The present invention relates to a method of producing a high value-added compound from polyethylene terephthalate.
Polyethylene terephthalate (PET) is polyester of terephthalic acid (TPA) and ethylene glycol (EG). Because of its excellent physical properties, PET has been widely used in synthetic fibers and packaging materials. In 2015, annual global PET production reached 33 million tons, making PET the most commonly produced polyester in the world. Since PET does not completely decompose naturally, it causes serious environmental problems, such as the prevalence of microplastics in terrestrial ecosystems and the accumulation of waste plastics in the ocean. However, biodegradable plastics having similar physical properties and economic efficiency to PET are not yet available. Reducing PET production in the near future is unlikely, necessitating stricter PET recycling to reduce waste PET released in nature.
Among various plastics, PET and polyethylene (PE) are the only ones that are physically recyclable, and recycled plastics are produced from these waste plastics. Mechanical PET recycling has been performed for decades, but the rate of this traditional recycling is lower than approximately 21% in the United States. This low rate seems to be mainly due to the lower quality and higher costs of recycled PET (e.g., $1.3 to 1.5/kg PET) compared to virgin PET ($1.1 to 1.3/kg PET). To improve the high costs and low economic feasibility of mechanical recycling functioning as downcycling, for example, blending mechanically recycled PET with lignin for producing carbon fibers has been studied as an alternative application of mechanically recycled PET.
To overcome the problem of downcycling PET via mechanical recycling, chemical recycling in which PET is depolymerized into monomers and the monomers are repolymerized to PET was developed. However, PET production by the depolymerization and chemical recycling of PET also has no economic advantages. Therefore, it is necessary to improve the economic efficiency of PET recycling through upcycling by converting monomers to higher-value products than PET.
Recently, a method of chemically upcycling waste PET into high value-added plastics by the chemical modification of PET and reinforcement with glass fibers has been developed. In this case, the PET is biologically converted to plastic monomers such as polyhydroxyalkanoate (PHA). However, the economic sustainability of the bioconversion to PHA is still questionable.
Therefore, in the present invention, the biological valorization of PET monomers was verified for the first time to improve the economic efficiency of waste PET recycling and develop effective PET upcycling strategies. For the biological valorization of PET, PET was depolymerized by chemical hydrolysis and TPA and EG monomers were converted to various high value-added compounds using various metabolically engineered whole-cell microbial catalysts. In particular, by introducing a TPA degradation pathway into microbes, TPA is converted to high value-added aromatic compounds or aromatic-derived compounds, that is, protocatechuic acid (PCA), gallic acid (GA), pyrogallol, catechol, muconic acid (MA), and vanillic acid (VA), which are used for manufacturing pharmaceuticals, cosmetics, sanitizers, animal feeds, bioplastic monomers, and the like. Specifically, the present invention was completed by identifying key enzymes capable of catalyzing reactions required to convert TPA and microbes capable of fermenting EG into glycolic acid (GLA), and investigating their potential as key components of PET valorization.
The present invention is directed to providing a method of producing a high value-added compound from waste PET.
One aspect of the present invention provides a method of producing a high value-added compound from polyethylene terephthalate, comprising:
producing terephthalic acid and ethylene glycol through hydrolysis of polyethylene terephthalate; and
producing one or more compounds selected from the group consisting of gallic acid, pyrogallol, catechol, muconic acid, and vanillic acid through bioconversion of the terephthalic acid in the presence of a biocatalyst, wherein protocatechuic acid is an intermediate produced by the bioconversion, or
producing glycolic acid through fermentation of the ethylene glycol.
According to the present invention, by using one or a combination of the hydroxylation, decarboxylation, oxidation ring cleavage, and methylation reactions of TPA which is a PET hydrolysate, and using PCA as an intermediate, it is possible to convert PET to a variety of higher value-added compounds such as GA, pyrogallol, catechol, MA, and VA. In addition, since another PET monomer, EG, is converted to GLA using microbes capable of fermenting the same, the possibility of recycling waste PET is provided.
Hereinafter, the composition of the present invention will be described in detail.
One aspect of the present invention provides a method of producing a high value-added compound from polyethylene terephthalate, comprising:
producing terephthalic acid and ethylene glycol through hydrolysis of polyethylene terephthalate; and
producing one or more compounds selected from the group consisting of gallic acid, pyrogallol, catechol, muconic acid, and vanillic acid through bioconversion of the terephthalic acid in the presence of a biocatalyst, wherein protocatechuic acid is an intermediate produced by the bioconversion, or
producing glycolic acid through fermentation of the ethylene glycol.
