CN110819697B - Detection method of uranyl ions - Google Patents
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Abstract
Description
技术领域technical field
本发明涉及铀酰离子的检测领域,特别是基于DNA镊子探针和DNA酶催化裂解的一步法扩增检测铀酰离子方法领域。The invention relates to the field of detection of uranyl ions, in particular to the field of a method for one-step amplification and detection of uranyl ions based on DNA tweezers probes and DNase catalyzed cleavage.
背景技术Background technique
浓缩铀可以用作核能燃料和核武器材料。全球范围内的铀消费可能导致铀矿开采和核废料将其释放到环境中,从而导致严重的环境污染和人类健康问题。铀可以通过食物链富集到人体中,这可能导致严重的儿童白血病,肺癌和其他与辐射有关的疾病。因此,美国环境保护署(EPA)设定了水中铀酰离子的最大污染水平(130nM)。Enriched uranium can be used as nuclear energy fuel and nuclear weapons material. The worldwide consumption of uranium may lead to the release of uranium mining and nuclear waste into the environment, which can lead to serious environmental pollution and human health problems. Uranium can be enriched into the human body through the food chain, which can lead to severe childhood leukemia, lung cancer, and other radiation-related diseases. Therefore, the U.S. Environmental Protection Agency (EPA) has set a maximum contamination level (130nM) for uranyl ions in water.
到目前为止,已经开发了许多用于铀检测的技术,包括电感耦合等离子体质谱法和原子发射光谱法等。但是,他们需要昂贵的仪器和复杂的操作。最近,结合酶链(E-DNA)和底物链(S-DNA)的DNA酶被用于设计金属离子的生物传感器,例如铀酰离子,Mg2+,Cu2+,Pb2+,Zn2+和Cd2+。已经报道了多种基于DNA酶的铀酰离子检测方法,包括比色法,荧光法和电化学法等。此外,基于DNA酶的探针已用于在活细胞中对铀酰离子进行荧光成像。So far, many techniques have been developed for uranium detection, including inductively coupled plasma mass spectrometry and atomic emission spectrometry, among others. However, they require expensive instruments and complicated operations. Recently, DNA enzymes that combine enzyme strands (E-DNA) and substrate strands (S-DNA) have been used to design biosensors for metal ions such as uranyl ions, Mg2+, Cu2+, Pb2+, Zn2+, and Cd2+. A variety of DNase-based methods for the detection of uranyl ions have been reported, including colorimetric, fluorescent, and electrochemical methods. In addition, DNase-based probes have been used for fluorescent imaging of uranyl ions in living cells.
DNA纳米机是一种可以在纳米级实现纳米机械运动的DNA组装纳米结构。DNA纳米机是由通用材料“DNA”进行编程和构建的,它具有一些独特的优点,例如易于化学合成,良好的热稳定性和功能修饰。而且,DNA纳米机器是具有生物纳米设计,药物输送和具有一维,二维和三维纳米结构的逻辑分子计算的有前途的平台。已经设计出了具有纳米级可控性和生物相容性的严肃的DNA纳米机械,例如DNA镊子,DNA Walker,DNA电机,DNA齿轮和DNA纳米笼。DNA镊子是典型的纳米机器,可以对不同的外部刺激做出反应,包括核酸,金属离子,蛋白质,酶和pH值。到目前为止,尚无DNA镊子与DNA酶结合用于金属离子检测。A DNA nanomachine is a DNA-assembled nanostructure that can realize nanomechanical motion at the nanoscale. DNA nanomachines are programmed and constructed from the universal material "DNA", which has some unique advantages such as easy chemical synthesis, good thermal stability and functional modification. Moreover, DNA nanomachines are promising platforms for bionanodesign, drug delivery, and logical molecular computing with one-, two-, and three-dimensional nanostructures. Serious DNA nanomachines with nanoscale controllability and biocompatibility have been designed, such as DNA tweezers, DNA walkers, DNA motors, DNA gears, and DNA nanocages. DNA tweezers are typical nanomachines that can respond to different external stimuli, including nucleic acids, metal ions, proteins, enzymes, and pH. So far, there is no DNA tweezers combined with DNase for metal ion detection.
