CN110118769A - A kind of gold nanoparticle and preparation method thereof for detecting heavy metal ion - Google Patents
A kind of gold nanoparticle and preparation method thereof for detecting heavy metal ion Download PDFInfo
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- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 title claims abstract description 62
- 239000010931 gold Substances 0.000 title claims abstract description 62
- 229910052737 gold Inorganic materials 0.000 title claims abstract description 62
- 239000002105 nanoparticle Substances 0.000 title claims abstract description 62
- 229910001385 heavy metal Inorganic materials 0.000 title claims abstract description 36
- 238000002360 preparation method Methods 0.000 title claims abstract description 8
- 150000002500 ions Chemical class 0.000 claims abstract description 103
- 238000001514 detection method Methods 0.000 claims abstract description 50
- 238000010521 absorption reaction Methods 0.000 claims abstract description 30
- 238000000034 method Methods 0.000 claims abstract description 8
- 239000000243 solution Substances 0.000 claims description 118
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 45
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical compound CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 claims description 24
- 239000008399 tap water Substances 0.000 claims description 20
- 235000020679 tap water Nutrition 0.000 claims description 20
- 229910052500 inorganic mineral Inorganic materials 0.000 claims description 19
- 239000011707 mineral Substances 0.000 claims description 19
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 18
- 238000006243 chemical reaction Methods 0.000 claims description 15
- DKIDEFUBRARXTE-UHFFFAOYSA-N 3-mercaptopropanoic acid Chemical compound OC(=O)CCS DKIDEFUBRARXTE-UHFFFAOYSA-N 0.000 claims description 14
- PZXYILUXRGTFGD-UHFFFAOYSA-N 2,5,8,11,14,17-hexaoxabicyclo[16.4.0]docosa-1(18),19,21-trien-20-amine Chemical compound O1CCOCCOCCOCCOCCOC2=CC(N)=CC=C21 PZXYILUXRGTFGD-UHFFFAOYSA-N 0.000 claims description 10
- 239000012086 standard solution Substances 0.000 claims description 10
- 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 9
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- 238000000862 absorption spectrum Methods 0.000 claims description 4
- 238000002198 surface plasmon resonance spectroscopy Methods 0.000 claims description 4
- 239000000126 substance Substances 0.000 claims description 2
- WDSPXPVKEVYDEH-UHFFFAOYSA-N ethanol;3-sulfanylpropanoic acid Chemical compound CCO.OC(=O)CCS WDSPXPVKEVYDEH-UHFFFAOYSA-N 0.000 claims 1
- 230000008859 change Effects 0.000 abstract description 30
- 238000005054 agglomeration Methods 0.000 abstract description 6
- 230000002776 aggregation Effects 0.000 abstract description 6
- 238000005516 engineering process Methods 0.000 abstract description 4
- 229910052739 hydrogen Inorganic materials 0.000 abstract description 4
- 239000001257 hydrogen Substances 0.000 abstract description 4
- 150000002894 organic compounds Chemical class 0.000 abstract description 4
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 abstract description 3
- 125000003277 amino group Chemical group 0.000 abstract description 2
- 230000000694 effects Effects 0.000 abstract description 2
- 230000007246 mechanism Effects 0.000 abstract description 2
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 abstract 3
- 239000011259 mixed solution Substances 0.000 description 56
- 239000000203 mixture Substances 0.000 description 11
- 239000003086 colorant Substances 0.000 description 9
- 229910001422 barium ion Inorganic materials 0.000 description 4
- 239000008367 deionised water Substances 0.000 description 4
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- 241000282414 Homo sapiens Species 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 3
- RVPVRDXYQKGNMQ-UHFFFAOYSA-N lead(2+) Chemical compound [Pb+2] RVPVRDXYQKGNMQ-UHFFFAOYSA-N 0.000 description 3
- 229910021645 metal ion Inorganic materials 0.000 description 3
- 230000035945 sensitivity Effects 0.000 description 3
- XEZNGIUYQVAUSS-UHFFFAOYSA-N 18-crown-6 Chemical compound C1COCCOCCOCCOCCOCCO1 XEZNGIUYQVAUSS-UHFFFAOYSA-N 0.000 description 2
- FAXDZWQIWUSWJH-UHFFFAOYSA-N 3-methoxypropan-1-amine Chemical compound COCCCN FAXDZWQIWUSWJH-UHFFFAOYSA-N 0.000 description 2
- 238000002835 absorbance Methods 0.000 description 2
