ppm drinking water animal study is quoted from the 1997 hazard assessment abstract; species and duration beyond lifetime are not given there.
    • Fresh water concentrations (0.011 to 0.022 µg/L for tap, river and seawater) appeared only in a search summary and are not written.
    • The silicon analogy (uptake into biogenic opal, river and ocean Ge/Si ratios) rests on the Frontiers review and on search summaries of the 1985 and 1988 germanium papers, which were not reachable; no ratio is written.

    Gaps

    • No river, groundwater, geothermal, municipal or industrial wastewater concentration was read (the 1988 review of germanium biogeochemistry and the geothermal papers were not reachable).
    • No pKa of germanic acid or solubility of GeO₂ was read.
    • No removal process for germanium from water was read; none is practised.
    • No GCC discharge standard was read.
    • No aquatic ecotoxicity data were 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)
    Speciation of germanium in environmental water reference materials by hydride generation and cryotrapping in combination with ICP-MS/MS, Talanta (2021), doi 10.1016/j.talanta.2020.121972 (abstract, PubMed 33592806)
    Hazard assessment of germanium supplements, Regulatory Toxicology and Pharmacology (1997), doi 10.1006/rtph.1997.1098 (abstract, PubMed 9237323)
    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 Ge (metalloid chemistry, GeO2, GeCl4, sources in zinc residues and lignite) (data/elements/Ge.json, data/reference/text/Ge.json)
    Ghosh A., Hintersatz C., Kretzschmar J., Foerstendorf H., Tsushima S., Jain R., Recovery of germanium from optical fiber industry wastewater using desferroxamine B, Journal of Hazardous Materials 494, 138444 (2025), doi 10.1016/j.jhazmat.2025.138444 (abstract)
    Liu K., Hong Y., Dai J., Di H. and others, Selective extraction of germanium from lead slag washing wastewater by tannic acid coordination and precipitation method, Arabian Journal of Chemistry 18 (2025), doi 10.25259/ajc_288_2024 (abstract)
    Kawakita H., Morisada S., Ohto K., Germanium recovery using ion-exchange membrane and solvent extraction, Journal of Ion Exchange 25(4), 88 to 92 (2014), doi 10.5182/jaie.25.88 (abstract)

    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.