In the method of producing a high value-added compound from polyethylene terephthalate according to the present invention, monomers terephthalic acid and ethylene glycol are produced through the chemical hydrolysis of polyethylene terephthalate, various high value-added aromatic compounds or aromatic-derived compounds such as GA, pyrogallol, catechol, MA, and VA are produced through the bioconversion of TPA which is a PET hydrolysate, and glycolic acid is produced through the fermentation of ethylene glycol.
The chemical hydrolysis of PET may be carried out through the application of microwaves at a temperature of 170 to 230° C. for 15 to 50 minutes. The PET hydrolysate may be separated into TPA solids and an EG-containing solution by filtration.
For the bioconversion of TPA, PCA is selected as a first product and a key intermediate. PCA can be a precursor compound for producing various high value-added aromatic compounds or aromatic-derived compounds such as GA, pyrogallol, catechol, MA, and VA.
As an efficient biocatalyst capable of converting TPA to PCA, TPA 1,2-dioxygenase and 1,2-dihydroxy-3,5-cyclohexadiene-1,4-dicarboxylate (DCD) dehydrogenase are used, wherein TPA 1,2-dioxygenase converts TPA to DCD, and DCD dehydrogenase converts DCD to PCA. TPA 1,2-dioxygenase and DCD dehydrogenase may be derived from Comamonas sp. E6, and their respective coding gene names are TphAabc and TphB. These enzymes may utilize NADH and NADPH as cofactors. According to one embodiment of the present invention, to obtain PCA from TPA, a PET hydrolysate, microbes expressing TphAabc and TphB may be used as a biocatalyst.
Next, the bioconversion of TPA to GA may be implemented by inducing hydroxylation at the meta-position of PCA, in which case, the PCA is converted to GA. The hydroxylation may be achieved using p-hydroxybenzoate hydroxylase. The p-hydroxybenzoate hydroxylase may be derived from Pseudomonas putida (P. putida) KT2440, and its coding gene name is PobA. In addition, according to one embodiment of the present invention, a PobA mutant, that is, PobAMut (T294A/Y385F), may be constructed to increase GA production yield, and microbes expressing PobAMut may be used as a biocatalyst. Preferably, to produce GA from TPA, microbes expressing TphAabc, TphB, and PobAMut or a combination of microbes expressing TphAabc and TphB and microbes expressing PobAMut may be used as a biocatalyst.
According to one embodiment of the present invention, to improve GA production yield from TPA, microbes expressing TphAabc, TphB, and PobAMut (strain GA-1) and having an OD600 value of 30 may be reacted with TPA, or microbes expressing TphAabc and TphB (strain PCA-1) and microbes expressing PobAMut (strain HBH-2) and having OD600 values of 10 and 30, respectively, may be reacted with TPA, so that the GA production yield can be improved without the accumulation of PCA.
Next, the bioconversion of TPA to pyrogallol via GA may be implemented through two routes: via the decarboxylation of GA synthesized by PCA hydroxylation (first route), and via the hydroxylation of catechol that can be synthesized by PCA decarboxylation (second route).
In the case of the first route, microbes expressing TphAabc, TphB, and PobAMut due to including GA decarboxylase (coding gene name: LpdC) for the decarboxylation of GA synthesized by PCA hydroxylation may be used as a biocatalyst. According to one embodiment of the present invention, microbes expressing TphAabc, TphB, PobAMut, and LpdC (strain PG-1a) may be reacted with TPA to produce pyrogallol.
In the case of the second route, PCA decarboxylase (coding gene name: AroY) and a phenol hydroxylase (coding gene name: PhKLMNOPQ) for catechol hydroxylation may be used as a biocatalyst. According to one embodiment of the present invention, a combination of microbes expressing TphAabc, TphB, and AroY (strain CTL-1) and microbes expressing PhKLMNOPQ (strain CH-1), whose OD600 values are 10 and 30, respectively, may be used and reacted with TPA, so that pyrogallol can be produced while minimizing the accumulation of catechol.
Next, the bioconversion from TPA to MA may be implemented by the ring cleavage of catechol synthesized from TPA via PCA, in which case, catechol is converted to MA. The ring cleavage of catechol may be implemented using catechol 1,2-dioxygenase (coding gene name: CatA) derived from P. putida KT2440. According to one embodiment of the present invention, microbes expressing TphAabc, TphB, AroY, and CatA (strain MA-1) may be reacted with TPA to produce MA.
Next, the bioconversion of TPA to VA may be implemented by converting PCA to VA by an OMT. In an O-methylation reaction catalyzed by an OMT, since adenosyl and methyl groups are supplied from ATP and methionine, S-adenosyl methionine (SAM) may be used as a co-substrate.
