Molybdenum
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.
| matrix | typical range | note |
|---|---|---|
| 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/Lhistoric | 1944 survey |
| drinking water | usually below 10; up to 200 near mining µg/Lregion-dependent; old surveys | US 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 2015 | detected in 40 percent of samples; 0.2 percent above 40 µg/LUS only | 25,377 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 |
| seawater | 0.01 mg/Lsingle abundance figure | estimated 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.
| condition | dominant species | note |
|---|---|---|
| oxic water, pH above 6 | MoO₄²⁻ | dominant; mobile; the form in supplies and cooling water |
| acid mine water, pH below 4 | HMoO₄⁻, H₂MoO₄, polymolybdates at high concentration | sorbs on ferric hydroxide; constants not printed in the sources read |
| sulfidic, reducing sediment | MoS₂ and thiomolybdates | the fixation sink named by the element entry; not covered by the water sources read |
| steel surface in molybdate treated cooling water | Mo(VI) adsorbed on the passive oxide film; calcium molybdate precipitate in hard alkaline water | the 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.
4 · Role in treatment
5 · Removal and control
- Efficiency
- not read for molybdenum
- Interferences
- selenate, arsenate, phosphate, silicate on the same sites; ineffective at neutral and alkaline pH
- Efficiency
- not read
- Interferences
- sulfate
- Efficiency
- not read
- Efficiency
- not read
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS | EPA 200.8 (mass 98); ISO 17294-2; Standard Methods 3125 | EPA 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/L | ruthenium-98 is isobaric with molybdenum-98 (EPA 200.8); irrelevant in water |
| ICP-OES | EN ISO 11885; Standard Methods 3120 | not read | adequate for mine water and cooling water at mg/L |
| colorimetry (thiocyanate) and GFAAS | Standard Methods 3111 D and 3113 for the metal; no molybdenum colorimetric method read | not 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.
| body | limit | note |
|---|---|---|
| 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 2020/2184 | not set | molybdenum is not an Annex I parameter |
| US EPA NPDWR | not 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) |
| body | limit | note |
|---|---|---|
| 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-dependent | molybdenum does not appear in Table 1 |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | 10 mg/L region-dependent; sewer discharge, not receiving water | Table A₄ maximum allowable concentration for trade effluent to the sewer network |
| sector | body | limit | note |
|---|---|---|---|
| textile | ZDHC 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, 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
Identity
- Name and symbol
- Molybdenum, Mo
- Atomic number
- 42 protons
- Position
- group 6 · period 5 · d-block · transition metal
- CAS number
- 7439-98-7
Atomic structure
- Atomic mass
- 95.95 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s¹ 4d⁵
[Kr] 5s¹⁴d⁵ - Electrons per shell
- 2, 8, 18, 13, 1
- Valence electrons
- 6 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 92Mo | 91.906 807(1) | 14.6 % |
| 94Mo | 93.905 084(1) | 9.1 % |
| 95Mo | 94.905 8374(8) | 15.8 % |
| 96Mo | 95.904 6748(8) | 16.6 % |
| 97Mo | 96.906 017(1) | 9.5 % |
| 98Mo | 97.905 404(1) | 24.2 % |
| 100Mo | 99.907 468(2) | 9.7 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 2,896 K (2,622.85 °C)
- Boiling point
- 4,912 K (4,638.85 °C)
- Density
- 10.2 g/cm3
- Appearance
- gray metallic
- Thermal conductivity
- 138 W/(m·K)
- Electrical resistivity
- 53.4 nΩ·m at 20 °C
- Electrical conductivity
- 18.73 MS/m
- Crystal structure
- body-centered cubic
- Molar heat capacity
- 24.06 J/(mol·K)
Chemical properties
- Oxidation states
- +6
- Electronegativity
- 2.16 (Pauling Scale)
- Ionisation energy
- 7.092 eV
1st 684.3, 2nd 1,560, 3rd 2,618 kJ/mol - Electron affinity
- 0.746 eV
- Atomic radius
- empirical 154, covalent 154, van der Waals 209 pm
- Ionic radius
- Mo³⁺ 69; Mo⁴⁺ 65; Mo⁵⁺ 61; Mo⁶⁺ 59 pm
- Reactivity
- A hard, refractory group 6 metal that shows no visible reaction with air or water at room temperature and has little tendency to form a simple cation in solution; it is attacked by the halogens, hydrogen peroxide and oxidising acids.
- with water
- Does not react with water at room temperature.
- with oxygen, air
- No visible reaction at room temperature; oxidises weakly from 300 C and in bulk above 600 C to the volatile trioxide: .
- with acids
- Resists non-oxidising acids; it is attacked by oxidising agents such as hydrogen peroxide and by nitric acid or aqua regia, which oxidise it towards molybdic acid.
- with halogens
- Attacked by the halogens; fluorine gives the stable hexafluoride: , and chlorine gives the pentachloride: .
