Geeta A Zalmi1, Dinesh N Nadimetla1, Pooja Kotharkar2, Avinash L Puyad3, Meenal Kowshik2, Sheshanath V Bhosale1. 1. School of Chemical Sciences, Goa University, Taleigao Plateau, Goa 403206, India. 2. Department of Biological Sciences, BITS Pilani, K. K. Birla Goa Campus, Zuarinagar, Goa 403726, India. 3. School of Chemical Sciences, Swami Ramanand Teerth Marathwada University, Nanded, Maharashtra 431606, India.
Abstract
Cyanide is one of the highly poisonous pollutants to our environment and toxic to human health. It is important to develop the widely applicable methods for their recognition to secure safe uses for people coming into contact and handling cyanide and their derivatives. In this regard, the aggregation-induced emission materials possess high potential for the development of simple, fast, and convenient methods for cyanide detection through either "turn-off" or "turn-on". Among the AIE-based materials, tetraphenylethylene is a promising sensor for various sensing applications. In this paper, we have designed and synthesized a TPE-based chemosensor, which shows high sensitivity and displays good selectivity for cyanide (CN-) over others in the presence of interfering Cl-, I-, F-, Br-, HSO4 -, H2PO4 -, NO3 -, HCO3 -, and ClO4 - anions employed. The naked-eye, UV-vis, and fluorescence methods are employed to evaluate the performance of probe 1 toward CN- detection. From these experiments, CN- ions can be detected with a limit of detection as low as 67 nM, which is comparatively lower than that of the World Health Organization (WHO) permissible limit of the cyanide anion, that is, 1.9 μM. From the Job's plot, the 1:1 stoichiometric complexation reaction between probe 1 and CN- was found. The probe was efficiently applied for the detection of CN- ions using a paper strip method. The probe 1 also showed the potential of detecting CN- ions in various food items and in the cell line.
Cyanide is one of the highly poisonous pollutants to our environment and toxic to human health. It is important to develop the widely applicable methods for their recognition to secure safe uses for people coming into contact and handling cyanide and their derivatives. In this regard, the aggregation-induced emission materials possess high potential for the development of simple, fast, and convenient methods for cyanide detection through either "turn-off" or "turn-on". Among the AIE-based materials, tetraphenylethylene is a promising sensor for various sensing applications. In this paper, we have designed and synthesized a TPE-based chemosensor, which shows high sensitivity and displays good selectivity for cyanide (CN-) over others in the presence of interfering Cl-, I-, F-, Br-, HSO4 -, H2PO4 -, NO3 -, HCO3 -, and ClO4 - anions employed. The naked-eye, UV-vis, and fluorescence methods are employed to evaluate the performance of probe 1 toward CN- detection. From these experiments, CN- ions can be detected with a limit of detection as low as 67 nM, which is comparatively lower than that of the World Health Organization (WHO) permissible limit of the cyanide anion, that is, 1.9 μM. From the Job's plot, the 1:1 stoichiometric complexation reaction between probe 1 and CN- was found. The probe was efficiently applied for the detection of CN- ions using a paper strip method. The probe 1 also showed the potential of detecting CN- ions in various food items and in the cell line.
