Subscriber access provided by UB + Fachbibliothek Chemie | (FU-Bibliothekssystem)
Article
Facile Preparation of Titanium (IV)-immobilized Hierarchically Porous Hybrid Monoliths Haiyang Zhang, Junjie Ou, Yating Yao, Hongwei Wang, Zhongshan Liu, Yinmao Wei, and Mingliang Ye Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/acs.analchem.7b00242 • Publication Date (Web): 18 Mar 2017 Downloaded from http://pubs.acs.org on March 20, 2017
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Analytical Chemistry is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
1 2
Facile Preparation of Titanium (IV)-immobilized Hierarchically
3
Porous Hybrid Monoliths
4 5
Haiyang Zhanga, b, c, Junjie Oua,*, Yating Yaoa, c, Hongwei Wanga, c, Zhongshan Liua, c,
6
Yinmao Weib,*, Mingliang Yea,*
7 8
a
9
Chemical Physics, Chinese Academy of Sciences (CAS), Dalian, 116023, China
Key Laboratory of Separation Science for Analytical Chemistry, Dalian Institute of
10
b
11
of Education, College of Chemistry and Materials Science, Northwest University,
12
Xi'an 710069, China
13
c
Key Laboratory of Synthetic and Natural Function Molecule Chemistry of Ministry
University of Chinese Academy of Sciences, Beijing 100049, China
14
1
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
15
Page 2 of 28
ABSTRACT
16
Hierarchically porous materials have become a key feature of biological materials
17
and have been widely applied for adsorption or catalysis. Herein, we presented a new
18
approach to directly prepare a phosphate-functionalized hierarchically porous hybrid
19
monolith (HPHM), which simultaneously contained mesopores and macropores. The
20
design
21
vinylsilsesquioxanes (vinylPOSS) and vinylphosphonic acid (VPA) by adding
22
degradable polycaprolactone (PCL) additive. The phosphate groups could be directly
23
introduced into the hybrid monoliths. This approach was simple and time-saving, and
24
overcame the defect of rigorous complex process of preparing traditional
25
Ti4+-immobilized metal ion affinity chromatography (IMAC) materials. The specific
26
surface area of optimal hybrid monolith could reach 502 m2/g obtained by nitrogen
27
adsorption/desorption measurements, which originated from the degradation of PCL.
28
Meanwhile, the characterization of scanning electron microscopy (SEM) and mercury
29
intrusion porosimetry (MIP) also suggested that the macropores existed in the hybrid
30
monoliths. The size of macropores could be controlled by the content of PCL in the
31
polymerization mixture. The prepared Ti4+-IMAC HPHMs exhibited high adsorption
32
capacity (63.6 mg/g for pyridocal 5’-phosphatemonohydrate), excellent enrichment
33
specificity (tryptic digest of β-casein/BSA at a molar ratio of 1:1000) and sensitivity
34
(tryptic digest of 5 fmol of β-casein). Moreover, the Ti4+-IMAC HPHMs provided
35
effective enrichment ability of low-abundance phosphopeptides from human serum
36
and Hela cell digests.
was
based
on
the
copolymerization
of
2
ACS Paragon Plus Environment
polyhedral
oligomeric
Page 3 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
37
INTRODUCTION
38
As one of crucial tools for signaling in cellular networks, protein phosphorylation
39
has become a major regulatory machinery in regulating many complicated biological
40
processes.1,2 Nowadays, mass spectrometry (MS)-based techniques have become a
41
preferred technique for the characterization of protein phosphorylation. Owing to the
42
co-existence of abundant non-phosphopeptides, the direct MS analysis was not able to
43
identify low abundant phosphopeptides in the complex peptide mixtures generated
44
from protein digest. Therefore, it was indispensable to specifically isolate subsets of
45
phosphopeptides from biological samples prior to MS analysis.
46
Biological matter still sets important guiding principles for materials science, and
47
various materials have been developed for selective enrichment of phosphopeptides.3-8
48
Among them, nanoparticles, polymer-based monoliths and microspheres are the most
49
commonly used materials. Nanoparticles, such as titanium dioxide,9,10 mesopores
50
silica,11 magnetic nanoparticles12,13 and metal-organic framework nanoparticles,14,15
51
showed high enrichment specificity and sensitivity for phosphopeptides in biological
52
samples. However, these materials usually required a few steps to modify their
53
surfaces with specific function, which was troublesome and time-consuming.
54
Titanium (IV) immobilized polymeric monoliths16-22 were also remarkable materials
55
for enrichment of phosphopeptides. Although monolithic supports had the advantages
56
such as high porosity and convective mass transport, relatively low specific surface
57
area of monoliths,23 which was less than tens of square meters per gram (m2/g) and
58
limited their application. In 2013, Heck and Zou et al24 developed a titanium (IV)
59
immobilized mono-dispersed microsphere and applied for immobilized metal ion
60
affinity chromatography (Ti4+-IMAC). This kind of Ti4+-IMAC microsphere also
61
exhibited excellent enrichment performance of phosphopeptides. However, the
62
fabrication process of Ti4+-IMAC microsphere also required several steps such as
63
formation of mono-dispersed polystyrene microspheres, coupling of phosphonate
64
groups onto the mono-dispersed microspheres and so on, which was really
65
complicated and time-consuming. Therefore, the design and synthesis of a novel 3
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 4 of 28
66
IMAC material for high selectivity of enriching phosphopeptides is still attracting
67
attention.
68
Hierarchical porous materials were key materials used for adsorption or catalysis,
69
which were predominantly understood as a structural feature and have been in the
70
focus of scientific research for more than ten years.25-28 These materials
71
simultaneously contain a percolating pore structure and a continuous matrix structure
72
that may combines micro- (< 2 nm), meso- (2-50 nm) and macropores (> 50 nm).
