Nishtha Khansili1, Prayaga Murali Krishna1. 1. Department of Basic and Applied Science, National Institute of Food Technology Entrepreneurship and Management (NIFTEM), Haryana 131028, India.
Abstract
The work reports on zinc oxide bentonite nanocomposite (ZnOBt) chemical route synthesis, characterization, and investigation of curcumin (Cur) functionalization for a label-free colorimetric detection of total aflatoxins (AFs) in foods. XRD of ZnO nanoparticles (NPs) confirmed the wurtzite structure (2θ = 36.2°) and that of ZnOBt showed the intercalated interlayer composite phase. The Debye-Scherrer relation calculated the crystallite size as 20 nm (ZnO) and 24.4 nm (ZnOBt). Surface morphology by SEM exhibited flower-like hexagonal, rod-shaped ZnO NPs on the bentonite surface. Colorimetric reaction involved two-stage redox reactions between ZnOBt and dye Cur followed by AFs phenolic group and Zn(Cur)OBt. Cur gets oxidized at its diketone moiety in the presence of ZnOBt to form a red colored complex Zn(Cur)OBt, which further scavenge protons from AFs phenolic group, and gets oxidized to AFs-Zn(Cur)OBt (yellow). Binding of AFs-Zn(Cur)OBt is characterized by FT-IR ascribed to C-H bending (1966.615 cm-1), O-H stretching (3256.974 cm-1), and C=O stretching (1647.362 cm-1). 1H NMR chemical shifts (δ) (ppm) showed an increase in proton at the aliphatic region (0 to 4.4) while removal of proton in ether at 4.4 to 6 regions. Job plot calculation using UV-Vis data resulted in a higher total AF binding coefficient of Zn(Cur)OBt (K a = 3.77 × 106 mol-1 L) compared to Zn(Cur)O (K a = 0.645 × 106 mol-1 L) as well as a molar ratio of 1:1 by the Benesi-Hildebrand plot equation. Corn and almond food samples showed the total AFs LOD of 2.74 and 4.34 ppb, respectively. The results are validated with standard LC/MS-MS in compliance with MRL value as per the regulatory standard (EU).The NP-based method is facile and rapid and hence can be utilized for onsite detection of total AFs in foods.
The work reports on zinc oxide bentonitenanocomposite (ZnOBt) chemical route synthesis, characterization, and investigation of curcumin (Cur) functionalization for a label-free colorimetric detection of total aflatoxins (AFs) in foods. XRD of ZnO nanoparticles (NPs) confirmed the wurtzite structure (2θ = 36.2°) and that of ZnOBt showed the intercalated interlayer composite phase. The Debye-Scherrer relation calculated the crystallite size as 20 nm (ZnO) and 24.4 nm (ZnOBt). Surface morphology by SEM exhibited flower-like hexagonal, rod-shaped ZnONPs on the bentonite surface. Colorimetric reaction involved two-stage redox reactions between ZnOBt and dye Cur followed by AFsphenolic group and Zn(Cur)OBt. Cur gets oxidized at its diketone moiety in the presence of ZnOBt to form a red colored complex Zn(Cur)OBt, which further scavenge protons from AFsphenolic group, and gets oxidized to AFs-Zn(Cur)OBt (yellow). Binding of AFs-Zn(Cur)OBt is characterized by FT-IR ascribed to C-H bending (1966.615 cm-1), O-H stretching (3256.974 cm-1), and C=O stretching (1647.362 cm-1). 1HNMR chemical shifts (δ) (ppm) showed an increase in proton at the aliphatic region (0 to 4.4) while removal of proton in ether at 4.4 to 6 regions. Job plot calculation using UV-Vis data resulted in a higher total AF binding coefficient of Zn(Cur)OBt (K a = 3.77 × 106 mol-1 L) compared to Zn(Cur)O (K a = 0.645 × 106 mol-1 L) as well as a molar ratio of 1:1 by the Benesi-Hildebrand plot equation. Corn and almond food samples showed the total AFs LOD of 2.74 and 4.34 ppb, respectively. The results are validated with standard LC/MS-MS in compliance with MRL value as per the regulatory standard (EU).The NP-based method is facile and rapid and hence can be utilized for onsite detection of total AFs in foods.
Aflatoxins
have major subtypes as B1, G1, B2, and G2 and are n class="Disease">carcinogenic,
heterocyclic, oxygenated, stable difuranocoumarins metabolites of Aspergillus flavus and Aspergillus
parasiticus, prevalent mostly in cereals, nuts, and
tree nuts.[1] Lately, 20 different subtypes
of AFs are known, which occur naturally in feed and foods. Whilst
13 of them are naturally produced by mold, the rest are known as toxic
metabolized derivatives produced by animals, microorganisms, and humans.[2] Out of them, aflatoxin M1 (AFM1) is very important
and requires major attention to combat its prevalence in dairy products.
Meanwhile, other derivatives are also prevalent since they can rapidly
invert to the potent AFB1 and can become intermediate for synthesis
of other potent mycotoxins. Hence, due to the higher risk evidence
of parent AFs and its derivative molecule as a carcinogen for animals
and humans, the International Agency for Research on Cancer (IARC)
reported AFs as a class I carcinogen.[3] The
analysis by the Council for Agriculture Science and Technology (CAST)
reported that, each year, a significant proportion of world’s
crop (especially corn) and oilseed supply would be contaminated with
AFs.[4] As a result of which, several countries
have adapted distinct maximal residual action limit for AFs for food
in the range of 8 to 30 ppb.[5−8]
Of late there are different chromatographic
and mass spectroscopic
analytical techniques available for AFs detection in agricultural
food crops and feeds.[5,9,10] Additionally,
commercial rapid detection kits[11−17] are effortless and quick. They involve high-grade AFs-selective
antibody, aptamer, and DNA-enzyme-based conjugates for attaining higher
selective and sensitive detection. However, due to their instability
and tedious production, cost and attainment of these conjugates have
always been a menace. A label-free biosensor holds the solution to
this problem by offering a simple target mediated approach for cost-effective,
time-based, and facile detection. Further, for AFs detection, generally
two or more AFssimultaneously contaminate the food grain,[11] and many immunoassays are specific to detect
individualaflatoxins[14−17] and hence cannot quantify AFs together in foods. Literature review
indicated a few label-free analytical reports[18] using spectroscopic techniques for AFs detection, like Raman spectroscopy,[19] hyperspectral system,[20] and near-infrared spectroscopy, indicating good results in foods.
