In: Chemistry
Determination of the chloride ion in water sample (e.g swimming pool or tap water) by two different analytical methods:
1) Voltammetry
:
It is easy-to-operate and highly sensitive free chlorine
determination method using differential
pulse voltammetry(DPV) with an Au
working electrode has been developed. This method can be used to
monitor the residual free chlorine concentration in drinking water.
The electrochemical measurements were carried out using a single
compartment cell. An Au disk (1.6 mm diameter), Ag/AgCl (saturated
KCl) and Pt wire is used as the working, reference and counter
electrodes, respectively. For pretreatment of the Au working
electrode, the surface of the electrode is polished with an
aluminium oxide suspension, carefully sonicated in water, and then
rinsed with Milli-Q water. A 0.1 mole/dm3 potassium
chloride solution us as the supporting electrolyte. The
pH of solution for the DPV measurements was adjusted to 5 using
acetate buffer solution. To a 20 cm3 water sample, potassium
chloride is added until the final concentration is 0.01
mole/dm3. All measurements are carried out at room
temperature thermostated at about 25 °C. A set of measurements of
different concentration is done ti plot a calibration curve.
The limit of
detection (LOD) was estimated
using the 3ЅB/m IUPAC criteria, where m
is the slope of the linear calibration plot and the ЅB
correspond to the standard deviation of the sensor response in the
absence of chlorine (blank). The detection limit of this method is
0.04 mg Cl /dm3.
2) Iodometry
:
The indirect iodometric titration method or iodometry deals with
the titration of iodine liberated (as
triiodide,i.e.,I3―) in chemical reactions. This
titration method is one of the oldest methods for determining
chlorine, and is generally used for the total chlorine
determination above 1 mg/L Cl2. To determine chlorine in
a sample solution, a small excess of potassium iodide (KI) is added
to the sample solution to react with chlorine to form the triiodide
(I3-) as shown in equation below―
Cl2 + 3I―→ I3―+ 2Cl―
The triiodide thus formed is then titrated with a sodium thiosulfate (Na2S2O3) solution as:
I3― + 2S2O3― → 3I―+ S4O62―
In the titration of above equation starch is added at the beginning of the titration as an end-point indicator. The end-point of the titration is indicated by the disappearance of the blue coloured starch-iodide complex. The titration method is usually performed at a sample pH between 3 - 4. It has been shown that sample temperatures above 20°C can produce significant errors if starch is used as the titration end-point indicator. This indicated the release of triiodide from the starch helix is temperature-dependent. In order to get the maximum accuracy, iodometric titrations using the starch indicator should be performed at sample temperatures less than 20°C. A “back titration” should be performed for waters containing potential chemical interferences. In the back titration, a known amount of thiosulfate is added in excess of the chlorine in the sample solution to completely reduce the chlorine. The amount of unreacted thiosulfate is then titrated with a standard iodine solution. The total chlorine is calculated from the amount of the reacted thiosulfate. Since, sensitivity of the iodometric titration is not very high, it requires a large volume of sample to titrate the sample with a low chlorine concentration.