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Nano. Chem. Res., 1(1): 127-141, Winter and Spring 2016 Review Paper
DOI: 10.7508/ncr.2016.01.014
Modification of mesoporous silica SBA-15 with different organic molecules to gain
chemical sensors: a review
N. Lashgaria
, A. Badieia,b,
* and G. Mohammadi Ziaranic
a
School of Chemistry, College of Science, University of Tehran, Tehran, Iran
b
Nanobiomedicine Center of Excellence, Nanoscience and Nanotechnology Research Center, University of Tehran, Tehran, Iran
c
Department of Chemistry, Faculty of Science, Alzahra University, Tehran, Iran
(Received 21 October 2015, Accepted 2 November 2015)
ABSTRACT: The recognition of the biologically and environmentally important ions is of great interest in the field of chemical
sensors in recent years. The fluorescent sensors as a powerful optical analytical technique for the detection of low level of various analytes
such as anions and metal cations have been progressively developed due to the simplicity, cost effective, and selectivity for monitoring
specific analytes in various systems. Organic-inorganic hybrid nanomaterials have important advantages as solid chemosensors and various
innovative hybrid materials modified by fluorescence molecules were recently prepared. On the other hand, the homogeneous porosity and
large surface area of mesoporous silica make it a promising inorganic support. SBA-15 as a two-dimensional hexagonal mesoporous silica
material with stable structure, thick walls, tunable pore size, and high specific surface area is a valuable substrate for modification with
different organic chelating groups. This review highlights the fluorescent chemosensors for ionic species based on modification of the
mesoporous silica SBA-15 with different organic molecules, which have been recently developed from our laboratory.
Keywords: SBA-15; Surface modification; Hybrid materials; Fluorescent chemosensors
INTRODUCTION
The molecular design and construction of chemosensors
to detect biologically and environmentally important ionic
species are currently of great interest [1,2]. Several
analytical techniques, such as mass spectrometry, high
performance liquid chromatography, ion sensitive
electrodes, and atomic absorption spectroscopy have been
used to monitor the concerned targets. However, their wide
utilization is largely limited due to their extremely high cost
and time consuming procedures together with the use of
sophisticated instrumentation. In this regard, the techniques
based on fluorescence sensors present a number of
appealing advantages in terms of high selectivity, high
sensitivity and instantaneous response to these species [3-5].
Very recently, covalent immobilization of organic
chelating groups onto the inorganic nanomaterial substrates
*Corresponding author. E-mail: abadiei@khayam.ut.ac.ir
has attracted extensive interest in the field of fluorescent
sensor [6]. These hybrid materials have important
advantages. First, immobilized receptors on inorganic
supports can liberate the guest molecules (metal ions or
anions) from the pollutant solution. Second, the solid
chemosensors display extremely high selectivity and
sensitivity to the fluorescence and absorption changes
compared to spherical structures because of their larger
surface areas and well-defined pores. Finally, the organic-
inorganic hybrid nanomaterials can be recycled by suitable
chemical treatment.
Among various nanomaterials, mesoporous silica
materials are promising inorganic supports due to having
many advantages such as tunable pore size, stable structure,
and high specific surface area with abundant Si-OH active
bonds on the pore walls or surface [7]. Therefore, silica
nanomaterials were the first choice for the preparation of
functionalized nanosensors [8-14].
SBA-15, a hexagonally ordered mesoporous silica, first
Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
128
prepared by Zhao et al. [15], appears to be more attractive
as the sensor scaffold. In addition to their use as
chemosensors, functionalized SBA-15 materials have been
increasingly used as catalysts [16], adsorbents [17,18] and
carrier materials in drug delivery [19-21]. Though SBA-15
itself is non-fluorescent, it is suitable as a sensor scaffold
because it can supply a high surface area covered with a
layer of hydroxyl groups that can act as binding sites for
covalent grafting of silanes on a silicon wall. Particularly,
the reason that SBA-15 can supersede other mesoporous
materials is that its ordered structure can maintain after
occlusion of guest molecules, deriving from the thicker wall
that aids to the maintenance of the structural integrity [22].
There are two main methods to modify the surface of SBA-
15: direct synthesis or post-grafting [23,24]. In this current
review, we focus on the fluorescent chemosensors for metal
ions and anions based on modification of mesoporous silica
SBA-15 with different organic molecules, which have been
recently developed from our laboratory.
MODIFICATION OF SBA-15 WITH
ORGANIC MOLECULES AND ITS ROLE
AS A CHEMOSENSOR
One of the interesting molecules for incorporation into
the channels of mesoporous silicas is 8-hydroxyquinoline
(HQ) and its derivatives due to their chelating ability
towards various metal ions and high luminescence
Fig. 1. Synthesis route of SBA-SPS-AlQ3.
Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
129
efficiency of resulting metal complexes [25-27]. In 2011,
our group presented a new method for covalently linking 8-
HQ in nanochannels of SBA-15 in two steps: attachment of
aminopropyl on SBA-15 followed by covalent linkage of 8-
HQ via stable sulfonamide bond and then aluminum
complexes of 8-HQ was covalently bonded to SBA-SPS-Q
(Fig. 1) [28]. The prepared materials were characterized by
powder X-ray diffraction (XRD), scanning electron
microscopy (SEM), transmission electron microscopy
(TEM), fourier transform infrared (FT-IR), N2
adsorption/desorption, and thermal analysis (TGA-DTA).
Figure 2 shows the low angle XRD patterns of SBA-15 and
the functionalized SBA-15 with amine and 8-HQ groups.
All samples have a single intensive reflection at 2θ angle
around 0.85◦ similar to the typical SBA-15 materials.
However, in the case of functionalized SBA-15 materials
the peak (100) intensity decreases after immobilizations due
to the difference in the scattering contrast of the pores and
the walls, and to the erratic coating of organic groups on the
nano-channels. Figure 3 illustrates the SEM and TEM
images of SBA-SPS-Q. The SEM image (Fig. 3a) shows
uniform particles about 1 µm and the same morphology was
observed for SBA-15. On the other hand, the TEM image
(Fig. 3b) reveals the parallel channels, resembling the pore
configuration of SBA-15. This indicates that the pore of
SBA-SPS-Q has not collapsed during two steps of reaction
and this is quite in agreement with the XRD results.
It was followed by the investigation of the interaction of
aluminum ion with this fluorophore material using
fluorescence spectroscopy. Figure 4 shows the
photoluminescence (PL) spectra of all samples containing
HQ. In the emission spectra of SBA-SPS-Q (Fig. 4a),
intense luminescence was remarkably observed around 477
nm, while SBA-SPS-QAl and SBA-SPS-AlQ3 exhibit a
very intense fluorescence around 505 nm in the mixed
solution (Fig. 4b and c). The observed blue shift in the
fluorescence spectra of SBA-SPS-Al(QS)3 (Fig. 4e)
indicates that emission spectra of grafted complexes on the
SBA-SPS-Q can be easily tuned through the ligand
exchange reaction. In a related study, we also reported one
pot synthesis of functionalized SBA-15 through co-
condensation of tetraethylorthosilicate with an 8-
hydroxyquinoline-5-sulfonamide-modified organosilane
precursor in the presence of P123 as structure-directing
Fig. 2. XRD patterns for (a) SBA-15, (b) SBA-Pr-NH2 and
(c) SBA-SPS-Q [28].
agent [29]. Then, aluminum quinolate complex was attached
covalently to this functionalized SBA-15 by using
coordinating ability of grafted 8-HQ. Its emission spectra
showed the characteristic fluorescence of the corresponding
AlQ3 complex in solution with a slightly blue shift in
emission maximum.
Later on, it was found that SBA-SPS-AlQx has a high
selectivity and sensitivity to detect Cr2O7
2-
ion over other
anions (Fig. 5). Therefore, this fluorescent nano-material
may be used as a chemo-sensor for determination of
dichromate anions in aqueous solutions [30]. By monitoring
the fluorescence of SBA-SPS-AlQx with Cr2O7
2-
, a linear
response is observed in the range of 0.16-2.9 µM with the
detection limit of 0.2 ng ml-1
.
In a similar study, SBA-SPS-AlQx showed a remarkable
fluorescent quenching in the presence of MnO4
-
anion over
other anions, because of the higher stability of its inorganic
complex with permanganate anion (Fig. 6) [31]. In other
Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
130
Fig. 3. SEM (a) and TEM (b) images of the SBA-SPS-Q compound [28].
Fig. 4. Emission spectra excited at 377 nm of (a) SBA-SPS-Q, (b) SBA-SPS-QAl, (c) SBA-SPS-AlQ3, (d)
AlQ3, and (e) SBA-SPS-Al(QS)3 [28].
Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
131
Fig. 5. Fluorescence response of SBA-SPS-AlQx upon addition of different anions in aqueous solution [30].
Fig. 6. Fluorescence emission spectra of SBA-SPS-AlQx in the presence of various anions [31].
Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
132
Fig. 7. Fluorescence emission spectra of SBA-SPS-Q suspended in an aqueous solution in the presence of
different metal ions [34].