However, simple UV–Vis, which is a widely available instrument,
is reported less for AFs screening.Lately, there are a few
colorimetric method-based reports for quantification
of macro organic molecules like pollutants and[21] heavy n class="Chemical">metals[22,23] by colorimetric binding
with supported metal oxideNPs on clay composites. The detection involved
estimating the direct output signal proportional to the interaction
caused between the analyte and supported composite material. Among
other metal oxide nanomaterials, ZnO has several advantages due its
wide band gap (3.35 eV), low cost, high aspect ratio, and improved
optoelectronic properties. It shows unique structural properties like
it has a second coordination sphere, which entails itself in hydrogen
binding likely with ligands, water molecules, and hydrophobic cores,
for improved binding results.[24] Additionally,
it was reported that catalytic activity of these oxide materials can
be enhanced when they are linked or immobilized on a natural clay
material such as bentonite, which has a higher surface area.[25] Moreover, introducing nanoparticles with other
substrates/fillers would result in composites with novel and enhanced
properties that cannot be achieved by the individual components. Clay
minerals are excellent fillers for metal composites. Clay minerals
have been gaining attention of manufacturers and scientists throughout
the world because of their low cost, high specific surface area, chemical/mechanical
stability, them having a variety of surfaces, higher adsorption, and
structural properties.[26] Gumpu et al.[27] reported increased specific reaction and electron
transfer rate between the target analyte and metallic nanoparticle-based
clay nanocomposite on the electrode surface in aqueous solution.[23,28,29] Treatment of bentonite with ZnONPs are in accordance with the study published by Rashid et al.,[25] which reports the binding efficiency of bentonite
clay increased with ZnONPs for AFs within biological cells. It is
essentially due to Zn ions on the bentonite surface, which creates
a AFs-Zn chelation complex at the dicarbonyl functional group of AFs.[30,31]
However, ZnOBt sensitization toward visible light for detecting
AFs requires splitting of band gap into several sub-gaps and can be
performed by incorporation of fullerenes,[46] organic materials,[45] and polymers.[47−49] The Cur dye-modified ZnO-based nanocomposite studies for optical,
colorimetric, and electro-chemical sensors are not explored much.
In this work, we attempted to prepare a new Cur-functionalized ZnOBt
nanomaterials, which is termed here as Zn(Cur)OBt, and apply it for
developing a label-free visible sensing scheme for AFs as depicted
in Scheme to achieve
simple, low cost, easier, rapid, sensitive and selective results.
The curcuminoid complex is widely acknowledged for its medicinal role
in therapy and pharmacy and for major diseases.[32−34] It has very
unique photophysical and fluorescence characteristics.[35] As a fluorescent probe, it has been widely realized
to be installed in several sensing schemes[36−38] and acts as
a reducing agent with metalNPs[39] and nanorods.[40] It forms a chelating complex with different
metal ions[41−43] and zinc salt by forming a Zn-Cur complex.[44] Thus, functionalizing ZnOBt with Cur may enhance
the absorption and luminescence properties of ZnO and overall adsorption
efficiency of ZnOBt and hence can be utilized for colorimetric total
AFs detection in our colorimetric sensor studies.
Scheme 1
Schematic Representation
for Colorimetric Detection of Total AFs
by the Zn(Cur)OBt Composite at Alkaline pH (9.54)
Zn(Cur)OBt in the absence
of AFs remained red in control samples and changes to yellow color
and forms AFs- Zn(Cur)OBt, reducing alkaline pH to neutral pH in the
presence of AFs.
Schematic Representation
for Colorimetric Detection of Total AFs
by the Zn(Cur)OBt Composite at Alkaline pH (9.54)
Zn(n class="Chemical">Cur)OBt in the absence
of AFs remained red in control samples and changes to yellow color
and forms AFs- Zn(Cur)OBt, reducing alkaline pH to neutral pH in the
presence of AFs.
Results
and Discussions
Characterization of the
ZnOBt Nanocomposite
The crystallite phase, surface morphologicn class="Chemical">al,
colloidal stability,
optical properties and functional groups of ZnOBt required for AFs
colorimetric assay were characterized by XRD, SEM, UV–Vis,
and FT-IR. XRD confirmed the crystallite wurtzite phase of nanosized
ZnONPs and the hexagonal phase of bentonite in the ZnOBt nanocomposite.
The crystallite sizes of ZnONPs and ZnOBt were calculated by X-ray
beam interference using Bragg’s law or the Debye–Scherrer
equation (D = 0.9λ/β cos θ) as
20 and 24.4 nm, respectively. Figure a,b shows the XRD spectra of ZnO and the ZnOBt nanocomposite.
The maximum intensity peak (2θ) at 36.2° and 26.5°
indexed to crystalline planes at Miller indices of (101) for ZnO and
(210) for bentonite was observed in the ZnOBt nanocomposite. The values
were matched and found in accordance with the standard (JCPDS file
number 750526).[50−52] Further, XRD of ZnOBt revealed broadening of peaks
as compared with bare ZnONPs. This was observed due to potency of
ZnONPs to bridge the adjacent silicate units present in interlayers,
similar to a behavior shown by different oxides in the intermittent
layers of bentonite as conferred by Sonawane et al.[53] Additionally, in comparison with the natural clay, ZnOBt
nanoclay intercalation is more advanced in a higher 2θ region
(30–40°), showing generation of the intercalated composite.[54]
Figure 1
XRD of (a) ZnO and (b) ZnOBt. SEM images of (c, d) ZnO
NPs and
(e, f) ZnOBt. UV–Vis spectra (inset, Tauc plot) of (g) ZnO
NPs and (h) ZnOBt. FT-IR spectra of (i) ZnO NPs and ZnOBt and (j)
Cur and Zn(Cur)OBt.
XRD of (a) ZnO and (b) n class="Chemical">ZnOBt. SEM images of (c, d) ZnONPs and
(e, f) ZnOBt. UV–Vis spectra (inset, Tauc plot) of (g) ZnONPs and (h) ZnOBt. FT-IR spectra of (i) ZnONPs and ZnOBt and (j)
Cur and Zn(Cur)OBt.
SEM morphologies obtained
similar results indicative of intercn class="Chemical">alation
for bare ZnONPs on the surface and interlayers of bentonite. ZnONPs showed flower-like, spherical, hexagonal rods (Figure c,d) as shown in our previous
study,[55] while the ZnOBt nanoclay exhibited
a platelet structure of bentonite in tactoid form with uniform stacking
of flower-shaped ZnO nanostructures on the surface and interlayers
as shown in Figure e,f. Embedded ZnONPs in the interlayers of bentonite for the ZnOBt
nanocomposite also indicated a decrease in size, conferred with XRD
and surface area morphology of ZnONPs as per unit surface area of
bentonite clay mineral.[56] This was further
evidenced with UV–vis spectra, where a blue shift of 5 nm was
observed for bare ZnONPs at 373–368 nm for the ZnOBt nanocomposite.
