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The Louis Berger Group, Inc.
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Edward A. Garvey, PhD, PG
The Louis Berger Group, Inc.
Morristown, NJ
EBC Seminar Series
Part I: Advances in Sediment Site Characterization
September 23, 2011
Using Sediment Tracers to Identify Release
Events, Differentiate Sources, and Assess
Monitored Natural Recovery
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Session Outline
Background on Sediments and Dating
Time Clocks and Horizon Markers
Tracer Examples
Applications
• Current Conditions
• Historical Conditions
• Estimating Natural Recovery
Conclusions
2
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Nature of Sediment and Contamination
4
Increasing energy
Sediment is NOT wet dirt…
• It moves!
Energy changes everything
• ocean vs. lake vs. estuary vs. river
• deep water vs. shoreline
Influence of water
Solids transport
Dissolved phase transport
Partitioning and KD
Diagenesis
Understanding time of deposition
deconvolves impacts of energy
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How Do We Establish Time of Deposition?
(1)
6
Established principals for geological dating can be
applied to recent deposition as well.
Geologist’s Time Keepers (Clocks)
• Radioisotope Clocks (Isotope , half-life)
Age of the universe (Th232, 1010 yrs)
Age of the earth (U-238, 109 yrs)
Age of the dinosaurs (U/Pb, 108 yrs)
Age of the ice ages (U-234, 105 yrs, Th-230, 104 yrs)
Age of the Egyptians (C-14, 103 yrs)
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How Do We Establish Time of Deposition?
(2) Geological Marker Horizons
• Banded Iron Formations
Appearance 3,800 My
Disappearance 1,700 My
• Fossils (trilobites) (530-250 My)
Appearance 530 My
Disappearance 250 My
• Iridium maximum
End of the dinosaurs 65 My
7
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How Do We Establish Time of Deposition?
Environmental Geochemist’s Tools
Radioisotope Time Clocks
• Be-7 (53 days)
• Pb-210 (Excess) (22 yrs)
Horizon Markers
• Appearance of DDT (~1940)
• Bomb Radiocesium (Cs-137)
Appearance 1954
Maximum 1963
• Soda Can Tabs (1960-1975)
• Appearance of PBDEs (1970s)
• Appearance of Fluorinated Surfactants (PFOA/PFOS) -appearance 1950s,
max ~2000
• Appearance of Quaternary Ammonium Surfactant (ATMAC-22) ~1990
8
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Beryllium-7 as a Radiotracer
Half life of 53 days
Highly particle reactive
Effective Partition Coefficient >104
Tags recently deposited sediment
Typically limited to upper 2 to 3 centimeters in
sediment
Sediments containing Be-7 are considered very
recently deposited, <1 year.
9
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Atmospheric Production
Be-7
Sediment
Resuspension
and new solids
entering the
system
Be-7 Tidal Transport
and Redeposition
Particle Reactive
Sediment Bed
Water Column
Upland Sources
Deposition
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CESIUM-137 CORE DATING
Three Deposition Rate Formulas:
Dep
th
1963 Peak
1954 Appearance
Cesium-137 (pCi/g)
2005, year of
collection
Rate 3 = Depth of Appearance –Depth of Peak
(1963– 1954)
3
Ideally the
same rate
Ideally the
same rate
Rate 2 = Depth of Cs137 Peak
(Time of core collection – 1963)
2
Rate 1 = Depth of Cs137 Appearance
(Time of core collection – 1954)
1
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Chemical Marker Examples
DDT first appearance circa 1940
Fluorinated Surfactants (PFOA/PFOS)-appearance
1950s, max ~2000
PBDE first appearance circa 1978, max 2000 to
present
PBB first appearance circa 1970, max 1980, decline
to present
Appearance of Quaternary Ammonium Surfactant
22 (ATMAC-22) ~1990
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Chemical Marker Examples
15
Poly Brominated Diphenyl Ethers Poly Brominated Biphenyls
From Zhu, et al., 2005
PBB-153
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Quaternary Ammonium Surfactants
ATMAC 22 provides an indicator of post 1990
deposition
16
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Idealized
Dated Core
17
Excess
Pb-210
Concentration
Dep
th
Year of collection
1 Year prior
1990
Cs-137
1963
1954
1978
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Use of Beryllium-7 to Identify Current Spatial Trends
17-mile long
estuary
RM 0 RM 17
Tidal Estuary Example
Inflow
Tidal Currents
Dam
Major Tidal
Exchange
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Use of Beryllium-7 to Identify Current Spatial Trends
Four studies of 2,3,7,8-TCDD and 4,4-DDE.
