Multidrug resistant bacterial infections threaten to become the number one cause of death by the year 2050. Development of antimicrobial dendritic polymers is considered promising as an alternative infection control strategy. For antimicrobial dendritic polymers to effectively kill bacteria residing in infectious biofilms, they have to penetrate and accumulate deep into biofilms. Biofilms are often recalcitrant to antimicrobial penetration and accumulation. Therefore, this work aims to determine the role of compact dendrons with different peripheral composition in their penetration into Pseudomonas aeruginosa biofilms. Red fluorescently labeled dendrons with pH-responsive NH3+ peripheral groups initially penetrated faster from a buffer suspension at pH 7.0 into the acidic environment of P. aeruginosa biofilms than dendrons with OH or COO- groups at their periphery. In addition, dendrons with NH3+ peripheral groups accumulated near the top of the biofilm due to electrostatic double-layer attraction with negatively charged biofilm components. However, accumulation of dendrons with OH and COO- peripheral groups was more evenly distributed across the depth of the biofilms than NH3+ composed dendrons and exceeded accumulation of NH3+ composed dendrons after 10 min of exposure. Unlike dendrons with NH3+ groups at their periphery, dendrons with OH or COO- peripheral groups, lacking strong electrostatic double-layer attraction with biofilm components, were largely washed-out during exposure to PBS without dendrons. Thus, penetration and accumulation of dendrons into biofilms is controlled by their peripheral composition through electrostatic double-layer interactions, which is an important finding for the further development of new antimicrobial or antimicrobial-carrying dendritic polymers.
Multidrug resistant bacterial infections threaten to become the number one cause of death by the year 2050. Development of antimicrobial dendritic polymers is considered promising as an alternative infection control strategy. For antimicrobial dendritic polymers to effectively kill bacteria residing in infectious biofilms, they have to penetrate and accumulate deep into biofilms. Biofilms are often recalcitrant to antimicrobial penetration and accumulation. Therefore, this work aims to determine the role of compact dendrons with different peripheral composition in their penetration into Pseudomonas aeruginosa biofilms. Red fluorescently labeled dendrons with pH-responsive NH3+ peripheral groups initially penetrated faster from a buffer suspension at pH 7.0 into the acidic environment of P. aeruginosa biofilms than dendrons with OH or COO- groups at their periphery. In addition, dendrons with NH3+ peripheral groups accumulated near the top of the biofilm due to electrostatic double-layer attraction with negatively charged biofilm components. However, accumulation of dendrons with OH and COO- peripheral groups was more evenly distributed across the depth of the biofilms than NH3+ composed dendrons and exceeded accumulation of NH3+ composed dendrons after 10 min of exposure. Unlike dendrons with NH3+ groups at their periphery, dendrons with OH or COO- peripheral groups, lacking strong electrostatic double-layer attraction with biofilm components, were largely washed-out during exposure to PBS without dendrons. Thus, penetration and accumulation of dendrons into biofilms is controlled by their peripheral composition through electrostatic double-layer interactions, which is an important finding for the further development of new antimicrobial or antimicrobial-carrying dendritic polymers.
