Tantalum

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

    minorTantalum has no drinking water guideline, no effluent limit and no treatment role: Ta(V) hydrolyses to the neutral Ta(OH)₅ and the insoluble pentoxide, dissolved tantalum in the sea is tens of femtomoles per kilogram and is the least soluble of the group 4 and 5 metals, and whatever a coltan or capacitor plant discharges is particulate oxide that any generic solids removal step takes out.

    Typical wastewaters

    • secondary tantalum recovery (capacitor scrap, tantalum sludge and tantalum alloy scrap leaching) dissolved and fine particulate tantalum in the acid leach and rinse water, the tantalum powder acid wash water and the leaching scrubber water, together with copper, lead, nickel and zinc from the scrap 40 CFR 421.283 sets a tantalum limit as a daily maximum only, in mg per kg of tantalum powder produced: 103.8 for tantalum alloy leach and rinse, 9.09 for capacitor leach and rinse, 92.39 for tantalum sludge leach and rinse, 0.158 for tantalum powder acid wash and rinse, 2.196 for leaching wet air pollution control; no monthly average and no concentration in mg/L is given
    • primary columbium-tantalum hydrometallurgy (hydrofluoric acid digestion, MIBK solvent extraction, K₂TaF₇ precipitation and reduction to metal) spent hydrofluoric acid raffinate, ammonia precipitation filtrate, tantalum salt drying and tantalum powder wash water: a fluoride and ammonia matrix in which tantalum is the process metal but not a regulated pollutant 40 CFR 421.113 limits lead, zinc, ammonia and fluoride per kg of concentrate digested or salt handled (solvent extraction raffinate: fluoride 324.0 and ammonia as N 1233 mg/kg daily maximum; tantalum powder wash: fluoride 715.2 and ammonia as N 2724 mg/kg); EPA names the raffinate containing the spent hydrofluoric acid and the scrubber liquors as wastewater; no tantalum concentration in any stream was read

    1 · Identity

    Symbol, number
    Ta, 73
    Oxidation states in water
    +5 only; in seawater the neutral hydroxo complex Ta(OH)₅ (Ueki 2023). No redox chemistry in water.
    Note
    The element entry covers the metal, coltan and the capacitor industry. This chapter says only how little tantalum water carries and why.

    2 · Occurrence in water

    Natural sources
    Weathering of columbite-tantalite and of tin ore, which carries it (element entry). In the subarctic North Pacific dissolved tantalum is uniform with depth at about 0.015 pmol/kg, unlike hafnium, which rises with depth (Ueki 2023).
    Anthropogenic sources
    No effluent figure was read. The plausible sources are coltan concentrators and tin smelter slag processing, tantalum chemical plants making potassium heptafluorotantalate, and capacitor manufacture; the fluoride route keeps tantalum dissolved as fluoro complexes until the fluoride is stripped.
    matrixtypical rangenote
    seawater0.006 to 0.026 pmol/kg
    one ocean basin; PubChem's compilation figure of 0.000002 mg/L (about 11 pmol/L) in the element entry is about three orders of magnitude higher and is not consistent with the measured profile
    subarctic North Pacific, 0.015 plus or minus 0.005 pmol/kg and uniform with depth; detection limit 0.006 pmol/kg

    3 · Speciation

    Ta(V) hydrolyses fully at natural pH; the dissolved species in seawater is the neutral Ta(OH)₅ (Ueki 2023). The pentoxide is insoluble and inert to every acid but hydrofluoric, which dissolves it as fluoro complexes such as TaF₇²⁻ (element entry). The near uniform depth profile means tantalum is neither strongly scavenged nor regenerated once dissolved, but the absolute level is so low that the element is effectively absent from water.

    conditiondominant speciesnote
    seawater, pH 8Ta(OH)₅ (aq)Ueki 2023
    hydrofluoric acid processing liquorTaF₇²⁻ and related fluoro complexesthe K₂TaF₇ route of the element entry; no constants read
    Solubility
    Tantalum pentoxide is insoluble at natural pH; no solubility product was read.
    Hydrolysis
    Complete at natural pH; the dissolved remainder is the neutral pentahydroxo complex.
    Complexation
    Hydroxide and fluoride; carbonate and organic complexes were not sourced.
    Precipitates
    Ta₂O₅ and hydrous tantalum oxide.
    TaX5++5HX2OTa(OH)X5(aq)+5HX+\ce{Ta^5+ + 5 H2O -> Ta(OH)5 (aq) + 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)
    tantalum is a hydrolysed solid at neutral pH and leaves with the suspended solids
    no tantalum specific study read; fluoride bearing liquors need the fluoride precipitated first
    Efficiency
    not read
    Interferences
    fluoride keeps it dissolved

    6 · Analytics

    methodstandarddetection limitnote
    chelating resin preconcentration and high resolution ICP-MSresearch method (Ueki 2023)0.006 pmol/kg in seawaterneeded for natural levels; tantalum is not an analyte of EPA 200.8
    Sampling pitfalls
    Tantalum adsorbs to container walls and particles at these levels; filter and acidify at once, and keep fluoride out of the sample train unless it is meant to be there.

    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 tantalum 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
    Non toxic, no biological role, no immune response, which is why it is implanted in the body (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 source statements are qualitative.

    Gaps

    • No source read gives tantalum in groundwater, rivers, municipal or industrial wastewater.
    • EU DWD 2020/2184 Annex I was not read this session; its absence of a tantalum parameter is not asserted.
    • No hydrolysis constants or solubility product for tantalum were read; the speciation is taken from the seawater species named by Ueki 2023.
    • No tantalum 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.