CN115896154A - A microbial fluorescence sensor for detecting p-nitrophenol and its preparation method and application - Google Patents
A microbial fluorescence sensor for detecting p-nitrophenol and its preparation method and application Download PDFInfo
- Publication number
- CN115896154A CN115896154A CN202210937245.1A CN202210937245A CN115896154A CN 115896154 A CN115896154 A CN 115896154A CN 202210937245 A CN202210937245 A CN 202210937245A CN 115896154 A CN115896154 A CN 115896154A
- Authority
- CN
- China
- Prior art keywords
- nitrophenol
- pnpr
- seq
- gfp
- fluorescence sensor
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- BTJIUGUIPKRLHP-UHFFFAOYSA-N 4-nitrophenol Chemical compound OC1=CC=C([N+]([O-])=O)C=C1 BTJIUGUIPKRLHP-UHFFFAOYSA-N 0.000 title claims abstract description 49
- 230000000813 microbial effect Effects 0.000 title claims abstract description 29
- 238000002360 preparation method Methods 0.000 title claims abstract description 10
- 238000001514 detection method Methods 0.000 claims abstract description 13
- 108010043121 Green Fluorescent Proteins Proteins 0.000 claims abstract description 11
- 102000004144 Green Fluorescent Proteins Human genes 0.000 claims abstract description 7
- 239000005090 green fluorescent protein Substances 0.000 claims abstract description 6
- 239000013612 plasmid Substances 0.000 claims description 24
- 239000012634 fragment Substances 0.000 claims description 12
- 239000002773 nucleotide Substances 0.000 claims description 11
- 125000003729 nucleotide group Chemical group 0.000 claims description 11
- 108090000623 proteins and genes Proteins 0.000 claims description 11
- 230000004927 fusion Effects 0.000 claims description 8
- 238000011084 recovery Methods 0.000 claims description 7
- 230000015556 catabolic process Effects 0.000 claims description 6
- 238000006731 degradation reaction Methods 0.000 claims description 6
- 241000894006 Bacteria Species 0.000 claims description 5
- 229930027917 kanamycin Natural products 0.000 claims description 5
- 229960000318 kanamycin Drugs 0.000 claims description 5
- SBUJHOSQTJFQJX-NOAMYHISSA-N kanamycin Chemical compound O[C@@H]1[C@@H](O)[C@H](O)[C@@H](CN)O[C@@H]1O[C@H]1[C@H](O)[C@@H](O[C@@H]2[C@@H]([C@@H](N)[C@H](O)[C@@H](CO)O2)O)[C@H](N)C[C@@H]1N SBUJHOSQTJFQJX-NOAMYHISSA-N 0.000 claims description 5
- 229930182823 kanamycin A Natural products 0.000 claims description 5
- 230000004044 response Effects 0.000 claims description 5
- 239000013598 vector Substances 0.000 claims description 5
- 239000007787 solid Substances 0.000 claims description 4
- 239000012880 LB liquid culture medium Substances 0.000 claims description 3
- 241000320117 Pseudomonas putida KT2440 Species 0.000 claims description 3
- 230000029087 digestion Effects 0.000 claims description 3
- 102000034356 gene-regulatory proteins Human genes 0.000 claims description 3
- 108091006104 gene-regulatory proteins Proteins 0.000 claims description 3
- 239000013600 plasmid vector Substances 0.000 claims description 3
- 239000003242 anti bacterial agent Substances 0.000 claims description 2
- 238000011897 real-time detection Methods 0.000 claims description 2
- 239000000356 contaminant Substances 0.000 claims 2
- 230000003213 activating effect Effects 0.000 claims 1
- 230000003115 biocidal effect Effects 0.000 claims 1
- 238000012258 culturing Methods 0.000 claims 1
- 239000007850 fluorescent dye Substances 0.000 claims 1
- 230000001939 inductive effect Effects 0.000 claims 1
- 239000000523 sample Substances 0.000 claims 1
- 230000002194 synthesizing effect Effects 0.000 claims 1
- 239000003344 environmental pollutant Substances 0.000 abstract description 18
- 231100000719 pollutant Toxicity 0.000 abstract description 18
- 230000035945 sensitivity Effects 0.000 abstract description 5
- 244000005700 microbiome Species 0.000 abstract description 2
- 108700005075 Regulator Genes Proteins 0.000 abstract 1
- 238000003752 polymerase chain reaction Methods 0.000 description 13
- 239000000243 solution Substances 0.000 description 11
- 238000002965 ELISA Methods 0.000 description 7
- 230000001580 bacterial effect Effects 0.000 description 7
- 239000001963 growth medium Substances 0.000 description 7
- 230000007613 environmental effect Effects 0.000 description 6
- 238000001917 fluorescence detection Methods 0.000 description 6
- 239000002609 medium Substances 0.000 description 6
- 238000000034 method Methods 0.000 description 6
- 238000012408 PCR amplification Methods 0.000 description 4
- 238000012544 monitoring process Methods 0.000 description 4
- 239000010413 mother solution Substances 0.000 description 4
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 description 3
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 3
- 108091027981 Response element Proteins 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 238000010276 construction Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 108091008146 restriction endonucleases Proteins 0.000 description 3
- 239000002904 solvent Substances 0.000 description 3
- 239000011550 stock solution Substances 0.000 description 3
- 108020004414 DNA Proteins 0.000 description 2
- 241000620209 Escherichia coli DH5[alpha] Species 0.000 description 2
- QIGBRXMKCJKVMJ-UHFFFAOYSA-N Hydroquinone Chemical compound OC1=CC=C(O)C=C1 QIGBRXMKCJKVMJ-UHFFFAOYSA-N 0.000 description 2
- 108091028043 Nucleic acid sequence Proteins 0.000 description 2
- 108700008625 Reporter Genes Proteins 0.000 description 2
- YCIMNLLNPGFGHC-UHFFFAOYSA-N catechol Chemical compound OC1=CC=CC=C1O YCIMNLLNPGFGHC-UHFFFAOYSA-N 0.000 description 2
