Basic and
Advanced Logical Concept Derived from Surface Enhanced
Infrared Spectroscopy (SEIRS) as Sensing Probe for Analysis
of Chemical Species: A Brief Review
Shubhra Sinha1, Manas Kanti Deb1*,
Indrapal Karbhal1, Suryakant Manikpuri1, Rajiv Nayan1,
Babita Markande1
1School
of Studies in Chemistry, Pt. Ravishankar Shukla University, Raipur-492010
Chhattisgarh, India
Abstract
The worldwide concern for environmental pollution,
climate change and health hazards caused by various pollutants has
significantly increased in the recent past. Various techniques have so far been
employed for sensing applications of such organic as well as inorganic
pollutants. Amongst the different techniques, surface enhanced infrared
spectroscopy (SEIRS) is a powerful tool which is utilized for label-free and
unambiguous identification of molecular species. SEIRS overcomes the limitations
of the conventional infrared spectroscopy and has emerged as a potential
technique with high surface sensitivity by enhancing the signals by many folds and
also facilitates new studies from the fundamental aspect to applied sciences. The current
review is dedicated to a comprehension of the SEIRS technique to provide a
critical overview of its application as sensing probe for analysis of chemical
species. The major features of Fourier Transform Infrared spectroscopy and
SEIRS have been critically discussed.
Keywords:
Vibrational
Spectroscopy; FTIR; SEIRS; Pollutants; Functional Group.
Introduction
Infrared
(IR) spectroscopy is an immensely important technique based on the vibrations
of constituent atoms of a molecule which involves the interaction of IR
radiation with matter. Its major concern is to measure vibrational frequencies
in any molecule and especially specific functional groups present in a
molecule. The applicability of IR spectrometry to qualitative and quantitative
determination of chemical functionality of a gamut of chemical substances,
including polymers, liquids, gases, and solids (crystalline as well as
amorphous) is its major strength [Mohamed et al., 2017]. This method is conducted with the help of IR
spectrometers which produce an IR spectrum. The IR spectrum is a visualized
plot between transmitted/absorbed frequency and the intensity of
transmission/absorption.
IR is basically a part of the electromagnetic
spectrum, ranging from 50 to 12500 cm-1. It is further divided into
three main regions namely, Near IR (14000–4,000 cm−1), Mid IR
(4000–400 cm−1), and Far IR (400–50 cm−1). As
compared to other spectroscopic techniques, IR is on the upper hand with the
facts of being almost a universal technique,
relatively fast and inexpensive, highly sensitive, easy to handle and giving
rich spectral information. But the picture has a darker side too as, only
those species are considered detectable and IR responsive whose IR photons
alter the dipole moment of the molecule [Kurrey et al., 2019a,
Rodriguez-Saona et al., 2011]. Also, it cannot detect certain compounds, mixtures and water
since IR
wavelengths correspond to only those sizes of molecular bonds which have
lighter elements.
According
to a famous saying, “Necessity is the
mother of invention,” the drawbacks of IR spectroscopy led to the urge of
using technique like Fourier Transform Infrared (FTIR) spectroscopy. FTIR spectroscopy
is a technique used to obtain an IR spectrum of absorption of a solid, liquid
or gas. An FTIR spectrometer collects high-spectral-resolution data
over a wide spectral range concurrently. The
emergence of FT instrumentation facilitated the increase of speed and accuracy
of the conventional IR technique by replacing the use of traditional prism and
grating monochromators with an interferometer. FTIR spectroscopy at present is an appealing technique
due to its remarkable characteristics such as little sample preparation,
rapid analysis, better signal-to-noise (SNR) ratio and minimized use of
hazardous solvents [Rodriguez-Saona et al., 2011]. It utilizes the
radiation’s interferometric modulation to measure multiple frequencies synchronously and produces an
interferogram which is then recalculated using complicated algorithms that
give the original spectrum. It
is a well-established technique much earlier than Raman spectroscopy and
provides a greater sensitivity and reliability compared to Surface Enhanced
Raman Spectroscopy (SERS). This technique is used for the determination of
variety of analytes in environmental and biological samples as its high sensitivity
allows to detect the analyte at very low concentration [Kurrey et al.,
2019a].
This analytical technique is commonly used
for characterization and monitoring of organic and some cases of inorganic
pollutants based on molecular structure and chemical bonding [Mohamed et al., 2017]. Pollutants are usually the
substances that are introduced into the environment that have undesired effects
on the usefulness of various resources. Organic pollutants are a class of
environmental pollutants which are basically carbon pollutants which include a
variety of chemical compounds depicting variant structures, origin, functions,
and properties and may cause long-term or short-term detriment to the
surroundings and its living beings [Mas et al., 2010]. In the last few years, the various techniques
have been developed for the analysis of organic and inorganic pollutants in
different composition and origins. Literatures report that these pollutants have
previously been detected in the environmental samples by chromatographic and
hyphenated techniques such as gas chromatography (GC), liquid
chromatography-mass spectrometry (LC-MS), gas chromatography-mass spectrometry
(GC-MS) and ion chromatography (IC) with low limits of detection (LOD) [Wille et al.,
2012; Petrovic et al., 2010; Lim et al., 2003; Santos et al., 2003; Santos
et al., 2002]. However, it is seen that such methodologies are extortionate,
tedious, time consuming and require sample pre-treatment. Other proposed
detection techniques for the afore detections are based on fluorimetry and
phosphorimetry which too have the limitations of being sensitive to presence of
even traces of heavy metals, halides, or dissolved oxygen and to slight changes
in the pH. Therefore, to overcome these cruxes, FTIR spectroscopy proves out to
be an excellent technique of detection for the same.
Furthermore,
surface enhanced infrared spectroscopy (SEIRS) is an advanced version of attenuated
total reflectance FTIR in which a nanostructured metal film is at the
prism–sample interface, providing enhancement in the detection of vibrational
modes of molecules adsorbed on the metal film via surface plasmon resonances.
It is a strictly surface sensitive technique that exploits the electromagnetic
properties of nanostructured metal films to enhance the vibrational bands of a
molecular adlayer [Haung et. al., 2023]. It is noteworthy that, the phenomenon
of SEIR absorption (SEIRA) was first reported by Hartstein and co-workers in 1980. The SEIRA spectra follow the surface selection
rule in a similar way as the reflection‐absorption spectra of thin films do on
smooth metal substrates. It is seen that when the metal nanoparticles (MNPs)
are in close contact, i.e., they begin to
exceed the percolation limit, the bands in the adsorbate spectra start to
suppose a dispersive shape [Khalkho et al., 2021].
