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Trace metal complexation in natural waters

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Trace metal complexation in natural waters - Pseudopolarography - Metal complexing capacity (MCC) Dario Omanovi , Petra Cmuk, Ivanka Pi eta Center for Marine and ... – PowerPoint PPT presentation

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Title: Trace metal complexation in natural waters


1
Trace metal complexation innatural waters
  • - Pseudopolarography
  • - Metal complexing capacity (MCC)
  • Dario Omanovic, Petra Cmuk, Ivanka Pižeta
  • Center for Marine and Environmental Research,
  • Ruder Boškovic Institute, Croatia
  • Yoann Louis, Rudy Nicolau
  • Laboratoire PROTEE, Université de Toulon et du
    Var
  • BP 132, 83957 La Garde, France
  • Cedric Garnier
  • LPTC, Université Bordeaux I, 351 Crs. de la
    Libération, F-33405 Talence CEDEX, France

2
Distribution of trace metals
  • Operationally defined
  • Particulate - gt 0.45 µm
  • Dissolved - lt 0.45 µm
  • Colloidal - between 1 kD and 0.45 µm
  • Truly dissolved - lt 1 kD

3
Distribution of trace metals
  • Physico-chemical classification
  • Inorganic complexes
  • Organic complexes
  • Associated to particles

4
Distribution of trace metals
  • Methodological (electrochemical) classification
  • Labile complexes
  • Mostly inorganic complexes (Cl-, OH-, SO42-, ...)
  • Fast dissociation rate
  • Mostly reducable
  • Inert complexes
  • Mostly organic complexes
  • Very stable high stability constant
  • Only partly reducable

5
Electrochemical characteristics
Inert complexes
  • Labile complexes

6
Construction of pseudopolarogram
Voltammograms
Pseudopolarogram
7
Model titrations one ligand
8
Model titrations one ligand
Experimental CdCC 0.97010-7 M log Kapp
8.37 Theoretical CdCC 110-7 M log Kapp
8.44
9
Model titrations two ligands
Stability constants _at_ µ 0.1 M Log K CdNTA
9.76 Log K CdEDTA 16.4
Theoretically ?Erev 0.059log K / n Exp. for
CdNTA ?E 0.320 V log K 10.8
10
Model titrations two ligands
Eacc -0.75 V CdCC 0.97310-7 M
Eacc -1.15 V CdCC 0.50310-7 M
11
Seawater sample addition of NTA
  • CADMIUM
  • Fast complexation with NTA
  • Two separate peaks of labile Cd and CdNTA

12
Seawater sample addition of EDTA
  • CADMIUM
  • Very slow complexation with EDTA (cca. 3 h)
  • Two separate peaks of labile Cd and CdEDTA

13
Seawater sample not clean (Šibenik)
Copper
Eacc -0.45 V
No separated well defined waves
CuCC 4.210-8 M Log Kapp 9.2
14
Seawater sample clean (Zlarin)
Copper
Two well separated waves - labile copper
complexes _at_ E -0.34 V - inert copper
complexes _at_ E -1.40 V
15
Experimental setup - parameters
Copper - clean seawater (Zlarin)
Eacc -1.6 V, tacc 300 s
Eacc -0.45 V, tacc 297 s and Eacc -1.6 V,
tacc 3 s
Eacc -0.45 V, tacc 300 s
16
Experimental setup - parameters
Copper - clean seawater (Zlarin)
17
Seawater sample clean (Zlarin)
Cadmium
without well separated waves
18
Conclusion
  • Pseudopolarography is a tool for the
    characterisation of an interaction of trace metal
    ions in natural samples
  • It is the fingerprint of the sample
  • The position and the shape of the waves give us
    additional information about complexing ability
    of the particular natural sample
  • It is very useful in complexing capacity
    determination measurements
  • The composition of natural water samples is very
    complex and, unfortunatelly, it is very hard to
    obtain behaviours like in model solutions
  • Additional efforts should be done to resolve
    problems associated with the experimental setup
    as well as to interpret data regarding both
    pseudopolarograms and metal complexing capacity
    determination
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