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Ultra-fast Screening of a Novel Moderate Hydrophilic Angiotensin Converting Enzyme Inhibitory Peptide RYL from Silkworm Pupa Using Fe-doped Silkworm Excrement Derived Biocarbon: Waste Conversion by Waste Long Liu, Yanan Wei, Qing Chang, Huaju Sun, Kungang Chai, Zuqiang Huang, Zhenxia Zhao, and Zhongxing Zhao J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.7b04442 • Publication Date (Web): 07 Dec 2017 Downloaded from http://pubs.acs.org on December 12, 2017
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Journal of Agricultural and Food Chemistry
Ultra-fast Screening of a Novel Moderate Hydrophilic Angiotensin Converting Enzyme Inhibitory Peptide RYL from Silkworm Pupa Using Fe-doped Silkworm Excrement Derived Biocarbon: Waste Conversion by Waste Long Liu, Yanan Wei, Qing Chang, Huaju Sun, Kungang Chai, Zuqiang Huang, Zhenxia Zhao, and Zhongxing Zhao*1 Guangxi Colleges and Universities Key Laboratory of New Technology and Application in Resource Chemical Engineering, School of Chemistry and Chemical Engineering, Guangxi University, Nanning 530004, China
1*
Corresponding Authors Phone +86-771-3233718; fax +86-771-3233718; e-mail
[email protected] (Zhongxing Zhao) 1
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ABSTRACT: A novel moderate hydrophilic peptide (RYL) with high ACE inhibitory
2
activity was ultra-fast screened via a concept of waste conversion using waste. This
3
novel peptide was screened from silkworm pupa using Fe-doped porous biocarbon
4
(FL/Z-SE) derived from silkworm excrement. FL/Z-SE possessed magnetic property
5
and specific selection for peptides due to Fe’s dual functions. The selected RYL with
6
moderate hydrophilicity (LogP =-0.22) exhibited a comparatively high ACE
7
inhibitory activity (IC50=3.31±0.11 µM). Inhibitory kinetics and docking simulation
8
results show that, as a competitive ACE inhibitor, RYL formed 5 hydrogen bonds with
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ACE residues in S1 and S2 pockets. In this work, both of screening carbon material
10
and selected ACE inhibitory peptide were derived from agricultural wasters (silkworm
11
excrement and pupa), and it offers a new way of thinking for development of
12
advanced utilization of the silkworm by-product/waster.
13 14 15
KEYWORDS: silkworm pupa protein, silkworm excrement, moderate hydrophilic
16
peptide, ACE inhibitory activity, ultra-fast screening, molecular docking
17
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■ Introduction
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Hypertension has been one of the major cardiovascular diseases that seriously affects
20
people’s health.1 One of the most commonly used anti-hypertensive therapies is an
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inhibitor of angiotensin-converting enzyme (ACE). It can effectively control blood
22
vessels and decrease blood pressure.2 Currently, purification ACE inhibitor peptides
23
with high bioactivity from natural sources are attracting more attention than the
24
development of synthetic drugs due to their fewer side effects.3
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Many researches have shown that many selected peptides having high ACE
26
inhibitory activity from new natural sources are known as be composed entirely or
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partly of more hydrophobic amino acids. For instance, VVLTK and FQPS were
28
separated from plant proteins with IC50 values of 53.394 and 27.0 µM,5 respectively.
29
PAFG, MPFLKSPIVPF and AHLL purified from marine sources had the IC50 value of
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35.9,6 1.717 and 13.5 µM.8 MPFLKSPIVPF derived from a food source possessed the
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IC50 value of 27.0 µM.9 Many selected peptides having good ACE inhibitory function
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exhibit hydrophobic property to our knowledge. However, hydrophobic peptides
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usually have low solubility and high aggregation in water solution. It will strongly
34
decrease their physiological functions,10-12 drug absorption and bioavailability,13 and
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the reaction efficiency of chemical catalysis.14, 15 Thus, exploration of some moderate
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hydrophilic peptides with high ACE inhibition activity has attracted increasing
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scientific attention.
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Adsorption and separation strategy using porous materials, including affinity
39
separation, magnetic separation and porous adsorption, facilitates rapid screening
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peptides with specific activity from protein hydrolysates.16,17 Porous materials, as the
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core of adsorption approach, can be efficiently captured peptides with specific
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property by their surface and pore physical properties. Jiang and co-workers18 3
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prepared Fe3O4@SiO2@graphene microspheres to enrich bioactive peptides at low
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concentrations with high efficiency. Hippauf et al.19 employed microporous activated
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carbons to isolate ACE inhibitory peptides from lactalbumin hydrolysates, and
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obtained a sixfold-concentrated the selected ACE-inhibitors. So far, these researches
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are mainly focused on selection of peptides through molecular sieving effects.
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However, few reports have been published on peptide selective adsorption based on
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surface property of adsorbents.
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Silkworm industry is very developed in China's western region and other East
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Asian countries. Herein, we proposed to synthesize a Fe-bifunctional porous
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biocarbon using a silkworm waste (silkworm excrement, SE) to high-throughput
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screen peptide for ACE inhibition from another silkworm waste (silkworm pupa
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protein, SP). We used “waste” protein source via “waste” material to acquire a novel
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peptide with high ACE inhibitory activity. The high surface biocarbon was further
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modified by Fe elements doping (FL/Z-SE), which enables sample to have surface
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acidity and magnetic dual functions. The unique surface makes us realize a rapid
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capture and separation of moderate hydrophilic peptides from a complex mixed
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hydrolysis process. The novel ACE inhibitory peptide (RYL, LogP =-0.22) was
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quickly isolated and identified by using FL/Z-SE separation and matrix-assisted laser
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desorption/ionization time-of-flight tandem mass spectrometry (MALDI-TOF-TOF),
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respectively. Its ACE inhibition pattern and ACE inhibition mechanism of RYL were
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then systematically studied by the classic Lineweaver-Burk model and molecular
64
docking. Herein, both of separation carbon material (Fe-C) and selected ACE
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inhibitory peptides were derived from silkworm wasters (silkworm excrement and
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pupa). It was then a promising alternative for replacement of the current high-cost and
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tedious peptides screening process and purification. Besides, it offers a new way of 4
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thinking for development of advanced utilization of the silkworm by-product/waster.
