electrochemical sensors for oceanography€¦ · (e.g., oxygen electrode), a potential is applied...
TRANSCRIPT
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ELECTROCHEMICAL SENSORSFOR OCEANOGRAPHY:
From Glass Electrodes to Nanosubmarines
Joseph WangDepartment of Nanoengineering,
UCSD
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HISTORICAL PROSPECTIVE
pH Glass electrode Oxygen Clark electrode Mercury drop electrodes
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ELECTROCHEMICAL SENSORSBackground: Rely on measurements ofelectrical quantities (e.g. current, potential)and their relationship to chemicalparameters (usually concentration).
In the widely-used amperometric sensors(e.g., oxygen electrode), a potential isapplied onto the working electrode to drivean electron-transfer reaction, and theresultant current is measured.Potentiometric devices (e.g. pH sensors)rely on potential measurements.
-0.8-0.6-0.4-0.20.0
Potential / V
Cur
rent
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Why Electrochemical Detection?• High Sensitivity and Selectivity (toward EA species)
• EC ‘loves’ salt (including 0.54M NaCl)
• Inherent Miniaturization
• Advanced Microfabrication
• Low Power Requirements (+low costs)
• Rapid (Temporal) Detection
• Easy to use
Electrochemical devices offer great promise for in-situ worksand autonomous platforms!
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EC Sensors
Meeting the 4 S Requirements forSuccessful in-situ Monitoring:Sensitivity – Extremely high (down to pM)Selectivity – Towards electroactive species,
with potential overlapping peaksSpeed – Extremely fast (down to msec)Stability – Limited (due to surface fouling)
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Properties of Controlled-Potential Techniques
SpeedWorking Detection (time per Response
Technique* Electrode‡ Limit, M cycle), min Shape---------------------------------------------------------------------------------------------DC polarography DME 10-5 3 WaveNP polarography DME 5x10-7 3 WaveDP polarography DME 10-8 3 PeakDP voltammetry Solid 5x10-7 3 PeakSW polarography DME 10-8 0.1 PeakAC polarography DME 5x10-7 1 PeakChronoamperometry Stationary 10-5 0.1 TransientCyclic voltammetry Stationary 10-5 0.1-2 PeakStripping voltammetry Bi SPE, MFE 10-10 3-6 PeakAdsorptive stripping HMDE, Bi 10-10 2-5 PeakvoltammetryAdsorptive stripping Solid 10-9 4-5 PeakVoltammetryAdsorptive-catalytic HMDE, Bi 10-12 2-5 Peakstripping voltammetry
*DC = direct current; NNP = normal pulse; DP = differential pulse; SW = square wave.
From: Analytical Electrochemistry, J. Wang, 2006 (Wiley)
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Determination of the zinc complexingcapacity in seawater by cathodicstripping voltammetry, C. van denBerg, Marine Chemistry, 1985
In situ voltammetric measurements innatural waters: Future prospects andchallenges, J. Buffle, Electroanalysis,1993
Measurement of copper and zinc in SanDiego Bay by automated anodicstripping voltammetry, A. Zirino, EST,1978
Direct determination of iodide inseawater by cathodic stripping squarewave voltammetry, G. Luther, Anal.Chem., 1988.
Major Contributions of Buffle, Luther, Zirino, Florence,van den Berg, and many more……….in-situ and speciation studies since the1970s…………..
The speciation of trace elements inwaters, T.M. Florence, Talanta, 1982.
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My Own Journey (PhD in late 1970s)
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TOWARDS FIELD DEPLOYABLE DEVICESTraditionally, laboratory-based electrochemical measurements have
relied on relatively bulky and expensive electrodes, such as the rotatingdisc electrode or the static mercury drop electrodes (SMDEs) (with theirheavy motor or large mercury reservoir, respectively). Such electrodeswere combined with large cells (of 20-50 ml solution volume), theoperation of which required careful cleaning, oxygen removal, solutionstirring,, standard additions and replacement with new solution.
We would like to replace the conventional, cumbersome approachwith more imaginary ones (that meet the field demands of the 21st
Century).
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1994: Tools Developed Towards Cleanup of DOE National Labs Upon theEnd of the Cold War (e.g., remote sensors for groundwater monitoring ofCr and U).
Changing the way we do electrochemistry!!!
