It is well known that microbial populations and their interactions are largely influenced by their secreted metabolites. Noninvasive and spatiotemporal monitoring and imaging of such extracellular metabolic byproducts can be correlated with biological phenotypes of interest and provide new insights into the structure and development of microbial communities. Herein, we report a surface-enhanced Raman scattering (SERS) hybrid substrate consisting of plasmonic Au@Ag@mSiO2 nanorattles for optophysiological monitoring of extracellular metabolism in microbial populations. A key element of the SERS substrate is the mesoporous silica shell encapsulating single plasmonic nanoparticles, which furnishes colloidal stability and molecular sieving capabilities to the engineered nanostructures, thereby realizing robust, sensitive, and reliable measurements. The reported SERS-based approach may be used as a powerful tool for deciphering the role of extracellular metabolites and physicochemical factors in microbial community dynamics and interactions.
It is well known that microbial populations and their interactions are largely influenced by their secreted metabolites. Noninvasive and spatiotemporal monitoring and imaging of such extracellular metabolic byproducts can be correlated with biological phenotypes of interest and provide new insights into the structure and development of microbial communities. Herein, we report a surface-enhanced Raman scattering (SERS) hybrid substrate consisting of plasmonic Au@Ag@mSiO2 nanorattles for optophysiological monitoring of extracellular metabolism in microbial populations. A key element of the SERS substrate is the mesoporous silica shell encapsulating single plasmonic nanoparticles, which furnishes colloidal stability and molecular sieving capabilities to the engineered nanostructures, thereby realizing robust, sensitive, and reliable measurements. The reported SERS-based approach may be used as a powerful tool for deciphering the role of extracellular metabolites and physicochemical factors in microbial community dynamics and interactions.
Microbial biofilms,
the most common form of existence of microorganisms
in nature, are indispensable living entities governing the global
biogeochemical cycle and the healthy activity of the microbiota.[1] Biofilms can act as infectious agents,[2] and they are responsible for biofouling and biocorrosion
of materials, thereby causing a substantial economic burden in the
industry.[3] These microbial communities
possess genotypic and physiologic traits different from their planktonic
(e.g., free-living) counterparts being significantly more resistant
to antibiotics and other chemical agents.[4] Recently, the World Health Organization outlined antimicrobial resistance
as one of the 10 major threats to global health.[5] Hence, the study of microbial biofilms and their development
is essential to understand this microbial way of life and thus facilitate
strategies that allow their control and eradication.Biofilms
composed of multiple microbial species or by a single
species are enclosed at high cell densities within a self-produced
extracellular matrix. In such densely populated environments, as a
result of their metabolic activities, microbes excrete bioactive chemical
compounds that can act as cues and signals for intercellular communication,[6,7] as well as metabolic byproducts that can also greatly influence
the development and composition of biofilms.[8,9] For
instance, microbial fermentation can lead to the production of acids
that can lower the local pH significantly. Such acidification can
affect the physiological state of resident microbes,[10] promote resistance to antibiotics,[11] or induce enamel demineralization and dental caries.[12] Notably, the detection of pH has been used as
an indicator to reveal microbial growth. Moreover, biofilms are known
to affect wound healing. The capacity to eradicate the microbes from
the wound is significantly affected by changes in pH, as these will
influence the antimicrobial efficacy of antibiotics.[13] Thus, noninvasive and simultaneous monitoring of extracellular
bioactive metabolites and physicochemical factors (e.g., pH) with
spatial and temporal resolution can provide valuable information regarding
the mechanisms that regulate the biogenesis, composition, and function
of microbial communities.The rapid development of nanotechnology
and materials science in
recent years has made possible the rational design and fabrication
of a wide variety of nanostructured sensors for the noninvasive assessment
of the cell. Compared with molecular probes, nanosensors can effectively
enhance sensitivity, specificity, and targeting ability, as well as
provide additional multimodal, multiplexing, and multifunctional capabilities.[14,15]Several technologies have been reported for pH biosensing,
including
microelectrodes, nuclear magnetic resonance imaging, and field-effect
transistors; however, these methods are limited by slow response times
and low spatial resolution.[16] Optical sensing
of pH based on distinct absorption or fluorescence changes of reporter
molecules upon their protonation/deprotonation at different pH values
is gaining increasing attention owing to their noninvasive nature,
high sensitivity, and spatiotemporal resolution.[17−23] In this context, fluorescence microscopy is a popular technique
that has been widely used to study the role of hydrogen ions and pH
in physiological and pathological processes. Indeed, a wide array
of fluorescent molecules, as well as fluorescent nanoparticle-based
nanosensors, have been developed and successfully applied for real-time
imaging of pH in biological systems.[24−26]Surface-enhanced
Raman scattering (SERS) spectroscopy excels for
its ability to combine high sensitivity with rich vibrational information,
