In summary, a benzothiazolium derivative-based
colorimetric and fluorescent chemosensor has been
presented. It can be used for selective detection of
mercury ions in presence of competing metal ions,
including Cd2+, Fe2+, Co3+, Cu2+, Zn2+, Pb2+, Ca2+,
Na+ and K+ ions. The detection limits of the
colorimetric and fluorescent method for mercury
ions are 15.3 and 11.8 ppb, respectively. The
formation of Hg2L2 complex between L and Hg2+
ions led to a significant transfer of electron density
from ligands to the metal ions, and broke the π-
electron conjugated system. This is important cause
leading to fluorescence quenching and color change
in the complex
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Vietnam Journal of Chemistry, International Edition, 54(6): 692-698, 2016
DOI: 10.15625/0866-7144.2016-00389
692
A benzothiazolium-derived colorimetric and fluorescent chemosensor
for detection of Hg2+ ions
Doan Thanh Nhan
1,4
, Nguyen Khoa Hien
2
, Nguyen Thi Ai Nhung
3
, Nguyen Van Binh
1
,
Nguyen Chi Bao
1
, Duong Tuan Quang
1*
1
Department of Chemistry, Hue University of Education, Hue University
2
Mientrung Institute for Scientific Research, Vietnam Academy of Science and Technology
3
Department of Chemistry – Hue University of Sciences, Hue University
4
Kontum Department of Education and Training
Received 10 August 2016; Accepted for publication 19 December 2016
Abstract
A benzothiazolium-derived colorimetric and fluorescent chemosensor (L) for detection of mercury ions has been
prepared. The detection limits of the colorimetric and fluorescent method for mercury ions are 15.3 and 11.8 ppb,
respectively, much lower than the reported chemosensors based on similar derivatives of benzothiazolium. The
optimized molecular structures, absorption and fluorescence characteristics of the chemosensor and its complex with
mercury ions were carried out using the calculations at the B3LYP/LanL2DZ level of theory, combination with Atoms
in Molecules and Natural Bond Orbitals analyses.
Keywords. Colorimetric, fluorescent, chemosensor, Hg
2+
ions, benzothiazolium.
1. INTRODUCTION
Mercury is of great concern in the toxic heavy
metals and the least abundant in the crust of the Earth
[1]. At the concentration levels of ppb, mercury ions
can cause the negative impacts on the environment,
animals, plants and humans. Mercury ions are toxic
and danger to most living organisms at the higher
concentration levels [2,3]. On humans, mercury can
cause the changes in the structure of DNA and
damage to the brain, gingivitis, stomatitis, digestive
system and cause neurological disorders, even death.
It is also believed to be associated with spontaneous
abortion and congenital malformation [4-8].
The development of analytical methods for
heavy metals, especially mercury ions, at ppb levels,
has been attracting the attention of scientists [9-10].
In particular, the optical methods, including
colorimetric and fluorescence methods, are of
particular interest because they are simple, less
expensive, as well as imaging methods for using in
the fieldwork or in the living cells [11-13]. Until
now, a number of colorimetric and fluorescent
chemosensors for detection of mercury ions have
been reported. However, most of the developed
chemosensors have some defects, for instance, low
sensitivity, the effects of competitive metal ions, and
working in a large amount of organic solvents. As a
result, the scientists are continuing efforts to develop
the new chemosensors for detection of mercury ions
[14, 15]. Many different dye and fluorescent
compounds have been used as the the original
substances for design of the colorimetric and
fluorescent chemosensors to detect mercury ions,
including derivatives of naphthalene [16],
rhodamine [17], fluorescein [18], dansyl [19],
dimethylaminocinnamaldehyde [20], and
benzothiazole [15], etc. However, the fluorescent
chemosensors for detection of mercury ions based
on benzothiazole derivatives, including
benzothiazolium derivatives, are still very little
reported until now. The limits of detection for
mercury ions of most published chemosensors are
still quite high, from 214 to 1767 ppb [15, 21, 22]. In
our previous work [23], we reported the design and
preparation of a benzothiazolium hemicyanine
derivative. Its complex with Hg
2+
may be used for
selective and sensitive sensing of thiol biomolecules
through the reversible visual color and florescence
changes. In this work, a further investigation on this
benzothiazolium hemicyanine derivative with the
combination of quantum chemical calculations and
VJC, 54(6) 2016 Duong Tuan Quang, et al.
