Scandium

    group 3 · period 4 · d-block · transition metal

    minorScandium has no drinking water guideline, no discharge limit and no treatment role; its water literature is oceanographic and geochemical (a particle reactive trivalent trace element at picomolar levels), and its only industrial water footprint is that of the host processes it is recovered from (titanium dioxide, nickel laterite, uranium), which the element entry already says.

    Typical wastewaters

    • titanium dioxide pigment production (chloride process spent iron chloride acid) Sc³⁺ at 10 to 140 ppm in the acidic iron chloride by-product solution, co-extracted with Zr, Ti and V on ion exchange
    • titanium dioxide production waste acid and solid waste scandium in the waste acid used to leach scandium-bearing solid waste, recovered by P₂₀₄ and TBP solvent extraction after iron removal
    • acid mine drainage (abandoned mine, San Luis, Argentina) trace Sc³⁺ measured by on-line preconcentration ICP-OES detection limit 4 ng/L, linear to 10 mg/L

    1 · Identity

    Symbol, number
    Sc, 21
    Oxidation states in water
    +3 only, as Sc³⁺ hydrolysed and complexed: Klimpel and Bau (2023) state that scandium forms strong bonds with organic ligands and with OH⁻ and F⁻, and that these complexes usually dominate its speciation in natural water.
    Note
    A small, hard trivalent ion that behaves like a light rare earth but is scavenged by particles even more strongly.

    2 · Occurrence in water

    Natural sources
    Trace substitution in more than 100 minerals (element entry); weathered into rivers bound to organic colloids and nanoparticles, then scavenged onto particles in the ocean. Dissolved scandium correlates with dissolved organic carbon in boreal rivers (r squared 0.67), so organic colloids carry it.
    Anthropogenic sources
    None documented in the sources read; scandium is a by-product of titanium dioxide, nickel laterite and uranium processing and any release is inside those effluents (element entry).
    matrixtypical rangenote
    rivers, boreal Sweden (twelve rivers, filtered)189 to 1,170 pmol/Lregion-dependent; one studySkellefteälven 374, Klarälven 710, Västerdalälven 1,170 pmol/L; at the high end of world rivers, organic particle rich
    seawater0.30 to 30.3 pmol/kgquoted through Klimpel and BauNorth Atlantic 5.70 to 30.3, North Pacific 0.80 to 28.8, South Pacific 0.30 to 18.3 (Parker and others 2016 as cited); nutrient type profile, higher in deep water

    3 · Speciation

    Sc³⁺ is hydrolysed and complexed by hydroxide, fluoride and organic ligands at natural pH and is strongly particle reactive; in rivers it rides on organic colloids and in the sea it is scavenged, giving picomolar concentrations. It decouples from the rare earths in organic rich rivers (Klimpel and Bau 2023). Not relevant to treatment.

    conditiondominant speciesnote
    organic rich river waterSc bound to organic colloids and nanoparticles; Sc(OH)n^(3-n)+ and ScF²⁺ complexesKlimpel and Bau 2023
    seawaterhydroxo complexes; scavenged by particlesnutrient type profile
    Solubility
    Not relevant; Sc(OH)₃ and ScPO₄ would control at concentrations never met in water.
    Hydrolysis
    Strong; the trivalent ion hydrolyses at low pH like the light rare earths.
    Complexation
    Organic ligands, hydroxide and fluoride dominate (Klimpel and Bau 2023).
    Precipitates
    None relevant in water treatment.

    4 · Role in treatment

    Not relevant or not given for this element.

    5 · Removal and control

    Not relevant or not given for this element.

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after preconcentrationno numbered water standard read; scandium is often the internal standard in ICP methods, which rules it out as an analyte therepicomolar in research methods (Klimpel and Bau 2023 report filtered river concentrations of hundreds of pmol/L)research only
    Sampling pitfalls
    Filter in the field; colloidal and particulate scandium dominate, so filtered and unfiltered results differ many fold.

    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, EU DWD 2020/2184, US EPA NPDWRno guideline scandium appears in none of the three: the EU Annex I (legislation.gov.uk mirror) and the US NPDWR table were both checked for scandium this session; WHO has no fact sheet for it

    8 · Health and environmental effects

    Toxicity
    Not addressed in the sources read; the element entry notes no biological role.
    Bioaccumulation
    Not addressed in the sources read.
    Ecotoxicity
    Not addressed in the sources read.

    Flags

    • The seawater ranges are quoted through Klimpel and Bau 2023, not from Parker and others 2016 directly.
    • The scandium as internal standard remark is general laboratory practice, not from a source read.

    Gaps

    • No toxicity, ecotoxicity, discharge or industrial water figure exists in the sources read; the sections are left as not relevant.
    • Parker and others 2016 (Geophysical Research Letters) was not read directly.

    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.