enabling detection limits down to the single-molecule level under
optimal conditions. The Raman signal can be excited with a wide range
of wavelengths, shows higher photostability, and displays narrower
bandwidth, which allows for simultaneous sensing of multiple analytes.[27] This makes SERS a powerful technique for multiplex
(bio)chemical analysis.[28] However, in situ
SERS detection of metabolic compounds is challenged by the biological
matrix, which can hamper the interaction of the target analyte with
the metal surface, as well as increase the background signal.[29,30]The combination of plasmonic nanostructures with molecular
sieve
materials is a way to overcome the aforementioned limitations of SERS
for bioanalysis. The porous size of certain materials, such as mesoporous
silica (mSiO2), zeolites, metal-organic frameworks (MOFs),
or covalent organic frameworks (COFs), among others, is similar to
that of bioactive metabolites. Therefore, those materials could be
applied as molecular sieves by size exclusion for SERS analysis when
combined with Au or Ag nanostructures.[31] These mesoporous structures allow diffusing only small molecules
toward the plasmonic nanostructure, while keeping large biomolecules
(peptides, proteins, etc.) away, thereby avoiding the need for sample
pretreatment. Several reports have already shown the molecular sieving
effect of mSiO2 and mesoporous TiO2 (mTiO2) in the SERS analysis of samples in complex media.[32−34] For instance, core–shell Ag@mSiO2 nanoparticles
have demonstrated good performance for selective sensing of organophosphorus
pesticides in different complex vegetable matrices.[33] In this context, plasmonic nanorattle structures with a
characteristic core@void@shell (yolk–shell) configuration,
are widely used materials in different fields due to the tailorability
and functionality of both the core and hollow shells.[35−39] In the particular case of SERS analysis, the mesoporous shell in
a yolk–shell structure provides spatial confinement to the
plasmonic core keeping colloidal stability while avoiding undesired
interaction of biomolecules with the metal surface that can impair
the reliability of the sensor.Herein, we report on the synthesis
of mSiO2 nanorattles
containing single plasmonic core–shell Au@Ag nanoparticles
(Au@Ag@mSiO2) as nanoprobes for the noninvasive detection
of extracellular metabolism in bacterial cultures by SERS. Initially,
we show the in situ detection of the secretion of pyocyanin metabolite
in liquid cultures of Pseudomonas aeruginosa with a high dynamic range. We also demonstrate the application of
plasmonic nanorattles encoded with a pH-dependent Raman active molecule,
4-mercaptobenzoic acid (4-MBA),[40] and embedded
in a block of nutrient agar as a multifunctional SERS platform for
highly sensitive detection and spatiotemporal imaging of metabolic
pH changes in colonies of Escherichia coli. Our results highlight the great potential of the Au@Ag@mSiO2 nanoparticles as a SERS sensor for diagnostic and environmental
applications.
Results and Discussion
Plasmonic
Au@Ag@mSiO2 nanorattles were obtained via
a multistep process where Au@Ag@ZIF-8 core–shell–shell
nanocrystals acted as sacrificial templates (Figure A). The first step involves the single encapsulation
of Au@Ag core–shell nanorods (Figure B1) within ZIF-8 nanocrystals (Figures B2 and S1A in the Supporting Information), as previously reported.[41] Subsequently, the Au@Ag@ZIF-8 nanocrystals are
coated with mSiO2 (with a pore size ∼3 to 4 nm)[42] through a sol–gel process in the presence
of cetyltrimethylammonium bromide (CTAB) (Figures B3 and S1B in
the Supporting Information). As expected the silica coating led to
a change in the ζ-potential from +31.0 ± 1.8 to −10.5
± 0.4 mV. Finally, the plasmonic mSiO nanorattles (Au@Ag@mSiO2) were obtained through the selective
etching of the ZIF-8 shell by acid treatment through the protonation
of imidazolate ligands from the MOF matrix. After ZIF-8 etching, a
further decrease of the ζ-potential was observed (−18.4
± 0.8 mV), probably as a consequence of CTAB removal. The process
was also studied by ultraviolet–visible–near infrared
(UV–vis–NIR) spectroscopy. As shown in Figure C, while the mSiO2 coating leads to a slight blueshift in the localized surface plasmon
resonance (LSPR) of Au@Ag@ZIF-8 nanocrystals due to scattering effects,
the etching of the ZIF-8 shell strongly affects the optical response
of the nanocrystals. Thus, the main LSPR band is blue-shifted from
648 to 607 nm, produced by the lower refractive index of the solvent
(water, 1.333) compared with ZIF-8 (∼1.54), and the extinction
at short wavelengths decreases due to the diminution of scattering
effects. Additionally, the dissolution of the ZIF-8 shell and the
formation of plasmonic mSiO nanorattles were
confirmed by transmission electron microscopy (TEM) analysis (Figures B4,D and S1C in the Supporting Information). The majority
of the nanorattles are formed by a silica capsule containing one Au@Ag
nanoparticle in their interior. Moreover, the analysis reveals the
presence of folds and creases resulting from the collapse of mSiO nanorattles after their air-drying. These results
were further confirmed by energy-dispersive X-ray (EDX) elemental
analysis (see Figure S2 in the Supporting
Information).
Figure 1
(A) Schematic representation of the multistep fabrication
process
of plasmonic mSiO2 nanorattles: ZIF-8 coating of Au@Ag
nanorods, mSiO2 coating of Au@Ag@ZIF-8 nanoparticles, and
ZIF-8 etching of Au@Ag@ZIF-8@mSiO2. (B) TEM images of Au@Ag
nanorods (B1), Au@Ag@ZIF-8 nanoparticles (B2), Au@Ag@ZIF-8@mSiO2 nanoparticles (B3), and plasmonic mSiO2 nanorattles
(B4). (C) Normalized extinction spectra of Au@Ag@ZIF-8 nanoparticles
(blue), Au@Ag@ZIF-8@mSiO2 nanoparticles (green), and plasmonic
mSiO2 nanorattles (pink). (D) Representative TEM image
of plasmonic mSiO2 nanorattles.