73
Such multilevel porous architectures confer unique properties to materials depending
74
on the combination of pore sizes, in which micro- and mesopores generate a large
75
specific surface area, providing main functional sites, while macropores can improve
76
the mass transfer in the application process, increasing the accessibility of the active
77
sites.25,29-32 As a result, hierarchically porous materials exhibit lower backpressures,
78
higher permeability and better performance in separation and life science.33-36
79
However, there are few reports on hierarchically porous materials used for
80
phosphopeptides analysis.37,38
81
In this work, we developed a novel Ti4+-IMAC hybrid monolithic material with
82
hierarchical structure, which simultaneously consisting of micropores, mesopores and
83
macropores.
84
vinylphosphonic acid (VPA) as monomers, polycaprolactone (PCL) as additive and
85
tetrahydrofuran (THF) as single solvent were employed to prepare Ti4+-IMAC
86
hierarchically porous hybrid monoliths (HPHMs) via thermal-initiated free radical
87
polymerization. The preparation process was very simple and accessible, and the
88
resulting Ti4+-IMAC HPHMs with hierarchical structure demonstrated high binding
89
capacity of small molecules, high selectivity and detection sensitivity for
90
phosphopeptides in different biological samples.
Polyhedral
oligomeric
vinylsilsesquioxanes
(vinylPOSS)
and
91 92
EXPERMENTAL SECTION
93
Materials.
94
VinylPOSS was obtained from Hybrid Plastics, Inc (Hattiesburg, MS, USA). VPA 4
ACS Paragon Plus Environment
Page 5 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
95
(97%), PCL (average Mn~10,000), pyridoxal 5’-phosphate hydrate (≥ 98%), sodium
96
chloride (NaCl), trifluoroacetic acid (TFA), bovine serum albumin (BSA), β-casein,
97
protease inhibitor Cocktail (for use with mammalian cell and tissue extracts),
98
phosphatase inhibitor (1 mM NaF and 1 mM Na3VO4), TPCK treated trypsin, urea,
99
iodoacetamide (IAA), 1,4-dithiothreitol (DTT) and 2,5-dihydroxyl benzoic acid (DHB)
100
were obtained from Sigma (St Louis, MO, USA). 2,2-Azobisisobutyronitrile (AIBN)
101
and titanium sulfate were gotten from Shanghai chemical Plant (Shanghai, China).
102
Tetrahydrofuran (THF), hydrochloric acid (HCl) and methanol were of analytical
103
grade, and obtained from Tianjin Kermel Chemical Plant (Tianjin, China).
104
RPMI-1640 cell culturing medium was purchased from Gibco Invitrogen Corporation
105
(Carlsbad, CA). Formic acid (FA) was obtained from Fluka (Buches, Germany).
106
Acetonitrile (ACN, HPLC grade) and ammonia-water (NH3•H2O) were purchased
107
from Merck (Darmstadt, Germany). The water used in all experiments was doubly
108
distilled and purified by Milli-Q system (Millipore Inc., Milford, MA, USA).
109
Preparation of Phosphate-functionalized HPHMs.
110
VinylPOSS, VPA and PCL were dissolved in THF by sonication for 5 min, and the
111
detail composition of prepolymerization mixtures and porous properties of
112
phosphate-functionalized HPHMs were listed in Table 1. After AIBN was added into
113
the solution, the solution was transferred into an ampoule, and then placed in the
114
liquid nitrogen to solidify the solution. Meanwhile, the ampoule was vacuumized by a
115
vacuum pump, and the bottleneck of ampoule was sealed by using a butane torch at
116
the same time. After that the ampoule was put in 60 oC water bath for 24 h. The
117
obtained materials were washed with THF for three times to remove residual
118
monomer, and then dried in air atmosphere and put in the vacuum at 60 oC for 12 h.
119
Subsequently, the materials were degraded by placing them in vials containing 1 M
120
HCl in water/methanol (6/4, v/v) solution. The vials were sealed with parafilms and
121
heated for 3 days at 70 oC water bath to ensure complete hydrolysis of PCL. The
122
obtained bulk monoliths (7.0 mm diameter × 8.0 mm length, cylinder) were rinsed
123
with water and methanol repeatedly. Finally, the hybrid monoliths were dried in a
124
vacuum oven at 60 oC overnight. 5
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
125
Preparation of Ti4+-IMAC HPHMs.
126
Ti4+ was immobilized on phosphate-functionalized HPHMs by using the phosphate
127
groups existed in the hybrid monoliths as chelating agents. Prior to immobilization of
128
Ti4+, the monoliths were ground to amorphous granules (more than tens of
129
micrometers) in order to weigh easily. Titanium sulfate aqueous solution (100 mg/mL)
130
was prepared in centrifuge tube, and then the hybrid monoliths were added. The
131
centrifuge tube was put on the rolling incubator for 12 h to guarantee entire binding.
132
Then the hybrid monoliths were washed by water and 200 mM NaCl aqueous solution
133
(containing 0.1% TFA) to remove dissociative Ti4+.
134
Phosphopeptides Enrichment Using Ti4+-IMAC HPHMs
135
Before enrichment of phosphopeptides, 5 mg of Ti4+-IMAC HPHMs were placed in
136
a centrifuge tube and equilibrated by loading solution (80% ACN, 6% TFA). At the
137
same time, the tryptic peptide digest was mixed in loading solution (80% ACN, 6%
138
TFA) with identical volumes. Then the tryptic peptide digest in loading solution was
139
transferred into the centrifuge tube in which Ti4+-IMAC HPHMs existed. The mixture
140
was gently incubated at room temperature for 30 min. After removing the supernatant,
141
the Ti4+-IMAC HPHMs were washed twice with 200 µL of washing solution (50%
142
ACN, 6% TFA, 200 mM NaCl) and another washing solution (30% ACN, 0.1% TFA)
143
orderly to remove the non-specifically bound peptides. The captured phosphopeptides
144
were eluted twice by 100 µL of 10% NH3•H2O. After centrifugation, the supernatants
145
containing phosphopeptides were collected in the centrifuge tube. The obtained
146
phosphopeptides were lyophilized using a Speed-Vac (Thermo SPD SpeedVac) and
147
then stored at -30 oC for further LC-MS/MS analysis.
148
Instruments and Methods.
