Junfang Li1, Yanfang Xu1, Lulu Tian1, Yibo Yan1, Liyong Niu1,2, Xiaohong Li1,2, Zhijun Zhang1,2. 1. Engineering Research Center for Nanomaterials, Henan University, Kaifeng 475004, P. R. China. 2. Engineering Research Center for Nanomaterials Co. Ltd., Henan University, Jiyuan 459000, P. R. China.
Abstract
Poly(vinylpyrrolidone) (PVP) was used as both a modifier and reductant to in situ deposit silver nanoparticles (denoted Ag NPs) on the surface of silica nanospheres (nanosilica or nano-SiO2), affording Ag-decorated nanosilica (denoted SiO2@Ag). The as-obtained SiO2@Ag composite can form silver nanoparticle-decorated silica nanosphere arrays (denoted SiO2@Ag arrays) via evaporation-induced self-assembly. The as-prepared SiO2@Ag composite and SiO2@Ag array were used as the SERS substrates to measure the Raman signals of the dilute solutions of rhodamine 6G (denoted R6G), an organic dye that is a potential pollutant to the environment. The findings indicate that the as-prepared SiO2@Ag composite and SiO2@Ag array as potential SERS substrates simultaneously exhibit a high degree of metal coverage and small size of Ag NPs as well as good stability and abundant "hot spots", which contributes to their desired Raman enhancement capacities. For the detection of trace R6G, they provide a limit of detection of as low as 10-9-10-11 M as well as good reproducibility, showing promising potential for monitoring chemical and biological molecules.
Poly(vinylpyrrolidone) (PVP) was used as both a modifier and reductant to in situ deposit silver nanoparticles (denoted Ag NPs) on the surface of silica nanospheres (nanosilica or nano-SiO2), affording Ag-decorated nanosilica (denoted SiO2@Ag). The as-obtained SiO2@Ag composite can form silver nanoparticle-decorated silica nanosphere arrays (denoted SiO2@Ag arrays) via evaporation-induced self-assembly. The as-prepared SiO2@Ag composite and SiO2@Ag array were used as the SERS substrates to measure the Raman signals of the dilute solutions of rhodamine 6G (denoted R6G), an organic dye that is a potential pollutant to the environment. The findings indicate that the as-prepared SiO2@Ag composite and SiO2@Ag array as potential SERS substrates simultaneously exhibit a high degree of metal coverage and small size of Ag NPs as well as good stability and abundant "hot spots", which contributes to their desired Raman enhancement capacities. For the detection of trace R6G, they provide a limit of detection of as low as 10-9-10-11 M as well as good reproducibility, showing promising potential for monitoring chemical and biological molecules.
The
surface-enhanced Raman scattering (SERS) technique has been
applied in various fields, such as biomedicine,[1,2] chemistry,[3,4] environmental monitoring,[5,6] and food safety,[7,8] because of its high sensitivity, low detection limit, real-time
detection without time-consuming pretreatment of samples, and good
access to the information in the molecular fingerprint area.[9,10] To date, the electromagnetic mechanism (EM) and chemical mechanism
(CM) are generally recognized for SERS enhancement.[11,12] The former is connected with “hot spots” that are
dependent on the roughness of metal nanoparticles and the nanogaps
between neighboring nanoparticles, and the latter is attributed to
the charge transfer between the target molecule and the substrate
surface. Generally speaking, EM is significant for the detection of
target molecules. In other words, the SERS intensity highly relies
on the microstructure and composition of the SERS substrate on a nanometer
scale.[13,14] Therefore, it is imperative to fabricate
SERS substrates with high Raman scattering sensitivity, good reproducibility,
and low cost to obtain efficient Raman signals and achieve the widespread
application of the SERS technique.Noble metals (Au, Ag, etc.),
especially Ag nanostructures, are
ideal SERS substrates[15−17] because of their unique plasmonic properties in visible
and near-infrared spectral regions as well as low cost as compared
with Au. This could well explain why many researchers made considerable
efforts to design and fabricate a variety of Ag nanostructures such
as nanoparticles, nanorods, nanoprisms, nanoflowers, and nanowires
as the SERS substrates with sharp edges.[18−22] For example, Xu et al. prepared triangular Ag nanoplates
and obtained a detection limit of 3.125 × 10–7 M with SERS for rhodamine 6G.[20] Zhang
et al. found that Ag nanoparticles and nanowires can facilitate SERS
in the presence of rhodamine B since they can expose more active crystal
faces.[23] The noble metal SERS-active substrates,
especially their nanoparticles in a colloid solution, have the advantages
of easy preparation and tunable optical properties. However, it still
remains a challenge to get rid of the aggregation of nanoparticles
during random growth.[24,25] Such aggregation of metallic
nanoparticles is often inevitable, and the “hot spots”
generated by the aggregates often exhibit poor substrate reproducibility
and stability. To solve this problem, some researchers incorporate
Ag nanoparticles into or onto various stable matrices to form composites.[26−30] This strategy with stable matrices as carriers has two advantages.
