Application of Forensic Chemistry to Environmental · PDF fileApplication of Forensic...
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![Page 1: Application of Forensic Chemistry to Environmental · PDF fileApplication of Forensic Chemistry to Environmental Work Diane L. Saber, Ph.D Gas Technology Institute Environmental Science](https://reader034.fdocuments.net/reader034/viewer/2022052302/5aa458747f8b9a185d8be938/html5/thumbnails/1.jpg)
Application of Forensic Chemistry to
Environmental WorkDiane L. Saber, Ph.D
Gas Technology InstituteEnvironmental Science & Forensic Chemistry Group
Des Plaines, IL, USA
Presented at RemTech 2004Banff, Canada
September 15, 2004
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Outline of Presentation:
> Introduction to GTI> Manufactured Gas Plant Operations – an
environmental problem> Introduction to Forensic Chemistry> Application to a Test Site> Results> Conclusion
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Combustion
Fuel Cells Distributed Generation
GAS TECHNOLOGY INSTITUTE
> Independent, Not-for-Profit R&D Organization– 18-acre campus in Des Plaines, IL– 350,000 ft2 facility– Labs, test facilities, library, classrooms
> Natural Gas Focus> Formed in 1941> 7 Centers
Pipeline Materials
Exploration & Production
GasificationEnvironmental
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Environmental Science & Forensic Chemistry
> R&D Laboratory and Services> Research in:
– Microbiology/Molecular Biology– Chemistry/Geochemistry– Phytoremediation– Biorefining– Remediation Techniques
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“Environmental” means many things in the Gas Utilities Industry
> Greenhouse Gas Production/Mitigation> PCBs associated with Gas
Transmission> Air Quality – Indoor and Outdoor> Operations – Related: Corrosion> MGP Site Cleanups and Long-Term
Management:– Landside– Sediments
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Number of Former MGPs in the United States> The US EPA and others estimate that from 1815 to
1960 over 1,500 MGPs operated in the USA> Number operated at a given time -- difficult to say
1800 1820 1840 1860 1880 1900 1920 1940 1960
0
200
400
600
800
1000
1200
1400
1600
1800
2000
App
roxi
mat
e #
of
Ope
ratin
g M
GP
s
Year
Peaked in 1920(# unknown) ?
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Location of Former MGPs in the United States> Former MGPs are found everywhere the US, in small towns
and large cities, in industrial zones and in relatively rural settings
TX
CA
MT
AZ
ID
NV
NM
COIL
OR
UT KS
WY
IA
NE
SD MN
ND
OK
FL
WI
MO
AL
WA
GA
AR
LA
MI
IN PA
NY
NC
MS
TNKY VA
OH
SC
ME
WV
MI VTNH
MD
MA
Approximate Distribution MGP in 1909By State
1
5
10
50
100
Number of Operating MGPs
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Location of Former MGPs> Some former MGPs are located near waterfronts such as
rivers and lakes
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> “Town Gas” was produced in North America through combustion of coal/oil – produced “Manufactured Gas”
> The process produced “MGP” waste –mostly pyrogenic PAHs (tar-like materials)
> There are many sources of PAH-material in the environment – some look MGP waste
> Detecting PAHs alone can lead to the conclusion that all tar-like waste is from former MGP site.
> A technique was needed to discern PAH sources in the environment: FORENSIC CHEMISTRY
Nature of the Problem
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What is What is ““Chemical FingerprintingChemical Fingerprinting””--Forensic Chemistry?Forensic Chemistry?
It is the technique of analyzing samples and generating chemical “fingerprints”(chromatograms) which are distinctive to a type of waste.
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Chemical Fingerprinting Techniques
> GC/FID – gas chromatography with flame ionization detector
> GC/MS – gas chromatography with mass spectrometry
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Example of a "Example of a "PyrogenicPyrogenicSubstance" Substance" –– MGPMGP--Type TarType Tar
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Example of a "Petrogenic Example of a "Petrogenic Substance" Substance" –– Diesel FuelDiesel Fuel
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Example of Asphalt-Tar
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Example of Gasoline –No Tar Present
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Example of Both MGP-Type Tar & Asphalt Like Tar
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Example of Asphalt-Like Tar & Gasoline
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Difficult Conditions
Sediments Background
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Limitations of GC/FID & GC/MS
> Reliability decreases for:– A sample with multiple sources– Extensively weathered samples– Low-levels of contamination (< 50 ppm)
Coal Tar Coal Tar & Fuel Oil
WeatheredCoal Tar & Fuel Oil
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What is Background for PAHs?The definitions vary!