(A) Schematic representation of the multistep fabrication
process
of plasmonic mSiO2 nanorattles: ZIF-8 coating of Au@Ag
nanorods, mSiO2 coating of Au@Ag@ZIF-8 nanoparticles, and
ZIF-8 etching of Au@Ag@ZIF-8@mSiO2. (B) TEM images of Au@Ag
nanorods (B1), Au@Ag@ZIF-8 nanoparticles (B2), Au@Ag@ZIF-8@mSiO2 nanoparticles (B3), and plasmonic mSiO2 nanorattles
(B4). (C) Normalized extinction spectra of Au@Ag@ZIF-8 nanoparticles
(blue), Au@Ag@ZIF-8@mSiO2 nanoparticles (green), and plasmonic
mSiO2 nanorattles (pink). (D) Representative TEM image
of plasmonic mSiO2 nanorattles.Atomic force microscopy (AFM) was used to estimate the wall thickness
of the mesoporous silica shell and the dimensions of the nanorattles
(Figures and S3 and S4 in the Supporting Information). The
analysis of AFM height profiles performed on the dried nanorattles
(Figures A,B and S3 in the Supporting Information) indicates an
average mSiO2 shell thickness of 10.1 ± 1.1 nm, determined
as half of the height in the collapsed flat region. On the other hand,
the analysis of hydrated nanorattles shows an average diameter of
342.3 ± 38.3 nm, estimated as the horizontal distance measured
in the height profile (Figures C,D and S4 in the Supporting Information).
This value is in agreement with the dimensions of the Au@Ag@ZIF-8
obtained by TEM analysis. It should be noted that the clear differences
between the dried and hydrated states demonstrate the flexibility
of the mesoporous silica capsules.
Figure 2
(A) AFM topographic amplitude image of
multiple plasmonic mSiO2 nanorattles in the dried state.
(B) Height profile of a plasmonic
mSiO2 nanorattle in the dried state. (C, D) Representative
AFM topographic three-dimensional (3D) height image (C) and height
profile (D) of a hydrated plasmonic mSiO2 nanorattle.
(A) AFM topographic amplitude image of
multiple plasmonic mSiO2 nanorattles in the dried state.
(B) Height profile of a plasmonic
mSiO2 nanorattle in the dried state. (C, D) Representative
AFM topographic three-dimensional (3D) height image (C) and height
profile (D) of a hydrated plasmonic mSiO2 nanorattle.Next, we evaluated the capability of the plasmonic
mSiO2 nanorattles for SERS detection in a complex biological
medium. Selecting
as model metabolite commercial pyocyanin, we studied first the sensing
capabilities of the plasmonic nanorattles in water as well as in lysogeny
broth (LB), a complex nutrient medium commonly used for culturing
bacteria. The SERS spectrum of pyocyanin shows a group of peaks between
400–600 cm–1 corresponding to different ring
deformations (Figure S5A in the Supporting
Information).[34] The SERS data analysis
of samples containing different concentrations of pyocyanin shows
that the metabolite in water can be quantitatively detected in a concentration
range from 20 nM to 10 μM (Figure S5A,B in the Supporting Information), while in LB medium it is detected
in a concentration range from 0.5 to 50 μM, fitting in both
cases extremely well to a Langmuir isotherm (Figure S5C,D in the Supporting Information). Subsequently, the detection
of pyocyanin excreted by P. aeruginosa bacteria to the culture medium was investigated. To this aim, sample
aliquots were collected at different time intervals of bacteria growth,
mixed with the plasmonic mSiO2 nanorattles, and analyzed
by SERS and UV–vis-NIR spectroscopy without any sample treatment. Figure A shows the time
evolution of the SERS spectra during the bacteria growth where the
presence of pyocyanin is evidenced after 4 h, corresponding to 1.15
× 109 CFU/mL (estimated from the value of the optical
density at 600 nm, OD600nm, 1.434, (Figure B)). No evidence of signals from other molecules
secreted by bacteria are observed most probably due to the sieving
effect of the mSiO2 (see Figure S6 in the Supporting Information).[32] The
interpolation of the SERS intensity data at 675 cm–1 to the calibration curve obtained with commercial pyocyanin in LB
medium (Figure S5D in the Supporting Information)
allows obtaining the evolution curve of the production of pyocyanin.
As shown in Figure B, at 4 h the concentration of pyocyanin secreted by P. aeruginosa was approximately 1 μM, and subsequently,
it increased abruptly during the exponential growth of P. aeruginosa. Notably, no pyocyanin could be detected
at 4 h of bacterial growth by UV–vis-NIR spectroscopy (Figure S7 in the Supporting Information), which
indicates the higher sensitivity of our SERS sensor and its suitability
to detect pyocyanin at the early stages of bacterial growth. As expected,
control experiments performed with surfactant-stabilized Au@Ag nanorods
show their limitation to detect pyocyanin in LB medium due to the
lack of colloidal stability (Figure S8 in
the Supporting Information).
Figure 3
(A) SERS analysis of pyocyanin secreted by the P.
aeruginosa PA14 strain at different growth times.
For clarity, the spectra noted with ×5 were multiplied by a factor
of 5. (B) Growth curve of P. aeruginosa PA14 by measuring the optical density of the liquid culture at 600
nm (black squares) and amount of pyocyanin excreted by P. aeruginosa PA14 determined by SERS as a function
of time (red squares). The error bars represent the standard deviation
of three different measurements. All SERS measurements were carried
out with an excitation laser line at 785 nm employing a 15× objective,
maximum power of 53.1 mW, and an acquisition time of 10 s.
(A) SERS analysis of pyocyanin secreted by the P.
aeruginosa PA14 strain at different growth times.
For clarity, the spectra noted with ×5 were multiplied by a factor
of 5. (B) Growth curve of P. aeruginosa PA14 by measuring the optical density of the liquid culture at 600
nm (black squares) and amount of pyocyanin excreted by P. aeruginosa PA14 determined by SERS as a function
of time (red squares). The error bars represent the standard deviation
of three different measurements. All SERS measurements were carried
out with an excitation laser line at 785 nm employing a 15× objective,
maximum power of 53.1 mW, and an acquisition time of 10 s.Once we confirmed the suitability of colloidal Au@Ag@mSiO2 nanorattles toward plasmonic detection of a bacterial metabolite
in growth medium, we explored their application for monitoring extracellular
pH changes that result from the metabolic activities of bacteria.