On the one hand, stable matrices can increase the reaction sites of
metal nuclei to prevent randomized aggregation. On the other hand,
the stable matrices can create more “hot spots”, including
not only metal nanoparticles but also the nanogaps between neighboring
metal nanoparticles. With this strategy, it could be feasible to generate
abundant “hot spots” and increase the density of “hot
spots” in the substrates. Particularly, SERS substrates with
regular and ordered array structures are advantageous over those made
of ordinary metal composites.[31,32]In terms of the
study or application of SERS with noble nanoparticles,
spherical silica could be an excellent core or support, mainly because
of its remarkable features such as monodispersibility, high optical
transparency and thermal stability, good biocompatibility, and simple
synthesis by the standard Stöber method.[33−37] Furthermore, SiO2 can be easily surface-functionalized
by organosilanes, including polydiallylodimethyl ammonium chloride,[38] 3-mercaptopropyltrimethoxysilane,[39,40] 3-aminopropyl trimethoxysilane,[41] polyethyleneimine,
and other organic compounds such as dopamine[42] and vinylpyrrolidone.[43] The as-grafted
functional groups on the silica surface can create clinical sites
for the attachment and growth of Ag nanoparticles through the terminal
groups,[44] which could contribute to enhancing
SERS. Le Beulze et al. decorated Ag nanoparticles (diameter > 10
nm)
onto SiO2 microspheres surface-functionalized with organosilanes
and positively charged polymers to obtain a raspberry-like SiO2@Ag nanostructure that can function as a new type of SERS
substrate for the detection of analytical targets.[45] Wang et al. utilized a thin polyethyleneimine interlayer
to adsorb dense Au nanoparticles as seeds and prepared a silver shell/silica
core nanostructure as the SERS substrate with a limit of detection
as low as 10–9 M for the pesticide thiram.[46] Chen et al. deposited Ag onto a SiO2 nanosphere template and fabricated broccoli-like Ag arrays; the
as-obtained Ag arrays as the SERS for endocrine-disrupting chemicals
have a limit of detection of 2.2 × 10–8 M.[47] These research studies on Ag nanoparticle-decorated
SiO2 nanosphere for SERS, nevertheless, utilize complicated
and time-consuming procedures as well as strong reducing agents or
external energy sources for reducing the Ag precursor. This would
provide polydispersed Ag nanoparticles with good access to the surface
of silica nanospheres, thereby damaging the reproducibility and stability
of the as-prepared SERS substrate.Bearing those perspectives
in mind, here we adopt a facile and
versatile method to prepare a Ag nanoparticle-decorated raspberry-like
SiO2 composite (SiO2@Ag) as a novel SERS substrate.
In the presence of poly(vinylpyrrolidone) (PVP) as both a modifier
and reductant, Ag nanoparticles (Ag NPs) tend to in situ deposit on
the surface of SiO2 but not aggregate thereon, while SiO2 nanospheres function to prevent the aggregation of Ag nanoparticles
and facilitate the formation of a large amount of accessible “hot
spots” in the nanogap region for high SERS enhancement. Moreover,
Ag nanoparticle-decorated SiO2 nanosphere arrays (SiO2@Ag arrays) are assembled via the evaporation-induced self-assembly
of SiO2@Ag. This article reports the preparation of the
SiO2@Ag composite and SiO2@Ag arrays as well
as their use as the SERS substrates for the detection of rhodamine
6G (denoted R6G), a commonly used organic dye that is a potential
pollutant to the environment.
