Molybdenum

    group 6 · period 5 · d-block · transition metal

    fullMolybdenum is the molybdate anion of oxic water: mobile, usually below 10 µg/L, found in 40 percent of US supplies under UCMR 3, carrying a WHO health based value of 70 µg/L and an EPA lifetime health advisory of 40 µg/L, and dosed deliberately as a molybdate corrosion inhibitor that leaves with cooling water blowdown.

    Typical wastewaters

    • mine drainage (molybdenum and copper porphyry mines) molybdate MoO₄²⁻ leached from molybdenite bearing waste and tailings; protonated HMoO₄⁻ and molybdic acid in acid mine water the US ore mining subpart limits Cd, Cu, Zn, Pb and As in molybdenum mine drainage but not molybdenum; finished water near US mines up to 200 µg/L (WHO)
    • cooling tower blowdown and closed loop drains (molybdate corrosion inhibitor) molybdate MoO₄²⁻ dosed as sodium molybdate, leaving with blowdown Abu Dhabi limits molybdenum to 10 mg/L in trade effluent to sewer
    • steel, hydrodesulfurisation catalyst and pigment plants molybdate MoO₄²⁻ in oxic effluent above pH 6 named by the element entry; no effluent figure read

    1 · Identity

    Symbol, number
    Mo, 42
    Oxidation states in water
    +6 as molybdate, MoO₄²⁻, the stable form in oxic water at neutral and alkaline pH, with HMoO₄⁻ and H₂MoO₄ (molybdic acid) in acid water and polymolybdates only at high concentration and low pH; +4 as molybdenite (MoS₂) and MoO₂ under reducing conditions, where molybdenum is fixed as the sulfide.
    Note
    The element entry covers molybdenite, roasting and the alloy uses; this chapter is the anion in supplies, mine water and cooling systems.

    2 · Occurrence in water

    Natural sources
    Oxidative weathering of molybdenite: molybdenum disulfide is sparingly soluble but readily oxidised to the more soluble molybdates, which are stable in water in the absence of a reducing agent (WHO). Molybdenum is the most abundant dissolved transition metal in seawater at about 0.01 mg/L.
    Anthropogenic sources
    Molybdenum mining and copper porphyry mines (drinking water up to 200 µg/L near mining operations, tap water up to 580 µg/L in Colorado, WHO); molybdate corrosion inhibitors in cooling and closed loop systems, which leave with blowdown; molybdenum in fertilisers and seed treatment; steel, catalyst (cobalt molybdenum hydrodesulfurisation) and pigment plants (element entry); sewage sludge from all of these.
    matrixtypical rangenote
    surface water, 15 major US river basins (1960s)2 to 1,500, mean 60 µg/L
    1967 survey; modern UK and Wisconsin studies give much lower values
    present in 32.7 percent of samples
    groundwater (US survey)undetectable to 270 µg/Lhistoric1944 survey
    drinking waterusually below 10; up to 200 near mining µg/Lregion-dependent; old surveysUS finished water median 1.4 µg/L (undetectable to 68); a 1967 survey found 29.9 percent of 380 samples positive with mean 85.9 and range 3 to 1,024 µg/L; intake from water rarely above 20 µg/day
    US public water systems (finished water), UCMR 3 2013 to 2015detected in 40 percent of samples; 0.2 percent above 40 µg/LUS only25,377 of 62,986 samples at or above the 1 µg/L reporting level; 151 samples and 40 of 4,922 systems above the 40 µg/L reference concentration
    seawater0.01 mg/Lsingle abundance figureestimated oceanic abundance, Jefferson Lab via PubChem

    3 · Speciation

    Above pH 6 molybdenum is the molybdate dianion, unhydrolysed, unsorbed by most surfaces and as mobile as sulfate; in acid water it protonates to HMoO₄⁻ and molybdic acid and sorbs on iron and aluminium oxides in the manner of the other oxyanions. It has no redox chemistry in oxic water; under sulfidic, reducing conditions it is removed as molybdenum sulfide, which is why molybdenum is enriched in black shales and why sulfide reduction is the only chemical sink. Molybdate is a non oxidising anodic corrosion inhibitor: it adsorbs on the passive film of steel as Mo(VI) and competes with chloride without being reduced.