发明内容Contents of the invention
为解决上述问题,本发明提供一种基于基于DNA镊子探针和DNA酶催化裂解的一步法扩增检测铀酰离子方法。In order to solve the above problems, the present invention provides a method for the detection of uranyl ions based on one-step amplification based on DNA tweezers probe and DNase-catalyzed cleavage.
本发明包括如下步骤:The present invention comprises the steps:
一种溶液中铀酰离子浓度的检测方法,包括如下步骤:A method for detecting the concentration of uranyl ions in a solution, comprising the steps of:
(1)制备金纳米粒子;(1) preparing gold nanoparticles;
(2)用所述金纳米粒子修饰的DNA序列4,DNA序列4一端硫醇化,另一端连接荧光基团;(2) the
(3)用步骤(2)所得修饰金纳米粒子后的DNA序列4制备DNA镊子探针;(3) prepare DNA tweezers probes with the
(4)将步骤(3)所得DNA镊子探针、适量铀酰离子特异性DNA酶链、待测铀酰离子样品溶液混合;(4) mixing the DNA tweezers probe obtained in step (3), an appropriate amount of uranyl ion-specific DNA enzyme chain, and the uranyl ion sample solution to be measured;
(5)检测步骤(4)所得溶液的荧光信号,并利用标准曲线得出试样溶液中铀酰离子的浓度。(5) detecting the fluorescence signal of the solution obtained in step (4), and using the standard curve to obtain the concentration of uranyl ions in the sample solution.
其中,所述DNA序列4具体为:HS-TACCCAAAAAACCT GGCTGCAACTCACTATrAGGAAGAGATGGACGTGACATACGGTACAAAAACCCTA-FAM。Wherein, the
其中,步骤(3)中与DNA序列4一起制备DNA镊子探针的还有DNA序列1-3,其中DNA序列1为:TAGGCTTCGTAAGGTCCACATACATACATACACCAGCGAGAATGTTCCGT,DNA序列2为:TAGGGTTTTTGTACCGTACCGACGGAACATTCTCGCTGG,DNA序列3为:TGGACCTTACGAAGCCTAACTAGCCAGGTTTTTTGGGTA。Wherein, DNA sequence 1-3 is prepared together with
优选的,所铀酰离子特异性DNA酶链具体为:CACGTCCATCTCTGCAGTCGGGTAGTTAAACCGACCTTCAGACATAGTGAGT。Preferably, the uranyl ion-specific DNA enzyme chain is: CACGTCCATCTCTGCAGTCGGGTAGTTAAACCGACCTTCAGACATAGTGAGT.
优选的,步骤(2)具体为:将硫醇化的DNA序列4与金纳米粒子以1:1的摩尔比混合12小时,得到金纳米粒子修饰的DNA序列4。Preferably, the step (2) specifically includes: mixing the thiolated
优选的,步骤(3)具体为:通过在100mM MES缓冲溶液(pH 5.5)和300mM NaCl中混合100nM的DNA序列1-4,然后将混合物加热至95℃,并缓慢冷却以形成DNA镊子探针。Preferably, step (3) is specifically: by mixing 100 nM DNA sequences 1-4 in 100 mM MES buffer solution (pH 5.5) and 300 mM NaCl, then heating the mixture to 95° C., and cooling slowly to form DNA tweezer probes .
优选的,步骤(4)具体为:将30nM铀酰离子特异性DNA酶链和待测铀酰离子溶液与DNA镊子在含300mM NaCl的10mM MES缓冲溶液(pH 5.5)中混合,然后在40℃下孵育60分钟。Preferably, step (4) is specifically: mix 30nM uranyl ion-specific DNA enzyme chain and uranyl ion solution to be tested with DNA tweezers in 10mM MES buffer solution (pH 5.5) containing 300mM NaCl, and then mix at 40°C Incubate for 60 minutes.
