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Dr. Dr. Iulia Gabriela David Iulia Gabriela David Department of Analytical Chemistry Faculty of Chemistry University of Bucharest, ROMANIA KontakTUM Seminar -Singapore 2009

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Page 1: David singapore

Dr. Dr. Iulia Gabriela DavidIulia Gabriela David

Department of Analytical Chemistry

Faculty of Chemistry

University of Bucharest,

ROMANIA

KontakTUM Seminar -Singapore 2009

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KontakTUM Seminar -Singapore 2009

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chemical reactions

chemical reactionstransport

effects

fates

sourcessources

stu

dy

eff

ects

inin

KontakTUM Seminar -Singapore 2009

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KontakTUM Seminar -Singapore 2009

AIM AIM ---- ---- determination of nature quantity qualitative analysis quantitative analysis

WHATMATTER in

ENVIRONMENTALANALYTICALCHEMISTRY

ENVIRONMENTALANALYTICALCHEMISTRY

HOW MUCH

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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

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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

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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

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KontakTUM Seminar -Singapore 2009

Obtain &preserverepresentative

sample

Transform the sample to an analyzable form

Calculate the result

(Input)

(Black box)

(Output)

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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)

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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

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-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

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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

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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

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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

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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).

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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.

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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

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•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

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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

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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

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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=

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KontakTUM Seminar -Singapore 2009

Acknowledgement

Financial support is acknowledged from the

PN-II- project BIOXEN 32111-2008.

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KontakTUM Seminar -Singapore 2009