CN105572107A - Method for detecting acetamiprid in waste water by chemiluminiscence - Google Patents
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- 239000005875 Acetamiprid Substances 0.000 title claims abstract description 64
- WCXDHFDTOYPNIE-RIYZIHGNSA-N (E)-acetamiprid Chemical compound N#C/N=C(\C)N(C)CC1=CC=C(Cl)N=C1 WCXDHFDTOYPNIE-RIYZIHGNSA-N 0.000 title claims abstract description 62
- 238000000034 method Methods 0.000 title claims abstract description 29
- 239000002351 wastewater Substances 0.000 title claims abstract description 21
- 108091023037 Aptamer Proteins 0.000 claims abstract description 26
- SQGYOTSLMSWVJD-UHFFFAOYSA-N silver nitrate Substances [Ag+].[O-]N(=O)=O SQGYOTSLMSWVJD-UHFFFAOYSA-N 0.000 claims abstract description 26
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 claims abstract description 24
- 229910001961 silver nitrate Inorganic materials 0.000 claims abstract description 18
- 239000003153 chemical reaction reagent Substances 0.000 claims description 12
- 238000004020 luminiscence type Methods 0.000 claims description 8
- HWYHZTIRURJOHG-UHFFFAOYSA-N luminol Chemical compound O=C1NNC(=O)C2=C1C(N)=CC=C2 HWYHZTIRURJOHG-UHFFFAOYSA-N 0.000 claims description 8
- 229910000033 sodium borohydride Inorganic materials 0.000 claims description 4
- 239000012279 sodium borohydride Substances 0.000 claims description 4
- 239000001509 sodium citrate Substances 0.000 claims description 4
- 239000003381 stabilizer Substances 0.000 claims description 4
- NLJMYIDDQXHKNR-UHFFFAOYSA-K sodium citrate Chemical compound O.O.[Na+].[Na+].[Na+].[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O NLJMYIDDQXHKNR-UHFFFAOYSA-K 0.000 claims description 3
- 239000002245 particle Substances 0.000 claims description 2
- 238000002038 chemiluminescence detection Methods 0.000 claims 6
- 239000000126 substance Substances 0.000 claims 3
- 238000005259 measurement Methods 0.000 claims 1
- 238000004458 analytical method Methods 0.000 abstract description 20
- 238000001514 detection method Methods 0.000 abstract description 16
- 229910052709 silver Inorganic materials 0.000 abstract description 10
- 239000004332 silver Substances 0.000 abstract description 10
- 230000008859 change Effects 0.000 abstract description 7
- 230000003993 interaction Effects 0.000 abstract description 4
- 230000035945 sensitivity Effects 0.000 abstract description 4
- 230000003197 catalytic effect Effects 0.000 abstract description 3
- 230000009467 reduction Effects 0.000 abstract description 3
- 238000002347 injection Methods 0.000 abstract description 2
- 239000007924 injection Substances 0.000 abstract description 2
- 230000003068 static effect Effects 0.000 abstract description 2
- 239000000243 solution Substances 0.000 description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 230000006872 improvement Effects 0.000 description 5
- 238000002474 experimental method Methods 0.000 description 4
- IZUPBVBPLAPZRR-UHFFFAOYSA-N pentachlorophenol Chemical compound OC1=C(Cl)C(Cl)=C(Cl)C(Cl)=C1Cl IZUPBVBPLAPZRR-UHFFFAOYSA-N 0.000 description 4
- 230000004044 response Effects 0.000 description 4
- 239000011550 stock solution Substances 0.000 description 4
- 108091028043 Nucleic acid sequence Proteins 0.000 description 3
- 239000008367 deionised water Substances 0.000 description 3
- 229910021641 deionized water Inorganic materials 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 239000013582 standard series solution Substances 0.000 description 3
- 239000005944 Chlorpyrifos Substances 0.000 description 2
- 238000002965 ELISA Methods 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- SBPBAQFWLVIOKP-UHFFFAOYSA-N chlorpyrifos Chemical compound CCOP(=S)(OCC)OC1=NC(Cl)=C(Cl)C=C1Cl SBPBAQFWLVIOKP-UHFFFAOYSA-N 0.000 description 2
- 238000004737 colorimetric analysis Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000001506 fluorescence spectroscopy Methods 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 238000004949 mass spectrometry Methods 0.000 description 2