- 238000001976 enzyme digestion Methods 0.000 description 2
- 238000010353 genetic engineering Methods 0.000 description 2
- 238000012216 screening Methods 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- IQUPABOKLQSFBK-UHFFFAOYSA-N 2-nitrophenol Chemical compound OC1=CC=CC=C1[N+]([O-])=O IQUPABOKLQSFBK-UHFFFAOYSA-N 0.000 description 1
- 101001121408 Homo sapiens L-amino-acid oxidase Proteins 0.000 description 1
- 102100026388 L-amino-acid oxidase Human genes 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 239000003570 air Substances 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 229940088710 antibiotic agent Drugs 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009614 chemical analysis method Methods 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 238000010367 cloning Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000008878 coupling Effects 0.000 description 1
- 238000010168 coupling process Methods 0.000 description 1
- 238000005859 coupling reaction Methods 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 239000000975 dye Substances 0.000 description 1
- 238000002848 electrochemical method Methods 0.000 description 1
- 238000004520 electroporation Methods 0.000 description 1
- 231100000049 endocrine disruptor Toxicity 0.000 description 1
- 239000000598 endocrine disruptor Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000013604 expression vector Substances 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 239000002054 inoculum Substances 0.000 description 1
- 238000004811 liquid chromatography Methods 0.000 description 1
- 238000004949 mass spectrometry Methods 0.000 description 1
- 230000037353 metabolic pathway Effects 0.000 description 1
- 125000002496 methyl group Chemical group [H]C([H])([H])* 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 239000012452 mother liquor Substances 0.000 description 1
- LQNUZADURLCDLV-UHFFFAOYSA-N nitrobenzene Chemical compound [O-][N+](=O)C1=CC=CC=C1 LQNUZADURLCDLV-UHFFFAOYSA-N 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 238000011002 quantification Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000008844 regulatory mechanism Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000005060 rubber Substances 0.000 description 1
- 238000012163 sequencing technique Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000004611 spectroscopical analysis Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Images
Landscapes
- Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
Abstract
本发明公开了微生物荧光传感器及其制备方法和应用。所述微生物荧光传感器包括含有启动子PC1及其调控基因pnpR的感应元件和含有绿色荧光蛋白GFP的报告元件。所述的微生物荧光传感器能够特异性地响应不同浓度的对硝基苯酚,而产生不同RFU值的荧光,并将对硝基苯酚浓度与自发光RFU值进行偶联。本发明所述的微生物荧光传感器可实现对硝基苯酚的特异性识别和检测,且操作简便、灵敏度高,可在低浓度范围线性检测污染物分子,因此具有很好的应用前景。
The invention discloses a microbial fluorescence sensor, a preparation method and an application thereof. The microorganism fluorescence sensor comprises a sensing element containing a promoter P C1 and its regulatory gene pnpR and a reporter element containing a green fluorescent protein GFP. The microbial fluorescence sensor can specifically respond to different concentrations of p-nitrophenol to generate fluorescence with different RFU values, and couple the p-nitrophenol concentration with the self-luminous RFU value. The microbial fluorescence sensor of the invention can realize the specific identification and detection of p-nitrophenol, has the advantages of simple operation, high sensitivity, and can linearly detect pollutant molecules in a low concentration range, so it has a good application prospect.
Description
技术领域Technical Field
本发明属于基因工程和分子生物学技术领域,具体涉及一种检测对硝基苯酚的微生物荧光传感器及其制备方法和应用。The invention belongs to the technical field of genetic engineering and molecular biology, and specifically relates to a microbial fluorescence sensor for detecting p-nitrophenol and a preparation method and application thereof.
背景技术Background Art
对硝基苯酚(p-Nitrophenol,PNP)主要来源于农药、染料、医药、橡胶等领域,具有“三致”作用,被认定为环境内分泌干扰物,并被列入我国优先控制污染物。因此,对硝基苯酚的有效检测对于人们的健康以及环境保护具有重要的意义。p-Nitrophenol (PNP) is mainly derived from pesticides, dyes, medicines, rubber and other fields. It has "three-hazard" effects and is identified as an environmental endocrine disruptor and is listed as a priority controlled pollutant in my country. Therefore, the effective detection of p-nitrophenol is of great significance to people's health and environmental protection.
目前,常见的用于对硝基苯酚测定方法主要有:光谱法、电化学法、气相色谱法、液相色谱法、色谱质谱联用法等,这些化学分析方法大多存在操作繁琐、仪器昂贵、分析成本高等问题。近年来,微生物传感器因其选择性好,灵敏度高,使用简便,成本低,在复杂系统中连续在线监测等特点,作为环境监测的新型技术成为研究的热点。利用基因工程手段对微生物进行基因改造,从而使得微生物对环境中的某些特殊毒性物质或物理胁迫反应,产生可以测量的信号,最终实现对空气、土壤或水中的特定化学物质的检测和量化。At present, the common methods for the determination of p-nitrophenol are: spectroscopy, electrochemical method, gas chromatography, liquid chromatography, chromatography-mass spectrometry, etc. Most of these chemical analysis methods have the problems of cumbersome operation, expensive instruments, and high analysis cost. In recent years, microbial sensors have become a hot topic of research as a new technology for environmental monitoring due to their good selectivity, high sensitivity, ease of use, low cost, and continuous online monitoring in complex systems. Microorganisms are genetically modified by genetic engineering methods, so that they respond to certain special toxic substances or physical stresses in the environment and produce measurable signals, ultimately realizing the detection and quantification of specific chemicals in the air, soil or water.