    conditiondominant speciesnote
    oxic water, pH above 6MoO₄²⁻dominant; mobile; the form in supplies and cooling water
    acid mine water, pH below 4HMoO₄⁻, H₂MoO₄, polymolybdates at high concentrationsorbs on ferric hydroxide; constants not printed in the sources read
    sulfidic, reducing sedimentMoS₂ and thiomolybdatesthe fixation sink named by the element entry; not covered by the water sources read
    steel surface in molybdate treated cooling waterMo(VI) adsorbed on the passive oxide film; calcium molybdate precipitate in hard alkaline waterthe corrosion inhibitor mechanism (JES 2016)
    Solubility
    Molybdenum disulfide is sparingly soluble; sodium and ammonium molybdates are freely soluble; calcium molybdate precipitates on steel in calcium hydroxide solution (JES 2016). No solubility products are printed in the sources read.
    Hydrolysis
    Molybdic acid dissociates stepwise to HMoO₄⁻ and MoO₄²⁻ in acid water; the constants are not printed in the sources read, so none are quoted.
    Complexation
    Molybdate competes with selenate for zero valent iron surfaces (WHO selenium document citing Zhang 2005) and by extension for iron oxide sorption sites. No constants quoted.
    Precipitates
    Molybdenum sulfide under reducing conditions; calcium molybdate in hard alkaline water; ferric molybdate is not documented in the sources read.
    2MoSX2(s)+9OX2+6HX2O2MoOX4X2+4SOX4X2+12HX+\ce{2 MoS2 (s) + 9 O2 + 6 H2O -> 2 MoO4^2- + 4 SO4^2- + 12 H+}
    oxidative weathering of molybdenite to molybdate and sulfuric acid; WHO states the oxidation to soluble molybdates, the stoichiometry is written here
    HX2MoOX4HMoOX4X+HX+\ce{H2MoO4 <=> HMoO4^- + H+}
    the first dissociation of molybdic acid; molybdic acid and HMoO4^- appear only below about pH 4, in acid mine water and in acidified analytical solutions; the constants are not printed in the sources read
    HMoOX4XMoOX4X2+HX+\ce{HMoO4^- <=> MoO4^2- + H+}
    the second dissociation of molybdic acid; molybdate dominates above about pH 6; constant not printed in the sources read
    CaX2++MoOX4X2CaMoOX4(s)\ce{Ca^2+ + MoO4^2- -> CaMoO4 (s)}
    on carbon steel in pH 12.5 calcium hydroxide solution; the precipitate thins the passive film locally but reduces total oxidation of the steel (JES 2016 abstract)
    7MoOX4X2+8HX+MoX7OX24X6+4HX2O\ce{7 MoO4^2- + 8 H+ -> Mo7O24^6- + 4 H2O}
    condensation to heptamolybdate in acid at millimolar molybdenum; far above water treatment concentrations, but it is the species of a concentrated molybdate reagent and of acidified laboratory solutions; Baes and Mesmer, The Hydrolysis of Cations (1976), molybdenum chapter, from the chapter, not re-read
    MoOX4X2+4HX2SMoSX4X2+4HX2O\ce{MoO4^2- + 4 H2S -> MoS4^2- + 4 H2O}
    sulfidic water; the sum of the four stepwise sulfidations MoO(4-x)S(x)^2- that Erickson and Helz describe, each step about ten times slower than the one before, so the intermediate oxythiomolybdates persist in intermittently sulfidic water; tetrathiomolybdate is the stable dissolved species above about 11 µmol/L H2S at pH 8.1, and that switch is what fixes molybdenum in euxinic basins and in sulfidic sludge

    4 · Role in treatment

    as a problem
    molybdate is not removed by conventional treatment
    an unsorbed dianion at neutral pH, like sulfate
    the WHO documents read contain no treatment section; removal is by the oxyanion processes used for selenate and arsenate (low pH iron adsorption, anion exchange, reverse osmosis), none of which was read for molybdenum
    corrosion inhibitor residue
    molybdate dosed to cooling and closed systems leaves with blowdown and drains
    the CWW BREF names zinc from cooling water inhibitors as an effluent source; molybdate follows the same path and Abu Dhabi sets 10 mg/L for it in trade effluent to sewer
    mining district supplies
    molybdate leached from molybdenite bearing waste and tailings
    finished water up to 200 µg/L and tap water up to 580 µg/L reported near US mines (WHO); the US ore mining guideline for molybdenum mines limits cadmium, copper, zinc, lead and arsenic but not molybdenum
    taste
    ammonium molybdate
    slightly astringent above about 10 mg/L as molybdenum (WHO)
    as a reagent
    corrosion inhibitor: sodium molybdate
    non oxidising anodic inhibitor; molybdate adsorbs on the passive oxide film of steel as Mo(VI) and competes with chloride, so it needs dissolved oxygen or another oxidant to form the passive film; calcium molybdate precipitates over the surface in hard alkaline water
    CaX2++MoOX4X2CaMoOX4(s)\ce{Ca^2+ + MoO4^2- -> CaMoO4 (s)}
    14.6 mM molybdate prevented passivity breakdown of carbon steel in pH 12.5 solution with 564 mM chloride (JES 2016 abstract); a low toxicity replacement for chromate in cooling water treatment
    analytical reagent: ammonium molybdate
    forms the phosphomolybdate and silicomolybdate heteropoly acids that are reduced to molybdenum blue
    POX4X3+12MoOX4X2+27HX+HX3PMoX12OX40+12HX2O\ce{PO4^3- + 12 MoO4^2- + 27 H+ -> H3PMo12O40 + 12 H2O}
    the ascorbic acid orthophosphate method and the molybdosilicate method of Standard Methods 4500-P and 4500-SiO2 (cited by method number, not re-read); the equation is the 12:1 phosphomolybdic heteropoly acid that ascorbic acid then reduces to molybdenum blue, standard analytical chemistry rather than a stoichiometry printed by the method