- 239000011259 mixed solution Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- LCCNCVORNKJIRZ-UHFFFAOYSA-N parathion Chemical compound CCOP(=S)(OCC)OC1=CC=C([N+]([O-])=O)C=C1 LCCNCVORNKJIRZ-UHFFFAOYSA-N 0.000 description 2
- 239000000575 pesticide Substances 0.000 description 2
- 238000002360 preparation method Methods 0.000 description 2
- 239000012086 standard solution Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000012224 working solution Substances 0.000 description 2
- QKNYBSVHEMOAJP-UHFFFAOYSA-N 2-amino-2-(hydroxymethyl)propane-1,3-diol;hydron;chloride Chemical compound Cl.OCC(N)(CO)CO QKNYBSVHEMOAJP-UHFFFAOYSA-N 0.000 description 1
- 108020004414 DNA Proteins 0.000 description 1
- 102000053602 DNA Human genes 0.000 description 1
- 239000005906 Imidacloprid Substances 0.000 description 1
- 208000012902 Nervous system disease Diseases 0.000 description 1
- 208000025966 Neurological disease Diseases 0.000 description 1
- 108020004682 Single-Stranded DNA Proteins 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- QZPSXPBJTPJTSZ-UHFFFAOYSA-N aqua regia Chemical compound Cl.O[N+]([O-])=O QZPSXPBJTPJTSZ-UHFFFAOYSA-N 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 239000007853 buffer solution Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000002848 electrochemical method Methods 0.000 description 1
- 230000005518 electrochemistry Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000004401 flow injection analysis Methods 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 238000004128 high performance liquid chromatography Methods 0.000 description 1
- YWTYJOPNNQFBPC-UHFFFAOYSA-N imidacloprid Chemical compound [O-][N+](=O)\N=C1/NCCN1CC1=CC=C(Cl)N=C1 YWTYJOPNNQFBPC-UHFFFAOYSA-N 0.000 description 1
- 229940056881 imidacloprid Drugs 0.000 description 1
- 239000002917 insecticide Substances 0.000 description 1
- 238000004895 liquid chromatography mass spectrometry Methods 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 108091008104 nucleic acid aptamers Proteins 0.000 description 1
- 108020004707 nucleic acids Proteins 0.000 description 1
- 102000039446 nucleic acids Human genes 0.000 description 1
- 150000007523 nucleic acids Chemical group 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 239000000447 pesticide residue Substances 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000010206 sensitivity analysis Methods 0.000 description 1
- -1 silver ions Chemical class 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- HRXKRNGNAMMEHJ-UHFFFAOYSA-K trisodium citrate Chemical compound [Na+].[Na+].[Na+].[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O HRXKRNGNAMMEHJ-UHFFFAOYSA-K 0.000 description 1
- 229940038773 trisodium citrate Drugs 0.000 description 1
- 238000000870 ultraviolet spectroscopy Methods 0.000 description 1
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- 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
- G01N21/75—Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
- G01N21/76—Chemiluminescence; Bioluminescence
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Abstract
本发明公开了一种化学发光检测废水中啶虫脒的方法,用鲁米诺-硝酸银-纳米银化学发光分析体系,利用啶虫脒适配体和啶虫脒的相互作用,适配体构型的改变诱导纳米银形态的改变,从而导致纳米银催化性能的降低。采用静态注射的方式,实现化学发光分析检测废水中的啶虫脒。本发明所用仪器廉价,对技术人员几乎无要求;使用纳米银催化的鲁米诺-硝酸银化学发光分析体系,该体系稳定,使得本方法重现性好,RSD在2.9%~4.2%之间,灵敏度高,检出限达到2.0×10–9g/L。
The invention discloses a method for detecting acetamiprid in wastewater by chemiluminescence, which uses a luminol-silver nitrate-nanometer silver chemiluminescence analysis system, utilizes the interaction between acetamiprid aptamers and acetamiprid, aptamers The configuration change induces the change of nano-silver morphology, which leads to the reduction of the catalytic performance of nano-silver. The method of static injection is used to realize the detection of acetamiprid in wastewater by chemiluminescence analysis. The instruments used in the present invention are cheap and have almost no requirements for technicians; the luminol-silver nitrate chemiluminescent analysis system catalyzed by nano-silver is used, and the system is stable, so that the method has good reproducibility, and the RSD is between 2.9% and 4.2%. , high sensitivity, and the detection limit reaches 2.0×10 –9 g/L.
