Yttrium
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.
| matrix | typical range | note |
|---|---|---|
| fresh surface water, Netherlands | below 0.22 µg/L1990s detection limits | below detection; the detection limit is taken as background |
| salt surface water, Netherlands | below 0.22 µg/L1990s detection limits | below detection |
| groundwater, Netherlands | 0.077 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, Netherlands | below 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 |
| seawater | 0.013 µg/L | PubChem 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.
| condition | dominant species | note |
|---|---|---|
| acid groundwater and mine water, pH below 5 | Y³⁺, YSO₄⁺ | the mobile state |
| neutral to alkaline water | YCO₃⁺, Y(CO₃)₂⁻ | by analogy with the lanthanide pattern in the lanthanum entry; no yttrium specific constants read |
| phosphate rich water and sediment | YPO₄ (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.
4 · Role in treatment
Not relevant or not given for this element.
5 · Removal and control
- Efficiency
- to below detection with the exceptions noted
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS | no standard method text read; the RIVM data are 1990s ICP-MS with detection limits about 0.22 µg/L | 0.22 µg/L in the 1990s Dutch data; RIVM notes that HR-ICP-MS developed since reaches far lower | yttrium 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.
| body | limit | note |
|---|---|---|
| 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 2020/2184 | not set | not an Annex I parameter |
| US EPA NPDWR | not regulated | no MCL |
| WHO GDWQ Table A₆.1 (radionuclides) | 100 Bq/L | yttrium-90, the strontium-90 daughter; guidance level at 0.1 mSv per year |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), BAT 12 | not 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
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)
Identity
- Name and symbol
- Yttrium, Y
- Atomic number
- 39 protons
- Position
- group 3 · period 5 · d-block · transition metal
- CAS number
- 7440-65-5
Atomic structure
- Atomic mass
- 88.905 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d¹
[Kr] 5s²⁴d¹ - Electrons per shell
- 2, 8, 18, 9, 2
- Valence electrons
- 3 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 89Y | 88.905 838(2) | 100 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 1,795 K (1,521.85 °C)
- Boiling point
- 3,618 K (3,344.85 °C)
- Density
- 4.47 g/cm3
- Appearance
- silvery white
- Thermal conductivity
- 17.2 W/(m·K)
- Electrical resistivity
- α, poly: 596 nΩ·m
- Electrical conductivity
- 1.68 MS/m
- Crystal structure
- hexagonal close packed
- Molar heat capacity
- 26.53 J/(mol·K)
Chemical properties
- Oxidation states
- +3
- Electronegativity
- 1.22 (Pauling Scale)
- Ionisation energy
- 6.217 eV
1st 600, 2nd 1,180, 3rd 1,980 kJ/mol - Electron affinity
- 0.307 eV
- Atomic radius
- empirical 190, covalent 190, van der Waals 219 pm
- Ionic radius
- Y³⁺ 90 pm
- Reactivity
- A reactive transition metal that behaves like the heavier lanthanides: bulk metal is protected by a thin oxide film and looks stable in air, but turnings ignite above 400 C and the finely divided metal is very unstable in air.
- with water
- Reacts with water, slowly when cold and faster when hot, to yttrium hydroxide and hydrogen: .
- with oxygen, air
- Bulk metal is relatively stable under a protective Y2O3 film; turnings ignite above 400 C and burn to the oxide: .
- with acids
- Dissolves in most strong dilute acids to yttrium(III) salts and hydrogen: ; concentrated nitric and hydrofluoric acid attack it only slowly.
- with halogens
- Combines with the halogens above about 200 C to the trihalides: .
- Typical compounds
- Y₂O₃ yttrium oxide yttria; phosphor host, ceramics, stabiliser for zirconia
- YCl₃ yttrium chloride starting material for yttrium chemistry
- YF₃ yttrium fluoride reduced with calcium to make the metal
- Y₃Al₅O₁₂ yttrium aluminium garnet YAG laser host and simulated diamond
- Y₃Fe₅O₁₂ yttrium iron garnet microwave filters and acoustic transducers
- YBa₂Cu₃O₇ yttrium barium copper oxide high-temperature superconductor
Occurrence, production and use
- Crustal abundance
- 3.3×101 milligrams per kilogram
- Oceanic abundance
- 1.3×10-5 milligrams per liter
- Occurrence and sources
Yttrium occurs in nearly all of the rare-earth minerals. Analysis of lunar rock samples obtained during the Apollo missions show a relatively high yttrium content.
It is recovered commercially from monazite sand, which contains about 3%, and from bastnasite, which contains about 0.2%. Wohler obtained the impure element in 1828 by reduction of the anhydrous chloride with potassium. The metal is now produced commercially by reduction of the fluoride with calcium metal. It can also be prepared by other techniques.