The fermentation of glucose by E. coli leads to the production of lactic and acetic acid that can contribute
to the acidification of the external medium.[43] For obtaining a SERS-active pH nanosensor, the plasmonic surface
of the mSiO2 nanorattles was functionalized with a pH-sensitive
molecular probe such as 4-MBA. Since its SERS features strongly depend
on the pH of the surrounding environment,[44] 4-MBA has been used to fabricate SERS-based pH nanosensors.[45−48] The 4-MBA encoding was studied by SERS (Figure S9A,B in the Supporting Information) suggesting the rapid diffusion
of this molecule through the mesoporous SiO2 shell and
its attachment onto the metallic surface to form a monolayer within
the first 10 min. Typical SERS spectra of 4-MBA recorded in phosphate
buffer at different pHs are shown in Figure S9C in the Supporting Information. The peaks at 695, 848, 1430, and
1710 cm–1 are assigned to the vibrational modes
of the pH-sensitive carboxylic moiety of 4-MBA. While the bands at
848 cm–1 (COO– bending) and 1430
cm–1 (COO– stretching) arise in
an alkaline environment when the molecule is deprotonated, those at
695 cm–1 (COOH stretching) and 1710 cm–1 (C=O stretching) appeared when the molecule is protonated
in an acid environment.[44] Note that the
two prominent spectral bands at 1076 and 1586 cm–1, attributed to the aromatic ring breathing mode, are not pH-sensitive.[47] In the present study, we focused on the 695
and 848 cm–1 spectral bands. To evaluate the performance
of the plasmonic mSiO2 nanorattles as a pH sensor, they
were suspended in a series of buffered solutions with verified pHs
ranging between 2.5 and 12 (see the Experimental
Section) and we monitored the variation of the relative ratio
of the areas of the bands at 695 (A695) and 848 cm–1 (A848) as described elsewhere[44]By plotting R as a function of pH (see Figure S9D in
the Supporting Information), we
obtained a calibration curve that follows the typical trend of the
Henderson-Hasselbalch equation and that fitted to a sigmoidal equation
revealing a linear region in the pH range from 5.0 to 8.0. In addition,
compared with typical core–shell Au@Ag@mSiO2 nanoparticles,
the plasmonic Au@Ag@mSiO2 nanorattles featured higher sensitivity
(see further details in Figure S10 in the
Supporting Information).Next, the MBA-encoded plasmonic nanorattles
were tested for monitoring
the changes in the extracellular pH generated as a result of bacterial
metabolism in a liquid medium. The pH nanosensors were incubated with
aliquots taken from cultures of planktonic E. coli grown overnight in LB supplemented, or not, with 2% of glucose (Figure S11A in the Supporting Information). As
shown in Figure S11A in the Supporting
Information, the fermentation of glucose by E. coli induced acidification of the medium protonating the carboxylic group
of the Raman reporter detected by the appearance of the peak at 695
cm–1 (COOH stretching) and the disappearance of
the peak at 848 cm–1 (COO– bending).
These spectral changes were not observed in the bacterial culture
grown in LB without glucose, used as a control. Interpolation of the
SERS data to the calibration curve (Figure S9D in the Supporting Information) yielded pH values of ca. 5.0 and
7.3 in the culture media with and without glucose, respectively. These
values of pH were further confirmed using a conventional pH meter,
thereby demonstrating the reliability of the nanosensor. To confirm
that the 4-MBA spectral changes were produced by the metabolic activities
of bacteria, further experiments were carried out with P. aeruginosa (Figure S11B in the Supporting Information), a nonfermenter microbe unable to
lead to an acidification of the medium in the presence of glucose.
As expected, no significant spectral variations were observed in the
presence of glucose.In nature, bacteria often live as densely
packed colonies subjected
to multiple growth constraints that are absent in planktonic cultures.[49] In solid media, nutrients must diffuse through
the matrix into the colonies, whereas metabolic end-products diffuse
away.[50] In particular, the outward diffusion
of metabolic acids generates pH gradients that influence the development
and composition of the microbial populations.[10,51] Intending to monitor the extracellular pH of bacterial colonies,
we fabricated a hybrid substrate that consists of 4-MBA-encoded plasmonic
nanorattles embedded in an agar matrix containing nutrients (i.e.,
LB). Agar is a gelling agent commonly used as a support matrix for
growing bacteria in vitro. Its macroporous structure and its large
water fraction facilitate nutrient uptake, as well as diffusion of
metabolites and other chemical species to the local environment. The
4-MBA-encoded plasmonic nanorattles were embedded by simple addition
to molten LB-agar. As shown in Figure S12A in the Supporting Information, nanoparticles are homogeneously distributed
in the agar layer. The substrate, termed nanorattles@LB-agar, displays
an optical response similar to the colloidal nanorattles in water
with the main LSPR band centered at 608 nm, but with an increase of
extinction especially at shorter wavelengths attributed to the scattering
of light by the LB-agar matrix (Figure S12B in the Supporting Information). The pH sensing capabilities of the
nanorattles@LB-agar substrates were tested by adjusting the pH of
the molten LB-agar medium in the range of 2.6–9.2 (see Experimental Section for further details). Like
the colloidal nanorattles, the nanorattles@LB-agar can efficiently
produce pH-sensitive signals over a physiologically relevant range
(Figure A). Remarkably,
the calibration curve obtained (Figure B) demonstrates the high performance of this substrate.
