Yttrium

    group 3 · period 5 · d-block · transition metal

    minorYttrium is unregulated in drinking water and effluent everywhere read and has no treatment role; it behaves as a heavy rare earth in water, trivalent, carbonate complexed and phosphate limited, and the one quantitative environmental framework for it is the Dutch RIVM risk limit set (MPC 6.4 µg/L fresh, 0.94 µg/L salt) derived alongside the lanthanides.

    Typical wastewaters

    • acid mine drainage passive remediation (Iberian Pyrite Belt) YSO₄⁺ ion pair in high sulfate AMD, retained by basaluminite as a monodentate inner-sphere complex
    • coal mining acid mine drainage (solvent extraction recovery) yttrium with the heavy rare earths, over 75 percent extracted by Cyanex 272 South Africa
    • acid mine drainage treatment residuals rare earths and yttrium adsorbed on hydrous manganese oxides in treatment sludge at near ore grade over 99 percent REY uptake by biotic HMO within 7 days
    • rare earth industry wastewater Y³⁺ (10 to 110 mg/L test range) removed by biosorption 123.65 mg/g on Serratia marcescens

    1 · Identity

    Symbol, number
    Y, 39
    Oxidation states in water
    +3 only (Y³⁺); no redox chemistry in water
    Note
    The element entry covers the metal and its slow reaction with water. In natural water yttrium is a hard trivalent cation whose ionic radius puts it among the heavy lanthanides (holmium, dysprosium), and it is treated with them by RIVM.

    2 · Occurrence in water

    Natural sources
    Weathering of xenotime, monazite and the ion adsorption clays (element entry); released most in acid water. Dutch groundwater background 0.416 µg/L at pH 6.2 or above and 0.077 µg/L below pH 6.2 (RIVM Table 5.1).
    Anthropogenic sources
    Rare earth separation and phosphor, ceramic and laser manufacture (element entry); the Rhine estuary carries anthropogenic light rare earths (see La) and the RIVM report treats the estuary values as anthropogenic. Raw groundwater at some Dutch works carried enough for Y to reach 8 to 14 µg/L in drinking water at three works in 1994.
    matrixtypical rangenote
    fresh surface water, Netherlandsbelow 0.22 µg/L1990s detection limitsbelow detection; the detection limit is taken as background
    salt surface water, Netherlandsbelow 0.22 µg/L1990s detection limitsbelow detection
    groundwater, Netherlands0.077 to 0.416 µg/L
    region-dependent; 1991 to 1995 data
    background values used by RIVM: 0.416 at pH 6.2 or above, 0.077 below pH 6.2; raw groundwater at some works was higher
    drinking water, Netherlandsbelow detection to 8 to 14 µg/L
    1994 data, treatment may have changed
    normally below detection; Y, La, Ce and Nd reached 8 to 14 µg/L at Bilthoven, De Haere and Epe in 1994, called exceptions
    seawater0.013 µg/LPubChem figure carried in the element entry

    3 · Speciation

    Trivalent Y³⁺ throughout the natural pH and Eh range; the free ion and sulfate pairs in acid water, carbonate complexes in neutral to alkaline water, and phosphate solids as the solubility cap, the pattern described for the lanthanides in the lanthanum entry. Yttrium sits with the heavy lanthanides, whose carbonate complexes are the strongest, so it is relatively more mobile than lanthanum in alkaline water. RIVM cites Liu and Byrne (1997) on rare earth and yttrium phosphate solubilities as the solubility control.

    conditiondominant speciesnote
    acid groundwater and mine water, pH below 5Y³⁺, YSO₄⁺the mobile state
    neutral to alkaline waterYCO₃⁺, Y(CO₃)₂⁻by analogy with the lanthanide pattern in the lanthanum entry; no yttrium specific constants read
    phosphate rich water and sedimentYPO₄ (s) (xenotime is the crystalline form)solubility cap
    Solubility
    Phosphate controlled; Dutch surface water below 0.22 µg/L.
    Hydrolysis
    Minor below pH 8; Y(OH)₃ forms under lime, so lime neutralisation of acid water strips yttrium with the iron and aluminium hydroxides.
    Complexation
    Sulfate in acid water, carbonate in alkaline water (lanthanide pattern); no yttrium stability constants read this session.
    Precipitates
    YPO₄, Y(OH)₃ under lime, YF₃ near fluoride rich discharges.
    YX3++POX4X3YPOX4(s)\ce{Y^3+ + PO4^3- -> YPO4 (s)}
    phosphate limited solubility; RIVM cites the yttrium phosphate solubility work of Liu and Byrne (1997), the constant itself not read

    4 · Role in treatment

    Not relevant or not given for this element.