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From Bulky Mercury and Rotating Electrodes to Solid-State Microfabricated and Flexible Microelectrodes
DME
Thin and thick-filmmicrofabricated electrodes
Rotating disc electrode: RDECurrent electrode strips
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MINIATURIZED ANALYZERS
FROM BULKY EC ANALYZERS TO ADVANCED HAND-HELD ANALYZERS
1980s and 1990s
TOWARDS PORTABLE INSTRUMENTATION
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1990s: Towards Submersible Sensors
Remote Metal Sensors and Hand-Held Explosive Analyzers
The new devices allow us to move the measurement from the central laboratory to thefield, and to perform them rapidly, reliably and inexpensively (eliminating errors and
delays associated with sampling and storage to the main laboratory.
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Plume Tracking
Flexible Wetsuit Sensors Nano-submarines forEnvironmental Remediation
Wearable (Tattoo) Devices
21st Century Devices
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DISPOSABLE FLEXIBLE ELECTRODES AND MINIATURIZED ANALYZERS
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SUBMERSIBLE/REMOTEELECTROCHEMICAL SENSORS
Goal: Obtaining a fast and accurate return ofchemical data in a timely, safe, and cost-effectivemanner.
Benefits: Assessment of pollutant gradient; earlywarning of pollution events and security threats;characterization of hostile environments; Industrialprocess control.
Minimizing the errors, cost, and delays associatedwith the collection and transport of discrete samples.
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REMOTE STRIPPINGELECTRODES
(FOR METALPOLLUTANTS)
REMOTEBIOSENSORS
(FOR ORGANICPOLLUTANTS)
REMOTE MODIFIEDELECTRODES
(FOR ORGANICPOLLUTANTS)
REMOTE UCSDSENSORS
Fast return of the chemical information in a safe and timely manner.Effective monitoring of priority pollutants and threat compounds.
Assessment of chemical gradients
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Metal Analyzers
Of the available analytical techniques fortrace metal determinations (AAS, ICP, NA,ASV), electrochemical (stripping) methods offerremarkable sensitivity, combined with portable,low-cost/power instrumentation.
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Scope of ASV and AdSV of Trace Metals
Stripping Voltammetry:Electrolytic or Adsorptive Preconcentration
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WHY STRIPPING ANALYSIS?
Electrochemical stripping analysishas always been recognized as apowerful tool for measuring tracemetals. Its remarkable sensitivity(and pM detection limits) areattributed to the ‘built-in’preconcentration step, duringwhich the target metals aredeposited onto the workingelectrode.
In-Situ STRIPPING ANALYSIS OFTRACE METALS
THE POTENTIAL-TIMEWAVEFORM
THE RESULTINGVOLTAMMOGRAM
THE POTENTIAL-TIMEWAVEFORM
THE RESULTINGVOLTAMMOGRAM
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MICROMACHINED STRIPPING FLOW MICROANALYZER
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MEMSASV
For incorporation onto various monitoring platforms
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REPRODUCIBILITY
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Because of the toxicity of mercury, alternative (‘environmentally friendly’)electrode materials are highly desired for field applications. Bismuthelectrodes offer a very favorable performance and serve as attractivealternative to mercury electrodes. Bismuth stripping electrodes thus holdgreat promise for on-site and in-situ metal measurements.
Increasing levels of Zn, Cdand Pb in 10 ppb steps.
From Mercury to Bismuth Electrodes Wang, Anal. Chem. 2000
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REMOTE SENSING OF TRACEMETAL CONTAMINANTS
Wang et al, Anal. Chem. 34(1995)1481
STRIPPING-BASED SUBMERSIBLE PROBE, WITHA GOLD-FIBER MICROELECTRODE,
FOR IN-SITU MONITORING OFTRACE METALS
Originally developed for Groundwater Monitoring
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Electrodeconnections
Long shielded cable
Reference electrode
Counter electrodeWorking electrode
PVC type housing
Quick disconnect environmentally-sealed connector
REMOTE ELECTROCHEMICAL SENSOR
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WHAT ARE THE CHALLENGESTO SUBMERSIBLE ELECTROCHEMICAL PROBES?
Sensitivity, selectivity and reversibility
Changes of natural conditions (pH, salinity,
oxygen, temperature, convection)
Stability and baseline drift (Surface fouling under
prolonged operation; adsorption of macromolecules)
Robust in-situ calibration (How the quanititate?)
Power (harvesting energy from environment)
Signal handling and transmission
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Remote Stripping Probes
Obstacles to Submersible Operation:Traditional use of mercury electrodes, oxygenremoval, supporting electrolyte, or solution stirring.
Solutions:Use of gold or bismuth electrodes, potentiometricstripping operation, and of ultramicroelectrodes (thatoffer efficient deposition from unstirred solution andoperation in low ionic-strength media).
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UCSD Remote Submersible Sensors
Real-time in-situ monitoring of priority pollutants and threat compounds.