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■ Materials and Methods
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Reagents. Silkworm excrement purchased from Yi Zhou farmer (China). Neutral
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protease (AS1.398, 60 U/mg) was provided by Pangbo Biological Engineering Co.,
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Ltd. (Nanning, China). ACE from rabbit lung, hippuryl-L-histidyl-L-leucine (HHL),
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bovine serum albumin, ovalbumin, cyyochrome, insulin and vitamin B12 were offered
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from Sigma-Aldrich Chemical Co., Ltd. (St. Louis, MO). Pepsin from porcine gastric
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mucosa was supplied by Coolaber Science & Technology Co., Ltd. (Beijing, China),
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and pancreatin from porcine pancreas was offered by Shanghai Yuanye
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Bio-Technology Co., Ltd. (Shanghai, China). Methanol and acetonitrile for HPLC
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analysis were supplied by Thermo Fisher Scientific Co., Ltd. FeCl2·4H2O (AR, 99.0%)
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and ZnCl2 (AR, 99.0%) were supplied by Aladdin Industrial Co. Ltd. (Shanghai,
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China). The ultrapure water purified via the Smart-S15UV (18.2 MegaOhm-cm,
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Hitech Instruments Co., Ltd, Shanghai, China) was used throughout the experiments.
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All starting materials were commercially available reagents of analytical grade and
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used without further purification.
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Synthesis of Z-SE, FL/Z-SE, and FH/Z-SE Materials. Silkworm excrement (SE) was
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first washed with deionized water, filtered and dried at 110 °C overnight. Then, the SE
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was crushed to uniform particles in the range of 1-2 mm. 2.00 g of SE sample was
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first immersed a certain weight ratio of ZnCl2/FeCl2 solution for 8 h, followed by
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freeze-drying process to contain the original three-dimensional morphology. After that,
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the frozen SE was heated to 900 °C at a rate of 5 °C/min and maintained at this
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temperature for 2 hours under N2 atmosphere. Finally, activated samples were washed
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with 1.0 M HCl and 10% HF to remove the unconjugated iron, ZnO and SiO2. The
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corresponding FL/Z-SE and FH/Z-SE were designated as adjusting weight ratio of 5
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FeCl2/ZnCl2 equal to 0.5/1.0 and 1.0/1.0, respectively. For comparison, the porous
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biocarbon (Z-SE) without loading irons was also prepared in this work. The synthesis
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procedure of Z-SE was the same as that of FH/Z-SE expect for not adding FeCl2
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during the activation process.
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Physical Characterization. The morphologies of the synthesized materials were
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surveyed by a scanning electron microscope and a field-emission scanning electron
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microscope equipped with an energy dispersive X-ray spectrometer (SEM-EDX,
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Hitachi S-3400N). Powder X-ray diffraction (XRD) measurements were performed on
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a X-ray spectrometer (Rigaku) with Cu Ka radiation (λ=1.5406 Å). Specific surface
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area and pore size distribution were calculated on the basis of nitrogen physical
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adsorption with a Micromeritics ASAP 2460. Zeta potential and dynamic light
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scattering (DLS) were measured using a MALVERN Zetasizer Nano ZS90
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(Brookhaven NanoBrook Omni). The magnetic properties were analyzed on a
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Physical Property Measurement System PPMS-9 (Quantum Design).
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Assay of ACE Inhibition. ACE inhibitory activity assay was performed by
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measuring the concentration of hippuric acid liberated from hippuryl-histidyl-leucine
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(HHL) according to the method described by Cushman and Cheung20 with slight
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modifications. HHL was first dissolved in a 100 mM borate buffer (pH 8.3)
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containing 300 mM NaCl. Rabbit lung ACE was dissolved in the same buffer solution
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at a concentration of 10 mU·mL-1. After that, 40 µL of ACE solution and a certain
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concentration of peptide or their mixture solution (200 µL) were pre-incubated at
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37 °C for 10 min and the mixture was subsequently incubated with 10 µL of HHL
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solution for another 30 min at the same temperature. The reaction was then terminated
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by adding 50 µL of 1.0 M HCl. Finally, 20 µL of the solution injected directly onto a
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Zorbax SB C18 column (4.6 mm×150 mm, particle size 5 µm; Agilent) to detect the 6
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product, hippuric acid (HA) from HHL. The column was eluted with 15% methanol
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(in water, v/v) containing 0.1% trifluoroacetic acid (TFA) with flow rate of 1.0
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mL/min and absorbance of the eluate measured at 228 nm. ACE Inhibition activity (I,
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percent) is calculated by using the following equation:
=
− −
(1)
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where Ae is the relative area of HA peak generated without ACE inhibitors, Af is the
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relative area of HA peak generated in the presence of purified peptides, and Ab is the
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relative area of HA peak generated without ACE and purified peptides. The IC50 value
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defined as the concentration of inhibitor (millimolar) required to inhibit 50% of ACE
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activity, which was determined by regression analysis of ACE inhibition versus
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peptide concentration.
