Control of landfill leachates contaminated groundwater by a MULTIBARRIER approach
L. Diels, J. Dries, L. BastiaensFlemish institute for technological research, Vito
Mol, Belgium
NATO-CCMS Pilot StudyPrevention and Remediation in Selected Industrial Sectors:
Rehabilitation of old landfills Cardiff, May 23 – 26, 2004
NATO-CCMS, 11 juli 2004, Cardiff 2004
No measures
Landfill leakage: Multifunctional treatment zone or Multibarrier for removal of mixed pollutants
NATO-CCMS, 21 juli 2004, Cardiff 2004
Evaluation of several combinations– Chemical transformation (Fe°), – Biotransformation (aerobic/anaerobic),– Bioprecipitation– Sorption
Two solutions:
-Installation of a new landfill(20 – 40 million EURO)
-Installation of a MULTIBARRIER(2 - 4 million EURO)
Groundwater flow
GW level
EU-project MULTIBARRIER
NATO-CCMS, 31 juli 2004, Cardiff 2004
Microorganismsbacteria, fungi
Carrier material
Fe 0, Carbon,
Sand
Growth
addi
tives
Nutrien
ts, O
RC, com
post
Mixed pollution
heavy metalsVOCls
aromatics
PARTNERS:
Vito, MolUniversity of WageningenUniversity of InnsbruckTUniversity of MunchenIBA, HeiligenstadtBIOTECs, BerlinUniversity of PragueDEC, ZwijndrechtUniversity of Latvia, RigaUnivesity of Mining, Sofia, Bulgaria
ENDORSERS:Montgomery Watson Harza, BrusselsIntercommunale Hooge Maey, Antwerp
Mixed contamination plumes• Mixed contamination plumes require:
– a combination of different pollutant removal processes (biotic & physico-chemical)– a combination of barrier types = MULTIBARRIER
• Design and optimisation of multibarriers is more complex than single-barriers– Concept: sequential or mixed multibarrier?– Effect of the pollutants on the removal process (inhibition, stimulation or no effect)?– Effect of one pollutant removal process on an other one?
NATO-CCMS, 41 juli 2004, Cardiff 2004
MULTIBARRIER Key-components• Groundwater:
0.5 mM NaHCO3
0.5 mM KHCO3
0.5 mM CaCl2.2H2O0.5 mM MgCl2.6H2O
+ growth supporting additives (Nutrients, O2, compost,..)
• Carrier materials:Filter sand (1-2 mm)Zerovalent iron FeA4 (0.3-2 mm)Activated carbon
GAC F400GAC Ind. React. (landfills)
(Aquifer material)MetasorbZeolitesWood chips
•Mixed pollution:VOCls: 2 mg/l PCE
5 mg/l TCEMetals: 5 mg/l Zn as ZnCl2
0.2 mg/l As(V) as Na2HAsO4
BTEX: 2 mg/l benzene2 mg/l toluene2 mg/l m-xylene
Extra: AOX (LFU)DCM, 11 DCA (UW)Ni, Cr (Vito)o-xylene, p-xylene,Ethylbenzene (Vito)
•Micro-organisms:Aquifer material Enrichment culturesAxenic strains
NATO-CCMS, 51 juli 2004, Cardiff 2004
MULTIBARRIER materials
Filtersand
Specific surface [m2/g] (measured)
FiltersandEverzitMetasorbGAC F400Zerovalent Iron
1,9294,1
3,0764,4
1,0Everzit Metasorb GAC F400
magnitude: 500x
Zero Valent IronFiltersand
+ Aquifer as source of micro-organisms
NATO-CCMS, 61 juli 2004, Cardiff 2004
Design of multibarriers
NATO-CCMS, 71 juli 2004, Cardiff 2004
• Different multibarrier concepts:
• Concept = Site specific and depending on the pollutants present• Sorption barrier = polishing step
SorptionBiodegradationReduction - Fe0
Mix
ed p
ollu
tion
g
SorptionBiodegradation Reduction - Fe0
...Mixed multibarrier
MULTIBARRIER concepts: Sequential vs mixed
BIO
Fe0
TEA SEQUENTIAL MIXED
O2
NO3- ?