微生物传感器主要由感应元件和报告基因组成,感应元件通常由被检测化合物相关的特异识别蛋白基因和启动子元件构成,决定了该系统的专一性;而报告基因不需要特异性识别,其表达量和强度反应该系统的灵敏度和检测阈值。目前,尽管对硝基苯酚降解菌株的降解特性、代谢途径及调控机制研究较多,但对硝基苯酚特异性响应元件的发掘限制了对硝基苯酚微生物传感器的开发。Microbial sensors are mainly composed of sensing elements and reporter genes. The sensing elements are usually composed of specific recognition protein genes and promoter elements related to the detected compounds, which determine the specificity of the system; while the reporter gene does not require specific recognition, and its expression level and intensity reflect the sensitivity and detection threshold of the system. At present, although there are many studies on the degradation characteristics, metabolic pathways and regulatory mechanisms of p-nitrophenol-degrading strains, the discovery of p-nitrophenol-specific response elements has limited the development of p-nitrophenol microbial sensors.
发明内容Summary of the invention
为解决上述技术问题,本发明提供了利用高效降解菌株的特异性响应元件合成微生物荧光传感器的制备方法及其应用,所述微生物荧光传感器中含有调控蛋白及其相应启动子和绿色荧光蛋白,可以实现对硝基苯酚的特异性线性检测,且灵敏度高,适用于环境监测,具有广阔的应用前景。In order to solve the above technical problems, the present invention provides a preparation method and application of a microbial fluorescent sensor synthesized by using the specific response element of an efficient degradation strain. The microbial fluorescent sensor contains a regulatory protein and its corresponding promoter and green fluorescent protein, which can realize specific linear detection of p-nitrophenol with high sensitivity, is suitable for environmental monitoring, and has broad application prospects.
本发明采用以下技术方案予以实现:The present invention is implemented by the following technical solutions:
一种重组质粒,以pBBR-MCS2为出发载体,在BamH I和Xho I位点之间插入对硝基苯酚感应元件PR-pnpR-PC1和绿色荧光蛋白基因gfp所得,其中启动子PR的核苷酸序列如SEQID NO.1所示,调控蛋白PnpR核苷酸序列如SEQ ID NO.2所示,启动子PC1的核苷酸序列如SEQID NO.3所示。A recombinant plasmid is obtained by using pBBR-MCS2 as a starting vector and inserting a p-nitrophenol sensing element PR -pnpR- PC1 and a green fluorescent protein gene gfp between the BamH I and Xho I sites, wherein the nucleotide sequence of the promoter PR is shown in SEQ ID NO.1, the nucleotide sequence of the regulatory protein PnpR is shown in SEQ ID NO.2, and the nucleotide sequence of the promoter PC1 is shown in SEQ ID NO.3.
作为本发明的一种优选,所述绿色荧光蛋白基因gfp序列如SEQ ID NO.4所示。As a preferred embodiment of the present invention, the green fluorescent protein gene gfp sequence is shown as SEQ ID NO.4.
作为本发明的一种优选,所述对硝基苯酚感应元件PR-pnpR-PC1的核苷酸序列如SEQ ID NO.5所示。As a preferred embodiment of the present invention, the nucleotide sequence of the p-nitrophenol sensing element PR -pnpR-P C1 is shown in SEQ ID NO.5.
作为本发明的进一步优选,所述的重组质粒主要通过以下方法构建:As a further preference of the present invention, the recombinant plasmid is mainly constructed by the following method:
(1)以对硝基苯酚高效降解菌株DLL-E4基因组总DNA为模板,扩增对硝基苯酚响应元件PR-pnpR-PC1;(1) Using the total genomic DNA of the p-nitrophenol efficient degradation strain DLL-E4 as a template, the p-nitrophenol response element PR -pnpR-P C1 was amplified;
(2)通过PCR扩增绿色荧光蛋白GFP基因;(2) Amplify the green fluorescent protein (GFP) gene by PCR;
(3)以回收的PR-pnpR-PC1和gfp为模板扩增出融合片段PR-pnpR-PC1-gfp,再次纯化回收;(3) using the recovered PR -pnpR- PR1 and gfp as templates to amplify the fusion fragment PR- pnpR - PR1 -gfp, which was purified and recovered again;
(4)将质粒载体pBBR-MCS2利用BamH I和Xho I进行双酶切,将质粒酶切片段与融合片段以1∶2的摩尔比进行无缝连接得到。(4) The plasmid vector pBBR-MCS2 was double-digested with BamH I and Xho I, and the plasmid digested fragment and the fusion fragment were seamlessly connected at a molar ratio of 1:2.
作为本发明的更进一步优选,扩增PR-pnpR-PC1的引物序列如SEQ ID NO.7和 SEQID NO.8。As a further preferred embodiment of the present invention, the primer sequences for amplifying PR -pnpR- PC1 are SEQ ID NO.7 and SEQ ID NO.8.
一种检测对硝基苯酚的微生物荧光传感器的制备方法,包含以下步骤:A method for preparing a microbial fluorescence sensor for detecting p-nitrophenol comprises the following steps:
(1)本发明所述的重组质粒转化入KT2440感受态细胞,于含抗生素的LB固体平板上筛选阳性克隆,得到含重组质粒pBBR-PR-pnpR-PC1-gfp的工程菌PNPgfp-1;(1) The recombinant plasmid of the present invention is transformed into KT2440 competent cells, and positive clones are screened on an LB solid plate containing antibiotics to obtain an engineered bacterium PNPgfp-1 containing the recombinant plasmid pBBR- PR -pnpR-P C1 -gfp;
(2)将工程菌PNPgfp-1于含卡那霉素的LB液体培养基中培养活化生长至OD600=0.2,最终得到微生物荧光传感器。(2) The engineered bacteria PNPgfp-1 was cultured in LB liquid culture medium containing kanamycin and activated to grow to OD 600 = 0.2, and finally a microbial fluorescent sensor was obtained.
按照本发明所述的制备方法获得的能够线性响应对硝基苯酚的微生物荧光传感器。The microbial fluorescence sensor capable of linearly responding to p-nitrophenol is obtained according to the preparation method of the present invention.