Cyanide anions inhibit
the mitochondrial electron transport in
respiratory chain via binding with a ferric form
of cytochrome P450.[1] The cyanide anions
are the most toxic and cause serious damage to human health such as
affecting the central nervous system and living environment.[2−5] Cyanide is extensively utilized in industrial factories particularly
in gold mining, synthetic fiber, herbicides, and electroplating technology,
and the presence of cyanide in environment and drinking water can
cause a variety of diseases.[6−9] Furthermore, cyanide salts have been employed in
the preparation of organic compounds and polymers, for example, nylon,
nitrile rubber, acrylo nitrile-based polymer and acrylic plastics.[10] These human activities in the modern industry
releases cyanide anions in the environment which ultimately enters
the human body via drinking water and the food chain.[5,11,12] The World Health Organization
(WHO) stipulates the permissible limit of cyanide anions in water
to about 1.9 μM.[13] As a result of
extreme toxic nature of cyanide anions in physiological and environmental
systems, the efficient detection of cyanide (CN–) ions is the need of the hour (instead of becoming very important
for investigators).[14] Therefore, the development
of an artificial probe with the potential of selectively recognizing
and sensing CN– ion species is being actively investigated.[15,16] The sensing methods are based on the formation of cyanide complexes
with transition-metal ions,[17] the displacement
method,[18] H-bonding interactions,[19,20] and luminescent approach.[21] However,
these cyanide anion sensors exhibit some drawbacks such as poor selectivity
in the presence of competing anions, for example, acetate and fluoride
anions.[22] To overcome these drawbacks,
nucleophilicity of CN– ions has been utilized.[23] This method shows advantages of CN– ion detection with high selectivity and sensitivity. This includes
the nucleophilic reaction of CN– ions with dibenzothiophene-based
barbituric derivative,[24] carbazole-based
sensor,[25] salicylaldehyde,[26] oxazine,[27] pyrylium,[28] acryltrizene,[29] acridinium,[30] squaranine,[31] trifluoroacetophenone,[32] imine,[33] and trifluoroacetamide[34] derivatives. Many researchers have developed
optical methods/systems such as colorimetric and fluorescent probes
for the detection of CN– ions with the naked eye.[35−38] However, these molecules suffer from few drawbacks such as low sensitivity,
tedious synthesis, being expensive, and naked-eye sensing. Therefore,
it is still challenging to develop a sensor for the detection of CN– ions with respect to the abovementioned criteria.In 2001, Tang et al. reported the new fluorescence phenomenon termed
aggregation-induced emission (AIE).[39] They
have demonstrated that the AIE probes emit no fluorescence in organic
solutions, while it is significantly emissive in aqueous solutions
via aggregate formation.[40] The AIE phenomenon
results due to restriction of intramolecular motion in the aggregates.
The sensing probes with AIE have attracted much attention for CN– ion detection not only due to ease synthesis but also
due to low cost and selectivity.[41−44]In this manuscript, we
report a simple and an efficient AIE active
molecular architecture 1 (Scheme ) for the detection of CN– ions. Compound 1 showed high selectivity and sensitivity
toward CN– ions in tetrahydrofuran (THF)/H2O (fwater = 99%). The results are monitored
by employing naked eye, UV–vis, emission, and 1H
NMR changes. Furthermore, compound 1-based paper strips
under visible and UV light showed excellent and high sensitivity for
CN– ion detection. Moreover, it was employed successfully
for CN– ion detection in living cells with an obvious
fluorescence change.
Scheme 1
Synthesis of Compound 1
Results and Discussion
Synthesis and Characterization
of Compound
Synthesis of
the target molecule ethyl(Z)-2-cyano-3-(5-(4-(1,2,2-triphenylvinyl)phenyl)thiophen-2-yl)acrylate 1 was achieved via a multistep synthetic
reaction strategy and is illustrated in Scheme . At the first stage, (2-(4-bromophenyl)ethene-1,1,2-triyl)tribenzene
(2) was easily prepared by condensing diphenylmethane
and (4-bromophenyl) (phenyl)methanone in the presence of n-BuLi followed by treating the intermediate with PTSA in dry toluene
at reflux temperature. The yield of compound 2 was as
high as 65%. The Suzuki coupling reaction between 2 and
(5-formylthiophen-2-yl)boronic acid resulted in the formation of 5-(4-(1,2,2-triphenylvinyl)phenyl)thiophene-2-carbaldehyde 3. The target compound 1 was obtained by reacting
compound 3 with ethyl 2-cyanoacetate via the Knoevenagel condensation reaction. The structure of compound 1 was confirmed by 1H NMR, 13C NMR,
and elemental analysis (for the details, see the Supporting Information).
AIE Characteristics of
Compound 1
After
successful synthesis and characterization of compound 1, we studied the mechanochromic properties by employing the process
of grinding, fuming, and heating, as illustrated in Figure . The compound 1 in its solid powder form displays strong golden yellow fluorescence
(quantum fluorescence yield Φ =
62.10) indicating AIE characteristics. We presume that the molecular
packing in the solid state leads to exhibit strong emission properties
due to restricted nonradiative relaxation pathways. However, it is
observed that upon grinding, the color changes from golden yellow
to bright yellow which is ascribed to the reduction in the crystalline
size of the molecular architecture. Furthermore, on fuming the compound 1 with acetone, the grinded material could not revert to its
original color intensity. However, when the compound 1 was heated, the luminescent properties were insignificantly changed
from bright yellow to yellow. Thus, compound 1 exhibited
significant mechanochromic characteristics with changes in fluorescence.
Figure 1
(a) Mechanochromic
properties of probe 1 displaying
the luminescence changing of it after grinding, fuming, and heating.
(b) PL of powder, grinding, fuming, and heating of probe 1.