- 238000003968 anodic stripping voltammetry Methods 0.000 description 2
- 229910052788 barium Inorganic materials 0.000 description 2
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 2
- IWOUKMZUPDVPGQ-UHFFFAOYSA-N barium nitrate Chemical compound [Ba+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O IWOUKMZUPDVPGQ-UHFFFAOYSA-N 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- WLZRMCYVCSSEQC-UHFFFAOYSA-N cadmium(2+) Chemical compound [Cd+2] WLZRMCYVCSSEQC-UHFFFAOYSA-N 0.000 description 2
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- 238000011161 development Methods 0.000 description 2
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 2
- 150000002343 gold Chemical class 0.000 description 2
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- 239000002245 particle Substances 0.000 description 2
- 125000001997 phenyl group Chemical group [H]C1=C([H])C([H])=C(*)C([H])=C1[H] 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- KRKNYBCHXYNGOX-UHFFFAOYSA-K Citrate Chemical compound [O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O KRKNYBCHXYNGOX-UHFFFAOYSA-K 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- 241000282412 Homo Species 0.000 description 1
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- 235000021168 barbecue Nutrition 0.000 description 1
- 159000000009 barium salts Chemical class 0.000 description 1
- CJDPJFRMHVXWPT-UHFFFAOYSA-N barium sulfide Chemical compound [S-2].[Ba+2] CJDPJFRMHVXWPT-UHFFFAOYSA-N 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- XIEPJMXMMWZAAV-UHFFFAOYSA-N cadmium nitrate Inorganic materials [Cd+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XIEPJMXMMWZAAV-UHFFFAOYSA-N 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
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- 201000010099 disease Diseases 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
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- 238000001095 inductively coupled plasma mass spectrometry Methods 0.000 description 1
- 238000002354 inductively-coupled plasma atomic emission spectroscopy Methods 0.000 description 1
- 239000003112 inhibitor Substances 0.000 description 1
- RLJMLMKIBZAXJO-UHFFFAOYSA-N lead nitrate Chemical compound [O-][N+](=O)O[Pb]O[N+]([O-])=O RLJMLMKIBZAXJO-UHFFFAOYSA-N 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
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- NMHMNPHRMNGLLB-UHFFFAOYSA-N phloretic acid Chemical compound OC(=O)CCC1=CC=C(O)C=C1 NMHMNPHRMNGLLB-UHFFFAOYSA-N 0.000 description 1
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- 102000004169 proteins and genes Human genes 0.000 description 1
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- G01N21/17—Systems in which incident light is modified in accordance with the properties of the material investigated
- G01N21/25—Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
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Abstract
本发明公开了一种用于检测重金属离子的金纳米粒子及其制备方法,该技术方法基于团聚机理,利用有机化合物上的氨基和或羧基能够形成强的氢键作用或通过有机化合物上的苯环形成强的π‑π堆积作用,从而引起金纳米粒子团聚,使得溶液颜色发生变化,引起金纳米粒子表面等离子共振吸收峰的峰位以及吸收强度发生变化,直接利用肉眼和紫外可见吸收峰的峰位以及强度发生的变化,即可快速地检测样品中是否含有Cd2+、Ba2+、Pb2+离子及其浓度大小,实现对样品中Cd2+、Ba2+、Pb2+离子的快速检测。该技术具有操作简单、成本低、适用范围广等优点。
The invention discloses a gold nanoparticle for detecting heavy metal ions and a preparation method thereof. The technical method is based on agglomeration mechanism, using amino groups and/or carboxyl groups on organic compounds to form strong hydrogen bonds or through benzene on organic compounds. The ring forms a strong π-π stacking effect, which causes the agglomeration of gold nanoparticles, changes the color of the solution, and changes the peak position and absorption intensity of the plasmon resonance absorption peak on the surface of the gold nanoparticles. The change of peak position and intensity can quickly detect whether the sample contains Cd 2+ , Ba 2+ , Pb 2+ ions and their concentrations, and realize the detection of Cd 2+ , Ba 2+ , Pb 2+ ions in the sample. rapid detection. The technology has the advantages of simple operation, low cost and wide application range.
Description
技术领域technical field
本发明属于纳米材料和离子检测领域,具体涉及一种用于检测Cd2+、Ba2+、Pb2+重金属离子的金纳米粒子及其制备方法。The invention belongs to the field of nanomaterials and ion detection, in particular to a gold nanoparticle used for detecting heavy metal ions of Cd 2+ , Ba 2+ and Pb 2+ and a preparation method thereof.
