CN115420779A - Pt NPs@TPB NCs/dissolved O2 ternary electrochemiluminescence biosensor, preparation method and application - Google Patents
Pt NPs@TPB NCs/dissolved O2 ternary electrochemiluminescence biosensor, preparation method and application Download PDFInfo
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Abstract
本发明提供一种基于Pt NPs@TPB NCs/溶解O2三元电致化学发光体系的生物传感器、制备方法及应用。所述三元电致化学发光体系包括:四苯基‑1,3‑丁二烯纳米晶TPB NCs与内源性共反应剂溶解O2以及溶解O2的共反应促进剂铂纳米粒子Pt NPs构成的Pt NPs@TPB NCs/溶解O2ECL信号体系;所述铂纳米粒子包裹四苯基‑1,3‑丁二烯纳米晶Pt NPs@TPB NCs作为ECL发光材料。本发明的发光体系,展示出超高的ECL发光效率。基于此发光体系构建的新型ECL生物传感器,用于肿瘤标志物microRNA‑21的应用检测,具有操作简单、反应快速、检测范围为100aM到100pM、检测限低至83.8aM的优点。
The invention provides a biosensor based on a Pt NPs@TPB NCs/dissolved O 2 ternary electrochemiluminescence system, a preparation method and an application. The ternary electrochemiluminescence system includes: tetraphenyl-1,3-butadiene nanocrystalline TPB NCs and endogenous co-reactant dissolved O 2 and co-reaction accelerator platinum nanoparticles Pt NPs dissolved O 2 Constituted Pt NPs@TPB NCs/dissolved O 2 ECL signal system; the platinum nanoparticles wrap tetraphenyl-1,3-butadiene nanocrystal Pt NPs@TPB NCs as ECL luminescent material. The luminous system of the present invention exhibits ultra-high ECL luminous efficiency. The new ECL biosensor based on this luminescent system is used for the application detection of tumor marker microRNA-21, which has the advantages of simple operation, fast response, detection range of 100aM to 100pM, and detection limit as low as 83.8aM.
Description
技术领域technical field
本发明涉及电致化学发光领域及生物分析检测领域,具体涉及一种基于Pt NPs@TPB NCs/溶解O2三元电致化学发光体系的生物传感器、制备方法及应用。The invention relates to the field of electrochemiluminescence and the field of biological analysis and detection, in particular to a biosensor based on a Pt NPs@TPB NCs/dissolved O 2 ternary electrochemiluminescence system, a preparation method and an application thereof.
背景技术Background technique
电致化学发光(ECL)是由电化学过程激发的一项有前景的分析技术,由于其具有高可控性、低背景信号和高灵敏度1,已逐渐应用于环境监测2、食品安全3和临床诊断领域4。随着水相ECL发光体的发展5-8,聚集诱导发射(AIE)ECL研究的兴起9,10为有机分子的强ECL发射打开了大门。处于自由状态的AIE分子几乎没有明显的ECL信号,而在聚集状态下,通过多种机制(如配位诱导增强ECL11、离子诱导的AIE自组装12等)抑制AIE分子中的非辐射跃迁,增强辐射跃迁,从而提高其ECL信号。Electrochemiluminescence (ECL ) , a promising analytical technique inspired by electrochemical processes, has been gradually applied in environmental monitoring2, food safety3 and The field of clinical diagnosis 4 . With the development of aqueous ECL luminophores5-8 , the rise of aggregation-induced emission ( AIE ) ECL research9,10 opened the door to strong ECL emission from organic molecules. AIE molecules in the free state have almost no obvious ECL signal, while in the aggregated state, non-radiative transitions in AIE molecules are suppressed through various mechanisms (such as coordination-induced enhancement of ECL 11 , ion-induced AIE self-assembly 12 , etc.), Enhances the radiative transition, thereby enhancing its ECL signal.
然而,目前已报道的AIE纳米材料的ECL信号均源于ECL发光体与外源共反应试剂(如过二硫酸根(S2O8 2-),三丙胺(TPrA)等)之间的相互作用,外加共反应试剂增加了水溶液中ECL反应过程的复杂性13。与这些外源性共反应剂相比,溶解O2作为内源性共反应剂具有稳定且无毒的优势,是一种很有前景的共反应试剂,然而,由于溶解O2面临着产生活性氧自由基(ROS,如O2 ·-和OH·)的反应活性低的困境,目前还没有报道过以溶解O2为共反应试剂的AIE纳米材料ECL发光体系。However, the ECL signals of AIE nanomaterials reported so far are all derived from the interaction between ECL luminophores and exogenous coreactive reagents (such as peroxodisulfate (S 2 O 8 2- ), tripropylamine (TPrA), etc. role, the addition of co-reaction reagents increases the complexity of the ECL reaction process in aqueous solution 13 . Compared with these exogenous co-reactants, dissolved O2 as an endogenous co - reactant has the advantage of being stable and non-toxic, and is a promising co-reactant. Due to the low reactivity of oxygen radicals (ROS, such as O 2 ·- and OH · ), no AIE nanomaterial ECL luminescence system using dissolved O 2 as a co-reactant has been reported.
研究表明,microRNA在癌症致病机理及发生、发展中起着关键作用,因此,高效、超灵敏检测microRNA在人体癌细胞内的含量对癌症的早期诊断与治疗具有重要的意义。然而,目前microRNA检测技术(Northern blot杂交检测、反转录聚合酶链反应(RT-PCR)等)由于灵敏度相对较低、引物设计复杂等缺点,难于满足microRNA的快速、超灵敏检测。因此,建立灵敏度高、响应快速的癌症标志物microRNA分析新方法用于疾病的早期筛查、临床诊断及治疗具有重要的临床价值和社会意义,是本领域技术人员不懈努力的方向。Studies have shown that microRNA plays a key role in the pathogenesis, occurrence and development of cancer. Therefore, efficient and ultra-sensitive detection of the content of microRNA in human cancer cells is of great significance for the early diagnosis and treatment of cancer. However, the current microRNA detection technology (Northern blot hybridization detection, reverse transcription polymerase chain reaction (RT-PCR), etc.) is difficult to meet the rapid and ultra-sensitive detection of microRNA due to the shortcomings of relatively low sensitivity and complicated primer design. Therefore, establishing a new method for the analysis of cancer marker microRNA with high sensitivity and rapid response for early screening, clinical diagnosis and treatment of diseases has important clinical value and social significance, and is the direction of unremitting efforts of those skilled in the art.