(a) Mechanochromic
properties of probe 1 displaying
the luminescence changing of it after grinding, fuming, and heating.
(b) PL of powder, grinding, fuming, and heating of probe 1.Thus, the solid powder of compound 1 exhibits strong
golden yellow fluorescence. At first, we investigated the UV–vis
and emission spectra of the probe in different solvents such as THF,
acetonitrile (ACN), and dimethyl sulfoxide (DMSO). The results are
depicted in Figure . The compound 1 shows absorption peaks at 410, 430,
and 425 nm in THF, ACN, and DMSO (Figure a). Figure b shows that compound 1 displayed the
fluorescence emission peaks at 565, 567, and 628 nm in THF, ACN, and
DMSO solvents upon excitation at 410 nm, respectively. Herein, we
observed that in THF, compound 1 shows very weak emission
intensity as compared to ACN and DMSO. The UV–vis and emission
spectral study indicates that the solvent plays an important role
and attributed it as solvophobic effect.
Figure 2
Normalized spectra of
probe 1 in THF, acetonitrile,
and DMSO solvents: (a) UV–vis and (b) fluorescence emission
(λex = 410 nm), respectively.
Normalized spectra of
probe 1 in THF, acetonitrile,
and DMSO solvents: (a) UV–vis and (b) fluorescence emission
(λex = 410 nm), respectively.The compound 1 is insoluble in aqueous media, however,
displays good solubility in organic solvents, whereas its fluorescence
in a pure organic solvent is weak. With the addition of water fraction
from 0 to 99% in THF, compound 1 exhibits significant
fluorescence in a THF/H2O (fw = 99%) solvent mixture under visible (Figure a) as well as UV light (Figure b). The change in emission
properties suggests that the probe 1 clearly shows an
AIE effect. The AIE characteristics of compound 1 were
investigated using UV–vis absorption and fluorescence emission
spectra in the THF/H2O solvent mixture with different water
fractions (fw = 0 to 99%). UV–vis
absorption spectra of compound 1 in THF and THF/H2O are illustrated in Figure c. In THF, compound 1 exhibits the absorption
maxima at 418 nm. Upon addition of 99% water, compound 1 showed the prominent absorption maxima at 426 nm with a red shift
of 8 nm. This indicates that the addition of water leads to the formation
of J-aggregation of compound 1.
Figure 3
Photograph
of compound 1 (2 × 10–5 M) in
THF/H2O mixtures with different fw (0–99%) under (a) visible light and (b) 365 nm
UV light; (c) UV–vis absorption spectra in THF and THF/H2O fw (0 to 99%). (d) Fluorescence
emission spectra of the compound 1 in THF/H2O (v/v) mixtures with different water fractions at λex = 410 nm and (e) plot of relative fluorescence emission intensity
as a function of fw.
Photograph
of compound 1 (2 × 10–5 M) in
THF/H2O mixtures with different fw (0–99%) under (a) visible light and (b) 365 nm
UV light; (c) UV–vis absorption spectra in THF and THF/H2O fw (0 to 99%). (d) Fluorescence
emission spectra of the compound 1 in THF/H2O (v/v) mixtures with different water fractions at λex = 410 nm and (e) plot of relative fluorescence emission intensity
as a function of fw.The corresponding fluorescence emission spectra are illustrated
in Figure d. Upon
excitation at λex = 410 nm, compound 1 showed very weak emission spectra in THF solution at 565 nm (Figure d, green line). Upon
incremental addition of water (fw = 20,
40, and 60%), the fluorescence intensity slightly decreased with a
red shift may be due to small particular aggregates. A slight increase
in emission intensity was observed at fw = 80%. At 99% of water fraction in THF solution of compound 1, a significant fluorescence intensity enhancement was observed
(Figure d, red line).
Thus, the fluorescence quantum yields of compound 1 increased
from 1.3% in THF to 7.8% in THF/H2O solvent mixtures with
99% of water fraction. The change in emission intensity with % of
water in THF is illustrated in Figure d. These results indicated that the compound 1 possessed excellent AIE characteristics and exhibited the
highest fluorescence intensity in THF/H2O (fw = 99%).