    5 · Removal and control

    adsorption on iron oxides and zero valent iron at low pH
    protonated molybdate sorbs on ferric hydroxide and on the iron oxyhydroxide corrosion products of zero valent iron
    by analogy with selenate and arsenate; the WHO selenium document records molybdate competing with selenate on zero valent iron
    Efficiency
    not read for molybdenum
    Interferences
    selenate, arsenate, phosphate, silicate on the same sites; ineffective at neutral and alkaline pH
    anion exchange
    strong base resin exchanges the dianion
    not read for molybdenum; sulfate competition as for selenate
    Efficiency
    not read
    Interferences
    sulfate
    reverse osmosis
    rejection of the divalent anion
    not read for molybdenum
    Efficiency
    not read
    sulfide precipitation and biological sulfate reduction
    under strongly reducing sulfidic conditions molybdenum is fixed as the sulfide
    MoOX4X2+4HX2SMoSX4X2+4HX2O\ce{MoO4^2- + 4 H2S -> MoS4^2- + 4 H2O}
    the geochemical sink of the element entry; no engineered example read; the reaction shown is the sum of the stepwise sulfidation of Erickson and Helz, which needs H2S above about 11 µmol/L at pH 8.1 before tetrathiomolybdate is the stable species
    Efficiency
    not read

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MSEPA 200.8 (mass 98); ISO 17294-2; Standard Methods 3125EPA 200.8 instrument detection limit 0.1 µg/L scanning and 0.005 µg/L selected ion monitoring; UCMR 3 minimum reporting level 1 µg/Lruthenium-98 is isobaric with molybdenum-98 (EPA 200.8); irrelevant in water
    ICP-OESEN ISO 11885; Standard Methods 3120not readadequate for mine water and cooling water at mg/L
    colorimetry (thiocyanate) and GFAASStandard Methods 3111 D and 3113 for the metal; no molybdenum colorimetric method readnot read
    Sampling pitfalls
    Molybdate is stable and needs only acidification for total molybdenum; filter 0.45 µm for dissolved. In cooling water samples the inhibitor dose (mg/L) dwarfs natural levels (µg/L), so dilution blanks matter.

    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 occurs at concentrations well below health concern; a health based value of 0.07 mg/L (70 µg/L) is given for guidance, from a human NOAEL of 0.2 mg/L in a 2 year drinking water study with an uncertainty factor of 3; assessment 1993, revised 2011
    EU DWD 2020/2184not set molybdenum is not an Annex I parameter
    US EPA NPDWRnot regulated monitored under UCMR 3 with a 1 µg/L reporting level and a 40 µg/L reference concentration; lifetime health advisory 0.04 mg/L, one day and ten day 0.08 mg/L, RfD 0.005 mg/kg per day, DWEL 0.2 mg/L (2018 table)
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set molybdenum is not a BAT 12 parameter
    US EPA 40 CFR 440.102(e) to (h), molybdenum ore mines and mills (BPT)not set the subpart limits TSS, cadmium 0.10 and 0.05 mg/L, copper, zinc 1.0 and 0.5 mg/L, lead, arsenic and pH in molybdenum mine drainage, not molybdenum itself
    Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD)not set region-dependentmolybdenum does not appear in Table 1
    Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer10 mg/L
    region-dependent; sewer discharge, not receiving water
    Table A₄ maximum allowable concentration for trade effluent to the sewer network
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set molybdenum is not a ZDHC parameter

    8 · Health and environmental effects

    Toxicity
    Essential, estimated daily requirement 0.1 to 0.3 mg for adults; intakes 100 to 240 µg/day in the US; the human NOAEL of 0.2 mg/L in drinking water over 2 years underlies the WHO health based value, with concerns about that study's quality; EPA RfD 0.005 mg/kg per day (WHO, EPA).
    Bioaccumulation
    Not addressed in the sources read.
    Ecotoxicity
    Not addressed in the sources read; no US EPA aquatic criterion for molybdenum appears in the table.

