Stan B J Willems1,2,3, Anton Bunschoten1,2, R Martijn Wagterveld3, Fijs W B van Leeuwen1,2, Aldrik H Velders1,2. 1. Laboratory of BioNanoTechnology , Wageningen University and Research , Axis, Bornse Weilanden 9 , 6708 WG Wageningen , The Netherlands. 2. Interventional Molecular Imaging Laboratory, Department of Radiology , Leiden University Medical Center , Albinusdreef 2 , 2333 ZA Leiden , The Netherlands. 3. Wetsus, European Centre of Excellence for Sustainable Water Technology , Oostergoweg 9 , 8911 MA Leeuwarden , The Netherlands.
Abstract
Species-specific isolation of microsized entities such as microplastics and resistant bacteria from waste streams is becoming a growing environmental challenge. By studying the on-flow immobilization of micron-sized polystyrene particles onto functionalized silica surfaces, we ascertain if supramolecular host-guest chemistry in aqueous solutions can provide an alternative technology for water purification. Polystyrene particles were modified with different degrees of adamantane (guest) molecules, and silica surfaces were patterned with β-cyclodextrin (β-CD, host) through microcontact printing (μCP). The latter was exposed to solutions of these particles flowing at different speeds, allowing us to study the effect of flow rate and multivalency on particle binding to the surface. The obtained binding profile was correlated with Comsol simulations. We also observed that particle binding is directly aligned with particle's ability to form host-guest interactions with the β-CD-patterned surface, as particle binding to the functionalized glass surface increased with higher adamantane load on the polystyrene particle surface. Because of the noncovalent character of these interactions, immobilization is reversible and modified β-CD surfaces can be recycled, which provides a positive outlook for their incorporation in water purification systems.
Species-specific isolation of microsized entities such as microplastics and resistant bacteria from waste streams is becoming a growing environmental challenge. By studying the on-flow immobilization of micron-sized polystyrene particles onto functionalized silica surfaces, we ascertain if supramolecular host-guest chemistry in aqueous solutions can provide an alternative technology for water purification. Polystyrene particles were modified with different degrees of adamantane (guest) molecules, and silica surfaces were patterned with β-cyclodextrin (β-CD, host) through microcontact printing (μCP). The latter was exposed to solutions of these particles flowing at different speeds, allowing us to study the effect of flow rate and multivalency on particle binding to the surface. The obtained binding profile was correlated with Comsol simulations. We also observed that particle binding is directly aligned with particle's ability to form host-guest interactions with the β-CD-patterned surface, as particle binding to the functionalized glass surface increased with higher adamantane load on the polystyrene particle surface. Because of the noncovalent character of these interactions, immobilization is reversible and modified β-CD surfaces can be recycled, which provides a positive outlook for their incorporation in water purification systems.
Entities:
Keywords:
flow cell; microcontact printing; microparticles; supramolecular chemistry; water purification
Studying the interactions of microparticles with chemically modified
surfaces is an important step in the development of cell-targeting
platforms.[1,2] Immobilization of cells, for instance, bacteria,
to monolayers on surfaces provides an interesting field of research,
especially toward medical or water treatment applications.[3−6] However, within complex biological systems, such as bacterial cells,
it is difficult to investigate specific surface adhesion interactions
of microsized entities with functionalized surfaces. Importantly,
the feasibility of particle adhesion interactions with respect to
different length scales being studied, that is, between microparticles
and molecules, should be confirmed using a more controllable model
system. Therefore, the use of model microparticles such as polystyrene
(PS) particles, which have the same size as most bacteria, is a versatile
and valuable tool for investigating adhesion onto chemically functionalized
surfaces.In nature, the binding mechanisms of microsized entities
such as
cells are governed by numerous amounts of interactions. Among these
interactions, hydrophobicity plays a significant role in the attachment
or detachment of cells to surfaces.[7] Therefore,
Whitesides et al. have carried out protein and cell adhesion studies
by using monolayers of alkanethiolates or alkylsilanes on gold or
silicon surfaces in order to mimic cell-binding mechanisms within
nature.[8−11] Patterning of the surfaces through a soft lithographic technique,
such as microcontact printing (μCP),[12,13] allowed for spatial control of cell adhesion, which improved confirmation
of binding during analysis. In order to acquire more specificity within
cell adhesion studies, different targeting agents for bacteria were
investigated by Sankaran et al., who adhered bacteria to surfaces
via an azobenzene–mannose linker and a transmembrane protein
containing tryptophan and phenylalanine on cucurbit[8]uril layers.[8]uril-Mediated Adhesion of
Bacteria on Supported Lipid Bilayers. Small. 2015 ">14,15] Moreover, Di Iorio et al. studied the binding kinetics of virus
mimics to sialic acid residues via weak multivalent interactions in
order to predict the number of interactions involved in binding.[16] Based on these advances, the implementation
and investigation of supramolecular and multivalent interactions for
high-affinity, noncovalent, and reversible binding is an important
aspect for understanding cell immobilization. We here exploit this
type of binding as an outlook toward water treatment applications,
as it is desirable to capture cells rapidly and subsequently release
immobilized cells for reusability of surfaces.For fabrication
of reusable surfaces, we selected the noncovalent
binding of adamantane (Ad) to β-cyclodextrin (β-CD). Cyclodextrins
are cyclic carbohydrate molecules consisting of 1,4-α-d-glucopyranosides bound in a cone shape[17] and are used primarily in food, pharmaceutical, and drug-delivery
applications.[18,19] Hydrophobic molecules can form
reversible inclusion complexes through hydrophobic and van der Waals
interactions (host–guest chemistry) with the cyclodextrin cavity.