Sensing Performance of Probe 1
To the
solution of 2 × 10–5 M compound 1 (coded as: “probe 1” onward) in DMSO,
a series of anions in its tetrabutylammonium salts of CN–, Cl–, I–, F–, Br–, HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– (8 × 10–5 M) were added. The changes in color
under day light and UV–vis (365 nm) light were monitored and
illustrated in Figure a,b, respectively. Under day light, probe 1 in DMSO
displayed yellow fluorescence color (Figure a). With the addition of anions, we observed
that except CN– ions, the solutions with the test
anions showed yellow color. While the probe 1 solution
in DMSO with only CN– ions exhibited red fluoroscent
color. As shown in Figure b, under UV–vis light at 365 nm, the solutions of probe 1 (buff in color) with the addition of different anions showed
buff color, whereas in the presence of CN– ions
displayed wine red color. These results indicate that the compound 1 detected CN– ions with good selectivity.
Thus, probe 1 can be utilized as a naked-eye colorimetric
and fluorescent sensor for CN– ions.
Figure 4
Solutions of probe 1 in DMSO; probe 1 is without any anions and
respective with the addition of 4 equiv
of tetrabutylammonium salts of CN–, Cl–, I–, F–, Br–, HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– with
probe 1: (a) under visible light (naked eye) and (b)
under UV light 365 nm, respectively.
Solutions of probe 1 in DMSO; probe 1 is without any anions and
respective with the addition of 4 equiv
of tetrabutylammonium salts of CN–, Cl–, I–, F–, Br–, HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– with
probe 1: (a) under visible light (naked eye) and (b)
under UV light 365 nm, respectively.
UV–Vis Absorption Study
The UV–vis absorption
spectra of probe 1 and with the addition of each anion
were studied and are illustrated in Figure a. Probe 1 in DMSO (2 ×
10–5 M) exhibited absorption maxima at 425 nm. The
UV–vis absorption of probe 1 with the addition
of each tested anion (8 × 10–5 M) displayed
almost no significant change except for CN– ion
addition. The addition of CN– ions showed pronounced
changes in the absorption spectra, the absorption maxima at 425 were
completely disappeared and a new band appeared at 345 nm with the
shoulder peak at 302 nm. The UV–vis absorption changes might
be due to the nucleophilic addition of CN– ions
to probe 1. This may cause interruption of intramolecular
charge transfer (ICT) effect which ultimately led to affect the optical
and photophysical characteristics. Thus, probe 1 can
be utilized for the detection of CN– ions with high
selectivity. To get detail insight, we titrated probe 1 with CN– ions in DMSO and the results are depicted
in Figure b. The UV–vis
absorption changes were monitored with the incremental addition of
CN– (0 to 8 × 10–5 M) ions
to probe 1 in DMSO. We observed that with the increase
in amount of CN– ions in probe 1, the
absorption maxima at 425 nm gradually decreased and completely disappeared
at 4 equiv of CN– ions. At the same time, new absorption
maxima at 345 nm appeared with increasing intensity along with a shoulder
peak at 302 nm. Herein, one isosbestic point at 365 nm also appeared.
These UV–vis absorption spectral changes are attributed to
a nucleophilic addition reaction between probe 1 and
CN– ions resulting in the molecular structure changes.
Figure 5
UV–vis
absorption spectra of probe 1 (2 ×
10–5 M) in the presence of (a) 4 equiv of Cl–, I–, F–, Br–, HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– (8 × 10–5 M) as tetrabutylammonium salts
and CN– ions as a tetraethylammonium salt. (b) Addition
of the tetraethylammonium salt of CN– (0 to 8 ×
10–5 M) in DMSO.
UV–vis
absorption spectra of probe 1 (2 ×
10–5 M) in the presence of (a) 4 equiv of Cl–, I–, F–, Br–, HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– (8 × 10–5 M) as tetrabutylammonium salts
and CN– ions as a tetraethylammonium salt. (b) Addition
of the tetraethylammonium salt of CN– (0 to 8 ×
10–5 M) in DMSO.
Fluorescence Emission Study
A fluorescence emission
spectral study was performed to investigate the detection performance
of probe 1 toward CN– ions in DMSO.
The obtained results are illustrated in Figure a,b. As shown in Figure a, the probe 1 in DMSO upon
excitation at 410 nm exhibited the fluorescence emission band at 628
nm. With the addition of series of anions, tetrabutylammonium salts
of CN–, Cl–, I–, F–, Br–, HSO4–, H2PO4–, NO3–, HCO3–, and
ClO4– (8 × 10–5 M), the changes in the emission band at 628 nm were monitored. The
fluorescence spectra (628 nm) of probe 1 did not display
significant changes even with the addition of 4 equiv of each tested
anion except for CN– ions. It was observed that
in the presence of CN– ions, the emission intensity
of probe 1 at 628 nm completely disappeared. This is
attributed to the breaking of ICT of probe 1. Fluorescence
titration experiments were performed to investigate the sensing ability
of probe 1 with the incremental addition of CN– ions (0–8 × 10–5 M). The changes in
fluorescence emission spectra were recorded and are depicted in Figure b. As illustrated
in Figure b, with
the incremental addition of CN– ion to probe 1, the fluorescence emission band at 628 nm gradually decreased
and finally disappeared.