149
Fourier-transformed infrared spectroscopy (FT-IR) characterization was carried out
150
on Thermo Nicolet 380 spectrometer (Nicolet, Wisconsin, USA) using KBr pellets,
151
containing approximate 1 mg sample and 100 mg KBr. The microscopic morphology
152
and energy dispersive spectrometer (EDS) of hybrid monolithic materials were
153
obtained by scanning electron microscopy (SEM, JEOL JSM-5600, Tokyo, Japan).
154
The specific surface areas were calculated from nitrogen adsorption/desorption 6
ACS Paragon Plus Environment
Page 6 of 28
Page 7 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
155
measurements of dry bulk monoliths using a Quadrasorb SI surface area analyzer
156
(Quantachrome, Boynton Beach, USA). Samples were vacuumized and treated with
157
120 oC for 6 h before nitrogen adsorption/desorption analysis. The specific surface
158
areas were calculated via the Brunauer-Emmett-Teller (BET) method, and the pore
159
size
160
Barrett-Joyner-Halenda (BJH) method. The total pore volumes were determined at
161
P/P0 = 0.99. UV-vis spectra were recorded on a V550 spectrophotometer (JASO,
162
Japan). PoreMasre GT-60 (Quantachrome Boynton Beach, USA) was used to measure
163
macropores size distribution of hybrid monoliths by mercury intrusion porosimetry
164
(MIP). Thermogravimetric (TG) data were collected on Pyris 1 TGA (Perkin Elmer,
165
USA).
distributions
were
determined
from
adsorption
isotherm
by
the
166
The phosphopeptides were enriched without lyophilization according to the
167
previous described method. The mixture of phosphopeptides in 10% NH3•H2O (0.5
168
µL) and the matrix (0.5 µL of 25 mg/mL DHB in ACN/H2O/H3PO4 = 70/29/1, v/v/v)
169
were spotted on the MALDI plate, and analyzed by an AB Sciex 5800
170
MALDI-TOF/TOF mass spectrometer (AB Sciex, CA) equipped with a pulsed
171
Nd/YAG laser at 355 nm in linear positive ion mode.
172 173
RESULTS AND DISCUSSION
174
Preparation and Characterization of Ti4+-IMAC HPHMs
175
Polyhedral oligomeric silsesquioxanes (POSS), as a kind of organic-inorganic
176
hybrid nanocomposite, has been widely incorporated into various materials,39-41 which
177
can result in significant improvement in physical and mechanical properties due to the
178
reinforcement at the molecular level and the inorganic framework’s ceramic-like
179
properties.42,43 Poly(lactide) (PLA), a chemically degradable polymer, has been
180
employed to synthesize nanoporous polymers,44-46 and the structure of PCL is similar
181
with PLA. Thus, PCL can also be degraded in basic or acidic conditions. As shown in
182
Scheme 1, the preparation process of Ti4+-IMAC HPHMs was illustrated. The hybrid
183
monoliths were firstly formed via thermal-initiated free radical polymerization of 7
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 8 of 28
184
vinylPOSS and VPA as monomers, PCL as nonreactive additive and THF as the
185
solvent. In this way, the phosphate groups were directly introduced into the hybrid
186
monoliths. The approach overcame the defect of the immobilization of phosphate
187
groups into other Ti4+-IMAC materials. The PCL was trapped in the bulk monoliths in
188
the polymerization process and could be degraded after a treatment of acidic solution.
189
Although it took about five days to synthesize Ti4+-IMAC HPHMs, the operation
190
process was simple and labor-saving.
191
Figure 1a and c presented the nitrogen sorption isotherm and pore size distribution
192
of hybrid monolith II, respectively, which was prepared with equal molar of VPA and
193
vinylPOSS (vinyl group molar ratio of 1:8) and adding 25% (w/w) PCL. The results
194
clearly indicated the existence of both micropores and mesopores, and the hybrid
195
monolith exhibited pore volume of 0.32 cm3/g and high surface area of 502 m2/g. The
196
size of mesopores was smaller than 10 nm based on BJH analysis of the adsorption
197
isotherm (Figure 1c).The hybrid monolith VI was fabricated by adding more VPA into
198
the prepolymerization solution (vinyl group molar ratio of 1:4), which also contained
199
25% (w/w) PCL. As shown in Figure 1b and d, the specific surface area of hybrid
200
monolith VI was slightly decreased to 473 m2/g, and the size of mesopores was the
201
same as that of hybrid monolith II (less than 10 nm). Further increasing VPA into the
202
prepolymerization solution (vinyl group molar ratio of VPA/vinylPOSS, 1:2) to
203
prepare the hybrid monolith X, it could also be seen that the specific surface area was
204
further decreased to 360 m2/g as shown in Table 1. These results suggested that the
205
specific surface areas of hybrid monoliths decreased by adding more VPA into the
206
prepolymerization solution. This phenomenon was possibly related to either
207
homopolymerization of VPA or copolymerization of VPA and vinylPOSS. First, the
208
poly(vinylphosphonic acid) (poly(VPA)) was formed via homopolymerization of VPA,
209
which
210
phosphate-functionalized hybrid monolithic materials. The poly(VPA) was a kind of
211
linear polymer, which had relatively low specific surface areas.47,48 Thus, the
212
ingredient with relatively low specific surface areas would cause to decrease the
213
specific surface areas of hybrid monoliths. Meanwhile, part of phosphonate ligands
was
then
coupled
with
vinylPOSS
or
8
ACS Paragon Plus Environment
monoliths
to
form
Page 9 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
214
was embedded in the skeleton of the HPHM, which was not accessible. Second, a
215
VPA molecule was linked with two molecules of vinylPOSS monomer via
216
copolymerization reaction, which would form a flexible chain. Intertwining might
217
occur between these flexible chains, resulting in the decrease of specific surface areas
218
of hybrid monoliths. Therefore, the specific surface areas of hybrid monoliths
219
decreased with an increase of the content of VPA monomer in the prepolymerization
220
mixture. As shown in Figure S1, the Si and P were uniformly distributed on the
221
surface of hybrid monoliths. It was deduced that the phosphate groups were also
222
evenly distributed in the hybrid monoliths.
