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+ | <meta name="Keywords" content="product,degradation,soil,pesticide,residues"/> | ||
+ | <meta name="Description" content="A product for the degradation of soil pesticide residues"/> | ||
+ | <meta name="author" content="Lucky"/> | ||
+ | <meta name="copyright" content="IGEM Team:SSTi-SZGD"/> | ||
+ | <meta name="revised" content="Lucky Yang,9/26/17"/> | ||
+ | <title>SSTi-SZGD---Experiments</title> | ||
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+ | </head> | ||
+ | <body> | ||
+ | |||
+ | |||
+ | |||
+ | <!--SSTi-SZGD--> | ||
+ | <div class="SSTi-SZGD" onselectstart="return false;" unselectable="on" style=" -moz-user-select: none;"> | ||
+ | |||
+ | <div class="header a-fadeinT"> | ||
+ | |||
+ | <div class="logo"> | ||
+ | |||
+ | <img src="https://static.igem.org/mediawiki/2017/9/9d/SSTi-SZGD_logo.png"/> | ||
+ | <span>SSTi-SZGD</span> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | <!--nav--> | ||
+ | <nav class="nav"> | ||
+ | |||
+ | <!--nav_fist--> | ||
+ | <ul> | ||
+ | |||
+ | <!--Home--> | ||
+ | <li class="Home mainnav"> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD"> | ||
+ | <span>Home</span> | ||
+ | </a> | ||
+ | </li> | ||
+ | |||
+ | <!--Project--> | ||
+ | <li class="Project mainnav hvr-overline-from-center"> | ||
+ | <span>Project</span> | ||
+ | <!--Project_nav--> | ||
+ | <ul class="unify"> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Description">Description</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Design">Design</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Degradation">Degradation</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Expression">Expression</a> | ||
+ | </li> | ||
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+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Interlab">Interlab</a> | ||
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+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Safety">Safety</a> | ||
+ | </li> | ||
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+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Notebook">Notebook</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Experiments">Experiments</a> | ||
+ | </li> | ||
+ | </ul> | ||
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+ | |||
+ | <!--Application--> | ||
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+ | <span>Application</span> | ||
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+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Software">Software</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Hardware">Hardware</a> | ||
+ | </li> | ||
+ | </ul> | ||
+ | </li> | ||
+ | |||
+ | <!--Human Practices--> | ||
+ | <li class="Human_Practices mainnav hvr-overline-from-center"> | ||
+ | <span>Human Practices</span> | ||
+ | <!--Human Practices_nav--> | ||
+ | <ul class="unify"> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Summary">Summary</a> | ||
+ | </li> | ||
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+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Outreach">Outreach</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Entrepreneurship">Entrepreneurship</a> | ||
+ | </li> | ||
+ | </ul> | ||
+ | </li> | ||
+ | |||
+ | <!--Achievement--> | ||
+ | <li class="Achievement mainnav hvr-overline-from-center"> | ||
+ | <span>Achievement</span> | ||
+ | <!--Achievement_nav--> | ||
+ | <ul class="unify"> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Parts">Parts</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Medal">Medal</a> | ||
+ | </li> | ||
+ | </ul> | ||
+ | </li> | ||
+ | |||
+ | <!--Team--> | ||
+ | <li class="Team mainnav hvr-overline-from-center"> | ||
+ | <span>Team</span> | ||
