Abstract:
Rapid industrialization and urbanization has no doubt improved the quality oflife.
However its adverse effects are severe pollution of air, water and soil due to mobilization
of several harmful metals and organic pollutants into the environment. Environmental
pollution by toxic metals is well recognized and their toxicity leads to the accumulation
of toxins in ourtissues and organs. Presence of metals trace concentration in animal life
is useful but at higher concentration toxic effects appears and life is subjected to many
nutritional deficiencies, neurological disorders and can even lead to autoimmune
disorders, cancer and other debilitating chronic diseases. It is normally difficult for
anyone to avoid exposure to harmful metals as they are widely prevalent in environment
due to their presence in almost all products of modern consumerism viz. construction
materials, cosmetics, medicines, processed foods, variety offuel and various agricultural
products. In view of toxicity of these metals and their understood occurrence in the
environment, it is important to monitor these pollutants. A number of analytical
techniques such as Atomic Absorption Spectrometry, Inductive Coupled Plasma-Mass
Spectrometry, Ion Chromatography, Flame Photometry, Cyclic voltametry, isotopic
dilution, radiometric activation analysis are available for quantitative analysis of metals
present in the environmental samples. These techniques provide accurate results but their
maintenance and operational cost is high and requires adequate expertise and large scale
infrastructure back up. Thus, the analysis is generally limited to laboratory level only. A
reliable, low cost, quick and portable analytical technique is often required especially for
the analysis of large number of samples and such requirements are often met with ion
selective electrodes (ISEs) to a significant extent. The technique is generally non
destructive, adaptable to small sample volume with possible applications in real-time
analysis. Moreover, analysis of coloured and viscous samples can also be carried out
easily. Further the technique involves a number of advantages such as simple set up, low
cost and very convenient to use for online measurement. Due to these advantages the
determination of concentration of a particular ion using an ISE has taken a leading place
among all electrochemical methods of analysis. ISEs find application in a variety of
fields like clinical, environmental, industrial, agricultural and process monitoring, as well
as detectors in HPLC and capillary electrophoresis. As a result, a number of good ion
sensors have been developed and marketed which are now convenient tools for analysis.
These ion sensors have been used for the quantification of metals in food products,
biological fluids, soil, effluents and wastewater.
Membrane ion selective electrodes consist of a semi-permeable membrane that
separates two solutions of different concentrations of an appropriate electrolyte and
responds selectively to particular ion, even in the presence of other ions. The membrane
constituent is normally an active ion-exchanger ingredient generally called an ionophore
or electroactive material. In spite of great utility of ion sensors in analysis, it has not been
possible to prepare them for many ions of importance, mainly due to the non availability
of good ionophores. It is obvious that the development of good ion sensors requires an
ionophore which has high affinity for a particular cation/anion and poor for others but such
materials are not available in abundance. Due to importance of ion sensors various types of
materials such as solid electrolytes, inorganic and organic ion exchangers, insoluble salts
of multivalent metals, metal chelates, macrocycles, calixarenes, Schiff base, hydrogen
bonding receptors, other neutral carriers have been used as ionophores for the
development of ion selective electrodes. In recent past, intensive studies on the design
and synthesis of highly selective and sensitive ion-carriers as sensory molecules and their
applications as ion-selective electrodes for the routine assessments of various ions have
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been reported. However, many ofthese electrodes have not been very successful as they
exhibit a significant interference to other ions, poor sensitivity and selectivity, high
response time and function over a limited pH range. Therefore, it is desirable to further
explore different materials for the preparation of membranes which may act as selective
sensor for target ions.
The development ofpotentiometric membrane-based ion sensor with analytically
useful selectivity remains a formidable challenge. Work for developing new ISEs ofhigh
selectivity is always a useful goal. We have, therefore, explored some newly synthesized
and previously reported compounds as ionophores and used their membranes as ISEs for
some metals. For the sake of convenience, simplicity and clarity, the work embodied in
the thesis has been organized as following six chapters.
