Ytterbium
minorYtterbium has no water regulation and no treatment role; its water chemistry is the shared heavy lanthanide carbonate chemistry, with one Dutch groundwater figure (0.05 µg/L, the low end of the acidic groundwater range) and the curious finding that soft drink syrup adds Yb, Lu and Ce to tap water based beverages.
Typical wastewaters
- rare earth separation and processing (saponification wastewater) Yb³⁺ carried with the whole lanthanide row in ammonia rich separation plant wastewater (ammonia nitrogen 300 to 5,000 mg/L in Chinese saponification wastewater, 2005 estimate) no ytterbium specific concentration read
- coal mine drainage (acid) Yb³⁺ and the YbSO₄⁺ 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
1 · Identity
- Symbol, number
- Yb, 70
- Oxidation states in water
- +3 only (Yb³⁺)
- Note
- The metal's reactions are in the book entry; in water ytterbium shares the trivalent carbonate and phosphate chemistry of the lanthanide row.
2 · Occurrence in water
- Natural sources
- Weathering of monazite and xenotime; heavy lanthanide, carbonate complexed and relatively mobile in alkaline water. Dutch acidic groundwater (pH below 6.2) ranged from 0.05 µg/L for Yb up to 105 µg/L for La.
- Anthropogenic sources
- None read as a point source; soft drink syrup enriched Yb, Lu and Ce in post-mix beverages relative to the tap water (Schmidt 2019). Rare earth separation wastewater carries the whole row.
| matrix | typical range | note |
|---|---|---|
| seawater | 0.69 to 7.00 pmol/Lone station | western Pacific, 3 to 5663 m; concentrations rise with depth |
| groundwater, acidic (pH below 6.2) | 0.05 µg/L1991 data, one figure | the ytterbium value at the low end of the Dutch acidic groundwater range |
| 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 Yb³⁺ 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 YbSO₄⁺ 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 YbCO₃⁺ and Yb(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.
| condition | dominant species | note |
|---|---|---|
| acid mine drainage and acidic groundwater, pH below 5 | Yb³⁺, YbSO₄⁺ | 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 | YbCO₃⁺, Yb(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 | YbPO₄ (s) as a hydrated phosphate | REE phosphate solubility products can be as low as 10⁻25 (RIVM report citing Liu and Byrne 1997) |
- 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 ytterbium solid was read this session.
- Hydrolysis
- Hydrolysis of Yb³⁺ is minor in natural water; the hydroxide Yb(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
- YbPO₄ (hydrated phosphate), Yb₂(CO₃)₃, YbF₃ near fluoride rich discharges, Yb(OH)₃ at high pH; co-precipitated on iron, aluminium and manganese hydroxides.
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 | ytterbium is in the element list of ISO 17294-2 (catalogue abstract) |
| 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.
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 anywhere read; no acute or chronic human toxicity data for this element 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; Yb 6,607); 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 ytterbium: the RIVM report set risk limits only for Y, La, Ce, Pr, Nd, Sm, Gd and Dy. The one ytterbium number it carries is a field bioconcentration factor in amphipods of 6,607 (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.
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 ytterbium toxicity test 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
Schmidt, K., Bau, M., Merschel, G. and Tepe, N., Anthropogenic gadolinium in tap water and in tap water-based beverages from fast-food franchises in six major cities in Germany, Science of the Total Environment 687 (2019) 1401 to 1408 (abstract, PubMed 31412473)
US EPA, Rare Earth Elements: A Review of Production, Processing, Recycling, and Associated Environmental Issues, EPA 600/R-12/572 (December 2012), sections 4.5.1, 4.5.2 and 6.1.1
Identity
- Name and symbol
- Ytterbium, Yb
- Atomic number
- 70 protons
- Position
- no group (f-block) · period 6 · f-block · lanthanide
- CAS number
- 7440-64-4
Atomic structure
- Atomic mass
- 173.045 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d¹⁰ 5p⁶ 6s² 4f¹⁴
[Xe] 6s²⁴f¹⁴ - Electrons per shell
- 2, 8, 18, 32, 8, 2
- Valence electrons
- 16 ns, (n-1)d and (n-2)f
| isotope | mass (u) | abundance |
|---|---|---|
| 168Yb | 167.933 889(8) | 0.1 % |
| 170Yb | 169.934 767 25(7) | 3 % |
| 171Yb | 170.936 331 52(9) | 14.2 % |
| 172Yb | 171.936 386 66(9) | 21.7 % |
| 173Yb | 172.938 216 22(8) | 16 % |
| 174Yb | 173.938 867 55(8) | 31.8 % |
| 176Yb | 175.942 5747(1) | 12.8 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 1,092 K (818.85 °C)
- Boiling point
- 1,469 K (1,195.85 °C)
- Density
- 6.9 g/cm3
- Appearance
- silvery white; with a pale yellow tint
- Thermal conductivity
- 38.5 W/(m·K)
- Electrical resistivity
- β, poly: 0.250 µΩ·m
- Electrical conductivity
- 4 MS/m
- Crystal structure
- face-centered cubic
- Molar heat capacity
- 26.74 J/(mol·K)
Chemical properties
- Oxidation states
- +3, +2
- Electronegativity
- not in sources
- Ionisation energy
- 6.254 eV
1st 603.4, 2nd 1,174.8, 3rd 2,417 kJ/mol - Electron affinity
- not in sources
- Atomic radius
- empirical 187, covalent 187, van der Waals 242 pm
- Ionic radius
- Yb²⁺ 102; Yb³⁺ 87 pm
- Reactivity
- The lanthanide with the fullest 4f shell (4f14 6s2), so its +2 state is relatively stable and its density and melting point are lower than its neighbours; still an electropositive metal that dissolves quickly in acids, slowly in water, and oxidises slowly in air.
