Europium
minorEuropium has no water regulation and no treatment role; its water story is the one redox exception of the middle lanthanides (reduction to Eu²⁺ in hot reducing fluids, giving positive europium anomalies), and its use as the neighbour against which anthropogenic gadolinium and samarium anomalies are measured.
Typical wastewaters
- coal mine drainage (acid) Eu³⁺ and the EuSO₄⁺ ion pair dissolved at low pH in sulfate rich drainage; total rare earths averaged 282 µg/L over 141 Appalachian sites, per-element values not read co-precipitates into the iron, aluminium and manganese hydroxide sludge when the drainage is neutralised
- nuclear site discharges (UK monitoring) fission products Eu-154 and Eu-155 (half-lives 8.80 and 4.96 years) as Eu³⁺, listed in the RIFE radionuclide data tables monitoring tables only; discharge quantities were not read
1 · Identity
- Symbol, number
- Eu, 63
- Oxidation states in water
- +3 only (Eu³⁺)
- Note
- The metal's reactions are in the book entry; in water europium shares the trivalent carbonate and phosphate chemistry of the lanthanide row.
2 · Occurrence in water
- Natural sources
- Weathering of monazite and bastnaesite; the middle lanthanide most depleted from feldspar bearing rocks (negative Eu anomaly of shale) and enriched in hydrothermal fluids where Eu(III) is reduced to the larger, more soluble Eu(II). In seawater Eu/Eu* is 0.88 to 1.15; negative Eu anomalies appeared in an organic carbon reactive barrier at low Eh with methane and sulfide present, suggesting reduction even at low temperature.
- Anthropogenic sources
- No europium point source to water was read. Fission products Eu-154 and Eu-155 appear in the RIFE radionuclide data tables for UK nuclear site monitoring (half-lives 8.80 and 4.96 years); discharge quantities were not read.
| matrix | typical range | note |
|---|---|---|
| seawater | 0.28 to 2.04 pmol/Lone station | western Pacific, 3 to 5663 m; concentrations rise with depth |
| acid mine drainage (total rare earth elements) | 282 average µg/L sum of all REE, not this element | total REE in coal mine drainage of the northern and central Appalachian basins, 141 sites; per-element values not read |
| groundwater (total rare earth elements) | 0.36 to 1.66 µg/L sum of all REE, not this element | sum of REE at a pH 5.1 to 6.1 site; 973 µg/L mean at a pH 3.1 to 3.4 site; per-element values not read |
3 · Speciation
Trivalent Eu³⁺ throughout the natural pH and Eh range. Below about pH 6, and in sulfate rich water such as mine drainage, the free ion and the EuSO₄⁺ ion pair dominate (sulfate complexes above 90 percent at pH 3.1 to 3.4 in the EPA groundwater study). From neutral to alkaline pH the carbonate complexes EuCO₃⁺ and Eu(CO₃)₂⁻ take over, and they bind the heavy lanthanides more strongly than the light ones (at pH 5.1 to 6.1 the carbonate share rose from 5.0 percent for La to 19.2 percent for Lu). Phosphate, carbonate and fluoride solids and sorption to iron and manganese oxides cap the dissolved concentration at ng/L in oxic neutral water, and the light lanthanides ride partly on colloids. Europium adds a reduction step under strongly reducing conditions: Eu³⁺ to Eu²⁺, which no longer follows the trivalent lanthanides.
| condition | dominant species | note |
|---|---|---|
| acid mine drainage and acidic groundwater, pH below 5 | Eu³⁺, EuSO₄⁺ | the most mobile state; dissolved total REE in coal mine drainage averaged 282 µg/L (Part 2 survey), against ng/L in neutral water |
| neutral to alkaline groundwater and river water, pH 7 to 9 | EuCO₃⁺, Eu(CO₃)₂⁻; a small free ion fraction; part of the load on colloids below 0.2 µm | the carbonate complexes keep the element in solution and make the heavy lanthanides relatively more mobile |
| phosphate rich water, treated lake sediments | EuPO₄ (s) as a hydrated phosphate | REE phosphate solubility products can be as low as 10⁻25 (RIVM report citing Liu and Byrne 1997) |
| hot reducing fluids; possibly low Eh groundwater with sulfide and methane | Eu²⁺ | the positive europium anomaly of hydrothermal water; in the EPA groundwater study negative Eu anomalies in a reducing barrier suggested reduction despite theoretical constraints |
- Solubility
- Controlled by the phosphate, carbonate and fluoride solids and by sorption; the RIVM report puts total dissolved lanthanum and cerium in Dutch surface water at about 1 µg/L or less and the free ion fraction at 0.3 fM to 9 pM. No solubility product for a europium solid was read this session.