Tethering of β-CD on silicon dioxide surfaces,[20] known as the molecular printboard,[21] has been carried out by Reinhoudt and co-workers. This led to binding
control and characterizing binding strength of functionalized dendrimers,
nanoparticles, and fluorescent guest molecules with cyclodextrin inside
their hydrophobic cavity. In later work by Gonzalez-Campo et al.,
patterns of β-CD were created on glass surfaces through reactive
μCP, showcasing the possibility of fluorescent guest adsorption
from the solution to β-CD patterns or orthogonal supramolecular
printing of fluorescent guests.[22] The fluorescent
guest molecules in these cases contain two Ad moieties, which have
a high affinity for the β-CD cavity in water.[23] Furthermore, the reversibility and reusability of this
system has been tested by forming multivalent networks of β-CD-modified
gold nanoparticles with diferrocene-modified peptides, which functioned
as an ultrasensitive enzyme sensor.[24] In
order to test the immobilization via host–guest interactions
with larger constructs than molecules, silica nanoparticles and quantum
dots have also been immobilized on β-CD surfaces using an intermediary
Ad-functionalized dendrimer as “glue”.[25,26] The high binding affinity of multivalent host–guest interactions
has also been used for the adhesion of macroscopic acrylamide gels.[27] Based on these examples, the versatility of
host–guest interactions mediated by β-CD provides a reliable
tool for scaling up from nanoparticles to specific and reversible
immobilization of microparticles.To study the supramolecular
adhesion of microparticles, we functionalized
PS particles with different amounts of Ad on their surface, patterned
glass surfaces with β-CD, and subsequently applied a flow of
functionalized particles over the modified glass surface (Figure a). PEG backfilling
is included as an antifouling layer between β-CD patterns. The
functionalized glass slides were placed in a holder which was connected
to a syringe pump for controlling the flow rate of PS particle solutions
over the glass slides. Host–guest interactions between β-CD
and Ad allow for the capture of the functionalized PS particles on
the glass surface, which can then be analyzed via fluorescence microscopy. Figure b shows how the flow
cell holder setup is directly incorporated on the microscope to carry
out various flow experiments for characterizing binding of PS particles
to the β-CD-functionalized glass slide. Results regarding the
feasibility of this approach can also be used as a proof-of-concept
for the application in immobilizing similar-sized cells such as bacteria.
Figure 1
(a) Scheme
showing μCP of β-CD on the glass surface
and backfilling with poly(ethylene glycol) (PEG) and the principle
of binding: combined addition of nonfunctionalized PS particles with
Cyanine 3 (Cy3) fluorescent label (PS-Cy3, negative control) and Ad-functionalized
PS particles with Cyanine 5.5 (Cy5.5) fluorescent label (PS-Cy5.5-Ad)
to patterned β-CD surfaces. (b) Flow cell holder setup on a
fluorescence microscope containing a functionalized glass surface
to perform different types of flow experiments.
(a) Scheme
showing μCP of β-CD on the glass surface
and backfilling with poly(ethylene glycol) (PEG) and the principle
of binding: combined addition of nonfunctionalized PS particles with
Cyanine 3 (Cy3) fluorescent label (PS-Cy3, negative control) and Ad-functionalized
PS particles with Cyanine 5.5 (Cy5.5) fluorescent label (PS-Cy5.5-Ad)
to patterned β-CD surfaces. (b) Flow cell holder setup on a
fluorescence microscope containing a functionalized glass surface
to perform different types of flow experiments.
Experimental Section
Synthesis and Functionalization of Fluorescent
PS Particles
PS particles (10 wt %, ∼1 μm) were
synthesized following the protocol from Appel et al. using the reaction
mixture “pSIA25”.[28] Then,
125 g of deionized (DI) water, 25 g of styrene, 0.5 g of itaconic
acid, and 0.01 g of the fluorescent dye Cy3 or Cy5.5 (used for staining
the core of resulting PS particles, as shown in Figure S1) were taken in a one-neck round-bottom flask. The
flask was sealed with a rubber septum, and the reaction mixture was
flushed with nitrogen for 15 min, followed by heating at 85 °C
and stirring at 500 rpm for 15 min. A 0.1 M solution of 4,4′-azobis(4-cyanovaleric
acid) was prepared in 0.2 M NaOH, and 8.92 mL (0.25 g) of this solution
was injected to the reaction mixture to initiate colloid synthesis.
The reaction was allowed to proceed for at least 12 h at 85 °C
and stirring at 500 rpm. The following day, the reaction mixture was
filtered, spun down through centrifugation at 3260g for 30 min, and then washed three times with DIwater through centrifugation
at 3260g for 30 min per washing step. The concentration
in wt % was determined through freeze-drying PS particles and then
measuring the mass of the lyophilized particles. A 5 mL solution of
0.5% wt of PS-Cy5.5 particles in 10 mM 2-(N-morpholino)ethanesulfonic
acid buffer, pH 5.0, was modified with 0.53, 1.33, and 2.67 μmol
of 1-adamantylamine hydrochloride using 0.32 mmol 1-ethyl-3-(-3-dimethylaminopropyl)carbodiimide
hydrochloride (EDC), according to the covalent coupling protocol from
Bangs Laboratories, Inc.[29] After overnight
EDC coupling, the dispersion of PS particles was spun down in a centrifuge
at 3260g (30 min) and subsequently washed three times
with DIwater also by centrifugation at 3260g (30
min per washing step) in order to remove nonreacted 1-adamantylamine.
