CN114636682A - A high-throughput assay method and application of PET hydrolase activity based on fluorescence detection - Google Patents
A high-throughput assay method and application of PET hydrolase activity based on fluorescence detection Download PDFInfo
- Publication number
- CN114636682A CN114636682A CN202210182387.1A CN202210182387A CN114636682A CN 114636682 A CN114636682 A CN 114636682A CN 202210182387 A CN202210182387 A CN 202210182387A CN 114636682 A CN114636682 A CN 114636682A
- Authority
- CN
- China
- Prior art keywords
- pet
- fdl
- fluorescence
- hydrolase
- fluorescence detection
- 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
- 101000693878 Ideonella sakaiensis (strain NBRC 110686 / TISTR 2288 / 201-F6) Poly(ethylene terephthalate) hydrolase Proteins 0.000 title claims abstract description 35
- 101000693873 Unknown prokaryotic organism Leaf-branch compost cutinase Proteins 0.000 title claims abstract description 35
- 230000000694 effects Effects 0.000 title claims abstract description 30
- 238000000034 method Methods 0.000 title claims abstract description 29
- 238000001917 fluorescence detection Methods 0.000 title claims abstract description 17
- 238000012203 high throughput assay Methods 0.000 title claims description 12
- 102000004190 Enzymes Human genes 0.000 claims abstract description 24
- 108090000790 Enzymes Proteins 0.000 claims abstract description 24
- 229920000139 polyethylene terephthalate Polymers 0.000 claims abstract description 22
- 238000006243 chemical reaction Methods 0.000 claims abstract description 19
- 239000013592 cell lysate Substances 0.000 claims abstract description 12
- 239000012528 membrane Substances 0.000 claims abstract description 12
- 239000004033 plastic Substances 0.000 claims abstract description 10
- 229920003023 plastic Polymers 0.000 claims abstract description 10
- DHMQDGOQFOQNFH-UHFFFAOYSA-N Glycine Chemical compound NCC(O)=O DHMQDGOQFOQNFH-UHFFFAOYSA-N 0.000 claims abstract description 8
- 102000034287 fluorescent proteins Human genes 0.000 claims abstract description 7
- 108091006047 fluorescent proteins Proteins 0.000 claims abstract description 7
- 239000004471 Glycine Substances 0.000 claims abstract description 4
- GNBHRKFJIUUOQI-UHFFFAOYSA-N fluorescein Chemical compound O1C(=O)C2=CC=CC=C2C21C1=CC=C(O)C=C1OC1=CC(O)=CC=C21 GNBHRKFJIUUOQI-UHFFFAOYSA-N 0.000 claims description 11
- 230000005284 excitation Effects 0.000 claims description 10
- 238000013537 high throughput screening Methods 0.000 claims description 10
- MYTRGBGGRICZGN-UHFFFAOYSA-N (6'-dodecanoyloxy-3-oxospiro[2-benzofuran-1,9'-xanthene]-3'-yl) dodecanoate Chemical compound O1C(=O)C2=CC=CC=C2C21C1=CC=C(OC(=O)CCCCCCCCCCC)C=C1OC1=CC(OC(=O)CCCCCCCCCCC)=CC=C21 MYTRGBGGRICZGN-UHFFFAOYSA-N 0.000 claims description 4
- 229940043045 fluorescein dilaurate Drugs 0.000 claims description 4
- BYEAHWXPCBROCE-UHFFFAOYSA-N 1,1,1,3,3,3-hexafluoropropan-2-ol Chemical compound FC(F)(F)C(O)C(F)(F)F BYEAHWXPCBROCE-UHFFFAOYSA-N 0.000 claims description 3
- 229920002799 BoPET Polymers 0.000 claims description 3
- 238000002360 preparation method Methods 0.000 claims description 2
- 230000015572 biosynthetic process Effects 0.000 claims 1
- 238000012216 screening Methods 0.000 abstract description 8
- 230000000593 degrading effect Effects 0.000 abstract description 3
- 102000004157 Hydrolases Human genes 0.000 abstract description 2
- 108090000604 Hydrolases Proteins 0.000 abstract description 2
- 230000004927 fusion Effects 0.000 abstract description 2
- 239000005020 polyethylene terephthalate Substances 0.000 abstract 3
- 239000007853 buffer solution Substances 0.000 abstract 1
- -1 polyethylene terephthalate Polymers 0.000 abstract 1
- 239000000047 product Substances 0.000 description 20
- 238000006911 enzymatic reaction Methods 0.000 description 6
- 108020001507 fusion proteins Proteins 0.000 description 6
- 102000037865 fusion proteins Human genes 0.000 description 6
- 238000004519 manufacturing process Methods 0.000 description 5
- 102000004169 proteins and genes Human genes 0.000 description 5
- 108090000623 proteins and genes Proteins 0.000 description 5
- 238000001514 detection method Methods 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 4
- 238000011002 quantification Methods 0.000 description 4
- 238000009826 distribution Methods 0.000 description 3
- 238000011156 evaluation Methods 0.000 description 3
- 238000004128 high performance liquid chromatography Methods 0.000 description 3
- 238000006460 hydrolysis reaction Methods 0.000 description 3
- 108010054624 red fluorescent protein Proteins 0.000 description 3
