Abstract
Enzymatic/mild acidolysis lignin was extracted from both unbleached and bleached eucalyptus pulp, and the difference in lignin structures was analyzed by nuclear magnetic resonance spectroscopy. The unbleached pulp lignin was chlorinated with chlorine dioxide, and the mechanism of adsorbable organic halide (AOX) formation was investigated. Chlorinated reaction products were detected by gas chromatography-mass spectrometry. There is a possibility of producing three different chlorobenzene or chlorophenol products from S/S lignin dimers that are connected with β-O-4 bonds. Based on quantum chemistry theory, three reaction pathways were investigated using molecular simulation techniques. The results showed that pathway 1 possessed the lowest reaction activation energy, which made it the most favored thermodynamically. The β-O-4 bond of the lignin dimer was cleaved. Following that scission, 2-chloro-3,5-dimethoxy-methyl benzene was the most likely product to be generated from the chlorination reaction of the syringyl unit. These results provide theoretical guidance for further reduction of AOX in chlorine dioxide bleaching.
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Structural Transformation of Lignin from Eucalyptus during Chlorine Dioxide Bleaching
Chengrong Qin,a,b Lingzhi Huang,a,b Quanfeng Lv,a,b Shuangxi Nie,a,b and Shuangquan Yao a,b,*
Enzymatic/mild acidolysis lignin was extracted from both unbleached and bleached eucalyptus pulp, and the difference in lignin structures was analyzed by nuclear magnetic resonance spectroscopy. The unbleached pulp lignin was chlorinated with chlorine dioxide, and the mechanism of adsorbable organic halide (AOX) formation was investigated. Chlorinated reaction products were detected by gas chromatography-mass spectrometry. There is a possibility of producing three different chlorobenzene or chlorophenol products from S/S lignin dimers that are connected with β-O-4 bonds. Based on quantum chemistry theory, three reaction pathways were investigated using molecular simulation techniques. The results showed that pathway 1 possessed the lowest reaction activation energy, which made it the most favored thermodynamically. The β-O-4 bond of the lignin dimer was cleaved. Following that scission, 2-chloro-3,5-dimethoxy-methyl benzene was the most likely product to be generated from the chlorination reaction of the syringyl unit. These results provide theoretical guidance for further reduction of AOX in chlorine dioxide bleaching.
Keywords: Lignin; Chlorine dioxide; NMR; Chlorination reaction; Reaction pathway
Contact information: a: Department of Light Industrial and Food Engineering, Guangxi University, Nanning, 530004, PR China; b: Guangxi Key Laboratory of Clean Pulp & Papermaking and Pollution Control, Nanning 530004, PR China; *Corresponding author: yaoshuangquan@sina.cn
INTRODUCTION
Reactions with elemental chlorine (Cl2) and related chemicals such as ClO2 have long played a major role in the bleaching of pulp fibers for the production of paper products. Chlorination can be defined as the reaction between Cl2 and the residual lignin in pulp. During chlorination, lignin is degraded into fragments that dissolve in water or a dilute alkaline solution. The lignin fragments that are dissolved are removed in the next step, since the chlorination is performed in an acidic medium (Yao et al. 2018). When using Cl2, adsorbable organic halides (AOX), which are chlorinated lignin derivatives, are found in the wastewater of pulping and papermaking enterprises. The AOX is mainly produced during chlorine dioxide bleaching (Sharma et al. 2014). Although AOX formation has been remarkably reduced by using elemental chlorine-free bleaching sequences (Liu et al. 2015), the discharge volume of pulp and paper wastewater is large and AOX is the most notable persistent organic pollutant produced from bleaching. Persistent organic pollutants display characteristics of persistent residues, bioaccumulation, high toxicity, semi-volatility, and long-distance migration (Jaacks and Staimez 2015). Therefore, total AOX emissions to the natural environment accumulate continuously and the environmental threat is increasing. AOX reduction has been made possible by process optimization, the addition of chemical additives, and pretreatment (Yao et al.2017). Also, the presence of hemicellulose (Yao et al. 2017) and hexenuronic acid (Nie et al. 2015; Zhang et al. 2019) has had an effect on AOX formation. Nevertheless, the main source of AOX is the reaction between residual lignin and chlorinated bleaching agents (Nie et al. 2014). The oxidation of 1-(3,4-dimethoxyphenyl)ethanol (MVA), a lignin model compound, with chlorine dioxide under simulated bleaching conditions were studied.