Biofilms
are three-dimensional
microbial aggregates responsible for 60–80% of all microbial
infections.[1] In an infectious biofilm,
infecting organisms are protected by a matrix of self-produced extracellular
polymeric substances (EPS), impeding effective penetration of most
antimicrobials.[2] This protection mechanism
was already observed in 1684 by Antonie van Leeuwenhoek, describing
how the vinegar which he used to wash his teeth only killed those
bacteria which were on the outside of the scurf,[3] nowadays called “biofilm”. To date, with
the threat of antimicrobial-resistant bacterial infection becoming
the number one cause of death by the year 2050,[4] effective penetration of antimicrobials into biofilms is
still a major hurdle in the treatment of infectious biofilms.Dendritic polymers with dendrimers as the flagship are flawless
and symmetrically branched macromolecules with a treelike structure.[5] When composed of antimicrobial peptides,[6,7] such dendrimers are able to kill planktonic bacteria,[6] that is, suspended bacteria that are not in their
protected, adhering, biofilm-mode of growth. Also antimicrobial dendrimers
can prevent biofilm formation.[7] For the
treatment of existing infectious biofilms, dendrimers are under investigation
for use as an antimicrobial nanocarrier.[5] Vancomycin-tethered poly(amidoamine) dendrimers showed avid binding
to vancomycin-resistant Staphylococcus aureus surfaces.[8] However, it is unclear whether the peripheral
composition of dendritic nanocarriers stimulating avid binding to
biofilm inhabitants is favorable or not for their deep penetration
into an infectious biofilm. Dendrons are wedge-shaped structures that
are the major component of dendrimers.[9] These dendritic frameworks are inherently bifunctional containing
one chemically addressable group designated to the focal point and
a composition of multiple peripheral groups. Higher generation dendrons
are by definition dendrimers with an active core and therewith the
chemical composition of larger dendrons, similar to dendrimers, is
responsible for efficient penetration in infectious biofilms.Considering the importance of penetration and accumulation of antimicrobials
into an infectious biofilm and the promise of dendrimer-based antimicrobials
for infection control, this work aims to determine the role of dendron
peripheral composition in their penetration into Pseudomonasaeruginosa biofilms. P. aeruginosa causes
a range of infections across the human body[10] and is known to produce extensive amounts of EPS that can be especially
troublesome in cystic fibrosispatients.[2] Better understanding of the role of peripheral composition of dendrons
in their penetration and accumulation into biofilm will aid their
further development as an effective antimicrobial.To this end,
bifunctional dendrons were designed, consisting of
rhodamine B as a red-fluorescent marker, an unsymmetrical triethylene
glycol (TEG) linker, and three-generations (G3), multivalent 2,2-bis(hydroxymethyl)propionic
acid (bis-MPA) dendrons. Bis-MPA dendrons are biocompatible[11] and biodegradable[12] and can be synthesized with unprecedented structural control.[13] Three different dendrons with pH-responsive
peripheral composition were synthesized (see Figure a): rhodamine-TEG-G3-OH, rhodamine-TEG-G3-COO–, and rhodamine-TEG-G3-NH3+ (charges
indicated are as in the acidic environment inside a biofilm). Dendrons
were constructed using conventional divergent growth of bis-MPA.[14,15] Rhodamine B was covalently attached through fluoride-promoted esterification
(FPE) chemistry and the peripheral hydroxyls were activated yielding
the neutral dendritic scaffold, rhodamine-TEG-G3-OH. Esterification
of rhodamine-TEG-G3-OH yielded anionic rhodamine-TEG-G3-COO– and cationic rhodamine-TEG-G3-NH3+ (see Supporting Information for details).[14−16] Complete substitution and high structural purity were corroborated
using conventional characterization techniques for dendrimer chemistry,
that is, NMR (Figure b) and MALDI-TOF-MS (Figure c).
Figure 1
(a) Bifunctional dendrons displaying different pH-responsive peripheral
composition, consisting of fluorescent marker (rhodamine B), an unsymmetrical
TEG linker, and three generations (G3), multivalent bis-MPA dendrons.
Charges indicated are as in the acidic environment of a biofilm. (b) 1H NMR of TEG-G3-OH, rhodamine-TEG-G3-COO–, and rhodamine-TEG-G3-NH3+. 1H
NMR analyses were performed as described previously,[15] using a Brüker AM NMR (Brüker Biospin, Rheinstetten,
Germany). (c) MALDI-TOF-MS of rhodamine-TEG-G3-OH, rhodamine-TEG-G3-COO–, and rhodamine-TEG-G3-NH3+.
MALDI-TOF spectra were obtained as described previously,[15] using a Brüker UltraFlex MALDI-TOF MS
with SCOUT-MTP Ion Source (Brüker Daltonics, Bremen, Germany),
a gridless ion source with the nitrogen-laser (337 nm) and a reflector.
.
(a) Bifunctional dendrons displaying different pH-responsive peripheral
composition, consisting of fluorescent marker (rhodamine B), an unsymmetrical
TEG linker, and three generations (G3), multivalent bis-MPA dendrons.
Charges indicated are as in the acidic environment of a biofilm. (b) 1H NMR of TEG-G3-OH, rhodamine-TEG-G3-COO–, and rhodamine-TEG-G3-NH3+. 1H
NMR analyses were performed as described previously,[15] using a Brüker AM NMR (Brüker Biospin, Rheinstetten,
Germany). (c) MALDI-TOF-MS of rhodamine-TEG-G3-OH, rhodamine-TEG-G3-COO–, and rhodamine-TEG-G3-NH3+.