Fig. 8. The overall synthesis procedure of 8-hydroxyquinoline-5-sulfonic acid functionalized ordered nanoporous
of SBA-15 (HQS-SBA-15).
Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
133
related studies, modified SBA-15 was used as a selective
sensing element in construction of a nano-composite carbon
paste electrode for measurement of permanganate [32] and
dichromate ions [33].
Studies on fluorescence properties of SBA-SPS-Q reveal
a selective interaction between SBA-SPS-Q and Lu3+
ion
(Fig. 7) [34]. The enhancement of fluorescence is attributed
to the strong covalent binding of Lu3+
ion, evident from the
large binding constant value. This chemosensor has been
applied to determine Lu3+
ion in some soil samples where
domestic devices were stored.
A novel modified SBA-15 with 8-hydroxyquinoline-5-
sulfonic acid (HQS-SBA-15) as a hybrid optical sensor was
prepared by a two-step post synthesis of SBA-15:
functionalization with 3-(iodopropyl)-trimethoxysilane
followed by the covalent attachment of 8-hydroxyquinoline-
5-sulfonic acid (Fig. 8) [35]. Based on fluorescence
investigation of HQS-SBA-15, colloidal suspensions of this
matter in water make possible detecting selectively and
sensitively two ions with opposite charges, i.e. Pb2+
and I-
ions, in the presence of interfering cations and different
interfering anions, respectively (Figs. 9 and 10). It was
verified that HQS-SBA-15 sensor functions reversibly and
is applicable in a wide range of pH values and is able to
determine the presence of the ions in real samples.
Moreover, good linearity was obtained between the
fluorescence emission of HQS-SBA-15 and [Pb2+
] and [I-
]
with detection limits of 1.7 × 10-6
and 2.1 × 10-6
for Pb2+
and I-
, respectively.
In a study toward functionalization of SBA-15 materials
with fluorene, grafting of fluorene onto the pores of SBA-
15 was performed via attachment of three different
organosilica with one, two, and three amine groups
followed by covalent linkage of fluorene (Fig. 11) [36]. The
sensing ability of aqueous suspended solution of FM-SBA-
15, FD-SBA-15 and FT-SBA-15 was studied by addition of
the cations Fe3+
, Cr3+
, Mg2+
, Co2+
, Ni2+
, Cu2+
, Hg2+
and
Zn2+
. As shown in Fig. 12, of all the cations tested, addition
of Fe3+
ion to a suspension of these materials resulted in the
largest decrease in the fluorescence intensity. A good
linearity between the fluorescence intensity of FM-SBA-15,
FD-SBA-15 and FT-SBA-15 and the concentration of Fe3+
ion was constructed, which enabled these materials as
fluorescence chemosensors for detecting the Fe3+
ion.
Fig. 9. Fluorescence spectra of the aqueous suspended HQS-SBA-15 in the presence of different metal cations [35].
Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
134
Fig. 10. Fluorescence spectra of the aqueous suspended HQS-SBA-15 in the presence of different anions [35].
Fig. 11. Preparation of the functionalized mesoporous silica FM-SBA-15, FD-SBA-15 and FT-SBA-15.
Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
135
Furthermore, the fluorescence spectrum of FM-SBA-15
in acidic media was studied (Fig. 13), and it showed one
fluorescence emission at 305 nm in maximum absorption
wavelength (260 nm) as a result of the interaction of H+
with this material [37]. It was concluded that the structural
change between FM-SBA-15 and the protonated form might
be an effective candidate for acid-dependent molecular-
sensor models for advanced application in molecular
sensors in the future.
Motivated by the good results obtained from fluorene
functionalized SBA-15, our group also tried to synthesize a
new hybrid mesoporous chemosensor by utilizing a new
derivative of fluorene i.e. bis(2-aminoethyl)-2-(9-
fluorenyl)malonamide (FLen) (Fig. 14) [38]. The sensing
ability of the obtained material was studied by addition of
the cations Fe3+
, Cr3+
, Mg2+
, Co2+
, Ni2+
, Cu2+
, Hg2+
and Zn2+
to aqueous suspended solution of SBA-F. Among all metal
ions, the sensor showed highly selective and sensitive
Fig. 12. Bar graphs of the fluorescence emission intensity for 8 different metal ions showing the metal ions
selectivity profile of FM-SBA-15, FD-SBA-15 and FT-SBA-15 for each metal ion. I0 corresponds to
emission of FM-SBA-15, FD-SBA-15 and FT-SBA-15 without metal ions [36].
Fig. 13. Fluorescence emission of FM-SBA-15 and protonation of amine group [37].
Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
136
Fig. 14. Modification of SBA-15 with the synthesized bis(2-aminoethyl)-2-(9-fluorenyl)malonamide.
Fig. 15. Bar graphs of the fluorescence emission intensity of SBA-F for Fe3+
, Cr3+
, Mg2+
, Co2+
, Ni2+
, Cu2+
, Hg2+
and
Zn2+
cations. I0 corresponds to emission of SBA-F in the absence of metal ions [38].
Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
137
Fig. 16. Schematic representation of SBA-15-HA synthesis procedure.
Fig. 17. The quenching ratio ((F0-F)/F0) of fluorescence response of SBA-15-HA aqueous dispersion in the
presence of various metal ions at pH 7.0 [39].
Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
138
recognition toward Fe3+
. When Fe3+
was added to the
solution, a significant decrease of the fluorescence intensity
was observed (Fig. 15). A good linearity between the
fluorescence intensity of SBA-F and the concentration of
Fe3+
ion was constructed with a suitable detection limit of
1.35 × 10-5
.
In a careful study, a fluorescent sensor was designed
based on the attachment of 1-amino-8-naphthol-3,6-
disulphonic acid (H-acid) to the SBA-15 mesoporous silica
surface (SBA-15-HA) in a two-step modification process
(Fig. 16) [39]. The fluorescent sensing properties of SBA-
15-HA were examined toward several metal ions including
Li+
, Na+
, K+
, Ag+
, Ca2+
, Mg2+
, Al3+
, Mn2+
, Cr3+
, Cd2+
, Zn2+
,
Pb2+
, Co2+
, Ni2+
, Cu2+
, and Hg2+
and the results showed high
selectivity for Hg2+
(Fig. 17). Computational studies were
accomplished to find a detailed electronic description for
the quenching mechanism of H-acid fluorescence by Hg2+
ion as well as studying the structure and bonding in the [H-
acid] Hg2+
complex (Fig. 18). Based on the computational
results, a logical/rational mechanism for fluorescence
Fig. 18. Frontier molecular orbitals of [H-acid]Hg2+
calculated in aqueous solution at PBE0/6-31++G ** PCM
level of theory [39].
Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
139
quenching was proposed showing that the interaction
between H-acid and Hg2+
ions alters the electronic structure
of H-acid and converts its emissive lowest-lying excited
state to a dark state which has been observed as
fluorescence quenching.
In another publication from our group, a novel organic-
inorganic hybrid optical sensor (SBA-NCO) was designed
and synthesized through immobilization of
isocyanatopropyl-triethoxysilane and 1-amino-naphthalene
on to the surface of SBA-15 by post-grafting method (Fig.
19) [40]. Fluorescence experiments demonstrated that SBA-
NCO is a highly selective optical sensor for the detection of
Fe3+
directly in water over a wide range of metal cations
including Na+
, K+
, Mg2+
, Ca2+
, Cu2+
, Zn2+
, Mn2+
, Fe2+
, Co2+
,
Fig. 19. Synthesis procedure of SBA-NCO.
Fig. 20. Fluorescence spectra of the suspended SBA-15-NCO in the presence of various cations [40].
Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016.
140
Cd2+
, Pb2+
, Ni2+
, Cd+3
, Cr+3
, Al3+
, and Hg+2
in a wide pH
values (Fig. 20). Moreover, a good linearity between
normalized fluorescence intensity and concentration of Fe3+
(r2
= 0.9529) with detection limit of 4.5 × 10-6
M was
established (Fig. 21).
CONCLUSIONS
SBA-15 with a two-dimensional hexagonal structure
which provides a high surface area, uniform open pores,
thick walls, and high hydrothermal and thermal stability is a
valuable substrate for modification with different organic
chelating groups by the grafting method. This paper
reviewed modification of SBA-15 with different organic
molecules which have been recently developed from our
laboratory to provide selective, sensitive, low cost, and
rapid response optical sensors.
ACKNOWLEDGEMENTS
The authors thank the research council of University of
Tehran for financial support.