背景技术Background technique
随着工业和社会的急速发展,土壤、大气以及水体等生态环境受到重金属离子污染的严重威胁,引起了广大环保人士的关注。重金属污染与有机物或生物污染不同,其污染很难消除,并且可通过自然界生物的富集作用在生物体内积累,进入人体后可与蛋白质和酶产生一定的作用,使器官失活,导致慢性中毒或者引起人体内的疾病以及神经系统和内分泌系统的紊乱,因此,重金属污染对生物体的健康构成严重的潜在危害。With the rapid development of industry and society, the ecological environment such as soil, atmosphere and water body is seriously threatened by heavy metal ion pollution, which has attracted the attention of the majority of environmentalists. Heavy metal pollution is different from organic or biological pollution. Its pollution is difficult to eliminate, and it can accumulate in organisms through the enrichment of natural organisms. After entering the human body, it can interact with proteins and enzymes to inactivate organs and cause chronic poisoning. Or cause diseases in the human body and disorders of the nervous system and endocrine system. Therefore, heavy metal pollution poses a serious potential harm to the health of organisms.
钡是重金属,普遍用于各种工业过程,如电镀,玻璃工业,石油工业,新兴颜料业和腐蚀抑制剂等,其化合物也用于油漆,陶瓷和橡胶等。迄今为止,水污染中的Ba2+离子仍然是最常见的。Ba2+离子污染土壤和水资源,尤其是钡盐水溶性化合物和酸溶性化合物具有较高的毒性(例如,硫化钡)。水中高浓度的Ba2+离子能够以可溶性状态,通过植物进行积累并转移到其它动物身上。Barium is a heavy metal that is commonly used in various industrial processes, such as electroplating, glass industry, petroleum industry, emerging pigment industry and corrosion inhibitor, etc. Its compounds are also used in paints, ceramics and rubber, etc. Ba 2+ ions are still the most common in water pollution to date. Ba 2+ ions pollute soil and water resources, especially barium salt water-soluble compounds and acid-soluble compounds have high toxicity (eg, barium sulfide). High concentrations of Ba 2+ ions in water can accumulate in plants and transfer to other animals in a soluble state.
在重金属中,铅离子Pb2+和镉离子Cd2+的使用也非常普遍,如烧烤食品,油漆,汽油,化妆品等。Cd2+和Pb2+因其环境污染,对人类产生的危害而受到社会的高度关注。如今,湖泊,河流和自来水被认为是为人类和生态系统提供淡水的天然水库。因此,监测饮用水中重金属离子的污染,以及快速检测识别重金属离子污染,并最大限度地降低污染风险成为必然选择。传统的传感技术,如AAS、ICP-AES和ICP-MS,具有灵敏,灵活的特点,但复杂,昂贵,并且需要使用大型仪器设备,不适合实时检测。为了解决这些问题,人们成功开发了电化学检测方法,用于识别部分重金属离子,例如,阳极溶出伏安法(ASV),其具有高灵敏度、易操作和低成本等特点,是一种用于检测重金属离子的强大工具。但是,ASV现场检测需要传感系统,需要少量的小型仪器设备才能完成有效的检测。Among the heavy metals, the use of lead ion Pb 2+ and cadmium ion Cd 2+ is also very common, such as barbecue food, paint, gasoline, cosmetics, etc. Cd 2+ and Pb 2+ are highly concerned by society because of their environmental pollution and harm to human beings. Today, lakes, rivers and tap water are considered natural reservoirs that provide fresh water to humans and ecosystems. Therefore, monitoring the pollution of heavy metal ions in drinking water, as well as rapid detection and identification of heavy metal ion pollution, and minimizing the risk of pollution have become inevitable choices. Traditional sensing techniques, such as AAS, ICP-AES, and ICP-MS, are sensitive and flexible, but complex, expensive, and require the use of large-scale instruments, which are not suitable for real-time detection. In order to solve these problems, electrochemical detection methods have been successfully developed for the identification of some heavy metal ions, such as anodic stripping voltammetry (ASV), which has the characteristics of high sensitivity, easy operation and low cost. A powerful tool for the detection of heavy metal ions. However, ASV on-site detection requires a sensing system and requires a small number of small instruments to complete effective detection.
