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Nuclear Forensics Summer School Radiochemical separations and quantification. Aqueous chemical behavior of key radionuclides Oxidation state variation Solution phase speciation General separations Ion exchange/column chromatography Solvent extraction Precipitation/carrier Quantification
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Nuclear Forensics Summer SchoolRadiochemical separations and quantification • Aqueous chemical behavior of key radionuclides • Oxidation state variation • Solution phase speciation • General separations • Ion exchange/column chromatography • Solvent extraction • Precipitation/carrier • Quantification • Radiochemical methods • Spectroscopic • BOMARC example (at a later date) • Provide basis for linking chemical behavior with separations • Provide range of techniques suitable for quantification of radionuclides
Radionuclides of interest • Can differentiate fissile material and neutron energetics from fission products • A near 90 (Sr, Zr), 100 (Tc) and 105 (Pd) • Mass 110-125 (Pd, Ag, Cd, In, Sn, Sb) • Lanthanides (140 < A < 150) • Actinides • Polonium 235U fission yield
Fundamentals of separations • Oxidation state • Elements of different oxidation states easier to separate • Anionic and cationic speciation • UO22+,TcO4- • Variation of oxidation state • Addition of reductants/oxidants to control speciation • Method for separation of Pu from U • Varied stability of oxidation states
Fundamentals of separation • Ion size • Concentration of counter anion • Can form anionic species • ThCl4and PuCl5- will behave differently • Counter anion can effect overall charge • Varied by acid concentration or addition of salt • Ionic size difference basis of lanthanide separations
Chromatography Separations • Sample dissolution • Adjustment of solution matrix • Based on column chemistry and other elements in solution • Retention of target radionuclide on column • Removal of other elements • Solution adjustment • Acid concentration, counter ion variation • Addition of redox agent • Elute target radionuclide • Can include addition of isotopic tracer to determine yield • Chemical behavior measured by distribution
Solvent Extraction • Two phase system for separation • Sample dissolved in aqueous phase • Normally acidic phase • Aqueous phase contacted with organic containing ligand • Formation of neutral metal-ligand species drives solubility in organic phase • Organic phase contains target radionuclide • May have other metal ions, further separation needed • Variation of redox state, contact with different aqueous phase • Back extraction of target radionuclide into aqueous phase • Distribution between organic and aqueous phase measured to evaluate chemical behavior
Sr separations • Sr only as divalent cation • Isotopes • 88 (stable), 89 (50.5 d), 90 (28.78 a) • 90Sr/90Y (3.19 h for metastable, 2.76 d) can be exploited • Eichrom Sr Resin • 1.0 M 4,4'(5')-di-t-butylcyclohexano 18-crown-6 (crown ether) in 1-octanol
Sr separation • 8 M nitric acid, k' is approximately 90 • falls to less than 1 at 0.05 M nitric acid • Tetravalent actinide sorption can be limited by addition of oxalic acid • 90Sr determined by beta counting
Technetium separation • Exploit redox chemistry of Tc • TcO4- in aqueous phase • Separation from cations in near neutral pH solution • Anion exchange methods • Interference from other anions • Nitrate • Use Tc redox chemistry • Remove nitrates • Precipitate Tc (tetrabutylamonium) • Solvent extraction • UREX (i.e., 1 M HNO3, 0.7 M AHA) • UO22+ and TcO4- extracted • Back extraction (pH 2 acid), separate
Mass 110-125 (Pd, Ag, Cd, In, Sn, Sb) • Noble metals to group 15 • Divalent Pd and Cd • Monovalent Ag • Trivalent In • Sndi- and tetravalent • Sb stable as trivalent, pentavalent • Separation by changing conditions to target specific elements
HDEHP Pd to Sb • Extraction with HDEPH • Vary aqueous phase • Basic (pH 10) • Citric acid at pH 8 • 6 M HNO3 • Elements into different fractions
In, Sn, and Sb • Extraction with HCl and HI • Control of redox chemistry to enhance separations • Varied organics • Isoamyl acetate, benzene
In, Sn, and Sb • The extraction behavior of In, Sn and Sb in HI and HCl examined • Extraction of Sb(V) from Sn(IV) in 7 M HCl solution with isoamylacetate. • Selective removal of Sn(IV) or In (III) from Sb(V) by extraction into benzene or isopropylether from HI
Polonium • Essentially tracer chemistry due to short half-life of isotopes • 206Po 8.8 d EC to 206Bi; α to 202Pb • 207Po 5.80 h EC to 207Bi; α to 203Pb • 208Po 2.898 y EC to 208Bi; α to 204Pb • 209Po 102 y EC to 209Bi; α to 205Pb • 210Po 138.38 d α to 206Pb • Range of separations from environmental samples • Sediment • seawater
Polonium extraction • From aqueous α-hydroxyisobutyric acid • Varied organic phase • dioctyl sulphide, Cyanex 272, Cyanex 301 or Cyanex 302 in toluene • 2 mL each phase
Polonium extraction • Extraction of Po from 1M α-HIBA increases • Cyanex 272 < DOS < Cyanex 302 < Cyanex 301 • Extraction of Po with 1M extractants without α-HIBA aqueous phase • DOS < Cyanex 301 < Cyanex 302 < Cyanex 272.