Dynamic Light Scattering (DLS) Measurements
Dispersions of PS particle samples were diluted to an appropriate
concentration with DIwater and then analyzed on a Malvern Zetasizer
Nano S using the size intensity values. The samples were measured
three times with 10 runs per measurement at 25 °C. The size of
all particles was determined to be ca. 1 μm (Figure S2).
Conductometric Titration
As-synthesized
fluorescent PS-Cy5.5 particles were diluted 40× in 20 mL of DIwater. The pH was adjusted to 10 by using 10 mM NaOH to deprotonate
all the carboxyl groups on the PS particle surface. The conductivity
of the dispersion of PS particles was then measured upon addition
of 2 mM HCl in 40 μL increments until ca. pH 4.5 was reached.
The data were plotted as volume 2 mM HCl added versus conductivity
of the PS solution. From this graph, the total amount of CO2H groups on the PS particle surface could be determined.[30]
1H NMR Spectroscopy
The
supernatant of PS particles after EDC coupling with 1-adamantylamine
hydrochloride was collected and concentrated by rotary evaporation.
The resulting product was resuspended in 1 mL of deuterated water
(D2O) with 1 mM trimethylsilylpropionic acid (TMSP) as
the internal standard. A Bruker 500 MHz NMR system was used for obtaining
the 1H NMR spectra. The characteristic Ad peaks at 1.6
ppm in supernatant samples were integrated to the TMSP peak at 0 ppm
to calculate the concentration of unreacted Ad left in each sample.
Ad left within the dispersion of PS particles could then be determined
by the difference between the Ad added to the reaction mixture compared
to the unreacted Ad left in the supernatant.
Glass
Surface Functionalization
Isothiocyanate
monolayers on glass were prepared as described by Onclin et al.,[20] and the glass slides were cleaned and oxidized
with piranha solution (H2SO4 (95–98%)/H2O2 (35%), 3:1 v/v; Warning! Piranha solutions
must be handled with caution as they may unexpectedly detonate) for 45 min, rinsed with large amounts of DIwater, and dried under
a N2 atmosphere. The glass slides were placed in a high
vacuum preheated desiccator together with a glass vial containing
1 mL of 3-aminopropyltriethoxysilane (APTES, 99%) and then in an oven
at 70 °C overnight. Following amine monolayer formation, the
glass slides were removed from the desiccator and rinsed with toluene
and dichloromethane. The glass slides were then cured for at least
1 h in the oven at 70 °C. Next, the glass slides were immersed
in 0.1 M 1,4-phenylene diisothiocyanate (PDITC) in anhydrous toluene
for 2 h under an argon atmosphere to yield isothiocyanate-bearing
layers. Following immersion, the surfaces were rinsed with toluene
and dichloromethane and used immediately for μCP. Stamps were
made by using a technique reported by Whitesides.[10] Then, the stamps were prepared by casting a 10:1 (w/w)
mixture of poly(dimethylsiloxane) (PDMS) and a curing agent (Sylgard
184, Dow Corning) onto a silicon master to yield PDMS stamps with
150 μm broad line patterns and 50 μm broad spacing between
the lines. After overnight curing at 70 °C, the PDMS stamps were
cut out, oxidized by high-energy air plasma for 1 min, and incubated
in 0.72 mM heptakis(6-amino-6-deoxy)-β-CD heptahydrochloride
aqueous solution, pH 8.0, for 2 h. Before printing, excess solution
was dried off from the stamp surfaces using a stream of nitrogen.
The PDMS stamps were then brought into conformal contact with the
freshly prepared isothiocyanate-functionalized glass surfaces for
30 min. After carefully removing the stamps, the printed glass substrates
were rinsed thoroughly with DIwater. The glass substrates were then
incubated overnight in 1 mM methoxy PEGamine (PEG-NH2, Mw 2000 Da, Iris Biotech GmbH) aqueous backfilling
solution, pH 8.0, to react with unreacted isothiocyanates. Before
use, the glass substrates were rinsed with DIwater. When not used
within a day, substrates were stored in the backfilling solution at
4 °C.
Validation of β-CD
Patterns
The β-CD-printed glass substrates were incubated
for 15 min
on a droplet of 0.28 μM Cy5.5 dye solution in phosphate-buffered
saline (PBS), functionalized with two adamantyl moieties (Cy5-Ad2,[31] structures shown in Figure S1). After removal of the glass substrates
from the solution, they were rinsed with DIwater and dried with nitrogen.
The substrates were then analyzed by fluorescence microscopy.
Flow Experiments
An equimolar mixture
of PS-Cy3 and PS-Cy5.5-Ad at pH ≈ 10 was made to flow through
a resealable flow cell holder (fluidic connect PRO Resealable, Micronit;
for dimensions see Figure S3a + b) containing
a β-CD-printed glass surface (4515 extended resealable flow
cells, Micronit) using a syringe pump. The pH of the PS particles
was increased to 10 using 0.1 M NaOH to ensure that unreacted amine
groups of heptakis(6-amino-6-deoxy)-β-CD on the glass surface
were not protonated and therefore remain uncharged. Flow rates and
pumping times of 0.125 (40 h), 0.25 (20 h), 1.25 (4 h), 2.5 (2 h),
5 (1 h), 10 (30 min), 100 (3 min), and 200 (1.5 min) μL/min
were used to pump the particle solution over the glass surfaces. The
pumping time, listed in brackets after the respective flow rate, was
adjusted for different flow rates to keep the same total amount of
PS particles flowing over the surface. The flow cell holder was placed
directly on the stage of a Leica DMi8 epi-fluorescence microscope
to allow imaging before, during, and after flow. After flow incubation,
the pump was switched off and the inlet tubing was removed, causing
the solution to flow out of the resealable flow cell through the capillary
effect.