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Purification of ACE Inhibitory Peptides. The preparation of the SPP hydrolysate
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with neutral protease was already described elsewhere.21,22 The lyophilized SPP
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hydrolysate was dissolved in ultrapure water, and 10 mg of Z-SE, FL/Z-SE and
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FH/Z-SE was mixed with 1 mg/mL SPP hydrolysate at a ratio of 1:1 (w/v) and stirred
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at 30 °C for 15 min. Then, the FL/Z-SE was recovered through a magnet and washed
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three times with ultrapure water. After that, the adsorbed peptides were desorbed from
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the adsorbed FL/Z-SE by using absolute ethanol.
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The eluent with highest inhibitory activity was concentrated and freeze-dried and
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then was further separated on a Zorbax SB C18 column by RP-HPLC (Agilent 1260).
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The column was eluted by a linear gradient of acetonitrile (5-25%) containing 0.1%
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TFA at a flow rate of 0.50 mL/min within 60 min. The absorbance of the elution was
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monitored at 220 nm with diode array detector (DAD). The fractions collected from
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HPLC were lyophilized for further assay of ACE inhibitory activity. Subsequently, the
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lyophilized fraction with the highest ACE-inhibitory activity was purified by using the 7
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second step HPLC, eluting with 8% acetonitrile in water (v/v) containing 0.1% TFA at
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a flow rate of 0.50 mL/min. These fractions were collected and lyophilized to powder
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for further measurement of their ACE inhibitory activities and sequence identification.
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Characterization of Purified Peptide. Accurate relative molecular mass and amino
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acid sequence of the purified peptide (peptide A) with the highest ACE inhibitory
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activity were determined on a 4800 plus MALDI-TOF/TOF analyzer (Applied
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Biosystems, Beverly, MA). Spectra were acquired on a matrix-assisted laser
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desorption/ionization time-of-flight (MALDI-TOF) mass spectrometer with a 337 nm
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pulsed nitrogen laser (2 ns pulse duration, 3 Hz repetition rate). The purified peptides
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mass spectra were acquired in linear positive ion mode at a mass range of m/z 50 to
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500.
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Kinetics of ACE Inhibition. To determine the ACE inhibitory mechanism of
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inhibitory peptide A, kinetics of ACE inhibition was established by varying the
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concentration of the enzyme substrate HHL (1.044, 1.392, 1.740, and 2.088 mM) in
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the absence and presence of two different concentrations of inhibitory peptide (25.31
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µM and 50.27 µM).23, 24 The kinetics of ACE in the presence of the inhibitory peptide
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was determined using Lineweaver-Burk plots, where the reciprocal of HHL
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concentration is used as an independent variable (x-axis) and the reciprocal of
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production rate of HA as a dependent variable (y-axis). The inhibitory constants ( )
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was determined as the intercept of the Lineweaver-Burk lines.
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Molecular Docking. The structure of peptide A was constructed using Sybyl
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X-2.1.1 (Tripos International, St. Louis, MO), and the structure was energy minimized
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using the Powell conjugate gradient optimization algorithm with the Tripos force
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field.25 The crystal structure of human ACE-lisinopril (1O86) complex was obtained
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from the Protein Data Bank (http://www.rcsb.org/pdb/home/home.do). Before the 8
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docking, water molecules and the inhibitor lisinopril were removed, whereas the
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cofactor zinc atom was retained in ACE model. Then the protein structure was
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preanalyzed and prepared for the docking runs using the biopolymer structure
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preparation tool with default settings and the protomol was created by automatic. The
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Surflex-Dock program was used for docking studies. During the docking process, the
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parameter of additional starting conformation per molecule is 5, considering ring
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flexibility, and default settings for the rest. The binding affinity of the ligand is
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predicted by the software in terms of total score, which is expressed as LogKd, where
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Kd is the binding constant. A high value of total score indicates good protein-ligand
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binding.
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Statistical Analysis. All assays of ACE inhibitory activity were conducted in
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triplicate. Data were presented as mean ± standard deviation. Statistical analysis was
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performed in MS Excel (Microsoft Windows 2003) by use of Student’s t-test.
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Significant difference in means between the samples were determined at a 5%
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confidence level (p < 0.05).
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■ Results and Discussion
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Physical Characteristics. Figure 1 shows the SEM images and elemental
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compositions of SE, Z-SE, FL/Z-SE, and FH/Z-SE. The original silkworm excrement
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(SE) had a very smooth surface with regular wrinkle structure (Figure 1A). After the
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SE was activated by ZnCl2 at 900 °C, its morphology of surface wrinkles disappeared
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on Z-SE, and many holes with various sizes appeared on the sample surface (Figure
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1B). After being treated with FeCl2 and ZnCl2 at 900 °C, a honeycomb-like surface
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with large numbers of tiny holes appeared over the entire samples (FL/Z-SE and
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FH/Z-SE, Figure 1C-D). From element analysis in Figure 1, the original SE was
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mainly composed of carbon, nitrogen and oxygen elements, similar to other natural 9
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biomass materials. During activated process, large amount of oxygen groups was
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removed from original SE substrate, resulting in C element enrichment in three
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activated samples. Oxygen content presents an obvious decrease after being activated
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by ZnCl2 as activator. The ZnCl2 and FeCl2 activation process can generate Fe3C
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bonds on the carbon surfaces, and the content of Fe element in FH/Z-SE apparently
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more than that in FL/Z-SE accompany with the increase of adding FeCl2 amount.