Figure 6
Emission spectra of probe 1 (2
× 10–5 M) in the presence of (a) 4 equiv of
Cl–, I–, F–,
Br–, HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– (8 × 10–5 M) as tetrabutylammonium salts
and CN– ions as
a tetraethylammonium salt. (b) Addition of the tetraethylammonium
salt of CN– (0 to 8×10–5 M)
in DMSO.
Emission spectra of probe 1 (2
× 10–5 M) in the presence of (a) 4 equiv of
Cl–, I–, F–,
Br–, HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– (8 × 10–5 M) as tetrabutylammonium salts
and CN– ions as
a tetraethylammonium salt. (b) Addition of the tetraethylammonium
salt of CN– (0 to 8×10–5 M)
in DMSO.Subsequently, the quantum yield
of the probe 1 (Φ)
was estimated and found to be 6.3 in DMSO at room temperature. As
shown in Figure b,
the fluorescence intensity gradually decreased and disappeared with
the addition of CN– ions (4 equiv) and the quantum
yield of the 1:CN– decreased to 0.09.
This fluorescence emission behavior is attributed to the selective
detection of CN– ions.
Stoichiometry Analysis
and Binding Constant
In order
to determine the binding mode between probe 1 and CN– ion, the Job’s plot and Benesi–Hildebrand
plot[45] were analyzed and are illustrated
in ESI, Figure S1. The plot of changes
in fluorescence emission intensity against the molecular fraction
of [1]/[1+CN–] is illustrated
in Figure S1a. Job’s plot results
clearly indicate a 1:1 stoichiometric complexation reaction between
probe 1 and CN–. The Benesi–Hildebrand
plot (Figure S1b) was employed to determine
the binding constant (K) between probe 1 and CN– ions. The linear relationship of fluorescence
emission intensity as a function of [CN–] from 0
to 4 equiv (R = 0.9831) was found graphically. The
binding constant (Ka) of 1 with CN– was found to be 4.78 × 106 M–1.
Limit of Detection
The calculated
limit of detection
(LOD = 3σ/S), where σ is the standard
deviation of the blank sample and S is the absolute
value of the slope between fluorescence emission intensity and concentration
of CN– of the probe 1 is 67 nM, which
is very low as compared to the maximum permissible level of CN–, according to the WHO (1.9 mM) agency guide lines
(Figure S2, Table S2). This suggests that
the probe 1 could be employed as a sensitive fluorescent
probe for the quantitative detection of CN– at nanomolar
levels.
Competitive CN– Ion Binding
In order
to explore the specificity of the probe 1 as an anion-selective
fluorescence sensor for CN– ions, competitive experiments
of probe 1 were carried out by utilizing various anions
(4 equiv) as the interfering anions. As depicted in Figure S3, the blue bar corresponds to the probe 1 with the tested anions (F–, Cl–, Br–, I–, HSO4–, H2PO4–, OAc–, NO3–, ClO4–, and HCO3–), whereas
the red bar corresponds to the probe 1 with one of the
tested anions in the presence of CN– ions. It was
observed that CN– could clearly diminish the fluorescence
of probe 1 in the presence of other anions. The abovementioned
results strongly suggest that the tested anions has no effect on probe 1 for CN– ion detection. Thus, probe 1 could be employed as a fluorescence sensor for CN– ion recognition with outstanding selectivity and good anti-interference.
CN– Detection Mechanism by 1H NMR
Spectra of 1 and 1 in the Presence of CN–
To confirm the binding mechanism of the CN– ion with the probe 1, 1H NMR
experiments were performed in DMSO-d6 and
are illustrated in Figure . Probe 1 exhibits a characteristic peak at δ
8.55 ppm, attributed to the vinylidene proton “H1” (Figure a). Upon addition of TEACN (1.2 equiv) to the probe 1, the peak at 8.55 ppm in 1H NMR completely disappeared,
while the new peak at 5.09 ppm was observed. This peak was assigned
to H2 (Figure b). Subsequently, thiophene proton peaks move significantly
to higher frequencies. This leads to alteration in the original molecular
architecture of probe 1. These results indicate that
CN– ions with strong nucleophilicity attacked the
vinylideneC=C bond and break the ICT between electron donor
TPE and the electron acceptor functional group of the probe 1.