+ | <!--Team_nav--> | ||
+ | <ul class="unify"> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Team">Team</a> | ||
+ | </li> | ||
+ | <li> | ||
+ | <a href="https://2017.igem.org/Team:SSTi-SZGD/Attributions">Attributions</a> | ||
+ | </li> | ||
+ | </ul> | ||
+ | </li> | ||
+ | |||
+ | </ul> | ||
+ | |||
+ | </nav> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | <div class="topic a-bouncein"> | ||
+ | <p> | ||
+ | <span>Guardian of the wheatland</span> | ||
+ | <span>A product for the degradation of soil pesticide residues</span> | ||
+ | </p> | ||
+ | </div> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | |||
+ | |||
+ | <!--Content--> | ||
+ | <div class="Content"> | ||
+ | |||
+ | <div class="Headline">Experiments</div> | ||
+ | |||
+ | <!--MPD--> | ||
+ | <div class="MPD"> | ||
+ | |||
+ | <p class="Title">MPD Gene Experiment | ||
+ | <img src="https://static.igem.org/mediawiki/2017/4/4d/SSTi-SZGD_Experiments_icon_plus.png" class="plus"/> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/5/5e/SSTi-SZGD_Experiments_icon_reduce.png" class="reduce"/> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/1/16/SSTi-SZGD_logo_igem.png" class="igem"/> | ||
+ | </p> | ||
+ | |||
+ | <div class="content"> | ||
+ | |||
+ | <!--INTRODUCTION--> | ||
+ | <span>INTRODUCTION</span> | ||
+ | <p> | ||
+ | Synthetic organophosphates (OPS) are a group of highly toxic chemicals widely used to control various agriculture pests. Accounting for 38% of total pesticides used globally. OP pesticides are acetylcholinesterase (ACheE) inhibitors , and various clinical effects can occur from OP poisoning in humans. The growing public concern about their safety and the widespread use of OPs in modern agriculture has stimulated the development of effective and safe remediation strategies for detoxification of Ops. | ||
+ | </p> | ||
+ | <p> | ||
+ | Organophosphorus hydrolase (OPH), encoded by the opd gene of Pseudomonas diminuta MG and Flavobacterium sp. Strain ATCC27551, is a homodimeric phosphotriesterase that can hydrolyze a wide range of OPs (4, 5). Hydrolysis of OPs by OPH reduces their toxicity by several orders of magnitude (3). Practical applications of large-scale enzymatic degradation have always been limited by the cost of purification and stability of OPH. Although the use of whole cell as biocatalysts is an alternative strategy for treatment of OPs, the inaccessibility of the pesticides across the cell membrane reduces the overall catalytic efficiency (2, 6). This barrier of substrate transport can be overcome by displaying OPH on the cell surface. However, surface expression of OPH resulted in instability of the cell membrane and growth inhibition of the cells, arising from increased metabolic burden placed on the cell (2, 6). | ||
+ | </p> | ||
+ | <p> | ||
+ | Recently, an OP degradation gene (mpd) encoding methyl parathion hydrolase (MPH) was isolated from a methyl parathiondegrading bacterium Plesiomonas sp. strain M6, but it showed only 12% identity to opd gene at the amino acid level (17), suggesting | ||
+ | significant novelty of the gene-enzyme system. More recently, we cloned the mpd gene (GenBank accession no. DQ677027) from a chlorpyrifos-degrading bacterium Stenotrophomonas sp. Strain YC-1 (18). In the present study, to enable secretion of MPH to the periplasm of E. coli, we used the twin-arginine signal peptide of trimethylamine N-oxide reductase (TorA) from E. coli (19). We apply light control system to express a gene that encodes hydrolase to degrade pesticides residues. | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/7/74/SSTi-SZGD_Experiments_MPD_INTRODUCTION.png"/> | ||
+ | |||
+ | <!--MATERIALS AND METHODS--> | ||
+ | <span>MATERIALS AND METHODS</span> | ||