目前为止,重金属离子检测方法已经得到迅速发展,但是不同的检测体系其检测方法各不相同,并且应用的技术于不同,包含火焰原子吸收光谱法,光纤传感器和电化学方法。泰国Kasetsart大学的Kanokwan Chaichana开发了部分重金属检测办法,该检测方法具有灵敏度高等特点,但其样品制备复杂并且耗时费力等。近年来,纳米技术突飞猛进的发展,使其在重金属离子检测方面也有系统而深入的研究,并取得一定成果。本发明通过合成一种氨基苯并-18冠-6衍生物,然后用该衍生物和3-巯基丙酸共同修饰金纳米粒子,利用修饰后的金纳米粒子与Cd2+、Ba2+、Pb2+重金属离子的特定作用,引起金纳米粒子的颜色和紫外吸收光谱的变化,实现对Cd2+、Ba2+、Pb2+重金属离子的快速检测。So far, heavy metal ion detection methods have been developed rapidly, but different detection systems have different detection methods and applied technologies, including flame atomic absorption spectrometry, optical fiber sensors and electrochemical methods. Kanokwan Chaichana of Kasetsart University in Thailand developed some heavy metal detection methods. This detection method has the characteristics of high sensitivity, but its sample preparation is complicated and time-consuming. In recent years, the rapid development of nanotechnology has made systematic and in-depth research on the detection of heavy metal ions, and achieved certain results. In the present invention, a kind of aminobenzo-18 crown-6 derivative is synthesized, and then the derivative and 3-mercaptopropionic acid are used to co-modify gold nanoparticles, and the modified gold nanoparticles are combined with Cd 2+ , Ba 2+ , The specific action of Pb 2+ heavy metal ions causes changes in the color and ultraviolet absorption spectrum of gold nanoparticles, and realizes the rapid detection of Cd 2+ , Ba 2+ , and Pb 2+ heavy metal ions.
发明内容SUMMARY OF THE INVENTION
本发明要解决的技术问题是针对现有技术存在的不足,提供一种稳定性好、操作步骤简单、能够快速、准确检测出水溶液中Cd2+、Ba2+、Pb2+重金属离子的方法。The technical problem to be solved by the present invention is to aim at the deficiencies of the prior art, and to provide a method with good stability, simple operation steps, and capable of rapidly and accurately detecting Cd 2+ , Ba 2+ , and Pb 2+ heavy metal ions in an aqueous solution .
本发明解决上述技术问题所采取的技术方案为:一种用于检测重金属离子的金纳米粒子的制备方法,采用柠檬酸钠、4'-氨基-苯并-18-冠醚-6和3-巯基丙酸分别作为还原剂、修饰剂和稳定剂,将三价的金还原成零价的金,并制成稳定的、颗粒均匀的金纳米粒子(图1);将所制备的金纳米粒子的水溶液分别加到含一定浓度的Cd2+、Ba2+、Pb2+重金属离子的溶液中,溶液颜色从红色变成灰色或灰黑色。4'-氨基-苯并-18-冠醚-6和3-巯基丙酸作为修饰剂与金纳米粒子作用,金纳米粒子具有丰富多样的氢键作用,通过其氨基-NH2或羧基-COOH形成强的氢键作用或通过苯环形成强的π-π堆积作用,从而引起金纳米粒子团聚,使得溶液颜色发生变化,实现对溶液中Cd2+、Ba2+、Pb2+重金属离子的裸眼快速检测;通过金纳米粒子的团聚引起金纳米粒子表面等离子共振吸收峰的峰位以及强度发生变化,实现对溶液中Cd2+、Ba2+、Pb2+重金属离子的定量检测。The technical scheme adopted by the present invention to solve the above technical problems is as follows: a method for preparing gold nanoparticles for detecting heavy metal ions, using sodium citrate, 4'-amino-benzo-18-crown-6 and 3- As reducing agent, modifier and stabilizer, mercaptopropionic acid can reduce trivalent gold to zero-valent gold, and make stable and uniform gold nanoparticles (Figure 1). The aqueous solution was added to the solution containing a certain concentration of Cd 2+ , Ba 2+ , Pb 2+ heavy metal ions, and the color of the solution changed from red to gray or gray-black. 4'-Amino-benzo-18-crown-6 and 3-mercaptopropionic acid act as modifiers to interact with gold nanoparticles, which have rich and diverse hydrogen bonding through their amino- NH2 or carboxyl-COOH The formation of strong hydrogen bonds or the formation of strong π-π stacking through the benzene ring will cause the agglomeration of gold nanoparticles, which will change the color of the solution, and realize the elimination of Cd 2+ , Ba 2+ , Pb 2+ heavy metal ions in the solution. Rapid detection with naked eyes; the agglomeration of gold nanoparticles causes changes in the peak position and intensity of the surface plasmon resonance absorption peaks of gold nanoparticles to achieve quantitative detection of Cd 2+ , Ba 2+ , and Pb 2+ heavy metal ions in solution.
