Aguato

    Tungsten

    group 6 · period 6 · d-block · transition metal

    minor Tungsten travels in water as an anion rather than as a metal cation. Dissolved as tungstate it carries a negative charge, so the surfaces and the chemistry that catch ordinary metals in neutral and alkaline water do not catch it, and it stays mobile where a cation would have sorbed or precipitated. Iron and manganese oxides do take tungstate up, but they take it up better as the pH falls, so that route out of solution weakens in exactly the alkaline water where tungsten is most mobile; calcium precipitates it as the mineral scheelite. No regulator anywhere sets a drinking water limit for it. It is a groundwater contaminant of record all the same, in Fallon, Nevada, and it reaches hundreds of milligrams per litre in tungsten tailings water, and lower but still elevated levels in wastewater from hard metal and semiconductor manufacture.

    Typical wastewaters

    • tungsten mining and tailings
      tungstate WO₄²⁻ in tailings groundwater, up to 922 mg/L at the Yxsjoberg skarn tailings in Sweden; precipitates with calcium as scheelite where calcium is high
    • hard metal and tungsten carbide manufacture
      tungstate at hundreds of mg/L in hard metal and tungsten chemical effluents
      ferric coagulation at acid pH is the industrial removal route
    • semiconductor fabrication
      tungstate remaining at 400 µg/L in treated effluent from a Taiwanese science park

    1 · Identity

    Symbol, number
    W, 74
    Oxidation states in water
    +6 as the tungstate anion WO₄²⁻, the form in neutral and alkaline water; at lower pH tungstate polymerises to isopolytungstates (ATSDR); the metal and lower oxides are insoluble solids.
    Note
    The element chapter covers the metal, scheelite and wolframite. In water tungsten is a molybdate like oxyanion, mobile in alkaline sodium bicarbonate water and sorbed in acid water.

    2 · Occurrence in water

    Natural sources
    Weathering of tungsten mineral deposits and geothermal waters; Fallon, Nevada, municipal supplies had a mean of 19.1 µg/L (range 0.25 to 27.2) and private wells 37.5 µg/L (0.25 to 337); Icelandic groundwaters 0.03 to 11.5 µg/L and surface waters 0.015 to 0.49 µg/L in areas of natural tungsten mineralisation (ATSDR 2005).
    Anthropogenic sources
    Tungsten mining and tailings (groundwater in the Yxsjoberg skarn tailings in Sweden reached 922 mg/L), hard metal and tungsten carbide manufacture, semiconductor fabrication (treated wastewater from a Taiwanese science park still at 400 µg/L), tungsten ammunition at shooting ranges (pore water 1 to 400 mg/L) (Yang 2022); rainwater near a Russian hard metal factory 0.00014 and 0.00076 µg/L in solid and soluble phases (ATSDR).
    matrixtypical rangenote
    drinking water, Fallon, Nevada0.25 to 27.2, mean 19.1 (municipal); 0.25 to 337, mean 37.5 (private wells) µg/Lone townthe leukaemia cluster investigation area
    groundwater and surface water, Iceland0.03 to 11.5 (groundwater); 0.015 to 0.49 (surface) µg/Lregion-dependentnatural mineralisation
    tailings groundwater, Swedenup to 922 mg/Lone siteYxsjoberg historical oxidic sulfidic skarn tailings
    industrial wastewater400 (treated semiconductor park effluent, µg/L); 1 to 400 mg/L (shooting range pore water) as statedsingle sites

    3 · Speciation

    Tungstate WO₄²⁻ is the dissolved species in neutral and alkaline water; sorption to iron and manganese minerals increases as pH falls and tungstate polymerises to isopolytungstates at lower pH (ATSDR). Calcium precipitates it as scheelite CaWO₄ when concentrations are high (above about 5 mmol/L in the hydrocalumite study, Yang 2022).