223
In order to verify the effect of PCL additive on the porous properties of hybrid
224
monoliths, different amounts of PCL (from 16.7 to 31.8%) were added into the
225
prepolymerization solution, in which the vinyl group molar ratio of VPA/vinylPOSS
226
maintained 1:4 (shown in Table 1, monoliths III-VIII). It can be seen that the specific
227
surface areas of these monoliths after degradation of PCL were ranged in 406-473
228
m2/g, and the pore volumes were in the range of 0.26-0.35 cm3/g, which were
229
measured by nitrogen adsorption/desorption measurements. The size of mesopores in
230
monolith VI was also less than 10 nm (Figure 1d). For comparison, monolith III was
231
prepared without adding PCL, and the specific surface area reached 460 m2/g, in
232
which the micropores specific surface area was 225 m2/g by t-plot method, while the
233
mesopores specific surface area was 215 m2/g. Although the introduction of PCL did
234
not have remarkable effect on the specific surface areas and pore volumes, the
235
specific surface areas of hybrid monoliths without degradation of PCL were far lower
236
than those after degradation of PCL as shown in Table 1. It was clearly shown that the
237
specific surface area of hybrid monolith VI prior to degradation of PCL was only 174
238
m2/g, in which the micropores specific surface area reached 83 m2/g by the t-plot
239
method, while the mesopores specific surface area was only 91 m2/g. However, the
240
specific surface area reached 473 m2/g after degradation of PCL. The micropores
241
specific surface area reached 273 m2/g by the t-plot method, while the mesopores
242
specific surface area was 200 m2/g. Further increasing the content of PCL to 31.8%,
243
the result was the same, in which the specific surface area of monolith VIII increased 9
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
244
from 154 to 406 m2/g after degradation of PCL. Additionally, this phenomenon could
245
be observed on the monoliths II and X, which were prepared with other vinyl group
246
molar ratios of VPA/vinylPOSS (1:8 and 1:2, respectively, Table 1). The specific
247
surface area of monolith II increased from 195 to 502 m2/g after degradation of PCL,
248
while the specific surface area of monolith X increased from 97 to 360 m2/g after
249
degradation of PCL. These results indicated that PCL additive could occupy the
250
monolithic scaffold when the copolymerization of vinylPOSS and VPA occurred,
251
which was not be washed out by solvents, but only removed by acidic hydrolysis to
252
generate nanopores.
253
The characterization results of scanning electron microscopy (SEM) and mercury
254
intrusion porosimetry (MIP) further demonstrated that the hybrid monoliths prepared
255
with PCL possessed macroporous structure. As shown in Figure 2 and S2, the SEM
256
micrograph of monolith VI showed that the macropores clearly appeared when the
257
content of PCL reached 25%. However, as shown in Figure S3, the macropores could
258
not be observed in the monolith VI prior to degradation of PCL, also indicating that
259
the PCL could not be washed out by solvent. When the content of PCL was further
260
increased to 31.8%, the size of macropores in hybrid monolith VIII became larger
261
(Figure 2c and f) than that in hybrid monolith VI (Figure 2b and e). However, there
262
were not distinct macropores observed from the SEM micrograph of monolith III,
263
which was prepared without adding PCL (Figure 2a, d and S2a). It was indicated that
264
PCL also had effect on formation of macropores. Meanwhile, the macropores could
265
also be observed from Figure S4, as the content of PCL reached 25%, and the content
266
of VPA was changed (monolith II). The results of MIP characterization further
267
testified that macropores clearly appeared in monolith VI (Figure 3a), and the size of
268
macropores in monolith VIII became larger (nearly 1 µm) further increasing the
269
content of PCL to 31.8% (Figure 3b). The results of nitrogen adsorption/desorption
270
measurements, SEM and MIP proved that PCL could facilitate to form not only
271
nanopores, but also macropores in the framework of hybrid monoliths. Meanwhile,
272
the size of macropores can be controlled by the content of PCL in the
273
prepolymerization mixture. In a word, the phosphate-functionalized hybrid monoliths 10
ACS Paragon Plus Environment
Page 10 of 28
Page 11 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
274
(II, VI and VIII) simultaneously possessed micropores, mesopores and macropores,
275
indicating hierarchically porous structure. Therefore, the phosphate-functionalized
276
HPHMs were facilely prepared via free radical polymerization following the
277
degradation of PCL.
278
The Fourier-transformed infrared spectroscopy (FT-IR) characterization was
279
performed to inspect the formation of hybrid monolith by using vinylPOSS and VPA
280
as the monomers, as shown in Figure 4. It could be clearly observed that the peak
281
signals at 3030, 3070 cm-1 (assigned to C-H stretching vibrations from CH=CH2) and
282
1600 cm-1 (assigned to C=C stretching vibration) existed in the spectrum of
283
vinylPOSS monomer (Figure 4a). After the formation of hybrid monoliths, the peaks
284
at 3030 and 3070 cm-1 almost disappeared (Figure 4d). Compared to the FT-IR
285
spectrum of VPA (Figure 4b), the strong signal peak at 930 cm-1, which was assigned
286
to the symmetrical stretching vibration of phosphate radical, could be clearly observed
287
in the FT-IR spectrum of hybrid monolith (Figure 4d). It was indicated that phosphate
288
groups existed in hybrid monolith. However, other characteristic adsorption peaks of
289
phosphate (such as 1161 and 1003 cm-1, which assigned to the stretching vibration
290
P=O and P-O, respectively) were covered by the characteristic adsorption peaks of
291
vinylPOSS. A weak signal at 1730 cm-1 implied the appearance of carbonyl (C=O) in
292
PCL (Figure 4c), which still existed in hybrid monolith. This result suggested that
293
PCL could not be absolutely degraded by acidic condition, and part of PCL might be
294
wrapped in the skeleton. The existence of PCL would not have influence on the
295
properties of hybrid monoliths. Meanwhile, thermal stability of hybrid monolith was
296
investigated by TG, as shown in Figure S5. A significant mass loss began at 300 oC
297
and continued to 600 oC due to the pyrolysis of organic moieties under nitrogen
298
atmosphere. This result indicated that the obtained HPHMs exhibited satisfactory
299
thermal stability. Meanwhile, the residue of hybrid monolith VI before immobilization
300
of Ti4+ was 44.1%, while it was 62.8% after immobilization of Ti4+. It was due to the
301
residue contained titanium compounds, which could not sublimate at 800 oC. This
302
result also indicated that Ti4+ was successfully immobilized on hybrid monolith.
