actinide chemistry and repository science program in ......ans 14th biennial topical meeting la-ur...
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ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Actinide Chemistry and Repository Science Program in support of the Waste Isolation
Pilot Plant (WIPP)
J-F Lucchini M Borkowski MK Richmann and DT Reed
Los Alamos National Laboratory EES Carlsbad Operations
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
DOE weapons complex The WIPP is located in southeastern New Mexico 26 miles east of Carlsbad Waste disposal operations began on March 26 1999
The Waste Isolation Pilot Plant WIPP a cornerstone of the DOE s cleanup effort is designed to permanently dispose of defense-generated transuranic radioactive waste from research and production activities in the
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Transuranic waste is shipped to the WIPP from many generator and storage sites such as Savannah River Site Oak Ridge Argonne Rocky Flat Idaho Nevada Test Site Livermore and Los Alamos All shipments are done using specially designed TRUPAC-II containers
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Disposal rooms are excavated in an ancient stable salt formation 2150 feet (almost one-half mile) underground Transuranic waste which consists of clothing tools rags debris andother disposable items contaminated with radioactive elements mostly plutonium are emplaced in 55 gallon steel drums for permanent disposal
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Waste and magnesium oxide are placed in a WIPP Disposal Room On March 23 2006 the amount of 76156 containers are disposed in the underground
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Center an institute that is operated by New Mexico State University Our most important purpose is to provide laboratory research andprogram support on actinide-related issues to the DOE Carlsbad Field Office (CBFO) to maintain the certification of the WIPP Additionally we have the capability to conduct research programs in actinide environmental chemistry for other sponsors
The Actinide Chemistry and Repository Science Program (ACRSP) is part of a larger multi-disciplinary Los Alamos group (EES-12) working in Carlsbad We conduct our laboratory research programs at the Carlsbad Environmental Monitoring and Research
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove boxes with controlled atmosphere
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
DOE weapons complex The WIPP is located in southeastern New Mexico 26 miles east of Carlsbad Waste disposal operations began on March 26 1999
The Waste Isolation Pilot Plant WIPP a cornerstone of the DOE s cleanup effort is designed to permanently dispose of defense-generated transuranic radioactive waste from research and production activities in the
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Transuranic waste is shipped to the WIPP from many generator and storage sites such as Savannah River Site Oak Ridge Argonne Rocky Flat Idaho Nevada Test Site Livermore and Los Alamos All shipments are done using specially designed TRUPAC-II containers
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Disposal rooms are excavated in an ancient stable salt formation 2150 feet (almost one-half mile) underground Transuranic waste which consists of clothing tools rags debris andother disposable items contaminated with radioactive elements mostly plutonium are emplaced in 55 gallon steel drums for permanent disposal
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Waste and magnesium oxide are placed in a WIPP Disposal Room On March 23 2006 the amount of 76156 containers are disposed in the underground
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Center an institute that is operated by New Mexico State University Our most important purpose is to provide laboratory research andprogram support on actinide-related issues to the DOE Carlsbad Field Office (CBFO) to maintain the certification of the WIPP Additionally we have the capability to conduct research programs in actinide environmental chemistry for other sponsors
The Actinide Chemistry and Repository Science Program (ACRSP) is part of a larger multi-disciplinary Los Alamos group (EES-12) working in Carlsbad We conduct our laboratory research programs at the Carlsbad Environmental Monitoring and Research
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove boxes with controlled atmosphere
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Transuranic waste is shipped to the WIPP from many generator and storage sites such as Savannah River Site Oak Ridge Argonne Rocky Flat Idaho Nevada Test Site Livermore and Los Alamos All shipments are done using specially designed TRUPAC-II containers
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Disposal rooms are excavated in an ancient stable salt formation 2150 feet (almost one-half mile) underground Transuranic waste which consists of clothing tools rags debris andother disposable items contaminated with radioactive elements mostly plutonium are emplaced in 55 gallon steel drums for permanent disposal