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Figure 2 shows the PXRD patterns of the original SE, Z-SE, FL/Z-SE and FH/Z-SE
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samples. Four sharp diffraction peaks at 15.23/24.65º and 26.79/29.32º appeared in
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the original SE sample, which represented the species of CaCO3 and SiO2 in SE
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sample. These species might derive from silkworms’ food. Thus, we used water and
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hydrofluoric acid (HF) to remove these useless impurities afterwards. After being
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treated with Fe/Zn chlorides, some new and sharp peaks appeared in the patterns of
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FL/Z-SE and FH/Z-SE samples. It can be attributed to characteristic diffraction peaks
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of iron carbide (Fe3C/Fe5C2) and α-Fe26 respectively, indicating the formation of Fe-C
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structure. Besides, there were two broad peaks locating at 23º and 43º in three
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obtained samples, which corresponded to the (002) and (100) crystal planes of a
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typical graphitic structure.27
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Nitrogen adsorption/desorption isotherms and the physical properties of Z-SE,
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FL/Z-SE and FH/Z-SE are displayed in Figure 3 and Table 1, respectively. As shown,
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all of the Z-SE, FL/Z-SE and FH/Z-SE showed a type IV isotherm with hysteresis
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loop (H4) in Figure 3A. It indicated a typical hierarchical structure with micropores
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and mesopores. Z-SE showed a remarkable hysteresis loop from the N2 isotherm as
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evidence of more mesopores. Its BET surface areas and total volume were
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respectively calculated to be 1415.5 m2/g and 1.03 cm3/g. Its micropore area and
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micropore volume were only 350.8 m2/g and 0.14 cm3/g. After adding FeCl2 specie 10
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for activation, the surface area was decreased to a variable extent in FL/Z-SE and
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FH/Z-SE. It was probable that these species tend to aggregate into large particles and
219
led to a possibility of pore blocking resulting in reduced surface area. Clearly, low
220
content of FeCl2 did not much affect the surface area. However, the surface area
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suffered a sharp decline when the ratio of Fe/Zn increasing to 1:1 in FH/Z-SE. Figure
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3B shows the pore size distribution of these three samples. All of the samples
223
displayed very similar profile of pore size distribution. According to the DFT
224
calculation, the pore sizes were mainly concentrated at 5.0, 6.5-7.8, 11.6 and 27.4 Å,
225
possessing micropores and mesopores. From Table 1, although the pore size
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distribution was almost similar in these three samples, both of the micropore surface
227
area and pore volume were significantly increased with adding amount of FeCl2.
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These phenomena were possibly ascribed to the two functions of Fe species during
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carbonization process. Ferrous chloride could react with microcrystalline carbon on
230
the edge, and generate the micropore structure in iron-containing SE samples.
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Moreover, Fe species were reduced to Fe3C and Fe5C2 and 0-valent iron in the process
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of high-temperature carbonization. Another possibility might be that these new
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micropores came from the partly-blocked mesopores by reduced Fe species.
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Figure 4 shows the zeta potential and particle size of Z-SE, FL/Z-SE and FH/Z-SE.
235
The surface charges (ζ potential) of the Z-SE, FL/Z-SE and FH/Z-SE samples were
236
-24.66, -6.77 and 5.93 mV in water solution, respectively. The surface charge shows
237
an apparent rise with increasing Fe species in the sample. This indicated that iron
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species in FH/Z-SE and FL/Z-SE enhanced the surface positive charge density.
239
Subsequently, the particle size and aqueous stability of Z-SE, FH/Z-SE and FL/Z-SE
240
were further tested, and the result data are also shown in Figure 4. As seen, FH/Z-SE
241
and FL/Z-SE (~550 nm) had larger particle size than Z-SE (490 nm). Their particle 11
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sizes did not show the notable difference among these three samples. However, their
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soluble stability in water was significantly different. Z-SE suspension had almost
244
precipitated off and the water solution with Z-SE sample became clear quickly. On the
245
contrary, iron-containing Z-SE particles (FH/Z-SE and FL/Z-SE) were found to be
246
more stable under similar condition. Considering the similar particle size of these
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samples, FH/Z-SE and FL/Z-SE exhibited much higher compatibility with water than
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Z-SE sample (inset photographs of Figure 4), which may be ascribed to their
249
enhanced hydrophilic property of carbon surface. The decoration of Fe specie
250
increased ‘Lewis acidity’ sites of carbon surface,28 and thus increased surface local
251
polarity to a certain extent compared to Z-SE. Therefore, the Fe-containing Z-SE
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sample possesses two main adsorption sites: (1) hydrophobic (non-polar) sites on the
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graphitic carbon surface and (2) acid/hydrophilic (polar) metal sites. These active
254
adsorption sites will tend to adsorb some moderate hydrophilic peptides containing
255
basic and phenyl groups.29
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The magnetic properties of FL/Z-SE and FH/Z-SE were determined by a vibrating
257
sample magnetometer (VSM) and the results are shown in Figure 5. Both of these
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samples could not be observed obvious remanence and coercivity, signifying a
259
superpara-magnetism property of these Fe-C materials. Saturation magnetization
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values of FL/Z-SE and FH/Z-SE were 21.49 and 35.64 emu g/L at room temperature,
261
respectively. Apparently, FH/Z-SE exhibited a much higher saturation magnetization
262
than FL/Z-SE mainly due to the higher content of Fe in carbon materials. As shown in
263
inset photographs of Figure 5, with an external magnet, the homogeneous dispersion
264
of FH/Z-SE (sample 1) and FL/Z-SE (sample 2) microparticles could be separated
265
quickly from the solution and formed aggregates in only 10 s. The aggregate was
266
easily redispersed into the solution quickly after removing the magnet. Thus, similar 12
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to magnetic Fe3O4 nanoparticles, Fe-C (Fe3C/Fe5C2) carbons also possessed excellent
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magnetic responsivity and redispersibility, which is beneficial for peptides fast
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separation and screening.