Calculating Particle Density and Binding Specificity
of Particles
The particle density on β-CD patterns
was determined through analysis of microscope images after flow experiments.
For acquiring an average particle density, all individual experiments
were carried out three times and per glass slide the start, middle,
and the end of the flow path were analyzed using ImageJ software (9
images in total). The pixels related to nonaggregated particles were
initially segmented out of the image using the “Analyze particles”
function. Subsequently, the average pixel size for one particle was
determined. With the “Measure” function, the pixels
were counted over the desired line patterns (on β-CD patterns
or PEG backfilling), which were then converted into amounts of particles
based on the determined average pixel size for one particle. The particle
density over 100 μm2 was subsequently calculated
based on the total surface area of desired line patterns (β-CD
or PEG patterns) per image. The binding specificity of particles for
β-CD-printed patterns was then calculated as a percentage with
the following formulaHere, η (%) is the binding specificity,
σp (μm–2) is the particle
density on the β-CD patterns, and σn (μm–2) is the particle density on the PEG spacing. Throughout
the results and discussion, the terms “specificity”
and “selectivity” will be used frequently. Specificity
is a comparison between binding of PS-Cy5.5-Ad to either β-CD
or PEG while selectivity is a comparison between PS-Cy5.5-Ad or PS-Cy3
binding to β-CD.
Comsol Simulations
For simulating
the flow experiments, Comsol Multiphysics 5.4 with the Particle Tracing
Module was used. A 2D design of the microchannel was made (20 ×
0.3 mm, similar to the extended channel part of the Micronit resealable
flow cell) with an inlet on the left, outlet on the right, and stick
conditions for the top and the bottom channel wall (Figure S3c). For the simulations, particles of 1 μm
were chosen and the following conditions were applied: gravity, Brownian
motion, and creeping/laminar flow conditions. To simulate the different
flow rates used, the average flow velocity and particle release times
were varied between 0.0625 and 200 μL/min (shown in Table ). The particle addition
time entails the specific time points at which particles were infused
into the designed channel and are given as the start time (in all
cases at time 0 s), the interval time between the start and the end
time (i.e., if 200 s, every 200 s, 40 particles are added), and the
end time of the simulation for which no particles are added.
Table 1
Table Showing Conversion of Flow Rate
to Average Flow Velocity and the Particle Addition Times for Different
Flow velocitiesa
flow rate (μL min–1)
average flow
velocity within the flow channel (m s–1)
particle
addition times (start, interval, end) (s)
0.0625
2.14 × 10–7
0, 8000, 288 000
0.125
5.35 × 10–7
0, 4000, 144 000
0.25
1.07 × 10–6
0, 2000, 72 000
1.25
5.35 × 10–6
0, 400, 14 400
2.5
1.07 × 10–5
0, 200, 7200
5
2.14 × 10–5
0, 100, 3600
10
4.27 × 10–5
0, 50, 1800
100
4.27 × 10–4
0, 5, 180
200
8.54 × 10–4
0, 2.5, 90
40 particles are
added at time 0
s and at the given intervals with a total of 1480 particles for each
simulation.
40 particles are
added at time 0
s and at the given intervals with a total of 1480 particles for each
simulation.
Results and Discussion
Patterned monolayers of β-CD
were fabricated on glass surfaces,
and Ad-functionalized fluorescent PS microparticles were synthesized
with different degrees of Ad-surface loading, ranging from 0.15 to
0.8 Ad mole fraction of the available CO2H groups on the
PS particle surface. Both the surface functionalization and synthesis
of modified particles were characterized. Then, the immobilization
of the particles on the glass surface in flow, via host–guest
interactions, was validated
through patterned binding of particles. For reference, a control PS
particle without Ad functionality was always included to check the
selectivity of the system. Various flow experiments were carried out
to further investigate this model system, namely, flow rate variation,
immobilization of PS particles with different Ad loading on the PS
surface, and reusability of the glass slides after removal of bound
PS particles.
Characterization
Fabrication
of β-CD Patterns through
μCP
Glass slides were first silanized with APTES and
then functionalized with 1,4-phenylene diisothiocyanate (PDITC) to
create a surface reactive toward amines. The patterning of isothiocyanate
glass slides with heptakis amino β-CD was achieved through μCP,[13] and the unreacted areas were filled with PEG-NH2 (the first step in Figure b). Patterning was performed using μCP functions
as an internal control to observe the specific assembly of molecules
or particles on the β-CD surface. According to the literature,[20,32] the presence of β-CD patterns on the surface can be validated
through the addition of diadamantane-functionalized fluorophores.
We used a Cy5.5 (Cy5-Ad2) functionalized with two Ad molecules
for detecting β-CD patterns on the surface, which yielded a
bright fluorescence signal over printed lines of β-CD (Figure S4). Rinsing with DIwater did not remove
bound Cy5-Ad2, which indicates the presence of a high affinity
interaction between Cy5-Ad2 and β-CD.