本发明所述的微生物荧光传感器在对硝基苯酚实时检测中的应用。Application of the microbial fluorescence sensor of the present invention in real-time detection of p-nitrophenol.
作为本发明的一种优选,将所述微生物荧光传感器与待测样品以1:4的体积比混匀后,反应6h,取样加入黑色透底酶标板,利用酶标仪监测荧光强度RFU值。As a preferred embodiment of the present invention, the microbial fluorescence sensor and the sample to be tested are mixed at a volume ratio of 1:4, reacted for 6 hours, and then the sample is added to a black transparent ELISA plate, and the fluorescence intensity RFU value is monitored by an ELISA instrument.
作为本发明的一种优选,所述微生物荧光传感器能够感应到的污染物分子的浓度为10 ppm-100ppm。As a preferred embodiment of the present invention, the concentration of pollutant molecules that can be sensed by the microbial fluorescence sensor is 10 ppm-100 ppm.
进一步的,所述微生物荧光生物传感器能够感应不同浓度的污染物分子,从而生成不同 RFU值的荧光,将污染物分子浓度与自发光RFU值进行偶联来达到实时监测污染物分子的目的。Furthermore, the microbial fluorescent biosensor can sense pollutant molecules of different concentrations, thereby generating fluorescence with different RFU values, and coupling the pollutant molecule concentration with the self-luminous RFU value to achieve the purpose of real-time monitoring of pollutant molecules.
本发明与现有技术相比,具有以下优点和有益效果:Compared with the prior art, the present invention has the following advantages and beneficial effects:
本发明将污染物耐受菌株KT2440作为底盘细胞,从对硝基苯酚高效降解菌株DLL-E4中筛选获得调控单元pnpR-PC1作为感应元件,连接GFP蛋白作为报告蛋白,制备成微生物荧光传感器,该生物传感器能够在短时间内特异性的响应对硝基苯酚,从而生成不同RFU值的荧光,并在一定浓度范围呈线性关系,进而实现了对污染物分子的荧光检测。相比于现有的对硝基苯酚检测方法,该生物传感器响应迅速,特异性以及灵敏度高且环境适应能力强,因此在对硝基苯酚检测领域具有较为广阔的应用前景。The present invention uses pollutant-tolerant strain KT2440 as chassis cells, screens and obtains the regulatory unit pnpR-P C1 from the p-nitrophenol efficient degradation strain DLL-E4 as a sensing element, connects GFP protein as a reporter protein, and prepares a microbial fluorescent sensor. The biosensor can specifically respond to p-nitrophenol in a short time, thereby generating fluorescence with different RFU values, and is linearly related within a certain concentration range, thereby realizing the fluorescent detection of pollutant molecules. Compared with the existing p-nitrophenol detection method, the biosensor has a rapid response, high specificity and sensitivity, and strong environmental adaptability, so it has a relatively broad application prospect in the field of p-nitrophenol detection.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1为大肠杆菌DH5α在不同对硝基苯酚浓度水平下的生长情况。FIG1 shows the growth of Escherichia coli DH5α at different p-nitrophenol concentration levels.
图2为恶臭假单胞菌KT2440在不同对硝基苯酚浓度水平下的生长情况。Figure 2 shows the growth of Pseudomonas putida KT2440 at different p-nitrophenol concentration levels.
图3为重组质粒pBBR-PR-pnpR-PC1-gfp的质粒图谱。Fig. 3 is a plasmid map of the recombinant plasmid pBBR- PR -pnpR-P C1 -gfp.
图4为重组质粒pBBR-PR1-pnpR1-PA-gfp的质粒图谱。Fig. 4 is a plasmid map of the recombinant plasmid pBBR- PR1 -pnpR1- PA -gfp.
图5为构建的传感器菌株PNPgfp-1的荧光检测结果数据。FIG5 shows the fluorescence detection result data of the constructed sensor strain PNPgfp-1.
图6为构建的传感器菌株PNPgfp-2的荧光检测结果数据。FIG6 shows the fluorescence detection result data of the constructed sensor strain PNPgfp-2.
图7为构建的传感器菌株PNPgfp-1在12h内固定污染物浓度条件下荧光检测数据。FIG7 shows the fluorescence detection data of the constructed sensor strain PNPgfp-1 under fixed pollutant concentration conditions within 12 h.
图8为构建的传感器菌株PNPgfp-1的污染物特异性荧光检测结果数据。FIG8 shows the pollutant-specific fluorescence detection result data of the constructed sensor strain PNPgfp-1.
图9为构建的传感器菌株PNPgfp-1在不同pH条件下的荧光检测数据。FIG9 shows the fluorescence detection data of the constructed sensor strain PNPgfp-1 under different pH conditions.
具体实施方式DETAILED DESCRIPTION
下面结合具体实施例对本发明做进一步说明,但本发明不受实施例的限制。The present invention is further described below in conjunction with specific embodiments, but the present invention is not limited by the embodiments.
实施例中未注明具体技术或条件者,按照本领域内的文献所描述的技术或者按照产品说明书进行。所用试剂或仪器未注明生产厂商者,均为可通过购买获得的常规产品。If no specific techniques or conditions are specified in the examples, the experiments were carried out according to the techniques described in the literature in the field or according to the product instructions. If no manufacturer is specified for the reagents or instruments used, they are all conventional products that can be purchased.
实施例1:底盘细胞的筛选Example 1: Screening of chassis cells
配制不同浓度对硝基苯酚母液(120000ppm,60000ppm,30000ppm);溶剂使用无水乙醇。Prepare p-nitrophenol mother solutions of different concentrations (120000ppm, 60000ppm, 30000ppm); use anhydrous ethanol as the solvent.
不同浓度对硝基苯酚培养液配置:4mL LB培养基+1mL菌液+5μL相应浓度对硝基苯酚母液。Preparation of p-nitrophenol culture medium of different concentrations: 4 mL LB medium + 1 mL bacterial solution + 5 μL p-nitrophenol stock solution of corresponding concentration.