Results and Discussion
Figure a–c
shows the TEM images of SiO2 nanoparticles. It is seen
that the SiO2 nanoparticles obtained by the modified Stöber
method under different proportions of reactants (mass fraction of
TEOS, ethanol, and ammonium is 1:25:1, 2:22:1, and 2:25:1) have an
average diameter of 50, 150, and 300 nm, respectively. Figure d shows the FTIR spectra of
pure SiO2 nanoparticles and PVP-SiO2. The absorbance
bands near 1070 and 793 cm–1 are attributed to the
asymmetric stretching vibration and the symmetric stretching vibration
of Si–O–Si. The stretching vibration peak of Si–OH
emerges at 973 cm–1; the peaks at 1629 and 3419
cm–1 correspond to the bending vibration of H–O–H
and the stretching vibration of O–H, respectively.[48] The absorbance peak of the PVP-modified silica
at 1629 cm–1 is weaker than that of the pure silica,
which demonstrates that the content of −OH on the silica surface
decreases after surface-capping by PVP.[49] In addition, the −CH2 stretching vibration peaks
are located at 2927 and 2980 cm–1, which proves
that PVP is modified onto the surface of the nanosilica. Figure e shows the TEM image
of PVP-capped SiO2. It can be seen that the surface of
PVP-capped SiO2 is clean and relatively smooth, but the
surface of the SiO2@Ag composite is relatively rough because
of the formation of uniform and abundant Ag NPs.
Figure 1
TEM images of SiO2 nanoparticles with a size of (a)
50 nm, (b) 150 nm, and (c) 300 nm. (d) FTIR spectra of the pure SiO2 and PVP-modified SiO2. (e) TEM image of PVP-capped
SiO2.
TEM images of SiO2 nanoparticles with a size of (a)
50 nm, (b) 150 nm, and (c) 300 nm. (d) FTIR spectra of the pure SiO2 and PVP-modified SiO2. (e) TEM image of PVP-capped
SiO2.It is essential that
SERS substrates have abundant “hot
spots” (e.g., metal nanoparticles, nanogaps of closely spaced
metal nanoparticles) for acquiring good performance. Figure a–c shows the TEM images
of various SiO2@Ag composites. The Ag NPs in SiO2@Ag-50 exhibit a larger size and more uneven distribution than those
in other composites, and the particle size of Ag NPs in SiO2@Ag-150 and SiO2@Ag-300 is about 2–3 nm. As the
size of SiO2 increases from 50 to 150 and 300 nm, the plasmon
peak of corresponding SiO2@Ag composites blue-shifts from
476 to 442 and 442 nm, and the absorbance spectrum of SiO2@Ag-50 is broadened in association with the appearance of a new shoulder
peak (Figure d). The
nonuniform particle size and diverse shape of the Ag NPs in the SiO2@Ag-50 composite could be attributed to the fact that a less
amount of PVP is grafted onto the surface of a smaller nanosilica;
when the size of nano-SiO2 is about 50 nm, the steric hindrance
would be enhanced to hinder the nucleation of Ag NPs and allow the
full growth of Ag crystals. As a result, the amount of the surface-grafted
Ag nanoparticles would decrease and their average radius would increase,
thereby affording Ag NPs with nonuniform particle sizes and diverse
shapes. The SERS spectra of 10–4 M R6G on various
SiO2@Ag composites are shown in Figure e, where the intensity of the peak at 1645
cm–1 is quantified to compare the signal enhancement
ability of the nanosilica-based composites with different sizes of
PVP-SiO2 (Figure f). It is seen that all the three kinds of SiO2@Ag composites can enhance the Raman signal intensity, and composites
SiO2@Ag-150 and SiO2@Ag-300 provide a much stronger
Raman signal intensity than SiO2@Ag-50. This is because
the average radius of Ag nanoparticles decreases and the amount of
Ag nanoparticles grafted on the nanosilica surface increases with
increasing size of the nanosilica, which contributes to facilitating
the creation of “hot spots” under enhanced plasmon coupling
and local electric field and adding to Raman signal enhancement capability.
Figure 2
TEM images
of (a) SiO2@Ag-50, (b) SiO2@Ag-150,
and (c) SiO2@Ag-300 composites; insets are images with
a higher magnification; their (d) ultraviolet–visible light
(UV–vis) spectra and (e) Raman spectra; and (f) corresponding
intensities of peaks at 1198 and 1645 cm–1.