Tidal Estuary Example
1995 0-6 inch sample
2008 0-6 inch sample
2009 0-6 inch sample
2008 0-1 inch sample
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2,3,7,8-TCDD vs. Distance along Estuary
0.1
1
10
100
1000
10000
100000
0.0 2.0 4.0 6.0 8.0 10.0 12.0 14.0 16.0 18.0
2,3
,7,8
-TC
DD
Co
ncen
trati
on
(n
g/k
g)
River Mile
To the Sea
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4,4’-DDE vs. Distance along Estuary
0.1
1
10
100
1000
0.0 2.0 4.0 6.0 8.0 10.0 12.0 14.0 16.0 18.0
4,4
'-D
DE
Co
ncen
trati
on
(u
g/k
g)
River Mile
To the Sea
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Approximately 200-mile long river
Hudson River Example
Inflow Tidal
Exchange
4l
Cesium-137 Core Dating
Tidal Currents One directional
freshwater flow
Inflow
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Circa 1970 Peak Identified all the way to RM 0
Similar Recovery Rates Post 1980
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Cesium-137 Core Dating
17-mile long
estuary
RM 0 RM 17
Tidal Estuary Example
Inflow
Tidal Currents
Dam
Major Tidal
Exchange
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Cs-137 Profiles Permit Comparisons
across the Entire Length of the Estuary
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Depth to Cs-137 Maximum
3 ft 7 ft 13 ft 2 ft 4 ft
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1950
1955
1960
1965
1970
1975
1980
1985
1990
1995
2000
2005
0.001 0.01 0.1 1 10
Ap
pro
xim
ate
Ye
ar o
f D
ep
ositio
n
2,3,7,8 - TCDD (ug/kg)
Historical Dioxin Levels were Extremely High
Non-contiguous
core segment
1975
1980
1985
1990
1995
2000
2005
0.1 1 10
Ap
pro
xim
ate
Ye
ar o
f D
ep
ositio
n
2,3,7,8 - TCDD (ug/kg)
RM 1.4
RM 2.2
RM 7.8
RM 11
RM 12.6
2007
27
1975
1980
1985
1990
1995
2000
2005
0.1 1 10
Ap
pro
xim
ate
Ye
ar o
f D
ep
ositio
n
2,3,7,8 - TCDD (ug/kg)
RM 1.4
RM 2.2
RM 7.8
RM 11
RM 12.6
. . . but Recent Levels are Declining Slowly at Best
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Dated Sediment Cores Permit Forensic Analysis
of Historical Deposition and Sources
1935
1945
1955
1965
1975
1985
1995
2005
0.00 0.20 0.40 0.60 0.80 1.00 1.20
Ratio 2,3,7,8 - TCDD to Total TCDD
Depth
(R
epre
sente
d b
y Y
ear)
RM 1.4
RM 2.2
RM 7.8
RM 11
RM 12.6
Ap
pro
xim
ate
Year
of
Dep
osit
ion
Ratio
of ~0.7
28
Dioxin ratios have changed
only marginally over time.
Original source material is
largely unchanged.
But…Recent
release has
identifiably
different
signature..
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Dep
th (
repre
sen
ted b
y ye
ars
)
Peak Total PCB
Load 1960s
Decline in Total PCB Load
1970s-Present
4i
Cesium-137 Core Dating
Establishing The Current Rate of Recovery
Total PCB Concentration (ug/kg))
Rate of recovery is
equivalent to a 25
year half life.
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Conclusions Sediments are a complex media in an energetic
environment.
Sufficient tracers are available to establish time of
deposition for the last 50 to 100 years, with a resolution of
10 years or less.
Establishing time of deposition permits comparisons across
large spatial scales and avoids natural “noise.”
Particle-bound contaminant histories are recorded in the
sediment and can be readily established.
Current conditions can be easily and inexpensively
established using the right tracers and sampling techniques.
The contaminant record provides a basis for forensic
analysis and can be used to establish the current rates of
recovery.
30