In biomass, the chemical structure of lignin is complex (Kim et al. 2016; Xiong et al. 2017; Xing et al. 2019) and it is associated with cellulose and hemicellulose (Lin et al. 2018; Nie et al. 2018). The separation and purification of lignin is difficult, as it easily degrades and undergoes a condensation reaction (Smith et al. 2016; Servaes et al. 2017). The introduction of enzymatic/mild acidolysis lignin (EMAL) has improved the enzymatic method of obtaining lignin (Lou and Wu 2011; Edmunds et al. 2017). To evaluate the inhibition effects of pseudo-lignin on the enzymatic hydrolysis of cellulose compared with lignin, EMAL was isolated from poplar with an 8-min pretreatment at 170 °C in 0.5% H2SO4 (Hu et al. 2013). The results showed that the diluted acid-pretreated lignin inhibited hydrolysis in the initial stage. A high yield and high lignin purity were obtained using this method, and the lignin structure was not changed compared with that of enzymatically obtained lignin. Extracted lignin is suitable for the identification of lignin structures (Constant et al. 2016; Yue et al. 2016). The structure of lignin was studied (Lu et al. 2016), the main intermolecular lignin connection in wood biomass is the β-O-4 bond, which accounts for approximately 50% of intermolecular connections. The constitutional unit and intermolecular connections of lignin have a great influence on the chemical activity of lignin.
This paper mainly focused on the mechanism of lignin chlorination during chlorine dioxide bleaching. Lignin was extracted from unbleached and bleached eucalyptus pulp. The structural changes to lignin during chlorine dioxide bleaching were analyzed by nuclear magnetic resonance (NMR) spectroscopy. AOX formation from the chlorination reaction of the unbleached lignin was analyzed by gas chromatography-mass spectrometry (GC-MS). Three distinct reaction pathways for AOX formation were investigated. The activation energy of each reaction was calculated based on the quantum chemistry theory. The most favorable reaction pathway was determined.
EXPERIMENTAL
Materials
The eucalyptus wood and chlorine dioxide solution were provided by a local pulp and paper mill (Guangxi, China). The chemical composition of the eucalyptus wood (five-year-old Eucalyptus urophylla), was 1.70% ash, 1.49% benzene-alcohol extract, 18.2% sodium hydroxide extract, 22.4% lignin, 51.9% cellulose, and 24.0% hemicellulose. The effective chlorine in the chlorine dioxide solution was 14.6%. The content of chlorine dioxide and chlorine gas in the solution was 17.8 g/L and 2.20 g/L, respectively. Cellulase (255 FPU/mL) was purchased from Novozymes (Copenhagen, Denmark). All of the assay reagents were obtained from Sigma (St. Louis, USA). All of the other chemicals employed in this work were purchased from Aladdin Reagent CO. LTD. (Shanghai, China). All of the chemicals used were of analytical grade.
Methods
Cooking was conducted in a laboratorial digester that simulates a continuous digester (Greenwood Instruments, Andover, MA, USA) with six 1000-mL stainless steel cylindrical reactors. The general method consisted of 50 g of dry eucalyptus being added to pure water. The ratio of solid to liquid was 1:5, and 10% sodium hydroxide (% dry raw material) was added. The mixture was heated to 160 °C over 90 min. Thermal insulation occurred for 60 min at 160 °C. Then, the digester control program was stopped and the reaction was terminated.
The bleaching reaction was performed in a water bath kettle. Additionally, 10 g of unbleached dry pulp or lignin was mixed with pure water in a sealed polyethylene bag. The mixture concentration was 10%, and the mixture was thoroughly mixed for 5 min. The pH of the reaction solution was adjusted to approximately 3.5 to 4 using a sulfuric acid solution. Finally, 120-kg/tp (2.0% of 10 g unbleached dry pulp) (w/w) chlorine dioxide solutions were added to the mixture at 65 °C. The reaction time was 60 min. The mixture was kneaded every 5 min during the reaction and the pulp was washed to a neutral pH at the end of the reaction. The reaction solution was collected (Nie et al. 2015; Yao et al. 2017).