Wang, Anal. Chem. 67, 1481(1995).
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Anal. Chem. 1995
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SILVER REMOTE SENSING ELECTRODE
Anal. Chim. Acta 1996
Stability ingroundwater (A)and river water (B)samples
Discharge from a KodakPlant into Lake Ontario
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Mapping of San Diego Bay for Heavy MetalContaminants
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Anal. Chim. Acta 1995
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‘Lab on a Gondola’
Monitoring Trace Hg and Cu in Venice’sGrand Canal
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REMOTE SENSING OF METALS THAT CANNOTBE PLATED ELECTROLYTICALLY (Fe, Cr, U, V,
Mo, Ni)
USE OF ADSORPTIVE STRIPPING PROTOCOLSBASED ON THE ADSORPTIVE ACCUMULATIONOF CERTAIN COMPLEXES OF THE TARGET
METAL
M+n + L ML+n MLads+n
REQUIRE NEW PROBE DESIGN, WITHDELIVERY OF THE LIGAND SOLUTION
Extension to Adsorptive Accumulation:
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ADSORPTIVE STRIPPING VOLTAMMETRY
Accumulation and stripping steps in adsorptive stripping measurements of ametal ion in the presence of an appropriate chelate agent (L).
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AdSV: LAB-ON-A-CABLE
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REMOTE Cr STRIPPING SENSOR(W/ An internal delivery of DTPA)
Stability and Carry-Over
Analyst 1999
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IN-SITU SENSORS FOR METALSPECIATION
DIFFERENTIATION BETWEEN METAL SPECIESOF DIFFERENT SIZES.IN-SITU MANIPULATION OF COLLECTEDMETAL (via delivery of acid or ligand).ELIMINATION OF ERRORS INDUCED BYSAMPLE COLLECTION AND STORAGE(contamination, disturbance of equilibrium).
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ELECTROCHEMICAL SENSORSFOR EXPLOSIVES IN MARINE ENVIRONMENTS
The presence of the electroactivenitro group makes nitroaromatic andnitramine explosives makes them idealcandidates for electrochemical detection.Such nitro group is an excellent electronacceptor and its reduction can beexploited for sensitive and selectiveelectrochemical detection.
For Review: Electroanalysis 19(2007)415
Tools Developed for Security Applications (ONR CSME Program):
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In Situ Monitoring of Explosives
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Common nitroaromatic and nitramine explosives
EXPLOSIVE DETECTION INMARINE ENVIRONMENTS
Distinct electrochemical signatures
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REMOTE TNT SENSOR
Calibration Data : 250 ppb increments in sea water
-0.8-0.6-0.4-0.20.0
Potential / V
Cur
rent
0
4
8
12
0 1 2 3Conc. / ppm
Cur
rent
/ µA
5 µA
a
l
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REMOTE TNT SENSOR
-0.7-0.5-0.3-0.1
Potential / V
Cur
rent
3µA
High Stability:
60 repetitive measurementsof 0.7 ppm TNT for 5 h in seawater.
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HAND-HELD DIVER TNT SENSOR
SENSOR HEAD
POCKET PC ELECTRONIC
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HAND-HELDDIVER UNIT
Dual Detection: Direct Comparison to Fluorescence of T. Swager (MIT)
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RESPONSE NEAR SOURCE
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Deployment Onto U.S. Navy UnderwaterUnmanned Vehicle
U.S. Navy unmanned
underwater vehicle,
The Remus
TOWARDS ARTIFICIAL DOLPHINES
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High sensitivity (down to 1 ppb)and high speed (1-2 sec runs)
DEPLOYMENT ONTO UNDERWATER VEHICLES:Towards “Artificial Dolphins”
Carbon-FiberElectrode Assembly
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SENSOR ASSEMBLY ONTO THE AUV
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REMUS body ADCP Collar Nose Cone
PV with electronicsElectrode Unit
Connector
TNT sensor integrated onto the REMUS UUV
UNMANNED UNDERWATER VEHICLE (UUV)
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Plume-tracking and Source localization:
Finding/following plume to source(ONR CSME Program)
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0
1
2
3
0 50 100 150 200 250 300 350 400Run number
Cur
rent
/ uA
AUV TNT Map: Repetitive SWV Scan, every 2 sec
Duck Mission, NC (6/24/03)
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Electrochemical Arrays for Multiple Injuries
Parallel Detection of Various Forms of Injury
Towards Wearable Devices: Textile-Based Sensor Arrays
Printed Sensor on Gore-Tex Fabric
Stencil Patternfor Array
FabricationBiosensor ArrayLayout
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‘Lab-on-a-Sleeve’Textile-based Wearable Explosive Sensors
Square wave voltammograms (left) of GORE-TEXfabric-based sensors to DNT (A) and TNT (B).Electroanalysis 2010
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On-Body Wearable Devices: Wetsuit Sensors(for divers and surfers)
Analyst 2011
Monitoring environmental pollutants andsecurity threats in marine environments
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Printable Wetsuit Sensors
Underwater garments are highlycompatible with the thick-film (screen-
printing) fabrication process
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Wearable electrochemical sensors onunderwater garments comprised of the
synthetic rubber neoprene.Analyst 2011
Wearable screen-printed electrochemicalsensors on underwater garments
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Cyclic voltammograms for 5 mM ferricyanide at SPE on flexibleneoprene (A) and rigid alumina (B) substrates. C) Effect of ten 10
repeated bending operations. D) Relative currents obtained for theredox peaks of (C).