- Hydrolysis
- Hydrolysis of Eu³⁺ is minor in natural water; the hydroxide Eu(OH)₃ forms only at high pH, so lime or caustic neutralisation of acid mine water strips the element with the iron and aluminium hydroxides rather than as its own hydroxide (no hydrolysis constant read this session).
- Complexation
- Sulfate at low pH, carbonate at neutral to alkaline pH (the sources read); humic substances compete for the element in organic rich water and are out-competed by carbonate in alkaline water. No stability constants were read this session.
- Precipitates
- EuPO₄ (hydrated), Eu₂(CO₃)₃, Eu(OH)₃ under lime; Eu(III) compounds are far less soluble than the corresponding Ce(III) compounds (Dahle and Arai).
4 · Role in treatment
Not relevant or not given for this element.
5 · Removal and control
- Efficiency
- not quoted as a percentage
- Efficiency
- to below 2 to 4 ng/L
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS | ISO 17294-2:2023 | not read; the standard covers drinking, surface, ground and waste water | the ISO 17294-2 element list as read this session does not name europium; verify against the standard |
| ICP-MS after preconcentration | research methods: chelating resin columns or magnesium hydroxide co-precipitation, then quadrupole or high resolution ICP-MS | 0.012 to 0.98 pmol/L (procedural blanks 0.041 to 3.60 pmol/L) for the 14 lanthanides pooled, magnesium hydroxide co-precipitation with a factor of about 200; terbium has been measured at 7 fmol/kg in recycled water | the only way to reach the ng/L and sub-ng/L levels of rivers and seawater; the shale-normalised pattern, not the single concentration, is what the geochemists read |
- Sampling pitfalls
- Filtration defines the result: 0.2 or 0.45 µm filtrates still carry colloid bound lanthanides, and only ultrafiltration (10 kDa) separates the truly dissolved pool, which matters most for the light lanthanides. Acidify after filtration. Report the shale-normalised pattern so that anthropogenic anomalies (gadolinium, lanthanum, samarium) are visible. The ISO 17294-2 element list as read this session does not name europium, so the method's applicability must be checked against the standard itself. Eu is a natural neighbour for interpolating Gd* and was used in the Rhine work to quantify anthropogenic Sm, although its own redox anomalies can decouple it from the row.
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 |
|---|---|---|
| US EPA National Primary Drinking Water Regulations | not regulated | no lanthanide or rare earth element in the NPDWR table |
| body | limit | note |
|---|---|---|
| EU CWW BAT-AEL (Decision 2016/902), BAT 12 | not set | Tables 1 to 3 carry TOC, COD, TSS, TN, Ninorg, TP, AOX, Cr, Cu, Ni, Zn; no rare earth element |
8 · Health and environmental effects
- Toxicity
- No human health guideline; no toxicity data for europium were read this session.
- Bioaccumulation
- Field bioconcentration factors in Rhine estuary amphipods fall from the light to the heavy lanthanides (La 28,840 to Lu 4,786; Eu 11,220); carp muscle takes up little (BCF 0.22 to 1.10 for Ce, La, Nd, Pr, Sm) while internal organs reach 634 to 978. Anthropogenic La and Sm in the Rhine are taken into mussel shells, anthropogenic Gd is not, so speciation decides bioavailability.
- Ecotoxicity
- No MPC was derived for europium: the RIVM report set risk limits only for Y, La, Ce, Pr, Nd, Sm, Gd and Dy. The one europium number it carries is a field bioconcentration factor in amphipods of 11,220 (porewater basis).
Flags
- The RIVM MPCs, where they exist, are environmental risk limits from a 2000 report (LC₅₀ divided by 1000, background at the detection limit), not permit limits.
- The seawater range is one western Pacific station.
- The Eu reduction half reaction is written here; the sources describe the anomaly and infer reduction but print no equation.
- Europium's absence from the ISO 17294-2 list may be an omission in the catalogue summary read.
Gaps
- WHO GDWQ and EU DWD 2020/2184 Annex I were not read this session (eur-lex returned the articles without the annexes), so their absence of a rare earth parameter is not asserted here; only the US EPA table was read.