303 11
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
304
Page 12 of 28
Properties of Ti4+-IMAC HPHMs in Absorption and Enrichment
305
Pyridocal 5’-phosphatemonohydrate as a coenzyme plays an important role in all
306
transamination reactions and some decarboxylation or deamination reactions of amino
307
acids. Due to the existence of phosphate group, pyridocal 5’-phosphatemonohydrate
308
can be absorbed by Ti4+-IMAC materials based on the chelation between Ti4+ and
309
phosphate group. Therefore, it was selected to evaluate the adsorption capacity of
310
phosphate-functionalized HPHMs. Prior to use, the prepared phosphate-functionalized
311
HPHMs were firstly chelated with titanium ions to obtain Ti4+-IMAC HPHMs. The
312
curve of the adsorption isotherm of pyridocal 5’-phosphatemonohydrate was shown in
313
Figure 5A. Three kinds of Ti4+-IMAC materials, including Ti4+-IMAC hybrid
314
monolith without any macropores (monolith III), Ti4+-IMAC HPHM (monolith VI)
315
and Ti4+-IMAC microspheres (12 µm, diameter) prepared according to the reference24,
316
were employed to absorb pyridocal 5’-phosphatemonohydrate. It could be seen that
317
the adsorption equilibration (○) was achieved on monolith VI within 30 min, while it
318
would take 60 min to reach the adsorption equilibration (■) on monolith III. This
319
result demonstrated that macropores existed in monolith VI could facilitate to increase
320
the mass transfer rate. Although the adsorption equilibration (▲) using Ti4+-IMAC
321
microspheres mentioned above could be achieved within several minutes, the
322
adsorption
323
microspheres was only 49.7 mg/g, as shown in Figure 5b. Compared to the adsorption
324
capacity of Ti4+-IMAC microspheres, the adsorption capacity of monolith VI was
325
higher, which could reach 63.6 mg/g. However, the adsorption capacity of monolith
326
III was only 38.8 mg/g, which was far lower than those of other two materials. These
327
results illustrated that although the micropores and mesopores surface areas of
328
monolith VI (273 and 200 m2/g, respectively) were similar with those of monolith III
329
(225 and 215 m2/g, respectively), the macropores existed in the hybrid monoliths
330
could enhance the mass transfer rate and shorten the equilibration time. Meanwhile,
331
its high specific surface area could provide much more active sites and improve the
332
adsorption capacity. It was deduced that this kind of Ti4+-IMAC HPHMs was
333
applicable to enrich small molecules containing phosphate groups.
capacity
for
pyridocal
5’-phosphatemonohydrate
12
ACS Paragon Plus Environment
on
Ti4+-IMAC
Page 13 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
334
Considering the hierarchically porous property, monolith VI was selected for
335
evaluation of the ability of Ti4+-IMAC HPHMs in the enrichment of phosphopeptides.
336
Due to the low level of phosphopeptides in a complex biological sample, the
337
sensitivity and selectivity of Ti4+-IMAC HPHMs were two key parameters for the
338
enrichment performance. A standard phosphoprotein (β-casein) tryptic digest was
339
used to evaluate its performance. The tryptic digest of 1 µg of β-casein (100 fmol)
340
was incubated with 5 mg of Ti4+-IMAC HPHM in loading solution, and then the
341
bound peptides were eluted by 10% NH3•H2O after washing away nonspecific
342
peptides with washing solutions. Finally, 0.5 µL of the eluted solution was deposited
343
on the MALDI target for MALDI-TOF MS analysis. As shown in Figure S6a, the
344
tryptic digest of β-casein was directly analyzed by MALDI-TOF MS without any
345
enrichment. It could be seen that the signals of the phosphopeptides were severely
346
suppressed by many non-phosphopeptides, and the peaks of phosphopeptides could
347
not be clearly observed. However, the peaks of three expected phosphopeptides could
348
be clearly seen with a clear background after enrichment with HPHM as shown in
349
Figure S6b, along with one of its dephosphorylated counterparts was also detected.
350
Meanwhile, the non-phosphopeptides peaks nearly completely disappeared, which
351
indicated that this kind of Ti4+-IMAC HPHMs had high affinity toward
352
phosphopeptides. The sensitivity of phosphopeptides enriched by the Ti4+-IMAC
353
HPHMs with MALDI-TOF MS detection was also performed by using different
354
contents of β-casein tryptic digest as shown in Figure S6c and d. The results showed
355
that the phosphopeptides in β-casein tryptic digest whose content reached 10 fmol
356
could be still detected by MALDI-TOF MS after enriching with the monolith VI.
357
Even though the total amount of β-casein tryptic digest reached as low as 5 fmol, one
358
peak of phosphopeptide could still be identified in the spectrum. Therefore, it was
359
deduced that the Ti4+-IMAC HPHMs could be used to process trace amount of
360
samples. Furthermore, a mixture of β-casein and BSA tryptic digest as test sample
361
was used to evaluate the selectivity of the Ti4+-IMAC HPHMs for enrichment of
362
phosphopeptides. When the molar ratio of β-casein to BSA tryptic digest was 1:500,
363
three peaks of characteristic phosphopeptides in β-casein tryptic digest could be easily 13
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
364
detected by MALDI-TOFMS after enrichment using monolith VI, as shown in Figure
365
S7a. Even when the molar ratio of β-casein to BSA tryptic digest decreased to 1:1000,
366
three expected phosphopeptides could still be clearly identified in spite of the
367
interference signal from non-phosphopeptides was slightly increased as shown in
368
Figure S7b. These results illustrated that the prepared Ti4+-IMAC HPHMs had high
369
selectivity for the capture of phosphopeptides from a complex peptide mixture.