- ion-adsorption clays (weathered granite) Fujian, Guangdong, Jiangxi, Guangxi, Hunan in China and similar deposits in Myanmar; the main world source
- xenotime (YPO4, up to 50 percent yttrium phosphate) heavy-mineral placer sands; mined in China and Malaysia, present in Florida mineral-sand monazite concentrates
- monazite and bastnaesite Mountain Pass bastnaesite carries about 0.12 percent yttrium among its rare earths
- crustal and oceanic abundance about 33 ppm (BGS figure via RSC); 33 mg/kg crust and 0.000013 mg/L seawater (PubChem)
- Extraction, production
- Rare-earth separation to yttrium oxide
Ore concentrates are leached and the rare earths separated to Y2O3, the form in which most yttrium is traded; neither source states the separation chemistry
Calciothermic reduction of yttrium fluoride to metalRSC states yttrium fluoride reduced with calcium metal; calcium fluoride as the co-product is implied, not named
- Uses
Although metallic yttrium is not widely used, several of its compounds are. Yttrium oxide (Y2O3) and yttrium orthovanadate (YVO4) are both combined with europium to produce the red phosphor used in color televisions. Garnets made from yttrium and iron (Y3Fe5O12) are used as microwave filters in microwave communications equipment. Garnets made from yttrium and aluminum (Y3Al5O12) are used in jewelry as simulated diamond.
Yttrium oxide is one of the most important compounds of yttrium and accounts for the largest use. It is widely used in making YVO4 europium, and Y2O3 europium phosphors to give the red color in color television tubes. Hundreds of thousands of pounds are now used in this application.
Yttrium oxide also is used to produce yttrium-iron-garnets, which are very effective microwave filters.
Yttrium iron, aluminum, and gadolinium garnets, with formulas such as Y3Fe5O12 and Y3Al5O12, have interesting magnetic properties. Yttrium iron garnet is also exceptionally efficient as both a transmitter and transducer of acoustic energy. Yttrium aluminum garnet, with a hardness of 8.5, is also finding use as a gemstone (simulated diamond).
Small amounts of yttrium (0.1 to 0.2%) can be used to reduce the grain size in chromium, molybdenum, zirconium, and titanium, and to increase strength of aluminum and magnesium alloys.
Alloys with other useful properties can be obtained by using yttrium as an additive. The metal can be used as a deoxidizer for vanadium and other nonferrous metals. The metal has a low cross section for nuclear capture. 90Y, one of the isotopes of yttrium, exists in equilibrium with its parent 90Sr, a product of nuclear explosions. Yttrium has been considered for use as a nodulizer for producing nodular cast iron, in which the graphite forms compact nodules instead of the usual flakes. Such iron has increased ductility.
Yttrium also can be used in laser systems and as a catalyst for ethylene polymerization reactions.
It also has potential use in ceramic and glass formulas, as the oxide has a high melting point and imparts shock resistance and low expansion characteristics to glass.
- Ceramics and refractories: Y2O3 as the stabiliser in zirconia ceramics; abrasives, bearings and seals, continuous-casting nozzles, jet-engine thermal-barrier coatings, oxygen sensors, cutting tools
- Electronics, lighting and lasers: yttrium-aluminium garnet (YAG) laser crystals for surgery, cutting, welding and communications; yttrium-iron garnets in microwave radar filters; phosphors for flat-panel displays and lighting, white LEDs; high-temperature superconductors
- Metallurgy: grain-refining additive and deoxidiser; strengthening additive in aluminium and magnesium alloys, heating-element alloys and superalloys
- Chemicals: catalyst in ethene polymerisation; catalysts generally
- Medicine: yttrium-90 radiotherapy for liver and other cancers
- Glass: Y2O3 in optical and camera-lens glass for heat and shock resistance
- Safety, toxicity
- GHS classification, signal word Danger
- H228 Flammable solid Flammable solids
- H250 Catches fire spontaneously if exposed to air Pyrophoric liquids
- H302 Harmful if swallowed Acute toxicity, oral
- H312 Harmful in contact with skin Acute toxicity, dermal
- H332 Harmful if inhaled Acute toxicity, inhalation
- H413 May cause long lasting harmful effects to aquatic life to the aquatic environment, long-term hazard
- H371 May cause damage to organs Specific target organ toxicity, single exposure
Discovery and name
- Discovered by
- Johan Gadolin
- Discovered
- 1794
- First isolated
- Friedrich Wöhler
- Named by
- not in sources
- Origin of the name
- after Ytterby (Sweden) and its mineral ytterbite (gadolinite)
Yttrium has a silver-metallic luster and is relatively stable in air. Turnings of the metal, however, ignite in air if their temperature exceeds 400°C. Finely divided yttrium is very unstable in air.
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.