As shown in Figure g,h, the band gap was drawn using Tauc plot and the Eg value was found to be higher for ZnOBt (3.35 eV) than
bare ZnONPs (3.05 eV). The results were indicative of a decrease
in particle size for ZnONPs supported within the clay matrix due
to electron confinement at the nanoscale, with so-called “quantum
size effect”, as compared with unsupported bare ZnONPs.[56] The discrete and uniform distribution of in
situ prepared ZnONPs, anchored on the bentonite surface, was further
confirmed by chemical and functional bonds using FT-IR analysis. It
further affirmed the improved optical property and advanced surface-active
sites of ZnOBt.
As shown in Figure i, the FT-IR spectra of ZnONPs and ZnOBt
were compared, indicating
the presence of bentonite and ZnONPs in the intercalated nanocomposite.
The composite showed the band location at around 1500–1350
cm–1 for N–H stretch of bentonite and at
around 800–400 cm–1 for ZnO stretch.[57,58] The absorption in the region around 1574 cm–1 and
band centered at 1132 cm–1 was related to the H–O–H
bending vibration of water and siloxane (−Si–O–Si−)
group stretching for bentonite.[31,51,59] The capping agent and stabilization of as-synthesized ZnONPs may
be due to the coordination of ZnONPs with C=O and −OH
groups.[49,60] Other bands in the region between 1200 and
800 cm–1 were identified as Si–O–Al,
Si–O–Si, and Al–OH–Mg[31] peaks at 921.53, 1132.66, and 1574.23 in the ZnOBt nanocomposite.
Thus, characterization revealed ZnOBt synthesized for prevented free
release of supported ZnNPs into the environment, prevented agglomeration,
and effective colorimetric AFs detection in the food matrix in this
study. Further, to functionalize ZnOBt with Cur, fingerprint vibrations
were studied for both Cur and Zn(Cur)OBt, as shown in Figure j, to support their interaction. Table shows the molecular
band of the bare material and composite used for colorimetric detection.
ZnONPs showed no functional group at around 3500 cm–1 nor at 1600 cm–1. The absence of these bands indicates
no O–H stretching vibration for the hydroxyl group and surface
H–OH group bending vibration. Thus, no adsorption took place
on the surface of bare ZnONPs of any hydroxyl group.[64] Meanwhile, the peak shift in ZnOBt and Zn(Cur)OBt from
720 and 813 cm–1 to 921 and 931 cm–1 was less dominant to indicate the altered Zn–O bond in the
presence of bentonite and Cur.[65] The n(OH)
vibration at 3595 cm–1 in Cur indicated the frequency
region of phenolic groups, shifted to a lower frequency band at 3363
cm–1 in Zn(Cur)OBt to indicate Zn(Cur)O binding.
Cur has the prominent β-diketone group in its molecular structure,
which create the metal-chelation ability of Cur.[42,66,67] Khalil et al. reported the mass spectra
of Zn-Cur showing a four-coordination complex formed at the β-di-keto
system.[67] This is due to the presence of
a keto and enol tautomeric group in Cur. Thus, it indicated the formation
of a charge transfer complex by forming a weak or strong bond with
the Zn atom at the β-diketone moiety on the surface of ZnO. Figure j indicates the Cur
spectra with no peak in the carbonyl region (1700–1650 cm–1) as reported earlier, neither in the solid nor in
liquid state. It indicated that Cur exists mainly in the enol form;
however, the peak at 1635 cm–1 for Zn(Cur)OBt was
observed, which could be due to the formation of the n(C=O)
group in Cur. Tayyari et al. stated that the broadness and intensity
of the enol peak in Cur is dependent on the strength of the intramolecular
hydrogen bond.[68] It increases with a decrease
in intensity and an increase in broadness of enol band location. Meanwhile,
in Zn(Cur)OBt, there is a shift in ν (OH stretch) to the keto
band at 3325 cm–1 and an increase in peak intensity.
It indicated the formation of a chelate complex and the formation
of Zn(Cur)OBt.
Table 1
Assignment of Important Infrared Spectral
Bands (cm–1) for ZnO NPs, ZnOBt, Cur, and Zn(Cur)OBt
in FT-IR
AFs Sensor Mechanism and
Binding Confirmation
Characterization
The as-synthesized n class="Chemical">ZnOBt nanocomposite was
further investigated for colorimetric application. It comprised functionalizing
ZnOBt with Cur to detect not just AFB1 but also total standard
AFs (AFB1, AFB2, AFG1, and AFG2 in the ratio of 1:0.1:0.3:0.03) in the food matrix. In order
to create specific electrochemical bonds with Cur, the functional
moiety of AFs is unable to cause direct discoloration of the dye due
to the absence of ligand groups like nitro, sulfhydryl, or amino,
as shown in the chemical structure of AFs in Figure d. Certain reports suggested that colorimetric
methods[69] based on discoloration of dye,
adsorbed on the ZnOBt surface, causing electrochemical binding between
the analyte (small molecule) and ZnOBt may serve as an alternative
approach.[69]
Figure 6
Job’s
plot for Zn(Cur)OBt with AFs. The concentration of
ZnOBt is kept constant for ZnOBt+AFs at 0.5 mg/mL. ΔA indicates the difference between the absorbance before
and after addition of AFs.
Daković et al.