370 371
Application of Ti4+-IMAC HPHMs in Enrichment of Phosphopeptides from
372
Human Serum and Tryptic Digest of Human Hela Cells
373
To further demonstrate the feasibility of Ti4+-IMAC HPHMs in selective
374
enrichment of low abundance of phosphopeptides from practical biosamples, human
375
serum was selected as a real sample. As shown in Figure 6a, only one MS signal
376
intensity of phosphopeptides appeared owing to the low abundance of
377
phosphopeptides and high salt content, while several non-phosphopeptides with
378
intense MS signal appeared in the spectrum. Nonetheless, after treatment with
379
Ti4+-IMAC HPHM, four peaks of phosphopeptides with higher MS intensities could
380
be distinctly detected as shown in Figure 6b. The detail information of four
381
phosphopeptides from human serum was shown in Table S1. This result revealed that
382
the prepared Ti4+-IMAC HPHMs were capable of highly selective trapping of
383
phosphopeptides from a complicated biological sample.
384
Encouraged by its excellent performance in enrichment of phosphopeptides, the
385
phosphopeptides from human Hela cell digests were also enriched by Ti4+-IMAC
386
HPHMs. The 100 µg of human Hela cell digests and 5 mg of monolith VI were used
387
each time, and three technical repeats were performed in parallel. The obtained
388
phosphorylated peptides were then analyzed by LC-MS/MS. For comparison,
389
Ti4+-IMAC microspheres were also used to capture phosphopeptides from human
390
Hela cell digests under its optimal condition at the same time.24 The 1851, 1923 and
391
1894 of unique phosphopeptides were identified from 100 µg of Hela cell digests after
392
enriching by monolith VI, respectively, while only 1733, 1686 and 1683 of unique
393
phosphopeptides were identified after enriching by Ti4+-IMAC microspheres, 14
ACS Paragon Plus Environment
Page 14 of 28
Page 15 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
394
respectively.
Meanwhile,
the
enrichment
specificities
(the
percentages
of
395
phosphopeptides identified) after enriched by Ti4+-IMAC HPHM or Ti4+-IMAC
396
microspheres were all higher than 97.0%. These results indicated that the prepared
397
Ti4+-IMAC HPHMs exhibited excellent enrichment specificity and selectivity towards
398
to phosphopeptides and could be applied to comprehensive phosphoproteome
399
analysis.
400 401
CONCLUSIONS
402
In summary, a novel Ti4+-IMAC HPHM was successfully synthesized via
403
thermal-initiated free radical polymerization of vinylPOSS and VPA by introducing
404
degradable PCL additive. Phosphate groups could be directly introduced into the
405
hybrid monoliths, and the obtained hybrid monoliths possessed hierarchical structures
406
after degradation of PCL, which simultaneously possessed macropores, mesopores
407
and micropores. The nanopores came from the degradation of PCL additive in the
408
hybrid monolithic framework as well as the nanopores originated from the
409
copolymerization of vinylPOSS and VPA due to the steric hindrance could provide
410
large specific surface areas and lots of active phosphate sites. Meanwhile, the content
411
of PCL could also affect the formation of macropores, which could enhance the mass
412
transfer rate. Compared to the methods to prepare other Ti4+-IMAC microspheres and
413
nanomaterials, the method to prepare this kind of HPHMs was easy and time-saving
414
due to without extra steps to introduce the phosphate groups. The resulting Ti4+-IMAC
415
HPHMs exhibited excellent adsorption capacity, enrichment specificity and sensitivity
416
for phosphopeptides. Furthermore, this kind of Ti4+-IMAC HPHMs was used to
417
selectively enrich phosphopeptides from human serum and Hela cell digest, and the
418
results showed great practicability in identifying low-abundance phosphopeptides
419
from complicated biological samples.
420 421
AUTHOR INFORMATION
422
Corresponding Author 15
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
423
*E-mail:
[email protected] (J.J.
Ou);
[email protected] 424
[email protected] (Y.M. Wei)
425
Notes
426
The authors declare no competing financial interest.
Page 16 of 28
(M.L.
Ye);
427 428
SUPPORTING INFORMATION AVAILABLE
429
Additional information as noted in text. This material is available free of charge via
430
the internet at http://pubs.acs.org.
431 432
ACKONWLEDGMENTS
433
Financial support is gratefully acknowledged from the China State Key Basic
434
Research Program Grant (2016YFA0501402) and the National Science Fund for
435
Distinguished Young Scholars (21525524) to M. Ye, as well as the National Natural
436
Sciences Foundation of China (No. 21575141) to J. Ou.