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Rapid Screening of ACE Inhibitory Peptides with Fe-C Porous Carbon. The
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influence of adsorption time of three synthesized carbon samples on their fractional
272
residual amount of peptides was shown in Figure 6A. The fractional residual amount
273
of peptides in three solutions with different carbon adsorbents remained nearly
274
constant after 10 min. That means all peptides showed very fast adsorption kinetics,
275
which enabled samples to achieve equilibrium within very short time (10 min). The
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fast equilibrium may be attributed to two reasons: (1) the high adsorption affinity
277
between carbon surface and the adsorbed peptides with similar property,30 and (2)
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hierarchical pore size distribution with small diffusion resistance for peptides.29
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Besides, Fe-doped samples (FL/Z-SE and FH/Z-SE) had slightly lower fractional
280
adsorbed peptides in comparison to Z-SE samples, and their adsorbed amount showed
281
a similar trend with sample’s specific surface area (Table 1). Selective adsorption of
282
peptides with bioactivity or specific function is considered as a more crucial factor
283
except for the sample’s adsorption capacity. ACE inhibitory activity and relative
284
adsorbed amount within 10 min of Z-SE, FL/Z-SE and FH/Z-SE were shown in
285
Figure 6B. Surprisingly, the FL/Z-SE sample with lower Fe content exhibited the
286
highest ACE inhibitory activity, whose value increased to 2-fold of the original SPP
287
hydrolysate under similar tested conditions. In this regard, pore structure and surface
288
property are critical to determine to screen peptides with high bioactivity.
289
Pore size distribution and surface functional groups were also investigated to
290
understand the selection strategy of the FL/Z-SE sample. From Figure 7A, it can be
291
seen that FL/Z-SE was mainly composed of ultra-micropores (5.5, 6.6 and 8.3 Å), 13
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micropores (11.3 and 15.3 Å) and a wide mesopores distribution from 17-39 Å. These
293
peaks almost disappeared except for one at 12.7 Å in the peptide-adsorbed sample.
294
Obviously, only small chain peptides not exceeding 39 Å could be selected and
295
adsorbed on FL/Z-SE sample. The specific surface area of FL/Z-SE dramatically
296
dropped from 1396.1 to 150 m2/g after adsorbing peptides (Figure S1 and Table S1).
297
Ultramicropores of FL/Z-SE (< 10 Å) were completely filled with these small
298
peptides. Moreover, size-exclusion chromatography (SEC) was used to analyze these
299
adsorbed peptides from FL/Z-SE. For comparison, the SEC spectrum of SPP
300
hydrolysates before and after being adsorbed using FL/Z-SE were also present in
301
Figure 7B. The eluate SPP hydrolysate showed an obvious enhancement of peak
302
intensity between molecular weight of 73-799 Da and a weakness of peak intensity in
303
the region of 1390-4200 Da compared with original counterpart. It is suggested that
304
FL/Z-SE was preferably adsorbed some peptide fractions with low molecular weights
305
due to its pore size screening, and thus those peptides with high molecular weights
306
were excluded.31 As expected, the peptides with small molecule from FL/Z-SE sample
307
have high ACE inhibitory activity, and it is in accordance with previous reports.32,33
308
Besides their length of peptide chain, the hydrophobic/hydrophilic character of
309
peptides is also very crucial for their ACE inhibitory activity as well as their
310
biocompatibility.34 Moderate hydrophilic peptides with a certain ratio of hydrophobic
311
amino acid chains are considered to be ideal ACE inhibitors. Therefore, we prepared
312
hydrophobic porous carbon containing hydrophilic adsorption sites (Lewis acid Fe
313
ions) to screen moderate hydrophilic peptides from SPP hydrolysate.
314
To better understand the mechanism underlying the selective adsorption of the
315
obtained carbons, we next employed X-ray photoelectron spectroscopy (XPS)
316
analysis to investigate carbon component and surface properties of the carbon Z-SE 14
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317
and FL/Z-SE samples (Figure 8). Both of these two carbons (Z-SE and FL/Z-SE)
318
showed a high proportion of Sp2 C, indicating a relative higher graphitized carbon
319
structure than common activated carbon.35 After Fe species being doped in Z-SE,
320
some notable changes had taken place in their XPS spectra. First, the ratio of Sp2
321
C/Sp3 C was further increased due to the graphitization of amorphous carbon
322
catalyzed by Fe metal (Figure 8B).26 Second, the peaks of the FeC-like structures
323
(Fe3C) at 282.3 eV appeared in the FL/Z-SE (Figure 8B). Third, the concentration of
324
oxygen groups was significantly decreased in Fe-doped Z-SE. Thus, it can be deduced
325
that FL/Z-SE surface properties represented more heterogeneous surface containing
326
hydrophobic graphitic carbon36 and hydrophilic “Lewis acid” Fe37 in comparison to
327
Z-SE surface property. Based on the principle of high affinity between adsorbate with
328
adsorbent having similar property, the FL/Z-SE is hypothesized to prefer adsorbing
329
peptides with short and moderate hydrophilic chains. This was consistent with the
330
screening result showing from the above size-exclusion chromatography (Figure 7B).
331
HPLC Purification of ACE Inhibitory Peptides. The adsorbed peptides on FL/Z-SE
332
were eluted and then purified fraction with SB C18 column with gradient elution.