- Typical compounds
- MoS₂ molybdenum disulfide molybdenite, the ore; layered solid lubricant
- MoO₃ molybdenum trioxide from roasting the ore; reduced by hydrogen to the metal
- H₂MoO₄ molybdic acid parent of the molybdates
- (NH₄)₆Mo₇O₂₄ ammonium heptamolybdate soluble molybdate for catalysts and pigments
- MoF₆ molybdenum hexafluoride stable, volatile hexafluoride
- MoCl₅ molybdenum pentachloride dark green dimeric solid
Occurrence, production and use
- Crustal abundance
- 1.2 milligrams per kilogram
- Oceanic abundance
- 1×10-2 milligrams per liter
- Occurrence and sources
Molybdenum is also recovered as a by-product of copper and tungsten mining operations. The metal is prepared from the powder made by the hydrogen reduction of purified molybdic trioxide or ammonium molybdate.
- molybdenite (MoS2) in porphyry molybdenum deposits Climax and Henderson (Colorado); primary mines exist only in China and the United States
- by-product molybdenite in porphyry copper deposits Chile, Peru, Mexico, Arizona, Montana, Nevada, Utah
- crustal and oceanic abundance about 0.8 ppm (BGS figure via RSC); 1.2 mg/kg crust and 0.01 mg/L seawater (PubChem)
- Extraction, production
- Oxidative roasting of molybdenite concentrate to molybdic oxide
RSC states the ore is roasted to molybdenum oxide; USGS names the product as molybdic oxide (MoO3, 57 percent Mo) made at three US roasting plants; sulfur dioxide as the sulfur product is implied by roasting in air, not named. Rhenium is recovered from the roaster gases
Reduction of molybdic oxide to metal powder, ferromolybdenum and chemicalsRSC states the oxide is then reduced to the metal but names no reductant; USGS lists ferromolybdenum, metal powder and chemicals (ammonium molybdates, pigments) as the intermediate products
- Uses
Molybdenum has a high melting point and is used to make the electrodes of electrically heated glass furnaces. Some electrical filaments are also made from molybdenum. The metal is used to make some missile and aircraft parts and is used in the nuclear power industry. Molybdenum is also used as a catalyst in the refining of petroleum.
Molybdenum is primarily used as an alloying agent in steel. When added to steel in concentrations between 0.25% and 8%, molybdenum forms ultra-high strength steels that can withstand pressures up to 300,000 pounds per square inch. Molybdenum also improves the strength of steel at high temperatures. When alloyed with nickel, molybdenum forms heat and corrosion resistant materials used in the chemical industry.
Molybdenum disulfide (MoS2), one of molybdenum's compounds, is used as a high temperature lubricant. Molybdenum trioxide (MoO3), another molybdenum compound, is used to adhere enamels to metals. Other molybdenum compounds include: molybdic acid (H2MoO4), molybdenum hexafluoride (MoF6) and molybdenum phosphide (MoP2).
It is used in certain nickel-based alloys, such as the "Hastelloys(R)" which are heat-resistant and corrosion-resistant to chemical solutions. Molybdenum oxidizes at elevated temperatures. The metal has found recent application as electrodes for electrically heated glass furnaces and forehearths. The metal is also used in nuclear energy applications and for missile and aircraft parts. Molybdenum is valuable as a catalyst in the refining of petroleum. It has found applications as a filament material in electronic and electrical applications. Molybdenum is an essential trace element in plant nutrition; some lands are barren for lack of this element in the soil. Molybdenum sulfide is useful as a lubricant, especially at high temperatures where oils would decompose. Almost all ultra-high strength steels with minimum yield points up to 300,000 psi (lb/in.2) contain molybdenum in amounts from 0.25 to 8%. Biologically, molybdenum as a trace element is necessary for nitrogen fixation and other metabolic processes.
- Steel and alloys: alloying agent in cast iron, alloy and stainless steel and superalloys for strength, hardness, wear and corrosion resistance; heating elements, drills, saw blades, engine parts; little substitution possible principal use per USGS; no percentage given
- Chemicals (catalysts, pigments, lubricants): hydrodesulfurisation and other petroleum catalysts; molybdenum orange pigment; ammonium and other molybdates; molybdenum disulfide lubricant additive; circuit-board inks, electrodes
- Mining: primary porphyry molybdenum mines and by-product recovery at porphyry copper mines; molybdate in extractive-waste water
- Energy: strong demand expected from power generation and infrastructure projects
- Agriculture: essential micronutrient in nitrogenase and about 50 other enzymes
- Safety, toxicity
- GHS classification, signal word Danger
- H225 Highly Flammable liquid and vapor Flammable liquids
- H228 Flammable solid Flammable solids
- H361 Suspected of damaging fertility or the unborn child Reproductive toxicity
- H315 Causes skin irritation Skin corrosion/irritation
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
Discovery and name
- Discovered by
- Carl Wilhelm Scheele
- Discovered
- 1778
- First isolated
- Peter Jacob Hjelm
- Named by
- not in sources
- Origin of the name
- from Greek Μόλυβδος, 'lead', since its ores were confused with lead ores
The metal is silvery white, very hard, but is softer and more ductile than tungsten. It has a high elastic modulus, and only tungsten and tantalum, of the more readily available metals, have higher melting points. It is a valuable alloying agent, as it contributes to the hardenability and toughness of quenched and tempered steels. It also improves the strength of steel at high temperatures.
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.