In
this context, the present review is dedicated to a
comprehension of the SEIRS technique to provide a critical overview of its
application as sensing probe for analysis of chemical species. The major
features of FTIR and SEIRS have been critically discussed.
Assay for advanced logical concept derived
from SEIRS as sensing probe over conventional IR
SEIRA includes the equivalent advantages with that to
the conventional FTIR spectroscopy in addition to coupling with nanotechnology
and chemometric tools. Additionally, it is a non-destructive technique which
allows further experimental actions on the IR analyzed samples [Rytwo et al., 2015]. The phenomenon of SEIRA
involves the intensity enhancement of vibrational bands of adsorbates that
usually bond through carboxylic acid or thiol groups onto the thin
nanoparticulate metallic films that have been deposited on an appropriate
substrate. SEIRA spectra obey the surface selection rule similar to the
reflection‐absorption spectra of thin films on smooth metal substrates. When
the MNPs come in close contact, i.e., start to exceed the percolation limit,
the bands in the adsorbate spectra start to assume a dispersive shape. Unlike
SERS, which is usually only observed with silver, gold and, albeit less
frequently, copper, SEIRA is observed with most metals, including platinum and
even zinc [Griffiths, 2013]. Distinct from the
surface‐enhanced Raman scattering i.e. SERS, (usually
only observed with silver, gold and, though less frequently with copper), SEIRA
is observed with majority of metals, including platinum and even zinc.
In case of SERS, the Raman signal intensity of a molecule gets augmented by
many orders of magnitude when adsorbed to metallic nanostructures showing
atomic scale roughness. It is seen that SERS shows sensitivity only to
vibrational modes with changes in the polarizability of the molecules, while on
the other hand, vibrations resulting in an alteration of the dipolar moment are
reported by FTIR spectroscopy. Hence, SEIRS technique is used for the
determination of diversity of analytes in environmental as well as biological
samples, since, its ultra sensitivity allows detection of analyte at trace
concentrations [Yang et al., 2008].
IR
spectral information may be used for the identification of the presence and
amount of a particular compound in any sample mixture. IR spectroscopy is based
on vibrations of constituent atoms of a molecule which involves interaction of
IR radiation with matter. Its major concern is to measure vibrational
frequencies in any molecule and especially specific functional groups present
in a molecule. The IR region in the electromagnetic spectrum ranges from 50 to
12500 cm-1 and is further divided into three main regions, Near IR
(14000–4000 cm−1), Mid IR (4000–400 cm−1), and Far IR
(400–50 cm−1). The mid IR spectrum has following two regions,
namely, the fingerprint region
(400-1500 cm−1), which is exclusive for a molecule and the functional
group region (1500-4000 cm−1),
which is analogous for molecules having same functional groups (Figure 1).
Figure 1. Classification of IR
regions
The
molecules in the Finger print region show Stretching
and Bending modes of vibrations which
are further classified into Symmetric-Antisymmetric
stretching and In plane- Out of plane
bending (further diversified as scissoring, rocking, twisting and wagging)
correspondingly (Figure 2 and 3). Symmetric stretching occurs when the two
attached atoms move away and towards the central atom at the same time while
Antisymmetric stretching
occurs when the two attached atoms move away and towards the central atom at
different times.
Figure 2. Symmetric and antisymmetric
stretching
While in case of
Scissoring, just like the name suggests, it occurs when the two atoms move away
and towards each other. Rocking,
on the other hand refers to the motion like a pendulum on a clock going back
and forth. Here, an atom is the pendulum and there are two instead of one. Wagging can be explained by assuming a
person holding up their hand in front of them and putting their two fingers in
a "V" sign and bending wrist towards and away from them (the tips of
the fingers are the attached atoms and the wrist is the central atom).
Figure 3. In plane and out of
plane bending
Twisting can be depicted as a person
walking on a treadmill where waist of the person is the central atom and their
feet are the two attached atoms [Skoog et al., 2007]. The samples for analysis
may be of any state, liquids, solids, or gases. However, it is noteworthy that
molecules which under ordinary conditions are transparent to IR radiations are
monatomic and homonuclear molecules (like Ne, He, O2, N2,
and H2). Diverse classes of
chemical compounds contain structural units which absorb IR radiation at
essential similar frequencies and intensities within that class of compound and
these bands are known as “group frequencies”. The knowledge of these obtained group frequencies is used to
predict the structures of unknown molecules when the standard IR spectra are
not available. Sample collection and
presentation accessories are present which allow collection of spectra as
solids, liquids, vapours and in solution, at various temperatures, and also
while undergoing mechanical deformation. The experiments conducted under such conditions assist in the
determination of the structures of molecules in diverse phases as well as the
structure-property relationships of materials. It is notable that the modern
instrumentation allows collection of IR spectra of materials even trace levels.
The capability of IR spectroscopy to examine and identify materials under such
a broad diversity of conditions has made this technique the foremost position
as the “work horse” of analytical science [McKelvy
et al., 1998].
The
conventional IR spectrometers are being used for research purposes since 1940’s
[Kirk-Othmer, 2007]. However, the most remarkable development in the
field of IR spectroscopy started with the emergence of the FTIR. FTIR is an
analytical technique used to identify organic and inorganic materials which
measures the absorption of IR radiation by the sample material versus
wavelength. The IR absorption
bands help identifying molecular structures and components. Advantages
of FTIR over the conventional dispersive IR technique include low mechanical
wear on equipment as FTIR spectroscopy does not use moving grating parts; enhancing the SNR; increased incident beam
intensity going, giving a higher throughput; superior wavelength resolution and
advanced wavelength accuracy. Whether it is the analysis of biological matrices
or estimation of toxic elements in environmental and biological solid/liquid
samples, FTIR always proves out to be an outstanding tool for quantitative as
well as qualitative analysis.