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Waste and magnesium oxide are placed in a WIPP Disposal Room On March 23 2006 the amount of 76156 containers are disposed in the underground
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Center an institute that is operated by New Mexico State University Our most important purpose is to provide laboratory research andprogram support on actinide-related issues to the DOE Carlsbad Field Office (CBFO) to maintain the certification of the WIPP Additionally we have the capability to conduct research programs in actinide environmental chemistry for other sponsors
The Actinide Chemistry and Repository Science Program (ACRSP) is part of a larger multi-disciplinary Los Alamos group (EES-12) working in Carlsbad We conduct our laboratory research programs at the Carlsbad Environmental Monitoring and Research
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove boxes with controlled atmosphere
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Disposal rooms are excavated in an ancient stable salt formation 2150 feet (almost one-half mile) underground Transuranic waste which consists of clothing tools rags debris andother disposable items contaminated with radioactive elements mostly plutonium are emplaced in 55 gallon steel drums for permanent disposal
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Waste and magnesium oxide are placed in a WIPP Disposal Room On March 23 2006 the amount of 76156 containers are disposed in the underground
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Center an institute that is operated by New Mexico State University Our most important purpose is to provide laboratory research andprogram support on actinide-related issues to the DOE Carlsbad Field Office (CBFO) to maintain the certification of the WIPP Additionally we have the capability to conduct research programs in actinide environmental chemistry for other sponsors
The Actinide Chemistry and Repository Science Program (ACRSP) is part of a larger multi-disciplinary Los Alamos group (EES-12) working in Carlsbad We conduct our laboratory research programs at the Carlsbad Environmental Monitoring and Research
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove boxes with controlled atmosphere
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Waste and magnesium oxide are placed in a WIPP Disposal Room On March 23 2006 the amount of 76156 containers are disposed in the underground
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Center an institute that is operated by New Mexico State University Our most important purpose is to provide laboratory research andprogram support on actinide-related issues to the DOE Carlsbad Field Office (CBFO) to maintain the certification of the WIPP Additionally we have the capability to conduct research programs in actinide environmental chemistry for other sponsors
The Actinide Chemistry and Repository Science Program (ACRSP) is part of a larger multi-disciplinary Los Alamos group (EES-12) working in Carlsbad We conduct our laboratory research programs at the Carlsbad Environmental Monitoring and Research
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove boxes with controlled atmosphere
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Center an institute that is operated by New Mexico State University Our most important purpose is to provide laboratory research andprogram support on actinide-related issues to the DOE Carlsbad Field Office (CBFO) to maintain the certification of the WIPP Additionally we have the capability to conduct research programs in actinide environmental chemistry for other sponsors
The Actinide Chemistry and Repository Science Program (ACRSP) is part of a larger multi-disciplinary Los Alamos group (EES-12) working in Carlsbad We conduct our laboratory research programs at the Carlsbad Environmental Monitoring and Research
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove boxes with controlled atmosphere
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove boxes with controlled atmosphere
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Glove box for high radioactivity operation and LCS (behind)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Hoods for work with low radioactivity samples
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ICP-MS and Dr Mike Richmann as operator
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Lab Capability
ICP-MS designated for Pu and AmPhoto-acoustic spectroscopy with powerful laserXRD (x-ray diffraction)Spectroscopy (Cary 500)Ion ChromatographyCO2 analysis (down to ppb level)Liquid Scintillation CountingGlove boxes with controlled atmosphere (lt01 ppm O2)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The Actinide Chemistry and Repository Science Program (ACRSP) is conducted according to five Test Plans approved by CBFO
SolubilityStability of Uranium (VI) in WIPPbull Solubility of U(VI) in WIPP brine bull Redox stability of U(VI) in WIPP brine bull Effect of radiolytic products on uranium