    5 · Removal and control

    conventional drinking water treatment
    Dutch works reduced raw groundwater rare earths to below detection in nearly all cases; the three 1994 exceptions reached 8 to 14 µg/L
    1990s data
    Efficiency
    to below detection with the exceptions noted

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MSno standard method text read; the RIVM data are 1990s ICP-MS with detection limits about 0.22 µg/L0.22 µg/L in the 1990s Dutch data; RIVM notes that HR-ICP-MS developed since reaches far loweryttrium was used as an interference monitor in the PGE isopod study (see Pd), a reminder that it is a common ICP-MS internal standard and must not be added as one when it is the analyte
    Sampling pitfalls
    Filter before acidifying; colloid bound Y passes 0.45 µm filters. Do not use yttrium as the ICP-MS internal standard when yttrium is an analyte.

    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/Lyttrium-90, the strontium-90 daughter; 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.
    Bioaccumulation
    RIVM found bioaccumulation data for the rare earths limited and often contradictory and included no secondary poisoning assessment.
    Ecotoxicity
    RIVM (2000) environmental risk limits, not permit limits: MPA 6.2 µg/L fresh water (lowest LC₅₀ divided by 1000) and 0.72 µg/L salt water (lowest LC₅₀ divided by 1000); background 0.22 µg/L (detection limit); MPC 6.4 µg/L fresh and 0.94 µg/L salt; negligible concentrations 0.28 µg/L fresh and 0.22 µg/L salt. Data behind them: Daphnia magna 48 h EC₅₀ 6.2 mg/L and 21 d NOEC 0.3 to 0.7 mg/L, zebrafish 96 h LC₅₀ 14 mg/L; marine Acartia tonsa 48 h LC₅₀ 0.72 mg/L, Poecilia reticulata 96 h LC₅₀ 16.7 mg/L. Marine organisms were consistently more sensitive to the rare earths than freshwater ones.

    Flags

    • The RIVM MPCs are 2000 environmental risk limits from a very small data set with assessment factors of 1000; they are not discharge limits.
    • Dutch groundwater and drinking water figures are 1991 to 1995 data.
    • Carbonate speciation is written by analogy with the lanthanide pattern; no yttrium constants were read.

    Gaps

    • No yttrium specific stability constants or solubility product were read.
    • No municipal or industrial wastewater concentration was read.
    • No removal percentage for yttrium in any treatment other than the Dutch drinking water observation was read.
    • No GCC discharge standard was read.
    • World river average yttrium (Gaillardet et al. 2003) was not reachable.

    Sources

    Sneller, F. E. C., Kalf, D. F., Weltje, L. and Van Wezel, A. P., Maximum Permissible Concentrations and Negligible Concentrations for Rare Earth Elements (REEs), RIVM report 601501 011 (Bilthoven, 2000), Tables I, II, 4.1, 5.1 and Appendix 1 (yttrium rows), section 5.1
    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 Y (rare earth metal chemistry, xenotime and ion adsorption clay sources, seawater abundance) (data/elements/Y.json, data/reference/text/Y.json)
    Lozano A., Fernandez-Martinez A., Ayora C., Di Tommaso D., Poulain A., Rovezzi M. and others, Solid and aqueous speciation of yttrium in passive remediation systems of acid mine drainage, Environmental Science and Technology 53(19), 11153 to 11161 (2019), doi 10.1021/acs.est.9b01795 (abstract)
    Baloyi J., Masindi V., Muedi K. L., Chatzisymeon E., Foteinis S., Insights into the recovery of rare earth elements from acid mine drainage: fostering circular economy in mine water management, Environmental Research 305, 125116 (2026), doi 10.1016/j.envres.2026.125116 (abstract)
    Boothe-Lordon T. J., Capo R. C., Stewart B. W., Olds T. A., Rosenfeld C. E., Critical metal adsorption by biotic and abiotic hydrous manganese oxides: implications for acid mine drainage resource recovery, ACS Omega 10(37), 42577 to 42588 (2025), doi 10.1021/acsomega.5c04278 (abstract)
    Liang C. L. and Shen J. L., Removal of yttrium from rare-earth wastewater by Serratia marcescens: biosorption optimization and mechanisms studies, Scientific Reports 12, 4861 (2022), doi 10.1038/s41598-022-08542-0 (abstract)

    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.