Zirconium

    group 4 · period 5 · d-block · transition metal

    fullZirconium is unregulated in drinking water and effluent everywhere read and is almost insoluble in natural water, but it earns its water chapter as a reagent: zirconium oxychloride is a coagulant that outperforms alum on natural organic matter, and hydrous zirconium oxide is among the strongest adsorbents known for fluoride and phosphate.

    Typical wastewaters

    • water treatment residuals where zirconium coagulants or adsorbents are used hydrous zirconia in the floc and in spent fluoride and phosphate adsorbents; dissolved zirconium negligible
    • zircon milling, zirconia ceramic works and nuclear fuel cladding manufacture particulate zircon and hydrous zirconia; Zr(IV) is fully hydrolysed and insoluble at any natural pH named by the element entry; no effluent figure read

    1 · Identity

    Symbol, number
    Zr, 40
    Oxidation states in water
    +4 only; hydrolysed to Zr(OH)₄^0 and Zr(OH)₅⁻ (the seawater species) and polymerised to hydrous zirconia
    Note
    The element entry covers the corrosion resistant metal, zircon and ZrO₂. In water zirconium is a hard, fully hydrolysed tetravalent cation whose hydroxide surface binds fluoride and oxyanions.

    2 · Occurrence in water

    Natural sources
    Weathering of zircon, which is nearly insoluble, so dissolved zirconium is at picomolar to nanomolar levels; Japanese lake and spring waters 0.29 to 2.8 µg/L; seawater about 160 pmol/kg, depleted at the surface and enriched with depth, residence time 5600 years.
    Anthropogenic sources
    Zircon milling and zirconia ceramic works, nuclear fuel cladding manufacture (element entry); coagulant and adsorbent residuals where zirconium reagents are used. Zirconium-95 is a fission product.
    matrixtypical rangenote
    seawaterabout 160 pmol/kgaverage; surface depleted, deep enriched
    lake and spring water, Japan0.29 to 2.8 µg/Lold data, one regionNikko and Shiobara districts, lake and hot and cold springs, 1978

    3 · Speciation

    Fully hydrolysed Zr(IV): neutral Zr(OH)₄ and the anion Zr(OH)₅⁻ in seawater; at higher concentration the hydroxo species polymerise to hydrous zirconia, which is the working surface of every zirconium coagulant and adsorbent. Fluoride complexes zirconium strongly (the element entry notes that fluoride is what dissolves the metal), which is the chemistry behind defluoridation.

    conditiondominant speciesnote
    seawaterZr(OH)₅⁻MBARI periodic table statement
    coagulant dosing, pH 5 to 8hydrous zirconia flocs from hydrolysis of ZrOCl₂charge neutralisation and adsorption of NOM
    fluoride or phosphate water on a Zr adsorbent, pH 5 to 9surface Zr-F and Zr-O-P inner sphere complexesligand exchange of surface hydroxyl
    Solubility
    Very low; controlled by hydrous zirconia and zircon.
    Hydrolysis
    Complete at natural pH; polymerisation above micromolar concentration.
    Complexation
    Fluoride strongly; phosphate on surfaces; carbonate not read.
    Precipitates
    Hydrous ZrO₂, Zr(OH)₄, zirconium phosphate.
    ZrOClX2+3HX2OZr(OH)X4(s)+2HCl\ce{ZrOCl2 + 3 H2O -> Zr(OH)4 (s) + 2 HCl}
    hydrolysis of zirconium oxychloride on dosing as a coagulant; the acid consumes alkalinity as with alum and ferric
    Zr(OH)X4(s)+OHXZr(OH)X5X\ce{Zr(OH)4 (s) + OH- -> Zr(OH)5^-}
    the last hydrolysis step, which is why MBARI gives Zr(OH)5^- as the seawater species: at pH 8.1 the neutral hydroxide takes a fifth hydroxide and the little zirconium that is dissolved travels as an anion; no constant was read
    Zr(OH)X4(s)+FXZr(OH)X3F(s)+OHX\ce{Zr(OH)4 (s) + F^- -> Zr(OH)3F (s) + OH-}
    ligand exchange of surface hydroxyl by fluoride on hydrous zirconia, releasing hydroxide; the reason capacity falls at high pH and regeneration uses sodium hydroxide
    Zr(OH)X4(s)+HX2POX4XZr(OH)X3(HX2POX4)(s)+OHX\ce{Zr(OH)4 (s) + H2PO4^- -> Zr(OH)3(H2PO4) (s) + OH-}
    inner sphere phosphate complexation on a Zr surface, favoured at low pH (221.72 mg/g at pH 3 on Zr/Fe hydrogel beads)