TEM images
of (a) SiO2@Ag-50, (b) SiO2@Ag-150,
and (c) SiO2@Ag-300 composites; insets are images with
a higher magnification; their (d) ultraviolet–visible light
(UV–vis) spectra and (e) Raman spectra; and (f) corresponding
intensities of peaks at 1198 and 1645 cm–1.Figure a–d
shows the TEM images of various SiO2@Ag composites prepared
under different pH values (the numeral suffixes 7, 8, 9, and 10 refer
to the pH values). Sodium hydroxide not only acts as a pH regulator
but also plays an essential role during the reaction process. When
the pH of the reaction system is 10, excessive Ag2O will
be generated, as evidenced by the relevant XRD analysis shown in Figure e, and the presence
of Ag2O is harmful to SERS.[50] The UV–vis absorbance spectra of various SiO2@Ag
composites prepared under different pH values are shown in Figure f. It is seen that
SiO2 does not have a distinct UV–vis absorbance
signal. As the pH value of the reaction system increases from 7 to
9, the plasmon peaks of corresponding SiO2@Ag composites
slightly blue-shift from 468 to 462 and 456 nm, and their maximum
absorbance intensity gradually increases therewith, which means that
the size of Ag NPs decreases and their amount increases with increasing
pH. This could be because the increase of pH from 7 to 9, i.e., the
increase of −OH concentration, contributes to promoting the
nucleation of Ag NPs and slowing down the growth of Ag NPs. Furthermore,
the SERS spectra of R6G in Figure g and the signal intensities of the peak at 1645 cm–1 are quantified to compare the Raman signal enhancement
ability of the as-prepared SiO2@Ag composites (Figure h). It can be seen
that the SiO2@Ag composite prepared at a pH value of 9
exhibits stronger Raman signal enhancement capability than those composites
prepared at pH values of 7 and 8. The reason lies in that the increase
in the pH value of the reaction solutions results in the increase
of the amount of Ag NPs and the decrease of their size, which is favorable
for the formation of more closely spaced Ag NPs with dense inter-nanogaps
as the “hot spots”, thereby contributing to Raman signal
enhancement.
Figure 3
(a–d) TEM images of SiO2@Ag composites
obtained
under a reaction solution pH of 7, 8, 9, and 10 and their (e) XRD
patterns, (f) UV–vis spectra, and (g) Raman spectra as well
as (h) corresponding signal intensities of the absorbance peaks at
1198 and 1645 cm–1.
(a–d) TEM images of SiO2@Ag composites
obtained
under a reaction solution pH of 7, 8, 9, and 10 and their (e) XRD
patterns, (f) UV–vis spectra, and (g) Raman spectra as well
as (h) corresponding signal intensities of the absorbance peaks at
1198 and 1645 cm–1.The Ag nanoparticles decorated on the surface of SiO2 are
in direct contact with the analyte molecules and could significantly
affect the SERS activity. The SiO2@Ag prepared at an initial
Ag(NH3)2OH concentration of 0.15 M and a pH
of 9 under room temperature is used as the example and analyzed by
TEM in association with energy-dispersive X-ray (EDX) analysis to
clarify that supposition. Figure a,b shows the SEM images and EDX mapping of Ag. It
can be seen that the nanosilica spheres retain nearly unchanged shape
after the surface-capping by PVP and the decoration by Ag nanoparticles.
The modifier PVP as both a modifier and mild reductant can cover the
entire surface of the nanosilica and reduce Ag+ to form
Ag nanoparticles with highly uniform size and abundant nanogaps as
“hot spots”, which contributes to facilitating SERS. Figure c shows the SERS
spectra of R6G solutions with concentrations ranging from 10–9 to 10–2 M in the presence of the as-prepared SiO2@Ag composite as the substrate. It is seen that the Raman
characteristic peak at 1645 cm–1 can be detected
even under a very low R6G solution concentration of 10–9 M. Figure d shows
the natural logarithms of the Raman signal intensity of R6G solutions
versus the negative logarithms of their concentrations from 1.0 ×
10–9 to 1.0 × 10–4 M. It
is seen that there is a good linear relationship between the two parameters.
The linear equation is written as y = 5.5711 –
0.3402x, and the linear regression coefficient is
described as R2 = 0.9444, where y is the SERS intensity of the Raman spectra and x is the concentration of the R6G solution. The limit of
detection (LOD) for R6G is about 10–9 M. The SERS
enhancement factor (EF) is calculated as EF = (ISERS × cblank)/(Iblank × cSERS), where ISERS and Iblank are
the intensities of the sample under SERS and non-SERS conditions,
and cSERS and cblank are the concentrations of R6G solutions under SERS and non-SERS
conditions. The EF value of the peak at 1645 cm–1 is estimated to be 2.76 × 106. In addition, the
SERS detection toward 4-mercaptobenzoic acid (4-MBA) and 4-mercaptophenol
(4-MPh) was also performed. As shown in Figure S1, their SERS signals are greatly improved.