reported reduction of n class="Chemical">AFB1 in cattlefeed, by adsorption
on copper-modified montmorillonite. This was possible due to the formation
of a complex between the metal oxide-modified clay with the dicarbonyl
group of AFB1.[70] Likewise, ZnO
ions initially adsorb rapidly to the vacant site of bentonite to give
enhanced adsorption of AFs to the clay.[70] However, chromophore-like Cur when added previously to the ZnOBt
nanocomposite forms a chelate complex, which works as a mediation
for rapid reaction with the analyte.[69] AFs
thus showed improved binding with electrochemically reduced ZnONPs
in the presence of oxidized Cur to cause a significant change in the
color of the mixture as shown in our previous study.[55] In our current investigation, we have studied that ZnONPs incorporated bentonite nanocomposite when chelated at the diketone
moiety of Cur showed improved electrostatic binding and stable color
change in the presence of total AFs. Cur forms a chelate complex with
ZnOBt mainly due to extended conjugation at the 1,3 diketone moiety
as observed by FT-IR studies with lower wavelength shift in frequency
of OH stretch for Zn(Cur)OBt in the presence of AFs. Addition of ZnOBt
to Cur improved its ability to bind unsaturated aldehyde electrophiles
of AFs. AFs in a highly alkaline medium share the electrostatic bond
at an α,β-unsaturated ketone derivative with Zn(Cur)OBt
and convert it to a highly polar medium with an improved hydrogen
bond strength. Due to which, change in color of Zn(Cur)OBt from red
(510 nm) to yellow (430 nm) in the presence of AFs was recorded by
UV–Vis. This strategy significantly enhances the selectivity
because of lesser chance of false positive results.[30,31,71]
As shown in Scheme , the addition of Cur at n class="Chemical">alkaline pH (9.54)
to ZnOBt forms a red
dispersed suspension. The enol form of Cur in non-polar and basic
medium is prone to degradation. Hence, it stabilized in the presence
of ZnOBt toward polar and neutral medium to its di-keto form. Under
high basic pH conditions, aflatoxins are known to become unstable
and sensitive; thus, addition of AFs in alkaline medium (9.54) to
Zn(Cur)OBt suspension metabolizes AFs to coumaric acid or phenolate
anions. AFscoumaric acid bind at its carbonyl group moiety to ZnO
ions in the colored complex Zn(Cur)OBt and gradually change its color
from red to reddish orange and yellow. The product formed is less
deprotonated due to rapid oxidation of Cur and reduction in the pH
from 9.54 to 7 by increasing AFs concentration from 0 to 20 ppb in
food samples as shown in Scheme . This mechanism was studied and confirmed experimentally
using UV–Vis, FT-IR, and NMR and theoretically using Job’s
plot and Benesi–Hildebrand (B-H) equations.
Colorimetric
Binding by UV–Vis
The colorimetric binding of Zn(n class="Chemical">Cur)OBt
with increased AFs was studied
by UV–Vis in the range of 200–800 nm. Initially, the
Cur dye showed maximum absorption (λmax) in alkaline
medium (pH 9.54) at 479 nm as shown in Figure a. Further, with addition of pure ZnONPs
and nanocomposite ZnOBt, Cur showed enhanced blue shift by 14 and
29 nm for Zn(Cur)O and Zn(Cur)OBt at λmax 465 and
450 nm, respectively. This shift in absorption spectra could be due
to oxidation of Cur with the ZnOBt nanocomposite and increased band
gap between π–π∗ electronic transition from
bonding to antibonding orbitals in Cur.[72] It can be asserted that the formation of a mononuclear Zn(Cur)OBt
complex occurred at the diketone moiety of Cur, which has improved
optical and chemical stability with time as compared with complex
Zn(Cur)O.[73] Hence, suitably with addition
of AFs to Zn(Cur)OBt causing a high energy difference, advance oxidation
of dye Cur and improved electron transition between bonding and antibonding
orbitals of Cur to cause a rapid color change from red to yellow.
This is due to binding of AFscoumaric acid, which caused a decrease
in pH of the composite and improved binding with Zn(Cur)OBt. The effect
of solvent polarity in the absorption spectra of Zn(Cur)OBt was clearly
visible upon UV irradiation as a negative solvatochromic effect. It
can be seen from Figure a–c that there was no remarkable hypsochromic shift observed
with only Cur and ZnONPs in the presence of AFs in the solvent and
in the control samples of both Zn(Cur)O and Zn(Cur)OBt complex at
λmax 503 nm. Meanwhile, with the addition of AFs,
a remarkable blue shift of 39 and 73 nm was observed for AFs-Zn(Cur)O
and AFs-Zn(Cur)OBt at λmax 464 and 430 nm, respectively.
Remarkably, ZnOBt showed improved binding for AFs in the complex than
with bare ZnONPs and can be used as a suitable substrate for total
AFs binding in methanol with the food matrix.
Figure 2
UV–Vis colorimetric
binding of standard 5 ppm AFs (1 AFB1:0.1 AFB2:0.3 AFG1:0.03 AFG2) (I); (a) Cur (II), Cur+AFs
(III), Zn(Cur)O (IV), Zn(Cur)OBt (V);
(b) ZnO+AFs (II), Zn(Cur)O+control (III), Zn(Cur)O+AFs (IV); (c) UV–Vis
spectra of ZnOBt+AFs (II), Zn(Cur)OBt+control (III), Zn(Cur)OBt+AFs
(IV). Inset photographic images are the corresponding colorimetric
response.
UV–Vis colorimetric
binding of standard 5 ppm AFs (1 n class="Chemical">AFB1:0.1 AFB2:0.3 AFG1:0.03 AFG2) (I); (a) Cur (II), Cur+AFs
(III), Zn(Cur)O (IV), Zn(Cur)OBt (V);
(b) ZnO+AFs (II), Zn(Cur)O+control (III), Zn(Cur)O+AFs (IV); (c) UV–Vis
spectra of ZnOBt+AFs (II), Zn(Cur)OBt+control (III), Zn(Cur)OBt+AFs
(IV). Inset photographic images are the corresponding colorimetric
response.
Functional
and Molecular Binding by FT-IR
The molecular and functional
interaction of n class="Chemical">Zn(Cur)OBt in the presence
of AFs was studied by FT-IR. Figure shows AFs molecular sites that bind the Zn(Cur)OBt
composite possibly at 3256.974, 1966.615, and 1647.362 cm–1, indicating O–H stretching for carboxylic acid, C–H
bending for alkane, and C=O stretching for conjugated ketone,
respectively. Additionally, the fingerprint of two carbonyl oxygen
atoms in AFs showed increased peak intensity in the test samples at
1647.362 cm–1 as studied by a previous report.[74]Figure indicates the molecular site for standard pure AFs at nearby
3035–2821, 1770–1721, and 1570–1481 cm–1 spectral regions;[75] for solvent methanol,
at 3367.42 and 1934.85 cm–1;[76] and for Zn(Cur)OBt-methanol (control), at around 1654 cm–1 corresponding to stretching vibrations of ν(C=C)
and ν(C=O) in the Cur–Zn(II) interaction complex,
respectively;[77] ν(=C) and
ν(C=O) were red shifted to 1647.36 cm–1 due to Zn(Cur)OBt-AFs interaction. Additionally, a blue shift in
OH stretching and red shift in C–H bending are seen for Zn(Cur)OBt-AFs
complex at 3256 and 1966 cm–1, respectively, indicating
the presence of AFs in the composite. The π systems like phenyl
groups in Zn(Cur)Bt in the presence of AFs showed an increase in hydrogen
bond strength by conjugation with the enol group. The phenolic group
n(OH) vibrations showed the frequency region in FT-IR at 3367 cm–1 in methanol, but in the presence of AFs, it is shifted
to lower frequencies at 3256 cm–1. This could be
due to the formation of intermolecular and intramolecular hydrogen
bonding in the Cur molecule in the composite.