Description
技术领域technical field
本发明属于有机农药检测领域,尤其涉及一种化学发光检测废水中啶虫脒的方法。The invention belongs to the field of organic pesticide detection, in particular to a method for detecting acetamiprid in waste water by chemiluminescence.
背景技术Background technique
一直以来,农药残余对于环境所造成的污染备受关注。啶虫脒,又名乙虫脒、吡虫清,是继吡虫啉之后一种新型广谱性烟碱类杀虫剂,因其高效、低毒、内吸性强、用量少、残效期长、残留量低等特性,应用非常广泛,在市场上占有很高的份额。啶虫脒能够引起人类神经紊乱而中毒,因此,排放废水中啶虫脒残留和累积必定威胁着人们的健康。For a long time, the pollution caused by pesticide residues to the environment has attracted much attention. Acetamiprid, also known as ethiamiprid and acetamiprid, is a new type of broad-spectrum neonicotinoid insecticide after imidacloprid. , low residue and other characteristics, it is widely used and occupies a high share in the market. Acetamiprid can cause neurological disorders and poisoning in humans. Therefore, the residue and accumulation of acetamiprid in discharged wastewater must threaten people's health.
目前啶虫脒残留的检测方法主要有高效液相色谱法,气相色谱法,质谱法,液相色谱-质谱联用,电化学,比色法、荧光光谱法以及酶联免疫分析等方法。这些方法普遍存在样品前处理烦琐,费用高,上机检测时间比较长,工作效率低,使用有机溶剂量较多或基体本身的复杂性影响分析的准确度等不足;质谱联用技术由于仪器昂贵,因此得不到很好的普及;而酶联免疫分析方法很容易受干扰而稳定性差。比色法和荧光光谱法存在灵敏度低的问题,电化学方法无法解决异相操作的问题而难以自动化。因此,发展灵敏、快速且实用性强的分析检测啶虫脒的方法对于环境监测及人们的健康很有现实意义。At present, the detection methods of acetamiprid residue mainly include high performance liquid chromatography, gas chromatography, mass spectrometry, liquid chromatography-mass spectrometry, electrochemistry, colorimetry, fluorescence spectroscopy and enzyme-linked immunoassay. These methods generally have the disadvantages of cumbersome sample pretreatment, high cost, long detection time on the machine, low work efficiency, large amount of organic solvent used or the complexity of the matrix itself affecting the accuracy of the analysis; mass spectrometry is expensive due to the , so it is not well popularized; and the enzyme-linked immunoassay method is easily disturbed and has poor stability. Colorimetry and fluorescence spectroscopy have the problem of low sensitivity, and electrochemical methods cannot solve the problem of heterogeneous operation and are difficult to automate. Therefore, the development of a sensitive, rapid and practical method for the analysis and detection of acetamiprid is of great practical significance for environmental monitoring and people's health.
化学发光分析法具有灵敏度高、仪器简单、分析快速、易实现自动化等优点,但是使用化学发光分析检测啶虫脒的研究未见报道。纳米银能够催化鲁米诺与硝酸银的化学发光反应,而鲁米诺-硝酸银-纳米银化学发光分析体系是个稳定且灵敏性好的分析体系。本发明利用鲁米诺-硝酸银-纳米银化学发光分析体系,利用啶虫脒适配体和啶虫脒的相互作用,适配体构型的改变诱导纳米银形态的改变,从而导致纳米银催化性能的降低。采用静态注射的方式,实现化学发光分析检测废水中的啶虫脒。适配体对于目标物识别的高特异性使得本方法具有高度的选择性。Chemiluminescence analysis has the advantages of high sensitivity, simple instrument, rapid analysis, and easy automation. However, there is no report on the detection of acetamiprid using chemiluminescence analysis. Nano-silver can catalyze the chemiluminescence reaction between luminol and silver nitrate, and the luminol-silver nitrate-nano-silver chemiluminescence analysis system is a stable and sensitive analysis system. The present invention utilizes the luminol-silver nitrate-nanometer silver chemiluminescence analysis system, utilizes the interaction between the acetamiprid aptamer and acetamiprid, and the change of the configuration of the aptamer induces the change of the shape of the nano-silver, thereby leading to the change of the nano-silver reduction in catalytic performance. The method of static injection is used to realize the detection of acetamiprid in wastewater by chemiluminescence analysis. The high specificity of aptamers for target recognition makes this method highly selective.