The
secret behind the supremacy of FTIR as a potent quantitative tool lies in its
knack to carry multicomponent analyses. This
multiple component quantitation is based on the additive nature of the
Beer-Lambert’s law [Baravkar et al., 2011]. Fourier
transformation is a mathematical method which is capable of interconversion of
the two domains of distance and frequency. In a common FTIR spectrometer, the
radiation emerging from the IR source is allowed to pass through an
interferometer and then to the sample before reaching the detector. Figure 4
illustrates the instrumentation of FTIR spectrophotometer. The energy from the
source strikes the beamsplitter and produces two beams of almost same
intensity. One of the beams strikes the fixed mirror and returns to the
beamsplitter while the other goes to the moving mirror. The motion of this
moving mirror makes the total path length variable which is taken by the
stationary mirror beam. Some of the characteristic peaks for different functional
groups have been listed in Table 1 [Saha et al., 2022; Khan et al., 2018;
Fuente et al, 2003].
Table 1. Characteristic
IR peaks for different functional groups
S. No.
|
Functional Group Assignment
|
Characteristic peak (cm-1)
|
ALKANES
|
1.
|
C–H stretch
|
3000–2850
|
2.
|
C–H bend
|
1470-1450
|
3.
|
C–H rock
(methyl)
|
1370-1350
|
4.
|
C–H rock
(long chain)
|
725-720
|
ALKENES
|
5.
|
C=C stretch
|
1680-1640
|
6.
|
=C–H stretch
|
3100-3000
|
7.
|
=C–H bend
|
1000-650
|
ALKYNES
|
8.
|
–C≡C– stretch
|
2260-2100
|
9.
|
–C≡C–H: C–H stretch
|
3330-3270
|
10.
|
–C≡C–H: C–H bend
|
700-610
|
AROMATIC COMPOUNDS
|
11.
|
C–H stretch
|
3100-3000
|
12.
|
C–C stretch (in-ring)
|
1600-1585
|
13.
|
C–C stretch (in-ring)
|
1500-1400
|
14.
|
C–H
|
900-675
|
ALCOHOLS
|
15.
|
O–H stretch
|
3500-3200
|
16.
|
C–O stretch
|
1260-1050
|
KETONES
|
17.
|
C=O stretch (aliphatic
ketones)
|
1715
|
18.
|
α, β -unsaturated
ketones
|
1685-1666
|
ALDEHYDES
|
19.
|
H–C=O stretch
|
2830-2695
|
20.
|
C=O stretch
(aliphatic aldehydes)
|
1740-1720
|
21.
|
C=O stretch
(α, β -unsaturated aldehydes)
|
1710-1685
|
ESTERS
|
22.
|
C=O stretch (aliphatic)
|
1750-1735
|
23.
|
C=O stretch (α, β
-unsaturated)
|
1730-1715
|
24.
|
C–O stretch
|
1300-1000
|
CARBOXYLIC ACID
|
25.
|
O–H stretch
|
3300-2500
|
26.
|
C=O stretch
|
1760-1690
|
27.
|
C–O stretch
|
1320-1210
|
28.
|
O–H bend
|
1440-1395 and 950-910
|
ORGANIC NITROGEN
COMPOUNDS
|
29.
|
N–O asymmetric stretch
|
1550-1475
|
30.
|
N–O symmetric stretch
|
1360-1290
|
ORGANIC COMPOUNDS
CONTAINING HALOGENS
|
31.
|
C–H wag (-CH2X)
|
1300-1150
|
32.
|
C–X stretches (general)
|
850-515
|
33.
|
C–Cl stretch
|
850-550
|
34.
|
C–Br stretch
|
690-515
|
Figure 4. Optical system of a FTIR
spectrometer
When these
two beams convene for the second time at the beamsplitter, they recombine, and
the difference in their path lengths creates constructive as well as
destructive interference, which is called as an interferogram. The recombined beam passes through the sample
that absorbs all the wavelengths characteristic of the spectrum and then
deducts specific wavelengths from the interferogram. The detector now accounts
variation in energy-versus-time for all the wavelengths simultaneously. A laser
beam is superimposed to serve as a reference for the operation of the instrument. Upon amplification
of the signal, in which a filter priorly eradicates high frequency
contributions, the data are converted to a digital form by an
analogue-to-digital converter and is then transferred to the computer for
Fourier transformation (FT). The most widespread interferometer that is used in
FTIR spectrometry is a Michelson interferometer.
Recently, the
Miniaturized Micro Electro-Mechanical Systems (MEMS) IR gas sensors were
introduced as strong applicants for dense and low-cost solutions with a MEMS
FTIR spectrometer as the central building block. MEMS interferometer can be regarded
as a novel optical interferometer, which is based on the spatial splitting and
combining of optical beams and it uses the imaging properties of multimode
interference (MMI) waveguides. In principle, the light proliferates in air,
allowing operation over a gamut, covering both the IR as well as the visible
ranges. The overall interferometer and the beam splitter are made-up using deep
reactive ion etching technology on silicon-on-insulator wafer, which are
characterized in the visible and near-IR spectral ranges. The interferometer is
distinguished versus the wavelength and tested as a FT spectrometer, (the
spectral resolution being 2.5 nm at 635-nm wavelength). Advantages of MEMS
include low cost and compact size, improved sensitivity, shorter
response time, absence of interaction with the detected gas and ability to
detect and quantify a broad range of gases at the same time. MEMS
spectrometers can be considered as promising components in fields including
future healthcare and environmental monitoring applications, where Michelson
interferometers serve as the core optical engine. It is a noteworthy
fact that majority of the MEMS FTIR spectrometers function in the Near-IR (NIR)
with satisfactory performance taking the benefits of the high performance of
the light sources and detectors along with the lesser cost and availability of
the NIR optical fibres and lenses.
The strength of an IR signal relies on number
of factors, namely, the electromagnetic (EM) field strength, number of
molecules and corresponding absorption cross-section. It is noteworthy that
these factors are quite frequent among the optical absorption spectroscopy. In
principle, mid-IR spectroscopy is an essential, label-free, non-disturbing as
well as appropriate optical method since the signal origins
from matter-light interactions. Therefore, by
using mid-IR spectroscopy, the structural and functional changes of target
molecules during various biological events can be directly differentiated [Li
et al., 2017]. In addition to the conventional transmission FTIR (T-FTIR)
methods (eg. KBr-pellet or mull techniques) modern reflectance techniques such
as Attenuated total reflectance (ATR) and Diffuse Reflectance (DRS)/DRIFT- FTIR
are widely used presently in various scientific fields such as environmental,
agricultural, pharmaceuticals, medicine, and food studies.