Lignin was isolated from the unbleached and bleached eucalyptus pulp using the EMAL method (Lou and Wu 2011). The raw materials were pretreated with cellulases, and the volume fraction of the enzyme solution was 10%. Enzymatic hydrolysis of the raw materials was performed for 72 h in a shaking table at 200 rpm, 40 °C, and a pH of 4.5. The enzymatically hydrolyzed crude lignin was obtained by centrifugation. The isolated crude lignin was washed with 1.4% (w/w) dilute sulfuric acid at 165 °C for 8 min. The final crude lignin was freeze-dried. Then, the crude enzymatic lignin was dispersed in 100 mL of a dioxane-water mixture that contained 85 mL of dioxane and 15 mL of water, which was then refluxed at 87 °C under nitrogen for 2 h. After the reaction was completed, the mixture was filtered and the residue was washed with a neutral dioxane-water mixture to clarify the filtrate. The obtained filtrate was neutralized with sodium bicarbonate and concentrated under a reduced pressure at 35 °C. A small amount of concentrated solution was slowly added to a large amount of pure water. The mixture was centrifuged after standing for 12 h, and then the remaining solid was freeze-dried. The dried solid was purified with chromatographically pure n-hexane to remove the residual extract, and high purity EMAL was obtained.
The structural characteristics of the lignin were detected using 2D-heteronuclear single quantum coherence (HSQC)-NMR spectroscopy (Moghaddam et al. 2017). The structural changes of the lignin, bleached and unbleached, were analyzed. The basic detection methods were as follows. First, 50 mg of EMAL were dissolved in 1 mL of DMSO-d6. The solvent peak of the DMSO-d6 was used as a reference point for the internal chemical shift (δC/δH = 39.5/2.49). Additionally, 1H-13C correlation 2D-HSQC-NMR spectra were recorded at 25 °C on a Bruker DRX-500 spectrometer (Karlsruhe, Germany). The basic method and process for 1H-13C 2D-HSQC-NMR spectroscopy were described by Moghaddam et al. (2014).
The chemical composition of the reaction solution was analyzed by GC-MS (6890-5973, Agilent Technologies, Palo Alto, CA, USA). The organic chlorides were qualitatively and quantitatively analyzed, and the solution was concentrated. The concentrate was extracted by column adsorption and 1 μL of the concentrate was analyzed. The detailed operating conditions for GC-MS used in this study are described in previous studies (Nie et al. 2014; Yao et al. 2015).
Structural models were constructed by molecular simulation techniques using the visualizer module of Materials Studio (Neotrident Technology Limited, 7.0, Beijing, China). Density functional theory (DFT) calculations were performed using the Dmol3 program (Wu et al. 2014). The double numerical plus polarization function and generalized gradient approximation functional were used for all of the geometry optimizations. The atoms of the reactants and products were matched and the reaction barrier between the reactant and transition state was used as the reaction activation energy. The transition state was analyzed by the complete linear synchronous transit (LST) and quadratic synchronous transit (QST) methods.
RESULTS AND DISCUSSION
Response Analysis
The lignin extracted from both the unbleached and bleached eucalyptus pulp was analyzed by 2D-HSQC-NMR in the gel state according to previously published methods (Wen et al. 2013; Ando et al. 2017). The functional groups and basic structural units of the lignin and the bonding of basic structural units were depicted in the HSQC spectra (Fig. 1). The assignments of the main signals in Fig. 1 for the unbleached pulp lignin are listed in Table 1. The peak assignments were based on previous publications (del Río et al. 2015; Wen et al. 2015).
Table 1. Assignment of Main Signals in NMR Spectra of Unbleached Pulp Lignin
Cross-signals of methoxyl groups and β-O-4 substructures were present in all, but two lignin samples. The Cγ/Hγ correlation signals of the β-O-4 substructures (Aγ) and the Cα/Hα correlation signals of the β-O-4 structures (A’γ) were detected in all, but two lignin samples. Weak signals were observed in the bleached pulp lignin at δC/δH signals of 57.92/3.71, 59.02/3.71, and 62.9/4.22 for Aγ and A’γ. Signals for Aγ and A’γ in the lignin extracted from the bleached pulp were attenuated, which indicated that the β-O-4 bond of the lignin constitutional unit was cleaved during the chlorine dioxide reaction.