发明内容Contents of the invention
为解决现有测定啶虫脒的技术中存在的问题,本发明提供一种化学发光检测废水中啶虫脒的方法。In order to solve the problems existing in the existing technology for measuring acetamiprid, the invention provides a method for detecting acetamiprid in wastewater by chemiluminescence.
本发明是通过以下技术方案实现的:The present invention is achieved through the following technical solutions:
一种化学发光检测废水中啶虫脒的方法,包括以下步骤:A method for chemiluminescent detection of acetamiprid in wastewater, comprising the following steps:
将啶虫脒适配体与含啶虫脒的废水相互作用,加入纳米银溶液,而后将作用后的纳米银-适配体-啶虫脒溶液移入化学发光池中,注入鲁米诺-硝酸银化学发光试剂,进行发光反应,同时检测化学发光的信号。啶虫脒与其适配体作用后,适配体由单链DNA转变为特定的构象,啶虫脒适配体的构象改变诱导纳米银形态的改变,从而导致纳米银对鲁米诺-硝酸银的化学发光反应的催化活性的降低;对发光反应的强度进行定量测定,即可得到废水中啶虫脒的浓度。Interact the acetamiprid aptamer with the wastewater containing acetamiprid, add the nano-silver solution, and then move the effected nano-silver-aptamer-acetamiprid solution into the chemiluminescence pool, inject luminol-nitric acid The silver chemiluminescence reagent is used for luminescence reaction and detection of chemiluminescence signal at the same time. After the interaction between acetamiprid and its aptamer, the aptamer changes from single-stranded DNA to a specific conformation, and the conformational change of acetamiprid aptamer induces a change in the shape of nano-silver, which leads to the effect of nano-silver on luminol-silver nitrate. The reduction of the catalytic activity of the chemiluminescence reaction; the concentration of acetamiprid in the wastewater can be obtained by quantitatively measuring the intensity of the luminescence reaction.
进一步的改进,所述纳米银溶液中的纳米银粒径为15nm,浓度为3.2×10-10mol/L。As a further improvement, the nano-silver particle size in the nano-silver solution is 15nm, and the concentration is 3.2×10 -10 mol/L.
进一步的改进,适配体的浓度为6×10-6mol/L,适配体与啶虫脒的作用时间为10分钟。As a further improvement, the concentration of the aptamer is 6×10 -6 mol/L, and the interaction time between the aptamer and acetamiprid is 10 minutes.
进一步的改进,所述纳米银溶液采用如下方法制得:将25mL浓度为1×10-3mol/L的硝酸银溶液逐滴加入到高速搅拌的75mL浓度为2×10-3mol/L的硼氢化钠溶液中,反应10分钟,加入5mL质量分数为1%柠檬酸钠溶液作为稳定剂。As a further improvement, the nano-silver solution is prepared by the following method: 25 mL of silver nitrate solution with a concentration of 1×10 -3 mol/L is added dropwise to 75 mL of silver nitrate solution with a concentration of 2×10 -3 mol/L In the sodium borohydride solution, react for 10 minutes, and add 5 mL of 1% sodium citrate solution as a stabilizer.
进一步的改进,所述鲁米诺–硝酸银化学发光试剂是由5×10-5mol/L的鲁米诺溶液和1.0×10-4mol/L的硝酸银溶液以1:1体积比混合得到。As a further improvement, the luminol-silver nitrate chemiluminescent reagent is mixed with 5×10 -5 mol/L luminol solution and 1.0×10 -4 mol/L silver nitrate solution at a volume ratio of 1:1 get.