speciation
Plutonium (VI) Reduction by Ironbull Limited scope - confirmatory study on effect of various
form of iron iron oxide on plutonium redox reaction
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Neodymium (III) Solubility in WIPP Brinebull Solubility of Nd(III) in WIPP brine an analog for
Am(III) and Pu(III) studied as a function of pCH+and carbonate concentration and measured from over-saturation and under-saturation
Americium SolubilityStability in WIPP Brinebull Solubility of Am(III) in WIPP brine
bull Effect of radiolytic products and repository components on americium oxidation and stabilitysolubility of Am higher oxidation states at the repository conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Plutonium Speciation and Solubility in the WIPPbull Technical assessment of the current WIPP
Database on Pubull Relevance of Pu(III) in the WIPPbull Solubility of Pu(IV) in the WIPPbull Reduction of Pu(V0 and Pu(VI) in the WIPPbull Speciation of plutonium in the WIPP
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
1 Effect of radiolytic products of brine microbial activity and repository components on redox speciation of plutonium americium and uranium
2 Solubility of transuranium elements in WIPP brine (effect of pCH+ carbonate organic ligands etc)
Two major programmatic groups can be distinguished
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Brine Composition Used in Actinide Solubility StudiesERDA-6 GWB MgCl2simplified
NaCl simplified
Component gL ML gL ML gL ML gL MLNaCl 2486 4254 1678 2874 2922 50
MgCl26H2O 3667 0018 1934 0953 7519 3704
Na2SO4 2252 0159 2361 0166
NaBr 1074 0010 2565 0025Na2B4O710H2O 57 0015 1403 0037
KCl 6869 0092 3257 0437
LiCl - - 0174 0004
CaCl22H2O 1672 0011 1896 0013
Ionic strength 4965 M 6839 M 111 M 50 MDensity gmL 1183 1216 1252 1185
GWB - Generic Weep BrineERDA-6 - Energy Research and Development Administration Well 6
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Stability of H2O2 and OCl- in brine
0 20 40 60 80 100 120 140 160 18000
01
02
03
04
05
06
07
08
09
Abs
orba
nce
at 3
51 n
m
Time hours
GWB at pcH = 85 y = 0836e-0012t
ERDA-6 at pcH = 90 y = 0789e-0075t
Decomposition of H2O2 in brine
250 275 300 325 350 375 400
000
002
004
006
008
010
012
014
016
Abs
orba
nce
(rel
uni
t)Wavelength (nm)
t=0h t=6h t=12h t=18h t=24h t=30h t=36h t=42h t=48h t=54h t=60h t=66h
OCl- in 5 M NaCl
2 OCl- + H2O2 2 Cl- + H2O + O2
OCl- + Br- Cl- + OBr- + hellip
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Dependence of hypochlorite generation as a function of absorbed dose of α radiation and NaCl concentration
0 100 200 300 400 500 6000000
0001
0002
0003
0004
0005
0006
5 m NaCl
4 m NaCl
3 m NaCl
2 m NaCl
H
ypoc
hlor
ite C
once
ntra
tion
M
Dose (kGy)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Primary G-values calculated for different chloride concentrations
0 1 2 3 4 5 6 7 8 9 10 11 12 13000
001
002
003
004
005
006
Hyp
ochl
orite
Sat
urat
ion
M
238Pu Activity CiL
5 M NaCl
0380402044032305002740550235
GClOHGH2O2
Cl-concentration
[M]
Kelm M I Pashalidis IJ Kim Applied Radiation and Isotopes 51 (1999) 637-642
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The presence of Fe0 and Fe2+ resulted in the rapid loss of plutonium from solution In the case of ferric oxide some loss of Pu was noted but residual concentrations remained high and it was (postulated) due to sorption not reductionprecipitation The most complete and rapid loss of Pu occurred for magnetite which was the only iron phase that contained Fe2+ These results show that Fe0 and Fe2+ effectively remove dissolved plutonium from brine
0 100 200 300 400 500 600
0
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
Pu
conc
entra
tion
MTime in hours
Ferric oxide
Fe Powder
Fe Coupon
Magnetite
Reduction of Pu(VI) by Iron and Iron Oxides
Effect of various forms of iron on plutonium (VI) reduction in ERDA-6 brine at pCH+=92 and anoxic conditions
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
The absorption spectrum of the plutonium in GWB brine Since the pH is ~ 9 the plutonium is hydrolyzed (complexed with hydroxide) resulting in a 20 nm shift in the absorption maximum to 851 nm The absorption spectrum of this solution was stable over the three-month period that it was monitored
300 400 500 600 700 800 900
000
002
004
006
008
010
Opt
ical
Den
sity
Wavelength (nm)
Pu(VI) in GWB Brine
Peak at 851 nm is hydrolyzed Pu(VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Solubility of Nd(III) and U(VI)The goal of this research is to provide the experimental data for the solubility of trivalent and hexavalent actinides
In this study neodymium (III) was used as a redox-invariant analog for Am (III) and Pu (III)
The experiments in each approach are conducted in GWB and ERDA-6 as a function of pCH+ and carbonate concentration
Simplified brine 5 M NaCl was used for comparison
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Experimental limitations