Fe3+
SO42-
CO2
NATO-CCMS, 81 juli 2004, Cardiff 2004
TEA
SEQUENTIAL MIXED
O2 +
NO3- +
SO42- + +
Fe3+ + +
CO2 + +
As +
VOCls + +
Bio/Fe0
System A (O2) & System B (NO3)
NATO-CCMS, 91 juli 2004, Cardiff 2004
Biocolumns
Ironcolumns
Influent
PCETCE
Mixingvessel
N2
B T m-X
Aerobic/anoxicmedium
A
B
C2 1 3 4
Benzene removal in a denitrifying sequential system
NATO-CCMS, 101 juli 2004, Cardiff 2004
PCE+TCE
metals
BTX
1,2-cisDCE
BTX
NO3-
(1 mM)
BIO
Fe0 0
20
40
60
80
100
0 100 200 300 400 500
t (d)
% b
enze
ne r
emov
a
Fe(0)BioMB
[NO3] (mM): 1 0 1
HRTx 1.3
Systems D & E: Strictly anaerobic systems
1 2 3 4
Bio Bio
Bio
Bio+Fe
Fe
Fe
SR: 0.5 mM SO42-
IR: 2.5 mM Fe(III)EDTA
NATO-CCMS, 111 juli 2004, Cardiff 2004
System D: PCE & TCE degradation (SR columns)1 2 3 4
Bio Bio
Bio
Bio+Fe
Fe
Fe
NATO-CCMS, 121 juli 2004, Cardiff 2004
initial sorption
incomplete PCE degradation
complete TCE degradation
0
25
50
75
100
0 50 100 150 200
t (d)%
PC
E re
mov
al
C1 aqC2A FeC2B aqC2 MBC3A aqC3B FeC3 MBC4 mix
0
25
50
75
100
0 50 100 150 200
t (d)
% T
CE
rem
oval
C1 aqC2A FeC2B aqC2 MBC3A aqC3B FeC3 MBC4 mix
System D & E: Benzene removal
1 2 3 4
Bio Bio
Bio
Bio+Fe
Fe
Fe
NATO-CCMS, 131 juli 2004, Cardiff 2004
SR: no degradation
IR:- all MB- not in C2aq
0
25
50
75
100
0 50 100 150 200
t (d)%
ben
zene
rem
oval
C1 aqC2A FeC2B aqC2 MBC3A aqC3B FeC3 MBC4 mix
0
25
50
75
100
0 50 100 150 200
t (d)
% b
enze
ne re
mov
al
C1 aqC2A FeC2B aqC2 MBC3A aqC3B FeC3 MBC4 mix
SR
IR
System C: Partially mixed MB system
Columns (L = 50 cm)K1: test columnK2: abiotic control
Layers:L1: FS/Aq/Fe0 = 60/20/20 (W)L2:FS/Aq = 78/22 (W)
Monitoring:chemical analysesmicrobial ecology
NATO-CCMS, 141 juli 2004, Cardiff 2004
Partially mixed MULTIBARRIER: results
0123456789
10
0 100 200 300 400 500 600
Distance in column (mm)
pH
-500
-400
-300
-200
-100
0
100
200
300
ORP (mV)
pHORP
0
500
1000
1500
2000
2500
3000
3500
4000
0 200 400 600
Distance in column (mm)
PCE,
TC
E (p
pb)
0
5
10
15
20
25
30
35
40
45
50
cDC
E (p
pb)
PCETCEcDCE
0500
10001500200025003000350040004500
0 200 400 600
Distance in column (mm)
(ppb
) BTm-X
NATO-CCMS, 151 juli 2004, Cardiff 2004
NATO-CCMS, 161 juli 2004, Cardiff 2004
System 1-5: Results DCM &11DCA
100%
50%
10%
0% Noand
50% (2nd)
No
50%
No
>50%
Complete
Complete
No
Fe(0)
redox conditioningelectron donor
Results (% removal)
NATO-CCMS, 171 juli 2004, Cardiff 2004
Column trains
Characteristics (TEA) Acro-nym PCE TCE Benzene Toluene m-xylene
System A: Zerovalent iron wall followed by a micro-aerobic biobarrier 1
A1 1 – Fe(0)column A1-1 60-80 90-99 4-13 10-53 NA
2 – Bio column (O2) A1-2 80-100 92-100 99-100 99-100 > 90
System B: Zerovalent iron wall followed by a denitrifying biobarrier 1