    4 · Role in treatment

    as a reagent
    coagulant (zirconium oxychloride)
    hydrolysis to hydrous zirconia flocs; charge neutralisation and adsorption of natural organic matter and dye
    ZrOClX2+2HCOX3X+HX2OZr(OH)X4(s)+2COX2+2ClX\ce{ZrOCl2 + 2 HCO3^- + H2O -> Zr(OH)4 (s) + 2 CO2 + 2 Cl^-}
    against aluminium sulfate on NOM enriched chlorinated water, zirconium oxychloride surpassed alum in reducing NOM (absorbance slope index) and phenol by 57.98 percent and 49.02 percent respectively (the abstract's wording), cut chlorine demand within 30 minutes and lowered the modelled trihalomethane cancer risk about 2.3 fold; on an anthraquinone reactive dye 92.58 percent dye and 85.33 percent COD removal at 156.67 mg/L coagulant for 105.67 mg/L dye at pH 2, with no toxicity of the coagulant found up to 500 mg/L; written against alkalinity as the coagulant chapters write alum and ferric: two moles of bicarbonate per mole of zirconium, that is 0.56 mg/L of alkalinity as CaCO3 per mg/L of anhydrous ZrOCl2 (0.31 per mg/L of the octahydrate that is sold) or 1.10 mg/L as CaCO3 per mg/L of zirconium; the study prints doses, not the stoichiometry
    coagulant in coagulation-filtration for virus removal
    as for aluminium: enmeshment of virus in floc
    aluminium and zirconium coagulants each reduced virus by 99.9 percent in colour rich water and by 90 percent in water with less colour; chitosan reached 99.9 to 99.99 percent
    adsorbent for fluoride (hydrous zirconium oxide, zirconium-aluminium hybrids)
    electrostatic attraction, surface complexation and anion exchange at surface hydroxyls
    Zr(OH)X4(s)+FXZr(OH)X3F(s)+OHX\ce{Zr(OH)4 (s) + F^- -> Zr(OH)3F (s) + OH-}
    granular Zr-Al hybrid: Langmuir maximum 65.07 mg/g at 25 C, equilibrium within 12 h, removal held over pH 5 to 9, phosphate competes; 808 bed volumes of 5 mg/L fluoride water treated in a column; regenerated four times with sodium hydroxide keeping about 80 percent capacity; the uptake is the ligand exchange of one surface hydroxyl for fluoride, which releases hydroxide and so runs against itself as pH rises, and which sodium hydroxide reverses on regeneration
    adsorbent for phosphate (zirconium and zirconium-iron composites)
    electrostatic attraction, hydrogen bonding and inner sphere complexation; chemisorption dominated
    Zr(OH)X4(s)+HX2POX4XZr(OH)X3(HX2POX4)(s)+OHX\ce{Zr(OH)4 (s) + H2PO4^- -> Zr(OH)3(H2PO4) (s) + OH-}
    Zr/Fe chitosan alginate beads: 221.72 mg/g maximum at pH 3, Freundlich isotherm, real wastewater 19.02 to 0.985 mg/L phosphate, 73 percent efficiency after six cycles; the same ligand exchange with dihydrogen phosphate, the species that dominates at the pH 3 optimum, which is why phosphate and fluoride compete for the identical surface site

    5 · Removal and control

    not needed
    dissolved zirconium is negligible; coagulant residual leaves with the floc as hydrous zirconia
    Efficiency
    not quoted

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after preconcentrationMBARI statement; no standard method readpmol/kg in seawater
    Arsenazo III spectrophotometry after evaporation, acid digestion and TTA extraction with a zirconium-95 yield tracer1978 research methodsub-µg/L from 1 Lhistorical, shows how hard the element is to dissolve and keep in solution
    Sampling pitfalls
    Zirconium sorbs to container walls and colloids; acidify with fluoride-free acid only if the method tolerates it, and expect most of the total to be particulate. Fluoride in the sample keeps it dissolved and shifts speciation.

    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)100 Bq/Lzirconium-95; guidance level 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 anywhere read; the dye coagulation study found no toxicity of zirconium oxychloride up to 500 mg/L in its assay.
    Bioaccumulation
    Not read.
    Ecotoxicity
    Not read.

    Flags

    • The coagulant performance figures are single laboratory studies on one water each; the NOM comparison is against aluminium sulfate only.
    • Adsorbent capacities are Langmuir maxima from batch tests on synthetic solutions except where a real wastewater is named.
    • The seawater speciation and residence time come from a periodic table web page without named author.
    • Whether the 57.98 and 49.02 percent NOM and phenol figures are absolute removals or the margin over aluminium sulfate is ambiguous in the abstract; the wording is kept as given.

    Gaps

    • No river or groundwater survey beyond the 1978 Japanese springs was read; world river zirconium was not reachable.
    • No hydrolysis constants or solubility product were read.
    • The zirconium fluoride adsorbent review (hydrous zirconium oxide up to 68 mg/g at pH 7 in a search summary) was not reachable, so that figure is not written.
    • No full scale coagulant dose or alkalinity consumption for zirconium oxychloride was read.
    • No ecotoxicity data were read.
    • No GCC discharge standard was read.

    Sources

    MBARI periodic table of elements in the ocean, zirconium page (oxidation state, Zr(OH)5^- speciation, 160 pmol/kg average, 5600 year residence time, ICP-MS after preconcentration)
    Determination of zirconium in natural water by spectrophotometry following the concentration step with yield tracer, Radioisotopes 27 (1978), doi 10.3769/radioisotopes.27.12_705 (abstract, PubMed 746171)
    Understanding the coagulant activity of zirconium oxychloride to control THMs formation using response surface methodology, Ecotoxicology and Environmental Safety (2018), doi 10.1016/j.ecoenv.2018.04.036 (abstract, PubMed 29730406); and Decolorization of reactive dye by zirconium oxychloride as a novel coagulant, Water Science and Technology (2018), doi 10.2166/wst.2018.307 (abstract, PubMed 30101773)
    Coagulant residues' influence on virus enumeration as shown in a study on virus removal using aluminium, zirconium and chitosan, Journal of Water and Health (2018), doi 10.2166/wh.2018.028 (abstract, PubMed 30067241)
    Adsorptive removal of fluoride from water by granular zirconium-aluminum hybrid adsorbent: performance and mechanisms, Environmental Science and Pollution Research (2018), doi 10.1007/s11356-018-1711-1 (abstract, PubMed 29564704)
    Removal of phosphate from wastewater using zirconium/iron embedded chitosan/alginate hydrogel beads, International Journal of Biological Macromolecules (2024), doi 10.1016/j.ijbiomac.2024.136431 (abstract, PubMed 39389514)
    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 Zr (metal, zircon, ZrO2, fluoride attack, nuclear cladding) (data/elements/Zr.json, data/reference/text/Zr.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.