david singapore
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Dr. Dr. Iulia Gabriela DavidIulia Gabriela David
Department of Analytical Chemistry
Faculty of Chemistry
University of Bucharest,
ROMANIA
KontakTUM Seminar -Singapore 2009
KontakTUM Seminar -Singapore 2009
chemical reactions
chemical reactionstransport
effects
fates
sourcessources
stu
dy
eff
ects
inin
KontakTUM Seminar -Singapore 2009
KontakTUM Seminar -Singapore 2009
AIM AIM ---- ---- determination of nature quantity qualitative analysis quantitative analysis
WHATMATTER in
ENVIRONMENTALANALYTICALCHEMISTRY
ENVIRONMENTALANALYTICALCHEMISTRY
HOW MUCH
KontakTUM Seminar -Singapore 2009
Manahan Stanley E., Environmental Science, Tehnology and Chemistry, Environmental Chemistry, Boca Raton, CRC Press LLC, 2000
Major aquatic chemical processesMajor aquatic chemical processes
KontakTUM Seminar -Singapore 2009
essential elementsessential elements Fe, Se, Cu, Zn Fe, Se, Cu, Zn
toxic metals toxic metals Pb, Cd, Hg, AsPb, Cd, Hg, As
KontakTUM Seminar -Singapore 2009
elementsthat occur at very low levelsof a fewppm or less in agiven
system.
Manahan Stanley E., Environmental Science, Tehnology and Chemistry, Environmental Chemistry, Boca Raton, CRC Press LLC, 2000.
KontakTUM Seminar -Singapore 2009
KontakTUM Seminar -Singapore 2009
Obtain &preserverepresentative
sample
Transform the sample to an analyzable form
Calculate the result
(Input)
(Black box)
(Output)
KontakTUM Seminar -Singapore 2009
Pretreatments required for various water samples. Filtration and irradiation steps can be omitted for samples that don’t have particulate matter/significant organic content (e.g., tapwater and open ocean water); this is represented by the dashed line.
A.W.BottVoltam. Determ. of Trace Concentrof Metals in the Environm, Crt.Sep. 14:1 (1995)
KontakTUM Seminar -Singapore 2009
SampleSample
Pe
ristaltic pum
p
Carrier flow(HCl)
Reducing agent(NaBH4)
Mixing chamber
Inert gas(Ar)
Gas/liquid separator
Heated Heated quartz quartz
cellcell
Waste
Waste
Hydride(AsH3)
Decte
ctor
SCHEMATIC OF A Hydride Generation-Atomic Absorption Spectrometer
Application: Application: Antimony, arsenic, bismuth, germanium, lead, selenium, tellurium, tin
native3324 8HBOHO3H H BH
O23HA3H3H-33OAnativ6H ss
O23HA343BO3H3
-334AsO H 1543BH
sH
Valve
-high sensitivity
-high sample throughput
-minimal chemical interferences because only few
elements
are able to form hydrides
-enables speciation
-no interferences due to radiation scattering
KontakTUM Seminar -Singapore 2009
- limited applicability range
- expensive instrumentation
- relative sensitive to interferences
KontakTUM Seminar -Singapore 2009
SCHEMATIC OF AN ICP-AESpectrometer
Nebuliser
Ar
Sample
excited atoms
hDetector
Polychromator
(Ar+sample aerosole)
(T=8000Kh=12 cm)
(cooling, 12 L/min)
(0.8 L/min)
(1 L/min)
(0.002 l/min)
(Frequency 27.12 MHz Power adjustable 800 -1,600 W)
(165–210 nm;210-580 nm)
Plasma torch
KontakTUM Seminar -Singapore 2009
-low detection limits for over 70 elements (ppb)
[e.g. 10 ppb for Pb; 50 ppb for As]
-PDA detectors enable simultaneous multielemental analysis
-enables automatisation high sample throughput :
1-3 minutes for a complete analysis of 30 elements
- high Ar consumption-expensive instrumentation
KontakTUM Seminar -Singapore 2009
-HMDE-MFE-Bare C, Au, etc.
10-4 -10-5 Hg+2 for co-metal deposition.
A cathodic or reducingpotential is applied for afixed time interval reducing Mn+
Potential is scannedin anodic or oxidizingdirection to strip out Mo
KontakTUM Seminar -Singapore 2009
MeASVoltammogram of Cu.
Cu
MeASVoltammograms of Zn, Cd ,Pb).