- 239000000758 substrate Substances 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 230000007062 hydrolysis Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 230000035772 mutation Effects 0.000 description 2
- 239000013502 plastic waste Substances 0.000 description 2
- 230000035484 reaction time Effects 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- LLLVZDVNHNWSDS-UHFFFAOYSA-N 4-methylidene-3,5-dioxabicyclo[5.2.2]undeca-1(9),7,10-triene-2,6-dione Chemical compound C1(C2=CC=C(C(=O)OC(=C)O1)C=C2)=O LLLVZDVNHNWSDS-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000006047 enzymatic hydrolysis reaction Methods 0.000 description 1
- 238000003384 imaging method Methods 0.000 description 1
- 238000011005 laboratory method Methods 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 229920000728 polyester Polymers 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 238000012795 verification Methods 0.000 description 1
Images
Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
- G01N21/62—Systems in which the material investigated is excited whereby it emits light or causes a change in wavelength of the incident light
- G01N21/63—Systems in which the material investigated is excited whereby it emits light or causes a change in wavelength of the incident light optically excited
- G01N21/64—Fluorescence; Phosphorescence
- G01N21/6428—Measuring fluorescence of fluorescent products of reactions or of fluorochrome labelled reactive substances, e.g. measuring quenching effects, using measuring "optrodes"
Landscapes
- Health & Medical Sciences (AREA)
- Immunology (AREA)
- Chemical & Material Sciences (AREA)
- Physics & Mathematics (AREA)
- Analytical Chemistry (AREA)
- Optics & Photonics (AREA)
- Nuclear Medicine, Radiotherapy & Molecular Imaging (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- General Physics & Mathematics (AREA)
- Pathology (AREA)
- Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
- Investigating, Analyzing Materials By Fluorescence Or Luminescence (AREA)
- Investigating Or Analysing Materials By The Use Of Chemical Reactions (AREA)
Abstract
Description
技术领域technical field
本发明涉及酶活性测定技术领域,具体涉及一种基于荧光检测的PET水解酶活性高通量测定方法及应用。The invention relates to the technical field of enzyme activity determination, in particular to a high-throughput determination method and application of PET hydrolase activity based on fluorescence detection.
背景技术Background technique
塑料制品凭借着其良好的耐酸碱等优良特性被广泛应用于制造业,但同时这使得其难以被有效降解,仅通过热机械的手段降低其机械性能并进一步焚烧填埋无法实现真正意义上的循环利用。该过程所产生的塑料废物的积累会导致环境污染并进一步威胁生态系统,据欧盟统计局统计,2019年全球塑料总产量几乎达到3.7亿吨,其中中国产量占全世界总产量的31%。虽然目前已经有通过化学和物理技术处理塑料废物的方法,但是通过这些方法加工产生的副产品同样会对环境造成污染。所以,利用微生物降解塑料已成为当前的研究热点。对苯二甲酸乙二醇酯(PET)作为市场广泛应用的塑料材质之一,作为一种聚酯型塑料,其降解的关键一步是PET水解酶催化的酯键水解。鉴于PET水解酶重要的研究和应用价值,近年来有关该酶的人工改造成为一个热点。目前的PET水解酶改造主要是基于酶的结构对目标蛋白进行单点或多点氨基酸突变,将所有突变的目标蛋白分别纯化,进行酶反应后通过HPLC检测产物的生成量,这种方法不仅工作量大而且通量较低,能够检测和筛选的突变体数量有限,在理性设计PET水解酶突变时因为需向检测通量妥协而舍弃大量突变选择。Plastic products are widely used in the manufacturing industry due to their excellent properties such as good acid and alkali resistance, but at the same time, this makes it difficult to effectively degrade them. Only by thermal-mechanical means to reduce their mechanical properties and further incinerate and landfill can not achieve a real meaning. of recycling. The accumulation of plastic waste generated by this process can lead to environmental pollution and further threaten the ecosystem. According to Eurostat, the total global plastic production in 2019 reached almost 370 million tons, of which China’s production accounted for 31% of the world’s total. Although there are existing methods to dispose of plastic waste through chemical and physical technologies, the by-products produced by these methods also pollute the environment. Therefore, the use of microorganisms to degrade plastics has become a current research hotspot. Ethylene terephthalate (PET) is one of the widely used plastic materials in the market. As a polyester plastic, the key step of its degradation is the hydrolysis of ester bonds catalyzed by PET hydrolase. In view of the important research and application value of PET hydrolase, the artificial modification of this enzyme has become a hot spot in recent years. The current PET hydrolase transformation is mainly based on the structure of the enzyme to mutate the target protein at single or multi-point amino acids, purify all the mutated target proteins separately, and detect the production of the product by HPLC after the enzymatic reaction. This method not only works Due to the large amount and low throughput, the number of mutants that can be detected and screened is limited. When designing PET hydrolase mutations rationally, a large number of mutation selections are discarded because of the need to compromise the detection throughput.