发明内容Contents of the invention
有鉴于此,为了克服现有技术的不足,本发明提出一种由铂纳米粒子(PtNPs)包裹的四苯基-1,3-丁二烯纳米晶(Pt NPs@TPB NCs)/溶解O2三元ECL体系,其中PtNPs对溶解氧具有共反应促进作用。与现有技术的Ru(bpy)3 2+/溶解O2体系相比,Pt NPs@TPB NCs展示出超高ECL发光效率。并且基于此Pt NPs@TPB NCs/溶解O2三元ECL体系,结合目标物诱导的DNA步行器本发明构建了一种新型超灵敏的ECL生物传感器,可用于癌细胞中microRNA-21的检测。In view of this, in order to overcome the deficiencies of the prior art, the present invention proposes a tetraphenyl-1,3-butadiene nanocrystal (Pt NPs@TPB NCs)/dissolved O 2 wrapped by platinum nanoparticles (PtNPs) Ternary ECL system in which PtNPs have a co-reaction promoting effect on dissolved oxygen. Compared with the state-of-the-art Ru(bpy) 3 2+ /dissolved O 2 system, Pt NPs@TPB NCs exhibit ultrahigh ECL luminescence efficiency. And based on the Pt NPs@TPB NCs/dissolved O 2 ternary ECL system, combined with the target-induced DNA walker, a novel ultrasensitive ECL biosensor was constructed, which can be used for the detection of microRNA-21 in cancer cells.
本发明提供一种Pt NPs@TPB NCs/溶解O2的三元电致化学发光体系,所述三元电致化学发光体系包括:四苯基-1,3-丁二烯纳米晶TPB NCs与内源性共反应剂溶解O2以及溶解O2的共反应促进剂铂纳米粒子Pt NPs构成的Pt NPs@TPB NCs/溶解O2 ECL信号体系;The invention provides a ternary electrochemiluminescence system of Pt NPs@TPB NCs/dissolved O 2 , the ternary electrochemiluminescence system comprises: tetraphenyl-1,3-butadiene nanocrystal TPB NCs and Pt NPs@TPB NCs/dissolved O 2 ECL signal system composed of endogenous co-reactant dissolved O 2 and O 2 co-reaction accelerator platinum nanoparticles Pt NPs;
所述铂纳米粒子包裹四苯基-1,3-丁二烯纳米晶Pt NPs@TPB NCs作为ECL发光材料。The platinum nanoparticles wrap tetraphenyl-1,3-butadiene nanocrystal Pt NPs@TPB NCs as ECL luminescent material.
进一步,所述共反应促进剂Pt NPs是以柠檬酸钠为保护剂制备而成。Further, the co-reaction accelerator Pt NPs is prepared using sodium citrate as a protecting agent.
本发明还提供上述三元电致化学发光体系的构建方法,所述方法包括步骤:The present invention also provides a method for constructing the above-mentioned ternary electrochemiluminescent system, the method comprising the steps of:
A.制备铂纳米粒子包裹的四苯基-1,3-丁二烯纳米晶Pt NPs@TPB NCs作为ECL发光材料;A. Preparation of tetraphenyl-1,3-butadiene nanocrystalline Pt NPs@TPB NCs wrapped in platinum nanoparticles as ECL luminescent material;
B.将Pt NPs@TPB NCs溶液涂在玻碳电极GCE表面,干燥成膜后,将所述电极置于空气饱和的PBS中获得Pt NPs@TPB NCs/GCE的ECL响应。B. The Pt NPs@TPB NCs solution was coated on the surface of the glassy carbon electrode GCE, and after drying to form a film, the electrode was placed in air-saturated PBS to obtain the ECL response of Pt NPs@TPB NCs/GCE.
进一步,所述Pt NPs@TPB NCs的制备包括步骤:Further, the preparation of the Pt NPs@TPB NCs includes steps:
A.1.将TPB NCs分散到去离子水中以获得均匀的TPB NCs溶液,A.1. Disperse TPB NCs into deionized water to obtain a homogeneous TPB NCs solution,
A.2.将柠檬酸钠和H2PtCl6水溶液注入所述TPB NCs溶液中搅拌,在连续搅拌下快速加入冰冷NaBH4溶液;A.2. Inject sodium citrate and H 2 PtCl 6 aqueous solution into the TPB NCs solution and stir, and quickly add ice-cold NaBH 4 solution under continuous stirring;
A.3.溶液颜色变成深棕色后离心,将沉淀物溶解在去离子水中,得到Pt NPs@TPBNCs溶液。A.3. Centrifuge the solution after it turns dark brown, and dissolve the precipitate in deionized water to obtain a Pt NPs@TPBNCs solution.
进一步,所述TPB NCs的制备步骤包括:Further, the preparation steps of the TPB NCs include:
A.1.1将四苯基-1,3-丁二烯粉末溶解在四氢呋喃中,得到TPB溶液;A.1.1 Dissolve tetraphenyl-1,3-butadiene powder in tetrahydrofuran to obtain TPB solution;
A.1.2将TPB溶液逐滴注入泊洛沙姆188溶液中进行超声处理;A.1.2 Inject the TPB solution dropwise into the Poloxamer 188 solution for ultrasonic treatment;
A.1.3除去THF后,将溶液离心并用去离子水反复洗涤,离心,得到TPB NCs沉淀,将其溶于去离子水中得到所述TPB NCs。A.1.3 After removing THF, the solution was centrifuged and washed repeatedly with deionized water, centrifuged to obtain TPB NCs precipitate, which was dissolved in deionized water to obtain the TPB NCs.
本发明还提供基于上述三元电致化学发光体系的生物传感器,所述生物传感器包括:The present invention also provides a biosensor based on the above-mentioned ternary electrochemiluminescent system, the biosensor comprising:
I.上述的三元电致化学发光体系,并且GCE滴加己硫醇封闭非特异性位点;I. The above-mentioned ternary electrochemiluminescence system, and GCE is dripped with hexanethiol to block non-specific sites;
Ⅱ.修饰到GCE上的核苷酸捕获探针;Ⅱ. Nucleotide capture probes modified to GCE;
Ⅲ.待测物诱导的DNA步行放大器。III. Analyte-induced DNA walking amplifiers.
本发明还提供上述三元电致化学发光生物传感器的制备方法,所述方法包括步骤:The present invention also provides a method for preparing the above-mentioned ternary electrochemiluminescence biosensor, the method comprising the steps of:
(1)将Pt NPs@TPB NCs溶液涂在GCE表面上,在37℃的培养箱中干燥;(1) Apply the Pt NPs@TPB NCs solution on the GCE surface and dry it in an incubator at 37 °C;
(2)将带有氨基的捕获探针修饰到GCE上,在4℃下孵育过夜;(2) Modify the capture probe with amino groups onto GCE and incubate overnight at 4°C;
(3)用去离子水冲洗后,将修饰的GCE滴加己硫醇,封闭非特异性位点,得到生物传感器;(3) After washing with deionized water, the modified GCE was added dropwise with hexanethiol to block non-specific sites to obtain a biosensor;
(4)待测物诱导的DNA步行器放大产物溶液在制备的所述生物传感器上孵育,PBS洗涤后,在空气饱和的PBS溶液中测量生物传感器的ECL信号。(4) The analyte-induced DNA walker amplification product solution was incubated on the prepared biosensor, and after washing with PBS, the ECL signal of the biosensor was measured in an air-saturated PBS solution.