Lanthanides • Size separations • Lanthanide and actinide by elution with ammonium a-hydroxyisobutyrate from Dowex 50-X4 resin columns • pH variation • Determination of peak position with pH
Lanthanides HDEHP separations • Ln separation by HPLC using Di-(2-ethylhexyl) phosphoric acid (HDEHP) coated reverse phase column • a-hydroxy isobutyric acid for elution
Th Solution chemistry • Only one oxidation state in solution • Th(III) is claimed • Th4+ + HN3 Th3+ +1.5N2 + H+ • IV/III greater than 3.0 V • Unlikely based on reduction by HN3 • Claimed by spectroscopy • 460 nm, 392 nm, 190 nm, below 185 nm • Th(IV) azido chloride species • Structure of Th4+ • Around 11 coordination • Ionic radius 1.178 Å • Th-O distance 2.45 Å • O from H2O
Solution chemistry • Thermodynamic data • Eº= 1.828 V (Th4+/Th) • ΔfHº= -769 kJ/mol • ΔfGº= -705.5 kJ/mol • Sº= -422.6 J/Kmol • Hydrolysis • Largest tetravalent actinide ion • Least hydrolyzable tetravalent • Can be examined at higher pH, up to 4 • Tends to form colloids • Discrepancies in oxide and hydroxide solubility • Range of data • Different measurement conditions • Normalize by evaluation at zero ionic strength
Solution chemistry • Complexing media • Carbonate forms soluble species • Mixed carbonate hydroxide species can form • Th(OH)3CO3- • 1,5 • Phosphate shown to form soluble species • Controlled by precipitation of Th2(PO4)2(HPO4).H2O • logKsp=-66.6
Complexation • Inorganic ligands • Fluoride, chloride, sulfate, nitrate • Data is lacking for complexing • Re-evaluation based pm semiemperical approach • Interligand repulsion • Decrease from 1,4 to 1,5 • Strong decrease from 1,5 to 1,6 • Organic ligands • Oxalate, citrate, EDTA, humic substance • Form strong complexes • Determined by potentiometry and solvent extraction • Choice of data (i.e., hydrolysis constants) impacts evaluation
Th analytical methods • Low concentrations • Without complexing agent • Indicator dyes • Arzenazo-III • ICP-MS • Radiometric methods • Alpha spectroscopy • Liquid scintillation • May require preconcentration • Need to include daughters in evaluation
Th ore processing • Main Th bearing mineral is monazite • Phosphate mineral • strong acid for dissolution results in water soluble salts • Strong base converts phosphates to hydroxides • Dissolve hydroxides in acid • Th goes with lanthanides • Separate by precipitation • Lower Th solubility based on difference in oxidation state • precipitate at pH 1 • A number of different precipitation steps can be used • Hydroxide • Phosphate • Peroxide • Carbonate (lanthanides from U and Th) • U from Th by solvent extraction
Pa Solution chemistry • Both tetravalent and pentavalent states in solution • No conclusive results on the formation of Pa(III) • Solution states tend to hydrolyze • Hydrolysis of Pa(V) • Usually examined in perchlorate media • 1st hydrolyzed species is PaOOH2+ • PaO(OH)2+ dominates around pH 3 • Neutral Pa(OH)5 form at higher pH • Pa polymers form at higher concentrations • Constants obtained from TTA extractions • Evaluated at various TTA and proton concentrations and varied ionic strength • Fit with specific ion interaction theory • Absorption due to Pa=O
Solution chemistry • Pa(V) in mineral acid • Normally present as mixed species • Characterized by solvent extraction or anion exchange • Relative complexing tendencies • F->OH->SO42->Cl->Br->I->NO3-≥ClO4- • Nitric acid • Pa(V) stabilized in [HNO3]M>1 • Transition to anionic at 4 M HNO3 • HCl • Precipitation starts when Pa is above 1E-3 M • Pa(V) stable between 1 and 3 M • PaOOHCl+ above 3 M HCl • HF • High solubility of Pa(V) with increasing HF concentration • Up to 200 g/L in 20 M HF • Range of species form, including anionic