发明内容SUMMARY OF THE INVENTION
本发明的目的在于提供一种高通量筛选方法,该方法能够基于荧光检测对PET水解酶进行高通量的活性定量检测,可广泛应用于PET水解酶突变体库及环境中PET塑料水解酶的筛选鉴定。The purpose of the present invention is to provide a high-throughput screening method, which can perform high-throughput quantitative activity detection of PET hydrolase based on fluorescence detection, and can be widely used in PET hydrolase mutant library and PET plastic hydrolase in the environment screening identification.
为实现上述目的,本发明采用的技术方案如下:一种基于荧光检测的PET水解酶活性高通量测定方法,包括:In order to achieve the above object, the technical scheme adopted in the present invention is as follows: a high-throughput assay method for PET hydrolase activity based on fluorescence detection, comprising:
(1)将PET水解酶与荧光蛋白融合表达,在反应前测定细胞裂解液中荧光值,以确定酶的浓度;(1) The PET hydrolase and fluorescent protein are fused and expressed, and the fluorescence value in the cell lysate is measured before the reaction to determine the concentration of the enzyme;
(2)制备PET-FDL膜,所述PET-FDL膜为包埋了荧光素二月桂酸酯的PET膜;(2) preparing a PET-FDL film, the PET-FDL film is a PET film embedded with fluorescein dilaurate;
(3)将细胞裂解液与PET-FDL膜在甘氨酸缓冲液中于反应;反应结束后,测定产物中荧光值,以确定产物浓度;(3) react the cell lysate with the PET-FDL membrane in a glycine buffer; after the reaction, measure the fluorescence value in the product to determine the concentration of the product;
(4)计算产物中的荧光值与反应前细胞裂解液中荧光值的比值,即为PET水解酶的比酶活。(4) Calculate the ratio of the fluorescence value in the product to the fluorescence value in the cell lysate before the reaction, which is the specific enzyme activity of the PET hydrolase.
作为本发明的一种优选方式,所述步骤(1)中,荧光蛋白的荧光最大发射波长应与荧光素最大发射波长相差大于100nm。As a preferred mode of the present invention, in the step (1), the maximum emission wavelength of fluorescence of the fluorescent protein should be different from the maximum emission wavelength of fluorescein by more than 100 nm.
进一步地,所述步骤(2)中,PET-FDL膜的制备方法是:将FDL与PET塑料按照质量配比0.25~1μg/mg,一起溶解到六氟异丙醇后取40μL加入到96孔板里,在30℃至50℃下挥发后形成膜。Further, in the step (2), the preparation method of the PET-FDL film is as follows: FDL and PET plastic are dissolved in hexafluoroisopropanol according to a mass ratio of 0.25-1 μg/mg, and then 40 μL is added to 96 wells In the plate, a film is formed after volatilization at 30°C to 50°C.
进一步地,荧光蛋白的激发波长范围为485nm~670nm,最大激发波长为603nm,发射波长范围为610nm~805nm,最大发射波长为675nm。Further, the excitation wavelength range of the fluorescent protein is 485nm-670nm, the maximum excitation wavelength is 603nm, the emission wavelength range is 610nm-805nm, and the maximum emission wavelength is 675nm.
