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S bastien Sauv Department of Chemistry Universit de Montr al sebastien.sauve_at_umontreal.ca Ion selective electrodes Prejudiced against Often, presumed unreliable ... – PowerPoint PPT presentation

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Title: S


1
Sébastien SauvéDepartment of ChemistryUniversité
de Montréalsebastien.sauve_at_umontreal.ca
Metal speciation using ion-selective electrodes
2
Ion selective electrodes
  • Prejudiced against
  • Often, presumed unreliable
  • Very easy to use
  • Give a simple, direct measurement of free ionic
    activity
  • Commercial combined electrodes can be used with
    as little as 5 mL of solution sample
  • Cheap

3
Avdeef et al. 1983
4
Prejudice
  • Too often, confusion over the speciation vs.
    concentration comparisons, i.e., not accounting
    for complexation
  • The  limit of detection  in dilute salts given
    around 10-7 M is close the background
    concentration expected in clean solutions
    (resulting in a standard addition type of plateau)

5
Cupric Ion-Selective Electrodes
  • Linear, Nernstian response down to pCu2 of
  • 7 in dilute copper salts solutions (60 µgL-1)
  • 19 using solutions copper-buffered with ligands
    of known stability constants (10-19 M or 60
    agL-1)
  • Simple equipment
  • Extensive literature

6
Cupric Ion-Selective Electrodes
  • Interferences
  • Ionic strength variations
  • Need a relatively uniform IS
  • Aluminum
  • Mercury
  • Chloride
  • Electrode surface is sensitive

7
Cupric Electrode Calibration
  • Suggested Cu-IDA calibration solutions have
  • 110-3 M IDA
  • 110-4 M Cu(NO3)2
  • 610-3 M NaOH
  • 2.510-3 M KHphthalate
  • 110-2 M CaCl2 (media)
  • pH adjusted with HNO3
  • Use IDA stability constants reported in the
    literature, interpolated to 0.02 ionic strength

8
Calibration
  • Simultaneously determine the pH for calculations
    of pCu2

9
Calibration

10
Electrode Calibration
  • I considered the electrode to be equilibrated
    when the potential stays within the same 0.3 mV
    range for 3 min
  • (Very slow equilibration time about two hours
    in the lowest activity samples)
  • Calibration and samples are analyzed in order of
    increasing activities, otherwise a much longer
    equilibration time is neccessary (especially when
    there is a large decrease in activity between two
    samples)

11
Calibration Curve
12
Cu2 by potentiometry
13
Procedures
  • Soil preparation
  • Soil is air-dried and ground to 2 mm
  • Shake 5.00 g of soil in 10.00 mL of 0.01 M CaCl2
    for 20 min
  • Centrifuge 10 min at 10000 g
  • Determination of pCu2
  • Electrode potential measured in 20-mL polystyrene
    cups shaken by hand (or with stirrer, but
    systematically)

14
Ionic Strength
  • Statistically significant but negligible ionic
    strength effect
  • where EP is in mV and IS is the ionic strength
  • The IS in the soil extracts is 0.020.01 so, one
    SD 0.314 mV (0.01 pCu2)

15
Aluminum Interference
16
Chloride Interference
  • Cu(II) is reduced at the electrode surface to
    Cu(I), which is stabilized by chloride
    complexation
  • The electrode the respond to a combination of
    Cu(II) and Cu(I), which also changes the
    Nernstian slope from 59 to 29 mV/decade
  • Critical Cl concentration around 10-1.4 M
    (Westall et al. 1979), which prevents the use of
    the Cu ISE in seawater (0.5 M Cl)

17
Other ISEs
18
Other ISEs
  • Cadmium and Lead
  • They are somewhat selective but could still
    possibly be used to measure Cu2
  • Might be prone to interferences from natural
    organic matter and/or oxides
  • Will be useful in synthetic solutions of known
    composition

19
Large selection
  • NH3, NH4, Br, Cd2, Ca2, CO2, Cl-, Cl2, Cu2,
    CN-, F-, I-, Pb2, NO3-, NO2-, NOx, O2, ClO4-,
    K, Redox, Ag/S2-, Na, SCN-
  • Analytical confidence needs confirmation, but
    many environmental applications could be better
    exploited
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