Eucalyptus lignin is a copolymer primarily composed of guaiacyl (G) and syringyl (S) units. In the HSQC spectrum of the bleached pulp, signals for S units (S2,6) and methoxy (OMe) groups were barely observed. This was mainly because of the oxidizing reaction of the S unit structure during the bleaching process. Most lignin is oxidized by chlorine dioxide, and little is derivitized. The signals for S2,6 and OMe were obscured or offset by the partial substituents that were introduced. The intensities of the Cγ, G5, and Iγ signals were lower in the HSQC spectrum of the unbleached pulp, which indicated the existence of residual lignin following the bleaching process. The results showed that the S/S lignin dimer, which was connected by a β-O-4 bond in the unbleached pulp, participated in the substitution reactions to produce organic chlorides during chlorine dioxide bleaching.
Fig. 1. 2D-HSQC NMR spectra of the EMAL extracted from the (a) unbleached pulp lignin and (b) bleached pulp lignin
Fig. 2. GC-MS graph of the reaction solution
The residual lignin in unbleached pulp is the main source for AOX formation. To understand the mechanism of AOX formation, the organic chlorides produced by the reaction of lignin and chlorine dioxide need to be analyzed. The GC-MS graph of the bleaching effluent after chlorine dioxide bleaching is shown in Fig. 2.
Table 2. Main Organic Chlorides of the Reaction Solution
The organic chlorides identified by GC-MS in the chlorine dioxide bleaching effluent are shown in Table 2. AOX comprised eight categories. The highest concentrated organic chlorides were 2-chloro-3,6-dihydroxy-methyl benzoate (16.62 min) and 2-chloro-3,5-dimethoxy-methyl benzene (17.10 min). The lowest concentrated organic chloride was 1,4-dichloro-2-butanol (6.46 min). The lignin had a ring-opening reaction during oxidation between the lignin and chlorine dioxide (Behin and Zeyghami 2009). A substitution reaction occurred between the chain molecule and free chlorine in the solution. Then, 1,4-dichloro-2-butanol was produced. The organic chlorides that belong to the chlorobenzene or chlorophenol categories were 4-chlororesorcinol (13.38 min), 2-chloro-1,4-benzenediol (13.42 min), and 2-chloro-3,5-dimethoxy-methyl benzene. These chlorobenzenes and chlorophenols constitute more than half of the total organic chlorides. This finding was consistent with those of Yao et al. (2017).
Figure 1 shows that the unbleached pulp lignin mainly consisted of S units connected with β-O-4 bonds. The main fracture mode was β-O-4 bond cleavage during chlorine dioxide bleaching. Therefore, the S/S lignin dimer (connected by a β-O-4 bond) was the main source for AOX formation. The S/S lignin dimer is a natural compound; it is a fragment of a lignin macromolecule. Considering that the constitutional G unit was present in the bleached pulp lignin, it was more likely that the S unit was involved in chlorination. Based on the above conclusions, the β-O-4 bond of the unbleached pulp lignin was cleaved and the S unit participated in a chlorination reaction with hypochlorous acid during chlorine dioxide bleaching.
Based on the relative stability of the benzene ring, the chlorinated products from the reaction between the S unit and chlorine dioxide should contain the benzene ring structure, such as in chlorobenzene or chlorophenol. The main chlorinated products of the S/S dimer determined by GC-MS analysis were 2-chloro-3,5-dimethoxy-methyl benzene, 2-chloro-1,4-benzenediol, and 4-chlororesorcinol (Fig. 2). Therefore, there were three reaction AOX formation pathways between the unbleached pulp lignin and chlorine dioxide. These results are shown in Fig. 3.
Fig. 3. Suggested reaction pathways
Molecular Orbital Analysis
The lowest unoccupied molecular orbital (LUMO) and highest occupied molecular orbital (HOMO) of the S/S lignin dimer molecule model were calculated and analyzed (Sworakowski et al. 2016).