693
experiments is carried out for the purpose of Hg
2+
detection. It can be used as a colorimetric and
fluorescent chemosensor for determination of
mercury ions with the significantly low detection
limits, 15.3 and 11.8 ppb, respectively.
2. MATERIALS AND METHODS
2.1. Instruments
The experimental UV-Vis and fluorescence
properties were investigated by Shimadzu
spectrometers, including UV-1800 UV-vis
spectrophotometer and RF-5301 PC Series
fluorescence spectrometer. All computational
investigations were performed at the Laboratory of
Computation Science and Modeling of Quy Nhon
University (Vietnam), using a Supercomputer
Operating System (32-cores processor, 72-gigabytes
memory).
2.2. Reagents
2-Methylbenzothiazole, 4-diethylamino-2-
hydroxybenzaldehyde, bromopropionic acid, all amino
acids, and all perchlorate or chloride salts of metal
cations were obtained from Sigma - Aldrich, without
further purification. All used solvents were HPLC
reagents and surely free of fluorescent impurities.
2.3. Computational methods
Geometry optimizations of molecules were
calculated by applying the B3LYP density
functional theory with the LanL2DZ basis set 24,
25], using the Gaussian 09 program 26]. The excited
states and other time-dependent factors were carried
out using the time-dependent density functional
theory (TD-DFT) 27]. The chemical bonding and
electronic properties of molecules were evaluated
based on the interaction energies (E
(2)
) between the
donor of a natural bond orbital (NBO) and acceptor
of a NBO, obtained from the NBO analysis, using
NBO 3.1 program implemented in Gaussian 09 [28].
3. RESULTS AND DISCUSSION
A benzothiazolium-derived chemosensor L was
synthesized from the reaction of the 2-methyl-
benzothiazole and bromoacetic acid, followed by the
condensation reaction with 4-diethylamino-2-
hydroxybenzaldehyde in ca. 60% overall yield. The
structures of intermediate and final products were
confirmed by
1
H NMR,
13
C NMR, and mass spectra
[23]. The synthetic route was showed at scheme 1.
Scheme 1: The synthetic route to chemosensor L
Figure 1a shows that the free L exhibits a
characteristic absorption band peaked at 540 nm in
an ethanol/water solution (7/3, v/v). The molar
extinction coefficient of free L is determined and
very high (ca. 10
4
M
-1
.cm
-1
at 540 nm, in an
ethanol/HEPES solution). Upon the addition of Hg
2+
ions to the L solution, there is an increasing intensity
in a new absorption band at 460 nm, whereas there is
a gradually decreasing signal at 540 nm. The color
of the solution is changed gradually from pink (λmax
= 540 nm) to orange (λmax = 460 nm). Furthermore,
an isosbestic point is obviously observed at 490 nm.
These results indicate that there is a concentration
conversion of the light-absorbing compounds in the
solution.
350 400 450 500 550 600 650
0.0
0.2
0.4
0.6
0.8
(a)
Hg
2+
A
b
s
o
rb
a
n
c
e
Wavelength / nm
550 600 650 700
0
50
100
150
200
250
Hg
2+
F
lu
o
re
s
c
e
n
c
e
I
n
te
n
s
it
y
(
a
.u
.)
Wavelength / nm
(b)
Figure 1: Absorbance (a) and Fluorescence (b)
titration spectrum of L (3.10
-6
M) with Hg
2+
(0-1.5
equiv) in EtOH/H2O (7/3, v/v)
VJC, 54(6) 2016 A benzothiazolium-derived colorimetric and
694
In contrast, the free L shows a red emission at
585 nm in solution with a fluorescence quantum
yield of 0.175 based on rhodamine B solution as a
reference. The fluorescence intensity of L solution is
gradually quenched when Hg
2+
ions are added. It is
almost completely quenched (about 95 %) upon the
addition of one equivalent of Hg
2+
ions, and then no
more change in the fluorescence intensity is
observed when Hg
2+
ions are more added (figure
1b). These results indicate that Hg
2+
ions reacted
with L in 1:1 stoichiometry. Upon the addition of 1
equiv of Cysteine to the solution resulted from the
reaction between 1 equiv of Hg
2+
and 1 equiv of L,
the fluorescence intensity is restored to the original
value of free L. It indicates that Hg
2+
ions reversibly
react with L.