First Chapter; General Introduction:
It presents an up-to-date review of the literature on sensors of alkaline, alkali
earth, transition, rare earth metal ions and anions. The problem of present research
activities have also been posed in the context of the cited work.
Second Chapter; Theory andMethodology ofIon Selective Electrodes:
This encompasses classification of ISEs, theory of membrane electrodes, its
potentials and terms used in the study of ion selective electrode. The concept of the
selectivity of ion selective membranes and methods of its determination has also been
discussed.
Third Chapter; Schiffbaseas copper ionselective electrodes:
It is reported that Schiff base have been widely used as chelating ligands in the
coordination chemistry of transition metals and some of them show selective affinity for
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metals. It is, therefore, possible to use Schiff bases as selective ionophores in the
preparation of membrane electrodes of better characteristics. To test this possibility in a
realistic fashion, we investigated them as potential sensory component for the
development of membrane ion-selective electrodes. In this chapter, the synthesis and
characterization of 2-[{(2-hydroxyphenyl)imino}methyl]-phenol (Li) and 2-[{(3-
hydroxyphenyl)imino}methyl]-phenol (L2), and their analytical application as ionophores
for the fabrication of Cu2+ ion selective electrodes are described. Polymeric membranes
electrodes (PME) of Li and L2 have been prepared and investigated as Cu -selective
sensors. Poly (vinyl chloride) (PVC) was used as matrix for the sensor's design and
influence of the other membrane components i.e. ionophore, plasticizer and the lipophilic
additive that are known to have a dramatic effect on sensor's performance have also been
evaluated. Effect of various plasticizers viz., dibutyl phthalate (DBP), dibutyl sebacate
(DBS), benzyl acetate (BA), o-nitrophenyloctylether (o-NPOE) was studied in detail and
improved performance was observed in several instances by the addition of oleic acid
(OA) as anion excluder. Optimum performance for the electrodes based on Li was
observed with membrane having ingredients in composition Li:DBS:OA:PVC =
6:54:10:30 (%, w/w). This sensor worked satisfactorily in the concentration range 3.2 x
10"8 to 1.0 x 10"2mol L"1 with aNernstian slope of 29.5 mV decade"1 of acu2+ and having
01 1 the detection limit as 2.0 x 10" mol L" (1.27 ng mL" ). Optimization of membrane
composition of the electrodes based on L2 showed that the membrane having composition
L2:DBP:OA:PVC = 6:54:10:30 (%, w/w) exhibit the Nernstian slope (29.6 ± 0.5
mVdecade" of aa, ) and showed linear potential response in the concentration range of
2.5 x 10"7- 1.9 x 10"2 mol L"1 with limit of detection 1.2 x 10"7 mol L"1. Wide pH range
(3.0 •*- 8.5), fast response time (5 s), good performance in presence of small amounts of
(up to 20 % v/v) non-aqueous contents and adequate shelf life (3 months) indicate the
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utility of the proposed sensors. The selectivity coefficients for these electrodes were
determined by matched potential method (MPM) and the results indicate their selective
response for Cu +ions over various interfering ion. However, it was found that the sensor
based on ionophore (Li) has good selectivity over the sensor based on ionophore (L2).
These electrodes could be successfully used for the determination of copper in edible
oils, tomato plant material; river water and as an indicator electrode in potentiometric
titration of copper ion with EDTA.
