Speciation and Complexation of Cd in Soil Solutions
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Transcript Speciation and Complexation of Cd in Soil Solutions
Metal speciation using
ion-selective electrodes
Sébastien Sauvé
Department of Chemistry
Université de Montréal
[email protected]
© Sauvé 2002
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
© Sauvé 2002
Avdeef et al. 1983
© Sauvé 2002
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)
© Sauvé 2002
Cupric Ion-Selective Electrodes
Linear, Nernstian response down to pCu2+ of:
7 in dilute copper salts solutions (60 µg·L-1)
19 using solutions copper-buffered with ligands
of known stability constants (10-19 M or 60 ag·L-1)
Simple equipment
Extensive literature
© Sauvé 2002
Cupric Ion-Selective Electrodes
Interferences
Ionic strength variations
• Need a relatively uniform IS
Aluminum
Mercury
Chloride
Electrode surface is sensitive
© Sauvé 2002
Cupric Electrode Calibration
Suggested Cu-IDA calibration solutions have:
• 1·10-3 M IDA
• 1·10-4 M Cu(NO3)2
• 6·10-3 M NaOH
• 2.5·10-3 M KHphthalate
• 1·10-2 M CaCl2 (media)
• pH adjusted with HNO3
Use IDA stability constants reported in the
literature, interpolated to 0.02 ionic strength
© Sauvé 2002
Calibration
Simultaneously
determine the pH for calculations of pCu2+
IDA-Cu Calibration Buffer
-3
Free Cu2+ log(x) M
-5
-7
-9
-11
-13
-15
2.00
3.00
4.00
5.00
6.00
pH
© Sauvé 2002
7.00
8.00
9.00
10.00
Calibration
pH
10.00
9.95
9.90
9.85
9.80
9.75
9.70
9.65
9.60
…
© Sauvé 2002
pCu2+
13.53
13.52
13.51
13.49
13.48
13.46
13.44
13.42
13.39
pH
8.00
7.95
7.90
7.85
7.80
7.75
7.70
7.65
7.60
pCu2+
11.43
11.34
11.26
11.17
11.08
11.00
10.91
10.82
10.74
pH
6.00
5.95
5.90
5.85
5.80
5.75
5.70
5.65
5.60
pCu2+
8.51
8.46
8.40
8.35
8.30
8.24
8.19
8.14
8.09
pH
4.00
3.95
3.90
3.85
3.80
3.75
3.70
3.65
3.60
pCu2+
6.45
6.40
6.35
6.29
6.24
6.18
6.13
6.08
6.02
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)
© Sauvé 2002
Calibration Curve
Calculated pCu2+
2
4
pCu = -0.03027 EP + 10.23
corr. R 2 = 0.997***
6
8
10
12
14
-100
-50
0
50
100
150
Electrode Potential (mV)
200
250
Cu2+ by potentiometry
Free Cu (pCu2+)
2.0
4.0
6.0
8.0
10.0
y = -0.0299x + 10.107
12.0
R2 = 0.9948
14.0
300
200
100
0
Electrode potential (mV)
© Sauvé 2002
-100
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…)
© Sauvé 2002
Ionic Strength
Statistically significant but
negligible ionic strength effect
EP 32.07 pCu2 32.45 IS 340.4
(corr .R 2 0.991* * * )
where EP is in mV and IS is the ionic strength
© Sauvé 2002
The IS in the soil extracts is 0.02±0.01 so,
one SD = 0.314 mV (~0.01 pCu2+)
Aluminum Interference
3
pCu2+
4
5
pCu2+
0.1 mM Al
No Al
6
7
125
150
175
200
Electrode Potential (mV)
225
250
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)
© Sauvé 2002
Other ISEs
Electrode Potential (mV)
Pb-ISE Calibration
-100
-150
-200
-250
-300
-350
y = -24.571x - 87.952
2
R = 0.9431
-400
-450
13 12 11 10 9
8
7
pPb2+
© Sauvé 2002
6
5
4
3
2
Other ISE’s
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
© Sauvé 2002
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
© Sauvé 2002