ARTICLE IN PRESS
JID: MOLSTR
[m5G;December 8, 2020;15:13]
F.M. Aqlan, M.M. Alam, A.S. Al-Bogami et al.
Journal of Molecular Structure xxx (xxxx) xxx
cia [20,21]. It is also responsible to pathological change of central
nervous system and finally the damage [22]. The various reports
have been claimed that the toxicity of cadmium is destroy the soil
ecosystem due to killing of microorganisms which are necessary
for fertility of soil [23]. Globally, the significant amount of cad-
mium is accumulated in environment due to number of anthro-
pogenic and man making activities. Industrially, Cd is widely used
as anticorrosive agent, to stabilize PVC goods, pigment in cooler, in
batteries and fertilizers [24–26]. There is a great possibility to af-
2.2. Synthesis of
2-oxo-2-phenyl-N-(4-(trifluoromethyl)phenyl)acetohydrazonoyl
bromide (5)(HB)
Method A: To stir the solution of dimethylphenacylsulfonium
bromide (2) (50.0 mmol) in ethanol (250.0 ml), it was added the
sodium acetate trihydrate (12.0 g) into the reactor. After stirring for
10 min, the mixture was cooled to −5 °C as well as treated with
4-(trifluoromethyl)benzen diazonium salt solution [prepared by di-
azotizing 4-(trifluoromethyl)aniline (50 mmol) in hydrochloric acid
(6.0 M, 6.0 ml) with sodium nitrite solution (3.5 g, 50.0 mmol),
fect human and animals with toxicity of Cd2 ion through food
+
chain. Thus, it is very important to check Cd2 ion contamina-
+
tion of environment with a reliable method. The existing methods
in H O (15.0 ml)]. The addition of the diazonium salt was car-
2
to detection of Cd2 ions are atomic absorption [27], ICP-ES (in-
ductively coupled plasma-optical emission spectrometry) [28] and
ICP-MS (inductively coupled plasma-mass spectroscopy) [29]. But
these methods are uncomforted with expensive, large and heavy
instruments, time consuming and unfavorable for in-situ detection.
Recently, a number of researches based on electrochemical ap-
proach are efficiently executed to overcome these drawbacks [30–
+
ried out with rapid stirring over the period of 60 min. Later the
reaction mixture was stirred for further 2 h at 0 °C and then
left for 6 h at 4 °C into the refrigerator. The resulting solid pre-
cipitate was collected by filtration, washed thoroughly with wa-
ter, then finally dried. The crude solid product was crystallized
from ethanol to afforded 9.5 g (70% yield) of 2-oxo-2-phenyl-N-
(4-(trifluoromethyl)phenyl)acetohydrazonoyl bromide.
3
3]. Thus, this study will be reported the synthesis of new com-
Method B: To a solution of dimethylphenacylsulfonium bromide
(2) (10 mmol) in ethanol (50.0 ml), it was added with the N-
nitroso-N-(4-(trifluoromethyl)phenyl)acetamide (4) (10 mmol). The
reaction mixture was warmed slightly and shaken till complete
dissolution of the reactants, then finally continuously stirred for
4 h. The precipitated crystalline product was collected, washed
with methanol and re-crystallized from ethanol to afford com-
pound with identical in all respects to those synthesized by
method A. Finally the product is fully characterized and analyzed
pound based on the hydrazonyl bromide backbone scaffold bear-
ing trifluromethyl moiety (HB). Furthermore, In this study, the de-
sired Cd2 metal ion sensor was fabricated using a GCE coated
+
with prepare HB as thin uniform layer and applied to detect Cd2
+
ion in phosphate buffer medium. The analytical performances of
sensor prove were inspected in detail in-term of sensitivity, repro-
ducibility, stability, efficiency, linear dynamic range and detection
limit. Besides this, it was effectively to measure Cd2 ion real en-
vironmental samples successively. Thus, this effectual process to
development of heavy metal ion sensor might be a most reliable
methodology in approaching future.
+
for melting point, mixed melting points, IR spectroscopy, and 1
H
NMR spectrum.