以1%的接菌量接入OD600=1的DH5α和KT2440菌株(ATCC47057)分别在恒温摇床(37℃和30℃,180rpm)中培养。DH5α and KT2440 strains (ATCC47057) with OD 600 = 1 were inoculated at a 1% inoculum amount and cultured in a constant temperature shaker (37° C. and 30° C., 180 rpm), respectively.
定时取样200μL加入透明酶标板,做3个平行,测定不同时间的OD600,检测不同菌株的生长情况。200 μL of samples were taken at regular intervals and added to a transparent ELISA plate. Three parallel plates were made to measure the OD 600 at different times to detect the growth of different strains.
结果如图1与图2,相比菌株DH5α,菌株KT2400能够耐受高浓度的对硝基苯酚,因此选择KT2440作为底盘细胞构建生物传感器。The results are shown in Figures 1 and 2. Compared with strain DH5α, strain KT2400 can tolerate high concentrations of p-nitrophenol, so KT2440 was selected as the chassis cell to construct the biosensor.
实施例2:基因的获取和载体的构建Example 2: Gene acquisition and vector construction
1、基因的获取1. Gene acquisition
从硝基苯酚高效降解菌株DLL-E4(刘智,洪青等.甲基对硫磷降解菌DLL-E4降解对-硝基苯酚特性[J].中国环境科学,2003年第004期,435-439)中分别扩增出PR,pnpR和PC1基因,其核苷酸序列如SEQ ID NO.1,SEQ ID NO.2,SEQ ID NO.3所示,PR1,pnpR1和PA基因其核苷酸序列如SEQ ID NO.6,SEQ ID NO.7,SEQ ID NO.8所示,引物为分别为R-F 和R-R、PC1-F和PC1-R、R1-F和R1-R、PA-F和PA-R,模板为DLL-E4总DNA,进行聚合酶链式反应(PCR),其PCR扩增体系如下所示:PR, pnpR and PC1 genes were amplified from the nitrophenol efficient degrading strain DLL-E4 (Liu Zhi, Hong Qing et al. Degradation characteristics of p-nitrophenol by methyl parathion-degrading bacteria DLL-E4 [J]. China Environmental Science, Issue 004 , 2003, 435-439), and their nucleotide sequences are shown in SEQ ID NO.1, SEQ ID NO.2 and SEQ ID NO.3. The nucleotide sequences of PR1, pnpR1 and PA genes are shown in SEQ ID NO.6, SEQ ID NO.7 and SEQ ID NO.8. The primers are RF and RR, PC1 -F and PC1 -R, R1-F and R1-R, PA -F and PA -R, respectively. The template is DLL-E4 total DNA, and polymerase chain reaction (PCR) is performed. The PCR amplification system is as follows:
PCR程序为:95℃5min;32循环×(94℃30s,55℃30s,72℃45s);72℃5min; 4℃∞。The PCR program was: 95°C for 5 min; 32 cycles × (94°C for 30 s, 55°C for 30 s, 72°C for 45 s); 72°C for 5 min; 4°C∞.
引物序列如下所示:The primer sequences are as follows:
R-F:R-F:
5’-cgctctagaactagtggatccGGAAAGTGGCCGCTTCAAG-3’;5’-cgctctagaactagtggatccGGAAAGTGGCCGCTTCAAG-3’;
R-R:R-R:
5’-TCAGACGACCCAGCCACG-3’。5’-TCAGACGACCCAGCCACG-3’.
PC1-F: PC1 -F:
5’-CATTGAGCAGTGTTCGCGTTT-3’;5’-CATTGAGCAGTGTTCGCGTTT-3’;
PC1-R: PC1 -R:
5’-CGCATTCACCGCACTTGTT-3’。5’-CGCATTCACCGCACTTGTT-3’.
R1-F:R1-F:
5’-cgctctagaactagtggatccCGGGATTTGTGGGCCATC-3’;5’-cgctctagaactagtggatccCGGGATTTGTGGGCCATC-3’;
R1-R:R1-R:
5’-TCAGCAGTTTGCAAGGGCA-3’。5’-TCAGCAGTTTTGCAAGGGCA-3’.
PA-F: PA -F:
5’-GTGAATTCCTGAATACGTCATTGTTAG-3’;5’-GTGAATTCCTGAATACGTCATTGTTAG-3’;
PA-R:P A -R:
5’-GTAGGCGACTGCCCGCGG-3’。5’-GTAGGCGACTGCCCGCGG-3’.
PCR产物利用胶回收纯化试剂盒(Vazyme)进行胶回收纯化。The PCR product was purified by gel recovery using a gel recovery kit (Vazyme).
再以回收的PR-pnpR和PC1基因为模板,以R-F和PC1-R为引物进行聚合酶链式反应(PCR), 扩增融合片段PR-pnpR-PC1,其核苷酸序列如SEQ ID NO.5,其PCR扩增体系如下所示:Then, the recovered PR -pnpR and PC1 genes were used as templates, and RF and PC1 -R were used as primers to perform polymerase chain reaction (PCR) to amplify the fusion fragment PR- pnpR - PC1 , whose nucleotide sequence is shown in SEQ ID NO.5. The PCR amplification system is as follows:
PCR程序为:95℃5min;32循环×(94℃30s,55℃30s,72℃70s);72℃5min;4℃∞。The PCR program was: 95°C for 5 min; 32 cycles × (94°C for 30 s, 55°C for 30 s, 72°C for 70 s); 72°C for 5 min; 4°C∞.
再以上述方法以PR1-pnpR1和PA为模板,以R1-F和PA-R为引物,扩增融合片段 PR1-pnpR1-PA,其核苷酸序列如SEQ ID NO.9。The above method was then used to amplify the fusion fragment PR1- pnpR1- PA using PR1 -pnpR1 and PA as templates and R1-F and PA -R as primers. The nucleotide sequence of the fragment is shown in SEQ ID NO.9.