Figure 4
FESEM images of (a) SiO2@Ag composites; (b) associated
element mappings of Ag; (c) SERS spectra of R6G solutions with concentrations
ranging from 10–9 to 10–4 M; (d)
logarithm of the SERS intensity of R6G at 1645 cm–1 as a function of negative logarithm of R6G concentration.
FESEM images of (a) SiO2@Ag composites; (b) associated
element mappings of Ag; (c) SERS spectra of R6G solutions with concentrations
ranging from 10–9 to 10–4 M; (d)
logarithm of the SERS intensity of R6G at 1645 cm–1 as a function of negative logarithm of R6G concentration.It is known that the average SERS intensity of
an ordered nanostructure
is 2–4 orders of magnitude larger than that of a single nanostructure.[36] This is because the ordered nanostructure can
provide an ultrastrong coupled plasmon and greatly enhance the local
electric field, thereby greatly affecting the SERS activity. Figure a,b shows the SEM
images of the SiO2@Ag array samples prepared by the evaporation-induced
self-assembly of SiO2@Ag composites. The abundant small-sized
Ag NPs with small interseparations or gaps as well as small gaps between
Ag NPs and SiO2@Ag composites contribute to providing much
more “hot spots”, thereby largely enhancing SERS. The
SERS spectra of the R6G solutions with concentrations from 10–11 to 10–2 M in the presence of SiO2@Ag arrays as the substrate are shown in Figure c. The Raman characteristic
peak at 1645 cm–1 can be detected even when the
concentration of the R6G solution is as low as 10–11 M, and there is a linear relationship between the natural logarithms
of the Raman signal intensity of the R6G solutions and the negative
logarithms of their concentrations from 1.0 × 10–10 to 1.0 × 10–2 M (Figure d). The linear equation is written as y = 4.7787 – 0.1530x, and the linear
regression coefficient is described as R2 = 0.9899. In this case, the LOD for R6G is 10–11 M, and the SERS enhancement factor is about 6.29 × 108.
Figure 5
(a, b) FESEM images of SiO2@Ag arrays. (c) SERS spectra
of R6G solutions with concentrations ranging from 10–11 to 10–2 M. (d) Logarithm of the SERS intensity
of R6G at 1645 cm–1 as a function of the negative
logarithm of R6G concentration. (e) Raman spectra of SiO2@Ag arrays and (f) the corresponding peak intensities of eight randomly
measured sites at 1645 cm–1.
(a, b) FESEM images of SiO2@Ag arrays. (c) SERS spectra
of R6G solutions with concentrations ranging from 10–11 to 10–2 M. (d) Logarithm of the SERS intensity
of R6G at 1645 cm–1 as a function of the negative
logarithm of R6G concentration. (e) Raman spectra of SiO2@Ag arrays and (f) the corresponding peak intensities of eight randomly
measured sites at 1645 cm–1.Reproducibility is a vital factor for the SERS substrates. Figure e shows the Raman
spectra of the R6G solution (10–5 M) measured at
eight sites with SiO2@Ag arrays as the SERS substrates.
(Here, the to-be-measured sites are randomly selected on the SERS
substrate covered with R6G.) The intensities of typical Raman peaks
at 1645 cm–1 are chosen to investigate the reproducibility
of the SERS enhancement (Figure f). The relative standard deviation of the eight measured
Raman signals is 8.58%, which confirms that the SiO2@Ag
array SERS substrate is reliable and reproducible.
Conclusions
Ag nanoparticles are in situ deposited on the
surface of silica
nanospheres in the presence of PVP as both a modifier and reductant
to afford the SiO2@Ag composite. The SiO2 nanospheres
as a matrix can prevent the aggregation of Ag nanoparticles and facilitate
the formation of a large amount of accessible “hot spots”
in the nanogap region for high SERS enhancement. Furthermore, SiO2@Ag arrays are assembled via the evaporation-induced self-assembly
of SiO2@Ag. The as-prepared SiO2@Ag composite
and SiO2@Ag arrays exhibiting a high metal coverage and
good stability as well as abundant “hot spots” could
be potential SERS substrates with desired Raman signal enhancement
capability. Particularly, the SiO2@Ag arrays as the SERS
substrate can even well detect R6G at a concentration of as low as
10–11 M with good reliability and reproducibility,
showing promising prospects for the detection of chemical and biological
molecules.
Experiments and Methods
Materials
and Chemicals
Tetraethylorthosilicate
(TEOS, ≥98%, AR) was purchased from Tianjin Kemiou Chemical
Reagent Company. PVP (K15, Mw: 10 000,
analytical reagent), silver nitrate (AgNO3, ≥99.8%,
analytical reagent), and R6G (analytical reagent) were purchased from
Sigma-Aldrich. Sodium hydroxide (NaOH), ammonium hydroxide (28%),
and ethanol (≥95%) were commercially obtained. Distilled water
was prepared at our laboratory and used as the solvent.