As the OMT, one derived from eukaryotes may be used. For example, HsOMT from H. sapiens, SlOMT from S. lycopersicum, MsOMT from M. sativa, and the like may be used. To increase VA production yield, HsOMT from H. sapiens is preferred. In addition, to increase the protein solubility of HsOMT, HsOMT may be modified to have hexameric histidine at the N-terminus.
In addition, to improve VA production yield, aeration may be increased during the reaction of TPA and a biocatalyst. Increased aeration is correlated with the increased consumption of glycerol and methionine. That is, aeration is critical for increasing VA production from PCA because glycerol is efficiently metabolized to generate adenosine triphosphate (ATP), thus accelerating S-adenosyl methionine (SAM) synthesis from methionine by supplying S-adenosyl groups.
According to one embodiment of the present invention, to produce VA from TPA via PCA, microbes expressing TphAabc and TphB (strain PCA-1) and microbes expressing HsOMTHis (strain OMT-2His) and having OD600 values of 10 and 30, respectively, may be reacted with TPA in the presence of glycerol and methionine while increasing aeration to increase ATP production, and thereby VA production yield can be improved.
The method of the present invention is capable of producing GLA from EG, which is a PET hydrolysate, through fermentation. The fermentation may be performed using EG-fermenting microbes such as G. oxydans KCCM 40109, Clostridium glycolicum, P. putida, and the like.
The bioconversion of the present invention may be carried out in various reaction buffer systems. For example, the following may be used: TG-1 buffer, 50 mM Tris buffer (pH 7.0) containing 10% (w/v) glycerol; TG-2 buffer, 50 mM Tris buffer (pH 7.0) containing 2% (w/v) glycerol; TG-1/YP buffer, 50 mM Tris buffer (pH 7.0) containing 10% (w/v) glycerol, 10 g/L yeast extract, and 20 g/L peptone; TG-2/YP buffer, 50 mM Tris buffer (pH 7.0) containing 2% (w/v) glycerol, 10 g/L yeast extract, and 20 g/L peptone; TG-1/YPM buffer, TG-1/YP buffer supplemented with 2.5 mM L-methionine (Sigma-Aldrich); and TG-2/YPM buffer, TG-2/YP buffer supplemented with 2.5 mM L-methionine.
As used herein, the term “biocatalyst” refers to an enzyme involved in the bioconversion of TPA and is also used to refer to a microbe expressing the enzyme. The enzyme can be introduced into a host cell in the form of a recombinant vector containing a coding gene and expressed.
The term “recombinant vector” refers to a vector capable of expressing a target protein in an appropriate host cell and means a genetic construct including essential regulatory elements operably linked to express a gene insert in vivo or in vitro. In this specification, the terms “plasmid,” “vector,” and “expression vector” are used interchangeably.
Examples of the above-described vector include, but are not limited to, plasmid vectors, cosmid vectors, bacteriophage vectors, or viral vectors. Suitable expression vectors include expression control elements such as promoters, operators, start codons, stop codons, polyadenylation signals, and enhancers and additionally include signal sequences or leader sequences for membrane targeting or secretion, and they can be variously prepared according to the purpose. A promoter in a vector may be constitutive or inducible. In addition, the expression vector includes a selection marker for selecting a host cell including a vector, and in the case of a replicable expression vector, an origin of replication.
The term “operably linked” means that an appropriate nucleic acid molecule is linked to a regulatory sequence in such a way as to enable gene expression.
As used herein, the term “nucleic acid molecule” means any single or double-stranded nucleic acid molecule of cDNA, genomic DNA, synthetic DNA or RNA, PNAS or LNA origin, or a combination thereof. “Nucleic acid” and “polynucleotide” may be used interchangeably herein.
The recombinant vector of the present invention is preferably prepared by inserting the above-described gene into a general vector for expressing an E. coli strain. As the vector for expressing an E. coli strain, any commonly available E. coli expression vector can be used without limitation.
A host cell transformed by the recombinant vector can express an enzyme involved in the bioconversion of TPA. A method of achieving the transformation includes any method capable of introducing a nucleic acid into an organism, cell, tissue, or organ, and the transformation can be performed by selecting a standard technique suitable for the host cell, as is known in the art. Examples of such a method include, but are not limited to, electroporation, protoplast fusion, calcium phosphate (CaPO4) precipitation, calcium chloride (CaCl2) precipitation, agitation using silicon carbide fibers, agrobacterium-mediated transformation, and use of PEG, dextran sulfate, Lipofectamine, and the like.
In addition, since the expression level and modification of the protein are different according to the host cell, it is recommended to select and use the most suitable host cell for the purpose.