Besides, further experiments performed to test the repeatability and
uniformity of the substrates (Figure S13 in the Supporting Information) confirm their potential as robust
and reliable pH sensors.
Figure 4
(A) Representative SERS spectra of nanoratles@LB-agar
substrates
at different pHs. (B) Experimental calibration curve of ratio R = (A695 – A848)/(A695 + A848) as a function of pH. The error bars show the
standard deviation from the mean of n = 15 measurements.
SERS measurements were carried out at 785 nm with a 10× objective,
8.22 mW maximum power, 3 accumulations, and an acquisition time of
10 s. (C) Schematic illustration of in situ SERS monitoring of pH
changes as a result of bacterial metabolism.
(A) Representative SERS spectra of nanoratles@LB-agar
substrates
at different pHs. (B) Experimental calibration curve of ratio R = (A695 – A848)/(A695 + A848) as a function of pH. The error bars show the
standard deviation from the mean of n = 15 measurements.
SERS measurements were carried out at 785 nm with a 10× objective,
8.22 mW maximum power, 3 accumulations, and an acquisition time of
10 s. (C) Schematic illustration of in situ SERS monitoring of pH
changes as a result of bacterial metabolism.Since the nanorattles@LB-agar substrates can support bacterial
growth as colonies (Figure S14 in the Supporting
Information), we next assessed the suitability of the plasmonic platform
for space- and time-resolved monitoring of microbial metabolism in
situ by SERS during the growth of E. coli bacteria, as a single colony, with and without glucose (Figures C and 5). As shown in the scheme of Figure C, as the population of bacteria increases
with time, a gradient of pH should appear as a consequence of glucose
fermentation and the diffusion of metabolic acids. To prove that,
we performed SERS mappings over a selected area in the plasmonic platform
for 7 h (Figure A)
and then the pH was estimated by interpolating the relative ratio
of the areas of the bands at 695 (A695) and 848 cm–1 (A848) in the calibration curve from Figure B. Figure A shows the time evolution
of the extracellular pH distribution mappings monitored in a selected
area of the nanorattles@LB-agar substrate during the growth of an
individual colony of E. coli. Figure A also shows representative
SERS spectra recorded at different growth times of the E. coli colony in three different points of the nanorattles@LB-agar
substrate; (1) inside the colony, (2) at the border of the colony,
and (3) a few millimeters far from the colony, as indicated. The pH-sensitive
bands at 695 and 848 cm–1 were taken to estimate
the pH. While at 0.5 h of growth the data analysis reveals a homogeneous
pH value of 7.0 (Figure A), the time-course SERS analysis demonstrates the progressive acidification
of the extracellular medium and a pH gradient within the colony toward
its margins. After 7 h of growth, it was detected a substantial decrease
in the local pH, which achieved values as low as 5.5 in the interior
of the colony. As expected, the pH distribution mappings obtained
in the absence of glucose did not show any significant change of the
pH during the growth of a single E. coli colony (Figure B)
in the recorded spectra throughout the growth time analyzed, demonstrating
that the pH changes measured in our system were indeed produced by
the fermentation of glucose. These results are further supported by
additional experiments shown in the Supporting Information (Figures S15 and S16 in the Supporting Information).
Importantly, we evaluated the signal stability of the nanorattles@LB-agar
during bacterial growth by acquiring SERS spectra at 0.5, 3, 5, and
7 h, in distant regions from colonies, and using substrates without
glucose. As shown in Figure S13C,D in the
Supporting Information, no significant changes are observed in the
SERS spectra or the corresponding ratio R = (A695 – A848)/(A695 + A848) which further support the reliability of these platforms for pH
sensing. The utility of SERS for measuring pH has been demonstrated
in mammalian cells cultured in vitro.[45−48,52−56] However, to our knowledge, this is the first report describing the
application of SERS for monitoring pH changes in bacterial colonies.
Homeostasis of the bacterial pH is key for the regulation of important
cellular processes including gene expression, enzymatic function,
metabolism, motility, and division.[57] To
achieve pH homeostasis, bacterial cells possess regulatory networks
that govern the expression of distinct sets of genes under acid and
alkaline conditions. In this context, bacteria can metabolically adapt
to sublethal environmental acid stress (pH 5.5–4.5) by inducing
an adaptive tolerance response,[58] which
has been linked to antibiotic resistance.[59] Moreover, acidic pH sensing is required for virulence.[60] Also, the detection of pH changes as a result
of microbial metabolism during growth is a means to assess the bacterial
response to antibiotics.[61] Traditionally,
the molecular aspects of pH homeostasis in bacteria have been elucidated
through genetic and molecular biology tools.[57] However, these methods are generally destructive as they involve
the preparation of cellular extracts for biochemical analysis. In
this context, various fluorescence-based approaches have been developed
to noninvasively monitor pH changes in bacterial populations.[62] The aforementioned analytical approaches have
limited multiplex capabilities and generally only allow monitoring
a single parameter (e.g., pH). As shown herein, the plasmonic Au@Ag@mSiO2 nanorattles enabled not only the sensing of pH in bacterial
colonies but also the detection of secreted metabolites (e.g., pyocyanin)
in bacterial cultures, highlighting the promising potential of the
nanosensor for multiplex sensing of bacterial metabolism by SERS.
Figure 5
Spatiotemporal
pH distribution maps of a selected area of the nanorattles@LB-agar
substrate supplemented with glucose (A) and without glucose (B) during
the growth of a colony of E. coli.
