from diagnosis to real-time monitoring with geophysical … · 2017-03-09 · ohmmapper transmitter...
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From diagnosis to real-time monitoring
with geophysical techniques: Case studies and on-going questions at BRGM for pollution
detection and remediation
Jean-Christophe GOURRY
Geophysical parameters
> Electrical Resistivity • Conduction of electric current in soils
• Mainly due to ionic species in pore water
> Electrical chargeability • Capacitive effect of soils
• Polarization effects
Coal tar – cokery plant
primary source and plume
0 1000 m
Regional
Water flow
Monitoring wells
N
Drinking water well
3 km
Former coal refinery Plant Coal waste heap
Test Site
Preliminary geophysical works: 2006
4 ERT profiles (1 km long)
A
B
0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 750 800 850 900 950
-80
-60
-40
-20
0
water flow
Water tableBackfill silt
Chalk 1
Chalk 2
NS
E-W ProfilePzW PzN Pz1
Marl
Tar pond
43 m
A B
0 50 100 150 200 250 300 350 400 450 500 550 600 650 700 750 800 850 900 950
-80
-60
-40
-20
0
water flow (?)
Water table
PzW PzC
Tar pond
Backfill silt
Chalk 1
Marl
EW
Chalk 2Plume
N-S ProfilePzS
43 m
C D
D
C
Resistivity (ohm.m)
0.6
0.8
1 1.2
1.4
1.6
1.8
2 2.24 6.3 10 16 25 40 63 100 160
Pollution is conductive
3D interpolation of the 12 ERT profiles
Map at 20-30 m depth
3D ERT under the allotment
Map at 20-30 m depth
Contaminant
plume migration
Contamination
through fractures ?
30 Ohm.m
100 m
Oil spill in Genoa harbour
OhmMapper
Transmitter
Receiver
5m
5m
5m
Electrostatic injection and reception
0 à 20 cm
crude oil
2 m investigation depth
Gravels
Gravels
Brakich water
OhmMapper results
1120 1140 1160 1180 1200 1220 1240 1260 1280 1300 1320 1340 1360 1380 1400 1420 1440 1460 1480 1500
320
340
360
380
400
420
440
460
480
500
520
SIGEMI3 4
5 6
7
10
13
12
17
18
8
9
1
IPLOM
CHIMICO
LABORATORIO
AREA POMPE
INGRESSO
PRODOTTI FINITI
SERBATOIO
DI CONTROLLO
CENTRALE
AREA COMPRESSORI E POMPE
VASCA
SLOP
SPOGLIATOI
INGRESSO
EX AREA AGIP
SMW2
SMW8
SMW7
SMW3
SMW1
SMW6
SMW4SMW5
NMW3
NMW13
NMW4
NMW2
NMW1
NMW6
NMW5
NMW7
NMW14 NMW15
P1
P5
P4
P3
P2
P7
P6
11.522.533.544.555.566.577.588.599.51010.51111.51212.51313.51414.515
Resistivity (Ohm.m)
Bridge
> 20 cm oil over brakish water level (1 m deep)
Pollution
Pollution is resistive
Oxysol : In situ chemical
Oxidation of PAH (coal
refinery wastes)
Experiment description
> Lysimeter • Platform at Homecourt (GISFI)
• Cylinder of 2 m3 (Height = 2m ; Diameter : 1.12 m)
• Filled with tar-contaminated soils from a former cokery plant
• USEPA16 PAH : ~ 1500 mg/kg
• Organic matter : ~ 120 g/kg
16 Non polarizable
potential electrode
16 Metallic current electrode
0.45 m
0.65 m
0.90 m
1.05 m
1.20 m
1.35 m
1.50 m
0.75 m
Resistivimeter
PC
Monitoring Equipments and Fenton’s reagent H2O2 FeSO4
Time Day 5 Day 2 Day 3 Day 4 Day 1
3D Resistivity Tomography / 30 minutes
Injection periods
1.12 m
2 m3 tar contaminated soils
(1500 mg/kg PAH16)
Oxidation
Resistivity variations : (Rho(t) – Rho (t0))/Rho(t0)
Relative variations (%)
Top
-0.5 m
-1 m
-1.5 m
Start Injection #1
0
h
8
h
Stop Injection #1 Start Injection #2
20h
-2 m
Results : variation of resistivity and chargeability
0.45 m
0.90 m
1.35 m
FeSO4 + H2O2
Level 2
- resistivity decrease 100%
- Norm. Charg increase 50%
Level 1
- resistivity decrease 200%
- Norm. Charg increase 200%
No PAH degradation
[PAH] / 4
Oxidation reactions are characterized by
Normalized Chargeability increase
Chlorinated solvent
pumping tests
Chlorinated Solvents Pumping monitoring with electrical
Resistivity Tomography
18
> Site pilote :
• Bassin
• 4 casiers étanchéifiés
• Piézomètres et pompage
> Géophysique :
• Mesures de résistivité
électriques
• Domaine temporel et spatial
• Traverse tout le bassin
• 96 électrodes
Concrete Barriers
(10 m deep)
Pumping wells
Clay layer
Time zero (reference) Electrical Resistivity Tomography
20
Résistivité (Ω.m)
> Chlorinated solvents (DNAPL) = Resistive
pollutant
Injection wells Pumping well
Distance (m)
Altitu
de
(m
)
Distance (m)
Altitu
de
(m
)
012345678
176.5
177
177.5
178
178.5
179
179.5
20/07/2015 12:00 27/07/2015 12:00 03/08/2015 12:00 10/08/2015 11:00 17/08/2015 11:00 24/08/2015 11:00
pumping activity
Water/DNAPL interface (C4D)
Resistivity variation (%)
Altitu
de
(m
)
Distance (m) Distance (m)
Altitu
de
(m
)
Electrical Resistivity Tomography Monitoring
Conclusions
>Diagnosis • No direct detection of pollution with geophysics
• Resistivity contrasts are representative of pollution or
degradation by-products concentration
–Necessary to know site history
–A few boreholes and soil/water analyses to calibrate
resistivity/chargeability
>Monitoring during remediation • Resistivity and chargeability are very sensitive to
–pollution concentration variations during a pure phase Pumping
–Oxidation / reduction reactions plume during Chemical Oxidation
/ Reduction
– Biodegradation reactions due to bacteria activity
On-going works at BRGM
> Calibration of resistivity and chargeability
models at laboratory scale • Relation between resistivity or chargeability and residual
solvents during pumping stages
• Effect of temperature on resistivity and chargeability during tar
viscosity decrease by heating
• Physical modeling of chargeability during chemical oxido-
reduction process
Thanks for your attention