Figure 7
1H NMR spectral changes of probe 1: in
DMSO-d6 (a) and upon the addition of 1.2
equiv CN– anions (b).
1H NMR spectral changes of probe 1: in
DMSO-d6 (a) and upon the addition of 1.2
equiv CN– anions (b).
Theoretical Calculations
To further investigate the
sensing properties of 1 toward the CN– ion detection mechanism and photophysical characteristic changes,
density functional theory (DFT) and time-dependent DFT (TD-DFT) calculations
were performed. The results of the calculations carried out have been
obtained using the Gaussian 09 ab initio/DFT quantum
chemical simulation package.[46] The geometry
optimization of molecules in the series 1 and 1-CN– was carried out at the B3LYP/6-31G* level
of theory. In order to confirm the minima, frequency calculations
also have been carried out at the same level. The frontier molecular
orbitals (FMOs) of 1 and 1-CN– are generated using Avogadro[47,48] and are illustrated
in Figures and S4. The highest occupied molecular orbital (HOMO)
of probe 1 was mainly delocalized on the tetraphenylethylene
(TPE) moiety and thiophene ring system, whereas the lowest unoccupied
molecular orbital (LUMO) was distributed over the phenyl ring of TPE,
thiophene subunit, and nitrile functional group. In contrast, the
HOMO of 1-CN– was located on the ethylcyanoacetate
subunit along with the new CN– moiety, while the
LUMO was mainly delocalized over the TPE and thiophene ring system.
These results suggested that the introduction of the CN– subunit had an impact on the charge transition properties of the
probe 1. The DFT calculations were in agreement with
the experimental results, which suggested that the nucleophilic addition
reaction of CN– ions and probe 1 takes
place by reacting with the C=C bond. This resulted in the inhibition
of the ICT effect of 1 with the addition of CN–. Furthermore, the geometries of probe 1 and 1:CN– obtained at the B3LYP/6-31G* level were subjected
to TD-DFT studies using the B3LYP/6-31G* level for charge-transfer
excitations. TD-DFT results were analyzed by employing Gauss-Sum 2.2.5
program,[49] TD-DFT results obtained are
reported in Table S1, it shows LUMO density
toward cyanide, which is already discussed in the literature.[56] From the TD-DFT results, it is seen that probe 1 (Figure S5) has absorption with
high intensity compared with 1:CN– (Figure S6). Calculation of the HOMO and LUMO
from CV is shown in Table S3.
Figure 8
Optimized geometric
structures of 1 and 1:CN– are shown.
Optimized geometric
structures of 1 and 1:CN– are shown.
Test Strip for CN– Detection Using Probe 1
To employ the probe 1 for practical
purpose, we prepared the test strip using chloroform solution and
examined the detection of CN–. The results are depicted
in Figure S7a,b. The test paper of probe 1 is in yellow color. It was found that in sunlight, the paper
strip test paper of 1 changed its color from yellow to
colorless after CN– addition (Figure S7a), whereas other anions do not display any impact.
Moreover, we also investigated the color change on strip 1 under 365 nm UV light. It was observed that fluorescence of the
probe 1 changed from dark yellow to colorless (Figure S7b).
Application of Probe 1 in Food Samples
Furthermore, to investigate the
application of probe 1 in food analysis, we selected
food samples containing cyanogenicglycosides including bitter almonds, sweet potato, and sprouting potato
to check the utility of probe 1 to check the endogenous
cyanide.[50,51] The food samples were prepared by crushing
and pulverizing 10 g of food samples using mortar and pestle. After
that, 10 mL of water was added followed by the addition of 5 mg of
NaOH under constant stirring for 10 min and then the mixture was centrifuged
for 20 min and the mixture of cyanide-containing solution was obtained.[52,53] Upon the addition of cyanide-containing solution to the probe, the
fluorescence completely disappears, as shown in Figure . Therefore, the probe 1 could
be effectively and potentially used for detecting cyanide in cyanogenicglycoside-containing food samples. The details are as follows: a solution
of probe 1 in DMSO was taken in 5 different test vials.
To each vial, probe 1, water 2, NaOH 3, food extract 4, and TEACN–5 were added, respectively. It was observed that under
UV–vis light illumination at 365 nm, there was a significant
change in fluorescence, wherein complete quenching of fluorescence
takes place upon the addition of TEACN and food extract (Figure S9).
