Rare Earth Elements: A Review of Production, Processing ...
Rare Earth Elements: A Review of Production, Processing ...
Rare Earth Elements: A Review of Production, Processing ...
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<strong>Rare</strong> <strong>Earth</strong> <strong>Elements</strong> <strong>Review</strong> Appendix A – Selected Chemical Properties<br />
atomic number; however, bonding is predominantly ionic, even with extra electrons in the d-orbitals <strong>of</strong><br />
some lanthanides.<br />
An important chemical property is that the lanthanides will form strong complexes with a number <strong>of</strong><br />
different ligands. Water is a strong ligand for trivalent (M 3+ ) lanthanides (Weber, 2008). Trivalent (M 3+ )<br />
lanthanides strong affinity for water allows them to form a hydration shell around the Ln 3+ ion. The<br />
number <strong>of</strong> molecules <strong>of</strong> water that a lanthanide ion can bond with in an aqueous solution varies between 8<br />
and 9, depending on the element and species (Weber, 2008). Weber (2008) points out that the basic<br />
physico-chemical properties <strong>of</strong> lanthanides in natural aqueous systems (e.g., interstitial soil water in the<br />
unsaturated zone) depend significantly on the presence <strong>of</strong> other coordinating compounds that can displace<br />
the water molecules from around the lanthanide metal ion.<br />
In aqueous environments, the water ligand would only be displaced if ligands with small ionic radius<br />
were present with a high oxidation state, high electronegativity, and with the highest occupied molecular<br />
orbitals having low energy; examples <strong>of</strong> these chemical species are the hydroxyl anion (OH – ), fluorine<br />
(F – ), chlorine (Cl – ), ammonia (NH 3 ), acetic acid (CH 3 COO – ), carbonic acid (CO3 2– ), nitrate (NO 3- ), sulfate<br />
(SO4 2- ), phosphate (PO4 3- ), oxide (O 2- ), alcohols (R –OH), amines (R-NH2), and others containing highly<br />
electronegative donor atoms such as O and F. These chemical species would tend to form mainly an ionic<br />
bond with the lanthanides molecules within their unoccupied lower high-energy orbitals. Lanthanides<br />
preferentially bond with oxygen atoms in aqueous solutions, but one-to-one bonding between lanthanides<br />
and other compatible ions has been shown to be weak compared to bonding with oxygen or flourine<br />
atoms and easily hydrolyzed by water (Gupta and Krishnamurthy, 2004; Weber, 2008). However,<br />
polydentate ligands, which have multiple pairs <strong>of</strong> electrons that can bond to the lanthanide metal ion, will<br />
form stronger bonds that may be more stable in aquatic environments. In general, the lanthanide ion<br />
preference for donor atoms is O>N>S (Weber, 2008).<br />
At ambient temperatures, all REMs are not affected by air the same way. The ionization energies (or<br />
strength <strong>of</strong> the nuclear charge) <strong>of</strong> lanthanides are comparatively low, meaning it takes less energy to<br />
remove valence electrons. These elements are therefore highly electropositive and, as previously stated,<br />
form compounds that are essentially ionic in nature (Gupta and Krishnamurthy, 2004). Like most metals,<br />
the lanthanides have a gray luster or bright silvery appearance. Five <strong>of</strong> the elements (lanthanum, cerium,<br />
praseodymium, neodymium, and europium) are very reactive. When exposed to the air, they react with<br />
oxygen to form an oxide coating that tarnishes the surface almost immediately. A block <strong>of</strong> europium will<br />
be converted to an oxide in a few days or weeks. Under the same conditions, surface corrosion <strong>of</strong> a<br />
massive block <strong>of</strong> lanthanum or neodymium will occur in a few days, and a thick crust <strong>of</strong> oxide will<br />
develop in a few months.<br />
Analytical Methods<br />
There are a variety <strong>of</strong> methods employed to determine REE concentrations in environmental samples,<br />
such as (1) atomic absorption spectroscopy; (2) neutron activation; (3) isotope dilution thermal ionization<br />
mass spectrometry (ID-TIMS); and (4) inductively coupled plasma-mass spectrometry (ICPMS).<br />
Concentrations <strong>of</strong> REEs in unpolluted freshwater systems typically range in from parts-per-billion (ppb)<br />
to parts-per-trillion (ppt) (Lawrence et al., 2006). Therefore, a pre-concentration step such as ion<br />
exchange chromatography, Fe(OH)3 co-precipitation, or liquid-liquid extraction may be required prior to<br />
analysis. The specific method selected for analysis will provide guidance on sample preparation prior to<br />
analysis (e.g., an EPA 3000 series method).<br />
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