进一步,所述待测物诱导的DNA步行器放大产物溶液的制备步骤是:Further, the preparation steps of the DNA walker amplification product solution induced by the analyte are:
(a.)将DNA发夹探针HP形成茎环结构,同时底物DNA SD和二茂铁修饰的DNA探针P-Fc生成双链体结构SD/P-Fc;(a.) DNA hairpin probe HP is formed into a stem-loop structure, while substrate DNA SD and ferrocene-modified DNA probe P-Fc generate duplex structure SD/P-Fc;
(b.)将将羧基包裹的磁珠MBs用1-(3-二甲氨基丙基)-3-乙基碳二亚胺盐酸盐(EDC)活化,并与标记有氨基的HP和SD/P-Fc以及N-羟基琥珀酰亚胺(NHS)溶液混合,通过酰胺键将所述HP和SD/P-Fc交联在MBs上组装DNA步行器;(b.) The carboxyl-coated magnetic beads MBs were activated with 1-(3-dimethylaminopropyl)-3-ethylcarbodiimide hydrochloride (EDC) and mixed with amino-labeled HP and SD /P-Fc and N-hydroxysuccinimide (NHS) solutions were mixed, and the HP and SD/P-Fc were cross-linked through amide bonds to assemble DNA walkers on MBs;
(c.)磁性分离后,将DNA步行器重新分散在含有不同浓度目标物miRNA-21和Pb2+的反应液中30℃反应2小时;(c.) After magnetic separation, the DNA walker was redispersed in the reaction solution containing different concentrations of target miRNA-21 and Pb 2+ and reacted at 30°C for 2 hours;
(d.)通过磁分离收集含有SD/P-Fc的上清液作为DNA步行器放大产物溶液。(d.) The SD/P-Fc-containing supernatant was collected by magnetic separation as a DNA walker amplification product solution.
本发明还提供上述生物传感器的应用,所述应用是检测细胞中miRNA-21的表达水平。The present invention also provides the application of the above biosensor, the application is to detect the expression level of miRNA-21 in cells.
进一步,所述应用包括步骤:Further, the application includes the steps of:
a.将细胞裂解液中的miRNA-21诱导的DNA步行器放大反应后孵育到所述生物传感器中;a. Incubating the DNA walker amplification reaction induced by miRNA-21 in the cell lysate into the biosensor;
b.检测ECL信号;b. Detect ECL signal;
c.当待检细胞随着细胞个数增加,传感器的ECL响应略有下降,则miRNA-21在细胞中低表达;ECL信号明显降低,则表明miRNA-21在细胞中高表达。c. When the ECL response of the sensor decreases slightly with the increase of the number of cells to be tested, the expression of miRNA-21 in the cell is low; the ECL signal decreases significantly, indicating that the expression of miRNA-21 in the cell is high.
与现有技术相比,本发明的有益效果在于:Compared with prior art, the beneficial effect of the present invention is:
(1)本发明首次采用内源性ECL共反应试剂溶解O2作为聚集诱导发射(AIE)纳米材料的ECL共反应试剂,替代了传统毒性较大的胺类共反应试剂,有利于环境保护,同时避免了外源性共反应试剂的加入,简化了实验操作。(1) The present invention adopts endogenous ECL co-reaction reagent to dissolve O for the first time As the ECL co - reaction reagent of aggregation-induced emission (AIE) nanomaterials, it replaces the traditional toxic amine co-reaction reagent, which is beneficial to environmental protection, At the same time, the addition of exogenous co-reaction reagents is avoided, and the experimental operation is simplified.
(2)本发明提出了以铂纳米粒子包裹的四苯基-1,3-丁二烯纳米晶(Pt NPs@TPBNCs)作为ECL发光材料,展示出超高的ECL发光效率,同时探究了Pt NPs@TPB NCs/溶解O2三元ECL体系中PtNPs对溶解O2明显的共反应促进作用。(2) The present invention proposes tetraphenyl-1,3-butadiene nanocrystals (Pt NPs@TPBNCs) wrapped with platinum nanoparticles as an ECL luminescent material, which exhibits ultra-high ECL luminous efficiency. The obvious co-reaction promotion of dissolved O 2 by PtNPs in the NPs@TPB NCs/dissolved O 2 ternary ECL system.
(3)本发明基于Pt NPs@TPB NCs/溶解O2三元ECL体系提供强的ECL信号,结合目标物诱导的DNA步行器实现目标物microRNA-21的高效转化,构建了一种新型的ECL生物传感平台,有望应用于肿瘤标志物microRNA-21的临床检测,具有操作简单,反应快速,检测范围为100aM到100pM,检测限低至83.8aM的优点。(3) The present invention provides a strong ECL signal based on the Pt NPs@TPB NCs/dissolved O 2 ternary ECL system, combined with the target-induced DNA walker to achieve efficient conversion of the target microRNA-21, and constructs a new type of ECL The biosensing platform is expected to be applied to the clinical detection of tumor marker microRNA-21. It has the advantages of simple operation, fast response, detection range of 100aM to 100pM, and detection limit as low as 83.8aM.
附图说明Description of drawings
图1:TPB NCs/GCE在空气饱和的PBS中的CV曲线和相应的ECL信号;Figure 1: CV curves and corresponding ECL signals of TPB NCs/GCE in air-saturated PBS;
A.当在空气饱和的PBS溶液中扫描TPB NCs/GCE时,在-0.6V左右出现微弱的O2还原峰,B.在+1.25V处观察到TPB NCs的弱ECL信号(5a.u.)。A. When scanning TPB NCs/GCE in air-saturated PBS solution, a weak O2 reduction peak appeared around -0.6V, B. A weak ECL signal of TPB NCs was observed at +1.25V (5a.u. ).
图2:以a.Pt NPs-1,b.Pt NPs-2,c.Pt NPs-3,d.Pt NPs-4或e.Pt NFs作为共反应促进剂的TPB NCs修饰电极的A.CV曲线和B.相应的ECL曲线。Figure 2: A.CV of TPB NCs modified electrodes with a.Pt NPs-1, b.Pt NPs-2, c.Pt NPs-3, d.Pt NPs-4 or e.Pt NFs as co-reaction promoters Curves and B. Corresponding ECL curves.
图3:a.Pt NPs@TPB NCs/GCE在空气饱和PBS中,b.Pt NPs@TPB NCs/GCE在N2饱和的PBS中,c.Pt NPs@TPB NCs/GCE在含有30U mL-1SOD的空气饱和PBS中,或d.Pt NPs@TPBNCs/GCE在含有150nM L-cys的空气饱和PBS中的A.CV曲线和B.相应的ECL曲线。Figure 3: a.Pt NPs@TPB NCs/GCE in air-saturated PBS, b.Pt NPs@TPB NCs/GCE in N2 -saturated PBS, c.Pt NPs@TPB NCs/GCE in 30U mL -1 A. CV curves and B. corresponding ECL curves of SOD in air-saturated PBS, or d. Pt NPs@TPBNCs/GCE in air-saturated PBS containing 150 nM L-cys.