MALDI-TOF spectra were obtained as described previously,[15] using a Brüker UltraFlex MALDI-TOF MS
with SCOUT-MTP Ion Source (Brüker Daltonics, Bremen, Germany),
a gridless ion source with the nitrogen-laser (337 nm) and a reflector.
.Next, P. aeruginosa ATCC 39324 biofilms were grown
in a constant depth film fermenter (CDFF)[17] to a thickness of 100 μm, as verified using optical coherence
tomography (OCT result: 96 ± 15 μm, averaged across all
biofilms employed in this study). Biofilms were exposed to red-fluorescently
labeled dendron suspensions for 0.1, 1, 10, or 100 min to study their
penetration. In addition, biofilms after 100 min of exposure to a
dendron suspension in phosphate buffered saline (PBS, pH 7.0) were
subsequently placed in PBS without dendrons for another 100 min to
monitor dendron wash-out. Note that in a separate experiment (data
not shown), it was established that dendrons did not inadvertently
release covalently coupled rhodamine in buffer, regardless of pH.
After penetration and/or wash-out, biofilms were immediately embedded
into Tissue-Tek O.C.T. compound and flash-frozen in liquid nitrogen
after which 10 μm sections were made perpendicular to the biofilm
surface using a cryotome (Leica CM3050 S, Leica Microsystems, Wetzlar,
Germany) for fluorescence microscopy. Figure a,b shows examples of cross-sectional images
of biofilms after exposure to the different dendron suspensions at
different time points. Rhodamine on its own fully penetrated in the
biofilms (see Figure S1). Because all dendrons
were synthesized to possess a single fluorescent rhodamine group,
dendron distribution across the depth of the biofilms could be derived
from the depth-dependent fluorescence intensity (Figure c,d) in the biofilm image,
using a standard curve prepared using suspensions with known dendron
concentrations (see Figure S2).
Figure 2
(a) Cross-sectional
images of P. aeruginosa biofilms
exposed to 0.2 μM dendron suspensions in PBS with different
peripheral composition for 0.1, 1, 10, or 100 min and after 100 min
wash-out in PBS (initial exposure time to dendron suspensions: 100
min). Identical alignment of the biofilms after embedding and cryo-sectioning
was impossible, hence each fluorescence image is complemented with
a light-microscopic image to visualize the entire biofilm (grasped
within two arrows in the second image from the left, top row). The
white scale bar represents 100 μm. (b) Enlarged overlayer of
fluorescence and light-micrographs of dendrons accumulated in a biofilm.
Scale bar represents 100 μm. (c) A custom LabVIEW script was
used to calculate the fluorescence intensity in a 10 × 0.645
μm (corresponding with one pixel) biofilm column as a function
of biofilm depth (see also Experimental Section). (d) Example of fluorescence intensity as a function of biofilm
depth, calculated as described in panel c, from which the depth-dependent
dendron concentration was derived, using a standard curve (Figure S2).
(a) Cross-sectional
images of P. aeruginosa biofilms
exposed to 0.2 μM dendron suspensions in PBS with different
peripheral composition for 0.1, 1, 10, or 100 min and after 100 min
wash-out in PBS (initial exposure time to dendron suspensions: 100
min). Identical alignment of the biofilms after embedding and cryo-sectioning
was impossible, hence each fluorescence image is complemented with
a light-microscopic image to visualize the entire biofilm (grasped
within two arrows in the second image from the left, top row). The
white scale bar represents 100 μm. (b) Enlarged overlayer of
fluorescence and light-micrographs of dendrons accumulated in a biofilm.
Scale bar represents 100 μm. (c) A custom LabVIEW script was
used to calculate the fluorescence intensity in a 10 × 0.645
μm (corresponding with one pixel) biofilm column as a function
of biofilm depth (see also Experimental Section). (d) Example of fluorescence intensity as a function of biofilm
depth, calculated as described in panel c, from which the depth-dependent
dendron concentration was derived, using a standard curve (Figure S2).Dendrons with NH3+ groups at their
periphery
accumulated faster into the acidic environment of P. aeruginosa biofilms than dendrons with OH or COO– at their
periphery (Figure a,b), mostly accumulating near the top of the biofilms. Although
initially penetrating less than dendrons with NH3+ groups at their periphery, after 10 min exposure the accumulation
of dendrons with OH and COO– peripheral groups exceeded
accumulation of dendrons with NH3+ peripheral
groups in layers deeper than 30–40 μm into the biofilm
(Figure c,d). Distribution
of dendrons with OH and COO– peripheral groups was
more even across the depth of the biofilms than of dendrons with NH3+ groups at their periphery. Importantly, neither
the distribution (Figure e) nor the total concentration (Figure f) of dendrons with NH3+ groups at their periphery was affected by exposure to PBS, whereas
dendrons with OH or COO– peripheral groups were
largely washed-out during exposure to PBS.