437 438
439 440 441 442 443 444 445 446 447 448 449 450 451 452 453 454 455 456
REFERENCES (1) Ptacek, J.; Devgan, G.; Michaud, G.; Zhu, H.; Zhu, X.; Fasolo, J.; Guo, H.; Jona, G.; Breitkreutz, A.; Sopko, R.; McCartney, R. R.; Schmidt, M. C.; Rachidi, N.; Lee, S. J.; Mah, A. S.; Meng, L.; Stark, M. J.; Stern, D. F.; De Virgilio, C.; Tyers, M.; Andrews, B.; Gerstein, M.; Schweitzer, B.; Predki, P. F.; Snyder, M. Nature 2005, 438, 679-684. (2) Olsen, J. V.; Blagoev, B.; Gnad, F.; Macek, B.; Kumar, C.; Mortensen, P.; Mann, M. Cell 2006, 127, 635-648. (3) Nuhse, T. S.; Stensballe, A.; Jensen, O. N.; Peck, S. C. Mol. Cell. Proteomics 2003, 2, 1234-1243. (4) Lu, Z.; Ye, M.; Li, N.; Zhong, W.; Yin, Y. Angew. Chem. Int. Ed. 2010, 49, 1862-1866. (5) Thingholm, T. E.; Jensen, O. N.; Robinson, P. J.; Larsen, M. R. Mol. Cell. Proteomics 2008, 7, 661-671. (6) Mohammed, S.; Heck, A., Jr. Current opinion in biotechnology 2011, 22, 9-16. (7) Dong, M.; Wu, M.; Wang, F.; Qin, H.; Han, G.; Dong, J.; Wu, R.; Ye, M.; Liu, Z.; Zou, H. Anal. Chem. 2010, 82, 2907-2915. (8) Liu, F.; Wan, H.; Liu, Z.; Wang, H.; Mao, J.; Ye, M.; Zou, H. Anal. Chem. 2016, 88, 5058-5064. (9) Huang, H.; Haar Petersen, M.; Ibanez-Vea, M.; Lassen, P. S.; Larsen, M. R.; Palmisano, G. Mol. Cell. Proteomics 2016, 15, 3282-3296. (10) Wijeratne, A. B.; Wijesundera, D. N.; Paulose, M.; Ahiabu, I. B.; Chu, W. K.; Varghese, O. K.; 16
ACS Paragon Plus Environment
Page 17 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
457 458 459 460 461 462 463 464 465 466 467 468 469 470 471 472 473 474 475 476 477 478 479 480 481 482 483 484 485 486 487 488 489 490 491 492 493 494 495 496 497 498 499 500
Greis, K. D. ACS Appl. Mater. Inter. 2015, 7, 11155-11164. (11) Chen, Y.; Li, D.; Bie, Z.; He, X.; Liu, Z. Anal. Chem. 2016, 88, 1447-1454. (12) Jabeen, F.; Najam-Ul-Haq, M.; Rainer, M.; Guzel, Y.; Huck, C. W.; Bonn, G. K. Anal. Chem. 2015, 87, 4726-4732. (13) Xiong, Z.; Zhang, L.; Fang, C.; Zhang, Q.; Ji, Y.; Zhang, Z.; Zhang, W.; Zou, H. J. Mater. Chem. B 2014, 2, 4473. (14) Chen, Y.; Xiong, Z.; Peng, L.; Gan, Y.; Zhao, Y.; Shen, J.; Qian, J.; Zhang, L.; Zhang, W. ACS Appl. Mater. Inter. 2015, 7, 16338-16347. (15) Chen, L.; Ou, J.; Wang, H.; Liu, Z.; Ye, M.; Zou, H. ACS Appl. Mater. Inter. 2016, 8, 20292-20300. (16) Hou, C.; Ma, J.; Tao, D.; Shan, Y.; Liang, Z.; Zhang, L.; Zhang, Y. J Proteome Res 2010, 9, 4093-4101. (17) Feng, S.; Pan, C.; Jiang, X.; Xu, S.; Zhou, H.; Ye, M.; Zou, H. Proteomics 2007, 7, 351-360. (18) Krenkova, J.; Foret, F. Anal. Bioanal. Chem. 2013, 405, 2175-2183. (19) Wang, S. T.; Wang, M. Y.; Su, X.; Yuan, B. F.; Feng, Y. Q. Anal. Chem. 2012, 84, 7763-7770. (20) Cernigoj, U.; Gaspersic, J.; Fichtenbaum, A.; Lendero Krajnc, N.; Vidic, J.; Mitulovic, G.; Strancar, A. Anal. Chim. Acta. 2016, 942, 146-154. (21) Saeed, A.; Maya, F.; Xiao, D. J.; Najam-ul-Haq, M.; Svec, F.; Britt, D. K. Adv. Funct. Mater. 2014, 24, 5790-5797. (22) Krenkova, J.; Lacher, N. A.; Svec, F. Anal. Chem. 2010, 82, 8335-8341. (23) Liu, Z.; Ou, J.; Lin, H.; Liu, Z.; Wang, H.; Dong, J.; Zou, H. Chem. Commun. 2014, 50, 9288-9290. (24) Zhou, H.; Ye, M.; Dong, J.; Corradini, E.; Cristobal, A.; Heck, A. J.; Zou, H.; Mohammed, S. Nat. Protoc. 2013, 8, 461-480. (25) Verboekend, D.; Nuttens, N.; Locus, R.; Van Aelst, J.; Verolme, P.; Groen, J. C.; Perez-Ramirez, J.; Sels, B. F. Chem. Soc. Rev. 2016, 45, 3331-3352. (26) Schwieger, W.; Machoke, A. G.; Weissenberger, T.; Inayat, A.; Selvam, T.; Klumpp, M.; Inayat, A. Chem. Soc. Rev. 2016, 45, 3353-3376. (27) Zhang, Y.; Zhang, Y.; Burke, J. M.; Gleitsman, K.; Friedrich, S. M.; Liu, K. J.; Wang, T. H. Adv. Mater. 2016, 28, 10630-10636. (28) Lopez-Orozco, S.; Inayat, A.; Schwab, A.; Selvam, T.; Schwieger, W. Adv. Mater. 2011, 23, 2602-2615. (29) Sai, H.; Tan, K. W.; Hur, K.; Asenath-Smith, E.; Hovden, R.; Jiang, Y.; Riccio, M.; Muller, D. A.; Elser, V.; Estroff, L. A.; Gruner, S. M.; Wiesner, U. Science 2013, 341, 530-534. (30) Schneider, D.; Mehlhorn, D.; Zeigermann, P.; Karger, J.; Valiullin, R. Chem. Soc. Rev. 2016, 45, 3439-3467. (31) Huang, X.; Yu, H.; Chen, J.; Lu, Z.; Yazami, R.; Hng, H. H. Adv. Mater. 2014, 26, 1296-1303. (32) Hasell, T.; Zhang, H.; Cooper, A. I. Adv. Mater. 2012, 24, 5732-5737. (33) Konishi, J.; Fujita, K.; Nakanishi, K.; Hirao, K.; Morisato, K.; Miyazaki, S.; Ohira, M. J. Chromatogr. A 2009, 1216, 7375-7383. (34) López-Noriega, A.; Arcos, D.; Izquierdo-Barba, I.; Sakamoto, Y.; Terasaki, O.; Vallet-Regí, M. Chem. Mater. 2006, 18, 3137-3144. (35) Sanchez, C. m.; Belleville, P.; Popalld, M.; Nicolea, L. Chem. Soc. Rev. 2011, 40, 696-753. (36) Hartmann, M.; Schwieger, W. Chem. Soc. Rev. 2016, 45, 3311-3312. 17