333
Figure 9A shows the reverse-phase gradient HPLC chromatogram of the SPP
334
hydrolysate elutes from FL/Z-SE, which was divided into 10 fractions named from
335
FSP-1 to FSP-10 according to retention time. Their ACE inhibitory activities were
336
tested at each fraction concentration of 80 mg/L and shown in Figure 9B. From Figure
337
9B, it can be observed that FSP-5 fraction exhibited the highest ACE inhibitory
338
activity with a value of 81.23 ± 3.15%, and thus was chosen for further purification
339
using the second RP-HPLC.
340
Figure 10 shows the chromatogram of FSP-5 fraction and their ACE inhibitory
341
activities. Another 4 fractions corresponding to four peaks were separated and named 15
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342
as FSP-5x (x from 1 to 4) in Figure 10A. Among these four fractions (each fraction
343
concentration of 60 mg/L), FSP-53 possessed the highest ACE inhibitory activity with
344
a value of 78.44 ± 2.40% (Figure 10B). RP-HPLC technique is an important way to
345
separate peptide compounds with different polarities through non-polar stationary
346
phase.38 Based on this theory, the selected fractions of FSP-5 and FSP-53 with highest
347
ACE inhibitory activities were both obtained at the middle position of the whole
348
HPLC. From this, it can be deduced that some peptides with potential ACE inhibitory
349
activity come from some polar fractions containing greater amounts of hydrophilic
350
amino acids. Most amino acids are made of two parts: (1) typical hydrophilic
351
amino/carboxyl groups and (2) some other hydrophobic (benzene or alkyl) groups or
352
hydrophilic (N, O-containing) groups. Thus, Fe doping was proposed to modulate
353
hydrophilic surface and polarity, so that it can screen some moderate polar peptides
354
rather than high hydrophobic peptides from SPP hydrolysate source.
355
Identification of ACE Inhibitory Peptide by MALDI-TOF/TOF MS. The molecular
356
mass and amino acid sequence of fraction FSP-53 were identified by
357
MALDI-TOF/TOF MS and shown in Figure 11. The molecular mass of fraction
358
FSP-53 was determined to be of 452.55 Da. On the basis of this molecular mass and
359
tandem MS, the amino acid sequence was identified as Arg-Tyr-Leu (RYL), which is
360
a novel ACE-inhibitory peptide from silkworm pupa protein with the IC50 value of
361
3.31 ± 0.11 µM. The IC50 value was comparatively similar to some other peptides
362
GNPWM (IC50 = 21.70 µM) and GAMVVH (IC50 = 19.39 µM) obtained from the
363
same source (silkworm pupa protein).32
364
Comparison Adsorption Capacities of Different Tripeptides on FL/Z-SE.
365
LogP-value can be used to represent the hydrophobic/hydrophilic property of some
366
small molecules, whose definition is described in Eq. 2.39,40 As seen in this Eq. 2, 16
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367
negative value of LogP means the molecule having hydrophilic behavior, while
368
positive value means the molecule having hydrophobic behavior. Thus, we calculated
369
the LogP value of the identified RYL using ChemDraw Software V15.0 (Cambridge
370
Soft), and its value was about -0.22 presenting a moderate hydrophilic peptide. LogP = Log
Cn − octanol C water
(2)
371
where Cn−octanol and C water mean the concentration of peptide in n-octanol and water
372
solvent, respectively.
373
To further investigate influence of hydrophilic property of peptide on selective
374
adsorption on the synthesized FL/Z-SE. One designed experiment was carried out to
375
explore the relationship between LogP-value of tripeptides with similar molecular
376
weights and their corresponding adsorption capacity on FL/Z-SE. Figure 12 shows the
377
adsorption capacities of five selected tripeptides (FYL, RYF, RYL, RYM and RYN)
378
with different LogP-values on FL/Z-SE. As shown, the adsorption capacities of these
379
peptides display a volcano trend with the increase of LogP value. It indicated that the
380
FL/Z-SE is inappropriate to adsorb peptides having either strong hydrophilicity or
381
hydrophobicity. As expected, the moderate hydrophilic peptides RYL (LogP = -0.22)
382
possessed the highest adsorption capacity (1.21 mmol/g) among these selected
383
peptides on FL/Z-SE. The strong hydrophilic and hydrophobic peptides had
384
significantly lower adsorbed capacity (0.64 and 0.77 mmol/g). This consequence can
385
be attributed to the synergistic effect of hydrophobic graphitic carbon and hydrophilic
386
“Lewis acid” Fe on FL/Z-SE surface. The amphiphilic property of FL/Z-SE could
387
efficiently enhance the selective enrichment for moderate hydrophilic peptides from
388
hydrolysates, which was verified the XPS results in Figure 8.
389
Inhibition Pattern of the Inhibitory Peptide. To elucidate the mechanism of ACE 17
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390
inhibition, Lineweaver-Burk plot was used to determine for the inhibitory peptides
391
(RYL). As shown in Figure 13, the plot with coinciding intercept on the 1/S axis
392
indicate that RYL was competitive type of inhibition, which means that the bioactive
393
peptide (RYL) binding to the same catalytic site of ACE-HHL on the ACE molecule
394
to produce an inactive complex (enzyme-substrate-inhibitor).41 In general, lower
395
values indicate higher affinity and more potent inhibitory activity. The calculated
396
inhibition constant ( ) value of RYL was 1.4×10-5 M. In this case, the value of
397
RYL was clearly lower than some reported values of hemp protein hydrolysates
398
(6.0-8.9×10-4 M)42 and terminalia chebula retz protein hydrolysate (2.81×10-5 M).43
399
Thus, RYL has a potential ACE inhibitory capacity.