Figure 2: The optimized geometry of Hg2L2 at
the B3LYP/LanL2DZ level of theory
The most stable structure of the 1:1 interaction
between Hg
2+
and L is identified at the
B3LYP/LanL2DZ level of theory and is shown in
figure 2. The proposed interaction mechanism
between L and Hg
2+
ions is presented in scheme 2.
Scheme 2: The proposed interaction mechanism
between L and Hg
2+
The changes in UV-Vis and fluorescence spectra
of the L and Hg2L2 complex were elucidated by
theoretical investigations. The TD-DFT method was
used at the same level optimized structure to
calculate the excited states of L and Hg2L2 complex.
The calculated results were listed in table 1. Table 1
shows that the singlet electronic transitions from
ground states (S0) to excited states (Si) in the L and
Hg2L2 complex are mainly contributed by the S0→S2
transitions because the oscillator strength (f) of these
transitions are much stronger than that of the other
transitions.
Table 1: Calculated excitation energy (E), wavelength (λ), and oscillator strength (f) for
low-laying singlet state of L and Hg2L2
Compound Main orbital transition
TD-DFT/B3LYP/LanL2DZ
CIC
a
E(eV) (nm) f
L S0 S1 HOMO−1 LUMO 0.62576 2.05 604.7 0.0043
HOMO LUMO -0.32210
S0→S2 HOMO−2→LUMO -0.26505 2.18 569.7 0.1044
HOMO−1→LUMO 0.28864
HOMO→LUMO 0.58734
S0→S3 HOMO−3→LUMO 0.40392 2.33 533.0 0.0282
HOMO−2→LUMO 0.53836
HOMO−1→LUMO 0.13894
HOMO→LUMO 0.16346
Hg2L2 S0 S1 HOMO−1 LUMO -0.12571 1.31 948.3 0.1026
HOMO LUMO 0.43803
HOMO LUMO+1 0.53118
S0→S2 HOMO−1→LUMO 0.12116 1.40 888.0 0.6065
HOMO−1→LUMO+1 -0.13429
HOMO→LUMO 0.54547
HOMO→LUMO+1 -0.40365
S0→S3 HOMO−1→LUMO 0.49543 1.59 778.0 0.1175
HOMO−1→LUMO+1 0.47484
a
CIC expansion coefficients for the main orbital transitions.
VJC, 54(6) 2016 Duong Tuan Quang, et al.
695
In L, the S0→S2 transition energy is 2.18 eV
(569.7 nm). This transition resulted in the maximum
absorption peak at 560 nm in the UV-Vis spectra of
L. In three main orbital transitions of the S0→S2
transition, including the HOMO−2→LUMO,
HOMO−1→LUMO and HOMO→LUMO
transition, the HOMO→LUMO is transition
between two continuous MOs, therefore the PET
process does not occur, and this transition gave rise
to a red emission at 585 nm.
In the Hg2L2, the complexation leads to a
significant transfer of electron density from ligands
to the metal ions, resulting in the small energy gap
of HOMO and LUMO, about 1.39 eV. The
excitation and emission wavelengths will be shifted
to longer wavelength than 888 nm. As a result, there
is no significant strong peak in absorbance and
fluorescence spectra. It could be the cause of
fluorescence quenching in the complex.