PCR产物利用胶回收纯化试剂盒(Vazyme)进行胶回收纯化。The PCR product was purified by gel recovery using a gel recovery kit (Vazyme).
从含有绿色荧光蛋白GFP的质粒pMD19-T-gfp扩增出gfp基因,质粒购自武汉淼灵生物科技有限公司,其核苷酸序列如SEQ ID NO.4所示,引物为gfp-F和gfp-R进行聚合酶链式反应(PCR),其PCR扩增体系如下所示:The gfp gene was amplified from the plasmid pMD19-T-gfp containing green fluorescent protein GFP. The plasmid was purchased from Wuhan Miaoling Biotechnology Co., Ltd. The nucleotide sequence is shown in SEQ ID NO.4. The primers are gfp-F and gfp-R for polymerase chain reaction (PCR). The PCR amplification system is as follows:
PCR程序为:95℃5min;35循环×(94℃30s,55℃30s,72℃30s);72℃5min; 4℃∞。The PCR program was: 95°C for 5 min; 35 cycles × (94°C for 30 s, 55°C for 30 s, 72°C for 30 s); 72°C for 5 min; 4°C∞.
引物序列如下所示:The primer sequences are as follows:
引物1(gfp-F):Primer 1 (gfp-F):
5’-ATGAGTAAAGGAGAAGAACTTTTCACTG-3’;5’-ATGAGTAAAGGAGAAGAACTTTTCACTG-3’;
引物2(gfp-R):Primer 2 (gfp-R):
5’-ggtaccgggccccccctcgagGTGTATCCAGGAGCTGTTACAACTCA-3’。5’-ggtaccgggccccccctcgagGTGTATCCAGGAGCTGTTACAACTCA-3’.
再以回收的PR-pnpR-PC1和gfp基因为模板,以R-F和gfp-R为引物,扩增融合片段PR-pnpR-PC1-gfp,以PR1-pnpR1-PA和gfp为模板,以R1-F和gfp-R为引物,扩增融合片段 PR1-pnpR1-PA-gfp,进行聚合酶链式反应(PCR),其PCR扩增体系如下所示:Then, the recovered PR -pnpR-P C1 and gfp gene were used as templates, RF and gfp-R were used as primers to amplify the fusion fragment PR- pnpR-P C1 -gfp, and PR1 -pnpR1- PA and gfp were used as templates, R1-F and gfp-R were used as primers to amplify the fusion fragment PR1 -pnpR1- PA -gfp, and polymerase chain reaction (PCR) was performed. The PCR amplification system is as follows:
PCR程序为:95℃5min;32循环×(94℃30s,55℃30s,72℃70s);72℃5min; 4℃∞。The PCR program was: 95°C for 5 min; 32 cycles × (94°C for 30 s, 55°C for 30 s, 72°C for 70 s); 72°C for 5 min; 4°C∞.
PCR产物利用胶回收纯化试剂盒(Vazyme)进行胶回收纯化。The PCR product was purified by gel recovery using a gel recovery kit (Vazyme).
2、pBBR-PR-pnpR-PC1-gfp和pBBR-PR1-pnpR1-PA-gfp表达载体的构建2. Construction of pBBR- PR- pnpR-P C1 -gfp and pBBR- PR1 -pnpR1-PA - gfp expression vectors
(1)利用限制性内切酶1BamH I(Takara Bio,货号1010S)和限制性内切酶2Xho I(Takara Bio,货号1094S)双酶切pBBR-MCS2质粒,其酶切体系为:(1) The pBBR-MCS2 plasmid was double-digested with restriction endonuclease 1BamH I (Takara Bio, Catalog No. 1010S) and restriction endonuclease 2Xho I (Takara Bio, Catalog No. 1094S). The restriction digestion system was as follows:
酶切体系置于37℃孵育3h,进行胶回收纯化。The enzyme digestion system was incubated at 37°C for 3 h, and then the gel was recovered and purified.
利用无缝克隆将PR-pnpR-PC1-gfp和PR1-pnpR1-PA-gfp片段克隆到pBBR-MCS2质粒上,其体系如下所示: PR- pnpR-P C1 -gfp and PR1 - pnpR1- PA- gfp fragments were cloned into the pBBR-MCS2 plasmid using seamless cloning. The system is as follows:
连接体系置于37℃孵育30min。连接产物转化E.coli DH5α感受态,涂布到含有50mg/L 卡那霉素的LB固体平板上,筛选阳性克隆,从阳性克隆中提取重组质粒pBBR-PR-pnpR-PC1-gfp (图3)和pBBR-PR1-pnpR1-PA-gfp(图4),再通过限制性酶切和测序进行鉴定。The ligation system was incubated at 37°C for 30 min. The ligation product was transformed into E. coli DH5α competent cells and spread on LB solid plates containing 50 mg/L kanamycin to screen positive clones. Recombinant plasmids pBBR- PR -pnpR-P C1 -gfp (Figure 3) and pBBR- PR1- pnpR1-P A -gfp (Figure 4) were extracted from the positive clones and then identified by restriction enzyme digestion and sequencing.
实施例3:对硝基苯酚全细胞微生物传感器的构建Example 3: Construction of p-nitrophenol whole-cell microbial sensor
将重组质粒通过高压电穿孔法转化至Pseudomonas putida KT2440感受态细胞,涂布到含 100mg/L卡那霉素的LB固体平板上,通过PCR筛选获得阳性克隆,由此获得含有载体 pBBR-PR-pnpR-PC1-gfp的工程菌株PNPgfp-1和含有载体pBBR-PR1-pnpR1-PA-gfp的工程菌株 PNPgfp-2。The recombinant plasmid was transformed into Pseudomonas putida KT2440 competent cells by high-voltage electroporation, plated on LB solid plates containing 100 mg/L kanamycin, and positive clones were obtained by PCR screening, thereby obtaining the engineered strain PNPgfp-1 containing the vector pBBR- PR- pnpR-P C1- gfp and the engineered strain PNPgfp-2 containing the vector pBBR- PR1 -pnpR1-P A -gfp.