4'-氨基-苯并-18-冠醚-6和3-巯基丙酸的结构如下图所示:The structures of 4'-amino-benzo-18-crown-6 and 3-mercaptopropionic acid are shown in the figure below:
4'-氨基-苯并-18-冠醚-6的结构简图和3-巯基丙酸结构简图Schematic structure of 4'-amino-benzo-18-crown-6 and 3-mercaptopropionic acid
本发明提供的一种金纳米粒子的制备方法,具体包括如下步骤:The preparation method of a gold nanoparticle provided by the present invention specifically comprises the following steps:
在圆底烧瓶中加入一定浓度的氯金酸水溶液,搅拌加热至沸腾,快速加入柠檬酸钠的水溶液,反应5~15分钟,加入4'-氨基-苯并-18-冠醚-6的DMF溶液和3-巯基丙酸的乙醇溶液,得反应混合物溶液,反应混合物溶液的pH值用HCl调为10~13,溶液颜色由浅黄色变为红色,静置冷却至室温,制得金纳米粒子,放入0~4℃的冰箱中保存备用;Add a certain concentration of chloroauric acid aqueous solution to the round-bottomed flask, stir and heat to boiling, quickly add sodium citrate aqueous solution, react for 5 to 15 minutes, add DMF of 4'-amino-benzo-18-crown-6 solution and ethanol solution of 3-mercaptopropionic acid to obtain a reaction mixture solution, the pH value of the reaction mixture solution is adjusted to 10-13 with HCl, the color of the solution changes from light yellow to red, and it is left to cool to room temperature to obtain gold nanoparticles , put it in the refrigerator at 0 ~ 4 ℃ and save it for later use;
所述氯金酸水溶液的浓度为3~6mM;所述柠檬酸钠水溶液的质量分数为1%;The concentration of the chloroauric acid aqueous solution is 3-6 mM; the mass fraction of the sodium citrate aqueous solution is 1%;
所述4'-氨基-苯并-18-冠醚-6的DMF溶液的浓度为0.1mM;The concentration of the DMF solution of the 4'-amino-benzo-18-crown-6 is 0.1 mM;
所述3-巯基丙酸的乙醇溶液的浓度为0.15mM;The concentration of the ethanol solution of 3-mercaptopropionic acid is 0.15mM;
所述DMF为N,N-二甲基甲酰胺;所述参加反应的物质为分析纯。The DMF is N,N-dimethylformamide; the substances involved in the reaction are analytically pure.
本发明还提供了所述的金纳米粒子的用途,其特征在于,所述的金纳米粒子用于检测Cd2+、Ba2+、Pb2+重金属离子,具体包括如下步骤:The present invention also provides the use of the gold nanoparticles, characterized in that, the gold nanoparticles are used to detect Cd 2+ , Ba 2+ , Pb 2+ heavy metal ions, and specifically include the following steps:
将所制备的金纳米粒子的水溶液分别与不同浓度Cd2+、Ba2+、Pb2+重金属离子的标准溶液反应,根据不同的颜色变化制成标准卡片(图2),包括空白实验结果的卡片,用于不同环境下待检测样品的现场检测;或者The prepared aqueous solutions of gold nanoparticles were reacted with standard solutions of heavy metal ions with different concentrations of Cd 2+ , Ba 2+ , Pb 2+ , and standard cards were made according to different color changes (Fig. 2), including blank experimental results. Cards for on-site testing of samples to be tested in different environments; or
将所制备的金纳米粒子的水溶液与不同浓度Cd2+、Ba2+、Pb2+重金属离子的标准溶液反应,然后通过紫外可见吸收光谱,测试反应后的金纳米粒子表面等离子共振吸收峰的峰位以及强度发生的变化,绘制紫外可见吸收光谱和标准曲线(图3),用于不同环境下待检测样品的检测,将测试结果代入标准曲线,进行比对、计算,判断待测样品中是否存在Cd2+、Ba2+、Pb2+离子或计算待测样品中Cd2+、Ba2+、Pb2+离子的浓度,从而实现对样品中Cd2+、Ba2+、Pb2+重金属离子的定量检测;The prepared aqueous solution of gold nanoparticles was reacted with standard solutions of heavy metal ions with different concentrations of Cd 2+ , Ba 2+ , Pb 2+ , and then the surface plasmon resonance absorption peaks of the reacted gold nanoparticles were tested by ultraviolet-visible absorption spectrum. Changes in peak position and intensity, draw UV-Vis absorption spectrum and standard curve (Figure 3), which are used for the detection of samples to be tested in different environments, substitute the test results into the standard curve, compare and calculate, and judge the samples to be tested. Whether there is Cd 2+ , Ba 2+ , Pb 2+ ions or calculate the concentration of Cd 2+ , Ba 2+ , Pb 2+ ions in the sample to be tested, so as to realize the control of Cd 2+ , Ba 2+ , Pb 2 + Quantitative detection of heavy metal ions;
裸眼检测限为Cd2+为10nM,Ba2+为20nM,Pb2+为50nM;The naked eye detection limit is 10nM for Cd 2+ , 20nM for Ba 2+ , and 50nM for Pb 2+ ;
紫外可见光谱检测限为Cd2+为5nM,Ba2+为10nM,Pb2+为20nM;The detection limit of UV-Vis spectrum is 5nM for Cd 2+ , 10nM for Ba 2+ , and 20nM for Pb 2+ ;
所述待检测样品可以是矿泉水、自来水或湖水。The sample to be detected can be mineral water, tap water or lake water.