Transmission spectroscopy
It
is a bygone and most commonly used method for purposes like identifying various
organic/inorganic chemicals and also for providing specific information on
molecular structure and chemical bonding. It can be applied to study of all
types of (solids, liquids or gaseous) and is therefore an influential tool for
qualitative and quantitative studies. With
numerous advantages like high spectral quality, appreciable sensitivity, and
speed, easy to handle, reduced analysis time, this non-destructive technique has
applications in various fields like remote sensing, measurement and analysis of
atmospheric spectra, analysis of solids, liquids, gases and organic/inorganic
compounds. However, it has certain limitations such as the spectral quality is
affected by the thickness of KBr pellets, air bubbles might disrupt liquid
analysis and inconsistent liquid cell may produce irreproducible spectra. Also,
water may dissolve NaCl windows and hence, an alternative water tolerant window
material such as CaF2 for specific liquid sample is required to be
used.
Attenuated total reflectance (ATR)
ATR
spectroscopy is a non-destructive, versatile sampling technique, helpful for
surface studies, films, and solutions. It employs the phenomenon of total
internal reflection (which takes place when the angle of incidence at the
interface between the sample and the crystal is greater than the critical
angle). ATR is a swift analytical tool which is on the upper hand to the
conventional IR transmission spectroscopy as it requires less sample
preparation, improves sample-to-sample reproducibility and results in better
quality data for more precise material verification and identification [Rytwo et al.,
2015].
In
case of ATR, a beam of radiation entering the zinc selenide (ZnSe) crystal
undergoes total internal reflection. It is a reflection technique which
involves internal reflection of the IR light off the back surface of an
internal reflection element with high refractive index, which is in contact
with the sample. The IR beam travelling inside
the crystal results in a standing wave of radiation which is known as
evanescent wave [Elmer, 2004] and a sample in
contact with this crystal can interact with the evanescent wave, absorb IR
radiations and get its IR spectrum detected. The sample’s absorbance attenuates
the evanescent wave which originates its name ATR. This
avails the ATR with a diversified enhancement in the sample’s response in
comparison with the other singe-reflection crystals [Rodriguez-Saona et al., 2011].
It allows measurements of samples like gels, dispersions, liquids and pastes.
Different
designs of ATR cells enable examination of both liquid as well as solid samples. Placing a flow-through ATR cell is also likely by
including an inlet and outlet source into the apparatus [Ma et. al., 2024]. This permits continuous flow of the solutions through
the cell and allows monitoring the spectral changes with time. ATR-FTIR proves
out to be a novel and straightforward technique with lower susceptibility to
over and underestimations for the investigation of reactions at drying
interfaces [Dowding
et al., 2005].
The
small depth of penetration attained through ATR implicates that it measures a
relatively thinner layer of the sample which is in contact with the surface of
an ATR element. Hence, it is not just a surface technique. The same depth of
penetration is applied to ATR imaging, in which a layer of the sample, which is
a few micrometres thick, adjacent to the surface of the ATR crystal is scrutinised
by IR light within the imaging field of
vision. In this, the rest of the
sample (numerous micrometres beyond the surface) will not be quantified and
remarkably, it will not affect the measurement of the layer being studied. This
phenomenal feature of ATR analysis allows direct measurement of the samples
without any requirement for prior cross sectioning, microtoming or polishing [Kazarian and
Chan, 2013].
Diffuse Reflectance (DRS) FTIR
spectroscopy
DRS
is simple, sensitive and speedy analytical technique used for the
characterization and quality assurance of materials on the basis of functional
group, chemical bonding and molecular structures of chemical substances. It is
a reproducible technique which requires little to no sample preparation with
easy cleanup and automation. It is a dominant computer-based
technique which runs the rapid Fourier transform algorithm and removes
limitations like CO2/H2O vapour, water-present broad
interfering absorption bands [Kurrey et al.,
2019b]. Recently, Kurrey and co-workers have quantitatively analysed metal
ions, food adulterants and ionic species using different complexing agents in
environmental, biological and food samples based on the measurement of selected
absorption peak of analytes in FTIR spectra with the help of DRS-FTIR and have
statistically validated the same for its accuracy and precision [Kurrey et al.,
2018]. Figure 5 compiles various characteristic
features, advantages, disadvantages and applications of FTIR spectroscopy.
The
measurement of powdered samples typically results in relatively long path
lengths that increase the interaction of IR light and samples. It is to be
noted that concentrated samples may have absorbance values beyond the dynamic
range of the instrument which eventually result in higher noise. Therefore, to obtain the absorbance in linear range,
the samples need pre-dilution with non-absorbing and diffusely reflecting salts
like KBr. It is a viable alternative to the traditional sampling techniques for
paint and varnish surfaces, tablets and rigid polymers [Selvasembian
et. al., 2024].
DRS
is employed in high throughput monitoring, screening and compositional analysis
of solid samples – from soils and sediments to plants and wood. However, the
technique has disadvantages like even trace amounts of impurities might disturb
the signal; highly absorbing samples often need to be mixed with IR transparent
diluters like KBr; grinding is often required to attain small particle size
(which is laborious and can affect the sample due to the heat generated or the
bonds may also be broken). These spectra are capable of exhibiting both
absorbance and reflectance features caused by the contributions from
transmission, specular and internal reflectance components and the scattering
phenomena in the collected radiation [Schmitt and Flemming, 1998].
Figure 5. Features and applications of FTIR spectroscopy.
Some analytical
aspects for separation and detection of chemical species using SEIRS method
In
case of environmental studies, SEIRS is widely used to acquire significant
compositional and structural information. FTIR spectrometers are capable for
detection of over a hundred volatile organic compounds (VOCs) which are emitted
from various industrial and biogenic sources. It
is notable that the concentration of gases in the stratosphere and troposphere
were also ascertained using FTIR spectrometers.
FTIR
along with partial least square (PLS) techniques has been used in the
concurrent on-line determination of gases in smoke from burning textiles [Bulien, 1996].
The various compounds that have been determined using the afore technology
comprise water, CO2, CO, NO, NO2, SO2, C3H4O, HCl, HCN,
HBr, and HF. Lindblom and co-workers have determined the shelf life of
nitrocellulose containing single base propellants using FTIR and PLS
calibration techniques [Lindblom et al., 1995]. A PLS method using transmission FTIR spectroscopy has
recently been developed for the analysis of aldehyde formation and anisidine
value of thermally stressed oils. A PLS method has also been developed for the
quantitative FTIR analysis of fatty acid estersin the recent years. [Haines et al.,
1997; Dubois et al., 1996].