400
Molecular Docking. To further investigate the inhibition mechanism of inhibitor
401
(RYL) towards ACE, docking simulation with Sybyl X-2.1.1 was used to carry out in
402
this system. Figure 14A showed the interaction between RYL and ACE. As shown, the
403
RYL formed 5 hydrogen bonds with ACE residues, including Gln281 (2.0 Å), Lys511
404
(1.8 Å), Tyr520 (1.9 Å), Glu384 (2.1 Å) and Ala354 (2.1 Å), respectively. These
405
positions were mainly belonged to the active sites of S1 and S2 pockets from ACE.
406
We also used the same way to investigate the molecular docking between ACE and
407
HHL (Figure 14B). Docking result showed that HHL was found to form hydrogen
408
bonds with ACE residues on similar positions, which were Gln281 (1.8 Å), Ala354
409
(2.1 Å), His513 (2.1 Å) and Tyr520 (1.8 Å), respectively.44 Clearly, the selected RYL
410
would efficiently occupy some high active sites of ACE, and inhibited its bound with
411
HHL. This was consistent with RYL’s inhibition pattern from the inhibition kinetics
412
result.
413 414
■ Supporting Information 18
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415
Isotherms of nitrogen adsorption for FL/Z-SE before and after addition of protein
416
hydrolysate; physical properties for FL/Z-SE before and after adsorbed protein
417
hydrolysate.
418 419
Funding
420
This work was financially supported by National Natural Science Foundation of
421
China (No. 31401629, 21666004, 21676059 and 21606054), Guangxi Distinguished
422
Experts Special Foundation of China, Natural Science Foundation of Guangxi Zhuang
423
Autonomous
424
2017GXNSFFA198009), Scientific Research Foundation of Guangxi University (No.
425
XGZ130963) and Innovation and Entrepreneurship Training Program of Guangxi
426
Zhuang Autonomous Region (No. 201710593185).
Region,
China
(No.
2016GXNSFAA380229
and
427 428
Notes
429
The authors declare no competing financial interest.
430 431
■ Acknowledgments
432
We appreciate helpful suggestions from Dr. Wei Hu of state Key Laboratory for
433
Conservation and Utilization of Subtropical Agro-bioresources.
434 435
■ References
436
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Figure captions
Figure 1
SEM images and element contents of (A) SE, (B) Z-SE, (C) FL/Z-SE, and (D) FH/Z-SE.
Figure 2
PXRD patterns of (A) SE and (B) Z-SE, FL/Z-SE and FH/Z-SE.
Figure 3
(A) Isotherms of nitrogen adsorption/desorption and (B) DFT pore size distributions for Z-SE, FL/Z-SE and FH/Z-SE composites.
Figure 4
Zeta potentials and particle sizes of Z-SE, FL/Z-SE and FH/Z-SE at the concentration of about 0.1 mg/mL.
Figure 5
Magnetic hysteresis curves of FL/Z-SE and FH/Z-SE.
Figure 6
(A) Effects of adsorption time on residual fraction of peptides fractions and (B) fractional adsorbed amounts and the corresponding ACE inhibitory activity of peptides from protein hydrolysates eluted from Z-SE,
FL/Z-SE
and
FH/Z-SE
samples
(concentration
of
hydrolysate/elute: 1.00 g/L) Figure 7
(A) DFT pore size distributions for FL/Z-SE before and after addition of protein hydrolysate and (B) SEC of untreated silkworm pupea protein hydrolysate (dashed line) and the enriched eluate fraction from FL/Z-SE after elution (straight line).
Figure 8
High-resolution C1s XPS spectra of (A) Z-SE and (B) FL/Z-SE samples.
Figure 9
(A) Chromatogram of SPP hydrolysate elute from the FL/Z-SE and (B) their ACE inhibitory activities of the separated ten peptide fractions (concentration of each FSP fraction was ~80 mg/L).
Figure 10
(A) Chromatogram of FSP-5 fraction and (B) their ACE inhibitory 27
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activities of the separated four peptide fractions (concentration of each FSP-5x fraction was ~5 mg/L). Figure 11
Identification of molecular mass and amino acid sequence of the purified peptide. MS/MS spectrum of molecular ion m/z 452.55 Da.
Figure 12
Comparison between capacities of FL/Z-SE towards different tripeptides, starting concentration C0 = 1 mM, adsorbent mass mFL/Z-SE = 5 mg, volume of the liquid phase V0 = 25 mL, Temperature T = 23 °C.
Figure 13
Inhibition kinetic curves of ACE by inhibitory RYL.
Figure 14
Predicted binding modes between ACE and inhibitor RYL (A) or substrate HHL (B) after being docked at the ACE active site. The residues of ACE were shown as line, the inhibitor and substrate were shown as stick, and the hydrogen bond was shown as yellow dashed lines.