Figure 3
IR spectra of (a) standard
AFs, (b) methanol, (c) Zn(Cur)OBt+methanol,
and (d) Zn(Cur)OBt+standard AFs.
IR spectra of (a) standard
AFs, (b) n class="Chemical">methanol, (c) Zn(Cur)OBt+methanol,
and (d) Zn(Cur)OBt+standard AFs.
Nuclear Magnetic Resonance (NMR)
Proton
nuclear magnetic resonance (NMR) spectroscopy is a powerful
tool for chemicn class="Chemical">al profiling, also known as spectral fingerprinting,
for its inherent reproducibility. In this study, we analyzed the binding
mode of Zn(Cur)OBt with coumaric acid of AFs by 1HNMR.
As shown in Figure , in the absence of AFs, the Zn(Cur)OBt+Control displayed the chemical
shift (δ) region between 4.4 and 6.0 ppm to represent aromatic
ether protons, which are not found in the presence of AFs at 20 and
200 ppb due to stable polyphenolAFs-Zn(Cur)OBt formation. The number
of protons at the aliphatic region[79] between
0 and 4.4 increases as AFs concentration increased with Zn(Cur)OBt
due to gain of proton from the AFscoumaric acid group. Table shows the 1H chemical
shift alignment and % distribution in standard AFs, control, and test
samples for Zn(Cur)OBt at a AFs concentration of 20 and 200 ppb, respectively.
The results are in accordance with UV–vis spectroscopy as the
absorption maximum of fully deprotonated (red in color) Zn(Cur)OBt
in alkaline pH (pH 9.54) is at 450 nm. The pKa in the pH range of 9.54–7.5 changes Cur in the Zn(Cur)OBt
complex with an increase in AFs concentration from red to yellow.
The chemical reactivity and solubility of the anionic Cur, i.e., in
the neutral pH range, decrease, and this form of Cur is less water
soluble than the basic form.[78] Thus, an
increase in the number of protons observed at the aliphatic region
with increased AFs was indicative of AFs proton addition to Zn(Cur)OBt.
The cross-peaks indicated that Zn(Cur)OBt interacts with the carbonyl
group of AFscoumaric acid.[77] Interestingly,
aromatic ether protons of Cur showed clear cross-peaks in the mononuclear
Zn(Cur)OBt complex in the control sample but are not found in Zn(Cur)OBt-AFs
at 50 and 200 ppb. Thus, it indicated that the total number of protons
increased with increased AFs.
Figure 4
1H NMR chemical shift (δ) in
ppm for (a) standard
AFs (AFB1, AFB2, AFG1, and AFG2), (b) Zn(Cur)OBt+Control, and (c)
Zn(Cur)OBt-AFs at 20 ppb and (d) 200 ppb.
Table 2
% Distribution of 1H Based
on 1H NMR Analysis of Standard AFs and Zn(Cur)OBt with
Three AFs Concentration (0, 20, and 200 ppb)a
The total number of protons increased
in Zn(Cur)OBt-AFs with increased AFs.
1Hn class="Chemical">NMR chemical shift (δ) in
ppm for (a) standard
AFs (AFB1, AFB2, AFG1, and AFG2), (b) Zn(Cur)OBt+Control, and (c)
Zn(Cur)OBt-AFs at 20 ppb and (d) 200 ppb.
The total number of protons increased
inn class="Chemical">Zn(Cur)OBt-AFs with increased AFs.
Benesi–Hildebrand
(B-H) Plot
The Benesi–Hildebrand method is a statisticn class="Chemical">al
method in physical
chemistry used to define the equilibrium constant Ka as well as the stoichiometry of non-bonding molecular
interactions. It is used for defining a one-on-one charge-transfer
complex or host–guest complex interaction. Theoretically, it
is explained as, with the assumption that one of the reactants is
present in excess of the other, thus the absorption spectra of the
characteristic reactant are transparent for collective absorption
of the reaction system. Hence, by computing the absorption before
and after the formation of the product at its equilibrium, the association
constant value is determined. In Figure , the one-on-one interaction between the
substrate Zn(Cur)O and Zn(Cur)OBt with the analyte (AFs) by simple
UV–Vis is described. The core of this plot includes computing
the acquired absorbance of dispersed ZnO and ZnOBt with AFs wherein
concentration units play a critical role for the characteristic complex
formed using B-H. Thus, the entire B-H plot is used to compute the
binding constant Ka value to determine
the concentration scale, which binds correctly at simple equilibrium.
By plotting the ratio of the absorbance intensity with respect to
reciprocal concentration of AFs, the Benesi–Hildebrand association
constant for the complex formation (Ka) was calculated from the ratio of the slope to the intercept. The Ka value of Cur with AFs in the presence of ZnOBt
and ZnO was found to be 3.77 × 106 and 0.644 ×
106 mol–1 L as shown in Figure a,b. The higher value of the
binding constant indicates the strong interaction between ZnOBt and
AFs. Thus, in the presence of AFs, rapid color change and oxidation
of dye Cur are observed more with ZnOBt than with bare ZnONPs.
Figure 5
Benesi–Hildebrand
equation plot from the absorption titration
values at 367 nm for AFs in the presence of (a) Zn(Cur)O and (b) Zn(Cur)OBt.
Benesi–Hildebrand
equation plot from the absorption titration
vn class="Chemical">alues at 367 nm for AFs in the presence of (a) Zn(Cur)O and (b) Zn(Cur)OBt.
Binding Ratio by the
Job Plot Method
A Job plot is known as continuous variation
method used to define
the stoichiometric ratio of a binding event. The maximum and minimum
points in a Job plot correspond to the stoichiometric ratio of the
binding reactants. It provide an inn class="Chemical">sight into the equilibrium constant
(Keq) of the product formation. More curvature
in a Job plot represents the even distribution of equilibrium, while
a triangular plot indicates a large value of Keq. To determine Keq, the ratio
of analytes is established in a solution. In Figure , the binding stoichiometry ratio of Cur and AFs in the presence
of ZnOBt was plotted as the difference (ΔA)
between the absorbance at 367 nm before and after addition of AFs
versus function of the mole fraction of Zn(Cur)OBt under a constant
total concentration. The peak of the Job’s plot obtained correspond
to the mole fraction of Zn(Cur)OBt bound to AFs. The ΔA value reached a maximum when the mole fraction was 0.5,
indicating that the complex of Zn(Cur)OBt and AFs formed a 1:1 stoichiometric
ratio. Thus, analysis of absorbance data in terms of Job’s
plots and the Benesi–Hildebrand equation is indicative for
the efficient formation of a stable 1:1 complex due to the favorable
electrostatic bond interaction between the carbonyl group of AFs and
Zn ions bound with the Zn(Cur)OBt complex. Thus, Zn(Cur)OBt binds
efficiently with AFs established by Job’s plot method.