> Natural background> Anthropogenic background> Regulatory background> Area background> Urban background
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> Natural background– Pre-existing and naturally produced
> Atmospheric fallout– Transportation, heating systems, power
generation, industries
> Fill– Building materials– Debris, ash, trash
> Spills and sprays*** sometimes higher than MGP PAHs ***
Urban Background PAHs
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Isotope Analysis
> Gas chromatography with isotope ratio mass spectrometry (GC/IRMS)
> Measure the stable isotope ratios of individual compounds in complex mixtures (e.g., C, H, S, O)
> Carbon isotope– Two stable isotopes of carbon: 12C & 13C– Naturally occurring ratio of 12C/13C ≈ 99:1
Finnigan Delta + XL
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Compound Specific Carbon Isotope Ratios (CSIRs)
> CSIRs are reported relative to a standard carbon source (in ‰)
> Carbon isotope ratios of PAHs from different hydrocarbon sources are often different
1000C)C/(
C)C/( - C)C/( C δstd
1213std
1213spl
121313 ×⎥
⎦
⎤⎢⎣
⎡=
δ1
3 C(‰
) grasses
woody plants
creosoteMGP
Individual PAHs
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Technical ObjectiveMGP versus urban background using
GC/IRMS
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Background Sampling Design
> Select cities or towns– List and number all populated areas– Use a random number generator to select areas
> Grid placed over a map of each city or town to randomly select sampling sites
> Sites scouted and described> Soil samples collected 0-6”> NAPLs from MGP sites in each city or town
collected
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Sampling Sites
9 sites7 sites
1 site
1 site
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Site Selection Criteria> Sampling sites included:
– Parks and playgrounds– Schools– Roadway medians– Parking lot landscaping– Grounds of government buildings– Utility properties– Commercial properties– Residential properties
> All sites were free of any visual contamination and known PAH sources
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RESULTS: 3 Cities in Midwest USBackground Soils and Tar Reference Samples
RF01
RF06
RF08
RF09
Soil
Crude tar from a steel mill coke plant
T284
T282
NAPL
T185
DA05
DA09
DA10
T283
MT03
MT07
MT09
MT10
NAPLSoil
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Soil (µg/kg) and NAPL (mg/kg) ConcentrationsSample ID BAP NAP Total PAHs TOC (%)
DA05 68.8 11.5 834 2.7DA09 279 16.4 2,880 1.5DA10 3260 304 36,300 3.6MT 03 193 14.9 2,510 3.7MT 07 900 253 11,100 6.7MT 09 247 365 3,880 4.5MT 10 572 79.1 6,940 4.5RF01 372 37.7 3,970 2.8RF06 1760 23.1 15,800 17.0RF08 1500 67 19,100 4.2RF09 240 3.88 2,620 2.4
RF NAPL 1970 29900 90400MT NAPL 1220 33500 89400DA NAPL 1350 16000 52500
T 185 8260 98300 288000
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Background Soil Concentrations
0
5
10
15
20
25
30
35
40
DA05 DA09 DA10 MT03 MT07 MT09 MT10 RF01 RF06 RF08 RF09
Soil Sample
Con
c (m
g/kg
)
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Comparison of CSIRs of NAPL Samples
-30.00
-29.00
-28.00
-27.00
-26.00
-25.00
-24.00
-23.00
-22.00
napmn2mn1
acy
ace dbf flu phe ant fly pyr
baach
rbbkfbap
ip_dba bp
Compound
δ13
C (‰
)
T185RF NAPLMT NAPLDA NAPL
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Comparison of MT Soil and NAPL CSIR Results
-30.00
-29.00
-28.00
-27.00
-26.00
-25.00
-24.00
-23.00
-22.00
napmn2mn1
acy
ace dbf flu phe ant fly pyr
baach
rbbkfbap
ip_dba bp