SERS mappings were measured at 0.5, 3, 5, and 7 h, as indicated. Representative
SERS spectra were recorded at the points 1, 2, and 3 (indicated by
white dots) of maps shown in (A) and (B). The grey shaded regions
indicate the pH-sensitive bands at 695 and 848 cm–1 taken to estimate the pH through interpolation of the relative ratio
of their areas (A695 and A848) in the calibration
curve. Scale bars correspond to 1 mm. SERS measurements were carried
out at 785 nm with a 10× objective, 8.22 mW maximum power, 10
accumulations, and acquisition time of 1 s.
Spatiotemporal
pH distribution maps of a selected area of the nanorattles@LB-agar
substrate supplemented with glucose (A) and without glucose (B) during
the growth of a colony of E. coli.
SERS mappings were measured at 0.5, 3, 5, and 7 h, as indicated. Representative
SERS spectra were recorded at the points 1, 2, and 3 (indicated by
white dots) of maps shown in (A) and (B). The grey shaded regions
indicate the pH-sensitive bands at 695 and 848 cm–1 taken to estimate the pH through interpolation of the relative ratio
of their areas (A695 and A848) in the calibration
curve. Scale bars correspond to 1 mm. SERS measurements were carried
out at 785 nm with a 10× objective, 8.22 mW maximum power, 10
accumulations, and acquisition time of 1 s.
Conclusions
In conclusion, we developed a SERS-based approach for the space-
and time-resolved in situ monitoring of microbial metabolism. The
method relies on plasmonic Au@Ag@mSiO2 nanorattles comprising
a single plasmonic nanoprobe enclosed within a mesoporous silica capsule
that can efficiently enhance the Raman signal of pyocyanin and 4-MBA
in a complex biological medium (i.e., LB) bearing high ionic strength.
As reported in this work, the silica capsule is a key element that
facilitates robust and reliable SERS measurements as it provides colloidal
stability and molecular sieving capabilities. The intrinsic features
of the engineered nanorattles enable their incorporation into an agar
matrix for the fabrication of a biocompatible plasmonic substrate
(i.e., nanorattles@LB-agar) that supports bacterial growth as colonies
and cellular metabolism. We demonstrated that this hybrid plasmonic
sensor allowed spatial biosensing of extracellular pH in colonies
of E. coli, as well as sensing of secretion
of pyocyanin. Importantly, SERS sensing of pH in bacterial colonies
is shown for the first time. The reported SERS substrate shows not
only a strong signal but also a very good linear response to pH within
a wide range. Our approach based on plasmonic Au@Ag@mSiO2 nanorattles may also be adapted for real-time imaging of the biodistribution
of other metabolites, volatile compounds, etc. that result from cellular
metabolism. We envision that this new powerful tool will aid to gather
new insights regarding the role of extracellular metabolism in microbial
interactions and virulence, as well as in the development of antimicrobial
therapies.
Experimental Section
Materials
Cetyltrimethylammonium
bromide (CTAB, 98%),
cetyltrimethylammonium chloride (CTAC, 25% wt solution), sodium borohydride
(NaBH4, 99%), gold (III) chloride trihydrate (HAuCl4·3H2O, 99.9%), silver nitrate (AgNO3), l-(+)-ascorbic acid, 2-methylimidazole (2-MeIM, 99%),
zinc nitrate hexahydrate (Zn(NO3)2·6H2O, 99%), methanol, ethanol, tetraethyl orthosilicate (TEOS),
hydrochloric acid, agar, tryptone, yeast extract, sodium chloride,
sodium dihydrogen phosphate, sodium phosphate dibasic, 4-mercaptobenzoic
acid (4-MBA), and pyocyanin were purchased from Sigma-Aldrich. Milli-Q
water was used in all experiments.
Characterization
UV–vis–NIR absorption
spectra were recorded using an Agilent 8453 spectrophotometer. Transmission
electron microscopy was performed using a JEOL JEM 1010 microscope
operating at an acceleration voltage of 100 kV. EDX analysis was performed
using a JEOL 2100F field emission electron microscope equipped with
an energy-dispersive X-ray (EDX) spectrometer, operating at an accelerating
voltage of 200 kV. AFM images were collected on dry samples using
a Multimode 8 Nanoscope V (Veeco) in the tapping mode and an NCHV-A
cantilever (antimony (n)-doped Si, tip ROC < 10 nm, K = 40 N m–1, frequency 339–388 KHz). In
the case of hydrated samples, AFM images on were recorded using the
Peak Force QNM mode and a ScanAsyst-Fluid cantilever (silicon nitride,
tip ROC < 10 nm, K = 0.7 N m–1, frequency 150 KHz).
Synthesis of Au Nanorods
Au nanorods
(Au NRs) were
synthesized following a previously reported seed-mediated method.[63] Gold seeds were prepared by fast reduction of
HAuCl4 (10 mL, 0.5 mM) in 0.1 M CTAB aqueous solution upon
addition of 460 μL of freshly prepared NaBH4 (0.01
M dissolved in 0.01 M NaOH) under vigorous stirring. The color of
the solution changed from yellow to brownish-yellow and the seed solution
was aged at 27 °C for 30 min before use. Separately, a growth
solution was prepared by adding silver nitrate (70 μL, 0.1 M)
to HAuCl4 solution (10 mL, 0.5 mM) in 0.1 M CTAB, followed
by the addition of hydroquinone (500 μL, 0.1 M). The resulting
mixture was hand-stirred until it became clear. Next, 160 μL
of seed solution was added to the growth solution. The mixture was
mixed thoroughly and left undisturbed overnight at 27 °C. The
Au NRs were collected by centrifugation (8000 rpm, 20 min) and washed
twice with 10 mL of CTAC (80 mM). Finally, the Au NRs were redispersed
in 10 mL of CTAC (80 mM).