Wearable Wetsuit Sensor
Survive large mechanical deformations.
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Wetsuit-based biosensing of phenolic contaminants
Enzyme (tyrosinase) immobilization on awearable substrate towards amperometricbiosensing of phenolic contaminants in
seawater. A tyrosinase-containing carbon inkwas employed for printing the amperometric
biosensor.Analyst 2011
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Underwater Copper Monitoring
Stripping voltammograms for trace copper in untreatedseawater at the Au-modified neoprene SPE.
A) response to increasing copper concentrations in 10ppb steps. Deposition for 2 min at -1.0V. B) Calibrationcurve. C,D) Stability of the system with 100 ppb copper
over a 50 min period.
Analyst 2011
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Wearable Wetsuit System (‘Lab-on-a-Wetsuit’):Direct integration of a miniaturized potentiostat (supporting electronics)
directly on the underwater garments
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Wearable Wetsuit System:Integration of a miniaturized potentiostat directly on
the underwater garments
An encapsulated (watertight)miniaturized potentiostat that
provides the wearer with avisual ‘YES’ / ‘NO’ digital format
(via the illumination of a lightemitting diode).
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Wearable epidermal chemical sensingdevices based on
integration of tattoo-transfer and thick-film fabrication processes.
Withstand the mechanical stresses (pinching,stretching, bending) relevant to epidermal wear.
Chem Comm2012
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WEARABLE TATTOO pH SENSOR
Keep Smiling and responding
Analyst 2013
Under MechanicalStrain
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In 2008
Moving to UCSD and Becoming a Nanoengineer….
GOING NANO! TOWARDS NANOSUBMARINES
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1 meter
1 micrometer(1 millionth of a meter)
Barcode
GOING NANO! TOWARDS NANOSUBMARINES!
Locating explosives
or cancer cells
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Nanomotors - UCSD Propulsion Mechanisms
Tt
Towards Nanosubmarines
The motion of synthetic micromotors has received a considerable fundamental andpractical interest over the past decade. Bubble-propelled catalytic tubular microenginesoffer great promise for various practical applications due to their efficient propulsion invarious real-life media.
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High propulsion power of thePANI/Pt microtube engines:JACS 2011
Bubble-Propelled Catalytic Microengines:Bilayer Polymer-Platinum Microtubular Engines
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Advanced Motion Control - Towards complex movement patterns
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Micromotor-based strategy for water-quality testing based onchanges in the propulsion behavior of artificial biocatalytic
microswimmers in the presence of aquatic pollutants.
(analogous to changes in the swimming behavior andsurvival of natural fish used for toxicity testing.)
Nanofish for Water-Quality Testing
ACS Nano 2013
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TOWARDS ENVIRONMENTAL REMEDIATION:Superhydrophobic Alkanethiol-Coated Microsubmarines for
Effective Removal of Oil
ACS NANO 2012
The new SAM-modified micromotors thus offer a rapid highlyefficient collection and transport of oil droplets in aqueousenvironments through the interaction with the hydrophobicalkanethiol monolayer coating.
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Nano Letters, 2011
‘On-the-Fly’ Hybridization: ss-DNA-Functionalized micromotorsas selective transporters of complementary nucleic acid.
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Motion-based Pathogen DetectionCatalytic nanomotors ‘racing’ following hybridization assays of
different E. coli cells
Direct detection of raw bacterial ribosomal RNA without isolation or purification steps
Nature Comm., 2010
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Conclusions
Electrochemical devices are highlysuitable for decentralized on-site and in-situ marine survey. Over the past 2decades such devices have undergo adramatic change towards high-quality ,user-friendly, compact (hand-held)instruments. These developments shouldhave a substantial impact on marinesurveys and ocean science.
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