Job’s
plot for Zn(n class="Chemical">Cur)OBt with AFs. The concentration of
ZnOBt is kept constant for ZnOBt+AFs at 0.5 mg/mL. ΔA indicates the difference between the absorbance before
and after addition of AFs.
Optimization of Sensor Studies
To
optimize the colorimetric sensor, working conditions were investigated
with the following factors: concentrations of (a) ZnOBt,(b) n class="Chemical">NaOH,
and (c) curcumin and (d) incubation time and pH stability. Corresponding
figures (Figures S1–S4) and data
are shown in the Supporting Information. The test results indicated the best possible values at (a) 0.25
mL (of 0.5 mg ZnOBt/mL dispersion in DW); (b) 0.1 M NaOH; (c) 0.166
mL (of 1 mg curcumin/mL solution in ethanol); and (d) 2 min as total
incubation time and pH 9.54 for higher accuracy and stability of results.
Food samples were collected from local/commercial markets for comparative
analysis of the Zn(Cur)OBt sensor with the standard LC/MS-MS technique
to calculate the accuracy. Alike values were known between the two
sensing modes as shown in Figure S5a. The
biosensor showed optimal reproducible signals with related standard
deviation (RSD) achieved between 5.6% and 6.9% for three repetitive
measurements of AFs concentrations. The reproducibility was thus confirmed
at all stages of the reaction. The stability of the experiments was
checked at room temperature (RT, 25 °C) and investigated for
its function with respective 9 weeks at different time intervals.
The measurement obtained a consistent signal with time (Figure S5b), with minimal variation for 9 weeks
obtained to be 6%. This showed the stability of the Zn(Cur)OBt reactions
platform as 94%, which is optimal for food sample analysis. Adding
to it, the relative deviation of Zn(Cur)OBt with the standard LC/MS-MS
method was limited maximally to 14% over various samples to acquire
a minimum accuracy of 86% as shown in Table S1.
Interference Study of the Sensor with Mycotoxins
The selectivity of analyticn class="Chemical">al reports submitted previously for
AFs reported usual testing of the method with other mycotoxins species.
In our test, we have chosen three kinds of mycotoxins (OTA, ZEN, and
DON), mostly affecting corn and almond crops.[80,81] Further, we studied their colorimetric behavior to entail the selectivity
of the current method. For improved inter-assay and intra-assay comparison,
mycotoxins (10 ppm each) and total AFs (5 ppm) were tested for standard
pure solution and mixed mycotoxins, respectively. Figure a highlights that various other
mycotoxins recorded similar responses as the blank sample, showing
no interference with total AFs in inter- and intra-assay selectivity.
The results showed that the OTA, ZEN, and DON standard solutions showed
a red color with no observed peak at 430 nm, implying that they do
not bind with ZnOBt. Further, OTA, ZEN, and DON in the presence of
total AFs showed an orange color at the absorption peak of 430 nm,
respectively. It indicates that only AFs can bind selectively to ZnOBt
in the reaction composite, irrespective of any interference caused
by other mycotoxins or the blank sample. This was evident because
OTA, ZEN, and DON in their chemical structures contained no adjacent
carbonyl group or lactone moiety as apparently seen in the structure
of all primary AFs (Figure d). A similar pattern of color change with Zn(Cur)OBt for
AFs was found in test and control samples of corn and almond food
samples, as noticed by the L*a*b* value of a hand colorimeter as shown in Table S2, Supporting Information. Thus, Zn(Cur)OBt as a core
sensing material demonstrated an excellent selectivity for AFs detection.
Figure 7
Selectivity
of Zn(Cur)OBt-based colorimetric detection assay. (a,
b) Absorption spectra of Zn(Cur)OBt mixed solutions in the presence
of other related toxins; inset shows the corresponding visual observation
of Zn(Cur)OBt mixed solutions in the presence of other related toxins.
(c) Molecular structure of standard toxins.
Selectivity
of Zn(n class="Chemical">Cur)OBt-based colorimetric detection assay. (a,
b) Absorption spectra of Zn(Cur)OBt mixed solutions in the presence
of other related toxins; inset shows the corresponding visual observation
of Zn(Cur)OBt mixed solutions in the presence of other related toxins.
(c) Molecular structure of standard toxins.
Sensitivity of the Sensor
To analyze
the sensitivity of the sensor and compare ZnO with ZnOBt, a series
of different AFs concentration in the proportions of 1.0:0.1:0.3:0.03[80] were studied for the linear range from 0.25
to 5 μg/g. The increased AFs value caused a systematic increase
in absorbance value and color change at the characteristic peak for
standard AFs (367 nm) in ZnOBt (R2 = 0.99)
than bare ZnONPs (R2 = 0.95) as shown
in Figure a,b. Further,
ZnOBt are studied for spectroscopic analysis to detect total AFs in
almond kernel ground powder and corn flour as shown in Figure c,d. The linear correlation
existed for increased AFs in the linear range of 0.5–10 ppb
in corn with R2 = 0.9739 (Figure e,f) and 0.5–20 ppb
in almond with R2 = 0.9649 (Figure g,h). The AFs detection limit
(3σ) for respective food categories was calculated as 2.74 ppb
for corn and 4.37 ppb for almond, which is found to be lesser than
the maximum residual level (MRL) defined by India (30 ppb), China
(5 to 20 ppb), U.S. (20 ppb), and EFSA (8 or 10 ppb).[5−8] Essentially, the method can quantify total AFs without prior use
of an antibody, aptamer, enzyme, or any other expensive screening
techniques. Table shows a comparative view of our sensor studied in corn and almond
with respect to conventional and rapid biosensors. It indicated that
the current study has the potential to sensitively and selectively
detect total AFs together in corn and almond at LOD values complying
with the regulatory standards. Hence, it can be an interesting option
to replace traditional complicated, time-consuming, tedious, and expensive
techniques at the small scale for pre-processing, post-harvest processing,
and storage at the industrial scale for corn and almond, respectively.
Figure 8
(a, c)
UV–Vis spectra of ZnO NPs and ZnOBt containing 1
mg/mL Cur in the presence of AFs with different concentrations. The
inset portion shows the corresponding images of reaction. (b, d) Absorption
at 367 nm of ZnO NPs and ZnOBt versus the concentrations of AFs (error
bars represent the standard deviation of three data values). (e, g)
UV–Vis spectra of Zn(Cur)OBt in the presence of AFs spiked
corn and almond. (f, h) Absorption at 413 nm of Zn(Cur)OBt versus
the concentrations of AFs spiked corn and almond.