B1 1 – Fe(0)column B1-1 66-99 97-100 6-18 16-54 NA
2 – Bio column (NO3-) B1-2 80-93 97-100 89-100 99-100 > 90
System C: Partially mixed Fe(0)/biowall followed by anaerobic biowall 2, 1
C1 1 – mixed zone C1-1 95-100 1 95-100 1 20 2 30 2 40 2
2 – bio zone C1-2 95-100 1 95-100 1 20 2 30 2 50 2
System D: sequential and mixed barriers under sulfate reducing conditions 1
D1 1 – Bio column (SO42-) D1-1 0-11 0-15 11-44 97-100 NA
D2 1 – Fe(0)column D2-1 55-71 88-98 4-54 0-36 NA
2 – Bio column (SO42-) D2-2 55-78 89-98 23-67 12-36 < 25
D4 1 – Mixed column (SO42-) D4-1 76-89 99-100 18-62 7-23 > 90
System E: sequential and mixed barriers under iron reducing conditions 1
E1 1 – bio column (Fe3+) E1-1 0-11 9-18 24-29 100 NA
E2 1 – Fe(0)column E2-1 53-67 85-92 50-68 72-91 NA
2 – Bio column (Fe3+) E2-2 54-67 86-92 52-71 77-90 > 90
E4 1 – Mixed column (Fe3+) E4-1 58-73 94-97 55-64 94-98 > 90
Conclusions
NATO-CCMS, 181 juli 2004, Cardiff 2004
• Mixed contamination plumes are omnipresent.
• Remediation of mixed contamination plumes using barriersMULTIBARRIERs are required
• Fungi do not play a big role in a Multibarrier
• In lab-scale columns different Multibarrier-concepts have been shown to be effective for the remediation of a mixed plume (PCE, TCE, BTmX, Zn, As).
• Behaviour of AOX in a Multibarrier is under study
• No toxicity detected in effluent (toxicity reduction) • The design and optimisation of multibarriers is more complex in
comparison with ‘single barriers’Many influencing parameters have to be taken into accountMixed Multibarrier under iron or sulfate reducing conditions
Conclusions
NATO-CCMS, 191 juli 2004, Cardiff 2004
• Sequential Multibarrier: ZVI + Micro-aerofilic biobarrier– PCE, TCE dehalogenation in ZVI– Zn, As removal in ZVI– BTX degradation in biobarrier– No degradation of cDCE
• Sequential Multibarrier: ZVI + Anaerobic biobarrier(denitrifying)– PCE, TCE dehalogenation in ZVI– Zn, As removal in ZVI– T, X degradation in biobarrier– B partially degraded in biobarrier– No degradation of cDCE
• Mixed Multibarrier: filtersand, aquifer materiaal, ZVI + Anaerobic biobarrier in aquifer– PCE, TCE dehalogenation– Zn, As removal in ZVI– BTX degradation in mixed zone– No formation of cDCE or VC
NATO-CCMS, 201 juli 2004, Cardiff 2004
Upscaling promising multibarrier concept
Aquifer AquiferReactive materials
Groundwater
Closed system
Pollutant-mixing& monitoring unit Posttreatment
A: coarse zone (25 cm)
B: Aquifer material
C: mixed Bio/Fe0 barrier : FeA4/Aq/HM = 30/60/10
D: Biobarrier Aq/ HM (90/10)
E: Biobarrier Aq
E: coarse zone (25 cm)
F: Sorption barrier
0.5 m 1 m 3 m
BIOFe0/BIO
PCE, TCE, Zn, As, BTEX Polishing
BTEX?