Figure 3
(a–d) Concentration
of dendrons with different peripheral
composition as a function of P. aeruginosa biofilm
depth after exposure of biofilms to 0.2 μM dendron suspensions
in PBS for 0.1, 1, 10, and 100 min (note black and blue data may be
overlapping). (e) Concentration of dendrons in P. aeruginosa biofilms after 100 min exposure to a dendron suspension in PBS,
followed by wash-out in PBS without dendrons for 100 min (note black
and blue data are overlapping). (f) Total concentration of dendrons
in P. aeruginosa biofilms after 100 min exposure
to dendron suspensions and after subsequent wash-out for 100 min.
Error bars denote standard deviations over six different biofilms,
taken from different pans in three separate CDFF runs. Asterisks represent
significant differences (p < 0.05; ANOVA with
Tukey’s posthoc analysis) between dendron periphery compositions: *, NH3+ versus COO– and OH; #, COO– versus OH.
(a–d) Concentration
of dendrons with different peripheral
composition as a function of P. aeruginosa biofilm
depth after exposure of biofilms to 0.2 μM dendron suspensions
in PBS for 0.1, 1, 10, and 100 min (note black and blue data may be
overlapping). (e) Concentration of dendrons in P. aeruginosa biofilms after 100 min exposure to a dendron suspension in PBS,
followed by wash-out in PBS without dendrons for 100 min (note black
and blue data are overlapping). (f) Total concentration of dendrons
in P. aeruginosa biofilms after 100 min exposure
to dendron suspensions and after subsequent wash-out for 100 min.
Error bars denote standard deviations over six different biofilms,
taken from different pans in three separate CDFF runs. Asterisks represent
significant differences (p < 0.05; ANOVA with
Tukey’s posthoc analysis) between dendron periphery compositions: *, NH3+ versus COO– and OH; #, COO– versus OH.Penetration and accumulation of antimicrobials, including
antimicrobials
transported by nanocarriers such as dendrimers, is a conditio sine
qua non for effective bacterial killing in infectious biofilms. Most
studies on antimicrobial nanoparticle penetration and accumulation
in biofilms have focused on the effects of charge, but outcomes are
indecisive. Negatively charged nanoparticles are generally said to
penetrate more easily into biofilms[18−21] but oppositely also positively
charged particles have been described to penetrate better into biofilms.[22] Penetration depends on (1) the availability
of transportation channels in biofilms with sufficient width to allow
nanocarrier passage, (2) diffusion coefficients of the nanocarriers
depending on their configuration and composition, and (3) their interaction
with the channel walls, that is, the EPS matrix or bacterial cell
surfaces. Dendrons are extremely small in the order of 2–5
nm,[23] whereas water channel widths in biofilms
are likely minimally 10-fold larger.[5] Thus,
size differences between the dendrons applied and thus their diffusion
coefficients can be excluded as being causative to the difference
in penetration and accumulation observed between the three different
dendrons. Unfortunately, their small size did not allow reliable measurement
of their zeta potentials; however, based on their pH-responsive peripheral
composition it can be assumed that within an acidic P. aeruginosa biofilm (pH around 6.5[24,25]) NH3+ groups (pKa around 9) will be
protonated and positively charged, whereas COO– groups
(pKa around 2) are deprotonated and negatively
charged. The OH groups will remain uncharged inside P. aeruginosa biofilms. At the same time, EPS components[26,27] and bacterial cell surfaces, including Pseudomonas ones,[28] remain negatively charged around pH 6.5. Thus,
the accumulation of NH3+dendrons near the top
of a biofilm can be explained by strong, electrostatic double-layer
mediated adhesion of dendrons, impeding their penetration to deeper
biofilm layers. The OH and negatively charged COO– dendrons will migrate deeper into the biofilms, as they experience