综上所述,本发明提供了一种金纳米粒子及其制备方法,以及用所制备的金纳米粒子用于检测Cd2+、Ba2+、Pb2+重金属离子的技术;该技术方法基于团聚机理,利用修饰剂有机化合物上的氨基或羧基能够形成强的特定的氢键作用或通过有机化合物上的苯环形成强的π-π堆积作用,从而引起金纳米粒子团聚,使得溶液颜色发生变化,引起金纳米粒子表面等离子共振吸收峰的峰位以及吸收强度发生变化,因此,直接利用肉眼和紫外可见分光光度进行判定,即可快速地检测样品中是否含有Cd2+、Ba2+、Pb2+重金属离子或离子的含量,实现对样品中Cd2+、Ba2+、Pb2+重金属离子的快速检测。In summary, the present invention provides a gold nanoparticle and a preparation method thereof, as well as a technology for detecting Cd 2+ , Ba 2+ , Pb 2+ heavy metal ions by using the prepared gold nanoparticle; the technical method is based on Agglomeration mechanism, using the amino group or carboxyl group on the modifier organic compound can form a strong specific hydrogen bond or form a strong π-π stacking effect through the benzene ring on the organic compound, thereby causing the agglomeration of gold nanoparticles and making the solution color occur. Therefore, the naked eye and UV-visible spectrophotometry can be directly used to determine whether the sample contains Cd 2+ , Ba 2+ , The content of Pb 2+ heavy metal ions or ions realizes the rapid detection of Cd 2+ , Ba 2+ and Pb 2+ heavy metal ions in the sample.
与现有技术相比,本发明的优点在于:本发明提一种金纳米粒子及其制备方法与多种离子检测的应用技术,该技术方法操作简单方便、原料廉价易得、成本低、检测快速、灵敏度高、选择性强并且可实施现场裸眼比色检测,适用于矿泉水、自来水、湖水以及其他复杂体系中Cd2+、Ba2+、Pb2+的快速检测,具有广泛的潜在应用价值。Compared with the prior art, the advantages of the present invention are: the present invention provides a gold nanoparticle, a preparation method thereof, and a variety of application technologies for ion detection. Rapid, high sensitivity, strong selectivity and on-site naked eye colorimetric detection, suitable for rapid detection of Cd 2+ , Ba 2+ , Pb 2+ in mineral water, tap water, lake water and other complex systems, with a wide range of potential applications value.
附图说明Description of drawings
图1、本发明所述的金纳米粒子的TEM图,粒子直径范围10-20nm;Fig. 1, the TEM image of the gold nanoparticle of the present invention, the particle diameter range is 10-20nm;
图2、本发明所述的不同检测组分的标准卡片,包括空白实验结果的卡片;其中,图2a为Cd2+浓度(μM)的标准卡片,图2b为Ba2+(μM)浓度的标准卡片,图2c为Pb2+(μM)浓度的标准卡片;Figure 2. Standard cards of different detection components according to the present invention, including blank test results cards; wherein, Figure 2a is a standard card with Cd 2+ concentration (μM), and Figure 2b is a standard card with Ba 2+ (μM) concentration Standard card, Figure 2c is the standard card of Pb 2+ (μM) concentration;
图3、本发明所述的不同检测组分的紫外可见吸收光谱和标准曲线,标准曲线为所述检测金属离子的紫外可见吸收强度比率与金属离子浓度之间的线性关系,纵坐标为测试组分两个最大吸收波长对应的吸收强度的比率,横坐标为相应的金属离子的浓度;Fig. 3, the ultraviolet-visible absorption spectrum of different detection components of the present invention and the standard curve, the standard curve is the linear relationship between the ultraviolet-visible absorption intensity ratio of the described detection metal ion and the metal ion concentration, and the ordinate is the test group The ratio of the absorption intensity corresponding to the two maximum absorption wavelengths, and the abscissa is the concentration of the corresponding metal ion;
图4、不同组分的粒子表面等离子共振紫外可见吸收光谱,图中abc为4'-氨基-苯并-18-冠醚-6,3-MPA为3-巯基丙酸,AuNPs为金纳米粒子。Figure 4. Surface plasmon resonance UV-Vis absorption spectra of particles with different compositions, in the figure abc is 4'-amino-benzo-18-crown-6, 3-MPA is 3-mercaptopropionic acid, and AuNPs are gold nanoparticles .