进一步地,荧光素的激发波长范围为420nm~530nm,最大激发波长为494nm,发射波长范围为485nm~615nm,最大发射波长为525nm。Further, the excitation wavelength range of fluorescein is 420nm-530nm, the maximum excitation wavelength is 494nm, the emission wavelength range is 485nm-615nm, and the maximum emission wavelength is 525nm.
本发明还提供一种基于荧光检测的PET水解酶活性高通量测定方法的应用,该方法可应用于PET水解酶突变体的筛选。The invention also provides the application of a high-throughput assay method for PET hydrolase activity based on fluorescence detection, which can be applied to the screening of PET hydrolase mutants.
本发明提供的基于荧光检测的PET水解酶活性高通量测定方法及其应用,对PET水解酶具有很好的活性筛选效果。利用本发明的方法对包埋荧光素的PET薄膜进行降解,能够对突变体库进行高通量的筛选,得到活性高的突变体。本发明提供的高通量筛选方法,通量较高,成本低廉,操作方便,为筛选高效的塑料降解酶提供了新方法,具有广阔的应用前景。The high-throughput assay method for PET hydrolase activity based on fluorescence detection and its application provided by the invention have good activity screening effect on PET hydrolase. By using the method of the invention to degrade the PET film embedded with fluorescein, high-throughput screening of the mutant library can be performed to obtain mutants with high activity. The high-throughput screening method provided by the invention has high throughput, low cost and convenient operation, provides a new method for screening high-efficiency plastic degrading enzymes, and has broad application prospects.
附图说明Description of drawings
图1为融合蛋白浓度与红色荧光值关系图;Fig. 1 is a graph showing the relationship between fusion protein concentration and red fluorescence value;
图2为30℃挥发制成的不同比例的PET-FDL膜反应过程中荧光的释放;Figure 2 shows the release of fluorescence during the reaction of PET-FDL films with different proportions volatilized at 30°C;
图3为40℃挥发制成的不同比例的PET-FDL膜反应过程中荧光的释放;Figure 3 shows the release of fluorescence during the reaction of PET-FDL films with different proportions volatilized at 40°C;
图4为50℃挥发制成的不同比例的PET-FDL膜反应过程中荧光的释放;Figure 4 shows the release of fluorescence during the reaction of PET-FDL films of different proportions prepared by volatilization at 50°C;
图5为50℃挥发制成的FDL/PET为1μg/mg的自制膜反应后荧光值与产物产量的相关性;Figure 5 shows the correlation between the fluorescence value and the product yield after the reaction of the self-made membrane with FDL/PET of 1 μg/mg volatilized at 50 °C;
图6为50℃挥发制成的FDL/PET为0.5μg/mg的自制膜反应后荧光值与产物产量的相关性;Figure 6 shows the correlation between the fluorescence value and the product yield after the reaction of the self-made membrane with FDL/PET of 0.5μg/mg volatilized at 50°C;
图7为50℃挥发制成的FDL/PET为0.33μg/mg的自制膜反应后荧光值与产物产量的相关性;Figure 7 shows the correlation between the fluorescence value and the product yield after the reaction of the self-made membrane with FDL/PET of 0.33 μg/mg volatilized at 50 °C;
图8为50℃挥发制成的FDL/PET为0.25μg/mg的自制膜反应后荧光值与产物产量的相关性;Figure 8 shows the correlation between the fluorescence value and the product yield after the reaction of the self-made membrane with FDL/PET of 0.25μg/mg volatilized at 50°C;
图9本发明实施例中不同条件下高通量筛选实验稳定性参数Z factor的评估。Fig. 9 Evaluation of the stability parameter Z factor of high-throughput screening experiments under different conditions in the embodiment of the present invention.
具体实施方式Detailed ways
为了便于理解本发明,下面结合附图和具体实施例,对本发明进行更详细的说明。附图中给出了本发明的较佳的实施例。但是,本发明可以以许多不同的形式来实现,并不限于本说明书所描述的实施例。相反地,提供这些实施例的目的是使对本发明公开内容的理解更加透彻全面。In order to facilitate understanding of the present invention, the present invention will be described in more detail below with reference to the accompanying drawings and specific embodiments. Preferred embodiments of the invention are shown in the accompanying drawings. However, the present invention may be embodied in many different forms and is not limited to the embodiments described in this specification. Rather, these embodiments are provided so that a thorough and complete understanding of the present disclosure will be provided.