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
501 502 503 504 505 506 507 508 509 510 511 512 513 514 515 516 517 518 519 520 521 522
(37) Nischang, I.; Causon, T. J. TrAC Trends Anal. Chem. 2016, 75, 108-117. (38) Sun, M. H.; Huang, S. Z.; Chen, L. H.; Li, Y.; Yang, X. Y.; Yuan, Z. Y.; Su, B. L. Chem. Soc. Rev. 2016, 45, 3479-3563. (39) Nischang, I.; Bruggemann, O.; Teasdale, I. Angew. Chem. Int. Ed. 2011, 50, 4592-4596. (40) Ou, J.; Liu, Z.; Wang, H.; Lin, H.; Dong, J.; Zou, H. Electrophoresis 2015, 36, 62-75. (41) He, H. B.; Li, B.; Dong, J. P.; Lei, Y. Y.; Wang, T. L.; Yu, Q. W.; Feng, Y. Q.; Sun, Y. B. ACS Appl. Mater. Inter. 2013, 5, 8058-8066. (42) Cordes, D. B.; Lickiss, P. D.; Rataboul, F. Chem. Rev. 2010, 110, 2081-2173. (43) Zhang, H.; Ou, J.; Liu, Z.; Wang, H.; Wei, Y.; Zou, H. Anal. Chem. 2015, 87, 8789-8797. (44) Seo, M.; Hillmyer, M. A. Science 2012, 336, 1422-1425. (45) Saba, S. A.; Mousavi, M. P.; Buhlmann, P.; Hillmyer, M. A. J. Am. Chem. Soc. 2015, 137, 8896-8899. (46) Seo, M.; Kim, S.; Oh, J.; Kim, S. J.; Hillmyer, M. A. J. Am. Chem. Soc. 2015, 137, 600-603. (47) Higashihara, T.; Fukuzaki, N.; Tamura, Y.; Rho, Y.; Nakabayashi, K.; Nakazawa, S.; Murata, S.; Ree, M.; Ueda, M. J. Mater. Chem. A 2013, 1, 1457-1464. (48) Markiewicz, K. H.; Seiler, L.; Misztalewska, I.; Winkler, K.; Harrisson, S.; Wilczewska, A. Z.; Destarac, M.; Marty, J. D. Polym. Chem. 2016, 7, 6391-6399.
18
ACS Paragon Plus Environment
Page 18 of 28
Page 19 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
523
Figure captions
524
Scheme 1. Schematic approach for preparation of Ti4+-IMAC hierarchically porous
525
hybrid monoliths (HPHMs).
526
Figure 1. (a, b) Nitrogen sorption isotherms and (c, d) mesopores size distributions of
527
hybrid monoliths based on BJH analysis of the adsorption. Hybrid monoliths (a,c) II
528
and (b, d) VI.
529
Figure 2. SEM micrographs of hybrid monoliths (a, d) III, (b, e) VI and (c, f) VIII.
530
Figure 3. Macropores size distributions of hybrid monoliths (a) VI and (b) VIII by
531
MIP measurement.
532
Figure 4. FT-IR spectra of (a) vinylPOSS, (b) VPA, (c) PCL and (d) HPHM.
533
Figure 5. (a) Adsorption kinetics and (b) adsorption isotherms for pyridoxal
534
5’-phosphate hydrate by Ti4+-IMAC microspheres (▲), monolith III (■) and monolith
535
VI (○).
536
Figure 6. MALDI-TOF mass spectra of human serum (a) before and (b) after
537
enrichment by Ti4+-IMAC HPHM. (*) indicates phosphopeptides.
538
19
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
539 540 541
542 543
Scheme 1.
544 545 546 547 548 549 550
20
ACS Paragon Plus Environment
Page 20 of 28
Page 21 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
551 552 553 554 555 556 557 558 559 560 561 562 563 564 565
Figure 1.
21
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
566 567 568 569 570 571 572 573 574 575 576 577 578 579 580 581 582 583
Figure 2.
22
ACS Paragon Plus Environment
Page 22 of 28
Page 23 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
584 585 586 587 588 589 590 591 592 593 594 595 596 597 598 599 600 601 602 603 604 605 606 607
Figure 3.
23
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
608 609 610 611 612 613 614 615 616 617 618 619 620 621 622 623 624 625
Figure 4.
626 627 628 629 630 631 632 633 634 635 24
ACS Paragon Plus Environment
Page 24 of 28
Page 25 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
636
637 638
Figure 5.
639 640 641 642 643 644 645 646 647 648 649 650 651 652 653
25
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
654 655 656
Figure 6.
657
26
ACS Paragon Plus Environment
Page 26 of 28
Page 27 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
658 659
Table 1. Detail composition of prepolymerization mixtures and porous properties of
660
phosphate-functionalized hybrid monoliths Monolith
VPA a
PCL (%) b
before degradation I II III IV V VI VII VIII IX X
1:8 1:8 1:4 1:4 1:4 1:4 1:4 1:4 1:2 1:2
Pores volume (cm3/g)
Surface area (m2/g)
0 25.0 0 16.7 21.0 25.0 28.6 31.8 0 25.0
after degradation 501 502 440 409 438 473 413 406 368 360
195 ˗c ˗ 174 ˗ 154 97
0.32 0.32 0.28 0.26 0.28 0.35 0.27 0.29 0.25 0.29
661
a
The quantity of VPA was based on the vinyl group molar ratio of VPA/vinylPOSS.
662
b
All PCL content (w/w) was the ratio of the weight of PCL to the total weight of
663
vinylPOSS and PCL.
664
c
665
adsorption/desorption measurements.
The surface areas of hybrid monoliths had not been measured by nitrogen
666 667 668 669 670 671 672 673 674 675 676 677 678 27
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
679
for TOC only
680 681
28
ACS Paragon Plus Environment
Page 28 of 28