A B C D E F G
Set-up of MB on pilot scale
NATO-CCMS, 211 juli 2004, Cardiff 2004
NATO-CCMS, 221 juli 2004, Cardiff 2004
MULTIBARRIER Monitoring System (MMS)
NATO-CCMS, 231 juli 2004, Cardiff 2004
• On-line measuring and logging system pH, T, ORP, conductivity, O2 and pressure :
– Tested in the pilot system– Focus on EC-measurement
• in-well mixing system has been tested:– Works very well
Pilot MULTIBARRIER system: First experiment
• Monitoring strategy:
10-20 cm bgs170-180 cm bgs
90-100 cm bgs 90-100 cm bgs
10-20 cm bgs170-180 cm bgs
EC-measurementsStirred electrode set
Non-stirred electrode set
NATO-CCMS, 241 juli 2004, Cardiff 2004
NATO-CCMS, 251 juli 2004, Cardiff 2004
Monitoring of PRBs
A
B
B
B
C
C
C
D
E
E
E
F
G
G
Plume
Gravel
Reactive material
Monitoring well
100 m
- UK guidelines- US EPA guidelines- Flanders (OVAM) guidelines- Germany (in preparation?)
In situ mesocosm-systemsMonitoring of microbiology (molecular biology)
NATO-CCMS, 261 juli 2004, Cardiff 2004
WP3: HM + Mesocosms containerPearson correlation (Opt:0.90%) [0.0%-100.0%]MB
100
90807060504030
MB
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MESO A1 T0 AMESO A2 T0 A
MESO A2 T0 BMESO A1 T0 B
MESO A5 T0 A
MESO A5 T0 BMESO A7 T0 A
MESO A7 T0 Bmengsel HM/AqDEC (bulk) B
mengsel HM/AqDEC (bulk) A
AqDEC (bulk) BAqDEC (bulk) A
mengsel HM/AqDEC/FeA4 (bulk) Bmengsel HM/AqDEC/FeA4 (bulk) A
MB Aquifer
HM (bulk) BHM (bulk) A
JD 112JD 112
JD 107JD 106
JD 104
JD 105
HMHM
Aëroob 2 onderAëroob 2 (REF) boven
Aëroob 1 (MB) boven
Aëroob 1 onder
NATO-CCMS, 271 juli 2004, Cardiff 2004
MULTIBARRIER Modelling System: salt injection
new gage3
new gage2
new gage1
X
Y
Z
new gage3
new gage2
new gage1
X
Y
Z
NATO-CCMS, 281 juli 2004, Cardiff 2004
new gage3
new gage2
new gage1
X
Y
Z
new gage3
new gage2
new gage1
X
Y
Z
Modelled salt-peaks• Permeability: 24.17 m/dag• Dispersivity: 0.3 m• Monitoring wells: filter 100 cm bgs,• Result: migration of pollutant initally faster, afterwards slower in comparsion with
measured values
NATO-CCMS, 291 juli 2004, Cardiff 2004
0
10
20
30
40
50
60
70
80
90
0 5 10 15 20 25 30 35 40
d = 5 md = 3,5 md = 1,5 m
Time (days)
Conc%
NATO-CCMS, 301 juli 2004, Cardiff 2004
Pilot scale Multibarrier:Curilo deposit
Installation at Curilo deposit
3 m
2 m0.1 m0.6 m
1.5 m
2.0 m
1.5 m
1.0 m
5.0 m
0.8 m
1.0 m
12
34
5
0,5 m
3
4
17.5 m
15.0 m
1.6 m
NATO-CCMS, 311 juli 2004, Cardiff 2004
Curilo deposit: constructed wetland + Multibarrier
NATO-CCMS, 321 juli 2004, Cardiff 2004
Thanks to all the partnersand the European Commission
QLK3-CT-2000-00163+
QLRT-2001-02916
NATO-CCMS, 331 juli 2004, Cardiff 2004
www.multibarrier.vito.be