Hafnium

    group 4 · period 6 · d-block · transition metal

    minorHafnium has no drinking water guideline, no effluent limit and no treatment role: Hf(IV) hydrolyses completely at natural pH, the hydroxide and oxide are insoluble and the dissolved element sits at femtomolar to picomolar levels in the sea; where it appears in an effluent it is a particulate that leaves with the solids in any generic metal removal step.

    Typical wastewaters

    • primary zirconium and hafnium production (zircon sand chlorination and MIBK thiocyanate separation plants) hafnium in the filtrate left after the separated hafnium is precipitated as hydroxide, and in the MIBK iron extraction steam stripper bottoms; the hafnium filtrate is reused for its zirconium content or sent to evaporation ponds, so 40 CFR 421.333(h) gives it a zero allowance for chromium, cyanide, lead and nickel (a no discharge stream) the streams that are discharged (sand drying and chlorination scrubber waters, zirconium filtrate, MIBK stripper bottoms, acid leachate and leaching rinse from zirconium metal and alloy production) are limited for chromium, cyanide, lead, nickel and ammonia in mg per kg of zirconium dioxide plus hafnium dioxide produced (zirconium filtrate: chromium 14.35, cyanide 7.758, lead 10.86, nickel 21.33, ammonia as N 5171 mg/kg daily maximum); hafnium itself is not a limited pollutant and no hafnium concentration in any of these streams was read; EPA describes the zirconium filtrate as treated by ammonia steam stripping, chemical precipitation and sedimentation at 37,640 to 39,900 L per tonne of oxide

    1 · Identity

    Symbol, number
    Hf, 72
    Oxidation states in water
    +4 only; in seawater the anionic hydroxo complex Hf(OH)₅⁻ (Ueki 2023). No redox chemistry in water.
    Note
    The element entry covers the metal, the zirconium twin problem and the nuclear use. This chapter says only how little hafnium water carries and why.

    2 · Occurrence in water

    Natural sources
    Weathering of zircon and baddeleyite, in which hafnium rides with zirconium at about 1 part in 50 (element entry). Dissolved hafnium in the open ocean is depleted at the surface and rises with depth, a scavenged profile that follows dissolved silicon (Ueki 2023).
    Anthropogenic sources
    No effluent figure was read. The plausible sources are zirconium and hafnium chemical plants, nuclear fuel fabrication and heavy mineral sand processing, all of which discharge the element as particulate oxide.
    matrixtypical rangenote
    seawater0.09 to 0.78 pmol/kg
    one ocean basin; PubChem's compilation figure of 0.000007 mg/L (about 40 pmol/L) in the element entry is one to two orders of magnitude higher and is not consistent with the measured profile
    subarctic North Pacific, 0.09 pmol/kg in the surface layer rising to 0.78 pmol/kg below 1000 m; detection limit 0.05 pmol/kg

    3 · Speciation

    Hf(IV) is a small, highly charged cation that hydrolyses fully above pH 2 to 3; in seawater the dissolved species is the pentahydroxo anion Hf(OH)₅⁻ (Ueki 2023). Solid HfO₂ and hydrous hafnium oxide are insoluble and inert to everything but hydrofluoric acid (element entry), so the element partitions to particles and is scavenged from the water column. Fluoride is the only common ligand that keeps it in solution.

    conditiondominant speciesnote
    seawater, pH 8Hf(OH)₅⁻Ueki 2023; scavenged profile, surface depleted
    fluoride bearing acid, such as pickling or etching liquorhafnium fluoro complexesthe element entry names hydrofluoric acid as the one acid that dissolves the oxide film; no constants read
    Solubility
    Hafnium(IV) oxide and hydroxide are insoluble at natural pH; no solubility product was read.
    Hydrolysis
    Complete at natural pH; the dissolved remainder is anionic hydroxo complex.
    Complexation
    Hydroxide and fluoride; carbonate and organic complexes were not sourced.
    Precipitates
    HfO₂ and hydrous hafnium oxide, in practice a trace within zirconium oxide solids.
    HfX4++5HX2OHf(OH)X5X+5HX+\ce{Hf^4+ + 5 H2O -> Hf(OH)5^- + 5 H+}
    net hydrolysis to the seawater species of Ueki 2023; written from their stated species, not from constants

    4 · Role in treatment

    Not relevant or not given for this element.

    5 · Removal and control

    coagulation, sedimentation and filtration (generic particulate metal removal)
    hafnium is already a hydrolysed solid at neutral pH and leaves with the suspended solids
    no hafnium specific study read
    Efficiency
    not read
    Interferences
    fluoride keeps it dissolved

    6 · Analytics

    methodstandarddetection limitnote
    chelating resin preconcentration and high resolution ICP-MSresearch method (Ueki 2023)0.05 pmol/kg in seawaterneeded for natural levels; hafnium is not an analyte of EPA 200.8
    Sampling pitfalls
    Hafnium adsorbs to container walls and to any particle; filter and acidify at once, and expect fluoride in the sample to change the answer.

    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 GDWQno guideline hafnium does not appear in the Annex 3 chemical summary tables
    US EPA NPDWRnot regulated no entry in the table of regulated contaminants
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set BAT 12 metals are Cr, Cu, Ni and Zn only

    8 · Health and environmental effects

    Toxicity
    Low chemical toxicity and no biological role (element entry); no drinking water assessment exists.
    Bioaccumulation
    Not addressed in the sources read.
    Ecotoxicity
    Not addressed in the sources read.

    Flags

    • The seawater range is one Pacific study; the element entry's PubChem figure is inconsistent with it and is flagged above.
    • No industrial effluent or fresh water concentration was read; the sources statements are qualitative.

    Gaps

    • No source read gives hafnium in groundwater, rivers, municipal or industrial wastewater.
    • EU DWD 2020/2184 Annex I was not read this session; its absence of a hafnium parameter is not asserted.
    • No hydrolysis constants or solubility product for hafnium were read; the speciation is taken from the seawater species named by Ueki 2023.
    • No hafnium removal study was read; the removal row is by analogy with any hydrolysed metal.
    • No GCC discharge standard was read.

    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.