L.R.=0.1 - 500 μg/LD.L. = 0.05 μg/L (ppb)
Cu
PbZn
Cd
GaL.R.=0.5 - 50 μg/LD.L. = 0.05 μg/L
environmental matrices : -drinking or waste water.samples containing large amounts of chloride (e.g. sea water).
KontakTUM Seminar -Singapore 2009
•Sensitive and reproducible (RSD<5%) method for
trace metal ion analysis in aqueous media.
Accuracy is proportionate to the way of sample calibration:<5% when calibrated directly via the method of standard
additions. 10% when a calibration curve is built before measuring20% - 40% when operating uncalibrated
•Concentration limits of detection for many metals are in
the low ppb to high ppt range (S/N=3)
Part per million is instantaneous Part per billion in 20 seconds or less Part per trillion takes 1-3 minutes
compares favorably with AAS or ICP analysis.
KontakTUM Seminar -Singapore 2009
•Selectivity & sensitivity can be improved by electrode surface modification e.g.:-Bi deposition on GCE (DL=1.4×10-10 mol/L Pb²+; 0.03 μg/L)
[C. E. Cardoso et.al. Anal. Sci., 23, 1065, 2007]
-Heparin modified GCE (DL= 3×10-10 mol/L Pb²+; 0.06 μg/L) [N.-B. Li, J.-P. Duan, G.-N. Chen, Chin. J. Chem., 22, 553, 2004]
CSV of metal complexes e.g. Zn²+ and Pb²+ with dopamine (DA) from water samples DL=0.5 μg/L Pb²+; 0.06) =1,8 μg/L Zn²+)
Differential pulse voltammograms of a) Blank solution; b) Pb2++Zn2+ (40 ng/ml) without ligand (DA) ; c)Pb2++Zn2+ (40 ng/ml) complexes with DA; Conditions: HMDE, pH, 10; DA= 1.0×10-4 M; accumulation potential, 0.0 V;
accumulation time, 10 s; scan rate, 10 mV/s..
Alireza Asghari , Malaysian J. Anal.Sci.,12(2),410, 2008
•Simultaneous metal ions analysis.No interference between: Lead, Cadmium, Copper and Mercury Zinc, Lead, Cadmium and Mercury Zinc and Copper at low concentrations The method is inherently tolerant of saline solutions: unlike Graphite AA techniques, salinity does not impact the accuracy or performance of the metals measurement
•Inexpensive (field) instrumentation.A quarter of the cost of AA systems A tenth of the cost of ICP systems Use one electrode to measure up to five metals Robust electrodes can make thousands of
measurements
KontakTUM Seminar -Singapore 2009
KontakTUM Seminar -Singapore 2009
concentrations of the different physicochemical forms of the element (metal ions)
determination
hydrated complexes with
adsorbed on
ligands
inorganicorganic
Colloidal particles
inorganicorganic
As(V) (nontoxic) + As(III) (toxic)
Cu2+ HMDES1 As(III)
reduction
Cu2+ HMDES2 Astotal = As(III)+As(III)reduced
S2-S1 As(V)
inorganic lead and organometallic lead compounds
varying the deposition potential (Ed) in ASV.
Ed=-1.4 V : S1 Et3PbCl+ Et2PbCl2 +Pb(II)
Ed=-0.6 V : S2 Et2PbCl2 +Pb(II)
Complexation Pb(II) +EDTA
S3 Et2PbCl2Ed=-0.6 V :
S1-S2 Et3PbCl
Pb(II) S2-S3
KontakTUM Seminar -Singapore 2009
KontakTUM Seminar -Singapore 2009
PbH4 A2
inorganic lead [Pb(II) + Pb(IV)]
NaBH4
PbH4 A1 Pb(IV)Pb(IV)oxidation
(NH4)2S2O8
Pb(IV)oxidised + Pb(IV)NaBH4
Pbtotal=Pb(IV)oxidised + Pb(IV)
A2 - A1= Pb(II)Pb(II)
NaBH4
As(III) +As(V)
AsH3A1 As(III)As(III)
1
NaBH4
AsH3 A2
As(V)As(V)2 reduction, KI
As(III) +As(III)reduced
Astotal = As(III) + As(III)reduced
A2 - A1=
KontakTUM Seminar -Singapore 2009
Acknowledgement
Financial support is acknowledged from the
PN-II- project BIOXEN 32111-2008.
KontakTUM Seminar -Singapore 2009