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Table Table 1 Physical properties of Z-SE, FL/Z-SE and FH/Z-SE samples Sample
BET
Langmuir
surface area
SMeso/SMicro
Pore
Micropore
surface area
volume
volume
(m2/g)
(m2/g)
(mL/g)
(mL/g)
Z-SE
1415.5
1671.1
3.04
1.03
0.14
FL/Z-SE
1396.1
1651.3
2.36
0.85
0.16
FH/Z-SE
1246.8
1477.8
1.41
0.69
0.21
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Figure graphics
Figure 1
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180 160
•
♣ CaCO3 ♠ SiO2
♣ ♣
140
♦ •
♠
120 Intensity (a.u.)
∗ --- Fe • --- Fe3C ♥ --- Fe5C2 ♦ --- Graphitized Carbon ♥♦ ♥ ∗ ♥♥ FH/Z-SE
(B)
(A)
100
•
♠
•
80 60
♦ •
•
40 20
♥♦ ♥ ♥
∗
FL/Z-SE
♦ ♦
0
Z-SE
-20 10
20
30
40
50
60
70
10
80
20
2θ (Degrees)
Figure 2
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30
40 50 2θ (Degrees)
60
70
80
Journal of Agricultural and Food Chemistry
Quantity adsorbed (mmol/g)
30
(B)
(A)
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FH/Z-SE FL/Z-SE Z-SE
25 20 15
Adsorption Z-SE Desorption Z-SE Adsorption FL/Z-SE Desorption FL/Z-SE Adsorption FH/Z-SE Desorption FH/Z-SE
10 5 0 0.0
0.2
0.4 0.6 0.8 Relative pressure (P/P0)
1.0
5
10 15 20 25 30 35 40 45 50 55 60 Pore diameter (Å)
Figure 3
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Journal of Agricultural and Food Chemistry
700
60
Zeta potential (mv)
40
Zeta potential Paricle size
650 600
20 5.93 mv 557.2 nm 553.9 nm 0
550
-6.77 mv
492.7 nm -20 -24.66 mv
500 450
-40 Z-SM
FL/Z-SM
FH/Z-SM
Figure 4
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Particle size (nm)
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Journal of Agricultural and Food Chemistry
40 FH/Z-SE (1)
Ms (emu/g)
20
FL/Z-SE (2)
0
-20
-40 -20000
-10000
0 Field (G)
10000
Figure 5
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20000
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Journal of Agricultural and Food Chemistry
(A)
Z-SE FL/Z-SE FH/Z-SE
80 60 40 20 0 0
100
Relative bound amount (%)
Relative unbound amount (%)
100
20 10 Equilibrium time / min
60
Relative adsorbed amount ACE inhibitory activity
100.0%
(B)
76.6% 80
80
67.8% 56.4%
60
53.7%
100
49.6%
51.8% 60
39.4% 40
40
20 Protein hydrolysate Z-SE
Figure. 6
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20 FL/Z-SE
FH/Z-SE
ACE inhibitory activity (%)
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Journal of Agricultural and Food Chemistry
Page 36 of 45
2.1 0.6
1.8 1.5
0.2
0.6
0.0
AU
1.2
Original hydrolysate Eluate hydrolysate Residue hydrolysate
1390Da
0.4 4200 Da
19.5
21.0 Time (min)
0.9
22.5
AU
FL/Z-SM (before adsorption) FL/Z-SM (after adsorption)
AU
(A)
0.4
799 Da
0.2
73 Da
0.0 24
0.6 0.3
26 28 Time (min)
30
(B)
0.0 10
20
30 40 Pore diameter (Å)
50
60
0
10
Figure 7
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20 30 Time (min)
40
50
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Journal of Agricultural and Food Chemistry
(A)
Raw Simulated
2
Sp C
(B)
Raw Simulated
2
Intensity (a.u.)
Intensity (a.u.)
Sp C
3
Sp C C-O
3
Sp C Fe3C
O-C=O
282
284
286
288
290
282
Binding energy (eV)
C-O 284 286 Binding Energy (eV)
Figure 8
37
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O-C=O 288
290
Journal of Agricultural and Food Chemistry
FSP-1~4 FSP-5
100
FSP-6 ~ FSP-10
Relative inhibitory activity (%)
800
mAU
Intensity (mAU)
120
600
400
Page 38 of 45
110 100 90 14
15
Time (min)
16
200
(B)
81.23 74.83 67.44 66.12
80 60
50.74
47.86 43.54
37.48
40
28.10 20
18.74
(A)
0 0
10
20
30 40 Time (min)
50
0
60
1
Figure 9
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2
3
4
7 5 6 FSP - Series
8
9
10
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Journal of Agricultural and Food Chemistry
(A)
100
FSP-52
(B) ACE inhibitory activity (%)
500
Intensity (mAU)
400 300
FSP-53 FSP-51
200
FSP-54 100 0
78.44
80 60 40
30.59 19.41
20
10.73
-100 0
5
10 Time (min)
15
20
0
FSP-51
Figure 10
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ACS Paragon Plus Environment
FSP-52
FSP-53
FSP-54
338.46
Journal of Agricultural and Food Chemistry
b1 b2
100
R Y L
b1 157.34
40 392.49
20
451.72
434.43
320.45
60
60.23
Intensity (%)
80
b2
0 0
100
200 300 Mass (m/z)
400
Figure 11
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500
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Journal of Agricultural and Food Chemistry
1.4 Adsorption capacity (mmol/g)
Page 41 of 45
RYL Mw: 450.6
1.2
RYF Mw: 484.6 RYM Mw: 468.6
1.0
0.8
FYL Mw: 450.6
RYN Mw: 451.5
0.6 -3
-2
-1
LogP
0
1
Figure 12
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2
Journal of Agricultural and Food Chemistry
1.4 1/V0 (L⋅min⋅mM)
1.2
0 µM 25.31 µΜ 50.27 µΜ
1.0 0.8 0.6 0.4 0.2 0.0 0.0
0.2
0.4
0.6
0.8
1.0 -1
1/[S] (mM )
Figure 13
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Journal of Agricultural and Food Chemistry
Figure 14
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Table of Contents Graphic
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Journal of Agricultural and Food Chemistry
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