Figure 9
Vial “A” contains stock
solution of probe 1 in DMSO, and vial “B”
contains stock solution of probe 1 plus the respective
food sample. Images are taken separately
and included together in the single figure.
Vial “A” contains stock
solution of probe 1 in DMSO, and vial “B”
contains stock solution of probe 1 plus the respective
food sample. Images are taken separately
and included together in the single figure.
Application of Probe 1 in Living Cells
Cell Cytotoxicity
HeLa cells were stable until a concentration
of 30 nM, however, 10 nM showed a percentage viability of 100% even
after 24 h of incubation with probe 1. This shows that
10 nM concentration of probe 1 is not cytotoxic to HeLa
cells and hence the same was used for fluorescence uptake studies
(for details, see experimental Figure S8).
Cell Imaging
Figure a,b shows the HeLa cells under bright field and FITC
fluorescence filter, respectively. When the HeLa cells were incubated
with 10 nM of the probe 1 and observed under bright field
(Figure c) and FITC
fluorescence filters, the green fluorescence observed (Figure d) clearly shows that probe 1 is taken up by the cells and the cells remain viable. Upon
the addition of CN–, the presence of cells was confirmed
in the bright-field image (Figure e), however, no fluorescence was seen under the FITC
filter, clearly indicating the fluorescence quenching of probe 1 in HeLa cells, due to the reaction between intracellular
cyanide and probe 1 (Figure f). Thus, these results indicate that the
probe 1 penetrates through the HeLa cells and detects
the CN–. We believe that in future, probe 1 and similar AIE-active compounds could find potential applications
as in vivo fluorescence sensors for the detection
of CN– in live cells.
Figure 10
(a) HeLa cells in bright
field, (b) no auto fluorescence observed
in HeLa cells using an FITC filter, (c) HeLa cells incubated with
probe 1 in bright field, (d) HeLa cells with probe 1 exhibiting green fluorescence, (e) HeLa cells with probe 1 and CN in bright field, and (f) HeLa cells with probe 1 and CN in green fluorescence.
(a) HeLa cells in bright
field, (b) no auto fluorescence observed
in HeLa cells using an FITC filter, (c) HeLa cells incubated with
probe 1 in bright field, (d) HeLa cells with probe 1 exhibiting green fluorescence, (e) HeLa cells with probe 1 and CN in bright field, and (f) HeLa cells with probe 1 and CN in green fluorescence.Table S2 shows the comparison of probe 1 with small organic molecules used for cyanide sensing in
the literature. Inspite of the literature study of organic molecules
used for selective cyanide sensing with good LOD’s, however,
they suffer drawbacks of either lack of test strip, cell imaging,
or AIE activity.[54,55] Thus, our probe 1 is shown to be superior as compared with the literature probe, as
it produces very good LOD along with naked eye detection, colorimetric
fluorescence, and test strip as well as cell imaging.
Conclusions
In summary, we have successfully synthesized a probe 1 and employed for sensing of anions. Probe 1 shows naked
eye colorimetric and fluorescent sensing of CN– (tetraethylammonium
salt) selectively over other anions such as Cl–,
I–, F–, Br–,
HSO4–, H2PO4–, NO3–, HCO3–, and ClO4– (as a
tetrabutylammonium salt) used in this study in a DMSO solvent. The
selectivity and sensitivity for CN– ions with probe 1 are found to be very high. The probe 1 exhibited
very low LOD, that is, 67 nM. Furthermore, a paper strip was developed
to display the CN– sensing and also probe 1 was employed for the detection of CN– ions
from various food components. Furthermore, probe 1 was also used to
detect CN– ions in living cells, which clearly suggested
that the probe 1 could be a good sensor for practical
applications.
Experimental Section
Chemicals and Reagents
Compounds 2 and 3 were obtained through
the procedure mentioned in the literature,[54] and probe 1 was synthesized by
reacting ethyl cyanoacetate and 5-(4-(1,2,2-triphenylvinyl)phenyl)thiophene-2-carbaldehyde 3, in the presence of ammonium acetate and acetic acid as
a solvent. Various anions of tetrabutylammonium salts (Cl–, I–, F–, Br–, HSO4–, H2PO4–, HCO3–, NO3–, and ClO4–) and
tetraethylammonium cyanide (CN–) salt and DMSO were
purchased from Sigma-Aldrich and TCI. 1H NMR spectra were
recorded on 400 MHz and 13C NMR using a 100 MHz Bruker
spectrometer. Tetramethylsilane (TMS) was used as an internal standard.