Table 3
Comparative List of Selective Biosensor
with Current AFs Method in Foods
methods
food matrix
linear
range (ng/mL)
detection limit (ng/mL)
selectivity
the use of antibody
reference
enzyme-linked immunosorbent assay
peanut
0.12–103
0.05
AFB1 and G1
yes
(11)
chemiluminescence-based
immunoassay
rice, mung beans
0.003–0.03
0.0015
AFB1
yes
(14)
lateral flow immunoassay
pig feed
5
AFB1
yes
(13)
fluorescence immunoassays
peanut
0.01–5
0.008
AFB1
yes
(16)
immunochip
drinking water
0.04–1.69
0.01
AFB1 and M1
yes
(15)
membrane-based assays
cereal sample
20
AFB1
yes
(12)
immunosensor
(Cur-ZnOBt)
corn
0.05–200
0.02
AFB1
yes
(17)
corn
1–10
2.74
AFs
no
this study
almond
1–20
4.37
AFs
no
this study
(a, c)
UV–Vis spectra of ZnONPs and ZnOBt containing 1
mg/mL Cur in the presence of AFs with different concentrations. The
inset portion shows the corresponding images of reaction. (b, d) Absorption
at 367 nm of ZnONPs and ZnOBt versus the concentrations of AFs (error
bars represent the standard deviation of three data values). (e, g)
UV–Vis spectra of Zn(Cur)OBt in the presence of AFs spiked
corn and almond. (f, h) Absorption at 413 nm of Zn(Cur)OBt versus
the concentrations of AFs spiked corn and almond.
Validation
by Standard LC/MS-MS
Cereals
and tree nuts are widely consumed and mostly contaminated with n class="Chemical">AFs.[80] To study the applicability of the colorimetric
detection in corn and almond, validation studies were performed with
the standard LC/MS-MS method for AFs addition and recovery experiments.
In our study, corn and almond were determined as AFs-free (Figure S6, Supporting Information) and were spiked
with total AFs. As described in Table , the results hold good correlation between the spiked
and recovered value in visual by the developed Zn(Cur)OBt-based colorimetric
sensor and standard LC/MS-MS method. The mean recovery calculated
as 89.4–97.7% held acceptable RSD values, less than 8.1% for
the colorimetric method.
Table 4
Recovery Validation
Studies of Total
AFs by the Developed Colorimetric Sensor and LC/MS-MS for Corn and
Almond Samples (n = 5)
developed
colorimetric nanosensor (visual method)
LC-MS/MS
food samples
spiked AFs level (μg/kg)
mean ± SD
recovery (%)
RSD (%)
mean ± SD
recovery (%)
RSD (%)
corn
sample
5
4.82 ± 0.2
96.4
4.1
4.2 ± 0.2
83.3
4.3
15
13.7 ± 1.1
91.2
8.1
12.7 ± 0.6
84.5
5
30
26.8 ± 1.8
89.4
6.6
25.1 ± 1.7
83.5
6.9
almond sample
5
4.7 ± 0.4
94.1
8.6
4.2 ± 0.2
83.3
4.3
15
13.3 ± 1.3
83.2
9.6
12.7 ± 0.6
84.5
5
30
27 ± 1.6
90.2
6
25.1 ± 1.7
83.5
6.9
Thus, we
present a simple method of n class="Chemical">AFs label-free color-based
detection by UV–Vis. It does not include any use of high-grade
AFs-selective antibody, aptamer, DNA-enzyme, and chemical dye for
colorimetric results. It showed visible detection of all aflatoxins
(B1, B2, G1, and G2) in
corn and almond food products based on the cost-effective and environmentally
friendly metal oxide nanoclay composite and organic dye curcumin.
This is the first method reported based on the zinc oxide-bentonite
clay nanocomposite for total AFs detection in corn and almond.
Conclusions
A simple rapid label-free method un class="Chemical">sing
the ZnOBt nanocomposite
is developed for total AFs detection in corn and almond. ZnOBt showed
the improved morphological surface area and optical band gap of ZnOBt
than ZnONPs. The AFs presence in the Zn(Cur)OBt complex showed improved
binding as compared with bare Zn(Cur)O, causing rapid color change
from red (503 nm) to yellow (430 nm). The AFs-Zn(Cur)OBt binding is
characterized by 1HNMR, indicating the improved alkaline
proton in the complex at the 0–4.4 region with increased AFs
concentration. UV–Vis showed AFs binding to Zn(Cur)OBt at 367
nm, and FT-IR indicated binding at 1647 cm–1 for
the carbonyl group of AFscoumaric acid. The B-H plot and Job plot
also indicated theoretically that binding of the ZnOBt nanocomposite
for AFs increased in a 1:1 stoichiometric ratio. This is the first
report for colorimetric detection of total AFs in corn and almond
food crops at a LOD value of 2.74 and 4.37 ppb, respectively. However,
for large complex food matrices, it may require a pretreatment sample
clean up technique for remediating interferences. Hence, working on
its improved sensing system for total AFs detection will be our future
endeavor with different agro-products and nanocomposites.
Experimental Section
Reagents
All chemicn class="Chemical">als
and reagents
were of analytical grade and utilized without additional purification.
Aflatoxin B1 (AFB1), aflatoxin G1 (AFG1), aflatoxin G2 (AFG2), aflatoxin
B2 (AFB2), zearalenone (ZEN), deoxynivalenol
(DON), ochratoxin A (OTA), methanol, Cur, zinc acetate dehydrate, N,N-dimethylformamide (DMF), boric acid,
and sodium hydroxide were purchased from Merck Sigma-Aldrich Pvt.
Ltd., USA. The AFs and other mycotoxins mother stocks are kept in
an amber flask in a closed and refrigerated chamber at −20
°C. Bentonite (aluminum silicate hydratemontmorillonite) was
purchased from SRL Pvt. Ltd., India. Ultrapure water (18.2 MΩ·cm)
utilized in the experiment was obtained from a Milli-Q purification
system (Millipore), and NaOH, boric acid, and ZnOBt dispersion were
made with water. The respective standard solution of mycotoxins and
individualaflatoxins (in the ratio of 1.0:0.1:0.3:0.03) were mixed
in methanol at a ratio of 50 μg mL–1. The
required working solution was prepared with a methanol–water
solvent in a ratio of 3/7 (V/V).