Table 2: Significant second-order interaction energies (E
(2)
) between donor and acceptor orbitals in
benzothiazolium moieties of L and Hg2L2 (in kcal.mol
-1
, at the B3LYP/LanL2DZ level of theory)
Donor NBO
(i)
Acceptor NBO (j) E
(2)
Donor NBO (i) Acceptor NBO
(j)
E
(2)
L Hg2L2
π(C1-C2) π*(C3-C4) 19.44 π(C1-C2) π*(C3-C4) 21.64
π*(C1-C2) π*(C3-C4) 226.02 π*(C5-C6) π*(C1-C2) 71.76
π(C1-C2) π*(C5-C6) 22.30 π(C1-C2) π*(C5-C6) 24.93
π(C3-C4) π*(C1-C2) 22.02 π(C3-C4) π*(C1-C2) 19.39
π(C3-C4) π*(C5-C6) 25.33 π(C3-C4) π*(C5-C6) 30.17
π(C5-C6) π*(C1-C2) 19.66 π(C5-C6) π*(C1-C2) 19.34
π*(C5-C6) π*(C1-C2) 136.44 π*(C5-C6) π*(C3-C4) 77.75
π(C5-C6) π*(C3-C4) 16.45 LP(N7) π*(C5-C6) 20.97
π*(C5-C6) π*(C3-C4) 97.79 LP(N7) σ*(C8-S9) 12.65
π(N7-C8) π*(C5-C6) 12.95 LP(N7) π*(C8-C10) 16.63
π*(N7-C8) π*(C5-C6) 25.51 π(C5-C6) π*(C3-C4) 14.77
LP(S9) π*(C5-C6) 14.60 σ*(C8-S9) σ*(C6-S9) 11.42
LP(S9) π*(N7-C8) 28.44 LP(O25) σ*(C11-C24) 11.81
LP(O25) σ*(C11-C24) 17.13 LP(O25) LP*(C24) 139.46
LP(O25) σ*(C24-O26) 17.88 LP(O26) σ*(C11-C24) 14.84
LP(O25) σ*(C24-O25) 19.90 LP(O26) σ*(C24-C25) 19.31
LP(O25) π*(C24-O26) 115.15 LP(O26) LP*(C24) 176.95
LP(O26) σ*(C11-C24) 20.81 LP(O25) LP*(Hg(a)) 31.61
LP(O26) σ*(C24-O25) 18.95 LP(S9) LP*(Hg(b)) 51.90
LP(O26) LP*(Hg(b)) 10.96
The results obtained from NBO analysis as listed
in table 2 show that the π-electron conjugated
system of benzothiazolium moiety (as a fluorophore)
in free L extends throughout from C1 to C8 (see
Scheme 1 for numbering scheme), as evidenced by
the existence of π bonds with significantly large
degree of interaction energies (E
(2)
), including
π(C1−C2), π(C3−C4), π(C5−C6), and π(N7−C8)
bonds. These findings confirm that the free L is a
fluorescent compound with properties similar to
VJC, 54(6) 2016 A benzothiazolium-derived colorimetric and
696
those of the benzothiazolium derivatives.
The NBO analysis results also confirm that the
complexation of Hg2L2 is due to the contributions of
these metal-ligand interactions, including
O25 Hg(a), S9 Hg(b), O26 Hg(b), with
interaction energies (E
(2)
) for these interactions being
31.61, 51.90 and 10.96 kcal.mol
-1
, respectively. The
presence of these new interactions leads to break the
π(N7−C8) bond and creates the new π(C8−C10)
bond. As a result, the π-electron conjugated system
of fluorophore (benzothiazolium moiety) is broken
at the N7 atom. This is important cause leading to
fluorescence quenching in the complex.
350 400 450 500 550 600 650 700
0.0
0.2
0.4
0.6
0.8
1.0
Other ions
Cu
2+
Hg
2+
Sensor
A
b
s
o
rb
a
n
c
e
Wavelength / nm
550 600 650 700
0
50
100
150
200
250
Hg
2+
Other ions
Cu
2+
Sensor
F
lu
o
re
s
c
e
n
c
e
I
n
te
n
s
it
y
(
a
.u
)
Wavelength / nm
Figure 3: Absorbance (a) and fluorescence (b)
spectra of L (3.10
-6
M) with different metal ions (5
equiv each) in EtOH/H2O (7/3, v/v) [Hg
2+
, Cd
2+
,
Fe
2+
, Co
3+
, Cu
2+
, Zn
2+
, Pb
2+
, Ca
2+
, Na
+
, K
+
]
The selectivity of L for Hg
2+
ions in the presence
of other metal ions is also surveyed. Figure 3 shows
that there is no significant changes in the absorption
spectra and fluorescence spectra when 5 equiv of
competing metal ions is added to the L solution,
including Cd
2+
, Fe
2+
, Co
3+
, Cu
2+
, Zn
2+
, Pb
2+
, Ca
2+
,
Na
+
and K
+
ions. These results indicate that the L
can be used as a colorimetric and fluorescent
chemosensor for selective detection of Hg
2+
ions in
the presence of surveyed competing metal ions.