Synthesis of Au@Ag Core–Shell Nanorods
Au@Ag
core–shell nanorods were synthesized following a previously
reported method with slight modifications.[64] Briefly, 10 mL of the CTAC stabilized Au NRs was diluted to 40 mL
of CTAC (80 mM) followed by the addition of 3.5 mL of ascorbic acid
solution (0.1 M) and 3.5 mL of AgNO3 (0.01 M). The resulting
solution was placed in an oven at 60 °C for 3 h. After cooling
down to room temperature, the Au@Ag nanorods were washed twice with
10 mL of Milli-Q water (7000 rpm, 20 min) and finally redispersed
in 10 mL of Milli-Q water. The final CTAC concentration was adjusted
to 0.6 mM.
Synthesis of Au@Ag@ZIF-8 Nanoparticles
Au@Ag@ZIF-8
nanoparticles were prepared as described elsewhere.[41] In brief, 0.144 mL of CTAB (1 mM) was added to 1 mL of
an aqueous solution of 2-methylimidazole (1.32 M) and stirred for
5 min. Then, 1 mL of Zn(NO3)2·6H2O (24 mM) and 1 mL of Au@Ag nanorods (final CTAC concentration, ca.
0.6 mM) were sequentially added to the mixture, stirred for 5 min,
and left undisturbed for 3 h. The resulting Au@Ag@ZIF-8 nanoparticles
were washed once with 10 mL of methanol (5500 rpm, 5 min) and finally
redispersed in 3.14 mL of methanol.
Synthesis of Au@Ag@mSiO2 Nanorattles
Au@Ag@mSiO2 nanorattles were
prepared using a template selective etching
approach. First, Au@Ag@ZIF-8 nanoparticles were coated with a thin
layer of mesoporous silica following a previously reported protocol
with modifications.[65] In a typical experiment,
4 mL of Au@Ag@ZIF-8 nanoparticles was centrifuged at 5500 rpm for
5 min, dried at 60 °C for 1 h, and subsequently dispersed in
16 mL of a solution containing 1.5 mM CTAB and 8.25 mM 2-methylimidazole.
Mesoporous silica coating was then carried out by adding three aliquots
of TEOS (25 μL, 10 vol% in ethanol) at 60 min intervals to the
colloidal suspension under stirring. After the third addition of TEOS,
the mixture was stirred overnight. The resulting Au@Ag@ZIF-8@mSiO2 nanoparticles were washed twice with 10 mL of ethanol (6000
rpm, 10 min) and finally dispersed in 2 mL of ethanol. Next, the selective
etching of ZIF-8 to obtain the Au@Ag@mSiO2 nanorattles
was performed using HCl. Au@Ag@ZIF-8@mSiO2 nanoparticles
(2 mL) were centrifuged (6000 rpm, 10 min), and the pellet was dispersed
in 5 mL of Milli-Q water, followed by the addition of 3 mL of 0.06
M HCl. The suspension was sonicated for 15 min, and the final Au@Ag@mSiO2 nanorattles were washed three times by centrifugation (5000
rpm, 10 min) with 10 mL of ethanol and finally redispersed in 2 mL
of ethanol.
Synthesis of Core–Shell Au@Ag@mSiO2 Nanoparticles
In a typical experiment, Au@Ag nanoparticles
(8 mL) dispersed in
CTAC (0.6 mM) were centrifuged and redispersed in 25 mL of CTAB (6
mM). Then, 12 mL of ethanol, 200 μL of 2-methylimidazole, and
82 μL of TEOS (40% in ethanol) were sequentially added under
stirring to the mixture. After stirring overnight, the particles were
washed two times with ethanol and finally redispersed in ethanol.
Calibration Curve for pH Monitoring Using Colloidal Au@Ag@mSiO2 Nanorattles
First, 10 sample aliquots of 100 μL
Au@Ag@mSiO2 nanorattles were mixed with 100 μL of
a 5 mM ethanolic solution of 4-MBA. After 45 min, each aliquot was
centrifuged (4500 rpm, 5 min) twice, the first time the pellet was
redispersed in 1 mL of water and the second time in 20 μL of
water by sonication. Subsequently, the colloids were mixed with 500
μL of different 100 mM PB buffer solutions with pH values ranging
from 2.5 to 12. Finally, all of the samples were analyzed by SERS.
Calibration Curve for pH Monitoring in Au@Ag@mSiO2 Nanorattles@LB-Agar
Substrates
First, 10 aliquots of 300
μL of Au@Ag@mSiO2 nanorattles were mixed with 300
μL of a 5 mM ethanolic solution of 4-MBA. After 45 min, each
aliquot was centrifuged (4500 rpm, 5 min) twice, the first time the
pellet was redispersed in 1 mL of water and the second time in 20
μL of water by sonication. Separately, a series of buffered
lysogeny broth (LB) medium was prepared by dissolving tryptone (40
mg), yeast extract (20 mg), and sodium chloride (40 mg) in 4 mL of
100 mM PB solutions with pH values ranging from 2.6 to 9.2. The pH
of the resulting solutions was confirmed using a pH meter. Next, 60
mg of agar were added and the mixture was heated to dissolve the agar.
Immediately after, 100 μL of molten buffered LB-agar media was
added to the MBA-encoded nanorattles (20 μL) and the mixture
was transferred to a PDMS mold (1 × 1 × 0.5 cm3) placed over a glass slide. Once solidified, the different pH-adjusted
nanorattles@LB-agar substrates were analyzed by SERS.