Fourth Chapter; Gd3+ ion-selective coated graphite electrode based on N5 donor
chelating ligand:
This chapter incorporates investigation on the use of a N5 donor chelating ligand
as ionophore in the preparation of membrane electrode selective to Gd3+. Chelating
ligand 2,6-Bis-[l-{N-cyanoethyl,N-(2-methylpridyl)}aminoethyl]pyridine (L3) having
five nitrogen donor sites for complexation with cations has been synthesized. Stability
studies of the several metal-ligand complexes showed that L3 has high affinity towards
Gd +ion and therefore, it was used as a potential ionophore for the preparation ofcoated
graphite Gd ion selective electrode. Among several electrodes prepared, the one having
membrane of composition L3:NaTPB:PVC:o-NPOE = 8:4:30:58 (%, w/w) gave best
performance over the widest working concentration range of 2.8 x 10"7- 5.0 x 10"2mol L"
1showing Nernstian behaviour (19.6 ±0.3 mV decade"1) with lower limit ofdetection as
o 1 6.3 x 10" mol L" . Furthermore, it showed a fast response time (12 s) and can be used for
2.5 months without significant divergence in its characteristics. Further, the electrode can
tolerate the concentration of different surfactants upto 1.0 x lO^mol L"1 and can be used
successfully in ethanol 30 % (v/v) and methanol and acetonitrile 10 % (v/v) water
mixture. The useful pH range of this electrode for the detection of Gd3+ in a solution is
2.0 to 8.0. The potentiometric selectivity coefficients of the electrode were evaluated by
IUPAC recommended fixed interference method (FIM) and matched potential method
(MPM) and it was found that the electrode is sufficiently selective for Gd3+ over many
cations and could be used for the determination of Gd ions in waste water and rock
samples. It could also be used successfully as an indicator electrode in the potentiometric
titration of GdCl3 with EDTA.
Fifth chapter; Nation-selective coated graphite electrodes based on lariat
ethers:
This chapter describes the synthesis of novel lariat ethers viz 1,5-
di(cyanoethane)-2,4: 7,8:13,14-tribenzo-l,5-diaza-9,12-dioxacyclopentadeca-2,7,13-
triene (L4) and 1,5-di (cyanoethane)-2,3, 4-pyridine-7,8:13,14-dibenzo-l,3, 5-triaza-9,
12-dioxa cyclopentadeca-2,7,13-triene (L5) and their application as potential ionophores
for the fabrication of Nd selective and sensitive coated graphite electrodes.
Complexation study of the two ionophores towards various metal ions in acetonitrile
solutions revealed the formation of 1:1 metal-ionophore complexes. A number of PVC
based coated graphite electrodes (CGEs) of L4 with different plasticizers and lipophilic
additives were prepared and explored as Nd3+ selective electrodes. The results showed
that optimized membrane composition for the electrode based on L4 was found to be;
L4:o-NPOE:NaTPB:PVC = 5:57:3:35 (%, w/w). This electrode exhibited good
performance over the wide working concentration range 8.4 x 10"8 - 3.1 x 10"2 mol L"1
with Nernstian slope (19.8 ± 0.4 mVdecade"1 ofam3+) and low detection limit (3.8 x 10"8
mol L"). However, the electrode based on L5 having optimum membrane composition of
its ingredients L5:o-NPOE:NaTPB:PVC = 5:53:3:39 (%, w/w) performed best over the
widest working concentration range of 4.6 x 10"8-5.0 x 10"2mol L"1 with Nernstian slope
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(19.7 ± 0.5 mVdecade"1 of aNd3+) and low detection limit (1.6 x 10"8 mol L"1). The
potentiometric response of these electrodes was excellent in the range of pH 3.5 to 7.6
and they showed fast response time of 14 s and 10 s, for L4 and L5 based CGEs,
respectively with a shelf life of three months without significant divergence in the
performance characteristics. They could also tolerate up to 20%(v/v) methanol, ethanol
and acetonitrile, if present in the test solution. The presence of cationic and anionic
surfactants at 1.0 x 10"* mol L"1 or above caused significant interference in the
performance of the electrodes. Further, the values of selectivity coefficients determined
by FIM indicate that the proposed electrodes are efficiently selective over a number of
monovalent (Ag+, Na+, K+, Li+), divalent (Hg2+, Fe2+, Co2+, Ni2+, Cd2+, Mg2+, Ca2+, Zn2+,
Cu2+) and trivalent ions (Gd3+, Pr3+, Ce3+, La3+, Tb3+, Dy3+ Sm3+ and Yb3+). However,
higher concentration of Co2+, La3+, Pr3+ and Yb3+ caused some interference. These
electrodes were used successfully as indicator electrodes in the potentiometric titration of
Nd against EDTA and also direct determination ofNd3+ ions from binary mixtures and
water samples.