    Flags

    • The natural water concentrations are 1940s to 1960s US surveys; WHO says more modern studies show much lower levels.
    • The seawater figure (0.01 mg/L) is a single abundance figure from Jefferson Lab via PubChem.
    • The molybdenite oxidation and calcium molybdate equations are mass balances written here; WHO and the JES abstract describe them in words.
    • No removal process was read for molybdenum; the removal rows are analogies to selenate and arsenate and say so.
    • The brief's former WHO guideline value of 70 µg/L is consistent with the 2011 revision noted in the fact sheet, but the WHO history document was not read.
    • The corrosion inhibitor mechanism rests on one 2016 abstract in pH 12.5 calcium hydroxide, not on cooling water conditions.
    • Abu Dhabi lists molybdenum only for sewer discharge (10 mg/L); other GCC states not read.

    Gaps

    • No treatment performance data for molybdenum were read; WHO's documents have no treatment section.
    • Dissociation constants of molybdic acid, molybdate sorption constants and molybdenum sulfide solubility are not printed in the sources read.
    • No industrial or municipal wastewater concentrations were read; the mine water figures are drinking water near mines.
    • No ecotoxicity data or aquatic criterion was read.
    • Molybdenum in sewage sludge land application limits and in EU or GCC discharge standards beyond Abu Dhabi were not read.
    • The Standard Methods phosphate and silica methods are cited by number only.
    • The thiomolybdate stoichiometry is the sum of the four stepwise sulfidations reported in the Erickson and Helz abstract; the full paper was not read and no stability constants are quoted.
    • The heptamolybdate condensation is cited to Baes and Mesmer by chapter, from the chapter, not re-read.
    • The 12:1 phosphomolybdate stoichiometry is standard analytical chemistry; Standard Methods 4500-P was cited by number and not re-read.

    Sources

    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Molybdenum (pp. 433 to 434)
    WHO, Molybdenum in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/SDE/WSH/03.04/11/Rev/1 (2011), sections 1, 2 and 7
    WHO, Selenium in Drinking-water, background document (2011), section 6.2 (zero valent iron, molybdate competition)
    US EPA, Third Unregulated Contaminant Monitoring Rule (UCMR 3), Table 1 (contaminants, minimum reporting levels and methods)
    US EPA, The Third Unregulated Contaminant Monitoring Rule (UCMR 3): Data Summary, January 2017, EPA 815-S-17-001, Table 3 (reference concentrations and occurrence)
    US EPA, 2018 Edition of the Drinking Water Standards and Health Advisories Tables, EPA 822-F-18-001 (March 2018)
    US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, Table 1 instrument detection limits
    ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
    Standard Methods (online edition), 3125 Metals by Inductively Coupled Plasma-Mass Spectrometry
    Standard Methods for the Examination of Water and Wastewater, 4500-P Phosphorus (ascorbic acid method) and 4500-SiO2 Silica (molybdosilicate method); cited by number, url not looked up
    Tan, Y. T., Wijesinghe, S. L. and Blackwood, D. J., Effect of Molybdate on the Passivation of Carbon Steel in Alkaline Solutions under Open-Circuit Conditions, Journal of The Electrochemical Society 163(10):C649 (2016), doi 10.1149/2.0651610jes (abstract read)
    40 CFR 440.102, Effluent limitations representing BPT, ore mining and dressing, subpart J (copper, lead, zinc, gold, silver and molybdenum ores)
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III Table 1
    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 4 and BAT 12 Table 3 with footnotes 24 to 29
    Abu Dhabi Specification ADS 23/2017, Environmental Specifications for Land-Based Liquid Discharges to the Marine Environment (Environment Agency Abu Dhabi), Table 1
    Abu Dhabi Department of Energy, Trade Effluent Control Regulations 2022 (DoE/PD/R01/005, effective 1 January 2022), Appendix Table A4
    ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 1M (organotins), Table 2 (heavy metals) and Tables 4A and 4B (sludge)
    The Element Book, own entry for molybdenum (data/elements/Mo.json and data/reference/text/Mo.json)
    PubChem element summary for molybdenum; estimated oceanic abundance 1 x 10^-2 mg/L from Jefferson Lab
    Baes, C. F. and Mesmer, R. E., The Hydrolysis of Cations (Wiley, 1976), chapter on molybdenum (molybdate protonation and polymolybdates)
    Erickson, B. E. and Helz, G. R., Molybdenum(VI) speciation in sulfidic waters: stability and lability of thiomolybdates, Geochimica et Cosmochimica Acta 64(7), 1149 to 1158 (2000); abstract and the stepwise sulfidation scheme

    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.