图4:A.孵育不同浓度miRNA-21的生物传感器的ECL曲线(从a-g:100aM、1fM、10fM、100fM、1pM、10pM或100pM);B.ΔIECL强度与miRNA-21浓度对数之间的校准曲线;C.不同干扰miRNA下测试ECL生物传感器的特异性;(误差棒,SD,n=3);D.本发明生物传感器在miRNA-21浓度为100pM时,连续扫描14个周期下的稳定性。Figure 4: A. ECL curves of biosensors incubated with different concentrations of miRNA-21 (from ag: 100aM, 1fM, 10fM, 100fM, 1pM, 10pM or 100pM); B. Between ΔI ECL intensity and logarithm of miRNA-21 concentration Calibration curve; C. The specificity of testing the ECL biosensor under different interfering miRNAs; (error bars, SD, n=3); D. The biosensor of the present invention was continuously scanned for 14 cycles when the miRNA-21 concentration was 100pM stability.
图5:不同细胞数量的Hela和MCF-7中miRNA-21的检测,a.细胞数量10个,b.细胞数量102个,c.细胞数量103个,d.细胞数量104个,或e.细胞数量105个。Figure 5: Detection of miRNA-21 in Hela and MCF-7 with different cell numbers, a. 10 cells, b. 10 2 cells, c. 10 3 cells, d. 10 4 cells, Or e. The number of cells is 10 5 .
图6:制备的Pt纳米材料的形态学,其中A.比例尺:1cm=10nm,B.比例尺:1cm=5nm。Figure 6: Morphology of prepared Pt nanomaterials, where A. Scale bar: 1 cm = 10 nm, B. Scale bar: 1 cm = 5 nm.
图7:本发明的技术路线图:(A)Pt NPs@TPB NCs的合成示意图;(B)“signal off”ECL生物传感平台的构建;(C)待测目标物诱导的DNA步行器放大策略的原理。Figure 7: The technical roadmap of the present invention: (A) Schematic diagram of the synthesis of Pt NPs@TPB NCs; (B) construction of "signal off" ECL biosensing platform; (C) DNA walker amplification induced by the target to be tested The rationale for the strategy.
具体实施方式detailed description
实施例1:TPB NCs/溶解O2体系的ECL信号Example 1 : ECL signal of TPB NCs/dissolved O system
一、TPB NCs的制备1. Preparation of TPB NCs
首先,将5mg四苯基-1,3-丁二烯(TPB)粉末溶解在5mL四氢呋喃中,得到1mg/mLTPB溶液。随后,将1mL TPB溶液(1mg/mL)逐滴注入10mL泊洛沙姆188(普朗尼克F68)溶液(10mg/mL)中进行超声处理30分钟。然后,除去THF后,将溶液离心并用去离子水反复洗涤,离心,得到TPB NCs沉淀,将其溶于1mL去离子水中得到TPB NCs(1mg/mL)。First, 5 mg of tetraphenyl-1,3-butadiene (TPB) powder was dissolved in 5 mL of tetrahydrofuran to obtain a 1 mg/mL TPB solution. Subsequently, 1 mL of TPB solution (1 mg/mL) was injected dropwise into 10 mL of Poloxamer 188 (Pluronic F68) solution (10 mg/mL) for 30 minutes of sonication. Then, after removing THF, the solution was centrifuged and washed repeatedly with deionized water, and centrifuged to obtain a precipitate of TPB NCs, which was dissolved in 1 mL of deionized water to obtain TPB NCs (1 mg/mL).
二、检测过程2. Detection process
首先采用0.3和0.05μm的氧化铝粉末在麂皮上对玻碳电极(GCE,Φ=4mm)进行抛光,并置于超纯水和乙醇中交替超声清洁,氮气吹干待用。然后,将5μL TPB NCs溶液涂在GCE表面上,在37℃的培养箱中干燥成膜。随后,将修饰电极置于空气饱和的0.1M pH7.4PBS中采用MPI-EII型电致化学发光检测仪测量修饰电极的ECL信号,扫描电位为-1V至1.3V,扫描速率为0.3V/s。放大器增益设置为10×。Firstly, the glassy carbon electrode (GCE, Φ=4mm) was polished on the suede with 0.3 and 0.05 μm alumina powder, and then ultrasonically cleaned alternately in ultrapure water and ethanol, and dried with nitrogen gas for later use. Then, 5 μL of TPB NCs solution was coated on the surface of GCE and dried in a 37 °C incubator to form a film. Subsequently, the modified electrode was placed in air-saturated 0.1M pH7.4PBS and the ECL signal of the modified electrode was measured with an MPI-EII electrochemiluminescence detector, with a scanning potential of -1V to 1.3V and a scanning rate of 0.3V/s . The amplifier gain is set to 10×.
当在空气饱和的PBS溶液中扫描TPB NCs/GCE时,在-0.6V左右出现微弱的O2还原峰(图1A),在+1.25V处观察到TPB NCs的弱ECL信号(5a.u.,图1B),这表明TPB NCs作为ECL发光体可以在电极表面失去电子产生TPB NCs自由基阳离子(TPB NCs·+),与少量ROS反应生成TPB NCs的激发态(TPB NCs*)从而获得ECL信号。When scanning TPB NCs/GCE in air-saturated PBS solution, a weak O2 reduction peak appeared around -0.6V (Fig. 1A), and a weak ECL signal of TPB NCs was observed at +1.25V (5a.u. , Figure 1B), which indicates that TPB NCs as ECL emitters can lose electrons on the electrode surface to generate TPB NCs radical cations (TPB NCs + ), which react with a small amount of ROS to generate excited states of TPB NCs (TPB NCs * ) to obtain ECL Signal.
实施例2:不同Pt NPs对TPB NCs的共反应加速性能。Example 2: Co-reaction acceleration performance of different Pt NPs on TPB NCs.
纳米材料的共反应加速作用概括为两个方面,一是纳米材料对溶解氧(O2)的富集作用,二是材料表面促进溶解O2产生活性氧自由基(ROS)的能力。因此,通过制备不同PtNPs并测量以不同Pt NPs作为共反应促进剂的TPB NCs的电化学和ECL信号,研究了共反应加速能力与Pt NPs表面性质之间的相关性。并且通过透射电子显微镜(TEM)表征所制备的Pt NPs的相应形态。The co-reaction acceleration of nanomaterials can be summarized into two aspects. One is the enrichment of dissolved oxygen (O 2 ) by nanomaterials, and the other is the ability of the material surface to promote dissolved O 2 to generate reactive oxygen species (ROS). Therefore, by preparing different PtNPs and measuring the electrochemical and ECL signals of TPB NCs with different Pt NPs as co-reaction accelerators, the correlation between the co-reaction accelerating ability and the surface properties of Pt NPs was investigated. And the corresponding morphology of the as-prepared Pt NPs was characterized by transmission electron microscopy (TEM).
不同Pt纳米粒子的制备。Preparation of different Pt nanoparticles.