进一步的改进,所述鲁米诺-硝酸银化学发光试剂的pH值为12.0。As a further improvement, the pH value of the luminol-silver nitrate chemiluminescence reagent is 12.0.
与现有技术相比,本发明具有以下优点:Compared with the prior art, the present invention has the following advantages:
(1)采用化学发光分析技术,所用仪器廉价,对技术人员几乎无要求;(2)使用纳米银催化的鲁米诺-硝酸银化学发光分析体系,该体系稳定,使得本方法重现性好,RSD在2.9%~4.2%之间,灵敏度高,检出限达到2.0×10–9g/L;(3)核酸适配体对于目标物识别的高特异性,使得本方法选择性好;(4)整个实验操作温和,且均在液相体系中进行,易于操作,有利于自动化的分析操作;(5)实验操作简便快速,分析测试时间缩短为30分钟以内。本发明所建立的方法无疑填补了化学发光分析检测啶虫脒研究领域的空白。(1) The chemiluminescence analysis technology is adopted, the instruments used are cheap, and there is almost no requirement for technicians; (2) The luminol-silver nitrate chemiluminescence analysis system catalyzed by nano-silver is used, and the system is stable, which makes the method reproducible. , the RSD is between 2.9% and 4.2%, the sensitivity is high, and the detection limit reaches 2.0×10 –9 g/L; (3) The high specificity of the nucleic acid aptamer for target recognition makes the method selective; (4) The whole experiment operation is mild, and it is all carried out in a liquid phase system, which is easy to operate and is conducive to automatic analysis operation; (5) The experiment operation is simple and fast, and the analysis and test time is shortened to less than 30 minutes. The method established by the present invention undoubtedly fills the gap in the research field of chemiluminescence analysis and detection of acetamiprid.
附图说明Description of drawings
图1为鲁米诺-硝酸银-纳米银化学发光信号的响应图,其中a为适配体的发光信号,b为啶虫脒+适配体的发光信号;Fig. 1 is the response graph of luminol-silver nitrate-nanometer silver chemiluminescent signal, wherein a is the luminescence signal of aptamer, b is the luminescence signal of acetamiprid+aptamer;
图2为化学发光分析检测啶虫脒的灵敏度分析。Fig. 2 is the sensitivity analysis of detection of acetamiprid by chemiluminescence analysis.
具体实施案例Specific implementation cases
所用到的主要仪器设备和试剂:The main equipment and reagents used:
啶虫脒适配体是能与啶虫脒选择性结合的核酸,购自于上海生工生物科技有限公司,啶虫脒购自阿拉丁化学试剂有限公司。实验用水为二次去离子水。硝酸银购自上海化学试剂公司。使用的污水样品取自福州大学城污水处理厂的废水,分别将废水样用中速滤纸过滤后,用二次去离子水稀释定容于100mL容量瓶。IFFL-D流动注射化学发光分析仪及其配套设备(西安瑞迈分析仪器有限公司),TU-1901型紫外-可见分光光度仪(北京普析通用仪器有限公司),透射电子显微镜(日立公司,规格型号:H-600)。The acetamiprid aptamer is a nucleic acid capable of selectively binding to acetamiprid, which was purchased from Shanghai Sangon Biotechnology Co., Ltd., and acetamiprid was purchased from Aladdin Chemical Reagent Co., Ltd. The experimental water was secondary deionized water. Silver nitrate was purchased from Shanghai Chemical Reagent Company. The sewage samples used were taken from the sewage treatment plant in Fuzhou University City. After filtering the waste water samples with medium-speed filter paper, they were diluted with secondary deionized water and fixed in a 100mL volumetric flask. IFFL-D flow injection chemiluminescence analyzer and its supporting equipment (Xi'an Ruimai Analytical Instrument Co., Ltd.), TU-1901 ultraviolet-visible spectrophotometer (Beijing General Instrument Co., Ltd.), transmission electron microscope (Hitachi, Specification model: H-600).