Evaluation of polyolefin formulations using a multiple model approach and
discriminant analysis with process, chemistry, and spectroscopic information
have also been done [Van Every et al., 1996].
Sugarcane juices have been analysed by
developing principal component regression (PCR) and Principal component
analysis (PCA) [Cadet et al., 1997]. This method avails the qualitative
classification of spectra without the knowledge of their chemical composition.
The effect of PCA on mid-IR spectroscopy data has been inspected to
determine the effects of instrumental instability on results [Defernez and
Wilson, 1997]. Recently, Kurrey and co-workers have
developed a novel technique of SEIRS with silver nanoparticles (AgNPs)
assisted single drop microextraction (SDME) for the detection of total mixed
quaternary ammonium cationic surfactants (QACS) in water samples. They used SDME to separate and preconcentrate QACS from water
samples into organic solvent containing citrate-capped AgNPs through the
electrostatic and hydrophobic force of interactions and abbreviated the overall
procedure as an “AgNPs-SDME/(SEIRS)” method. In this method, AgNPs served to
augment the signal intensity of QACS through the aggregation of NPs which
resulted in the enhancement in the hot-spot density for effective absorption of
the IR radiation. For the determination of total mixed QACS in water sample.
They obtained linearity range of 1-20 μg L-1 with the limit of
detection (LOD) and limit of quantification (LOQ) as 0.03 μg L-1 and
2.0 μg L-1, respectively. [Kurrey et al., 2019a]
FTIR
spectroscopy has been employed in monitoring of gases generated during chemical
inhibition of fuel pool fires burning in the air. This technique, FTIR was
employed in the analysis of acid gases formed when Halon 1301 was used as fire
extinguishers. FTIR spectroscopy has also been exploited to study the nitric
acid ices that are formed from the vapours containing water. Also, passive FTIR
remote sensing has been utilized for the analysis of effluent clouds like
controlled gas releases chemical manufacturing facilities and power plant
emission stacks [Modiano et al., 1996].
Bacsik
and co-workers have reported that FTIR has always been a promising technique
for the non-destructive, simultaneous and real-time measurement of multiple gas
phase compounds in multifaceted mixtures like cigarette smoke [Bacsik and Mink,
2007]. In their study, Jager and co-workers have reported that FTIR
spectroscopy has the capability of measuring trace concentrations of CO2,
CH4, N2O and CO and also isotope ratios (especially that
of 13CO2) in gaseous samples [Simonescu, 2012], Ni
and Cr are omnipresent heavy metal pollutants in the aquatic environments which
bring out toxicities to aquatic organisms including microbes. FTIR spectroscopy
was used to examine the interaction of these two heavy metals on the toxicity
in Escherichia coli (E. coli).
The study revealed that binding of Ni(II) to E. coli was brawnier than that for
Cr(VI). It was observed that in the presence of Ni in E. coli, Cr showed
aggressive effects. FTIR analysis exhibited a decrease in lipid content in the
presence of Ni and not for Cr. Also, a reduction in the band area was observed
in the region of 3000–2800 cm-1 and at 1455 cm-1 (because
of a decrease in fatty acids and lipid molecules). Principle component method
from the FTIR data was used to distinguish the consequences between control and
metal toxicities in E. coli. [Gupta,
and Karthikeyan, 2016].
Kardas
and co-workers have examined and reported the alterations in cobalt-acclimated
bacteria using ATR-FTIR spectroscopy on feasible samples. They
investigated Bacillus sp. and Pseudomonas sp. isolated
from a temperate shallow lake and a finely established strain of E.
coli. This study provides updates at molecular level, supplying insight
into how dissimilar kinds of bacteria develop adaptations for survival in
aquatic environments exposed to heavy metals [Lewis and McElhaney, 2013].
Figure 6 compiles the steps involved in sample analysis
of organic and inorganic pollutants using FTIR spectroscopy.
Figure 6. Steps involved in sample
analysis of organic and inorganic pollutants using FTIR spectroscopy.
FTIR
spectroscopy has been engaged broadly for the characterization of nanodiamonds
(NDs) since last two decades. Features like ultra-sensitivity to the surface
functional groups of NDs, non-destructive nature and usually easy sample
preparation have established FTIR as a reference method for the
characterization of NDs surface chemistry. However, it is noteworthy that the
FTIR spectra of NDs can vary considerably between two studies, depending on the
type of NDs, their surface treatments and environmental conditions [Petit and Puskar,
2018].
SEIRS
is a flexible tool for the characterization of soil mineral components,
including mineral identification, structural assessment, and in situ monitoring
of the pedogenic processes (for instance, mineral formation). It harmonizes
other analytical techniques, most remarkably, X-ray diffraction (XRD) employed
in mineral identification. Specific absorption fingerprints are adequately
sensitive to differentiate among shared bond types (e.g., Si-O, Al-O) by the
local structural environment and hence facilitating soil mineral identification
and characterization [Margenot et al., 2016].
Erfan
and co-workers reported that the environmental gas sensing can be done in the
NIR but it requires comparatively very high SNR for detection of traces
concentrations of carbon dioxide (CO2) with the subsistence of the
water vapour (H2O) in the ambient air. However, the environmental
sensing in the Mid-IR (MIR) proves out to be advantageous since it shows strong
CO2 absorption and the absence (or the weakness) of the H2O
absorption as compared to the NIR. In their work, they have reported
environmental sensing of the ambient air (i.e. CO2 concentration) [Erfan et
al., 2017; Mortada
et al., 2016; Elsayed et al., 2016; Mortada et al., 2014; Al-Demerdash et
al., 2014] using the MIR MEMS FTIR spectrometer.
Studies
reveal that in the past times, reflectance FTIR spectroscopy has been employed
for the examination of the electrochemical mechanism for ethylene glycol
oxidation by polycrystalline platinum. IR spectroscopy has lately been utilized
in the study of fullerene and information related to intermolecular
interactions have also been discussed. In the past decade, the oxidation of
mesocarbon microbeads has been followed by thermogravimetric and FTIR
spectroscopic techniques. The quantitative determination of fluconazole has
also been discussed using KBr pellets of the material and the transmission FTIR
technique [McKelvy
et al., 1998].