本发明实施例中用到的原料和试剂如无特殊说明,均为市售商品。采用的实验方法、仪器设备均为实验室常规技术。本发明的分别引入了绿色荧光素和红色荧光蛋白对PET产物产量和酶量进行定量,随着酶解反应的进行,底物被分解,底物中的绿色荧光素被逐渐释放,此时,绿色荧光值与红色荧光值的比值即可代表酶的相对活性。以酶活为筛选条件,可以实现PET水解酶突变体高通量筛选。The raw materials and reagents used in the examples of the present invention are all commercially available commodities unless otherwise specified. The experimental methods and instruments used are all routine laboratory techniques. In the present invention, green fluorescein and red fluorescent protein are respectively introduced to quantify the yield of PET products and the amount of enzymes. As the enzymatic hydrolysis reaction proceeds, the substrate is decomposed, and the green fluorescein in the substrate is gradually released. The ratio of the green fluorescence value to the red fluorescence value can represent the relative activity of the enzyme. Using enzyme activity as the screening condition, high-throughput screening of PET hydrolase mutants can be achieved.
实施例1本实施例提供一种基于荧光检测的PET水解酶活性高通量测定方法,该方法包括以下详细步骤:
一、红色荧光值对酶量的定量1. Quantification of enzyme amount by red fluorescence value
为了对突变菌株中目标蛋白的表达量进行定量,本发明将红色荧光蛋白mCarmine(Fabritius,A.;Ng,D.;Kist,A.M.;Erdogan,M.;Portugues,R.;Griesbeck,O.Imaging-Based Screening Platform Assists Protein Engineering.Cell Chemical Biology2018,25,1554-1561.e8.)与PET降解酶融合表达得到融合蛋白。首先,为了证明该红色荧光值能够一定程度的反映该融合蛋白参与酶反应的酶量,本实施例将融合蛋白的浓度梯度稀释为2μM、4μM、6μM、8μM、10μM,并测试其不同浓度下红色荧光值与蛋白浓度的关系。结果如图1所示,表明两者的相关性R2大于0.99,说明红色荧光值能够精确的反映酶的浓度。In order to quantify the expression level of the target protein in the mutant strain, the present invention uses the red fluorescent protein mCarmine (Fabritius, A.; Ng, D.; Kist, AM; Erdogan, M.; Portugal, R.; Griesbeck, O. Imaging -Based Screening Platform Assists Protein Engineering. Cell Chemical Biology 2018, 25, 1554-1561.e8.) and PET-degrading enzyme were fused and expressed to obtain a fusion protein. First, in order to prove that the red fluorescence value can reflect the amount of the fusion protein involved in the enzymatic reaction to a certain extent, in this example, the concentration of the fusion protein was diluted to 2 μM, 4 μM, 6 μM, 8 μM, 10 μM, and tested at different concentrations. The relationship between the red fluorescence value and the protein concentration. The results are shown in Figure 1, indicating that the correlation R 2 between the two is greater than 0.99, indicating that the red fluorescence value can accurately reflect the concentration of the enzyme.
二、绿色荧光素对产物的定量2. Quantification of the product by green fluorescein
(1)绿色荧光素与PET融合的制膜条件(1) Film making conditions for fusion of green fluorescein and PET
酶活的测定涉及到酶的定量和产物的定量。为了对PET分解后产物的生成量进行定量,本实施例向底物PET中引入了绿色荧光素二月桂酯(Fluorescein dilaurate,FDL)。The determination of enzyme activity involves the quantification of the enzyme and the quantification of the product. In order to quantify the amount of products generated after PET decomposition, green fluorescein dilaurate (Fluorescein dilaurate, FDL) was introduced into the substrate PET in this example.
将二月桂酯FDL 5μg/ml,按不同质量配比:1μg/mg、0.5μg/mg、0.33μg/mg、0.25μg/mg,分别加入到5mg/ml、10mg/ml、15mg/ml、20mg/ml的PET中,一起溶解到六氟异丙醇后取40μL加入到96孔板里,并在30℃、40℃和50℃三个温度下分别制膜。Dilauryl FDL 5μg/ml, according to different mass ratios: 1μg/mg, 0.5μg/mg, 0.33μg/mg, 0.25μg/mg, were added to 5mg/ml, 10mg/ml, 15mg/ml, 20mg /ml of PET, dissolved in hexafluoroisopropanol together, and then added 40 μL to a 96-well plate, and formed membranes at three temperatures of 30°C, 40°C, and 50°C.