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Modification of mesoporous silica SBA-15 with different organic molecules to gain chemical sensors: a review

  • 1. Nano. Chem. Res., 1(1): 127-141, Winter and Spring 2016 Review Paper DOI: 10.7508/ncr.2016.01.014 Modification of mesoporous silica SBA-15 with different organic molecules to gain chemical sensors: a review N. Lashgaria , A. Badieia,b, * and G. Mohammadi Ziaranic a School of Chemistry, College of Science, University of Tehran, Tehran, Iran b Nanobiomedicine Center of Excellence, Nanoscience and Nanotechnology Research Center, University of Tehran, Tehran, Iran c Department of Chemistry, Faculty of Science, Alzahra University, Tehran, Iran (Received 21 October 2015, Accepted 2 November 2015) ABSTRACT: The recognition of the biologically and environmentally important ions is of great interest in the field of chemical sensors in recent years. The fluorescent sensors as a powerful optical analytical technique for the detection of low level of various analytes such as anions and metal cations have been progressively developed due to the simplicity, cost effective, and selectivity for monitoring specific analytes in various systems. Organic-inorganic hybrid nanomaterials have important advantages as solid chemosensors and various innovative hybrid materials modified by fluorescence molecules were recently prepared. On the other hand, the homogeneous porosity and large surface area of mesoporous silica make it a promising inorganic support. SBA-15 as a two-dimensional hexagonal mesoporous silica material with stable structure, thick walls, tunable pore size, and high specific surface area is a valuable substrate for modification with different organic chelating groups. This review highlights the fluorescent chemosensors for ionic species based on modification of the mesoporous silica SBA-15 with different organic molecules, which have been recently developed from our laboratory. Keywords: SBA-15; Surface modification; Hybrid materials; Fluorescent chemosensors INTRODUCTION The molecular design and construction of chemosensors to detect biologically and environmentally important ionic species are currently of great interest [1,2]. Several analytical techniques, such as mass spectrometry, high performance liquid chromatography, ion sensitive electrodes, and atomic absorption spectroscopy have been used to monitor the concerned targets. However, their wide utilization is largely limited due to their extremely high cost and time consuming procedures together with the use of sophisticated instrumentation. In this regard, the techniques based on fluorescence sensors present a number of appealing advantages in terms of high selectivity, high sensitivity and instantaneous response to these species [3-5]. Very recently, covalent immobilization of organic chelating groups onto the inorganic nanomaterial substrates *Corresponding author. E-mail: abadiei@khayam.ut.ac.ir has attracted extensive interest in the field of fluorescent sensor [6]. These hybrid materials have important advantages. First, immobilized receptors on inorganic supports can liberate the guest molecules (metal ions or anions) from the pollutant solution. Second, the solid chemosensors display extremely high selectivity and sensitivity to the fluorescence and absorption changes compared to spherical structures because of their larger surface areas and well-defined pores. Finally, the organic- inorganic hybrid nanomaterials can be recycled by suitable chemical treatment. Among various nanomaterials, mesoporous silica materials are promising inorganic supports due to having many advantages such as tunable pore size, stable structure, and high specific surface area with abundant Si-OH active bonds on the pore walls or surface [7]. Therefore, silica nanomaterials were the first choice for the preparation of functionalized nanosensors [8-14]. SBA-15, a hexagonally ordered mesoporous silica, first
  • 2. Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 128 prepared by Zhao et al. [15], appears to be more attractive as the sensor scaffold. In addition to their use as chemosensors, functionalized SBA-15 materials have been increasingly used as catalysts [16], adsorbents [17,18] and carrier materials in drug delivery [19-21]. Though SBA-15 itself is non-fluorescent, it is suitable as a sensor scaffold because it can supply a high surface area covered with a layer of hydroxyl groups that can act as binding sites for covalent grafting of silanes on a silicon wall. Particularly, the reason that SBA-15 can supersede other mesoporous materials is that its ordered structure can maintain after occlusion of guest molecules, deriving from the thicker wall that aids to the maintenance of the structural integrity [22]. There are two main methods to modify the surface of SBA- 15: direct synthesis or post-grafting [23,24]. In this current review, we focus on the fluorescent chemosensors for metal ions and anions based on modification of mesoporous silica SBA-15 with different organic molecules, which have been recently developed from our laboratory. MODIFICATION OF SBA-15 WITH ORGANIC MOLECULES AND ITS ROLE AS A CHEMOSENSOR One of the interesting molecules for incorporation into the channels of mesoporous silicas is 8-hydroxyquinoline (HQ) and its derivatives due to their chelating ability towards various metal ions and high luminescence Fig. 1. Synthesis route of SBA-SPS-AlQ3.