啶虫脒适配体用Tris-HCl缓冲溶液(pH7.5)溶解制备于冰箱冷冻储藏,使用前需于高温80℃加热5分钟而后冷却至常温待用。使用二次水溶解啶虫脒制得标准溶液,再使用标准溶液稀释出啶虫脒标准系列溶液。The acetamiprid aptamer was prepared by dissolving in Tris-HCl buffer solution (pH 7.5) and stored in the refrigerator. Before use, it should be heated at a high temperature of 80°C for 5 minutes and then cooled to room temperature for use. Use secondary water to dissolve acetamiprid to prepare a standard solution, and then use the standard solution to dilute acetamiprid standard series solutions.
纳米银的制备:采用硼氢化钠还原银离子,柠檬酸三钠作为稳定剂。制备过程中所用的玻璃器皿均使用王水浸泡清洗(1:3HNO3–HCl),然后用二次去离子水彻底冲洗干净,烘干备用。将25mL的1×10-3mol/L的硝酸银溶液逐滴加入到高速搅拌的75mL的2×10-3mol/L硼氢化钠溶液中,反应10分钟后,加入5mL质量分数为1%柠檬酸钠溶液作为稳定剂,继续搅拌10分钟,停止搅拌。将得到的纳米银溶胶放于棕色试剂瓶中,4℃冰箱中保存,熟化两天后待用。Preparation of nano-silver: sodium borohydride was used to reduce silver ions, and trisodium citrate was used as a stabilizer. The glassware used in the preparation process was soaked and cleaned with aqua regia (1:3HNO 3 -HCl), then thoroughly rinsed with secondary deionized water, and dried for later use. Add 25mL of 1×10 -3 mol/L silver nitrate solution dropwise into 75mL of 2×10 -3 mol/L sodium borohydride solution stirred at high speed, react for 10 minutes, add 5mL of 1% Sodium citrate solution was used as a stabilizer, and the stirring was continued for 10 minutes, and the stirring was stopped. Put the obtained nano-silver sol in a brown reagent bottle, store it in a refrigerator at 4°C, and ripen it for two days before use.
将4.43g鲁米诺固体粉末溶解在20mL0.10Mmol/L溶液中并稀释至1L,制备得到2.5×10–2mol/L鲁米诺储备溶液。使用之前避光保存一星期以确保试剂性质的稳定。鲁米诺的工作溶液通过储备溶液的稀释而得到。硝酸银用二次水溶解制备储备液,工作溶液通过稀释储备液而得。鲁米诺–硝酸银试剂是由5×10-5mol/L的鲁米诺溶液和1.0×10-4mol/L的硝酸银溶液以1:1体积比混合得到,其pH值为12.0。Dissolve 4.43g of luminol solid powder in 20mL of 0.10Mmol/L solution and dilute to 1L to prepare a 2.5×10 -2 mol/L luminol stock solution. Store in the dark for one week before use to ensure the stability of the reagent. Working solutions of luminol were obtained by dilution of stock solutions. Silver nitrate was dissolved in secondary water to prepare a stock solution, and the working solution was obtained by diluting the stock solution. The luminol-silver nitrate reagent is obtained by mixing 5×10 -5 mol/L luminol solution and 1.0×10 -4 mol/L silver nitrate solution at a volume ratio of 1:1, and its pH value is 12.0.
测定:将200μL啶虫脒标准系列溶液和待测样品分别与200μL啶虫脒适配体溶液混合,啶虫脒适配体溶液浓度为6×10-6mol/L,作用10分钟;加入纳米银溶液后,作用5分钟;而后加入50μL浓度为0.5mol/L的NaCl溶液,混匀后得到混合溶液;移取100μL混合溶液至化学发光池中,并注入200μL鲁米诺–硝酸银试剂,通过IFFL-D化学发光分析仪检测并记录发光信号,根据发光强度和啶虫脒溶液的浓度,制作标准曲线,再依据标准曲线计算待测样品中啶虫脒的浓度。代表的化学发光信号响应如图1所示。Determination: Mix 200 μL acetamiprid standard series solution and the sample to be tested with 200 μL acetamiprid aptamer solution respectively, the concentration of acetamiprid aptamer solution is 6×10 -6 mol/L, act for 10 minutes; add nano After the silver solution, react for 5 minutes; then add 50 μL of NaCl solution with a concentration of 0.5 mol/L, and mix to obtain a mixed solution; pipette 100 μL of the mixed solution into the chemiluminescent cell, and inject 200 μL of luminol-silver nitrate reagent, The luminescence signal was detected and recorded by the IFFL-D chemiluminescence analyzer, and a standard curve was prepared according to the luminescence intensity and the concentration of the acetamiprid solution, and then the concentration of acetamiprid in the sample to be tested was calculated according to the standard curve. Representative chemiluminescent signal responses are shown in Figure 1.