优选的,步骤(5)中荧光信号为492nm激发下500nm至600nm测量的荧光信号。Preferably, the fluorescence signal in step (5) is the fluorescence signal measured at 500nm to 600nm under excitation at 492nm.
本发明构建了一个基于DNA酶的一步扩增催化DNA镊子,用于铀酰离子的灵敏荧光检测。DNA镊子是通过DNA序列的杂交形成的。荧光团和金纳米颗粒(金纳米粒子)分别固定在DNA镊子的两个臂的末端。DNA镊子的两条臂通过单链DNA紧密连接,从而导致荧光信号淬灭。然后,在铀酰离子特异性DNA酶链和铀酰的存在下,接头序列被铀酰离子特异性DNA酶链切割,导致荧光强度的恢复。DNA酶可以循环切割其他DNA镊子,以显着提高灵敏度。The present invention constructs a DNase-based one-step amplification catalytic DNA tweezers for sensitive fluorescence detection of uranyl ions. DNA tweezers are formed by the hybridization of DNA sequences. Fluorophores and gold nanoparticles (AuNPs) were immobilized at the ends of the two arms of the DNA tweezers, respectively. The two arms of the DNA tweezers are tightly connected by single-stranded DNA, which leads to the quenching of the fluorescent signal. Then, the linker sequence is cleaved by the uranyl ion-specific DNase strand in the presence of uranyl ion-specific DNase strand and uranyl, resulting in restoration of fluorescence intensity. DNase can circularly cleave other DNA tweezers to dramatically increase sensitivity.
本发明创造性地将DNA镊子与DNA酶结合用于金属离子检测,提高了灵敏度,还使得检测过程容易操作,成本降低。The invention creatively combines DNA tweezers and DNA enzymes for metal ion detection, which improves the sensitivity, makes the detection process easy to operate, and reduces the cost.
附图说明Description of drawings
图1为本发明的原理图。Fig. 1 is a schematic diagram of the present invention.
图2为改变检测条件后的荧光信号强度图。Fig. 2 is a graph of fluorescence signal intensity after changing detection conditions.
图3(A)DNA镊子对不同浓度的铀酰离子的荧光光谱:0.1nM,5nM,10nM,30nM,60nM,100nM,150nM,200nM。(B)荧光强度与铀酰离子浓度之间的关系。插图:荧光强度和铀酰离子在0.1nM至60nM之间的校准图。Fig. 3 (A) Fluorescence spectra of DNA tweezers for different concentrations of uranyl ions: 0.1nM, 5nM, 10nM, 30nM, 60nM, 100nM, 150nM, 200nM. (B) The relationship between fluorescence intensity and uranyl ion concentration. Inset: calibration plot of fluorescence intensity and uranyl ion between 0.1 nM and 60 nM.
图4为含相同浓度(60nM)的铀酰离子、Ca2+,Mg2+,Pb2+,Sn2+,Hg2+,Zn2+,Cu2+和Co2+的溶液所产生的荧光信号强度图。Fig. 4 is a graph of fluorescence signal intensity generated by solutions containing uranyl ions, Ca2+, Mg2+, Pb2+, Sn2+, Hg2+, Zn2+, Cu2+ and Co2+ at the same concentration (60nM).
具体实施方式Detailed ways
下面结合实施方式对本发明作进一步详细的说明。The present invention will be described in further detail below in conjunction with the embodiments.