no electrostatic double-layer attraction with the channel walls and
utmost weak Lifshitz-van der Waals attraction. Therewith the deeper
penetration of neutral and negatively charged particles goes at the
expense of being easily washed-out, an aspect frequently neglected
in the current literature. We here show that prevention of dendron
wash-out critically depends on their peripheral composition, that
is, positive charged groups.Carefully engineered chemistries
of biomaterials or drug carriers,
including antimicrobial nanocarriers, can become compromised when
applied in the human body through interaction with components in the
blood, mucus, and extracellular matrix of human tissue. Because the
current study was designed to provide basic knowledge about the interaction
of dendrons with biofilm rather than demonstrate in vivo performance,
experiments were done in a buffer. In a protein rich environment,
proteins will adsorb on dendrons depending on their peripheral composition,[29] form a corona within 30 s, increase their hydrodynamic
diameter, and make dendron zeta potentials less negative.[29] Yet,[22] surface-engineered
nanoparticles possess the ability to permeate into cells,[30] tumors,[31] and pass
the blood–brain barrier.[32] Smart
micellar nanoparticles with adaptive, pH-responsive engineered surfaces
maintained their surface-engineered properties to penetrate and accumulate
in biofilms in vivo after transport through the blood.[22,33−38] This suggests maintenance of surface-engineered nanoparticle properties
when applied under in vivo conditions. For more macroscopic biomaterials,
it has been suggested[39] in the past that
proteins adsorbed and adjusted their conformation in a way that is
maintained to reflect the chemistry of the underlying material; however,
whether such an argument is valid to explain the abilities of engineered
nanoparticles in vivo remains to be demonstrated.In conclusion,
penetration and accumulation of dendrons into biofilms
is controlled by their pH-responsive peripheral composition. This
conclusion offers better understanding of interactions between dendrimers
and biofilm components during penetration and accumulation that is
important for the development of new antimicrobial dendritic nanocarriers
but in addition also offers the perspective of controlling the accumulation
depth of dendrimers inside a biofilm. Although the dendrons in this
study were labeled with rhodamine as a tool to measure their penetration,
rhodamine can easily be replaced with more therapeutically potent
antimicrobials. Most antibiotics have a similar size as rhodamine
and can be coupled to the focal point of the dendron, alike the rhodamine,
through a hydrolyzable ester or disulfide bond, provided the antibiotics
have a similar hydrophobicity. Subsequently, the dendron can control
the penetration and accumulation into a biofilm according to its peripheral
composition. Together with their good biocompatibility,[11] biodegradability,[12] and commercial availability, that is, often the biggest obstacle
in downward clinical translation,[40] this
warrants future exploitation of these dendrimers, as a new antimicrobial
strategy for infection control.
Experimental Section
Bacterial Strain, Growth
Conditions, and Harvesting
P. aeruginosa ATCC 39324, an isolate from a cystic
fibrosispatient, was grown aerobically for 24 h at 37 °C on
a blood agar plate from a frozen stock and stored at 4 °C until
use. One single colony was added to 10 mL of tryptone soya broth (TSB,
Oxoid, Basingstoke, United Kingdom) and grown for 24 h at 37 °C
after which the broth was added to 200 mL of TSB and incubated 16
h under rotary shaking at 150 rpm (37 °C). Bacteria were harvested
by centrifugation for 5 min at 5000g, after which
the bacterial pellet was washed two times with PBS (PBS, 10 mM potassium
phosphate, 150 mM sodium chloride, pH 7.0). Bacteria were suspended
in 200 mL TSB at a concentration of 5 × 107 bacteria
per mL, as determined using a Bürker-Türk counting chamber.