Sixth chapter; Ccf+ ion-selective electrodes based on N4, N2S2 and N2O2 type
chelating ligands:
This chapter describes the synthesis, characterisation and analytical application of
three chelating compounds N!,N2 -dicyanoethyl-N',N2-bis(pyridine-2-ylmethyl)benzene-
1,2-diamine [L6], N1,N2-dicyanoethyl-N1,N2-bis(thiophen-2-ylmethyl) benzene-1, 2-
diamine [L7] and N1,N2-dicyanoethyl-N1,N2-bis(furan-2-ylmethyl)benzene-l,2-diamine
[L8]. Membranes having constituents PVC, plasticizers, lipophilic anionic additives and
the ionophores were coated on the surface of spectroscopic graphite rods and their
potential response investigations carried out. The electrodes having membranes of
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different compositions were investigated and it was found that the among all the
electrodes of L^, the one having membrane composition in the ratio L^.o-
NPOE:NaTPB:PVC as 4:51:2.5:42.5 (%, w/w) performed best i.e. worked over a wide
working concentration range 2.5x10" -1.0x10" mol L" with Nernstian slope 29.5±0.07
1 R 1 mV decade" and low detection limit 7.8x10" mol L" . This electrode generated constant
potential in the pH range 2.0 to 8.0 with a fast response time (12 s) and shelf life of 4
weeks. The CGE based on L7 having membrane composition L7:o-NPOE:NaTPB:PVC =
3:52.5:1.5:43 (%, w/w) performed best i.e. widest linear working concentration range
1.7xl0"8 - l.OxlO"1 mol L"1 with Nernstian slope 29.6±0.08 mV decade"1 and lower
detection limit as 7.0x10"9 mol L . The useful pH range ofthis electrode was observed to
be 2.6 to 8.0. This electrode showed a fast response time of 7 s towards Cd2+ ion and the
potentiometric characteristics of the electrode do not change significantly over a period of
6 weeks. A similar optimization of membrane composition of the electrodes based on Lg
showedthat the electrode with composition L8:o-NPOE:NaTPB:PVC = 7:49:3.5:40.5 (%,
w/w) showed best performance in terms of wide working concentration range (4.6x10"7 -
5.0xl0"2 mol L"1), Nernstian slope (29.8± 0.05 mV decade"1) and low detection limit
Q 1 (8.4x10" mol L"). The response of the electrode is fast (17 s) and can work satisfactorily
in the pH range 3.0 to 7.5 with a shelf life of 4 weeks. Selectivity coefficients of the
electrodes were evaluated by FIM and the results showed that these electrodes have high
selectivity towards Cd2+ over a large number of cations and could tolerate upto 20 %
(v/v) non-aqueous impurity. In view of high sensitivity and selectivity, the utilityof these
electrodes was tested in the potentiometric determination of Cd2+ in medicinal plants, soil
and industrial waste water. They could also be used successfully as an indicator electrode
inthe potentiometric titration of Cd2+ against EDTA.
Thus, the present investigations on the membranes of Schiffs bases, chelating
ligands and lariat ethers have resulted in the development of selective and sensitive
sensors for Cu2+, Gd3+, Nd3+ and Cd2+ ions. The investigated sensors ofmetal ions have
been found to be better than reported sensors with respect to various response
characteristics and resulted in the availability of some improved and novel ion sensors
which can be used successfully for analytical purposes. Thus, the present work adds to
our knowledge in the field of chemical sensors