具体实施方式Detailed ways
下面通过具体实施例进一步描述本发明,但不限制本发明的内容。The present invention is further described below through specific embodiments, but the content of the present invention is not limited.
标准卡片的制作Production of standard cards
步骤(1)将5mL5mM的氯金酸溶液加入到91mL的去离子水中,并在边搅拌、边加热至沸腾的条件下,加入4mL质量分数为1%的柠檬酸钠溶液作为还原剂,反应15min后,制得柠檬酸根还原和修饰的金纳米粒子的水溶液;Step (1) 5mL of 5mM chloroauric acid solution was added to 91mL of deionized water, and under the condition of stirring and heating to boiling, 4mL of sodium citrate solution with a mass fraction of 1% was added as a reducing agent, and the reaction was performed for 15min Then, an aqueous solution of citrate-reduced and modified gold nanoparticles was prepared;
步骤(2)配置10μM的3-MPA-abc溶液:将0.1mmol的3-巯基丙酸(简写为3-MPA)溶于90mL的乙醇中,加热搅拌、溶解;然后在上述溶液中加入0.1mmol的4'-氨基-苯并-18-冠醚-6(简写为abc)和DMF溶剂10mL,加热搅拌、反应30min,添加乙醇,使溶液的体积为100mL,获得混合物溶液;取上述混合物溶液1.0mL,加99mL的乙醇进行稀释,得到最终的3-MPA-abc溶液的浓度为10μM;Step (2) Prepare 10 μM 3-MPA-abc solution: dissolve 0.1 mmol of 3-mercaptopropionic acid (abbreviated as 3-MPA) in 90 mL of ethanol, heat and stir to dissolve; then add 0.1 mmol to the above solution 4'-amino-benzo-18-crown-6 (abbreviated as abc) and 10 mL of DMF solvent, heated and stirred for 30 min, added ethanol to make the volume of the solution 100 mL to obtain a mixture solution; take the above mixture solution 1.0 mL, add 99 mL of ethanol for dilution to obtain a final 3-MPA-abc solution with a concentration of 10 μM;
用去离子水和硝酸镉配制一系列镉离子浓度的水溶液,终浓度依次为0μM、0.01μM、0.02μM、0.05μM、0.1μM、0.3μM、1μM、5μM、7μM和8μM的标准溶液,分别取不同浓度的标准溶液各0.1mL,并各自加入0.9mL步骤(1)所制备的金纳米粒子的水溶液,并加入步骤(2)中制备的3-MPA-abc溶液10μL,得混合溶液,静置20分钟,混合溶液的颜色呈现不同的变化,得到Cd2+离子浓度的标准卡片(图2a),包括空白实验结果的卡片。Deionized water and cadmium nitrate were used to prepare a series of aqueous solutions of cadmium ion concentrations, with final concentrations of 0 μM, 0.01 μM, 0.02 μM, 0.05 μM, 0.1 μM, 0.3 μM, 1 μM, 5 μM, 7 μM and 8 μM standard solutions, respectively. 0.1 mL of standard solutions with different concentrations were added to each, and 0.9 mL of the aqueous solution of gold nanoparticles prepared in step (1) was added, and 10 μL of the 3-MPA-abc solution prepared in step (2) was added to obtain a mixed solution. After 20 minutes, the color of the mixed solution showed different changes, and a standard card of Cd 2+ ion concentration was obtained (Fig. 2a), including a card with blank experimental results.