(1)Pt NPs-1以NaBH4为还原剂制备不含保护剂的Pt NPs。(1) Pt NPs-1 prepared Pt NPs without protective agent by using NaBH 4 as reducing agent.
首先,将5mL 0.01M现配的NaBH4溶液逐滴注入4mL 2mM H2PtCl6水溶液中,剧烈搅拌20分钟。离心后,沉淀用无水乙醇和去离子水交替洗涤,再溶于去离子水中备用。First, 5 mL of 0.01 M freshly prepared NaBH 4 solution was injected dropwise into 4 mL of 2 mM H 2 PtCl 6 aqueous solution and vigorously stirred for 20 min. After centrifugation, the precipitate was alternately washed with absolute ethanol and deionized water, and then dissolved in deionized water for later use.
(2)Pt NPs-2以十六烷基三甲基溴化铵(CTAB)作为保护剂的Pt NPs。(2) Pt NPs-2 Pt NPs with cetyltrimethylammonium bromide (CTAB) as protective agent.
将150mM CTAB和1.5mM K2PtCl4溶液在50℃下加热5分钟以混合均匀。然后,在注入冰冷的NaBH4(1mL,30mM)后,用保鲜膜盖住烧杯,并通过膜上的针头释放烧杯内的H2。随后用保鲜膜堵住针头,将溶液在50℃保持6小时。最后,将溶液以3000rpm离心30分钟得到上清液,再以12000rpm离心10分钟得到沉淀物。Heat the 150 mM CTAB and 1.5 mM K2PtCl4 solution at 50 °C for 5 min to mix well. Then, after injecting ice-cold NaBH 4 (1 mL, 30 mM), the beaker was covered with plastic wrap, and the H 2 in the beaker was released through a needle on the film. The needle was then blocked with plastic wrap and the solution was kept at 50°C for 6 hours. Finally, the solution was centrifuged at 3000 rpm for 30 minutes to obtain a supernatant, and then centrifuged at 12000 rpm for 10 minutes to obtain a precipitate.
(3)Pt NPs-3以3-噻吩丙二酸(TA)作为保护剂的Pt NPs(3) Pt NPs-3 Pt NPs with 3-thiophene malonate (TA) as protective agent
将1mL 0.038M H2PtCl6水溶液加入50mL去离子水中。然后,将0.5mL 0.3M TA滴加到上述溶液中,将所形成的溶液在100℃下加热20分钟,得到深棕色溶液。Add 1 mL of 0.038M H 2 PtCl 6 aqueous solution to 50 mL of deionized water. Then, 0.5 mL of 0.3 M TA was added dropwise to the above solution, and the resulting solution was heated at 100 °C for 20 min to obtain a dark brown solution.
(4)Pt NPs-4以柠檬酸钠为保护剂的Pt NPs。(4) Pt NPs-4 Pt NPs with sodium citrate as protective agent.
首先,将1mL H2PtCl6(16mM)水溶液和1mL 40mM柠檬酸钠溶液用去离子水稀释至38mL,避光搅拌30分钟。然后在2分钟内将0.2mL 50mM NaBH4溶液注入上述溶液中。当溶液颜色由浅黄色变为棕色时,溶液在暗处继续搅拌1小时,获得Pt NPs-4。First, 1 mL of H 2 PtCl 6 (16 mM) aqueous solution and 1 mL of 40 mM sodium citrate solution were diluted to 38 mL with deionized water, and stirred for 30 minutes in the dark. Then inject 0.2 mL of 50 mM NaBH4 solution into the above solution within 2 min. When the color of the solution changed from light yellow to brown, the solution was stirred for 1 hour in the dark to obtain Pt NPs-4.
(5)Pt NPs-5以葡萄糖为保护剂的Pt NPs。(5) Pt NPs-5 Pt NPs with glucose as protective agent.
将0.8g葡萄糖和0.2g抗坏血酸通过80℃水浴加热溶解到30mL去离子水中。随后,将1mL H2PtCl6(20mM)添加到溶液中,搅拌5分钟形成Pt NPs溶胶。然后,将溶液置于50℃的水浴中约15分钟,同时加入0.3mL H2PtCl6(20mM)以获得Pt纳米花(Pt NPs-5)。Dissolve 0.8 g of glucose and 0.2 g of ascorbic acid in 30 mL of deionized water by heating in a water bath at 80 °C. Subsequently, 1 mL of H 2 PtCl 6 (20 mM) was added to the solution and stirred for 5 min to form a sol of Pt NPs. Then, the solution was placed in a water bath at 50° C. for about 15 minutes while 0.3 mL of H 2 PtCl 6 (20 mM) was added to obtain Pt nanoflowers (Pt NPs-5).
不同Pt NPs对TPB NCs的CV及ECL信号的影响。Effects of different Pt NPs on the CV and ECL signals of TPB NCs.
首先采用0.3和0.05μm的氧化铝粉末在麂皮上对玻碳电极(GCE,Φ=4mm)进行抛光,并置于超纯水和乙醇中交替超声清洁,氮气吹干待用。然后,将5μL TPB NCs溶液涂在GCE表面上,在37℃的培养箱中干燥后,继续滴涂Pt NPs-1,并在37℃的培养箱中干燥成膜。随后,将修饰电极置于0.1M pH 7.4PBS中采用MPI-E型电致化学发光检测仪测量修饰电极的ECL信号,扫描电位为-1V至1.3V,扫描速率为0.3V/s。放大器增益设置为10×(Pt NPs-2~Pt NPs-5的修饰及检测过程与上述一致)。结果如下:Firstly, the glassy carbon electrode (GCE, Φ=4mm) was polished on the suede with 0.3 and 0.05 μm alumina powder, and then ultrasonically cleaned alternately in ultrapure water and ethanol, and dried with nitrogen gas for later use. Then, 5 μL of TPB NCs solution was coated on the GCE surface, and after drying in a 37 °C incubator, Pt NPs-1 was continued to be drip-coated and dried in a 37 °C incubator to form a film. Subsequently, the modified electrode was placed in 0.1M pH 7.4 PBS and the ECL signal of the modified electrode was measured with an MPI-E electrochemiluminescence detector, with a scanning potential of -1V to 1.3V and a scanning rate of 0.3V/s. The amplifier gain was set to 10× (the modification and detection process of Pt NPs-2~Pt NPs-5 were consistent with the above). The result is as follows:
与不含保护剂的Pt NPs-1的ECL信号(曲线a,图2B)相比,使用十六烷基三甲基溴化铵(CTAB)作为保护剂的Pt NPs-2显示出较弱的ECL信号(曲线b,图2B),这可能归因于PtNPs-2表面催化位点的不完全暴露会影响催化性能。值得注意的是,3-噻吩丙二酸(TA)稳定的Pt NPs(Pt NPs-3)在所有Pt NPs中表现出最弱的ECL响应,这归因于无定形态的Pt NPs-3具有低的催化性能。此外,我们还采用柠檬酸钠和葡萄糖作为保护剂合成了不同形态的PtNPs(Pt NPs-4和Pt NFs)。如图2A所示,Pt NPs-4和Pt NFs都从约-0.6V开始出现溶解O2的强还原电流(曲线d和e)。同时,作为共反应促进剂的Pt NPs-4显示出最高的ECL信号,这归因于粒径均匀的Pt NPs具有较大的比表面积富集氧气和优异催化活性产生大量的ROS。因此,Pt NPs的表面催化位点和粒径会强烈影响溶解O2中ROS的产生。因此,将柠檬酸钠还原的Pt NPs-4用于合成Pt NPs@TPB NCs以进行进一步的性能研究。制备的Pt纳米材料(PtNPs-4)的形态学如图6所示。Compared with the ECL signal of Pt NPs-1 without protecting agent (curve a, Figure 2B), Pt NPs-2 using cetyltrimethylammonium bromide (CTAB) as protecting agent showed weaker The ECL signal (curve b, Fig. 2B), which may be attributed to the incomplete exposure of catalytic sites on the surface of PtNPs-2 would affect the catalytic performance. Notably, 3-thiophenemalonic acid (TA)-stabilized Pt NPs (Pt NPs-3) showed the weakest ECL response among all Pt NPs, which was attributed to the amorphous Pt NPs-3 having low catalytic performance. In addition, we also synthesized different morphologies of PtNPs (Pt NPs-4 and Pt NFs) using sodium citrate and glucose as protective agents. As shown in Figure 2A, both Pt NPs- 4 and Pt NFs exhibit strong reduction currents for dissolved O starting from about −0.6 V (curves d and e). Meanwhile, Pt NPs-4 as a co-reaction promoter showed the highest ECL signal, which was attributed to the large specific surface area of Pt NPs with uniform particle size for enriching oxygen and excellent catalytic activity to generate a large amount of ROS. Therefore, the surface catalytic sites and particle size of Pt NPs can strongly affect the generation of ROS in dissolved O. Therefore, sodium citrate-reduced Pt NPs-4 was used to synthesize Pt NPs@TPB NCs for further performance studies. The morphology of the prepared Pt nanomaterials (PtNPs-4) is shown in Fig. 6.