  • 3. Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 129 efficiency of resulting metal complexes [25-27]. In 2011, our group presented a new method for covalently linking 8- HQ in nanochannels of SBA-15 in two steps: attachment of aminopropyl on SBA-15 followed by covalent linkage of 8- HQ via stable sulfonamide bond and then aluminum complexes of 8-HQ was covalently bonded to SBA-SPS-Q (Fig. 1) [28]. The prepared materials were characterized by powder X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), fourier transform infrared (FT-IR), N2 adsorption/desorption, and thermal analysis (TGA-DTA). Figure 2 shows the low angle XRD patterns of SBA-15 and the functionalized SBA-15 with amine and 8-HQ groups. All samples have a single intensive reflection at 2θ angle around 0.85◦ similar to the typical SBA-15 materials. However, in the case of functionalized SBA-15 materials the peak (100) intensity decreases after immobilizations due to the difference in the scattering contrast of the pores and the walls, and to the erratic coating of organic groups on the nano-channels. Figure 3 illustrates the SEM and TEM images of SBA-SPS-Q. The SEM image (Fig. 3a) shows uniform particles about 1 µm and the same morphology was observed for SBA-15. On the other hand, the TEM image (Fig. 3b) reveals the parallel channels, resembling the pore configuration of SBA-15. This indicates that the pore of SBA-SPS-Q has not collapsed during two steps of reaction and this is quite in agreement with the XRD results. It was followed by the investigation of the interaction of aluminum ion with this fluorophore material using fluorescence spectroscopy. Figure 4 shows the photoluminescence (PL) spectra of all samples containing HQ. In the emission spectra of SBA-SPS-Q (Fig. 4a), intense luminescence was remarkably observed around 477 nm, while SBA-SPS-QAl and SBA-SPS-AlQ3 exhibit a very intense fluorescence around 505 nm in the mixed solution (Fig. 4b and c). The observed blue shift in the fluorescence spectra of SBA-SPS-Al(QS)3 (Fig. 4e) indicates that emission spectra of grafted complexes on the SBA-SPS-Q can be easily tuned through the ligand exchange reaction. In a related study, we also reported one pot synthesis of functionalized SBA-15 through co- condensation of tetraethylorthosilicate with an 8- hydroxyquinoline-5-sulfonamide-modified organosilane precursor in the presence of P123 as structure-directing Fig. 2. XRD patterns for (a) SBA-15, (b) SBA-Pr-NH2 and (c) SBA-SPS-Q [28]. agent [29]. Then, aluminum quinolate complex was attached covalently to this functionalized SBA-15 by using coordinating ability of grafted 8-HQ. Its emission spectra showed the characteristic fluorescence of the corresponding AlQ3 complex in solution with a slightly blue shift in emission maximum. Later on, it was found that SBA-SPS-AlQx has a high selectivity and sensitivity to detect Cr2O7 2- ion over other anions (Fig. 5). Therefore, this fluorescent nano-material may be used as a chemo-sensor for determination of dichromate anions in aqueous solutions [30]. By monitoring the fluorescence of SBA-SPS-AlQx with Cr2O7 2- , a linear response is observed in the range of 0.16-2.9 µM with the detection limit of 0.2 ng ml-1 . In a similar study, SBA-SPS-AlQx showed a remarkable fluorescent quenching in the presence of MnO4 - anion over other anions, because of the higher stability of its inorganic complex with permanganate anion (Fig. 6) [31]. In other
  • 4. Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 130 Fig. 3. SEM (a) and TEM (b) images of the SBA-SPS-Q compound [28]. Fig. 4. Emission spectra excited at 377 nm of (a) SBA-SPS-Q, (b) SBA-SPS-QAl, (c) SBA-SPS-AlQ3, (d) AlQ3, and (e) SBA-SPS-Al(QS)3 [28].
  • 5. Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 131 Fig. 5. Fluorescence response of SBA-SPS-AlQx upon addition of different anions in aqueous solution [30]. Fig. 6. Fluorescence emission spectra of SBA-SPS-AlQx in the presence of various anions [31].
  • 6. Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 132 Fig. 7. Fluorescence emission spectra of SBA-SPS-Q suspended in an aqueous solution in the presence of different metal ions [34]. Fig. 8. The overall synthesis procedure of 8-hydroxyquinoline-5-sulfonic acid functionalized ordered nanoporous of SBA-15 (HQS-SBA-15).