PS Particle Characterization and Functionalization
with Ad Amine
PS particles covered with carboxyl groups were
synthesized according to the protocol demonstrated by Appel et al.,[28] with either Cy3 or Cy5.5 (Figure S1) dye used to stain the PS cores. This allowed for
facile analysis and discrimination using fluorescence imaging. After
particle synthesis, the concentration of PS particles was determined:
a known volume of the particles was lyophilized and the resulting
particles were weighed to determine the mass concentration (Table S1). From this value, we calculated the
as-synthesized particles to have a concentration of 1.82 × 1011 PS particles/mL (eq S1). The
amount of CO2H groups per PS particle was then determined
at 2.4 × 107 through reverse conductometric titration
(Figure S5).[30]PS-Cy5.5 particles were modified with 0.53, 1.33, and 2.67
μmol of Adamine via an EDC coupling reaction. Ad surface loading
on PS particles was determined through 1H NMR spectroscopy
of the PS particle supernatant (Figures S6 and S7), and the PS particle samples were named after their degree
of surface functionalization: PS-Cy5.5-0.15Ad, PS-Cy5.5-0.3Ad, and
PS-Cy5.5-0.8Ad (Table ). However, for PS-Cy5.5-0.8Ad, surprisingly high PS surface loading
of six Ad molecules per nm2 was determined, which is unlikely
to reflect six Ad moieties in a densely packed 2D-surface configuration
because the effective size of Ad is ca. 0.41 nm2 (based
on the reported Ad radius of 0.36 nm).[33] This can be explained by the surface roughness of PS particles which
increases the total surface area compared to that of the model of
a smooth sphere used for carrying out all the calculations.[34] The high values for Ad surface loading can also
be explained by nonspecific uptake of Adamine in the dispersion of
PS particles, which was determined by omitting EDC during coupling
(Table S2). Nevertheless, the Ad loading
determined through NMR analysis shows significant differences between
different concentrations of Ad used for modifying PS particles and
should therefore be seen as relative loading rather than as an absolute
value.
Table 2
Determining the Degree of Surface
Functionalization After NMR Analysis of the Supernatant of Different
PS-Cy5.5-Ad Samples
Flow Rate Variation
The immobilization
of the micrometer-sized particles was tested under different flow
conditions ranging from 0.125 to 200 μL/min. PS-Cy5.5-0.8Ad
particles (red) were successfully captured on β-CD lines as
observed in images i–iv of Figure a, confirming that microparticle immobilization
is feasible under flow conditions. Selectivity of Ad binding was shown
by mixing Cy3-stained PS particles (PS-Cy3, yellow) without Ad [Figure a (v–viii)].
A reference surface was created by using μCP glycine, instead
of β-CD, which confirmed that the immobilization of Ad-functionalized
particles on β-CD-functionalized surfaces was the result of
specific host–guest interactions (Figure S8; 5 μL/min for 1 h).
Figure 2
(a) Fluorescence images of patterned β-CD
glass surfaces
after addition of an equimolar mix of fluorescent PS particles PS-Cy5.5-Ad
(i–iv) and PS-Cy3 (v–viii). The patterns are oriented
perpendicular to the flow direction. From the left to right, a selection
of flow rates are shown: 0.125 (i,v), 2.5 (ii,vi), 100 (iii,vii),
and 200 (iv,viii) μL/min. All flow rate experiments are shown
in Figure S9. The top images (red) are
captured with a Cy5 filter and the bottom images (yellow) with a RHOD
filter. Images of different filters and the same flow rate are captured
at the same location to compare the effect of aspecific interactions.
Scale bars are 100 μm. (b) Graph showing the PS-Cy5.5-Ad particle
density on β-CD patterns vs all flow rates used. (c) Graph showing
the binding specificity for these respective patterns vs the flow
rate.
(a) Fluorescence images of patterned β-CD
glass surfaces
after addition of an equimolar mix of fluorescent PS particles PS-Cy5.5-Ad
(i–iv) and PS-Cy3 (v–viii). The patterns are oriented
perpendicular to the flow direction. From the left to right, a selection
of flow rates are shown: 0.125 (i,v), 2.5 (ii,vi), 100 (iii,vii),
and 200 (iv,viii) μL/min. All flow rate experiments are shown
in Figure S9. The top images (red) are
captured with a Cy5 filter and the bottom images (yellow) with a RHOD
filter. Images of different filters and the same flow rate are captured
at the same location to compare the effect of aspecific interactions.