The possibility of using L as a colorimetric and
fluorescent chemosensor for quantitative detection
of Hg
2+
ions is also surveyed.
0 100 200 300 400
0.0
0.1
0.2
0.3
0.4
0.5
(a)
Linear Regression for DATA1_B:
Y = A + B * X
Parameter Value Error
---------------------------------------
A 0.0118 0.0052
B 0.0011 0.0000
---------------------------------------
R SD N P
---------------------------------------
0.999 0.008 9 <0.0001
---------------------------------------
V
a
ri
a
ti
o
n
o
f
a
b
s
o
rb
a
n
c
e
[Hg
2+
], ug/L
0 100 200 300 400
0
20
40
60
80
100
120
140
(b)
Linear Regression for DATA1_B:
Y = A + B * X
Parameter Value Error
--------------------------------
A -0.99 0.35
B 0.31 0.00
--------------------------------
R SD N P
--------------------------------
0.999 0.57 9 <0.0001
--------------------------------
V
a
ri
a
ti
o
n
o
f
fl
u
o
re
s
c
e
n
c
e
i
n
te
n
s
it
y
(
a
.u
.)
[Hg
2+
], ug/L
Figure 4: Variation of absorbance at 540 nm (a) and
variation of fluorescence intensity at 585 nm (b)
of L (3.10
-6
M) in EtOH/H2O (7/3, v/v) vs the
concentration of Hg
2+
ions (0-400 µg/L)
Figure 4a shows that there is a good linear
relationship between the variation of absorbance of
L solution and the concentration of Hg
2+
ions. In the
concentration range of Hg
2+
ions from 0 to 400 μg/L,
the following equation was found from calibration
curves: ΔA540 = (0.01±0.01) + (0.0011±0.0000) ×
[Hg
2+
], R = 0.999. It indicates that L can be used as
a colorimetric chemosensor for quantification of
Hg
2+
ions. The limit of detection and limit of
quantification for Hg
2+
ions are 15.3 μg/L and 51.2
μg/L, respectively.
Figure 4b also indicates that the fluorescent
chemosensor L can be used to detect quantitatively
Hg
2+
ions. With concentrations of Hg
2+
ions ranging
from 0 to 400 μg/L, a good linear relationship was
recorded between variation of fluorescence intensity
of L and concentration of Hg
2+
to lead a calibration
curve: ∆I585= (-1.0±0.4) + (0.3±0.0) × [Hg
2+
], R=
0.999). The limit of detection and limit of
VJC, 54(6) 2016 Duong Tuan Quang, et al.
697
quantification for Hg
2+
ions are 11.8 μg/L and 39.3
μg/L, respectively.
4. CONCLUSION
In summary, a benzothiazolium derivative-based
colorimetric and fluorescent chemosensor has been
presented. It can be used for selective detection of
mercury ions in presence of competing metal ions,
including Cd
2+
, Fe
2+
, Co
3+
, Cu
2+
, Zn
2+
, Pb
2+
, Ca
2+
,
Na
+
and K
+
ions. The detection limits of the
colorimetric and fluorescent method for mercury
ions are 15.3 and 11.8 ppb, respectively. The
formation of Hg2L2 complex between L and Hg
2+
ions led to a significant transfer of electron density
from ligands to the metal ions, and broke the π-
electron conjugated system. This is important cause
leading to fluorescence quenching and color change
in the complex.
Acknowledgment. This research is funded by the
Vietnam National Foundation for Science and
Technology Development (NAFOSTED) under grant
number 104.04-2014.35 (DTQ).
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Corresponding author: Duong Tuan Quang
College of Education, Hue University, Hue City, Vietnam
No 34, Le Loi, Hue City
E-mail: duongtuanquang@dhsphue.edu.vn; Telephone: 0914050126.
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