  • 7. Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 133 related studies, modified SBA-15 was used as a selective sensing element in construction of a nano-composite carbon paste electrode for measurement of permanganate [32] and dichromate ions [33]. Studies on fluorescence properties of SBA-SPS-Q reveal a selective interaction between SBA-SPS-Q and Lu3+ ion (Fig. 7) [34]. The enhancement of fluorescence is attributed to the strong covalent binding of Lu3+ ion, evident from the large binding constant value. This chemosensor has been applied to determine Lu3+ ion in some soil samples where domestic devices were stored. A novel modified SBA-15 with 8-hydroxyquinoline-5- sulfonic acid (HQS-SBA-15) as a hybrid optical sensor was prepared by a two-step post synthesis of SBA-15: functionalization with 3-(iodopropyl)-trimethoxysilane followed by the covalent attachment of 8-hydroxyquinoline- 5-sulfonic acid (Fig. 8) [35]. Based on fluorescence investigation of HQS-SBA-15, colloidal suspensions of this matter in water make possible detecting selectively and sensitively two ions with opposite charges, i.e. Pb2+ and I- ions, in the presence of interfering cations and different interfering anions, respectively (Figs. 9 and 10). It was verified that HQS-SBA-15 sensor functions reversibly and is applicable in a wide range of pH values and is able to determine the presence of the ions in real samples. Moreover, good linearity was obtained between the fluorescence emission of HQS-SBA-15 and [Pb2+ ] and [I- ] with detection limits of 1.7 × 10-6 and 2.1 × 10-6 for Pb2+ and I- , respectively. In a study toward functionalization of SBA-15 materials with fluorene, grafting of fluorene onto the pores of SBA- 15 was performed via attachment of three different organosilica with one, two, and three amine groups followed by covalent linkage of fluorene (Fig. 11) [36]. The sensing ability of aqueous suspended solution of FM-SBA- 15, FD-SBA-15 and FT-SBA-15 was studied by addition of the cations Fe3+ , Cr3+ , Mg2+ , Co2+ , Ni2+ , Cu2+ , Hg2+ and Zn2+ . As shown in Fig. 12, of all the cations tested, addition of Fe3+ ion to a suspension of these materials resulted in the largest decrease in the fluorescence intensity. A good linearity between the fluorescence intensity of FM-SBA-15, FD-SBA-15 and FT-SBA-15 and the concentration of Fe3+ ion was constructed, which enabled these materials as fluorescence chemosensors for detecting the Fe3+ ion. Fig. 9. Fluorescence spectra of the aqueous suspended HQS-SBA-15 in the presence of different metal cations [35].
  • 8. Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 134 Fig. 10. Fluorescence spectra of the aqueous suspended HQS-SBA-15 in the presence of different anions [35]. Fig. 11. Preparation of the functionalized mesoporous silica FM-SBA-15, FD-SBA-15 and FT-SBA-15.
  • 9. Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 135 Furthermore, the fluorescence spectrum of FM-SBA-15 in acidic media was studied (Fig. 13), and it showed one fluorescence emission at 305 nm in maximum absorption wavelength (260 nm) as a result of the interaction of H+ with this material [37]. It was concluded that the structural change between FM-SBA-15 and the protonated form might be an effective candidate for acid-dependent molecular- sensor models for advanced application in molecular sensors in the future. Motivated by the good results obtained from fluorene functionalized SBA-15, our group also tried to synthesize a new hybrid mesoporous chemosensor by utilizing a new derivative of fluorene i.e. bis(2-aminoethyl)-2-(9- fluorenyl)malonamide (FLen) (Fig. 14) [38]. The sensing ability of the obtained material was studied by addition of the cations Fe3+ , Cr3+ , Mg2+ , Co2+ , Ni2+ , Cu2+ , Hg2+ and Zn2+ to aqueous suspended solution of SBA-F. Among all metal ions, the sensor showed highly selective and sensitive Fig. 12. Bar graphs of the fluorescence emission intensity for 8 different metal ions showing the metal ions selectivity profile of FM-SBA-15, FD-SBA-15 and FT-SBA-15 for each metal ion. I0 corresponds to emission of FM-SBA-15, FD-SBA-15 and FT-SBA-15 without metal ions [36]. Fig. 13. Fluorescence emission of FM-SBA-15 and protonation of amine group [37].
  • 10. Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 136 Fig. 14. Modification of SBA-15 with the synthesized bis(2-aminoethyl)-2-(9-fluorenyl)malonamide. Fig. 15. Bar graphs of the fluorescence emission intensity of SBA-F for Fe3+ , Cr3+ , Mg2+ , Co2+ , Ni2+ , Cu2+ , Hg2+ and Zn2+ cations. I0 corresponds to emission of SBA-F in the absence of metal ions [38].
  • 11. Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 137 Fig. 16. Schematic representation of SBA-15-HA synthesis procedure. Fig. 17. The quenching ratio ((F0-F)/F0) of fluorescence response of SBA-15-HA aqueous dispersion in the presence of various metal ions at pH 7.0 [39].