Biofilm Growth in the Constant Depth Film Fermenter
Biofilms
were grown on stainless steel disks in the constant depth
film fermenter (CDFF).[17] Sterile stainless
steel disks (diameter 5 mm) were placed in a pan, equipped with five
wells with adjustable depth to house five disks. Fifteen pans were
placed in the turntable of the CDFF. The well-depth was set to allow
growth of 100 μm thick biofilms with the aid of a scraper blade
passing over each pan during rotation of the turntable at 3 rpm and
maintaining the temperature inside the CDFF at 37 °C. For inoculation
of the disks in the CDFF, 200 mL of bacterial suspension was dripped
during 1 h on top of the pans, housing the disks. The turntable was
stopped from revolving for 30 min, allowing the bacteria to adhere
to the stainless steel disks, after which rotation was continued and
artificial sputum medium[41] was dropwise
added at a flow rate of 16 mL h–1 on top of the
pans and scraped across. After 18 h of biofilm growth, disks with
adhering biofilms were aseptically taken out of the pans. One CDFF
run was comprised of 75 disks, from each run 15 randomly selected
disk were taken from different pans for optical coherence tomography
(OCT) analysis, and 30 biofilms were selected for dendron penetration
experiments.
Optical Coherence Tomography
The
thickness of biofilms
was determined using OCT (Thorlabs Ganymade-II, Newton, NJ, U.S.A.).
Biofilms were submerged in PBS, and three-dimensional scans of the
complete biofilm were taken. OCT images were processed using a custom-made
LabVIEW (National Instruments, Austin, TX, U.S.A.) script, which was
corrected for background noise and possible tilting of the stainless
steel disk surface. The average biofilm thickness was calculated using
Otsu-thresholding of the image to determine the border between biofilm
and surrounding fluid.[42]
Dendron Penetration
in Biofilms and Cryo-Sectioning of Biofilms
Dendrons were
suspended to a concentration of 0.2 μM in PBS
and 20 μL of a dendron suspension was pipetted over a biofilm
surface. Dendron suspensions were spread evenly over the entire surface
of the biofilm. Biofilms were exposed to dendron suspensions for 0.1,
1, 10, or 100 min, after which the biofilms were dip-washed in PBS.
In addition, biofilms exposed for 100 min to a suspension of dendrons
in PBS were transferred to PBS without dendrons for another 100 min
to monitor dendron wash-out. Directly after washing, biofilms were
embedded in Tissue-Tek O.C.T. compound (Sakura Finetek Europe B.V.,
Alphen aan den Rijn, The Netherlands) and flash-frozen in liquid nitrogen.
Next, biofilms were detached from their stainless-steel substratum
for full embedding in Tissue-Tek and flash-freezing after which samples
were stored in −80 °C until usage. Biofilms were cut in
10 μm thick sections using a cryotome (Leica CM3050 S, Leica
Microsystems, Wetzlar, Germany) operating at −20 °C. Sections
were collected on Menzel-Gläser superfrost slides (Thermo Fischer
Scientific, Waltham, Massachusetts, U.S.A.) and kept in the dark until
imaging, which was performed on the same day.
Fluorescent Imaging and
Quantification of Dendron Penetration
and Accumulation
Fluorescence microscopy (Leica DM 4000 B,
Leica Microsystems Heidelberg Gmbh, Heidelberg, Germany) was carried
out to image the biofilm sections. Fluorescence images were analyzed
using a custom-built LabVIEW script to obtain the red-fluorescence
intensity along the biofilm depth (see Figure c). The LabVIEW script first divided the
biofilm image in vertical columns of 0.645 μm width (covering
1 pixel). Then, it aligned all the vertical columns with their tops
along a straight line, after which the script calculated the average
intensity profile as a function of biofilm depth. The dendron concentration
in the biofilm was derived from the fluorescence intensity with a
standard curve (Figure S2).
Authors: Marina A Dobrovolskaia; Anil K Patri; Jan Simak; Jennifer B Hall; Jana Semberova; Silvia H De Paoli Lacerda; Scott E McNeil Journal: Mol Pharm Date: 2011-11-10 Impact factor: 4.939
Authors: Wen-Chi Chiang; Martin Nilsson; Peter Østrup Jensen; Niels Høiby; Thomas E Nielsen; Michael Givskov; Tim Tolker-Nielsen Journal: Antimicrob Agents Chemother Date: 2013-03-11 Impact factor: 5.191
Authors: Henk J Busscher; Volker Alt; Henny C van der Mei; Paul H Fagette; Werner Zimmerli; T Fintan Moriarty; Javad Parvizi; Gerhard Schmidmaier; Michael J Raschke; Thorsten Gehrke; Roger Bayston; Larry M Baddour; Lynn C Winterton; Rabih O Darouiche; David W Grainger Journal: ACS Biomater Sci Eng Date: 2018-12-02
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