Scale bars are 100 μm. (b) Graph showing the PS-Cy5.5-Ad particle
density on β-CD patterns vs all flow rates used. (c) Graph showing
the binding specificity for these respective patterns vs the flow
rate.Rinsing of the functionalized
glass surfaces with DIwater did
not specifically remove immobilized particles, indicating strong binding
interactions. Patterned binding of Ad-modified PS particles to the
β-CD-modified glass surface confirms that the binding affinity
is high enough to overcome the drag forces acting on the particles
(see eq S1 and Table S3); the drag force acting on a microparticle for all flow
rates is approximately 105 times lower than the binding
strength of an individual Ad-β-CD host–guest complex
(10–11 N).[35] However,
this value for Ad-β-CD binding strength is based on ideal conditions,
not considering kinetic and concentration effects which are also important
for binding affinity and particle immobilization. Therefore, it is
still necessary to have multiple Ad-β-CD bonds for keeping particles
immobilized on the surfaces during flow.The influence of the
flow rate on particle capturing was studied
by varying the flow rate from 0.125 to 200 μL/min. Subsequently,
the different flow rates were compared both on the density of captured
particles and on specificity (Figures and S9). The values for
particle binding density and specificity of PS-Cy5.5-0.8Ad particles
for the printed β-CD lines on the glass surface were calculated
and plotted in Figure b,c. Looking at the particle binding density graph in Figure b and microscope images [Figure a (i–iv)],
increasing the flow rate from 2.5 μL/min until 200 μL/min
resulted in a decrease of immobilized particles from 3 to 0.5 PS-Cy5.5-0.8Ad
particles/102 μm on β-CD. This finding is in
line with the literature as particle deposition increases with lower
flow rates.[36]Another important factor
for assessing the immobilization of particles
to modified surfaces is the particle binding specificity. The particle
binding specificity, in this case, measures how well PS-Cy5.5-0.8Ad
particles bind specifically to the patterns of β-CD compared
to the aspecific binding to PEG backfilling and is plotted in (Figure c). From a flow rate
of 2.5 μL/min and above, samples have a binding specificity
of ≥80% for β-CD lines and with flow rates from 5 μL/min
and above, samples have the highest specificities above 90%. Using
a flow rate of 0.125 and 0.25 μL/min resulted in a lower binding
specificity most significantly compared to the other flow rates, which
is mostly because of the lower particle binding density. The amount
of particles captured on the functionalized surfaces at flow rates
from 10 μL/min and above is considerably lower than that with
2.5 and 5 μL/min flow rates (Figure b). Thus, a flow rate of 5 μL/min for
specific immobilization of these particles is most desirable, considering
the particle binding density and specificity.Surprisingly,
when we carried out particle-capturing experiments
at extremely low flow rates of 0.125 and 0.25 μL/min, almost
no particles were bound to the printed β-CD surface. Comsol
particle flow simulations were carried out to investigate the change
in particle binding to the β-CD-modified surface with flow rates.
These calculations were made using a 2D flow cell geometry of 20 mm
in length and 0.3 mm in height that represented the conditions in
the Micronit flow channel, 1 μm sized particles, similar flow
rates, and stick conditions for both the bottom and top channel walls
(Figure S3c). After carrying out simulations
at different flow rates, particles were counted over the center of
the bottom channel wall from 5 to 15 mm for each simulation, which
is approximately where the glass surface in the practical experiments
was patterned with β-CD through μCP. Indeed, a similar
trend in particle binding density to the practical flow experiments
was noticed in the Comsol particle tracing data, when we focused on
this area (Figure a–i), marked with a red line. It is also clear that the flow
profile of trajectory graphs (a–d) (0.0625–1.25 μL/min
flow rate) is mostly based on diffusion and settling of particles,
while in trajectory graphs (e,f) (2.5–200 μL/min flow
rate), a laminar flow profile is observed (Figure ). In trajectory graphs (a) and (b) from Figure , the particles stuck
to the marked area on the bottom channel wall decreases dramatically
because particles settle before they reach the designated area. The
trend seen in the graph in Figure j correlates well with the experimental findings for
the practical experiments in Figure . Therefore, a decrease is observed in particle binding
density because of the particle settling before reaching the functionalized
area with β-CD patterns in the middle of the channel. This was
confirmed by carrying out a flow experiment at 0.125 μL/min
with only the PS-Cy3 particle on PEG-functionalized glass surfaces,
which shows that most particles are situated in the inlet side of
the flow channel after flow incubation (Figure S10).
Figure 3
Comsol particle tracing data of flow rates (a) 0.0625,
(b) 0.125,
(c) 0.25, (d) 1.25, (e) 2.5, (f) 5, (g) 10, (h) 100, and (i) 200 μL/min.
The red line marks the area that was focused on for particle counting.
The scale on the right side of each image for (a–i) shows the
particle velocity in m/s. The particle size is scaled up for the viewing
purpose. Both the bottom and top channel walls have stick conditions.
(j) The graph showing the amount of particles stuck on the bottom
channel wall from Comsol simulation data vs flow rate used. The total
amount of particles was 1480 in each simulation.
Comsol particle tracing data of flow rates (a) 0.0625,
(b) 0.125,
(c) 0.25, (d) 1.25, (e) 2.5, (f) 5, (g) 10, (h) 100, and (i) 200 μL/min.
The red line marks the area that was focused on for particle counting.
The scale on the right side of each image for (a–i) shows the
particle velocity in m/s. The particle size is scaled up for the viewing
purpose. Both the bottom and top channel walls have stick conditions.