实验所用啶虫脒标准系列溶液浓度为:1.5×10-7、6.5×10-7、1.5×10-6、6.5×10-6、1.5×10-5、5.8×10-5g/L。实验结果表明,在优化的实验条件下,随着啶虫脒浓度的增加,化学发光信号逐渐降低。发现化学发光强度与啶虫脒浓度的对数值成线性相关性。根据测得的化学发光强度,绘制标准曲线。如图2所示,其检出限为2.0×10–9g/L(S/N=3)。并对6.5×10-6g/L的啶虫脒平行测定6次,其相对标准偏差为2.6%。实验结果表明该方法检出限低,精密度好,且操作简便。The concentrations of acetamiprid standard series solutions used in the experiment were: 1.5×10 -7 , 6.5×10 -7 , 1.5×10 -6 , 6.5×10 -6 , 1.5×10 -5 , 5.8×10 -5 g/L. The experimental results showed that under the optimized experimental conditions, the chemiluminescence signal gradually decreased with the increase of the concentration of acetamiprid. A linear correlation was found between the chemiluminescent intensity and the logarithm of the acetamiprid concentration. According to the measured chemiluminescence intensity, draw a standard curve. As shown in Figure 2, the detection limit is 2.0×10 –9 g/L (S/N=3). And 6.5×10 -6 g/L acetamiprid was measured in parallel for 6 times, and the relative standard deviation was 2.6%. The experimental results show that the method has low detection limit, good precision and easy operation.
同时测定污水样品,结果列于表1。实验结果表明,本发明所建立的方法具有较好的准确度和精密度,回收率分别为94.5%~106.13%,RSD在2.9%~4.2%之间,分析时间短,不需使用大型仪器,可用于废水中啶虫脒的快速检测。At the same time, the sewage samples were measured, and the results are listed in Table 1. Experimental results show that the method established by the present invention has better accuracy and precision, the recoveries are respectively 94.5%-106.13%, the RSD is between 2.9%-4.2%, the analysis time is short, no need to use large instruments, It can be used for rapid detection of acetamiprid in wastewater.
表1废水中啶虫脒测定的结果The result of determination of acetamiprid in the waste water of table 1
本方法的选择性分析:Selectivity analysis of this method:
以毒死蝉、对硫磷和五氯苯酚三种共存农药为代表,考察方法对啶虫脒测定的选择性。实验中考查了适配体/啶虫脒、适配体(无啶虫脒)、适配体/毒死蝉、适配体/对硫磷、适配体/五氯苯酚和任意DNA序列/啶虫脒对化学发光信号的响应。实验中,适配体和任意DNA序列作为识别DNA序列,其浓度均为6×10-6mol/L。其它对照农药浓度和啶虫脒浓度相同,均为1.5×10-5g/L,其余实验条件相同。实验结果发现,相比于其它几个化学发光的响应,适配体-啶虫脒显示出一个显著淬灭的化学发光信号。结果表明:本方法具有很好的选择性。Taking chlorpyrifos, parathion and pentachlorophenol as representatives, the selectivity of the method for the determination of acetamiprid was investigated. Aptamer/acetamiprid, aptamer (no acetamiprid), aptamer/chlorpyrifos, aptamer/parathion, aptamer/pentachlorophenol and arbitrary DNA sequence/ Acetamiprid response to chemiluminescence signal. In the experiment, the aptamer and any DNA sequence were used as the recognition DNA sequence, and the concentration was 6×10 -6 mol/L. The concentration of other control pesticides was the same as that of acetamiprid, both were 1.5×10 -5 g/L, and the rest of the experimental conditions were the same. The experimental results found that the aptamer-acetamiprid showed a significantly quenched chemiluminescent signal compared to several other chemiluminescent responses. The results show that this method has good selectivity.
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