The highest concentration of carbonate ion in GWB and ERDA-6 brine before the cloud point was observed was determined to be 2- 4 x 10-2 M
The highest pCH+ before the cloud point was observed was - for Erda-6 was equal to 108 - for GWB brine was equal to 87
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
00 05 10 15 20 250
2
4
6
8
10
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in ERDA-6 Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09998 pcH - 09438
Low pCH+ limit and pCH+ vs pH reading in ERDA-6 brine
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
Low pCH+ limit and pCH+ vs pH reading in GWB brine
00 05 10 15 20 25 30 35 40 45 500
2
4
6
8
0 2 40
2
4
pH re
adin
g
Volume of 100 M HCl mL
BaseAcid Titration in GWB Brine
Buffering by borate
Buffering by sulfate
pH re
adin
g
pCH+ calculated
pH reading vs pcH for HP water
pHread = 09749 pcH - 1229
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6
bull pCH+ range 75 ndash 12
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M and U(VI) was 17x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ERDA-6 cont
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in the under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 2 4 6 8 10 12 14 16 18 20 22 2410-8
10-7
10-6
10-5
10-4
pCH+
- 80 - 90 - 92
N
d C
once
ntra
tion
M
Equilibration Time days
ERDA-6kinetic of equilibration
oversaturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
- oversaturation - undersaturation - trend
Nd
Con
cent
ratio
n M
pCH+
ERDA-6carbonate free system
over- and under-saturation
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 1101E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M
- trend (no carb)
ERDA-6over- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-10
10-9
10-8
10-7
10-6
10-5
10-4
10-3
10-2
uranium detection limit
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=8 pCH+=9 pCH+=10 pCH+=11 pCH+=12
ERDA-6 carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
8 9 10 11 1210-10
10-9
10-8
10-7
10-6
10-5
ERDA-6
uranium detection limit
Ura
nium
con
cent
ratio
n M
pCH+
air atmosphere nitrogen atmosphere
initial uranium concentration
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWBbull pCH+ range 65 ndash 85
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
GWB CONT
bull NdOH(CO3) solid prepared in our lab was used in the under-saturation approach with carbonate
bull Nd(OH)3 solid commercial from Alfa Aesar was used in under-saturation approach without carbonate
bull All carbonate free experiments were conducted in the nitrogen glove box and carbonate ion was removed from the brine prior to the experiment
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
over- under- carbonate - 10-2 M - 10-3 M - 10-4 M - 10-5 M - trend
GWBover- and under-saturation
with carbonates
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
60 65 70 75 80 85 901E-9
1E-8
1E-7
1E-6
1E-5
1E-4
N
d C
once
ntra
tion
M
pCH+
- oversaturation - undersaturation - carbonate trend
GWBover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
0 25 50 75 100 125 15010-7
10-6
10-5
10-4
10-3
Ura
nium
con
cent
ratio
n M
Time Days
pCH+=6 pCH+=7 pCH+=8 pCH+=9
GWB carbonate free
U (VI)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
U (VI)
60 65 70 75 80 85 901E-7
1E-6
1E-5
1E-4
Ura
nium
con
cent
ratio
n M
pCH+
GWBcarbonate free over-saturation
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
5 M NaCl
bull pCH+ range 80 ndash 130
bull Initial carbonate concentrations
0 (carbonate free) 10-5 10-4 10-3 and 10-2 M
bull NdCl3 solution was used as a spike in the over-saturation approach
bull Initial Nd(III) concentration was 5x10-5 M
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
70 75 80 85 90 95 100 105 110 115 120 125 1301E-9
1E-8
1E-7
1E-6
1E-5
1E-4
Nd
Con
cent
ratio
n M
pCH+
- oversaturation - undersaturation - trend
5 M NaClover- and under-saturation
carbonate free
Nd (III)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe solubility experiments are still going on but preliminary conclusions can be madeThe trend in Nd(III) solubility measured as a function of pCH+ in 5 M NaCl is in good agreement with literature data however measured solubility is slightly higher than those reported in lower concentrations of NaCl Nd(III) and U(VI) solubilities are greater in GWB brine than in ERDA-6 brine The neodymium data obtained from over-saturation experiments is very close to data obtained from under-saturation experiments It means that in many cases a steady state was achievedAlmost no effect of carbonate on Nd(III) solubility was observed
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)
ANS 14th Biennial Topical Meeting LA-UR 05-9615 Carlsbad April 3-6 2006
ConclusionsThe following Nd(III) solubilities at pCH+ = 85 were measured
With carbonate No carbonate ERDA-6 2 x 10-8 M 4 x 10-8 MGWB 3 x 10-7 M 3 x 10-7 M
Calculated Estimated with Estimated with Microbial Presence Microbial Absence
Castile Brine 169 x 10-7 M 177 x 10-7 MSalado Formation Brine 307 x 10-7 M 307 x 10-7 M
Brush LH and Xiong Y Actinide Solubility for the WIPP PAB Calculations unpublished analysis (2005)