- No GCC discharge standard was read; no GCC row is written.
- World average river water concentrations (Gaillardet et al. 2003) were not reachable; river figures come from the Rhine and Dutch waters only.
- No source read this session gives municipal wastewater concentrations for this element beyond the gadolinium literature.
- ICP-MS oxide interference corrections between lanthanides are standard practice but no method text describing them was read, so none is written.
- No stability constants or solubility products for this element's carbonate, phosphate or hydroxide were read; the speciation is qualitative, taken from the EPA groundwater study and the RIVM report.
- No europium concentration in rivers or groundwater was read.
- No Eu-154 or Eu-155 discharge quantity was read.
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, 2.2 and 4.1, section 5.1 and Appendices 1 to 3
Rare earth element geochemistry characteristics of seawater and porewater from deep sea in western Pacific, Scientific Reports 7 (2017), Table 1 (Pigafetta basin, 3 to 5663 m)
Rare-Earth Elements as Natural Tracers for In Situ Remediation of Groundwater (open access, PMC7868090); REE speciation and concentrations at three US groundwater remediation sites
The occurrence and concentration of rare earth elements in acid mine drainage and treatment byproducts, Part 2: regional survey of northern and central Appalachian coal basins, Mining, Metallurgy and Exploration (OSTI 1577122)
Lawrence, M. G. et al., Removal of magnetic resonance imaging contrast agents through advanced water treatment plants, Water Science and Technology 61 (2010) 685 to 692 (abstract via Crossref)
Hatje, V., Bruland, K. W. and Flegal, A. R., Increases in anthropogenic gadolinium anomalies and rare earth element concentrations in San Francisco Bay over a 20 year record, Environmental Science and Technology 50 (2016) 4159 to 4168 (abstract via Europe PMC)
Kulaksiz, S., Rare earth elements as emerging contaminants in the Rhine River, Germany and its tributaries, PhD thesis, Jacobs University Bremen (2012), chapters III to V (the Environment International 2011, Applied Geochemistry 2011 and EPSL 2013 papers)
ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes (element list from the ISO catalogue abstract)
US EPA, National Primary Drinking Water Regulations (table of regulated contaminants; no lanthanide, rare earth or actinium entry; gross alpha 15 pCi/L)
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
Radioactivity in Food and the Environment, 2012 (RIFE 18), Appendix 1 CD supplement (Environment Agency, FSA, NIEA, SEPA, October 2013), section 3 and Annex table of radionuclide data
Dahle, J. T. and Arai, Y., Environmental geochemistry of cerium: applications and toxicology of cerium oxide nanoparticles, International Journal of Environmental Research and Public Health 12 (2015) 1253 to 1278 (open access, PMC4344665)
Identity
- Name and symbol
- Europium, Eu
- Atomic number
- 63 protons
- Position
- no group (f-block) · period 6 · f-block · lanthanide
- CAS number
- 7440-53-1
Atomic structure
- Atomic mass
- 151.964 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d¹⁰ 5p⁶ 6s² 4f⁷
[Xe] 6s²⁴f⁷ - Electrons per shell
- 2, 8, 18, 25, 8, 2
- Valence electrons
- 9 ns, (n-1)d and (n-2)f
| isotope | mass (u) | abundance |
|---|---|---|
| 151Eu | 150.919 857(9) | 47.81 % |
| 153Eu | 152.921 237(9) | 52.19 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 1,095 K (821.85 °C)
- Boiling point
- 1,802 K (1,528.85 °C)
- Density
- 5.24 g/cm3
- Appearance
- silvery white, with a pale yellow tint; but rarely seen without oxide discoloration
- Thermal conductivity
- est. 13.9 W/(m·K)
- Electrical resistivity
- poly: 0.900 µΩ·m
- Electrical conductivity
- 1.11 MS/m
- Crystal structure
- body-centered cubic
- Molar heat capacity
- 27.66 J/(mol·K)
Chemical properties
- Oxidation states
- +3, +2
- Electronegativity
- not in sources
- Ionisation energy
- 5.67 eV
1st 547.1, 2nd 1,085, 3rd 2,404 kJ/mol - Electron affinity
- not in sources
- Atomic radius
- empirical 198, covalent 198, van der Waals 233 pm
- Ionic radius
- Eu²⁺ 117; Eu³⁺ 95 pm
- Reactivity
- The most reactive of the lanthanides: its half-filled 4f7 shell makes the +2 state unusually stable, so europium behaves much like calcium, tarnishing in air within hours and attacking water briskly; Eu3+ still dominates its salts.