将制得的膜,与PET降解酶反应48h后,利用酶标仪测定绿色荧光的释放量,并利用HPLC检测酶反应过程中产物的生成量,如图2-4。由此得出,30℃、40℃、50℃下按照上述不同比例制得的PET-FDL与PET水解酶反应,产物的荧光值随时间而增强。其中,最佳制膜温度为50℃。After the prepared film was reacted with PET degrading enzyme for 48 hours, the release amount of green fluorescence was measured by a microplate reader, and the production amount of the product during the enzyme reaction was detected by HPLC, as shown in Figure 2-4. Therefore, it can be concluded that the PET-FDL prepared according to the above different ratios reacts with PET hydrolase at 30°C, 40°C and 50°C, and the fluorescence value of the product increases with time. Among them, the optimum film-forming temperature is 50°C.
(2)绿色荧光值与产物产量的相关性(2) Correlation between green fluorescence value and product yield
对上述酶反应后的反应液进行HPLC检测,测得相关产物浓度,如图5-8,通过计算得出R2均大于0.96,四种质量配比的PET-FDL膜释放的绿色荧光与产物浓度均呈线性,说明绿色荧光值的大小能精确的反映PET分解后产物的生成量。The reaction solution after the above enzymatic reaction was detected by HPLC, and the concentration of the relevant product was measured, as shown in Figure 5-8. It was calculated that R 2 was greater than 0.96, and the green fluorescence released by the PET-FDL membrane with the four mass ratios was related to the product. The concentrations are all linear, indicating that the green fluorescence value can accurately reflect the amount of products generated after PET decomposition.
三、PET降解酶活性的测定3. Determination of PET-degrading enzyme activity
(1)在反应前检测细胞裂解液中红色荧光值,通过mCarmine的红色荧光值对细胞裂解液中的酶(融合蛋白)浓度进行定量。(1) Detect the red fluorescence value in the cell lysate before the reaction, and quantify the enzyme (fusion protein) concentration in the cell lysate by the red fluorescence value of mCarmine.
(2)融合蛋白与PET-FDL膜进行水解反应。(2) The fusion protein is hydrolyzed with the PET-FDL membrane.
将细胞裂解液与PET-FDL膜在50mM甘氨酸缓冲液中于40℃条件下反应24h,进行水解反应。The cell lysate was reacted with the PET-FDL membrane in 50 mM glycine buffer at 40 °C for 24 h to carry out the hydrolysis reaction.
FDL会随着PET的水解而释放,并立刻被PET水解酶水解为绿色荧光素Fluorescein。FDL is released with the hydrolysis of PET and is immediately hydrolyzed to Fluorescein by PET hydrolase.
(3)测定反应后产物中绿色荧光值(3) Determination of the green fluorescence value in the product after the reaction
荧光素的释放与PET水解产物呈正比,可通过绿色荧光定量检测PET的水解产物。The release of fluorescein is proportional to the PET hydrolyzate, and the PET hydrolyzate can be quantitatively detected by green fluorescence.
(4)通过测得的绿色荧光值与红色荧光值的比值,可确定PET水解酶的活性。(4) The activity of PET hydrolase can be determined by the ratio of the measured green fluorescence value to the red fluorescence value.
以上检测方法可在酶标仪上快速实现,其中红色荧光蛋白mCarmine的激发波长范围为485nm~670nm,最大激发波长为603nm,发射波长范围为610nm~805nm,最大发射波长为675nm;绿色荧光素的激发波长范围为420nm~530nm,最大激发波长为494nm,发射波长范围为485nm~615nm,最大发射波长为525nm。The above detection methods can be quickly implemented on a microplate reader. The excitation wavelength range of red fluorescent protein mCarmine is 485nm-670nm, the maximum excitation wavelength is 603nm, the emission wavelength range is 610nm-805nm, and the maximum emission wavelength is 675nm; The excitation wavelength range is 420nm-530nm, the maximum excitation wavelength is 494nm, the emission wavelength range is 485nm-615nm, and the maximum emission wavelength is 525nm.