Examples of the host cell include, but are not limited to, prokaryotes such as E. coli, Zymomonas mobilis, Bacillus subtilis, Streptomyces, Pseudomonas, Proteus mirabilis, or Staphylococcus. In addition, eukaryotes such as fungi (e.g., Aspergillus) or yeast (e.g., Pichiapastoris, Saccharomyces cerevisiae, Schizosaccharomyces, Neurosporacrassa) may be used, but the present invention is not limited thereto.
Various culture methods can be applied for the (large-scale) culture of transformants, and for example, the large-scale production of expressed or overexpressed gene products from recombinant microbes can be achieved by batch or continuous culture methods. Batch and fed-batch culture methods are conventional and known in the art. Methods for controlling nutrients and growth factors for continuous culture processes and techniques for maximizing product formation rates are known in the microbial industry. In addition, as a culture medium, a medium formed of a carbon source, a nitrogen source, vitamins, and minerals may be used, and the composition of the culture medium may be configured as known in the art.
Hereinafter, the present invention will be described in more detail through Examples according to the present invention, but the scope of the present invention is not limited by the Examples presented below.
Granular PET chips (Sigma-Aldrich) were used for chemical hydrolysis experiments. PET hydrolysis reaction mixtures included 1 g granular PET in 13 mL deionized water and were input in a microwave reactor (Monowave 300, Anton Paar, Graz, Austria). PET hydrolysis was performed under microwave irradiation at various temperatures and durations: 170, 200, and 230° C. and 15, 20, 25, 30, 40, and 50 minutes. The TPA yield from hydrolysis of PET was calculated as TPA yield (% of theoretical maximum TPA=TPA produced (g)/theoretical maximum TPA produced from consumed PET (g)×100). The theoretical maximum mass of TPA to be produced from PET was calculated by multiplying PET mass by 0.864, a TPA yield coefficient for PET. Due to the high degree of polymerization of PET, the total number of cleaved ester bonds by hydrolysis was assumed to be the same as the total number of TPA and EG monomers. Therefore, the TPA yield coefficient of TPA from PET was calculated while assuming a TPA:EG:H2O molar ratio of 1:1:2. The TPA yield coefficient was 166.13/(166.13+62.06−2×18.01)=0.864, wherein 166.13, 62.06, and 18.01 are molecular weights (MWs) of TPA, EG, and H2O, respectively.
After the chemical hydrolysis of PET, TPA solids in the hydrolysate were separated from an EG-containing solution by filtration. The TPA solids in the residue were dissolved in 1 M NaOH and thereby converted to Na-TPA. After adding 2 M HCl to the Na-TPA solution, the formed TPA solids were filtered and dried in a vacuum oven at 80° C. The EG-containing solution was concentrated by evaporation and distilled to obtain purified EG. The TPA and EG purified from the PET hydrolysate were analyzed by nuclear magnetic resonance spectroscopy (NMR; Bruker 400 MHz, Billerica, Mass.) with 1H NMR and 13C NMR and compared with authentic TPA (Alfa Aesar, Haverhill, Mass.) and EG (Junsei Chemical, Tokyo, Japan) standard materials.
E. coli DH5α was used as a host strain for plasmid construction and maintenance. E. coli BL21 (DE3) was used as a host strain for OMT enzyme screening. E. coli XL1-Blue (Stratagene, San Diego, Calif.) and E. coli MG1655 (DE3) were used as host strains for whole-cell conversion. Recombinant E. coli strains were grown in lysogeny broth (LB) or on LB agar plates (2.0% w/v) containing 10 g/L tryptone, 5 g/L NaCl, and 5 g/L yeast extract. Appropriate antibiotics (50 μg/mL ampicillin, 40 μg/mL kanamycin, or 34 μg/mL chloramphenicol) were prepared and supplemented to the medium. Plasmids pKM212, pKE112, and pKA312 were constructed as described above. All plasmids and bacterial strains used in this experiment are listed in Table 1. G. oxydans KCCM 40109 (Korean Culture Center of Microorganisms, Seoul, Korea) was used as a whole-cell biocatalyst for the bioconversion of EG to GLA.
DNA cloning was performed per standard procedures. All genes except for pobA and catA genes were synthesized by IDT or GeneArt and extracted from P. putida KT2440 by polymerase chain reactions (PCR). PCR was performed using a C1000 Thermal Cycler (Bio-Rad, Hercules, Calif.). Primers and genes used for changing restriction enzyme sites are listed in Table 2 and Table 3, respectively.