    conditiondominant speciesnote
    alkaline sodium bicarbonate or sodium chloride groundwater, pH above 8WO₄²⁻, little sorbedthe mobile case at Fallon
    acid to neutral water with iron and manganese oxidessorbed tungstate; isopolytungstatessorption coefficients rise with falling pH (ATSDR)
    calcium rich alkaline water at high tungstenCaWO₄ (s) scheeliteYang 2022
    Solubility
    Scheelite is the sparingly soluble calcium salt; sodium tungstate is freely soluble. No solubility product read.
    Hydrolysis
    Tungstic acid H₂WO₄ forms and polymerises below about pH 6; not quantified in the sources read.
    Complexation
    Polytungstates with itself; sorption complexes on Fe and Mn oxides.
    Precipitates
    CaWO₄ scheelite; FeWO₄ and MnWO₄ (wolframite) in the ore; tungstate co-precipitated on ferric hydroxide.
    CaX2++WOX4X2−→CaWOX4(s)\ce{Ca^2+ + WO4^2- -> CaWO4 (s)}
    scheelite precipitation, the removal mechanism when calcium is released from hydrocalumite; dominant above about 5 mmol/L tungsten (Yang 2022)

    4 · Role in treatment

    as a problem
    mobile oxyanion in alkaline groundwater
    tungstate sorbs poorly above pH 8 and passes conventional treatment
    Fallon private wells to 337 µg/L (ATSDR)
    hard metal and tungsten chemical effluents
    hundreds of mg/L tungstate
    removal by ferric coagulation at acid pH is the industrial route
    as a reagent
    none
    tungsten is not dosed in water treatment

    5 · Removal and control

    calcium precipitation as scheelite
    calcium from lime, hydrocalumite or calcium salts precipitates CaWO₄
    CaX2++WOX4X2−→CaWOX4(s)\ce{Ca^2+ + WO4^2- -> CaWO4 (s)}
    effective at high tungsten (above about 5 mmol/L); at lower concentrations sorption on the layered double hydroxide dominates (Yang 2022)
    Efficiency
    not recorded
    Interferences
    carbonate competes for calcium
    sorption and coagulation with iron
    tungstate sorbs on ferric hydroxide, most strongly at low pH
    sorption increases with decreasing pH (ATSDR)
    Efficiency
    not recorded
    Interferences
    phosphate, molybdate and silicate compete; alkaline pH desorbs

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MSISO 17294-2 (tungsten not confirmed on its list); tungsten is not an EPA 200.8 analytenot recordedmass 182 to 186; polymerised tungsten needs alkaline or fluoride digestion
    Sampling pitfalls
    Do not acidify strongly: tungstate polymerises and sorbs to walls and particles below pH 6; keep samples near neutral or slightly alkaline and filter first.

    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 no chemical fact sheet; radionuclide guidance levels, where they exist, are in chapter 9 and Annex 6
    EU DWD 2020/2184not set not an Annex I parameter
    US EPA NPDWRnot regulated no MCL
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL 1not set not a BAT 12 parameter
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set not a ZDHC parameter

    8 · Health and environmental effects

    Toxicity
    ATSDR (2005) found the human data too limited for health guidance; no drinking water value exists in any body read.
    Bioaccumulation
    not relevant
    Ecotoxicity
    Elevated tungsten may inhibit ammonification and nitrification in surface waters (ATSDR); no aquatic criterion exists.

    Read these with care

    • The Fallon figures are one town's investigation; the USGS Carson Desert study (0.27 to 742 µg/L) was not reachable and is not quoted.
    • The Swedish, Taiwanese and shooting range figures are quoted from the introduction of a materials paper (Yang 2022), which cites the primary studies.
    • Ferric coagulation efficiency for hard metal effluent was seen only in a search summary and is not quoted.

    What this chapter does not cover

    • No survey of tungsten in groundwater, surface water or seawater beyond the ATSDR compilation was read.
    • Hard metal effluent treatment (ferric coagulation at pH below 6, adsorbents, ion exchange) is not sourced.
    • Polytungstate speciation constants and scheelite solubility are not in the sources read.
    • No GCC document mentions tungsten.

    Notes

    1. Decision 2016/902

    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.