Instrumentation
The surface-modified
functional groups of nanocomposites and binding mechanism of AFB1 with Zn(Cur)OBt weres explained by FT-IR (Agilent Technologies
Cary 630 FT-IR) having measured at a 8 cm–1 resolution
with a 1 min collection time and 16 scans. Meanwhile, the optical
absorption spectra of nanocomposites and colorimetric analysis for
AFs were analyzed by UV spectroscopy (Shimadzu UV-2600) with a 10
mm path length fused-silica cuvette at room temperature. The crystallinity
and size distribution of the nanocomposite were determined by XRD
(Ultima IV X-ray diffractometer), and the morphology was examined
by SEM (ZEISIS-EVO 18 special edition). NMR analyses were recorded
on a Varian Unity Inova spectrometer at a resonance frequency of 399.961
MHz for 1H using a 5 mm pulsed field gradient indirect
detection probe or a 10 mm broadband probe. 1H spectra
were obtained from samples dissolved in D2O2. The solvent signals (D2O21H 4.7
ppm) were used as the internal reference. The samples were extracted
in D2O2 solvent, and the extract was investigated
for 1HNMR spectroscopy. Subsequently, the spectra were
integrated over spectral regions to quantify classes of hydrogen atoms
in the complex and characterized the chemical bond formation and semi-quantitative
estimation for different AFs concentration bound with Zn(Cur)OBt at
concentration. The total color difference and the Commission Internationale
de l’Eclairage (CIE) L*a*b* coordinate values for colorimetric analysis were studied
using a hand colorimeter (CR 400, Konica Minolta, Japan).
Synthesis of ZnOBt
Addition of ZnO
to n class="Chemical">bentonite clay was prepared by a quick and simple alkaline ion
exchange method. Bentonite was submitted to an ion-exchange process
mainly by direct intercalation of ZnONPs to in situ clay interlayers.
To prepare the hybrid material, 10 g of purified sodium bentonite
was suspended with 2 g of zinc acetate dehydrate in 250 mL of DMF
and was further sonicated for 3 h to get a homogeneous dispersion.
To this mixture, 100 mL of NaOH/H2O (0.1 M solution) was
stirred constantly for 1 h. After centrifugation, the nanocomposite
obtained was dispersed in alcohol and dried at 75 °C under vacuum
for 4 h followed by calcination at 200 °C for 2–3 h.[31] The obtained dried ZnOBt was dispersed and found
stable in Milli-Q water (0.5 mg/mL). Cur-functionalized ZnOBt was
prepared by adding 0.25 mL of ZnOBt dispersed solution to 0.5 mL of
curcumin. Zn(cur)OBt was found to be stable in methanol at pH 9.54
for AFs colorimetric reaction.
Colorimetric
Detection of AFs
In
a typical experiment, 3 mL of n class="Chemical">NaOH (0.1 M), 1 mL of boric acid (0.1
M), and 2 mL of Cur (1:1 mg/mL in ethanol) were added to a cleaned,
dried test tube and vortexed for 2 min. To 0.5 mL of the above mixture,
3 mL of methanol was added. Then, we took 0.1 mL of the mixture (for
standard reaction) and 0.5 mL of the mixture in a separate test tube
(for food sample reaction) and added 0.25 mL of ZnOBt and 0.5 mL of
AFs test sample (for both the standard and food). Further, we incubated
it at RT for 2 min and analyze it for UV–Vis, FT-IR, and NMR
colorimetric studies.
Pretreatment of Food Samples
The
sample pretreatment for AFs analysis was done as per the standard
method given by the international organizations such as FAO/WHO.[80,82,83] Concisely, to 10 g of the ground
food matrix was added 25 mL of methanol/water in a ratio of 8/2 (V/V)
and stirred for 3 min. Post-centrifugation at 600 rpm for 5 min, the
supernatant (10 mL) was partitioned in a 50 mL centrifuge tube with n-hexane (6 mL) and vortexed for a minute. After partitioning
of the phases post-centrifuge (6000 rpm, 5 min), the upper phase including n-hexane was removed and added with 10 mL of chloroform
to the solution. The obtained mixture was mixed in a vortex for a
minute and centrifuged (6000 rpm, 5 min). It is followed by removal
of the upper phase, and chloroform was evaporated with a nitrogen
blow. The residue obtained was made up to 1 mL with methanol/water
and prepared in a ratio of 3/7 (V/V) for the analysis by the developed
colorimetric setup.
Determination of the Binding
Constant (Ka) by the B-H Plot and Stoichiometry
of Metal–Ligand
Complexes by Job’s Plot Experiment
The binding constant
(Ka) was determined from the Benesi–Hildebrand
equation[84,85] as follows:where A∞ and A are the absorbances
in the presence of n class="Chemical">AFs at saturation and an intermediate concentration,
respectively, and A0 is the absorbance
of Cur-ZnOBt in the absence of AFs. Ka could be calculated from the slope of (A∞ – A0)/(A – A0) against 1/[AFs].
Meanwhile, the continuous variation method, known as the Job plot,[85] is the most commonly applied method for the
determination of stoichiometry of very stable metal–ligand
complex chemicn class="Chemical">al entities. It is assumed that the HG complex is the only one formed
and therefore the only one giving rise to ΔY, where H is the host or reaction material, G is the guest or analyte,
and ΔY is a set of Y values
obtained gives a titration curve that is a plot of Y (or ΔY = Y – Y0) versus [G]0.
Calculation of Stability, Precision, and Accuracy
To
obtain efficient results and for generation of automated data
calculation of identified studied samples, it is essential to adapt
an approach that establishes the stability, accuracy, and reproducibility
of measurements. Stability was determined as variation in a detected
signal over a period of time or storage. Figure S5b denotes the baseline value of AFs determined by an average
of detected signal each week. Further, to calculate the stability
value, the RD of the detected signals with respect to the baseline
was deduced by following eq .Precision or reproducibility
was determined un class="Chemical">sing a coefficient of variation (CV; eq ) at each stage after addition of
the reaction composite and AFs to get a consistent reaction and production
of detected signals.
Accuracy
describes the variation between biosensor-detected values
and the actual values. In tests of unknown samples, realistic values
were determined and compared by the gold standard LC/MS-MS method.
The accuracy points for AFs detection was determined by eq .
Authors: József Németh; Geonel Rodríguez-Gattorno; David Díaz; América R Vázquez-Olmos; Imre Dékány Journal: Langmuir Date: 2004-03-30 Impact factor: 3.882
Authors: Fabrizio Bernini; Elena Castellini; Maria Franca Brigatti; Beatrice Bighi; Marco Borsari; Daniele Malferrari Journal: ACS Omega Date: 2021-11-23