For constructing plasmids pKE112TphAabc and pKM212TphB (PCA synthesis modules), plasmids pKE112 and pKM212 were digested using restriction enzymes KpnI/HindIII and EcoRI/KpnI, respectively. Corresponding TphAabc and TphB genes were digested using KpnI/HindIII and EcoRI/KpnI, respectively, and ligated into the plasmids pKE112 and pKM212.
For constructing pET28a-based plasmids for expressing genes Sl10OMT, HsOMT, MsOMT, and HsOMTHis, pET28a was digested with NdeI/XhoI, and corresponding genes were ligated. Plasmids used to directly convert TPA to PCA were constructed by ligating HsOMT and HsOMTHis into plasmid pKE112TphB using KpnI/BamHI. To investigate the PCA hydroxylation capabilities of PobA and PobAMut, these genes were ligated into plasmid pET28a using NdeI/XhoI for the construction of plasmids pET28aPobA and pET28aPobAMut, respectively. For the direct conversion of TPA to GA, the ligation of pobAMut into plasmid pKE112TphB was performed using SbfI/HindIII. For the direct conversion of TPA to PG, an 1pdC gene was introduced into plasmid pKE112TphBPobAMut using BamHI/SbfI. To construct catechol hydroxylation module pKA312PhKLMNOPQ, a phKLMNOPQ gene fragment was ligated into plasmids pKA312, pKA312PhKLM, pKA312PhKLMNOP, and pKA312PhKLMNOPQ using EcoRI/KpnI, KpnI/BamHI, BamHI/SbfI, and SbfI/HindII, respectively.
A plasmid for catechol synthesis was constructed by the ligation of aroY into pKE112TphB using KpnI/BamHI. For experiments related to evaluating preferred substrates of enzymes LpdC and AroY, corresponding plasmids pET28aLpdC and pET28aAroY were generated by the ligation of a corresponding enzyme into pET28a using NdeI/XhoI sites. For constructing a plasmid for MA synthesis, catA was introduced into plasmids pKE112 and pKE112TphBAroY using KpnI/BamHI sites.
Whole-cell conversion using engineered E. coli strains was performed as follows. Seed cultures were prepared overnight in 5 mL LB media using appropriate antibiotics. Subsequently, seed cultures were used to inoculate 1 L LB media in 2.8 L flasks and were incubated at 37° C. and 220 rpm. When cell densities reached an optical density of 0.4 at 600 nm (OD600), 0.1 mM isopropyl-p-D-thiogalactopyranoside (IPTG; Sigma-Aldrich, St. Louis, Mo.) was added to the cultures. Subsequently, an incubation temperature was adjusted to 16° C. for 16 hours to facilitate the soluble expression of the introduced genes. The engineered E. coli strains were harvested by centrifugation at 4300×g for five minutes at 10° C. The harvested cells were washed and resuspended with 50 mM Tris buffer (pH 7.0) containing 2% (w/v) glycerol.
For whole-cell conversion, microbial cell pellets were resuspended in 4 mL or 20 mL of reaction buffer with appropriate concentrations of substrates and incubated at 250 rpm and 30° C. The compositions of reaction buffers used for bioconversion in this experiment were as follows: TG-1 buffer, 50 mM Tris buffer (pH 7.0) containing 10% (w/v) glycerol; TG-2 buffer, 50 mM Tris buffer (pH 7.0) containing 2% (w/v) glycerol; TG-1/YP buffer, 50 mM Tris buffer (pH 7.0) containing 10% (w/v) glycerol, 10 g/L yeast extract, and 20 g/L peptone; TG-2/YP buffer, 50 mM Tris buffer (pH 7.0) containing 2% (w/v) glycerol, 10 g/L yeast extract, and 20 g/L peptone; TG-1/YPM buffer, TG-1/YP buffer supplemented with 2.5 mM L-methionine (Sigma-Aldrich); and TG-2/YPM buffer, TG-2/YP buffer supplemented with 2.5 mM L-methionine. All experiments were performed in triplicate unless otherwise indicated. The whole-cell conversion using the VA-2a system was performed in duplicate. TPA, PCA, GA, pyrogallol, catechol, MA, and VA standard materials were purchased from Sigma-Aldrich.