Solution chemistry • Sulfuric acid • Pa(V) hydroxide soluble in H2SO4 • At low acid (less than 1 M) formation of hydrated oxides or colloids • At high acid formation of H3PaO(SO4)3
Solution chemistry • Redox behavior • Reduction in Zn amalgam • Electrochemistry methods • Pt-H2 electrode • Acidic solution • Polarographic methods • One wave • V to IV • Calculation of divalent redox • Pa(IV) solution • Oxidized by air • Rate decreases in absence of O2 and complexing ions
Solution chemistry • Pa(IV) • Precipitates in acidic solutions • i.e., HF • Spectroscopy • 6d15f1 • Peak at 460 nm
Pa Analytical methods • Radiochemical • Alpha and gamma spectroscopy for 231Pa • Beta spectroscopy for 234Pa • Overlap with 234Th • Activation analysis • 231Pa(n,g)232Pa, 211 barns • Spectral methods • 263 lines from 264 nm to 437 nm • Microgram levels • Electrochemical methods • Potentiometric oxidation of Pa(V) • Absorbance • Requires high concentrations • Arsenazo-III • Gravimetric methods • Hydroxide from precipitation with ammonium hydroxide
Pa Preparation and purification • Pa is primarily pentavalent • Pa has been separated in weighable amounts during U purification • Diethylether separation of U • Precipitation as carbonate • Use of Ta as carrier • Sulfate precipitation of Ra at pH 2 • Inclusion of H2O2 removes U and 80 % of Pa • Isolated and redissolved in nitric acid • Pa remains in siliceous sludge • Ability to separate Pa from Th and lanthanides by fluoride precipitation • Pa forms anionic species that remain in solution • Addition of Al3+ forms precipitate that carriers Pa
Pa purification • Difficult to separate from Zr, Ta, and Nb with macro amounts of Pa • Precipitation • Addition of KF • K2PaF7 • Separates Pa from Zr, Nb, Ti, and Ta • NH4+ double salt • Pa crystallizes before Zr but after Ti and Ta • Reduction in presence of fluorides • Zn amalgam in 2 M HF • PaF4 precipitates • Redissolve with H2O2 or air current • H2O2 precipitation • No Nb, Ta, and Ti precipitates • Silicates • K, Na silicates with alumina
Pa purification • Ion exchange • Anion exchange with HCl • Adhere to column in 9-10 M HCl • Fe(III), Ta, Nb, Zr, U(IV/VI) also sorbs • Elute with mixture of HCl/HF • HF • Sorbs to column • Elute with the addition of acid • Suppresses dissociation of HF • Lowers Kd • Addition of NH4SCN • Numerous species formed, including mixed oxide and fluoride thiocyanates
Pa purification • Solvent extraction • At trace levels (<1E-4 M) extraction effective from aqueous phase into a range of organics • Di-isobutylketone • Pa extracted into organic from 4.5 M H2SO4 and 6 M HCl • Removal from organic by 9 M H2SO4 and H2O2 • Di-isopropylketone • Used to examine Pa, Nb, Db • Concentrated HBr • Pa>Nb>Db • Dimethyl sulfoxide
Pa purification • TTA • 10 M HCl • PaOCl63- • With TBP, Tri-n-octylphosphine oxide (TOPO), or triphenylphosphine oxide (TPPO) • Triisooctylamine • Mixture of HCl and HF • 0.5 M HCl and 0.01 M HF • Used to examine the column extraction • Sorbed with 12 M HCl and 0.02 M HF • Elute with 10 M HCl and 0.025 M HF, 4 M HCl and 0.02 M HF, and 0.5 M HCl and 0.01 M HF • Extraction sequence Ta>Nb>Db>Pa
Pa purification • Aliquat 336 • Methyl-trioctylammonium chloride • Extraction from HF, HCl, and HBr
Uranyl chemical bonding • Bonding molecular orbitals • sg2 su2 pg4 pu4 • Order of HOMO is unclear • pg<pu<sg<< suproposed • Gap for s based on 6p orbitals interactions • 5fd and 5ff LUMO • Bonding orbitals O 2p characteristics • Non bonding, antibonding 5f and 6d • Isoelectronic with UN2 • Pentavalent has electron in non-bonding orbital
f orbitals From LANL Pu chemistry