The CDCl3-d and DMSO-d6 were used as a deuterated solvent. Mass spectrometric
data were obtained using a positive electron spray ionization (ESI-MS)
technique on an Agilent Technologies 1100 Series (Agilent Chemistation
Software) mass spectrometer. UV–vis absorption spectra were
recorded using a UV–vis-1800 Shimadzu spectrophotometer and
fluorescence emission was measured on an Agilent, Carry Eclipse spectrofluorophotometer.
UV–Vis and Fluorescence Experiments
UV–Vis and Fluorescence
of the Probe 1 upon
the Addition of 4 equiv Anions
The 2 mL probe 1 (2 × 10–5 mol/L) in DMSO was placed in solution
in the quartz cell, and the absorption and fluorescence spectra were
recorded. Different anions (8 × 10–5 M) were
added as salts such as TBANO3, TBAF, TBACN, TBAH2PO4, TBACl, TBABr, TBAHCO3, TBAI, TBAHSO4, and TEACN, and the absorption and fluorescence spectra were
recorded at room temperature.
UV–Vis and Fluorescence
Titration of the Probe 1 upon
the Addition of CN– Anions
The 2 mL probe 1 (2 × 10–5 mol/L) in DMSO was placed
in solution in the quartz cell and fraction of TEACN (0–8 ×
10–5 M) ion solution was added, and the corresponding
absorption and fluorescence spectra of the probe were recorded at
room temperature.
Naked-Eye Detection
The stock solution
of the probe 1 was prepared by (2 × 10–5 mol/L)
dissolving it in DMSO solvent. The various anions of salt forms such
as TBANO3, TBAF, TBACN, TBAH2PO4,
TBACl, TBABr, TBAHCO3, TBAI, TBAHSO4, and TEACN
dissolved in DMSO (2 × 10–3 M) were added,
and the pictures were taken under visible light and UV light 365 nm.
Paper Strip Preparation
Test strips were prepared and
immersed in the solution of the probe in chloroform. The strips were
air-dried. These test strips were used for detecting cyanide in the
presence of other anions. The test strips were observed under a UV
lamp and used for easy naked-eye detection.
Sensing of Cyanide in Food
Samples
A solution of probe 1 (0.5 mL) in DMSO
was taken in a test vial, and second, vial
probe 1 (0.5 mL) and food extract were added (see details
in the Results and Discussion section), respectively.
It was observed that under UV–vis light illumination at 365
nm, there was significant change in fluorescence, wherein complete
quenching of fluorescence takes place upon the addition of food extract.
Cell Toxicity of Probe 1
For determining
the cytotoxicity of probe 1, HeLa cells were initially
grown in culture media comprising Dulbecco’s modified Eagle’s
medium (DMEM) supplemented with 5% fetal bovine serum. The exponentially
growing cells were then seeded at a density of 5 × 104 cells per well in a 96-well plate and incubated for 24 h in an environment
with 5% CO2 at 37 °C temperature. Subsequently, probe 1 was added to the wells at concentrations ranging from 10
to 100 nM and incubated for 24 h. The cells were given a PBS wash
and 0.5 mg/mL of MTT solution prepared in DMEM was added to the wells
and incubated for 4 h. The obtained formazan crystals were dissolved
in DMSO and the concentration of formazan crystals was measured using
a multiwell spectrophotometer (Schimadzu Multiskan Go) using untreated
cells as the control. All the experiments were carried out in triplicates.
Cell Imaging
For the detection of cyanide in a biological
system, HeLa cells were used to check the uptake of probe 1. HeLa cells were seeded on sterile cover slips in 12-well plates
at a density of 5 × 104 cells per well and incubated
at 37 °C for 24 h with 5% CO2 in a CO2 incubator
(Thermoscientific). The cells were then incubated with 10 nM conc.
of probe 1 for 60 min and imaged using an epifluorescence
microscope (Olympus Inverted Trinocular Microscope). Furthermore,
to check whether the fluorescence is affected by quenchers such as
cyanide, the cells treated with probe 1 were again incubated
with cyanide for 30 min and the fluorescence was observed under an
epifluorescence microscope.
Authors: Kishor S Jagadhane; Sneha R Bhosale; Datta B Gunjal; Omkar S Nille; Govind B Kolekar; Sanjay S Kolekar; Tukaram D Dongale; Prashant V Anbhule Journal: ACS Omega Date: 2022-09-21