(j) The graph showing the amount of particles stuck on the bottom
channel wall from Comsol simulation data vs flow rate used. The total
amount of particles was 1480 in each simulation.Adversely, when increasing the flow rate within the laminar flow
regime (between flow rates of 2.5 and 200 μL/min), the particle
binding density also decreases within the practical experiments and
simulation because the effect of gravity and diffusion is low. The
effect of diffusion can be explained using the Péclet (Pe) number, which describes the effect of flow advection
compared to that of particle diffusion. As mentioned above, we assume
the laminar flow within the microfluidic channel at flow rates 2.5–200
μL/min, which means that the particle velocity decreases close
to the channel walls (eq S2, Table S4). When the advection, that is, flow
rate, increases and Pe numbers increase far above
1, particle diffusion can be seen as negligible. In Table S4, the Pe numbers were calculated
for the different flow velocities of the particles that are 1 μm
above the channel wall using eqs S3 and S4. For flow rates of 100 and 200 μL/min, the Pe numbers were considerably higher than 1, which explains the small
difference in particle binding density. This is caused by a limitation
in the amount of particles that can reach the bottom channel through
diffusion or settling, while at flow rates from 2.5 to 10 μL/min,
particle diffusion to the channel wall is possible from a larger distance
(Figures S11 and S12). Therefore, there
is a specific range of flow rates in which the increased effect of
diffusion combined with advection allows for more Ad-functionalized
PS particles to come in contact with the area patterned with β-CD
and thus be immobilized.For nonfunctionalized PS-Cy3 particles,
significantly lower binding,
ranging from 0.008 to 0.04 particles per 100 μm2 (for
flow rates 2.5–200 μL/min), was observed (Figure S13). The amount of PS-Cy3 particles,
however, increases when higher amounts PS-Cy5.5-Ad particles were
immobilized on the surface, which could be caused by aggregation of
PS-Cy3 particles with PS-Cy5.5-Ad particles. An experiment with only
PS-Cy3 particles carried out as a control at 5 μL/min flow showed
that almost no particles were bound to the glass surface (Figure S14).To study the effect of particle
settling on PS-Cy5.5-0.8Ad particle
binding to the functionalized surface, an upside down flow experiment
at 2.5 and 5 μL/min was carried out by turning the flow cell
holder upside down (Figure ). These flow rates were chosen because the transition to
laminar flow occurs at 2.5 and 5 μL/min, according to the particle
trajectories in Figure . As observed in the microscopic images (Figure a), PS particle binding to β-CD patterns
is still possible in upside down flow situations and was selective
for PS-Cy5.5-0.8Ad particles. Compared to the upright flow experiment
(Figure b), binding
to the surface was ∼six times lower for 2.5 μL/min at
0.4 particles per 100 μm2 and ∼three times
lower for 5 μL/min at 0.8 particles per 100 μm2 on β-CD patterns (Figure b). Therefore, particle settling has a significant
effect in improving the contact of the PS particles with the bottom
channel wall. Nevertheless, PS-Cy5.5-0.8Ad particle binding to β-CD
patterns is still feasible and specific through host–guest
interactions without the aid of particle settling (Figure c).
Figure 4
(a) Fluorescence microscope
images of equimolar ratios of PS-Cy5.5-0.8Ad
(i,ii) and PS-Cy3 particles (iii,iv) bound to β-CD-patterned
glass surfaces after upside down flow incubation at 2.5 μL/min
(i,iii) and 5 μL/min (ii,iv). The patterns are oriented perpendicular
to the flow direction. The top images are captured with a Cy5 filter
and the bottom images with a RHOD filter. Scale bars are 100 μm.
(b) Graph showing particle density vs flow rate for upside down flow
on β-CD patterns. (c) Graph showing binding specificity vs flow
rate for upside down flow on β-CD patterns.
(a) Fluorescence microscope
images of equimolar ratios of PS-Cy5.5-0.8Ad
(i,ii) and PS-Cy3 particles (iii,iv) bound to β-CD-patterned
glass surfaces after upside down flow incubation at 2.5 μL/min
(i,iii) and 5 μL/min (ii,iv). The patterns are oriented perpendicular
to the flow direction. The top images are captured with a Cy5 filter
and the bottom images with a RHOD filter. Scale bars are 100 μm.
(b) Graph showing particle density vs flow rate for upside down flow
on β-CD patterns. (c) Graph showing binding specificity vs flow
rate for upside down flow on β-CD patterns.
Ad Loading Effect on PS Particle Binding
The PS-Ad samples with different surface coverages of Ad were made
to flow over the β-CD glass surfaces and compared (Figure ). At a flow rate
of 5 μL/min, a clear increase in the particle density is observed
for PS particles with higher Ad surface coverage and 0.15 Ad-loaded
PS-Cy5.5 particles obtain a clear lower particle surface density (0.4
particles/100 μm2 β-CD) than 0.3 and 0.8 Ad-loaded
PS particles (1 and 2 particles/100 μm2, Figure a,b). An increase
in the negative control PS-Cy3 particle density on β-CD is also
seen with higher Ad loading of PS-Cy5.5-Ad (Figure S9). However, the PS-Cy3 particle density is still approximately
100 times lower than PS-Cy5.5-Ad density on cyclodextrin. PS-Cy5.5-Ad
particle binding was very specific in all cases for β-CD patterns.
Figure 5
(a) Fluorescence
microscope images of PS particles adhered to β-CD
lines with different Ad loading on PS-Cy5.5-Ad particles of 0.15,
0.3, and 0.8 at a flow rate of 5 μL/min. The patterns are oriented
perpendicular to the flow direction. The Cy5 filter (red) shows PS-Cy5.5-Ad
particles and the RHOD filter (yellow) shows PS-Cy3 particles. Scale
bar is 100 μm. (b) Graph showing particle density on β-CD
vs Ad loading on the PS-Cy5.5 particle surface. (c) Graph showing
binding specificity for β-CD patterns vs Ad loading on the PS-Cy5.5
particle surface.