Whole-cell bioconversion by G. oxydans KCCM 40109 was performed as follows. Seed cultures were prepared overnight in 5 mL media in 50 mL conical tubes. The media contained 80 g/L sorbitol, 20 g/L yeast extract, 5 g/L (NH4)2SO4, 2 g/L KH2PO4, and 5 g/L MgSO4.7H2. The seed cultures were inoculated 1 L media in 2.8 L flasks and were incubated at 30° C. and 220 rpm. The cells were collected by centrifugation at 6500×g for eight minutes at 10° C. and were washed and resuspended in phosphate buffer (pH 7.0). Whole-cell bioconversion mixtures were prepared by appropriate resuspending concentrations of whole-cell catalysts in 4 or 20 mL buffers and were incubated at 30° C. and 250 rpm for 12 hours. Bioconversion buffers were composed of 40 g/L sorbitol, 10 g/L yeast extract, 2.5 g/L (NH4)2SO4, 1 g/L KH2PO4, and 2.5 g/L MgSO4.7H2O. The bioconversion buffers were supplemented with EG at different concentrations: 11.3, 28.6, and 67.6 mM.
The expression of eukaryotic OMT enzymes SlOMT, HsOMT, and MsOMT in E. coli BL21 (DE3) cells was verified using sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE). Recombinant E. coli BL21 (DE3) cells harboring the respective plasmids were cultivated in 100 mL LB media in 500 mL flasks at 37° C. and 220 rpm. The cultures were supplemented with 0.1 mM IPTG upon reaching an OD600 of 0.4 and were cultivated for 16 hours at 16° C. and 180 rpm. Cell pellets were collected by centrifugation at 6,500×g for 10 minutes at 4° C. and washed with 16 mL of 100 mM sodium phosphate buffer (pH 7.0).
Aliquots were prepared from the cell suspension and were used as total protein samples for SDS-PAGE. Cell lysates of recombinant E. coli were obtained by sonication (Branson 450, Marshall Scientific, Hampton, N.H.). Solid and liquid fractions containing insoluble and soluble proteins, respectively, were separated by centrifugation at 16,000×g for 20 minutes at 4° C. The separated solid fraction was resuspended in 16 mL of 100 mM sodium phosphate buffer (pH 7.0). The aliquoted cell suspension and the liquid and solid fractions were mixed with 5×SDS buffer (Biosesang, Seongnam, Korea) and boiled at 100° C. for 10 minutes. Protein samples were separated by 12% (w/v) SDS-PAGE with a pre-stained SDS standard marker (Bio-Rad).
The OD600 was measured using a spectrophotometer (xMark™, Bio-Rad). TPA and products converted from TPA were analyzed using HPLC (Agilent 1100, Agilent Technologies, Santa Clara, Calif.) equipped with an OptimaPak C18 column (RS tech, Daejeon, Korea) at a flow rate of 1.0 mL/min while maintaining a column temperature at 30° C.
A mobile phase was composed of 10% (v/v) acetonitrile in 0.1% (v/v) trifluoroacetic acid (Sigma-Aldrich) in deionized water. The injection volume was 5 μL, and UV detection was performed at 254 nm. Concentrations of EG, GLA, and glycerol were measured by HPLC (Agilent 1100) equipped with a refractive index (RI) detector and an Aminex HPX-87H column (Bio-Rad) at 65° C. with a 0.01 N H2SO4 mobile phase at a flow rate of 0.5 mL/min.
GC/MS analysis was used to verify the conversion of TPA to PCA, GA, pyrogallol, catechol, MA, and VA and the conversion of EG to GLA and quantify L-methionine. The GC/MS analysis was performed using Agilent 7890A GC/5975C MSD (Agilent Technologies) equipped with an RTX-5Sil MS capillary column (30 m×0.25 mm, 0.25 μm film thickness; Restek, Bellefonte, Pa.) with an additional 10 m integrated guard column. One microliter of a sample was injected in a splitless mode with an inlet temperature of 250° C. The oven temperature was initially maintained at 50° C. for one minute and then increased to 320° C. at a rate of 20° C./min and then maintained for 25 minutes. Helium was used as a carrier gas at a 1 mL/min flow rate, and mass spectra were recorded by scanning from 50 to 700 m/z. Temperatures of a transfer line and an ion source were set at 280 and 230° C., respectively.
The computational modeling of a protein structure PobA derived from P. putida KT2440 was performed using the Discovery Studio software (BIOVIA, San Diego, Calif.). The FAD-bound structure of PobA (PDB code: 6DLL) was used in computational docking simulations. A wild-type PobA structure does not have 4-hydroxybenzoic acid (4-HBA) in its active site, indicating that the crystal structure of wild-type PobA may not represent the complex conformation of 4-HBA and FAD. For the docking simulations, the binding conformation of FAD in the active site of P. putida KT2440 PobA was modeled using MODELER by comparing its active site with that of Pseudomonas fluorescence PobA complexed with 4-HBA and FAD (PDB codes: 1PBE and 1BGN). The structure of PobAMut (T294A/Y385F) was constructed by MODELER. The flexible docking of substrate PCA was performed using AutodockFR, and nine residues (Y386, Y201, T294, L210, S212, R220, W185, Y222, and I43) were selected as flexible residues. All parameters were set at default values for docking simulations, and the resulting binding mode was analyzed using the PyMOL software (PyMOL Molecular Graphics System, ver. 1.4.1; Schrodinger, New York, N.Y.).