实施例3:Pt NPs@TPB NCs的ECL增强机制Example 3: ECL enhancement mechanism of Pt NPs@TPB NCs
一、Pt NPs@TPB NCs的制备1. Preparation of Pt NPs@TPB NCs
将1mL TPB NCs(1mg/mL)重新分散到9mL去离子水中以获得均匀的TPB NCs溶液,然后将0.25mL柠檬酸钠(40mM)和375μL 1%H2PtCl6水溶液注入上述溶液中搅拌60分钟。在连续搅拌下快速加入0.5mL新鲜制备的冰冷NaBH4溶液(30mM)。最后,溶液颜色变成深棕色,表明PtNPs原位还原到TPB NCs上。离心后,将沉淀物溶解在2mL去离子水中,得到Pt NPs@TPB NCs(0.5mg/mL)溶液供进一步使用。
二、在空气饱和的PBS溶液中Pt NPs@TPB NCs/GCE的CV和ECL响应2. CV and ECL responses of Pt NPs@TPB NCs/GCE in air-saturated PBS solution
当在TPB NCs上原位生成Pt NPs后,在空气饱和的PBS溶液中研究了Pt NPs@TPBNCs/GCE的CV和ECL响应。Pt NPs@TPB NCs于约-0.604V开始出现强阴极还原峰值电流,于1.25V出现强烈的ECL发射(17340a.u.),即Pt NPs@TPB NCs的ECL信号相对于TPB NCs增加了数千倍,这归因于在TPB NCs上引入Pt NPs作为共反应促进剂。为了进一步评估Pt NPs对TPB NCs/溶解O2体系的ECL增强作用,在氮气(N2)饱和的PBS中测量了Pt NPs@TPB NCs/GCE的CV和ECL响应。如图3A的曲线b所示,由于缺乏溶解O2作为共反应试剂,电流强度迅速降低,并伴随着几乎不可见的ECL信号(曲线b,图3B)。随后,超氧化物歧化酶(SOD)和L-半胱氨酸(L-cys)分别被用作超氧化物(O2 ·-)和羟基自由基(OH·)和O2 ·-的有效清除剂,以研究三元ECL体系中多种ROS的ECL增强作用。如图3B所示,Pt NPs@TPB NCs/GCE在含有L-cys的PBS溶液中的ECL信号(曲线c)比在含有SOD的PBS溶液中的相同修饰电极扫描下降得更多(曲线d),这表明OH·和O2 ·-都可以与TPB NCs·+反应生成TPB NCs*,用于Pt NPs@TPB NCs/溶解O2体系的ECL增强。After in situ generation of Pt NPs on TPB NCs, the CV and ECL responses of Pt NPs@TPBNCs/GCE were investigated in air-saturated PBS solution. Pt NPs@TPB NCs began to show a strong cathodic reduction peak current at about -0.604V, and a strong ECL emission (17340a.u.) appeared at 1.25V, that is, the ECL signal of Pt NPs@TPB NCs increased by several thousand relative to TPB NCs times, which was attributed to the introduction of Pt NPs on TPB NCs as co-reaction promoters. To further evaluate the ECL enhancement effect of Pt NPs on TPB NCs/dissolved O 2 system, the CV and ECL responses of Pt NPs@TPB NCs/GCE were measured in nitrogen (N 2 ) saturated PBS. As shown in curve b of Figure 3A, due to the lack of dissolved O2 as a co-reactant, the current intensity decreased rapidly, accompanied by a barely visible ECL signal (curve b, Figure 3B). Subsequently, superoxide dismutase (SOD) and L-cysteine (L-cys) were used as effective sources of superoxide (O 2 ·- ) and hydroxyl radical (OH · ) and O 2 ·- scavengers to study the ECL-enhancing effect of multiple ROS in the ternary ECL system. As shown in Fig. 3B, the ECL signal of Pt NPs@TPB NCs/GCE in PBS solution containing L-cys (curve c) decreased more than that of the same modified electrode scan in PBS solution containing SOD (curve d). , which indicated that both OH · and O 2 ·- could react with TPB NCs ·+ to generate TPB NCs * , which was used for ECL enhancement of Pt NPs@TPB NCs/dissolved O 2 system.
在此,基于上述实验结果,Pt NPs@TPB NCs/溶解O2三元ECL体系的高ECL信号归因于产生了大量ROS以及TPB NCs和ROS之间的快速电子转移,相应机理如下所示。Here, based on the above experimental results, the high ECL signal of the Pt NPs@TPB NCs/dissolved O ternary ECL system is attributed to the generation of a large number of ROS and the fast electron transfer between TPB NCs and ROS, and the corresponding mechanism is shown below.
O2 ·-+H2O2→O2+OH-+OH· [3]O 2 ·- +H 2 O 2 →O 2 +OH - +OH · [3]
TPB NCs-e-→TPB NCs·+ [4]TPB NCs-e - → TPB NCs + [4]
TPB NCs+O2 ·-→TPB NCs·-+O2 [5]TPB NCs+O 2 ·- →TPB NCs ·- +O 2 [5]
TPB NCs·-+OH·→TPB NCs*+OH- [6]TPB NCs ·- +OH →TPB NCs * +OH - [6]
TPB NCs·++TPB NCs·-→TPB NCs*+TPB NCs [7]TPB NCs + +TPB NCs - →TPB NCs * +TPB NCs [7]
TPB NCs*→TPB NCs+hv [8]TPB NCs * →TPB NCs+hv [8]
实施例4:ECL生物传感器的性能Example 4: Performance of ECL biosensors
一、生物传感器的制备:1. Preparation of biosensors:
首先,将5μL Pt NPs@TPB NCs溶液涂在GCE表面上,在37℃的培养箱中干燥。随后,将10μL带有氨基(NH2)的捕获探针(CP DNA,2uM)修饰到GCE上,在4℃下孵育过夜。用去离子水冲洗后,将修饰的GCE滴加10μL己硫醇(HT,5mM)1小时,封闭非特异性位点,得到生物传感器备用。First, 5 μL of Pt NPs@TPB NCs solution was coated on the GCE surface and dried in an incubator at 37 °C. Subsequently, 10 μL of capture probes (CP DNA, 2 uM) with amino groups (NH 2 ) were modified onto the GCE and incubated overnight at 4°C. After rinsing with deionized water, 10 μL of hexanethiol (HT, 5 mM) was added dropwise to the modified GCE for 1 hour to block the non-specific sites to obtain a biosensor for use.
二、目标物诱导的DNA步行器放大:2. Target-induced DNA walker amplification:
将4μM DNA发夹探针(HP)在95℃下退火5分钟,然后缓慢冷却至室温,形成茎环结构。同时,在底物DNA(SD)和二茂铁修饰的DNA探针(P-Fc)的浓度比保持1∶1的情况下,通过加热至85℃10分钟生成4μM DNA双链体结构(SD/P-Fc),然后慢慢冷却至室温。随后,将40μLEDC(1-(3-二甲氨基丙基)-3-乙基碳二亚胺盐酸盐,0.2M)添加到20μL磁珠MB(5mg/mL)中并搅拌30分钟,活化磁珠(MBs)的羧基。随后,将40μL NHS(N-羟基琥珀酰亚胺,0.05M)、50μLHP和50μL SD/P-Fc与上述溶液混合,并在4℃下摇晃过夜,通过酰胺键将上述DNA交联在MBs上组装DNA步行器。磁性分离后,将DNA步行器重新分散在100μL含有不同浓度目标物miRNA-21(100aM-100pM)和100μM Pb2+的反应液中,30℃反应2小时。最后,通过磁分离收集含有S1/P-Fc的上清液作为产物溶液备用。4 μM DNA hairpin probe (HP) was annealed at 95°C for 5 minutes, then slowly cooled to room temperature to form a stem-loop structure. At the same time, with the concentration ratio of substrate DNA (SD) and ferrocene-modified DNA probe (P-Fc) kept at 1:1, a 4 μM DNA duplex structure (SD /P-Fc), and then slowly cooled to room temperature. Subsequently, 40 μL of LEDC (1-(3-dimethylaminopropyl)-3-ethylcarbodiimide hydrochloride, 0.2 M) was added to 20 μL of magnetic beads MB (5 mg/mL) and stirred for 30 minutes to activate Carboxyl groups of magnetic beads (MBs). Subsequently, 40 μL of NHS (N-hydroxysuccinimide, 0.05M), 50 μL of HP, and 50 μL of SD/P-Fc were mixed with the above solution and shaken overnight at 4 °C to cross-link the above DNA on MBs via amide bonds Assemble the DNA walker. After magnetic separation, the DNA walker was redispersed in 100 μL of reaction solution containing different concentrations of target miRNA-21 (100aM-100pM) and 100 μM Pb 2+ , and reacted at 30°C for 2 hours. Finally, the supernatant containing S1/P-Fc was collected by magnetic separation as a product solution for future use.
三、本发明ECL生物传感器的性能Three, the performance of the ECL biosensor of the present invention
将产物溶液在制备的生物传感器上孵育2小时。用PBS洗涤后,在0.1M pH 7.4PBS中测量生物传感器的ECL信号,扫描电位为-1V至1.3V,扫描速率为0.3V/s。放大增益设置为10×。The product solution was incubated on the prepared biosensor for 2 hours. After washing with PBS, the ECL signal of the biosensor was measured in 0.1 M pH 7.4 PBS with a scan potential ranging from −1 V to 1.3 V at a scan rate of 0.3 V/s. The amplification gain is set to 10×.
在最佳实验条件下(HP和SD/P-Fc浓度比1∶2,CP和含有P-Fc的产物溶液之间的孵育时间2小时),在生物传感器上孵育了从100aM到100pM的不同浓度miRNA-21所产生的S1/P-Fc溶液。如图4A所示,ECL响应随着miRNA-21浓度的增加而逐渐降低。此外,ECL强度的变化(ΔIECL=I0-I)与miRNA-21浓度的对数之间存在良好的线性关系(图4B),线性回归方程表示为ΔI=8583.86+2032.52lg c(R=0.998),检测限(LOD)低至83.8aM(S/N=3)。此外,以其他miRNA(miRNA-141、miRNA-199a、miRNA-155)作为干扰,通过比较miRNA-21与干扰物质在相同条件下的ECL信号,研究了该ECL生物传感器的特异性。如图4C所示,尽管干扰物浓度(100pM)比miRNA-21(10pM)高10倍,但与空白对照相比,干扰miRNA在ECL响应上表现出轻微变化。然而,当向上述干扰物中加入目标物miRNA-21,ECL信号明显下降,这与单独孵育miRNA-21得到的ECL信号基本一致。上述结果证明了所提出的ECL生物传感器对目标miRNA-21的突出特异性。此外,为了进一步评估生物传感器的稳定性,连续扫描14个周期(图4D)测量ECL信号,未表现出明显的波动(RSD=1.51%),这表明所提出的生物传感器具有良好的稳定性。Under optimal experimental conditions (HP and SD/P-Fc concentration ratio 1:2, incubation time between CP and P-Fc-containing product solution for 2 h), different Concentration of miRNA-21 produced by S1/P-Fc solution. As shown in Figure 4A, the ECL response gradually decreased with increasing miRNA-21 concentration. In addition, there is a good linear relationship between the change of ECL intensity (ΔI ECL =I 0 -I) and the logarithm of miRNA-21 concentration (Fig. 4B), and the linear regression equation is expressed as ΔI=8583.86+2032.52lg c (R= 0.998), the limit of detection (LOD) was as low as 83.8aM (S/N=3). In addition, using other miRNAs (miRNA-141, miRNA-199a, miRNA-155) as interference, the specificity of this ECL biosensor was investigated by comparing the ECL signal of miRNA-21 with the interfering substances under the same conditions. As shown in Figure 4C, although the interferor concentration (100 pM) was 10-fold higher than that of miRNA-21 (10 pM), the interfering miRNA exhibited a slight change in ECL response compared with the blank control. However, when the target miRNA-21 was added to the above interferents, the ECL signal decreased significantly, which was basically consistent with the ECL signal obtained by incubating miRNA-21 alone. The above results demonstrate the outstanding specificity of the proposed ECL biosensor for the target miRNA-21. In addition, to further evaluate the stability of the biosensor, the ECL signal was measured by continuous scanning for 14 cycles (Fig. 4D), which showed no obvious fluctuation (RSD = 1.51%), which indicated the good stability of the proposed biosensor.
实施例5:癌细胞中miRNA-21的分析Example 5: Analysis of miRNA-21 in cancer cells
首先,通过细胞计数仪将分别取106个宫颈癌细胞(HeLa)和人乳腺癌细胞(MCF-7),用RNA提取试剂盒处理得到细胞裂解液。通过测试在HeLa和MCF-7细胞裂解液中miRNA-21的表达情况研究该方法在癌细胞分析中的实用性。First, 10 6 cervical cancer cells (HeLa) and human breast cancer cells (MCF-7) were collected respectively by a cell counter, and treated with an RNA extraction kit to obtain cell lysates. The practicability of this method in cancer cell analysis was investigated by testing the expression of miRNA-21 in HeLa and MCF-7 cell lysates.
分别将两种细胞裂解液稀释为不同细胞个数(102~106)的样品溶液。将样品溶液代替标准的miRNA-21溶液,进行目标物诱导的DNA步行器放大反应后孵育到生物传感器中,并检测其ECL信号。如图5所示,当HeLa的细胞数量从10个细胞增加到105个细胞,传感器的ECL响应略有下降,这意味着miRNA-21在HeLa细胞中低表达。而在MCF-7细胞中,随着细胞个数从10个增加到105个,ECL信号明显降低,表明miRNA-21在MCF-7细胞中高表达,这与文献报道的研究结果非常一致。上述结果表明,本发明所提出的方法在监测癌细胞miRNA生物标志物表达方面具有很大的可行性。The two cell lysates were diluted to sample solutions with different cell numbers (10 2 -10 6 ). The sample solution was replaced with the standard miRNA-21 solution, and after the target-induced DNA walker amplification reaction, it was incubated into the biosensor, and its ECL signal was detected. As shown in Fig. 5, when the number of HeLa cells increased from 10 cells to 105 cells, the ECL response of the sensor decreased slightly, which meant that miRNA-21 was underexpressed in HeLa cells. In MCF-7 cells, as the number of cells increased from 10 to 10 5 , the ECL signal decreased significantly, indicating that miRNA-21 was highly expressed in MCF-7 cells, which was very consistent with the research results reported in the literature. The above results show that the method proposed in the present invention has great feasibility in monitoring the expression of miRNA biomarkers in cancer cells.
本发明在TPB NCs上原位还原的Pt NPs不仅为O2提供了大量的活性位点、以原位产生ROS与TPB NCs反应获得强ECL发射作为“信号增强”状态,而且还通过Pt-N键用于固定捕获探针(CP DNA),以进一步杂交二茂铁标记的产物DNA(P-Fc)。随后,在均相中进行目标物诱导的DNA步行器放大过程。如图1C所示,将发夹(HP)、底物DNA(SD)和标记有二茂铁的DNA链(P-Fc)按比例组装在磁珠(MBs)上,以获得DNA步行器。在目标物miRNA-21存在的情况下,MBs上的HP可以与miRNA-21杂交,形成部分双链体结构,其中单链部分作为DNA摆臂。目标物诱导的DNA步行器在Pb2+DNA酶的辅助下开始运作。并且,SD DNA被含有酶链DNA序列的DNA摆臂特异性识别,并被Pb2+DNA酶切割,释放DNA摆臂参与另一个剪切过程,同时产生大量的S1/P-Fc。磁分离后,将含有S1/P-Fc的产物溶液孵育到生物传感器上,通过P-Fc与CP DNA的杂交作用将P-Fc捕获到电极表面,由于二茂铁的强猝灭作用,呈现降低的ECL信号,将其作为“信号猝灭”的状态。值得注意的是,基于Pt NPs@TPB NCs中共反应加速和结晶诱导增强ECL发射的协同效应以及目标物诱导的DNA步行器放大策略,本发明开发了一个超灵敏的ECL生物传感平台,能实现miRNA-21的超灵敏检测,检测范围为100aM到100pM,检测限为83.8aM。因此,该方法在生物学分析和临床诊断中显示出巨大的潜力。The present in situ reduced Pt NPs on TPB NCs not only provide a large number of active sites for O2 to in situ generate ROS to react with TPB NCs to obtain strong ECL emission as a "signal enhancement" state, but also through the Pt-N The bond is used to immobilize the capture probe (CP DNA) for further hybridization of the ferrocene-labeled product DNA (P-Fc). Subsequently, the target-induced DNA walker amplification process is performed in homogeneous phase. As shown in Figure 1C, hairpins (HP), substrate DNA (SD), and ferrocene-labeled DNA strands (P-Fc) were assembled on magnetic beads (MBs) in scale to obtain DNA walkers. In the presence of target miRNA-21, HP on MBs can hybridize with miRNA-21 to form a partial duplex structure, in which the single-stranded part acts as a DNA swing arm. The target-induced DNA walker is assisted by Pb 2+ DNase. Moreover, SD DNA is specifically recognized by the DNA swing arm containing the DNA sequence of the enzyme chain, and is cut by Pb 2+ DNase, releasing the DNA swing arm to participate in another cutting process and producing a large amount of S1/P-Fc at the same time. After magnetic separation, the product solution containing S1/P-Fc was incubated on the biosensor, and P-Fc was captured to the electrode surface through the hybridization of P-Fc and CP DNA. Due to the strong quenching effect of ferrocene, the Reduced ECL signal, referred to as the "signal quenched" state. Notably, based on the synergistic effect of Pt NPs@TPB NCs co-reaction acceleration and crystallization-induced enhancement of ECL emission and target-induced DNA walker amplification strategy, the present invention developed an ultrasensitive ECL biosensing platform capable of realizing Ultrasensitive detection of miRNA-21 with a detection range of 100aM to 100pM and a detection limit of 83.8aM. Therefore, this method shows great potential in biological analysis and clinical diagnosis.
最后说明的是,以上优选实施例仅用以说明本发明的技术方案而非限制,尽管通过上述优选实施例已经对本发明进行了详细的描述,但本领域技术人员应当理解,可以在形式上和细节上对其作出各种各样的改变,而不偏离本发明权利要求书所限定的范围。Finally, it should be noted that the above preferred embodiments are only used to illustrate the technical solutions of the present invention and not to limit them. Although the present invention has been described in detail through the above preferred embodiments, those skilled in the art should understand that it can be described in terms of form and Various changes may be made in the details without departing from the scope of the invention defined by the claims.
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