Compound
δ13C
(‰)
MT03MT07MT09MT10MT NAPL
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Correlation of PAH Patterns to CSIRs
-28-27.5
-27-26.5
-26-25.5
-25-24.5
-24
0 0.2 0.4 0.6 0.8 1 1.2 1.4 1.6
fluoranthene/pyrene
δ13C
(‰) p
yren
e
T185
RF08
RF09RF01RF06
RF NAPL
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Application to a Site
> Former water gas MGP Site near a major lake
> Areas surrounding the properties consist of:– Industrial land– Wastewater treatment plant– Former coal dock with large aboveground fuel oil
storage tanks– Commercial/residential properties
> Soil consists of a few feet of fill overlying native red clay
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Study Design
> 8 soil samples from site (Soils 1-8)> 5 sediment samples from the major lake
near the site (Sediments 1-5)> Analyses
– GC/FID– GC/MS– GC/IRMS
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Chemical Fingerprinting
Soil Sediment
> Soils & Sediments: both pyrogenic & petrogenic sources> But [PAHs] much lower in sediment samples
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Chemical Concentrations: mg/kg
SedimentSoilCompounds
0.15793Fluorene
ND56.2Dibenzofuran
0.28590Acenaphthene
0.091160Acenaphthylene
0.235541-Methylnaphthalene
0.243602-Methylnaphthalene
0.521260Naphthalene
ND1381,2,4-Trimethylbenzene
0.05156o-Xylene
ND241Styrene
0.2185m/p-Xylenes
0.1478.8Ethylbenzene
0.35116Toluene
0.342.3Benzene
SedimentSoilCompounds
0.45951Benzo[g,h,i]perylene
0.07147Dibenz[a,h]anthracene
0.16511Indeno[1,2,3-cd]pyrene
0.09112Perylene
0.37637Benzo[a]pyrene
0.24447Benzo(e)pyrene
0.22453Benzo[k]fluoranthene
0.21305Benzo[b]fluoranthene
0.34518Chrysene
0.32533Benz[a]anthracene
0.771820Pyrene
0.61410Fluoranthene
0.22803Anthracene
0.812670Phenanthrene
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Selected Source Ratios
0.7 0.8 0.9 1.0 1.1 1.2 1.3 1.4
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
Soil 2
Soil 4Soil 1
CWG
Sediment 4
Soil 6Soil 3
Sediment 2
Sediment 5
Soil 8
CO
CO
COCC
CC
Dib
enzo
fura
n/Fl
uore
ne
Fluoranthene/Pyrene
CC - Coal CarbonizationCWG - Carburetted Water GasCO - Coke Oven
CC
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CSIRs
NA
PM
N2
MN
2A
CY
AC
EFL
UP
HE
AN
TFL
YP
YR BA
AC
HR
BB
KF
BaP
IPD
BA
BP
-34-33-32-31-30-29-28-27-26-25-24-23-22
Soil Sediment
δ13 C
(‰)
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Overall Project Results> Chemical fingerprints show that soils on
the site & sediments near the site possess both pyrogenic & petrogenic sources
> Although selected source ratios suggest that pyrogenic substances in the soils & sediments are from CWG tar, the concentrations of PAHs in the sediments are much lower than those of the soils
> CSIRs show that PAH source(s) of the sediments are, in fact, different than those of the soils (e.g., urban runoff)
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Conclusion> Chemical fingerprinting is a powerful tool
for environmental work.> Forensic chemistry has been used for
conclusive waste ownership in soils> Forensic chemistry has applications for
waste ownership in sediments> GC/IRMS techniques are powerful for
background PAH identification> GC/IRMS has application in waste dating,
indoor air quality work, compound fate and transport, weathering, bioavailability and many others
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For further questions, pleasecontact me. Thank you for
your attention.
Diane L. Saber, Ph.D.Director
Office:847-768-0538Fax:847-768-0546
Email: [email protected]