- with water
- Reacts with water about as vigorously as calcium, giving the hydroxide and hydrogen: , so the metal is stored under oil or argon.
- with oxygen, air
- Oxidises quickly in air (a centimetre piece is oxidised through in days) and ignites at 150 to , the pale pink sesquioxide.
- with acids
- Dissolves readily in dilute sulfuric acid to pale pink Eu3+ solutions: , with hydrogen evolved.
- with halogens
- Burns in the halogens to the trihalides: , and the trihalides are easily reduced (by hydrogen or the metal) to divalent EuCl2.
- Typical compounds
- Eu₂O₃ europium(III) oxide red phosphor in screens and lamps
- EuCl₃ europium(III) chloride soluble salt, source of Eu3+ in solution
- EuCl₂ europium(II) chloride divalent halide, made by reducing EuCl3 with hydrogen
- Eu₂(SO₄)₃ europium(III) sulfate soluble salt from the metal and sulfuric acid
- Eu(NO₃)₃ europium(III) nitrate soluble salt used to make doped phosphors
Occurrence, production and use
- Crustal abundance
- 2.0 milligrams per kilogram
- Oceanic abundance
- 1.3×10-7 milligrams per liter
- Occurrence and sources
Europium has been identified spectroscopically in the sun and certain stars. Seventeen isotopes are now recognized. Europium isotopes are good neutron absorbers and are being studied for use in nuclear control applications.
- monazite (phosphate) and bastnaesite (fluorocarbonate) the main minerals, with the other lanthanides, in heavy-mineral sands and carbonatite deposits
- Extraction, production
- Ion exchange and solvent extraction from monazite and bastnaesite to europium oxide
europium oxide 99.99 percent averaged 27 dollars per kilogram in 2024 (usgs-mcs2025, PDF p148, printed p144)
Europium metal by heating europium(III) oxide with an excess of lanthanum under vacuumno balanced equation printed by the source
- Uses
Europium is the most reactive of the rare earth elements. There are no commercial applications for europium metal, although it has been used to dope some types of plastics to make lasers. Since it is a good absorber of neutrons, europium is being studied for use in nuclear reactors.
Europium oxide (Eu2O3), one of europium's compounds, is widely used as a red phosphor in television sets and as an activator for yttrium-based phosphors.
Europium-doped plastic has been used as a laser material. With the development of ion-exchange techniques and special processes, the cost of the metal has been greatly reduced in recent years.
- Lighting, displays and security printing: red phosphor in euro banknotes that glows under ultraviolet light to reveal forgeries; red-emitting phosphor in low-energy light bulbs limited quantities of rare earths were recovered from fluorescent lamps in the United States in 2024 (usgs-mcs2025)
- Nuclear: neutron absorber in reactor control rods
- Lasers and superconductors: europium-doped plastic as a laser material; thin superconducting alloys
- Rare earth mining and separation: mined as bastnaesite (a rare-earth fluorocarbonate) at Mountain Pass, California, and as monazite (a phosphate) in heavy-mineral-sand concentrates; separated from the other rare earths by ion exchange and solvent extraction world mine production of rare earths 390,000 t of rare-earth-oxide equivalent in 2024 (USGS estimate), of which China 270,000 t (production quota), the United States 45,000 t, Burma 31,000 t, Australia, Nigeria and Thailand 13,000 t each; reserves over 90 million t, China 44 million t, Brazil 21 million t (usgs-mcs2025, PDF p149, printed p145)
- Safety, toxicity
- GHS classification, signal word Danger
- H228 Flammable solid Flammable solids
- H250 Catches fire spontaneously if exposed to air Pyrophoric liquids
- H260 In contact with water releases flammable gases which may ignite spontaneously Substances and mixtures which in contact with water, emit flammable gases
Discovery and name
- Discovered by
- Eugène-Anatole Demarçay
- Discovered
- 1896
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- after Europe
As with other rare-earth metals, except for lanthanum, europium ignites in air at about 150 to 180°C. Europium is about as hard as lead and is quite ductile. It is the most reactive of the rare-earth metals, quickly oxidizing in air. It resembles calcium in its reaction with water. Bastnasite and monazite are the principal ores containing europium.
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.