  • 12. Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 138 recognition toward Fe3+ . When Fe3+ was added to the solution, a significant decrease of the fluorescence intensity was observed (Fig. 15). A good linearity between the fluorescence intensity of SBA-F and the concentration of Fe3+ ion was constructed with a suitable detection limit of 1.35 × 10-5 . In a careful study, a fluorescent sensor was designed based on the attachment of 1-amino-8-naphthol-3,6- disulphonic acid (H-acid) to the SBA-15 mesoporous silica surface (SBA-15-HA) in a two-step modification process (Fig. 16) [39]. The fluorescent sensing properties of SBA- 15-HA were examined toward several metal ions including Li+ , Na+ , K+ , Ag+ , Ca2+ , Mg2+ , Al3+ , Mn2+ , Cr3+ , Cd2+ , Zn2+ , Pb2+ , Co2+ , Ni2+ , Cu2+ , and Hg2+ and the results showed high selectivity for Hg2+ (Fig. 17). Computational studies were accomplished to find a detailed electronic description for the quenching mechanism of H-acid fluorescence by Hg2+ ion as well as studying the structure and bonding in the [H- acid] Hg2+ complex (Fig. 18). Based on the computational results, a logical/rational mechanism for fluorescence Fig. 18. Frontier molecular orbitals of [H-acid]Hg2+ calculated in aqueous solution at PBE0/6-31++G ** PCM level of theory [39].
  • 13. Modification of Mesoporous Silica SBA-15/Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 139 quenching was proposed showing that the interaction between H-acid and Hg2+ ions alters the electronic structure of H-acid and converts its emissive lowest-lying excited state to a dark state which has been observed as fluorescence quenching. In another publication from our group, a novel organic- inorganic hybrid optical sensor (SBA-NCO) was designed and synthesized through immobilization of isocyanatopropyl-triethoxysilane and 1-amino-naphthalene on to the surface of SBA-15 by post-grafting method (Fig. 19) [40]. Fluorescence experiments demonstrated that SBA- NCO is a highly selective optical sensor for the detection of Fe3+ directly in water over a wide range of metal cations including Na+ , K+ , Mg2+ , Ca2+ , Cu2+ , Zn2+ , Mn2+ , Fe2+ , Co2+ , Fig. 19. Synthesis procedure of SBA-NCO. Fig. 20. Fluorescence spectra of the suspended SBA-15-NCO in the presence of various cations [40].
  • 14. Lashgari et al./Nano. Chem. Res., Vol. 1, No. 1, 127-141, June 2016. 140 Cd2+ , Pb2+ , Ni2+ , Cd+3 , Cr+3 , Al3+ , and Hg+2 in a wide pH values (Fig. 20). Moreover, a good linearity between normalized fluorescence intensity and concentration of Fe3+ (r2 = 0.9529) with detection limit of 4.5 × 10-6 M was established (Fig. 21). CONCLUSIONS SBA-15 with a two-dimensional hexagonal structure which provides a high surface area, uniform open pores, thick walls, and high hydrothermal and thermal stability is a valuable substrate for modification with different organic chelating groups by the grafting method. This paper reviewed modification of SBA-15 with different organic molecules which have been recently developed from our laboratory to provide selective, sensitive, low cost, and rapid response optical sensors. ACKNOWLEDGEMENTS The authors thank the research council of University of Tehran for financial support. REFERENCES [1] B. Valeur, I. Leray, Coord. Chem. Rev. 205 (2000) 3. [2] M.A. Martín, A.I. Olives, B. del Castillo, J.C. Menéndez, Curr. Pharm. Anal. 4 (2008) 106. [3] Y. Jeong, J. Yoon, Inorg. Chim. Acta 381 (2012) 2. [4] S.K. Sahoo, D. Sharma, R.K. Bera, G. Crisponi, J.F. Callan, Chem. Soc. Rev. 41 (2012) 7195. [5] H.N. Kim, W.X. Ren, J.S. Kim, J. Yoon, Chem. Soc. Rev. 41 (2012) 3210. [6] W.S. Han, H.Y. Lee, S.H. Jung, S.J. Lee, J.H. Jung, Chem. Soc. Rev. 38 (2009) 1904. [7] C.T. Kresge, M.E. Leonowicz, W.J. Roth, J.C. Vartuli, J.S. Beck, Nature 359 (1992) 710. [8] R. Métivier, I. Leray, B. Lebeau, B. Valeur, J. Mater. Chem. 15 (2005) 2965. [9] H.J. Kim, S.J. Lee, S.Y. Park, J.H. Jung, J.S. Kim, Adv. Mater. 20 (2008) 3229. [10] Z. Jiannan, X. Chuan, F. Qiang, L. Ming, W. Baojun, Fig. 21. The fluorescence response of the suspended SBA-15-NCO with different concentrations of Fe3+ . The inset is the Stern-Volmer plot [40].
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