E. coli XL1-Blue
E. coli MG1655 (DE3)
G. oxydans KCCM 40109
E. coli XL1-Blue with pKM212TphAabc and pKE112TphB
E. coli MG1655 (DE3) with pET28aPobA
E. coli MG1655 (DE3) with pET28aPobAMut
E. coli XL1-Blue with pKM212TphAabc and
E. coli MG1655 (DE3) with pET28aLpdC
E. coli MG1655 (DE3) with pKA312PhKLMNOPQ
E. coli MG1655 (DE3) with pET28aAroY and
E. coli XL1-Blue with pKM212TphAabc and
E. coli XL1-Blue with pKM212TphAabc,
E. coli MG1655 (DE3) with pET28aAroY
E. coli XL1-Blue with pKM212TphAabc and pKE112TphBaroY
E. coli XL1-Blue with pKE112CatA
E. coli XL1-Blue with pKM212TphAabc and
E. coli BL21 (DE3) with pET28aHsOMT
E. coli BL21 (DE3) with pET28aSlOMT
E. coli MG1655 (DE3) with pET28aHsOMT
E. coli MG1655 (DE3) with pET28aHsOMTHis
E. coli XL1-Blue with pKM212TphAabc and
Comamonas sp.
Comamonas sp.
H. sapiens
S. lycopersicum
M. sativa
CATCACCATCACCATCATGGCGATACCAAAGAACAGCG
P. putida KT2440
P. putida KT2440
P. putida KT2440
L. plantarum
P. stutzeri OX1
P. putida KT2440
For the depolymerization of PET into monomers TPA and EG, 1 g of PET in 13 mL of water was reacted, and thus the depolymerization of PET was carried out at various temperatures of 170, 200, and 230° C. using microwaves for various reaction times of 15 to 50 minutes (
The PET hydrolysate was separated into solid and liquid fractions by filtration. First, to obtain TPA, the solid fraction containing TPA was dissolved in 1 M NaOH, and Na-TPA was then precipitated as TPA by 2 M HCl at room temperature. The precipitated TPA was filtered and vacuum-dried at 80° C. (
For the separation of EG from the PET hydrolysate obtained by chemical hydrolysis, the liquid fraction was distilled, and 1H and 13C NMR analyses were performed to confirm the identity of the EG samples (
To experimentally validate the applicability of TPA obtained from waste PET as a feedstock for producing higher-value compounds than PET, PCA was selected as a first product as well as a key intermediate. PCA can serve as a precursor compound for producing various high value-added aromatic compounds or aromatic-derived compounds such as GA, pyrogallol, catechol, MA, and VA (
In this experiment, TphAabc which is TPA 1,2-dioxygenase and TphB which is DCD dehydrogenase, both derived from Comamonas sp. E6, were used for a biosynthesis route from TPA to PCA in E. coli. Unlike other corresponding enzymes of other microbes, these two enzymes have the advantage of possessing dual cofactor utilization capability for both NADH and NADPH. To dissolve TPA in a buffer solution, NaOH was added to adjust pH to 7, and then a 50 g/L TPA solution was prepared for further conversion reactions wherein TPA can be dissolved at a concentration of more than 0.5 g/L. When TPA from the PET hydrolysate was incubated with E. coli strain PCA-1 expressing TphAabc and TphB in TG-1 buffer (
GA is currently used in the pharmaceutical industry to produce trimethoprim, an antibacterial agent, and propyl gallate, an antioxidant. When a PCA hydroxylase having hydroxylating activity at the meta-position of PCA is identified, TPA can be converted to GA via PCA (
In this experiment, PobA from P. putida KT2440 was expressed in E. coli (Strain HBH-1) to test the ability of PobA from P. putida KT2440 to hydroxylate the meta-position of PCA. As a result, strain HBH-1 produced 1.4 mM GA from PCA at a molar yield of 40.1% after 12 hours in TG-2 buffer at 30° C. and 250 rpm (
First, the single-catalyst GA-1 system consisting of E. coli strain GA-1 expressing TphAabc, TphB, and PobAMut was tested to produce GA from TPA. The GA-1 system produced only 1.3 mM GA at a molar yield of 46.6% from TPA after 12 hours in TG-2 buffer, but 1.1 mM PCA remained (
Pyrogallol is another high value-added compound that can be produced from TPA via PCA. Pyrogallol is currently used as an antioxidant in the oil industry. Pyrogallol can be biosynthesized through two routes: via the decarboxylation of GA synthesized by PCA hydroxylation (
To develop biosynthesis routes for pyrogallol via GA, LpdC, which was found to be a GA decarboxylase in vitro, was introduced as a GA decarboxylation module into the GA biosynthesis route. As a result, E. coli strain PG-1a expressing TphAabc, TphB, PobAMut, and LpdC was constructed (
For relieving catechol accumulation due to LpdC promiscuity, it was necessary to convert accumulated catechol to pyrogallol. Although a catechol hydroxylase capable of converting catechol to pyrogallol has not yet been reported, a PhKLMNOPQ operon encoding a phenol hydroxylase from Pseudomonas stutzeri OX1 was recently found to exhibit promiscuous activity in converting catechol to pyrogallol. E. coli strain CH-1 expressing PhKLMNOPQ produced 2.6 mM pyrogallol from catechol at a molar yield of 67.1% after 24 hours (
To synthesize pyrogallol without forming a catechol byproduct caused by the promiscuity of LpdC, an alternative pyrogallol synthesis route via catechol was adopted. Based on the PCA synthesis module for TPA conversion to PCA (i.e., the PCA-1 system), the pyrogallol synthesis route was constructed by integrating the PCA decarboxylation module for PCA conversion to catechol and the catechol hydroxylation module for catechol conversion by PhKLMNOPQ in either a single- or double-strain system (i.e., the PG-2a and PG-2b systems, respectively) (
Next, in the PG-2a system, when the PCA synthesis strain PCA-1 and the PCA-to-pyrogallol conversion strain PDC-CH-1 expressing AroY and PhKLMNOPQ were simultaneously incubated with 3.1 mM TPA, only 0.2 mM pyrogallol was produced, but 2.4 mM catechol remained unconverted after 20 hours in TG-2 buffer (
Catechol synthesized from TPA via PCA can be converted to MA by the ring cleavage of catechol. MA is currently used in the chemical industry to produce adipic acid, which is widely used to produce plastics. To develop an MA biosynthesis route from TPA, CatA, a catechol 1,2-dioxygenase originating from P. putida KT2440, was tested as the ring-cleavage module. When 4.5 mM catechol was incubated with E. coli strain CDO-1 expressing CatA, its complete conversion to MA occurred after 10 minutes (
VA is used as the direct precursor of vanillin in the pharmaceutical industry. PCA is converted to VA by an OMT both in vitro and in vivo. To supply a methyl group to this O-methylation reaction catalyzed by an OMT, SAM is used as a co-substrate, and the adenosyl and methyl groups are supplied from ATP and methionine, respectively. Currently known OMTs are derived from eukaryotes; however, in the present invention, the expression of OMTs from various sources was tested in E. coli BL21 (DE3) to construct a VA synthesis module. Among the three OMTs examined in the present invention, HsOMT from H. sapiens, SlOMT from Solanum lycopersicum, and MsOMT from M. sativa, only HsOMT and SlOMT were expressed in active forms (
To produce VA directly from TPA via PCA, the biosynthesis route of TPA to PCA was connected to the PCA to VA route using HPAOM by constructing E. coli strain VA-1 expressing TphAabc, TphB, and HsOMT (
To improve the low PCA conversion to VA by strain VA-1 (
To further improve the low conversion of PCA to VA, conversion conditions were optimized using strain OMT-2His. In particular, since endogenous SAM regeneration may be inefficient, it was promoted by supplementing methionine in TG-2/YPM buffer. When strain OMT-2His was incubated in TG-2/YP buffer lacking supplemented methionine, only 0.9 mM VA was produced from 2.9 mM PCA after 48 hours (
In the single-catalyst system, PCA was accumulated due to the negligible conversion of PCA to VA. To bolster the conversion of PCA to VA, the present inventors developed the double-catalyst VA-2a system in which strain PCA-1 expressing TphAabc and TphB and strain OMT-2His expressing HsOMTHis (
In the VA-2b system, however, 1.4 mM TPA remained unconverted (
To experimentally validate the applicability of EG from waste PET as a feedstock, an EG sample obtained from the PET hydrolysate was tested using G. oxydans KCCM 40109 to produce GLA (
The present invention is applicable to the field of PET upcycling.
Number | Date | Country | Kind |
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10-2019-0040992 | Apr 2019 | KR | national |
Filing Document | Filing Date | Country | Kind |
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PCT/KR2020/004769 | 4/8/2020 | WO | 00 |