(a) Fluorescence
microscope images of PS particles adhered to β-CD
lines with different Ad loading on PS-Cy5.5-Ad particles of 0.15,
0.3, and 0.8 at a flow rate of 5 μL/min. The patterns are oriented
perpendicular to the flow direction. The Cy5 filter (red) shows PS-Cy5.5-Ad
particles and the RHOD filter (yellow) shows PS-Cy3 particles. Scale
bar is 100 μm. (b) Graph showing particle density on β-CD
vs Ad loading on the PS-Cy5.5 particle surface. (c) Graph showing
binding specificity for β-CD patterns vs Ad loading on the PS-Cy5.5
particle surface.To shed light on the
amount of Ad and β-CD pairs that are
interacting to immobilize one Ad-functionalized PS particle, the accessible
contact area of PS and β-CD was calculated to be ca. 2000 nm2, when a PS particle touches the glass surface (based on an
Ad-NH2 linker length of 0.6 nm). Assuming the Ad loading
previously determined, the amount of Ad moieties present on the PS
particle surface within the 2000 nm2 contact area is approximately
2000 for PS-Cy5.5-0.15Ad, 4000 for PS-Cy5.5-0.3Ad, and 12 000
for PS-Cy5.5-0.8Ad. When assuming a β-CD surface density of
6 × 10–11 mol/cm2 on glass from
the literature,[25] ca. 800 β-CD units
are present in 2000 nm2 on glass. Interestingly, β-CD-Ad
couples are therefore limited by the number of β-CD molecules
rather than that of Ad. However, as mentioned before, in the characterization
of the PS particles, actual Ad loading on the PS surface is most likely
lower than the amounts calculated via NMR analysis. More importantly,
the surface roughness of PS particles and glass can also reduce the
amount of accessible Ad and β-CD molecules for host–guest
interactions. Furthermore, the binding affinity is also governed by
concentration gradients within a solution and kinetic effects, which
increases the complexity in determining the amount of interactions
required for microparticle immobilization to a surface. Therefore,
we argue that these experimental findings and analyses show that determining
the amount of interactions required for microparticle immobilization
is not straightforward and requires further research. Nevertheless,
these results do show that changing the relative amount of targeting
molecules on the microparticle surface, thereby tuning the multivalency,
plays an important role for increasing microparticle immobilization
on functionalized surfaces.
Reversibility and Reusability
of β-CD
Glass Surfaces
The reversible nature of particle immobilization
mediated by host–guest interactions was tested by removal of
particles and re-addition of “new” particles (Figure ). The addition of
the PS particle mix (PS-Cy5.5-0.8Ad and PS-Cy3) at 5 μL/min
was carried out over the β-CD surfaces as before, and the surface
was analyzed on the microscope. Rinsing with EtOH was attempted to
diminish the hydrophobic interaction between β-CD and Ad.[37] In addition, rinsing with a concentrated solution
of β-CD was performed to compete in the host–guest interaction.[32] Unfortunately, both approaches did not result
in significant release of the multivalently bound microparticles.
Next, a more rigorous ultrasonic treatment in EtOH and subsequently
water was applied. It is observed in Figure a that complete removal of PS particles was
achieved and the glass surface is still functional for the subsequent
particle immobilization experiment. Quantitative analysis for two
particle immobilization experiments shows that two times less PS-Cy5.5-Ad
particles are immobilized the second time (Figure b). This could be due to loss of β-CD
functionality through ultrasonic treatment or because some EtOH is
still present on the glass substrate that can diminish binding affinity
of Ad for the β-CD cavity.
Figure 6
(a) Fluorescence microscope images of
PS particles adhered to β-CD
lines and subsequent removal and readdition of PS particles at a 5
μL/min flow rate. Cy5 channels (red) show PS-Cy5.5-Ad particles
and the RHOD channel (yellow) shows PS-Cy3 particles. (b) Particle
density on β-CD after multiple uses.
(a) Fluorescence microscope images of
PS particles adhered to β-CD
lines and subsequent removal and readdition of PS particles at a 5
μL/min flow rate. Cy5 channels (red) show PS-Cy5.5-Ad particles
and the RHOD channel (yellow) shows PS-Cy3 particles. (b) Particle
density on β-CD after multiple uses.
Conclusions
In summary, a chemically modified
glass platform has been developed
that can capture micrometer-sized particles on flow in a recyclable
manner. The capture of “large” particles, about 103 times larger than the host molecule β-CD, was possible
through multivalent host–guest interactions between Ad and
cyclodextrin. Immobilization of Ad-functionalized PS particles to
β-CD-modified platforms was flow rate-dependent, with an optimal
capturing density at 2.5–5 μL/min. Changing the degree
of Ad functionalization on the PS particles influenced the degree
of binding on the glass surfaces, underpinning the effect of multivalent
host–guest interactions on particle binding. The modified glass
platforms could also be recycled, highlighting the potential of using
such systems in water purification setups. The depicted results of
this model system show that host–guest interactions can bridge
the gap between the nano- and microscale and also give insight into
certain parameters and hurdles that are important to be taken into
account for approaching the application of bacterial cell targeting
in wastewater. Moreover, the experimental setup of this model system
can be easily used for immobilization tests with different types of
molecules or particles.
Authors: Roberto de la Rica; Raluca M Fratila; Anna Szarpak; Jurriaan Huskens; Aldrik H Velders Journal: Angew Chem Int Ed Engl Date: 2011-05-17 Impact factor: 15.336
Authors: A A Torkelson; A K da Silva; D C Love; J Y Kim; J P Alper; B Coox; J Dahm; P Kozodoy; R Maboudian; K L Nelson Journal: J Appl Microbiol Date: 2012-08-30 Impact factor: 3.772