Chen
and co-workers have characterized and investigated the adsorption mechanism of
well-structured cotton derived porous carbon (CDPC) along with the cotton
derived porous carbon oxide (CDPCO) which were fabricated via a simplistic and
economic alkaline etching method and exploited as adsorbents for waste water
cleanup. The natural cotton waste, as a carbon source, was dehydrated with
sodium hydroxide (NaOH) at low temperatures and was further etched in a thermal
treatment process at elevated temperatures. This
blended CDPCO exhibited a phenomenal adsorption performance of organic
pollutants and heavy metal ions such as methylene blue (MB), 1-naphthylamine,
Cd(II) and Co(II) in aqueous solutions. The FTIR spectra of the adsorbents
prior and subsequent to the
adsorption were attained to identify the respective adsorption mechanism. It
was reported that CDPC shows no expected adsorption peaks, signifying a pure
carbon sample. In the CDPCO spectrum, the peaks of the functional groups –OH at
3360 cm-1, C=O at 1450 cm-1 and C–O at 1067 cm-1
were obtained, which recommended the subsistence of –OH and –COOH groups. It is
seen that these oxygen functional groups on the surface of CDPCO significantly
augment its hydrophilic properties and also serve as binding sites for the
organic pollutant molecules. A shift from 1318 cm-1
to 1324 cm-1 was observed for the adsorption of MB, attributing to
the surface complexation of MB on CDPCO [Chen et al., 2015].
Moreover,
SEIRS has also been employed in the analysis of pertinent amount of
compositional and structural information concerning the environmental samples [Grube et al.,
2008]. The analysis is not only performed to establish the nature of
pollutants, but also in the determination of the bonding mechanism in case of
pollutants removal by sorption processes. The techniques like continuous air
pollutants analyzer (used for gases like SO2, NO2, O3,
NH3), on-line gas chromatography (GC) which were employed in
measurement of gas pollutants made use of simple real-time instruments to
quantify the gas pollutants. It is a notable fact that innumeral sensors are
needed to be used for the analysis of multiple gas pollutants simultaneously.
In recent decades, FTIR spectroscopy coupled with erstwhile spectroscopic
techniques like AAS (atomic absorption spectroscopy) have been exploited to
investigate the impact of industrial as well as natural activities on air
quality [Simonescu,
2012; Kumar et al., 2005; Childers et al., 2001].
FTIR
spectroscopy has broadly been utilized for the characterization and
identification of microorganisms like bacteria and yeasts, by reason of the
fact that they are hydrophilic microorganisms and thus can effortlessly be
suspended in water for sample preparation. Fischer and co-workers described the
identification of airborne fungi employing FTIR spectroscopy and reported that
the method was appropriate to reproducibly distinguish between Aspergillus and
Penicillium species [Simonescu, 2012, Duygu et
al., 2009; Fischer
et al., 2006; Essendoubi et al., 2005].
In
case of air pollution, SEIRS is productively employed for the measurement of
gas pollutants due to its advantages like real time monitoring of multiple
gases; prevention and analysis of IR spectra of sample can be done for a
prolonged time; direct detection and measurement of criteria of toxic
pollutants in ambient air and measurement of both organic as well as inorganic
compounds. In addition, it can also be utilised in the characterization and
analysis of microorganisms and monitoring of biotechnological processes. It was
reported that, FTIR is usually installed at one fixed location, but is
sometimes portable and can be operated using battery for certain short-term
surveys [Simonescu, 2012; Santos et al., 2010].
FTIR
spectroscopy has also been employed in the identification of the nature of
possible interactions between sorbent (biosorbent) and pollutants (including
heavy metals, inorganic compounds and organic compounds). Biomass FTIR spectra
before and after the biosorption were taken to determine the characteristic
functional groups involved in copper removal by fungal biomass which were
responsible for biosorption. Interpretation of IR absorption spectra can enable
[Simonescu, 2012] the determination of the bonding mechanism between copper and
biomass (fungal strain, cyanobacteria or other microorganism) [Burnett et al.,
2006; Ye et al., 2004;].
Flores-Jardines and
co-workers, in their study, have specially focussed on FTIR emission
spectroscopy, the purported “passive
technique” because there are several originally hot gaseous samples like
volcanic plumes, stack gas plumes, automobile gases or flames. They have
abridged the basic literature in the field of special environmental
applications of FTIR spectroscopy, including power plants, petrochemical and
waste disposals, natural gas plants, agricultural, and industrial sites and
also the detection of gases produced in biomass burning, in flames and in
flares. Figure 7 summarizes the wide applicability of SEIRS as a sensing probe
for various chemical species.
Figure 7. Various applications of SEIRS as
a sensing probe for chemical species.
In
order to evaluate the impact of air traffic on the upper and lower layers of
the troposphere, it is essential to discover an effectual remote-sensing method
for the measurement of the authentic gas emissions of aircraft engines at all
attitudes and at defined thrust level. Numerous scientists around the world are
investigating the eventual impact of such emissions on the Earth’s atmosphere [Dai et al., 2015; Flores-Jardineset al., 2007; Bacsik et al., 2005; Flores-Jardines et al., 2005;].
It has been reported that Fourier transform spectrometers have been employed in
a diversity of suitable techniques, ranging from high-precision measurements of
a single emission-rotation vibrational band (i.e. laser spectroscopy) to the
measurement of broadband spectra. It is
seen that FTIR emission spectroscopy (FTIRES) method appears to accomplish all
the afore-mentioned requirements by detecting the thermal radiations of the hot
(temp ~ 300–500ºC) exhaust gases yielding details about the compounds present
during the measurements [Bacsik et al., 2005].
Shrivas
and co-workers have developed a smartphone-paper based sensor impregnated with
AgNPs/CTAB for uncomplicated determination of ferric iron (Fe3+)
from water and blood plasma samples. They made use of a smartphone to record an
image of the paper substrate past the deposition of analyte followed by
quantitative determination of Fe3+. They have exploited FTIR
spectroscopy to illustrate and validate the sensing mechanism for the
determination of Fe3+ employing the smartphone coupled with
paper-based sensor. They believe that in the upcoming decades, these smartphone-paper-based
chemical sensors can prove out to be extremely useful for the determination of
iron in environmental as well as biological samples [Shrivas et al., 2020].