- with water
- Dissolves slowly in cold water and quickly in hot water to the hydroxide and hydrogen: , so it is stored in closed containers.
- with oxygen, air
- Tarnishes slowly in air, taking a golden or brown hue under a protective oxide layer; the finely divided metal oxidises readily and burns: , white ytterbia.
- with acids
- Readily attacked and dissolved by dilute and concentrated mineral acids, liberating hydrogen; in dilute sulfuric acid it gives colourless Yb3+ solutions: , the sulfate.
- with halogens
- Reacts with all the halogens to the white trihalides: , and the trihalides are reduced by hydrogen, zinc or the metal to the dihalides.
- Typical compounds
- Yb₂O₃ ytterbium(III) oxide ytterbia, white oxide, dopant for fibre lasers
- YbCl₃ ytterbium(III) chloride white, soluble trihalide
- YbF₃ ytterbium(III) fluoride white trihalide used in dental composites
- YbCl₂ ytterbium(II) chloride divalent halide made by reducing YbCl3 with hydrogen
- Yb₂(SO₄)₃ ytterbium(III) sulfate colourless salt from sulfuric acid
Occurrence, production and use
- Crustal abundance
- 3.2 milligrams per kilogram
- Oceanic abundance
- 8.2×10-7 milligrams per liter
- Occurrence and sources
Ytterbium occurs along with other rare earths in a number of rare minerals. It is commercially recovered principally from monazite sand, which contains about 0.03%. Ion-exchange and solvent extraction techniques developed in recent years have greatly simplified the separation of the rare earths from one another.
- monazite the principal source, with the other lanthanides
- Extraction, production
- not in sources
- Uses
Ytterbium has few uses. It can be alloyed with stainless steel to improve some of its mechanical properties and used as a doping agent in fiber optic cable where it can be used as an amplifier. One of ytterbium's isotopes is being considered as a radiation source for portable X-ray machines.
Ytterbium metal has possible use in improving the grain refinement, strength, and other mechanical properties of stainless steel. One isotope is reported to have been used as a radiation source substitute for a portable X-ray machine where electricity is unavailable. Few other uses have been found.
- Safety, toxicity
Ytterbium has a low acute toxic rating.
GHS classification, signal word Danger- H228 Flammable solid Flammable solids
- H250 Catches fire spontaneously if exposed to air Pyrophoric liquids
- H252 Self-heating in large quantities; may catch fire Self-heating substances and mixtures
- H302 Harmful if swallowed Acute toxicity, oral
- H312 Harmful in contact with skin Acute toxicity, dermal
- H315 Causes skin irritation Skin corrosion/irritation
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H332 Harmful if inhaled Acute toxicity, inhalation
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
Discovery and name
- Discovered by
- Jean Charles Galissard de Marignac
- Discovered
- 1878
- First isolated
- Wilhelm Klemm and Heinrich Bommer
- Named by
- not in sources
- Origin of the name
- after Ytterby (Sweden), where it was mined
Ytterbium has a bright silvery luster, is soft, malleable, and quite ductile. Even though the element is fairly stable, it should be kept in closed containers to protect it from air and moisture. Ytterbium is readily attacked and dissolved by dilute and concentrated mineral acids and reacts slowly with water. Ytterbium has three allotropic forms with transformation points at -13°C and 795°C: The beta form is a room-temperature, face-centered, cubic modification, while the high-temperature gamma form is a body-centered cubic form. Another body-centered cubic phase has recently been found to be stable at high pressures at room temperatures. The beta form ordinarily has metallic-type conductivity, but becomes a semiconductor when the pressure is increased about 16,000 atm. The electrical resistance increases tenfold as the pressure is increased to 39,000 atm and drops to about 10% of its standard temperature-pressure resistivity at a pressure of 40,000 atm. Natural ytterbium is a mixture of seven stable isotopes. Seven other unstable isotopes are known.
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.