实施例2利用实施例1的方法进行PET降解酶高通量筛选的评估Example 2 Evaluation of high-throughput screening of PET-degrading enzymes using the method of Example 1
Z值(Z factor)是目前高通量筛选实验评估和验证中应用广泛的参数,其方法为在96孔板中分别检测样品组和对照组,分别计算样品组的平均值和标准差(SD)。Z值的计算公式及应用方法如下:Z factor (Z factor) is a widely used parameter in the evaluation and verification of high-throughput screening experiments. ). The calculation formula and application method of Z value are as follows:
当0.5≤Z<1时,该检测系统中样品信号分布与对照信号分布的分离程度良好,这表明该分析方法非常好;当0<Z<0.5时表示中等程度的分布分离,表明可进行分析;当Z<0时,说明该系统基本上不可能用于筛选。When 0.5≤Z<1, the separation of the sample signal distribution and the control signal distribution in the detection system is good, which indicates that the analysis method is very good; when 0<Z<0.5, it indicates a moderate degree of distribution separation, indicating that the analysis can be carried out ; When Z<0, it means that the system is basically impossible for screening.
本实施例测试了不同细胞破碎液的量在三个时间下酶反应得到的绿色荧光值和红色荧光值比值的Z值,如图9。In this example, the Z value of the ratio of the green fluorescence value and the red fluorescence value obtained by the enzymatic reaction with different amounts of cell disrupting liquid at three times, as shown in FIG. 9 .
实验选取的细胞破碎液的量为2μL、10μL、15μL,酶反应时间为17h、24h和62h,根据Z值大小可以得出细胞破碎液的最佳用量为10μL时,Z值在不同反应时间下变化最稳定,且均大于0.5,说明该条件下的高通量筛选被验证为有效的。The amount of cell disrupting solution selected in the experiment was 2 μL, 10 μL and 15 μL, and the enzyme reaction time was 17 h, 24 h and 62 h. According to the size of Z value, it can be concluded that the optimal amount of cell disrupting solution was 10 μL, and the Z value was under different reaction times. The changes were the most stable and were all greater than 0.5, indicating that the high-throughput screening under this condition was validated as effective.
最后应说明的是:以上仅用以说明本发明的技术方案,而非对其限制。尽管参照前述各步骤对本发明进行了详细的说明,但本领域的普通技术人员应当理解,其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分或者全部技术特征进行等同替换,而这些修改或者替换,并不使相应技术方案的本质脱离本发明各实施例技术方案的范围。Finally, it should be noted that the above is only used to illustrate the technical solution of the present invention, but not to limit it. Although the present invention has been described in detail with reference to the foregoing steps, those of ordinary skill in the art should understand that the technical solutions described in the foregoing embodiments can still be modified, or some or all of the technical features thereof can be equivalently replaced. , and these modifications or substitutions do not make the essence of the corresponding technical solutions deviate from the scope of the technical solutions of the embodiments of the present invention.
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210182387.1A CN114636682A (en) | 2022-02-25 | 2022-02-25 | A high-throughput assay method and application of PET hydrolase activity based on fluorescence detection |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210182387.1A CN114636682A (en) | 2022-02-25 | 2022-02-25 | A high-throughput assay method and application of PET hydrolase activity based on fluorescence detection |
Publications (1)
Publication Number | Publication Date |
---|---|
CN114636682A true CN114636682A (en) | 2022-06-17 |
Family
ID=81947473
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202210182387.1A Pending CN114636682A (en) | 2022-02-25 | 2022-02-25 | A high-throughput assay method and application of PET hydrolase activity based on fluorescence detection |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN114636682A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2025015288A1 (en) * | 2023-07-12 | 2025-01-16 | Triad National Security, Llc | Methods to improve enzymes that degrade polyethylene terephthalate |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101426923A (en) * | 2006-02-10 | 2009-05-06 | 杜邦塔特和莱尔生物产品有限责任公司 | Biodegradable compositions comprising renewably-based, biodegradable 1,3-propanediol |
CN103348016A (en) * | 2010-05-25 | 2013-10-09 | 三菱丽阳株式会社 | Fluorescent substrate for detection of enzymatic activity of nitrile-related enzyme |
US20140072990A1 (en) * | 2010-05-25 | 2014-03-13 | The University Of Tokyo | Fluorescent substrate for detection of enzymatic activity of nitrile-related enzyme |
CN109880885A (en) * | 2019-01-25 | 2019-06-14 | 浙江工业大学 | A method for double fluorescence screening of β-alanine synthase |
CN110563650A (en) * | 2019-08-27 | 2019-12-13 | 湖南大学 | Ratio type two-photon fluorescent probe of sulfatase, synthetic method and application thereof |