如图1所示,本发明的原理为:DNA镊子结构与序列1-4组合在一起。序列2和3分别与序列1的末端区域部分互补。它们可以分别与序列1的末端杂交形成DNA镊子的两个臂。然后,在两端用FAM和金纳米粒子修饰的序列4可以分别与序列2和3的单一部分杂交,形成一个完整的DNA镊子结构。序列4的中间部分紧密连接DNA镊子的两个臂,从而导致严重的荧光猝灭。连接区具有与铀酰特异性DNA酶的底物链相同的序列。它可以与铀酰离子特异性DNA酶链杂交形成铀酰离子特异性DNA酶。可以在铀酰离子存在的情况下切割连接区域,从而分离出FAM和金纳米粒子。然后,铀酰离子特异性DNA酶链可以与其他DNA镊子重新结合以形成另一个DNA酶结构,然后催化裂解DNA镊子的连接部分,因此,荧光信号被显著恢复。铀酰的浓度可以通过荧光强度定量检测。As shown in Fig. 1, the principle of the present invention is: the DNA tweezers structure is combined with sequences 1-4.
下列实验验证了本发明检测方法的可行性:将最佳检测过程的检测结果和改变最佳检测过程的部分条件后的检测结果进行对比,证明本方法的可行性。所述最佳检测过程为:制备金纳米粒子;用所述金纳米粒子修饰的DNA序列4(HS-TACCCAAAAAACCTGGCTGCAACTCACTATrAGGAAGAGATGGACGTGACATACGGTACAAAAACCCTA-FAM),DNA序列4一端硫醇化,另一端连接荧光基团;用所得修饰金纳米粒子后的DNA序列4制备DNA镊子探针;将所得100nM DNA镊子探针、30nM铀酰离子特异性DNA酶链(CACGTCCATCTCTGCAGTCGGGTAGTTAAACCGACCTTCAGACATAGTGAGT)、待测铀酰离子样品溶液混合,然后在40℃下孵育60分钟;测量所得溶液的荧光信号(图2中样品6的信号)。样品1为空白溶液,即,待测液中不含有铀酰离子,其余过程同最佳检测过程,在没有铀酰离子的情况下,DNA镊子仍处于“关闭”状态,因此,可获得弱荧光信号(图2中样品1的信号)。样品2为没有铀酰离子特异性DNA酶链的样品,其余过程同最佳检测过程(图2中样品2的信号),具有与样品1相似的荧光强度,表明没有铀酰离子特异性DNA酶链不能形成铀酰离子特异性DNA酶,并且序列4的接头仍然完整。样品3为将最佳检测过程中的铀酰离子特异性DNA酶链替换成Pb2+特异性DNA酶链:CATCTCTTCTCCGAGCCGGTCGAAATAGTGAGT,其余过程同最佳检测过程(图2中样品3的信号)。样品3的低荧光强度原因在于Pb2+特异性DNA酶链不能与序列4形成铀酰离子特异性DNA酶,导致遇铀酰离子时镊子不能打开。样品4为半反应时间,即,与待测铀酰离子样品溶液混合后在40℃下孵育30分钟,其余过程同最佳检测过程(图2中样品4的信号),荧光强度被显着恢复。这是因为裂解反应在一半的反应时间内已经进行到一定程度,部分镊子已经打开。样品5为铀酰离子特异性DNA酶链与DNA镊子的摩尔比变为2:10,其余过程同最佳检测过程(图2中样品5的信号),由于DNA酶裂解反应不完整,而DNA酶量较少,导致荧光强度降低。The following experiments have verified the feasibility of the detection method of the present invention: the detection results of the optimal detection process are compared with those after changing some conditions of the optimal detection process to prove the feasibility of the method. The optimal detection process is: preparing gold nanoparticles; using the
为了确定铀酰离子的荧光响应,用形成的DNA镊子探针测试了不同浓度的铀酰离子。如图3A所示,荧光信号随着铀酰离子在0.1nM至200nM的范围内逐渐升高。在荧光强度和铀酰浓度之间的0.1nM至60nM范围内,可获得良好的线性关系,相关系数为0.993(图3B)。根据3σ空白标准,该敏感DNA镊子的检出限评估为25pM。这种检测限与其他报道的基于DNA酶的方法(包括荧光,比色法和电化学方法)相当。六次重复测量的0.1nM铀酰离子的RSD为8.8%,表明该DNA镊子探针具有令人满意的重现性。To determine the fluorescence response of uranyl ions, different concentrations of uranyl ions were tested with the formed DNA tweezer probes. As shown in Figure 3A, the fluorescence signal gradually increased with uranyl ions ranging from 0.1 nM to 200 nM. In the range of 0.1 nM to 60 nM between fluorescence intensity and uranyl concentration, a good linear relationship was obtained with a correlation coefficient of 0.993 (Fig. 3B). Based on the 3σ blank standard, the detection limit of this sensitive DNA tweezers was estimated to be 25pM. This detection limit is comparable to other reported DNase-based methods, including fluorometric, colorimetric, and electrochemical methods. The RSD of 0.1 nM uranyl ion for six repeated measurements was 8.8%, indicating that the DNA tweezer probe has a satisfactory reproducibility.