Experimental Procedure
PVP-modified
SiO2 particles, raspberry-like SiO2@Ag composite,
and SiO2@Ag arrays were prepared through the procedure
schematically shown in Scheme .
Scheme 1
Schematic Diagram of the Preparation of the SiO2@Ag Composite
and SiO2@Ag Arrays
Preparation of Monodispersed SiO2 Nanoparticles
via the Stöber Method
SiO2 nanoparticles
were prepared by the modified Stöber method.
Briefly, ethanol and ammonium were mixed in a three-neck flask under
gentle stirring while a certain amount of TEOS was added dropwise
into the mixed solution (the proportion (mass fraction) of TEOS, ethanol,
and ammonium was adjusted to be 1:25:1, 2:22:1, and 2:25:1 to obtain
SiO2 nanoparticles with different sizes). The mixed solution
becomes opaque in 20 min due to the formation of SiO2 nanoparticles.
No sedimentation was observed over a period of several hours, which
suggests that the as-generated SiO2 nanoparticles were
colloidally stable. The product was collected through filtration and
washed with deionized water and ethanol three times.
Preparation of PVP-Modified SiO2 Nanoparticles
SiO2 nanoparticles (2 g) and 100
g of water were charged into a 250 mL three-neck round-bottom flask.
The mixture was vigorously stirred until SiO2 was uniformly
dispersed in the reaction system. Then, an aqueous PVP solution (10
mL, 5 mM) was added into the colloid solution of SiO2 nanoparticles.
The resultant dispersion was allowed to react for 2 h. The product
was collected by filtration and rinsed with deionized water and ethanol
three times. The as-obtained modified SiO2 particles were
denoted PVP-SiO2.
Preparation of the SiO2@Ag Composite
PVP-SiO2 (0.4 g) was added
in 30 mL of water under vigorous
stirring, while a certain amount of NaOH (1 M) was added and stirred
for 10 min to adjust the pH of the mixed solution to 7–11.
Then, freshly prepared Ag(NH3)2OH (0.075–0.6
M) was quickly added to the PVP-SiO2 dispersion. The color
of the mixture changes from white to yellow or brown immediately due
to the formation of Ag nanoparticles. The PVP-SiO2 dispersion
was allowed to react for 2 h so as to achieve the sufficient deposition
of Ag nanoparticles on the PVP-SiO2 surface, yielding more
active sites.
Preparation of the SiO2@Ag Arrays
The SiO2@Ag arrays were prepared
by the evaporation-induced
self-assembly. In brief, a glass substrate was placed in a 10 mL vessel
containing 6 mL of ethanolic suspension of the SiO2@Ag
composite (0.8 wt %). Then, the vessel was placed vertically in a
constant temperature oven to evaporate ethanol and afford SiO2@Ag arrays via the orderly arrangement of the SiO2@Ag composite on the glass substrate under capillary force.
Characterization and SERS Measurement
The as-prepared
nanosilica was characterized by Fourier transform
infrared spectroscopy (FTIR, Nicolet 170sx, Thermo Fisher Scientific
Inc.). The morphology of the samples was observed with a transmission
electron microscope (TEM; JEM-2010, JEOL, Japan) and a scanning electron
microscope (SEM; Japan Electronics, Japan). The X-ray powder diffraction
(XRD) patterns of the products were obtained with an X-Pert Pro diffractometer
(Cu Kα radiation; λ = 0.15418 nm; voltage: 40 kV; current:
40 mA). The UV–visible absorbance spectra of SiO2@Ag composites were recorded with a Jinghua 723PC spectrometer (Shanghai,
China). The Raman spectra were collected with a laser confocal Raman
spectrometer (Renishaw RM-1000, U.K.) at an excitation wavelength
of 532 nm.For the SERS measurements, standard R6G solutions
at a concentration from 10–2 to 10–11 M were prepared. In addition, a proper amount of concentrated SiO2@Ag dispersion (10–2 M) was placed onto
a glass substrate and dried at room temperature. Onto the as-dried
glass substrate was dropped the R6G solution and dried at an ambient
condition to immobilize the organic dye on the surface of the substrate.
Upon completion of the immobilization of the R6G dye, the glass substrate
was used for SERS measurements to detect R6G.