Khalkho
and co-workers have exploited FTIR spectroscopic the detection of vitamin B1
in food and water samples by making use of L-cysteine modified AgNPs, using
plasmonic colorimetric sensor and visual (naked eye) methods under the
optimized conditions. These methods were based on change in colour and red
shift of the Localized Surface Plasmon Resonance (LSPR) band from 390 nm to 580
nm, the reason being the interaction of vitamin B1 towards the L-cysteine
through strong electrostatic interaction disquieting the stability of AgNPs
that further directed the aggregation of particles. The size, shape, diameter
distribution and optical properties of AgNPs were also investigated by FTIR [Khalkho et al.,
2020].
Evolved
gas analysis (EGA) from thermal analyzers such as thermogravimetry (TG) or
concurrent thermal analysis (STA) which refers to simultaneous TG-DSC is well
recognized because it significantly augments the value of TG or TG-DSC results.
The coupling interface between thermal analyzers and FTIR spectrometers
frequently consists of heated adapters and a flexible, heated transfer line.
Schindler and co-workers developed a unique direct coupling of an STA
instrument and an FTIR spectrometer without a transfer line. They directly
mounted a tiny FTIR spectrometer on top of the STA furnace leading to a compact
and fully integrated STA-FTIR coupling system and concluded that the time delay
caused by the volume of the transfer line itself is slightly negligible while a
considerably better correlation between gas detection and TG results was
observed in case of certain highly condensable decomposition gases [Risoluti et al.,
2017].
In
the recent years, Jin and co-workers prepared a nitrocellulose aerogel by
sol-gel synthetic approach and supercritical carbon dioxide drying method as a
latest energetic matrix for the nano-composite energetic materials. They
derived the decomposition mechanism by making use of the TG-FTIR coupled
analysis of the condensed phase and on the basis of the experimental results
obtained [Jin et al., 2015].
Wang
and co-workers recently experimentally examined the behaviour of pollutant gas
emissions during the firing of wheat straw and coal blends by employing
thermogravimetric analysis (TGA). They
determined the emission characteristics of gas pollutants including HCl, SO2,
CO2 and NOx by exploiting coupled FTIR
measurements and concluded that HCl, SO2, CO2 and NOx emissions
were intimately related to the volatile combustion along with char reacting
stages [Wang
et al., 2011].
Textile
dyes symbolize some of the most intricate environmental pollutants because of
their diversity and complex structure. In the recent years, plasma oxidation
methods have evolved as practicable techniques for effective decay of these
pollutants. Tichonovas and
co-workers have examined the degradation of a gamut (in total 13) of industrial
textile dyes in a pilot dielectric barrier discharge (DBD) semi-continuously
operated plasma reactor. They generated plasma in a quartz tube with central
liquid-filled electrode engrossed in wastewater while ambient air was employed
as a feeding gas for the reactor. They used the production of ozone (gas and
liquid phase) as a basis for the evaluation of performance of the reactor and
exploited FTIR analysis and toxicity tests to determine the kinetics and
by-products of the oxidation process [Tichonovas et al., 2013].
Recently, Cincinelli and
co-workers have surveyed and investigated for the first time, the
occurrence and extent of microplastic (MPs) contamination in sub surface waters which
is gathered near-shore and off-shore the coastal area of the Ross Sea
(Antarctica). Furthermore, they proposed a non-invasive method employing FTIR
2D Imaging, using an FPA detector for the analysis of the MPs, consisting in
filtration after water sampling and also the analysis of the dried filter. They
confirmed the presence of variant types of MPs using FTIR spectroscopy, with
principal profusion of polyethylene and polypropylene. The
study also evidenced the potential environmental impact occurring from
scientific activities which include marine activities for scientific purposes
and from the sewage treatment plant
[Cincinelli et al., 2017].
In
the recent years, thermogravimetric simultaneous analyzer coupled with a FTIR
measurements have been employed in the investigation of the kinetic thermal
behaviour and gaseous pollutant emissions of co-combustion between paper sludge
and oil-palm solid wastes with a complete range of amalgamation ratio. Lin and
co-workers reported that the co-combustion paper sludge along with oil-palm
solid wastes produced noteworthy alterations in the thermal behaviours. They
observed and suggested that the blending of paper sludge with oil-palm solid
wastes enhanced the comprehensive combustion performance. Moreover, the
analysis of the emission profiles of gaseous pollutants further exposed that
the co-combustion paper sludge and oil-palm solid wastes cause a reduction in
gaseous emissions (SO2, NO and CO2). In addition,
co-combustion endorsed the KCl of oil-palm solid wastes to convert into HCl in
fuel gas, which otherwise, had the capability of reducing the possibility of
slagging, corrosion as well as fouling during co-combustion. They employed the
nth order reaction model by the Coats–Redfern method for the determination of
the kinetics parameters for the co-combustion of paper sludge, oil-palm solid
wastes and their individual blended fuels. The results of the analysis
illustrated that the nth order reaction model could fit the co-combustion
process thoroughly [Lin et al., 2015].
In
last few decades, microplastics (MPs) have been identified as promising marine
pollutants of momentous concern, because of their characteristics including
their persistence, toxic potential and ubiquity [Engler, 2012]. It is seen
that the bulky plastic debris crumble and become smaller and also the analysis
of MPs in a variety of environmental samples necessitate the identification of
the same from natural materials. However, the identification technique is short
of a standardized protocol. Therefore, in their recent study, Song and
co-workers employed stereomicroscope and FTIR identification methods for MPs
(<0.05) underestimated and fibre was considerably overestimated using the
stereomicroscope both in the SML as well as beach samples. By FTIR studies,
they concluded that the overall abundance was higher than by microscope in
both, the SML as well as beach samples
[Song et al., 2015].