实施例4:微生物荧光传感器检测对硝基苯酚的应用Example 4: Application of microbial fluorescence sensor to detect p-nitrophenol
1、菌株活化和培养1. Strain activation and cultivation
将测序正确的工程菌株PNPgfp-1和PNPgfp-2分别转接至含有100mg/L卡那霉素的LB 液体培养基中,30℃培养过夜,得到菌液。The correctly sequenced engineered strains PNPgfp-1 and PNPgfp-2 were respectively transferred to LB liquid culture medium containing 100 mg/L kanamycin and cultured at 30° C. overnight to obtain bacterial suspension.
2、传感器的剂量效应检测2. Dose effect detection of sensors
配制不同浓度对硝基苯酚母液(100000ppm,80000ppm,60000ppm,50000ppm,40000ppm,30000ppm,20000ppm,10000ppm);溶剂使用无水乙醇。Prepare p-nitrophenol mother solutions of different concentrations (100000ppm, 80000ppm, 60000ppm, 50000ppm, 40000ppm, 30000ppm, 20000ppm, 10000ppm); use anhydrous ethanol as the solvent.
不同浓度对硝基苯酚培养液配置:4mL LB培养基+1mL菌液+5μL相应浓度对硝基苯酚母液得到对硝基苯酚浓度分别为100ppm,80ppm,60ppm,50ppm,40ppm,30ppm,20ppm,10ppm的培养液。Preparation of p-nitrophenol culture medium with different concentrations: 4 mL LB medium + 1 mL bacterial solution + 5 μL p-nitrophenol mother solution of corresponding concentration to obtain culture medium with p-nitrophenol concentrations of 100 ppm, 80 ppm, 60 ppm, 50 ppm, 40 ppm, 30 ppm, 20 ppm, and 10 ppm, respectively.
在恒温摇床(30℃,180rpm)中培养6h。The cells were cultured in a constant temperature shaker (30°C, 180 rpm) for 6 h.
取样200μL加入透底黑色酶标板,每个实验组做3个平行。Take 200 μL of the sample and add it to a transparent black ELISA plate. Make three parallels for each experimental group.
3、传感器的特异性检测3. Specificity detection of sensors
配制不同结构类似污染物母液40000ppm(苯,对苯二酚,邻苯二酚,对硝基苯酚,对硝基苯);溶剂使用无水乙醇。Prepare 40000ppm of mother liquor of pollutants with similar structures (benzene, hydroquinone, catechol, p-nitrophenol, p-nitrobenzene); use anhydrous ethanol as solvent.
不同污染物培养液配置:4mL LB培养基+1mL菌液+5μL相应污染物母液得到终浓度均为40ppm的不同结构类似污染物培养液。Preparation of culture medium for different pollutants: 4 mL LB medium + 1 mL bacterial solution + 5 μL corresponding pollutant mother solution to obtain culture medium for pollutants with different structures and similar structures with a final concentration of 40 ppm.
在恒温摇床(30℃,180rpm)中培养6h。The cells were cultured in a constant temperature shaker (30°C, 180 rpm) for 6 h.
取样200μL加入透底黑色酶标板,每个浓度做3个平行。Take 200 μL of the sample and add it to a clear black ELISA plate. Make 3 parallels for each concentration.
3、传感器的响应时间检测3. Sensor response time detection
污染物培养液配置:4mL LB培养基+1mL菌液+5μL对硝基苯酚母液(40000ppm)。Configuration of pollutant culture medium: 4 mL LB medium + 1 mL bacterial solution + 5 μL p-nitrophenol stock solution (40000 ppm).
在恒温摇床(30℃,180rpm)中培养12h,每两小时取样检测。The culture was incubated in a constant temperature shaker (30°C, 180 rpm) for 12 h, and samples were taken every two hours for testing.
取样200μL加入透底黑色酶标板,每个实验组做3个平行。Take 200 μL of the sample and add it to a transparent black ELISA plate. Make three parallels for each experimental group.
4、传感器的pH适应性检测4. pH adaptability test of the sensor
配制不同pH的LB培养基(使用NaOH和HCl调节PH)。LB medium with different pH values was prepared (pH was adjusted using NaOH and HCl).
不同污染物培养液配置:4mL LB不同pH LB培养基+1mL菌液+5μL 40000ppm对硝基苯酚污染物母液Different pollutant culture medium configuration: 4mL LB medium with different pH values + 1mL bacterial solution + 5μL 40000ppm p-nitrophenol pollutant stock solution
在恒温摇床(30℃,180rpm)中培养6h。The cells were cultured in a constant temperature shaker (30°C, 180 rpm) for 6 h.
取样200μL加入透底黑色酶标板,每个实验组做3个平行。Take 200 μL of the sample and add it to a transparent black ELISA plate. Make three parallels for each experimental group.
5、荧光检测5. Fluorescence detection
用酶标仪(Biotek)恒温30℃检测菌液浓度OD600。The concentration of bacterial solution OD 600 was detected by using a microplate reader (Biotek) at a constant temperature of 30°C.