Fig. 4. Orbital of the HOMO (a) and LUMO (b) in the S/S lignin dimer
The HOMO was mainly distributed on the C1, C2, C3, C4, C5, phenolic hydroxyl groups, and methoxy groups of the S unit (Fig. 4). The electrons of these atoms are easily excited. This indicated that a facile nucleophilic reaction can occur in the benzene, phenol hydroxyl, and two methoxy groups. The energy of the HOMO formation was found to be -0.180 eV. The LUMO was mainly distributed on the benzene carbons, methoxy groups, and methyl groups of the S unit, and its energy was found to be -0.061 eV. The reactivity of S units is higher because of the increased number of methoxy groups (Kim et al. 2017). The electrons on the HOMO can be transferred to the neighboring carbon atoms, and substitution reactions can occur at the C-C bonds of the S unit because of the weakening of the C-OH and C-OCH3 bonds. The difference in orbital energy between the HOMO and LUMO formations was 0.119 eV, which indicated that the β-O-4 bond of the S/S lignin dimer was relatively unstable. The reaction of the S-lignin and chlorine dioxide was favored as the S unit exhibited a higher reactivity. These observations verified the conclusions from the NMR analysis of the lignin.
In the basic structural unit of lignin, the reactivity of the S-lignin is the highest (Jongerius et al. 2013). The HOMO and LUMO of the S unit molecular models were calculated and analyzed to better understand the reactivity of this functional group. Figure 5 shows that the HOMO was mainly distributed on the C1, C3, C4, C5, C6, phenolic hydroxyl groups, and methoxy groups of the S unit. These carbon atoms tend to lose electrons, and the associated functional groups, e.g., phenolic hydroxyl and methoxy groups, were replaced. The energies of the HOMO and LUMO were found to be -0.189 eV and -0.066 eV, respectively. The difference in the orbital energy was 0.123 eV, which was greater than that of the S/S lignin dimer. This indicated that the reactivity of the S unit was greater than that of the S/S lignin dimer. The branched chain of C1 was easy to break during the reaction between an S unit and chlorine dioxide. Chlorobenzene or chlorophenol was produced when a chlorine substitution reaction occurred at C2. The methoxy groups on C3 and C5 were removed, and hydroxyl addition reactions occurred on these active carbon atoms. Additionally, the hydroxyl group on C4 was removed. The results of the GC-MS analysis were verified by this data.
Fig. 5. Orbital of the HOMO (a) and LUMO (b) in an S unit
Reaction Pathway Analysis
Reaction pathway 1
The HOMO and LUMO formations were distributed on C1 and C4 of the S unit. This meant that C1 and C4 can easily gain and lose electrons. The branched chain of C1 was easy to break, and when it was broken, Cα was retained. An elimination reaction occurred at C4, which removed the phenolic hydroxyl group. The LUMO was also distributed on C2, which allowed this carbon to more easily gain electrons. The chlorine substitution reaction occurred at C2, where 2-chloro-3,5-dimethoxy-methyl benzene was produced. Acetic acid was produced by the reductive elimination of the β-hydroxy groups on the propanoid chain of the S unit. The para-hydroxy group was removed to form water molecules. These results are shown in Fig. 3.
The DFT was used to propose a mechanism for reaction pathway 1. Models of the intermediates in reaction pathway 1 were created using the visualizer module in Materials Studio. All of the atoms were matched after the structures of the reactants and products were geometrically optimized. The reaction transition state (TS) was determined by LST/QST, while the activation energy and heat of reaction were also obtained. The change curve of the path coordinate of energy vs. LST, QST, and conjugate gradient is shown in Fig. 6.
Fig. 6. Transition state of reaction pathway 1
Fig. 7. Reaction pathways and energies of organic chloride formation
The transient search process was monitored. The change curve of the path coordinate showed that there was one intermediate product in pathway 1. This also meant that C1, C2, and C4active site free radicals were formed simultaneously. The energy of pathway 1 is shown in Fig. 7. The energy of the reactant and product were -794361.52 kcal/mol and -794405.76 kcal/mol, respectively. The energy of TS 1 (energy saddle point) was -794278.00 kcal/mol. The activation energy (ΔE) of pathway 1 was 83.75 kcal/mol. The heat of reaction (ΔH) was -44.23 kcal/mol. This showed that reaction pathway 1 was exothermic, with an overall ΔH of less than 0.
Reaction pathway 2
The HOMO was distributed on C1, C3, and C5 of the S unit. The branched chain of C1 was removed as a whole. Elimination reactions occurred at C3 and C5, and the methoxy groups were removed. The LUMO was distributed on C1. The hydroxyl group was connected to C1 after the branched chain was removed. The LUMO was distributed on C2, which was the location of the chlorine substitution reaction. During this reaction, 2-chloro-1,4-benzenediol was produced. Additionally, methylacetic acid was produced by the reductive elimination of the α-hydroxy groups on the propanoid chain of the S unit. These results are shown in Fig. 3.