特异性方面,将上述最佳检测过程中“含铀酰离子的样品溶液”改变为含相同浓度(60nM)的Ca2+,Mg2+,Pb2+,Sn2+,Hg2+,Zn2+,Cu2+和Co2+的溶液,其余检测过程同所述最佳检测过程,所得荧光信号可忽略不计(参见图4)。可见,其他金属离子的荧光强度远低于铀酰离子。同时实验证明,即使上述干扰离子浓度是铀酰离子的100倍,其产生的干扰也可以忽略不计。该方法的良好选择性可归因于铀酰离子特异性DNA酶链的强特异性。In terms of specificity, change the "sample solution containing uranyl ions" in the above optimal detection process to a solution containing the same concentration (60nM) of Ca2+, Mg2+, Pb2+, Sn2+, Hg2+, Zn2+, Cu2+ and Co2+, and the rest of the detection process With the optimal detection procedure described, the resulting fluorescent signal was negligible (see Figure 4). It can be seen that the fluorescence intensity of other metal ions is much lower than that of uranyl ions. At the same time, experiments have proved that even if the concentration of the above-mentioned interfering ions is 100 times that of uranyl ions, the interference produced by them can be ignored. The good selectivity of this method can be attributed to the strong specificity of the uranyl ion-specific DNase chain.
检测实际样品中的铀酰离子:Detection of uranyl ions in real samples:
通过不同的水样(饮用水,自来水和河水)评估了该方法检测铀酰离子的可行性和适用性。通过离心纯化水样并用0.22μm膜过滤。将上述样品的pH调节至5.5。然后根据所述最佳检测过程检测样品。用这种方法测定的自来水水样中的铀酰浓度为2.9nM,河水中为4.7nM。加标样品测定的回收率在91.0%至107.0%之间。另外,RSD从5.6%到9.2%。结果表明,该DNA镊子是可行的,可用于实际水分析。The feasibility and applicability of this method for the detection of uranyl ions were evaluated by different water samples (drinking water, tap water and river water). Water samples were purified by centrifugation and filtered through a 0.22 μm membrane. The pH of the above sample was adjusted to 5.5. Samples are then tested according to the optimal testing procedure described. The concentration of uranyl in tap water samples determined by this method was 2.9nM, and in river water was 4.7nM. The recoveries determined for the spiked samples ranged from 91.0% to 107.0%. Plus, the RSD ranged from 5.6% to 9.2%. The results show that the DNA tweezers are feasible and can be used for practical water analysis.
以上所述仅为本申请的优选实施例而已,并不用于限制本申请,对于本领域的技术人员来说,本申请可以有各种更改和变化。凡在本申请的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本申请的保护范围之内。The above descriptions are only preferred embodiments of the present application, and are not intended to limit the present application. For those skilled in the art, there may be various modifications and changes in the present application. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of this application shall be included within the protection scope of this application.
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Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102288568A (en) * | 2011-07-29 | 2011-12-21 | 广西师范大学 | Method for rapidly measuring nanogold catalysis-silver nitrate reduction luminosity of UO2<2+> in water |
CN104774915A (en) * | 2014-01-14 | 2015-07-15 | 东华理工大学 | Catalytic light mark and preparation method thereof, and method for determination of trace uranium by catalytic light mark |
CN104964942A (en) * | 2015-07-01 | 2015-10-07 | 福州大学 | Visualization method for rapidly detecting trace amount of uranyl ions in water environment |
CN105241945A (en) * | 2015-09-30 | 2016-01-13 | 中国工程物理研究院材料研究所 | Sensor for detecting uranyl ions, and making method and application thereof |
CN106841130A (en) * | 2016-12-28 | 2017-06-13 | 成都理工大学 | A kind of method of uranyl ion content in unmarked fluoroscopic examination water sample |
CN107828417A (en) * | 2017-11-15 | 2018-03-23 | 华北电力大学 | A kind of binary channels fluorescence uranyl ion probe and its application |
CN108700535A (en) * | 2015-12-23 | 2018-10-23 | 加利福尼亚大学董事会 | Nanosensors for nucleic acid detection and identification |
CN109929823A (en) * | 2018-11-30 | 2019-06-25 | 清华大学 | 39E DNA enzymatic and its application |
CN109946279A (en) * | 2019-03-29 | 2019-06-28 | 重庆工商大学 | A kind of detection method of uranyl ion |
CN110106226A (en) * | 2019-06-04 | 2019-08-09 | 中国工程物理研究院化工材料研究所 | Bio-sensing chip of recyclable detection trace uranyl ion and preparation method thereof, application method |
-
2019
- 2019-11-27 CN CN201911180266.8A patent/CN110819697B/en not_active Expired - Fee Related
Patent Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102288568A (en) * | 2011-07-29 | 2011-12-21 | 广西师范大学 | Method for rapidly measuring nanogold catalysis-silver nitrate reduction luminosity of UO2<2+> in water |
CN104774915A (en) * | 2014-01-14 | 2015-07-15 | 东华理工大学 | Catalytic light mark and preparation method thereof, and method for determination of trace uranium by catalytic light mark |
CN104964942A (en) * | 2015-07-01 | 2015-10-07 | 福州大学 | Visualization method for rapidly detecting trace amount of uranyl ions in water environment |
CN105241945A (en) * | 2015-09-30 | 2016-01-13 | 中国工程物理研究院材料研究所 | Sensor for detecting uranyl ions, and making method and application thereof |
CN108700535A (en) * | 2015-12-23 | 2018-10-23 | 加利福尼亚大学董事会 | Nanosensors for nucleic acid detection and identification |
CN106841130A (en) * | 2016-12-28 | 2017-06-13 | 成都理工大学 | A kind of method of uranyl ion content in unmarked fluoroscopic examination water sample |
CN107828417A (en) * | 2017-11-15 | 2018-03-23 | 华北电力大学 | A kind of binary channels fluorescence uranyl ion probe and its application |
CN109929823A (en) * | 2018-11-30 | 2019-06-25 | 清华大学 | 39E DNA enzymatic and its application |
CN109946279A (en) * | 2019-03-29 | 2019-06-28 | 重庆工商大学 | A kind of detection method of uranyl ion |
CN110106226A (en) * | 2019-06-04 | 2019-08-09 | 中国工程物理研究院化工材料研究所 | Bio-sensing chip of recyclable detection trace uranyl ion and preparation method thereof, application method |
Non-Patent Citations (3)
Title |
---|
A turn-off fluorescent biosensor for the rapid and sensitive detection of uranyl ion based on molybdenum disulfide nanosheets and specific DNAzyme;HongYan Zhang et al.;《Spectrochimica Acta Part A: Molecular and Biomolecular Spectroscopy》;20151231;第1-6页 * |
DNA-based machines;Moritz K. Beissenhirtz and Itamar Willner;《Organic & Biomolecular Chemistry》;20061231;第3394页右栏第1-2段,图4 * |
基于DNA酶的铀酰离子传感方法;姜交来等;《核化学与放射化学》;20180430;第89-97页 * |
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