用酶标仪恒温30℃检测PNPgfp-1菌株荧光强度(FU),计算RFU=FU/OD600-FUCK/OD’600 The fluorescence intensity (FU) of PNPgfp-1 strain was detected by microplate reader at 30℃, and RFU was calculated as FU/OD 600 - FU CK /OD' 600
结果如图5和图6表明,相比构建的PNPgfp-2重组菌株,本发明构建的PNPgfp-1重组菌株,作为感应污染物分子的微生物荧光传感器,在不同浓度对硝基苯酚的作用下,其RFU值呈现出不同的变化,对硝基苯酚浓度越高,其RFU值越高,检测效果越明显,且在10-100ppm 呈现线性关系。由图7可知PNPgfp-1重组菌株在2小时即可迅速产生响应,且随着时间的增加,荧光强度增强。基于响应时间和荧光强度,选择微生物荧光传感器的培养时间为6小时。结果如图8和图9表明,PNPgfp-1重组菌株能特异性地对对硝基苯酚响应并表达强烈的荧光信号,并在较为广泛的pH范围内能保持菌株的污染物响应能力。As shown in Figures 5 and 6, compared with the constructed PNPgfp-2 recombinant strain, the PNPgfp-1 recombinant strain constructed by the present invention, as a microbial fluorescent sensor for sensing pollutant molecules, shows different changes in its RFU value under the action of different concentrations of p-nitrophenol. The higher the concentration of p-nitrophenol, the higher the RFU value, the more obvious the detection effect, and a linear relationship is shown at 10-100ppm. As shown in Figure 7, the PNPgfp-1 recombinant strain can respond quickly in 2 hours, and the fluorescence intensity increases with time. Based on the response time and fluorescence intensity, the cultivation time of the microbial fluorescence sensor is selected to be 6 hours. As shown in Figures 8 and 9, the PNPgfp-1 recombinant strain can specifically respond to p-nitrophenol and express a strong fluorescence signal, and can maintain the pollutant response ability of the strain in a relatively wide pH range.
以上实施例仅用以说明本发明的技术方案,而非对其进行限制;尽管参照前述实施例对本发明进行了详细的说明,对于本领域的普通技术人员来说,依然可以对前述实施例所记载的技术方案进行修改,或者对其中部分技术特征进行等同替换;而这些修改或替换,并不使相应技术方案的本质脱离本发明所要求保护的技术方案的精神和范围。The above embodiments are only used to illustrate the technical solutions of the present invention, rather than to limit the same. Although the present invention has been described in detail with reference to the aforementioned embodiments, it is still possible for a person skilled in the art to modify the technical solutions described in the aforementioned embodiments, or to replace some of the technical features therein by equivalents. However, these modifications or replacements do not deviate the essence of the corresponding technical solutions from the spirit and scope of the technical solutions claimed to be protected by the present invention.
Claims (10)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210937245.1A CN115896154A (en) | 2022-08-12 | 2022-08-12 | A microbial fluorescence sensor for detecting p-nitrophenol and its preparation method and application |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210937245.1A CN115896154A (en) | 2022-08-12 | 2022-08-12 | A microbial fluorescence sensor for detecting p-nitrophenol and its preparation method and application |
Publications (1)
Publication Number | Publication Date |
---|---|
CN115896154A true CN115896154A (en) | 2023-04-04 |
Family
ID=86477078
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202210937245.1A Pending CN115896154A (en) | 2022-08-12 | 2022-08-12 | A microbial fluorescence sensor for detecting p-nitrophenol and its preparation method and application |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN115896154A (en) |
-
2022
- 2022-08-12 CN CN202210937245.1A patent/CN115896154A/en active Pending
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN113005070B (en) | Preparation method for synthesizing microbial autoluminescent biosensors by utilizing autoluminescent operons, corresponding biosensors and applications | |
CN103626852B (en) | A kind of AraC mutant protein and application thereof | |
CN102021219A (en) | Microbial cell sensor for detecting toluene organic pollutants | |
CN108251446A (en) | A kind of construction method of lead ion responsive type whole-cell biological sensor | |
Behzadian et al. | Construction and characterization of Escherichia coli whole-cell biosensors for toluene and related compounds | |
CN102021220A (en) | Improved technology of microbial cell sensor for detecting toluene organic pollutants | |
CN112725339A (en) | Novel promoter element for improving sensitivity of explosive molecule detection and screening method and application thereof | |
CN113604495B (en) | A molecular biosensor for explosives synthesized using regulatory elements and its preparation method and application | |
CN115896154A (en) | A microbial fluorescence sensor for detecting p-nitrophenol and its preparation method and application | |
CN114480388B (en) | Screening and application of novel promoter element responding to explosive molecules | |
CN112481278A (en) | Biosensor based on AIP induction and application thereof | |
Li et al. | Identification of xenobiotic response element family transcription regulator SadR from sulfonamides-degrading strain Microbacterium sp. HA-8 and construction of biosensor to detect sulfonamides | |
CN115160416B (en) | AraC mutant for sensing submarine metal ions Cd (II), and potential-detecting microorganism sensor constructed by AraC mutant and application of AraC mutant | |
CN113388566B (en) | A novel MR-1 condensed bead for detecting explosive molecules and its preparation method and application | |
KR101270657B1 (en) | Pigment-based whole-cell biosensor system for cadmium detection using genetically engineered Deinococcus radiodurans and manufacturing method thereof | |
CN113717260A (en) | Polybrominated diphenyl ether sensing protein and whole-cell microbial sensor constructed by same | |
KR100470961B1 (en) | Recombinant bioluminescent/fluorescent bacteria for the detection oxidative damage and DNA damage simultaneously | |
CN113528412B (en) | Explosive visual biosensor based on escherichia coli cell surface display technology and preparation method and application thereof | |
CN106883290B (en) | DntR mutants and their application in the detection of catechol | |
CN119799710A (en) | An optimized promoter PyqjfC55 and its application in the preparation of high temperature resistant microbial sensors | |
CN119899855A (en) | A whole-cell biosensor based on transcription factors, construction and detection methods and applications | |
US20240376514A1 (en) | Bacterial biosensors for monitoring and detection of naphthenic acids in the environment | |
KR101430685B1 (en) | Artificial biosensor for non-degradable harmful aromatic compound detection and manufacturing method thereof | |
CN118256414A (en) | Construction and application of whole-cell biosensor for detecting polychlorinated biphenyl | |
WO2017128302A1 (en) | Method for screening gene for resistance against hppd inhibitor-type herbicide and application |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |