Analysis of Total PCB Content by Reductive
Dechlorination to Biphenyl
John G. Doyle, TeriAnn Miles, Erik Parker,
I. Francis Cheng
Department of Chemistry
University of Idaho
Moscow, Idaho 83844-2343 ifcheng@uidaho.edu
(208) 885-6387
Outline
1.
Short History of PCBs
2.
Present state of PCB analysis
Multi-component – 209 congeners
Associated problems with GC-ECD
3.
Chemical Reaction to Single Species
Carbon Skeleton
Perchlorination
4.
Complete dechlorination at RTP.
Pd/Mg bimetallic particles
Performance with Arochlor
1221
5.
Elimination of Interferences by other Halocarbons
Mixtures of DDT and Arochlor 1260
PCB history
Clx Cly
10
x + y
Industrial uses 1930 – 1977
Dielectric fluids, capacitors and transformers
Printing inks
Paints
Pesticides
Health and Environmental Risks
Occupational exposure (1936)
Bio-accumulative (low water solubility)
Banned by TSCA 1977
EPA policy
Soils: nonrestricted access areas must 10 ppm or less
PCB analyses
Clx
Cly
209 possible congeners
GC-FID of a PCB mixture
Complicating Features
CG-ECD analysis based on pattern recognition of key congener peaks.
1.
Matrix effects
-DDT/DDE metabolites
-Other Halocarbons
2.
Environmental aging
-Different rates of dechlorination for each congener
-Volatility differences for each congener
3.
ECD response
-Varies with each congener
“
Sources and Magnitude of Bias Associated with Determination of
Polychlorinated Biphenyls in Environmental Samples”
Analytical Chemistry ,
1991 , 63 , 2130-2137.
Chemical Reaction of PCBs
To one predominate species
1. Reductive Dechlorination:
Clx
+ 2(x+y) e -
+ (x+y) Cl -
Cly
2. Perchlorination:
Clx
Cly
+ 2 (10-x+y) Cl -
Cl
Cl
Cl
Cl
Cl
Cl
Cl
Cl
Cl
+ (10-x+y) H + + (10-x+y) e -
Cl
Requirements for Chemical Reaction to Single
Species
1.
Reproducible and Quantitative
100% Yield
2.
Rapid
R oom Temperature and Pressure
3.Simple minimal work-up
Literature methods
Reductive Dechlorination:
Procedure Analysis Detection
Limit
150 ng H
2
reduction on Pd catalyst @ 305 0 C
GC-FID
Heated Pd catalysts GC-FID
Na reduction Cl ISE
10 ng
10 mg
LiAlH
4
HPLC UV@248 nm 100 ng
Perchlorination
SbCl
5
@ 205 0 C GC-ECD ?
Most of the above involve extensive procedures.
Rapid reductive dechlorination under mild conditions
1. Standard Reduction Potential of PCBs
Clx
+ 2(x+y) e -
+ (x+y) Cl -
Cly
E 0 red
= 0.5 to 1.0 volts
2. Reducing Agents (aqueous)
Fe
Fe 2+ + 2e -0.44 V
Cr
Cr 3+ + 3e -0.74 V
Mn
Mn 2+ + 2e -1.182 V
Mg
Mg 2+ + 2e -2.36 V
E 0 red
Complete dechlorination of PCB by zero-valent metals is slow.
1.
Most congeners are completely stable in presence of metal reducing agents at RTP.
2.
Requires catalyst.
Pd/Fe bimetallic system*.
2 g, 10
m, 99.9% Fe particles
0.05 % Pd w/w
5 ml 20 ppm Arochlor 1260
(30% MeOH , 20% acetone, 50% water)
Complete dechlorination in 10 minutes
Majority product, biphenyl
*C. Grittini, M. Malcomson, Q. Fernando, N. Korte
Environ. Sci. & Tech., 1995 , 29 , 2898-2900.
Analysis of total PCB by reductive dechlorination with Pd/Mg bimetal.
1.
Mg vs. Fe
Fe surface requires extensive pretreatment
Anaerobic acid washing
Air sensitive
Mg requires no special treatment
2.
Deposition of Pd onto Mg
Untreated 0.5 grams 20 mesh Mg
(98%, Aldrich)
20 mg K
2
PdCl
6
PdCl
6
2 + 2Mg = Pd + 6Cl + 2Mg 2+
Pd
Mg
PCB dechlorination
Analyte solution
3-5 ml of 50/50 v/v 2-propanol/water
1 – 60
M Arochlor 1221
0.5 grams 20 mesh Mg particles
20 mg K
2
PdCl
6
powder
reaction complete in 5 minutes
Preparation for HPLC
syringe filter 0.2 ml of above
Role of Pd in the catalysis of zero-valent metal reduction of halocarbons.
R-H + H + + Cl -
Mg 2+ 2H +
Pd
.
H
Pd island
H
H
R-Cl
Metal surface
2e -
Pd is a catalytic surface for hydrogen evolution
Increases Mg dissolution (galvanic corrosion)
Hydrogen intercalates in bulk Pd
May result in excellent surface for hydrodehalogenation
Pt fails as hydrodehalogenation catalyst
I.F. Cheng, Q. Fernando, N. Korte, Environmental
Science and Technology, 1997, 31 (4) 1074-1078.
Analytical performance of Mg/Pd reductive dechlorination system
HPLC analysis
50 uL sampling loop
UV absorbance detector 200 nm (HP 79853C)
Isocratic 65/35 v/v acetonitrile/water
C-8 Zorbax column
Arochlor 1221 biphenyl content, 3.3%
Biphenyl Calibration Curve
Biphenyl
4.50E+07
4.00E+07
3.50E+07
3.00E+07
2.50E+07
2.00E+07
1.50E+07
1.00E+07 y = 7.95E+11x + 3.59E+05
R
2
= 9.99E-01
5.00E+06
0.00E+00
0.00E+00 1.00E-05 2.00E-05 3.00E-05 4.00E-05 5.00E-05 6.00E-05
Concentration (M)
Biphenyl from Arochlor 1221 dechlorination
Biphenyl From Arochlor 1221 with Mg/Pd
4.50E+07
4.00E+07
3.50E+07
3.00E+07
2.50E+07
2.00E+07
1.50E+07
1.00E+07
5.00E+06 y = 7.76E+11x - 1.53E+06
R
2
= 9.97E-01
0.00E+00
0.00E+00 1.00E-05 2.00E-05 3.00E-05 4.00E-05 5.00E-05 6.00E-05
Concentration (M)
Biphenyl yield = 98% (from slopes)
Chemical Interferences
DDT and major impurities and metabolites
10 major GC-FID peaks
Co-elute with PCBs
DDT
Cl Cl
CCl
3
DDE
Cl Cl
CCl
2
DDO
Cl Cl
CH
3
DDNS
CCl
3
Cl
Reductive dechlorination of DDT/metabolites by
Pd/Mg.
RTP reaction completed in 10 minutes
Only demonstrated method for the complete and rapid dechlorination of DDT at RTP
Procedure as with PCB dechlorination
Cl
Pd/Mg
+ 5 Cl -
CCl
3
CH
3
Major product of DDT/metabolite reductive dechlorination
GC-FID of PCB & DDT mixtures
Illustrates DDT interference
Top 50 ppm PCB (Arochlor 1260) and 50 ppm DDT
Bottom 50 ppm DDT
Pd/Mg Treatment of DDT/PCB mixtures
GC-FID
Conclusions and Future Work
Advantages
PCB reductive dechlorination by Pd/Mg to biphenyl
Rapid (< 5mins)
Reproducible (98% yield)
Detection Limit (no sample preconcentration)
5 x 10 -6 M
100 ppb
5 ng
Disadvantages
Loss of congener specific information
Requires analysis for biphenyl background
Future
Elimination of halocarbon interferences (DDT)
Acknowledgements
Co-authors
John G. Doyle
TeriAnn Miles
Erik Parker
Other Contributors
Mark Engelmann
Kristy Henscheid
Keri Colvin
Roshan Koshravi
Josh Linard
University of Idaho Research start-up funds
Contact Information:
Frank Cheng
Department of Chemistry
University of Idaho
Moscow, Idaho 83844-2343 ifcheng@uidaho.edu
(208) 885-6387