Reaction pathway 2 was simulated using the same method as reaction pathway 1. The results are shown in Fig. 8. The change curve of the path coordinate showed that there were five intermediate products in pathway 2. This also meant that C1, C2, C3, and C5 active site free radicals were formed successively. Branched-chain cleavage and hydroxyl addition reaction of C1 occurred successively. This was consistent with the process analysis of pathway 2. Figure 7 shows TS 2 and the energy of pathway 2. The energy of the reactant and product was -794340.43 kcal/mol and -794393.77 kcal/mol, respectively. The energy of TS 2 (energy saddle point) was -794203.01 kcal/mol. The ΔE of pathway 2 was 137.66 kcal/mol. The ΔH was -53.74 kcal/mol. This showed that pathway 2 was exothermic, as the ΔH was less than 0. Comparing the ΔE of pathways 1 and 2, the ΔE of pathway 1 was smaller, which meant that pathway 1 was more favorable than pathway 2.
Fig. 8. Transition state of reaction pathway 2
Reaction pathway 3
The HOMO was distributed on C1, C3, C4, and C5 of the S unit. The branched chain of C1 was removed as a whole. The elimination reaction occurred on C3, C4, and C5, which removed the methoxy and phenolic hydroxyl groups. The LUMO was distributed on C2, C3, and C5. The hydroxyl groups were grafted after the methoxy groups were removed from C3 and C5. The chlorine substitution reaction occurred on C2, and 4-chlororesorcinol was produced. Methylacetic acid was produced by the reductive elimination of the α-hydroxy groups on the propanoid chain of the S unit. The para-hydroxy group was removed to form water molecules and the results are shown in Fig. 3.
Pathway 3 was simulated using the same method as reaction pathway 1. The results are shown in Fig. 9. The change curve of the path coordinate shows that there were two intermediate products in pathway 3. This also meant that C1, C3, C4, and C5 active site free radicals were formed simultaneously. The hydroxyl addition reactions of C3 and C5 occurred successively. Figure 7 shows TS 3 and the energy of pathway 3. The energy of the reactant and product were -794357.36 kcal/mol and -794401.92 kcal/mol, respectively. The energy of TS 3 (energy saddle point) was -794014.74 kcal/mol. The ΔE of pathway 3 was 342.70 kcal/mol. The ΔH was -44.82 kcal/mol. This showed that pathway 3 was exothermic, as ΔH was less than 0. Comparing the ΔE of pathways 1, 2, and 3, pathway 1 had the lowest activation energy, which meant that pathway 1 was more favorable than pathway 2 or 3.
Fig. 9. Transition state of reaction pathway 3
The highest organic chloride content detected was 2-chloro-3,5-dimethoxy-methyl benzene, which was produced by the reaction of the unbleached lignin and chlorine dioxide. Based on the contents of the reaction products, reaction pathway 1 was the most favorable. This finding was consistent with the conclusions of the molecular modeling calculations. These results introduce a new methodology to study the complex chemical reaction system of AOX produced by lignin and chlorine dioxide.
CONCLUSIONS
- Enzymatic/mild acidolysis lignin was extracted from both unbleached and bleached eucalyptus pulp. The β-O-4 bond of the S/S lignin dimer, which came from the unbleached pulp, was cleaved during ClO2 bleaching. The S unit was the main reactant from which organic chlorides were produced during the bleaching process.
- Chlorinated products contained three kinds of chlorobenzenes or chlorophenols, of which 2-chloro-3,5-dimethoxy-methyl benzene had the highest content. Three chlorination pathways were speculated. The pathways were calculated using molecular simulation technology. Pathway 1 was found to be optimal because it had the lowest activation energy. The compound 2-chloro-3,5-dimethoxy-methyl benzene was most easily produced between the reaction of the S unit and chlorine dioxide.
ACKNOWLEDGMENTS
This project was sponsored by the National Natural Science Foundation of China (Grant Nos. 31760192 and 21466004) and supported by the Guangxi Natural Science Foundation of China (Grant No. 2016GXNSFBA380234).
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Article submitted: September 26, 2018; Peer review completed: December 15, 2018; Revised version received and accepted; December 19, 2018; Published: December 21, 2018.
DOI: 10.15376/biores.14.1.1265-1278