The physical data of the synthesized compound are listed be-
low:
2
. Experimental
orange solid; mp 157–159 °C; IR (KBr) v/cm 1: 3320 (NH),
−
1
1
702(CO), 1601 (C = N); H NMR (DMSO–d ): δ7.41–7.43 (m,
2
.1. Reagents and methodology
6
3
H, ArH), 7.65–7.69 (m, 4H, ArH), 7.92–7.94 (m, 2H, ArH),
1
1.18 (br s, 1H, NH, D O exchangeable);13C NMR (DMSO–d ):
All organic solvents were purchased from commercial sources
2
6
δ 117.0,120.1(q, 2JCF = 32.93 Hz), 124.2 (q, 1JCF= 270.10 Hz),
and used as received unless otherwise stated. From Sigma-Aldrich
USA), the analytical grade cobalt (II) nitrate, barium (II) nitrate,
1
26.14 (q, 3JCF = 6.55 Hz), 128.65,129, 134.32, 137.85, 146,
(
1
64, 185;19F NMR (DMSO–d ): δ −61.21; MS (m/z): 369
magnesium (II) chloride, silver nitrate, arsenic (III) chloride, zinc
sulfate, cadmium sulfate, mercury (II) chloride, chromium (III)
chloride and aluminum sulfate were procured and used with-
out farther any treatment. The other sub-ordinary chemical such
6
+
M ); C15H BrF N O: Anal. Calcd: C, 48.54; H, 2.72; N, 7.55.
10 3 2
(
Found C, 48.79; H, 2.64; N, 7.39%.
as NH , nafion (5% nafion suspension in ethanol), monosodium
2.3. Modification of glassy carbon electrode (GCE) using HB
3
and disodium phosphate buffer were implemented to fulfill this
study. All other chemicals were purchased from Merck, Aldrich or
Acros and used without further purification. Thin-layer chromatog-
raphy (TLC) was performed on pre-coated Merck 60 GF254 silica
gel plates with a fluorescent indicator, and detection by means
of UV light at 254 and 360 nm. The melting points were mea-
sured on a Stuart melting point apparatus and are uncorrected.
IR spectra were recorded on a Smart iTR, which is an ultra-high-
performance, versatile Attenuated Total Reflectance (ATR) sampling
accessory on the Nicolet iS10 FT-IR spectrometer. The NMR spec-
tra were recorded on a Bruker Avance III 400 (9.4 T, 400.13 MHz
for 1H, 100.62 MHz for 13C and 376.25 MHz for 19 F) spectrom-
eter with a 5-mm BBFO probe, at 298 K. Chemical shifts (δ in
2
The modification of GCE (Surface area: 0.0316 cm ) is the most
important task of this study before development of sensor HB/GCE
probe. Using ethanol, the prepared HB was subjected to make
thicker slurry and was to deposit onto the flat part of GCE as thin
uniform layer. Then, it was kept at laboratory conditions to dry
and smooth the fabricated film completely. To bringing the stabil-
ity of modified GCE during the electrochemical analysis in phos-
phate buffer medium, a drop of 5% nafion (1.0 μL) was added on
GCE and put inside a low temperature oven at 35 °C temperature
to dry. After complete the modification of GCE, an electrochemi-
cal cell was arranged with Keithley electrometer, the modified GCE
was used as working and a simple Pt-wire as counter electrode
ppm) are given relative to internal solvent, DMSO–d6 2.50 for 1
H
respectively. A series of Cd
2+
ion solution ranging the concentra-
and 39.50 for 13C. Mass spectra were recorded on a Thermo ISQ
Single Quadrupole GC–MS. Elemental analyses were carried out
on a EuroVector instrument C, H, N, S analyzer EA3000 Series.
dimethylphenacylsulfonium bromide (2) [34] and N-nitroso-N-(4-
tion as 0.1 nM ~ 0.01 mM were prepared in deionized water and
used as desired analyte. A curve known as calibration was plot-
ted as current versus concentration of Cd2 ion relation. The slope
+
of resulted calibration curve was used to estimate the sensitivity
and detection limit (DL) of desired Cd2 ion electrochemical sen-
sor. Considering the maximum linear segment in calibration curve,
the linear dynamic range (LDR) was identified and related all ana-
lytical parameters were also calculated from this range.
+
(trifluoromethyl)phenyl)acetamide (4) [35] were prepared accord-
ing to reported literature. For electrochemical analysis, the Keith-
ley electrometer (Model: 6517B, USA) was used to find the sensor
parameters.
2