Preparation
of Au@Ag@mSiO2 Nanorattles@LB-Agar Substrates
for In Situ Monitoring of pH
Au@Ag@mSiO2 nanorattles
(900 μL) were mixed with 500 μL of a 5 mM ethanolic solution
of 4-MBA and allowed to diffuse for 45 min. The 4-MBA-encoded nanorattles
were centrifuged (4500 rpm, 5 min) twice, the first time the pellet
was redispersed in 1 mL of water and the second time in 20 μL
of water by sonication. For the substrate preparation, the 4-MBA-encoded
nanorattles were mixed with 300 μL of molten LB-agar (10 g of
tryptone, 5 g of yeast extract, 10 g of NaCl, and 15 g of agar per
liter of water) containing 2% glucose and then poured in a PDMS mold
(2 × 2 × 0.5 cm3) placed over a glass slide.
Once solidified, the LB-agar substrate doped with 4-MBA-encoded Au@Ag@mSiO2 nanorattles was transferred to a humidity chamber to avoid
dehydration. A drop of 2 μL of the bacterial suspension of E. coli (OD600nm of 10) was spotted on
the substrate and allowed to grow at 30 °C. For control experiments,
substrates were also prepared in the absence of glucose.
Bacterial
Strains and Culture Conditions
Typically,
bacterial cells of P. aeruginosa PA14
and E. coli MG1655 were streaked from
frozen stocks onto lysogeny broth (LB) agar plates and incubated overnight
at 30 °C. Single colonies of P. aeruginosa strains were used to inoculate 10 mL of LB medium (LB: 10 g of tryptone,
5 g of yeast extract, and 10 g of NaCl per liter of water) and grown
at 37 °C with agitation (220 rpm) for 18 h. Next, the culture
was washed three times with fresh LB (7000 rpm, 3 min) and the cell
pellet was resuspended in 50 mL of fresh LB. The culture was incubated
at 37 °C with agitation (220 rpm), and the samples were collected
at various times for analysis for SERS analysis and measurement of
the concentration of cells through optical density at 600 nm (OD600nm). E. coli strains were
used to inoculate 10 mL of LB medium and grown at 37 °C with
agitation (220 rpm) for 18 h. Next, the culture was centrifuged (4000
rpm, 10 min), and the cell pellet was resuspended in LB medium to
an optical density at 600 nm (OD600) of 10.
Pyocyanin
Extraction Assay
Pyocyanin extraction was
performed as previously reported.[34] Aliquots
of bacterial culture of P. aeruginosa were collected at 4, 7, and 24 h of bacterial growth and centrifuged
at 4000 rpm for 10 min. The supernatant (4 mL) was filtered using
a syringe filter (0.2 μm pore size) and subsequently mixed with
6.7 mL of chloroform under vigorous agitation to extract pyocyanin
to the organic phase. Next, the sample was centrifuged at 9000 rpm
for 6 min and 3 mL of the organic phase was collected and mixed with
1.5 mL of a 0.2 M HCl solution to extract pyocyanin to the aqueous
phase. Finally, the sample was centrifuged (9000 rpm, 6 min) and the
aqueous phase containing pyocyanin was analyzed by UV–vis-NIR
spectroscopy at 520 nm.
SERS Measurements
SERS experiments
were conducted in
a Renishaw InVia Reflex system, composed of a confocal microscope,
a CCD camera, high-resolution diffraction gratings (1200 grooves cm–1), monochromatic light source (laser 785 nm), and
optical components (filters and lenses).
Detection and Quantification
of Secreted Pyocyanin in Planktonic
Cultures
First, a calibration curve was obtained. Thus, aliquots
of 100 μL of Au@Ag@mSiO2 nanorattles in ethanol were
added each to 100 μL water and centrifuged at 4500 rpm, 5 min.
The pellets were resuspended in 500 μL of commercial pyocyanin
solutions in LB (diluted 10× in water). The concentration of
pyocyanin varied from 0.5 to 50 μM. SERS spectra of liquid samples
were collected using a Renishaw macrosampler accessory, using a 785
nm laser line, 15× objective, 53.1 mW maximum power, and an acquisition
time of 10 s. The detection and quantification of secreted pyocyanin
were done similarly resuspending the pellets in 500 μL of bacteria-free
supernatants obtained from cultures of P. aeruginosa at different growth times (previously diluted 10× in water
and centrifuged). After 30 s of sonication, the samples were analyzed
by SERS.SERS spectra of Au@Ag@mSiO2 nanorattle-doped LB-agar substrates adjusted at different pH values
were performed using laser excitation of 785 nm, 10× objective,
8.22 mW maximum power, 10 s acquisition time, and 3 accumulations.
Sixteen spectra were randomly recorded in an area of 16 mm2. SERS mapping on Au@Ag@mSiO2 nanorattle-doped LB-agar
substrates during bacterial growth was performed using laser excitation
of 785 nm, 10× objective, 8.22 mW maximum power, 1 s acquisition
time, and 10 accumulations. SERS images were obtained using a point-mapping
method at the selected area (1.8 mm2), in which each SERS
spectrum is measured every 150 μm. All data were processed using
WiRE software v 4.3 (Renishaw, U.K.).
Authors: Birte Hollmann; Mark Perkins; Veeren M Chauhan; Jonathan W Aylott; Kim R Hardie Journal: NPJ Biofilms Microbiomes Date: 2021-06-17 Impact factor: 7.290
Authors: Gustavo Bodelón; Verónica Montes-García; Vanesa López-Puente; Eric H Hill; Cyrille Hamon; Marta N Sanz-Ortiz; Sergio Rodal-Cedeira; Celina Costas; Sirin Celiksoy; Ignacio Pérez-Juste; Leonardo Scarabelli; Andrea La Porta; Jorge Pérez-Juste; Isabel Pastoriza-Santos; Luis M Liz-Marzán Journal: Nat Mater Date: 2016-08-08 Impact factor: 43.841