Table 2. Comparison table for detection of various chemical
species employing SEIRS and FTIR technique
S.No
|
Species
|
Sample Type
|
Techniques
|
Remarks
|
Reference
|
1.
|
Mixed
quaternary ammonium cationic surfactants (QACS)
|
Liquid
|
SEIRS
|
Simple
and low cost for rapid monitoring of total mixed QACS from wastewater
sample
without the use of column separation and chromophoric reagents which are
required in chromatographic and spectrophotometric methods.
|
[Kurrey et al., 2019a]
|
2.
|
CO2,
CO, NO, NO2, SO2, C3H4O, HCl,
HBr, HCN, HF.
|
Gas
|
FTIR
|
Filtration
of the smoke is an unavoidable and possible source of error
|
[Bulien,
1996]
|
3.
|
Ni
and Cr toxicity in E. coli in aquatic environment.
|
Liquid
|
PCA
coupled FTIR
|
Ni(II)
to E. coli was brawnier than that for Cr(VI). It was observed that in
the presence of Ni in E. coli, Cr showed aggressive effects.
|
[Gupta,
and Karthikeyan, 2016]
|
4.
|
Nanodiamonds
(NDs)
|
Solid
|
FTIR
|
FTIR
spectra of NDs can vary considerably between two studies, depending on the
type of NDs, their surface treatments and environmental conditions.
|
[Petit and Puskar, 2018]
|
5.
|
Soil
mineral component analysis.
|
Solid
|
FTIR
harmonized with XRD
|
Specific
absorption fingerprints are adequately sensitive to differentiate among
shared bond types (e.g., Si-O, Al-O) by local structural environment and
hence facilitating soil mineral identification and characterization.
|
[Margenot et al., 2016]
|
6.
|
Adsorption
mechanism of cotton derived porous carbon (CDPC) and CDP carbon oxide (CDPCO)
|
Solid
|
FTIR
|
FTIR
spectra confirms presence of –OH and –COOH. The oxygen functional groups on
the surface of CDPCO significantly augment its hydrophilic properties and
also serve as binding sites for the organic pollutant molecules
|
[Chen et al., 2015]
|
7.
|
Air
Quality assessment for gases like SO2, NO2, O3
and NH3
|
Gas
|
FTIR
coupled with AAS
|
Excellent
technique for the investigation of impact of industrial as well as natural
activities on air quality
|
[Grube et al., 2008]
|
8.
|
Biomass
(biosorbents) and pollutants (including heavy metals, organic and inorganic
compounds)
|
Solid,
Liquid
|
FTIR
|
Interpretation
of IR absorption spectra can enable the determination of the bonding
mechanism between copper and biomass (fungal strain, cyanobacteria)
|
[Burnett et al 2006; Yee et al., 2004]
|
9.
|
Ferric
ion (Fe3+) from water and blood plasma samples
|
Liquid
|
FTIR
|
The
discoloration is attributed to the electron transfer reaction taking place on
the surface of NPs in the presence of CTAB.
|
[Shrivas et al., 2020]
|
10.
|
Vitamin
B1 in food and water samples
|
Liquid
|
FTIR
|
Change
in colour is due to interaction of vitamin B1 towards the L-cysteine through
strong electrostatic interaction disquieting the stability of AgNPs that
further directed the aggregation of particles
|
[Khalkho et al., 2020]
|
11.
|
Nano-composite
energetic materials
|
Gas
|
TG-DSC
coupled FTIR
|
Time
delay caused by the volume of the transfer line slightly negligible while a
better correlation between gas detection and TG results was observed when
certain highly condensable decomposition.
|
[Risoluti et al., 2017;
Jin et al., 2015]
|
12.
|
Emissions
during firing of wheat straw and coal blends
|
Gas
|
TG-FTIR
|
HCl,
SO2, CO2 and NOx emissions were
intimately related to the volatile combustion along with char reacting
stages.
|
[Wang et al., 2011]
|
13.
|
Industrial
textile dyes in a pilot dielectric barrier discharge (DBD) semi-continuously
operated plasma reactor
|
Liquid
|
FTIR
|
Production
of ozone (gas and liquid phase) was used as a basis for the evaluation of
performance of the reactor.
|
[Tichonovas et al., 2013]
|
14.
|
Microplastics
|
Solid
|
FTIR,
2D Imaging
|
The analysis
results indicate that 10–30% of paper sludge in the blends could be
determined as the optimum ratio range for co-combustion paper sludge and
oil-palm solid wastes.
|
[Cincinelli et al., 2017]
|
15.
|
Paper
sludge and oil-palm solid wastes
|
|
TG
simultaneous analyzer couples with FTIR
|
Coats–Redfern
method was used for determination of the kinetics parameters for the
co-combustion of paper sludge, oil-palm solid wastes and their individual
blended fuels which illustrated that the nth order reaction model could fit
the co-combustion process thoroughly.
|
[Lin et al., 2015]
|
Conclusions
and outlook
The
major strength of IR spectrometry lies in its applicability to qualitative as
well as quantitative determination of chemical functionality of a gamut of
chemical substances, including polymers, liquids, gases and solids. The most
remarkable development in the field of IR spectroscopy began with the emergence
of the FTIR, which is an analytical technique employed in the identification of organic
and inorganic materials. Furthermore, SEIRS has lately promoted the
creation of advanced alternative detection techniques and has come up as a
useful detection tool with ultra sensitivity and simpler protocols. The SEIRA spectra follow the surface selection rule in a similar way as
the reflection‐absorption spectra of thin films do on smooth metal
substrates. It is worth
mentioning that SEIRS is now emerging as a standard technique for the detection
of molecular vibrations with enhanced sensitivity. Advantages of SEIRS over the
conventional dispersive IR technique include low mechanical wear on equipment
as FTIR spectroscopy does not use moving grating parts; enhancing the SNR;
increased incident beam intensity going, giving a higher throughput; superior
wavelength resolution and advanced wavelength accuracy. Whether it be the
analysis of biological matrices or the estimation of toxic elements in
environmental and biological solid/liquid samples, SEIRS proves out to be an
exceptional tool for quantitative as well as qualitative analysis. Other features
like improvement of the sample-to-sample reproducibility; better quality data
for more precise material verification as well as identification; non-destructive
technique make it phenomenal for characterization and identification of
molecules. SEIRS is a well-established technique much earlier than Raman
spectroscopy and provides a greater sensitivity and reliability as compared to
SERS. The conventional methodologies employed in environmental analysis are
extortionate, tedious, time consuming and require sample pre-treatment and have
the limitations of being sensitive to presence of even traces of heavy metals,
halides or dissolved oxygen and also to slight changes in the pH. Hence, to
overcome these cruxes, SEIRS proves out to be an outstanding technique for
detection of the same.
Acknowledgements
The
authors are thankful to DST-PURSE Project (SR/PURSE/2022/145) for financial
assistance. One of the authors (SS) is grateful to Pt. Ravishankar Shukla
University, Raipur, India for providing research scholarship vide letter no.
557/Fin/Scholarship/2022.
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