US20210115476A1 (en) * | 2018-06-28 | 2021-04-22 | Light Bio, Inc | Enzymes of luciferin biosynthesis and use thereof |
US20220056387A1 (en) * | 2018-12-14 | 2022-02-24 | Novozymes A/S | Nanoparticles based method for screening enzyme or microorganism |
-
2022
- 2022-02-25 CN CN202210182387.1A patent/CN114636682A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101426923A (en) * | 2006-02-10 | 2009-05-06 | 杜邦塔特和莱尔生物产品有限责任公司 | Biodegradable compositions comprising renewably-based, biodegradable 1,3-propanediol |
CN103348016A (en) * | 2010-05-25 | 2013-10-09 | 三菱丽阳株式会社 | Fluorescent substrate for detection of enzymatic activity of nitrile-related enzyme |
US20140072990A1 (en) * | 2010-05-25 | 2014-03-13 | The University Of Tokyo | Fluorescent substrate for detection of enzymatic activity of nitrile-related enzyme |
US20210115476A1 (en) * | 2018-06-28 | 2021-04-22 | Light Bio, Inc | Enzymes of luciferin biosynthesis and use thereof |
US20220056387A1 (en) * | 2018-12-14 | 2022-02-24 | Novozymes A/S | Nanoparticles based method for screening enzyme or microorganism |
CN109880885A (en) * | 2019-01-25 | 2019-06-14 | 浙江工业大学 | A method for double fluorescence screening of β-alanine synthase |
CN110563650A (en) * | 2019-08-27 | 2019-12-13 | 湖南大学 | Ratio type two-photon fluorescent probe of sulfatase, synthetic method and application thereof |
Non-Patent Citations (1)
Title |
---|
THOMAS ET AL.: "High-Throughput Analysis of Enzymatic Hydrolysis of Biodegradable Polyesters by Monitoring Cohydrolysis of a Polyester-Embedded Fluorogenic Probe", ENVIRONMENTAL SCIENCE & TECHNOLOGY, vol. 51, no. 8, 31 January 2017 (2017-01-31), pages 4358 - 4367, XP055945915, DOI: 10.1021/acs.est.6b06060 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2025015288A1 (en) * | 2023-07-12 | 2025-01-16 | Triad National Security, Llc | Methods to improve enzymes that degrade polyethylene terephthalate |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Phillips et al. | Recent advances in surface plasmon resonance based techniques for bioanalysis | |
JP2020511648A (en) | Analyte detection | |
KR100784437B1 (en) | Sol composition for sol-gel biochip for fixing labeling substance on untreated surface and screening method | |
JP2015524561A (en) | Single molecule protein sequencing | |
CN102105586A (en) | Method for detecting or quantifying DNA | |
WO2010021394A1 (en) | Method for quantification or detection of dna | |
EP1218741A1 (en) | Biosensor detector array | |
CN103714267B (en) | Detection based on kind of characteristic sequences or the method for auxiliary detection test strains | |
CN114636682A (en) | A high-throughput assay method and application of PET hydrolase activity based on fluorescence detection | |
Zhang et al. | Detection of single peptide with only one amino acid modification via electronic fingerprinting using reengineered durable channel of Phi29 DNA packaging motor | |
Zhang et al. | A single-molecule nanopore sequencing platform | |
Zhang et al. | A CRISPR/Cas12a-assisted array for Helicobacter pylori DNA analysis in saliva | |
US20100297779A1 (en) | Biochip Self-Calibration Process | |
CN106033087B (en) | The method system of built-in property standard curve detection substance molecular number | |
Sugai et al. | Fingerprint-based Protein Identification in Cell Culture Medium Using Environment-sensitive Turn-on Fluorescent Polymer. | |
CN102141533B (en) | Method for analyzing result of loop-mediated isothermal amplification | |
CN114894753A (en) | Aptamer biosensor based on CRISPR-Cas14 system and application thereof | |
CN116769043B (en) | An antigen-triggered fluorescent probe based on quinalphos nanoantibody and its preparation method and application | |
CN108089006B (en) | A method for measuring the activity of coagulation factor X activator | |
CN115792231B (en) | DNase I biosensor based on thrombin aptamer-regulated enzyme cascade reaction | |
CN103667039B (en) | Quality sensor for gene detection as well as preparation method and application of quality sensor | |
TWI855793B (en) | Biosensor chip and related method | |
Tomita et al. | Chemical tongues as multipurpose bioanalytical tools for the characterization of complex biological samples | |
CN112501267B (en) | RNA exonuclease-nanopore complex and preparation method and application thereof | |
WO2011127042A1 (en) | High capacity analyte detection |
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 |