+ | <p class="Subtitle">Bacterial strains and Plasmid Construction</p> | ||
+ | <p> | ||
+ | The DH5 alpha E.coli strain was used to amplify plasmid and a negative expression control. The Luria Bertani broth medium used in this study was composed of 1.0 % (w/v) tryptone , 0.5% (w/v) yeast extract and 0.5% (w/v) NaCl in distilled water . the ph was adjusted to 7.0 with a NaOH solution-soid plates were obtained by adding 1.5% (w/v) agar . the antibiotic 1000ug/ml Penicillin and streptomycin (final concentration) was added during plate preparation after solution cooling or to the LB medium prior to culture. | ||
+ | </p> | ||
+ | <p> | ||
+ | The torA gene fragment encoding the signal peptide and the first four amino acid residues of the mature TorA was amplified by polymerase chain reaction (PCR) from plasmid pSCTorAGFP using primers P1 and P2. The PCR products were digested with EcoRI and BamHI, and then ligated into similarly digested pUC18 to generate pUT18. The mpd gene was amplified by PCR from plasmid pMDQ using primers P3 and P4. The PCR products were digested with BamHI and HindIII, and then ligated into similarly digested pUT18 to generate pUTM18. To construct a control plasmid expressing cytoplasmic MPH, the mpd gene was amplified by PCR from plasmid pMDQ usingprimers P5 and P4. The PCR products were digested with EcoRI and HindII I, and then ligated into similarly digested pUC18 to generate pUM18. All plasmid constructions were verified by DNA sequence analysis. Transformation of the plasmid into E. coli was carried out by using the below method. | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/3/34/SSTi-SZGD_Experiments_MPD_MATERIALS.png"/> | ||
+ | <p class="Subtitle">Cell condition and Cell Fractionation</p> | ||
+ | <p> | ||
+ | Sub-cultures were grown overnight to added suitable the concentration of antibiotics in 5ml LB and used to inoculate 30ml LB liquid to a starting OD600 of 0.5, cells were shaking culture at 37℃, when cultures reached a cell density of 1.0~2.0, used silver paper to make the culture be in dark ambient induce recombinant protein expression. | ||
+ | </p> | ||
+ | <p> | ||
+ | Cells were fractionated to yield cytoplasmic by the cell lysis solution ,and periplasmic samples by the Arginine buffer as follows, the E.coil strain cell medium by centrifugation 10000rpm, 5 min, and the 1 g cell added 10ml concentration of arginine buffer 0.4mol/L ,pH8.0, after extracting time 45 min on the ice by the centrifugation 10000rpm, the supernatant is periplasmic. | ||
+ | </p> | ||
+ | <p> | ||
+ | And we used “Soluble protein solution” to extract the cytoplasmic, used in this study was composed of 0.0625mol/L Tris- HCl, the ph was adjusted to 6.8 , 2% (w/v) SDS, 10%(w/v) glycerol and 5% 2-mercaptoethanol were obtained extract . Take the strain centrifugation 10000rpm,5min at 4℃, 15ml PB wash cell, centrifugation by the bacterium suspension, discard the supernatant, Repeat that steps twice. Added 200ul to soluble protein solution, to make the bacteria fully suspended and,10min boilingwater to make it inactive. Centrifugation 12000rpm,15min collect supernatant, keep at -20℃. | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/2/2c/SSTi-SZGD_Experiments_MPD_MATERIALS2.png"/> | ||
+ | |||
+ | <!--Analytical assays--> | ||
+ | <span>Analytical assays</span> | ||
+ | <p> | ||
+ | Periplasmic protein were (OD600=1.0) in 100 mM phosphate buffer (pH 7.4). MPH activity assay mixtures (1 mL, 3% methanol) contained 50 μg/mL methyl parathion (added from a 10 mg/mL methanol stock solution), 870 μL of 100 mM phosphate buffer (pH 7.4), and 100 μL of cells. The enzyme activity was measured using a UV/VIS spectrophotometer (UV-1601PC; Shimadzu Corp., Kyoto, Japan) at 30 C by monitoring the increases of linear optical density over time at 405 nm as methyl parathion was hydrolyzed to p-nitrophenol (ε405=17,700 M-1 cm-1). Activities were expressed as units (1 μmol of p-nitrophenol formed per minute) per OD600 whole cells. | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/9/98/SSTi-SZGD_Experiments_MPD_Analytical.png"/> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | <!--MHEI--> | ||
+ | <div class="MHEI"> | ||
+ | |||
+ | <p class="Title">Project—Mhei-mcherry in E.Coli DH5α Strain | ||
+ | <img src="https://static.igem.org/mediawiki/2017/4/4d/SSTi-SZGD_Experiments_icon_plus.png" class="plus"/> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/5/5e/SSTi-SZGD_Experiments_icon_reduce.png" class="reduce"/> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/1/16/SSTi-SZGD_logo_igem.png" class="igem"/> | ||
+ | |||
+ | </p> | ||
+ | |||
+ | <div class="content"> | ||
+ | |||
+ | <!--Background--> | ||
+ | <span>Background</span> | ||
+ | <p> | ||
+ | There is only one Earth for human beings living,we concerned about the environmental problems but can’t reduce its damage. Our project aim at pesticide residues,and degradation of pesticide residues in soil and plants which serves a positive role in Earth and maintaining balance. | ||
+ | </p> | ||
+ | <p> | ||
+ | Carbendazim,alias carbendazol、benzimidazole 44; belongs to the Carbamate Pesticide, is a highly activity, keenly priced, broad-spectrum fungicide widely used for the control of plant fungal diseases on arable crops、fruits、vegetables and ornamentals which results in potential environmental contamination. Annual output just after Organphosphorous pesticide and ranked the second place. This kind of pesticide has a control effect on a variety of crops caused by fungi (such as semi-bacterial bacteria, multi-seed bacteria) and can be used for foliar spraying, seed treatment and soil treatment. Also can prevent wheat disease, anti-rice disease, anti-fruit and vegetable poisoning, prevention and control of cotton diseases etc. On the contrary, there are many reports on its toxicity at both here and abroad,such as it has toxicity to Low aquatic organisms、low soil animals、 plants etc. It can inhibit the root development of alfalfa affect the number of nodulation and nitrogen fixation capacity too. Carbendazim also occurs in the mammal’s stomach nitrosation reaction, and formation of nitrite compounds, causing rodent testis and epididymal damage, may also damage the liver and endocrine system, cause animals have mutagenic and teratogenic effects. What ‘more,Carbendazim pesticides after rainwater scouring or dust landing will get into the soil, once entering into the soil mays effect microbial community to grow. | ||
+ | </p> | ||
+ | <p> | ||
+ | - Reference by Biodegradation of carbendazim by a novel actinobacterium Rhodococcus jialingiae djl-6-2 | ||
+ | </p> | ||
+ | |||
+ | <!--Materials and methods--> | ||
+ | <span>Materials and methods</span> | ||
+ | <p>Construction of recombinant plasmid pLEVI(408)-mhei-mcherry(1) 6545bp</p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/3/31/SSTi-SZGD_Experiments_MHEI_MATERIALS.jpeg"/> | ||
+ | |||
+ | <!--Cloning and expression of MheI--> | ||
+ | <span>Cloning and expression of MheI</span> | ||
+ | <p> | ||
+ | Mycobacterium sp.SD-4 is a Carbendazim-degrading bacterium,and its MheI hydrolases play a role,we synthesize MheI gene and subcloned into light-off plasmid. Use pMD 18-T vector transformed it into E.coli DH5α Strain which we have Optimization codon .Culture bacteria in 18 h LB medium (Fig 1).. Then,use TAKARA MiniBEST Plasmid Purification Kit Ver.4.0 to extraction plasmid (Fig 2). | ||
+ | </p> | ||
+ | <p> | ||
+ | -Reference by Identification of the key amino acid sites of the Carbendazim hydrolase(MheI)from a novel Carbendazim-degrading strain Mycobacteria sp.SD-4 | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/0/0c/SSTi-SZGD_Experiments_MHEI_Cloning.jpeg"/> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/e/ec/SSTi-SZGD_Experiments_MHEI_Cloning2.jpeg"/> | ||
+ | |||
+ | <!--Verification of recombinant gene--> | ||
+ | <p class="Subtitle">Verification of recombinant gene</p> | ||
+ | <p> | ||
+ | Design two primers one is ColonyF(GCGGCGTAGCTTTTATGCTG) the other is Mhei-colonyR(CACATAGGGGTTCAGCGAGG) Pick ten typical colony from the plate【Fig 3】and add in PCR Reaction system(Use TAKARA Taq). Agarose gel test the result.【Fig 4】. | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/0/0b/SSTi-SZGD_Experiments_MHEI_Verification.jpeg"/> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/1/1f/SSTi-SZGD_Experiments_MHEI_Verification2.jpeg"/> | ||
+ | |||
+ | <!--Protein extraction--> | ||
+ | <p class="Subtitle">Protein extraction</p> | ||
+ | <p> | ||
+ | Pick typical colony in 5 mL LB liquid medium and incubated for 17 h to OD600 about 0.5 and remove 2 mL bacteria liquid in 30 mL LB liquid medium, incubated and pack paper all over for 17 h to OD600 was about 2. Extraction of cytoplasmic protein by ultrasonic crushing. Make SDS-PAGE【Fig 5】(12% Resolver and 6% Stacker) | ||
+ | </p> | ||
+ | <p> | ||
+ | -Reference by ISOLATION AND CHARACTERIZATION OF | ||
+ | CARBENDAZIM-DEGRADING STRAINS,CLONING AND EXPRESSION OF THE MheI GENE | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/1/17/SSTi-SZGD_Experiments_MHEI_Protein.jpeg"/> | ||
+ | |||
+ | <!--Determination of protein content--> | ||
+ | <p class="Subtitle">Determination of protein content</p> | ||
+ | <p> | ||
+ | Coomassie brilliant blue determination of protein content,preparation of bovine serum albumin standard curve. | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/1/17/SSTi-SZGD_Experiments_MHEI_Determination.png"/> | ||
+ | <p> | ||
+ | We calculated the total protein content of MheI was about 33.969 ug/ mL. | ||
+ | </p> | ||
+ | |||
+ | <!--Enzyme activity assay--> | ||
+ | <p class="Subtitle">Enzyme activity assay</p> | ||
+ | <p> | ||
+ | Enzymatic activity of MheI-6F was examined using MBC as the substrate. Samples were pretreated according to a protocol adapted from Xu et al. (2006) and improved for determining the catalytic activity of MheI-6F in our study. Five milliliters of hydrolyzing system that includes 0.2 mol/L disodium hydrogen phosphate—0.1 mol/L citric acid buffer solution (pH 7.0) and 40 μmol/L MBC was pipetted into three 10 mL flasks.MheI-6F was added to each flask at the final concentration of 0.10 μg/mL. The mixtures were then incubated at 37°C for 1 hr, and warmed in a hot-water bath for 5 min to terminate the reaction. Five milliliters of ethyl acetate was added to each flask to terminate enzyme activity after 1 hr incubation. After 2 min of extraction by ethyl acetate, the organic phase was collected and dried over anhydrous sodium sulfate. Hydrolysis of MBC by MheI-6F was measured by examining the absorbance of MBC at 287 nm by ultraviolet spectrophotometry (U-3310, Hitachi Limited, Japan) | ||
+ | </p> | ||
+ | <p> | ||
+ | -reference by Hydrolysis mechanism of Carbendazim hydrolase from the strain microbacterium sp.djl-6F | ||
+ | </p> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/1/1b/SSTi-SZGD_Experiments_MHEI_Enzyme.png"/> | ||
+ | |||
+ | <!--Results and Analysis--> | ||
+ | <span>Results and Analysis</span> | ||
+ | <p> | ||
+ | The Carbendazim hydrolase was a constitutive enzyme,mainly located in cell.The optimum Ph value and temperature for the Carbendazim hydrolyzing activity of this enzyme was 7.0 and 37℃. | ||
+ | </p> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | |||
+ | |||
+ | <!--footer--> | ||
+ | <footer class="footer_box"> | ||
+ | |||
+ | <div class="footer"> | ||
+ | |||
+ | <!--sponsor--> | ||
+ | <div class="sponsor"> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/9/9d/SSTi-SZGD_logo.png"/> | ||
+ | <img src="https://static.igem.org/mediawiki/2017/e/e0/SSTi-SZGD_logo_SSTI.png"/> | ||
+ | </div> | ||
+ | |||
+ | <!--copyright--> | ||
+ | <div class="copyright"> | ||
+ | <p> | ||
+ | <span class="left">A product for the degradation of soil pesticide residues</span> | ||
+ | <span class="right">Copyright © 2017 Lucky power by IGEM Team:SSTi-SZGD</span> | ||
+ | </p> | ||
+ | </div> | ||
+ | |||
+ | </div> | ||
+ | |||
+ | |||
+ | </footer> | ||
+ | |||
+ | |||
+ | |||
+ | </body> | ||
+ | </html> |
Revision as of 09:05, 26 September 2017
Guardian of the wheatland A product for the degradation of soil pesticide residues
MPD Gene Experiment
Synthetic organophosphates (OPS) are a group of highly toxic chemicals widely used to control various agriculture pests. Accounting for 38% of total pesticides used globally. OP pesticides are acetylcholinesterase (ACheE) inhibitors , and various clinical effects can occur from OP poisoning in humans. The growing public concern about their safety and the widespread use of OPs in modern agriculture has stimulated the development of effective and safe remediation strategies for detoxification of Ops.
Organophosphorus hydrolase (OPH), encoded by the opd gene of Pseudomonas diminuta MG and Flavobacterium sp. Strain ATCC27551, is a homodimeric phosphotriesterase that can hydrolyze a wide range of OPs (4, 5). Hydrolysis of OPs by OPH reduces their toxicity by several orders of magnitude (3). Practical applications of large-scale enzymatic degradation have always been limited by the cost of purification and stability of OPH. Although the use of whole cell as biocatalysts is an alternative strategy for treatment of OPs, the inaccessibility of the pesticides across the cell membrane reduces the overall catalytic efficiency (2, 6). This barrier of substrate transport can be overcome by displaying OPH on the cell surface. However, surface expression of OPH resulted in instability of the cell membrane and growth inhibition of the cells, arising from increased metabolic burden placed on the cell (2, 6).
Recently, an OP degradation gene (mpd) encoding methyl parathion hydrolase (MPH) was isolated from a methyl parathiondegrading bacterium Plesiomonas sp. strain M6, but it showed only 12% identity to opd gene at the amino acid level (17), suggesting significant novelty of the gene-enzyme system. More recently, we cloned the mpd gene (GenBank accession no. DQ677027) from a chlorpyrifos-degrading bacterium Stenotrophomonas sp. Strain YC-1 (18). In the present study, to enable secretion of MPH to the periplasm of E. coli, we used the twin-arginine signal peptide of trimethylamine N-oxide reductase (TorA) from E. coli (19). We apply light control system to express a gene that encodes hydrolase to degrade pesticides residues.
MATERIALS AND METHODSBacterial strains and Plasmid Construction
The DH5 alpha E.coli strain was used to amplify plasmid and a negative expression control. The Luria Bertani broth medium used in this study was composed of 1.0 % (w/v) tryptone , 0.5% (w/v) yeast extract and 0.5% (w/v) NaCl in distilled water . the ph was adjusted to 7.0 with a NaOH solution-soid plates were obtained by adding 1.5% (w/v) agar . the antibiotic 1000ug/ml Penicillin and streptomycin (final concentration) was added during plate preparation after solution cooling or to the LB medium prior to culture.
The torA gene fragment encoding the signal peptide and the first four amino acid residues of the mature TorA was amplified by polymerase chain reaction (PCR) from plasmid pSCTorAGFP using primers P1 and P2. The PCR products were digested with EcoRI and BamHI, and then ligated into similarly digested pUC18 to generate pUT18. The mpd gene was amplified by PCR from plasmid pMDQ using primers P3 and P4. The PCR products were digested with BamHI and HindIII, and then ligated into similarly digested pUT18 to generate pUTM18. To construct a control plasmid expressing cytoplasmic MPH, the mpd gene was amplified by PCR from plasmid pMDQ usingprimers P5 and P4. The PCR products were digested with EcoRI and HindII I, and then ligated into similarly digested pUC18 to generate pUM18. All plasmid constructions were verified by DNA sequence analysis. Transformation of the plasmid into E. coli was carried out by using the below method.
Cell condition and Cell Fractionation
Sub-cultures were grown overnight to added suitable the concentration of antibiotics in 5ml LB and used to inoculate 30ml LB liquid to a starting OD600 of 0.5, cells were shaking culture at 37℃, when cultures reached a cell density of 1.0~2.0, used silver paper to make the culture be in dark ambient induce recombinant protein expression.
Cells were fractionated to yield cytoplasmic by the cell lysis solution ,and periplasmic samples by the Arginine buffer as follows, the E.coil strain cell medium by centrifugation 10000rpm, 5 min, and the 1 g cell added 10ml concentration of arginine buffer 0.4mol/L ,pH8.0, after extracting time 45 min on the ice by the centrifugation 10000rpm, the supernatant is periplasmic.
And we used “Soluble protein solution” to extract the cytoplasmic, used in this study was composed of 0.0625mol/L Tris- HCl, the ph was adjusted to 6.8 , 2% (w/v) SDS, 10%(w/v) glycerol and 5% 2-mercaptoethanol were obtained extract . Take the strain centrifugation 10000rpm,5min at 4℃, 15ml PB wash cell, centrifugation by the bacterium suspension, discard the supernatant, Repeat that steps twice. Added 200ul to soluble protein solution, to make the bacteria fully suspended and,10min boilingwater to make it inactive. Centrifugation 12000rpm,15min collect supernatant, keep at -20℃.
Analytical assaysPeriplasmic protein were (OD600=1.0) in 100 mM phosphate buffer (pH 7.4). MPH activity assay mixtures (1 mL, 3% methanol) contained 50 μg/mL methyl parathion (added from a 10 mg/mL methanol stock solution), 870 μL of 100 mM phosphate buffer (pH 7.4), and 100 μL of cells. The enzyme activity was measured using a UV/VIS spectrophotometer (UV-1601PC; Shimadzu Corp., Kyoto, Japan) at 30 C by monitoring the increases of linear optical density over time at 405 nm as methyl parathion was hydrolyzed to p-nitrophenol (ε405=17,700 M-1 cm-1). Activities were expressed as units (1 μmol of p-nitrophenol formed per minute) per OD600 whole cells.
Project—Mhei-mcherry in E.Coli DH5α Strain
There is only one Earth for human beings living,we concerned about the environmental problems but can’t reduce its damage. Our project aim at pesticide residues,and degradation of pesticide residues in soil and plants which serves a positive role in Earth and maintaining balance.
Carbendazim,alias carbendazol、benzimidazole 44; belongs to the Carbamate Pesticide, is a highly activity, keenly priced, broad-spectrum fungicide widely used for the control of plant fungal diseases on arable crops、fruits、vegetables and ornamentals which results in potential environmental contamination. Annual output just after Organphosphorous pesticide and ranked the second place. This kind of pesticide has a control effect on a variety of crops caused by fungi (such as semi-bacterial bacteria, multi-seed bacteria) and can be used for foliar spraying, seed treatment and soil treatment. Also can prevent wheat disease, anti-rice disease, anti-fruit and vegetable poisoning, prevention and control of cotton diseases etc. On the contrary, there are many reports on its toxicity at both here and abroad,such as it has toxicity to Low aquatic organisms、low soil animals、 plants etc. It can inhibit the root development of alfalfa affect the number of nodulation and nitrogen fixation capacity too. Carbendazim also occurs in the mammal’s stomach nitrosation reaction, and formation of nitrite compounds, causing rodent testis and epididymal damage, may also damage the liver and endocrine system, cause animals have mutagenic and teratogenic effects. What ‘more,Carbendazim pesticides after rainwater scouring or dust landing will get into the soil, once entering into the soil mays effect microbial community to grow.
- Reference by Biodegradation of carbendazim by a novel actinobacterium Rhodococcus jialingiae djl-6-2
Materials and methodsConstruction of recombinant plasmid pLEVI(408)-mhei-mcherry(1) 6545bp
Cloning and expression of MheIMycobacterium sp.SD-4 is a Carbendazim-degrading bacterium,and its MheI hydrolases play a role,we synthesize MheI gene and subcloned into light-off plasmid. Use pMD 18-T vector transformed it into E.coli DH5α Strain which we have Optimization codon .Culture bacteria in 18 h LB medium (Fig 1).. Then,use TAKARA MiniBEST Plasmid Purification Kit Ver.4.0 to extraction plasmid (Fig 2).
-Reference by Identification of the key amino acid sites of the Carbendazim hydrolase(MheI)from a novel Carbendazim-degrading strain Mycobacteria sp.SD-4
Verification of recombinant gene
Design two primers one is ColonyF(GCGGCGTAGCTTTTATGCTG) the other is Mhei-colonyR(CACATAGGGGTTCAGCGAGG) Pick ten typical colony from the plate【Fig 3】and add in PCR Reaction system(Use TAKARA Taq). Agarose gel test the result.【Fig 4】.
Protein extraction
Pick typical colony in 5 mL LB liquid medium and incubated for 17 h to OD600 about 0.5 and remove 2 mL bacteria liquid in 30 mL LB liquid medium, incubated and pack paper all over for 17 h to OD600 was about 2. Extraction of cytoplasmic protein by ultrasonic crushing. Make SDS-PAGE【Fig 5】(12% Resolver and 6% Stacker)
-Reference by ISOLATION AND CHARACTERIZATION OF CARBENDAZIM-DEGRADING STRAINS,CLONING AND EXPRESSION OF THE MheI GENE
Determination of protein content
Coomassie brilliant blue determination of protein content,preparation of bovine serum albumin standard curve.
We calculated the total protein content of MheI was about 33.969 ug/ mL.
Enzyme activity assay
Enzymatic activity of MheI-6F was examined using MBC as the substrate. Samples were pretreated according to a protocol adapted from Xu et al. (2006) and improved for determining the catalytic activity of MheI-6F in our study. Five milliliters of hydrolyzing system that includes 0.2 mol/L disodium hydrogen phosphate—0.1 mol/L citric acid buffer solution (pH 7.0) and 40 μmol/L MBC was pipetted into three 10 mL flasks.MheI-6F was added to each flask at the final concentration of 0.10 μg/mL. The mixtures were then incubated at 37°C for 1 hr, and warmed in a hot-water bath for 5 min to terminate the reaction. Five milliliters of ethyl acetate was added to each flask to terminate enzyme activity after 1 hr incubation. After 2 min of extraction by ethyl acetate, the organic phase was collected and dried over anhydrous sodium sulfate. Hydrolysis of MBC by MheI-6F was measured by examining the absorbance of MBC at 287 nm by ultraviolet spectrophotometry (U-3310, Hitachi Limited, Japan)
-reference by Hydrolysis mechanism of Carbendazim hydrolase from the strain microbacterium sp.djl-6F
Results and AnalysisThe Carbendazim hydrolase was a constitutive enzyme,mainly located in cell.The optimum Ph value and temperature for the Carbendazim hydrolyzing activity of this enzyme was 7.0 and 37℃.