用去离子水和硝酸钡配制一系列钡离子浓度的水溶液,终浓度依次为0μM、0.02μM、0.05μM、0.08μM、0.5μM、1μM、5μM、8μM、10μM和15μM的标准溶液,分别取不同浓度的标准溶液各0.1mL,并各自加入0.9mL步骤(1)所制备的金纳米粒子的水溶液,并加入步骤(2)中制备的3-MPA-abc溶液10μL,得混合溶液,静置20分钟,混合溶液的颜色呈现不同的变化,得到Ba2+离子浓度的标准卡片(图2b),包括空白实验结果的卡片。A series of aqueous solutions of barium ion concentration were prepared with deionized water and barium nitrate, and the final concentrations were 0 μM, 0.02 μM, 0.05 μM, 0.08 μM, 0.5 μM, 1 μM, 5 μM, 8 μM, 10 μM and 15 μM standard solutions, respectively. 0.1 mL of each concentration standard solution, and 0.9 mL of the gold nanoparticle aqueous solution prepared in step (1) was added to each, and 10 μL of the 3-MPA-abc solution prepared in step (2) was added to obtain a mixed solution. minutes, the color of the mixed solution showed different changes, and the standard cards of Ba 2+ ion concentration were obtained (Fig. 2b), including the cards of blank experimental results.
用去离子水和硝酸铅配制一系列铅离子浓度的水溶液,终浓度依次为0μM、0.05μM、0.1μM、0.3μM、0.5μM、0.8μM、1μM、3μM、5μM、和6μM的标准溶液,分别取不同浓度的标准溶液各0.1mL,并各自加入0.9mL步骤(1)所制备的金纳米粒子的水溶液,并加入步骤(2)中制备的3-MPA-abc溶液10μL,得混合溶液,静置20分钟,混合溶液的颜色呈现不同的变化,得到Pb2+离子浓度的标准卡片(图2c),包括空白实验结果的卡片。A series of aqueous solutions of lead ion concentrations were prepared with deionized water and lead nitrate, and the final concentrations were 0 μM, 0.05 μM, 0.1 μM, 0.3 μM, 0.5 μM, 0.8 μM, 1 μM, 3 μM, 5 μM, and 6 μM standard solutions, respectively. Take 0.1 mL of standard solutions of different concentrations, add 0.9 mL of the gold nanoparticle aqueous solution prepared in step (1), and add 10 μL of the 3-MPA-abc solution prepared in step (2) to obtain a mixed solution. After standing for 20 minutes, the color of the mixed solution showed different changes, and a standard card of Pb 2+ ion concentration was obtained (Fig. 2c), including a card with blank experimental results.
绘制标准曲线:Plot a standard curve:
对上述制备得到的标准样品进行紫外-可见吸收光谱测量,在400~800nm区间内测得的紫外-可见吸收强度的变化,并记录525nm及685nm、695nm、690nm处的吸光度比值。以标准样品的浓度作为横坐标,吸光度比值作为纵坐标,制得标准曲线(图3);通过线性拟合,得到Cd2+离子溶液标准曲线的线性方程为y=0.9937 X+0.1588,R2=0.9917;Ba2+离子溶液标准曲线的线性方程为y=0.0524 X+0.0289,R2=0.9984;Pb2+离子溶液标准曲线的线性方程为y=0.0823 X+0.0213,R2=0.9934。The standard sample prepared above was measured by UV-Vis absorption spectrum, the change of UV-Vis absorption intensity was measured in the interval of 400-800nm, and the ratio of absorbance at 525nm and 685nm, 695nm and 690nm was recorded. Taking the concentration of the standard sample as the abscissa and the absorbance ratio as the ordinate, the standard curve was prepared (Fig. 3); through linear fitting, the linear equation of the standard curve of the Cd 2+ ion solution was obtained as y=0.9937 X+0.1588, R 2 =0.9917; the linear equation of the standard curve of Ba 2+ ion solution is y=0.0524 X+0.0289, R 2 =0.9984; the linear equation of the standard curve of Pb 2+ ion solution is y=0.0823 X+0.0213, R 2 =0.9934.
利用标准卡片和标准曲线对不同浓度Cd2+、Ba2+、Pb2+重金属离子进行检测,裸眼检测限:Cd2+为10nM,Ba2+为20nM,Pb2+为50nM;紫外可见光谱检测限:Cd2+为5nM,Ba2+为10nM,Pb2 +为20nM;紫外可见光谱检测限的计算公式为K×SD/S,K=3,SD为标准偏差,S为斜率。Different concentrations of Cd 2+ , Ba 2+ , Pb 2+ heavy metal ions were detected using standard cards and standard curves. The detection limit of naked eye: Cd 2+ was 10nM, Ba 2+ was 20nM, Pb 2+ was 50nM; UV-visible spectrum Detection limit: Cd 2+ is 5nM, Ba 2+ is 10nM, Pb 2+ is 20nM ; the calculation formula of UV-Vis detection limit is K×SD/S, K=3, SD is the standard deviation, S is the slope.
实施例1Example 1
在圆底烧瓶中加入10mL6mM浓度的氯金酸水溶液,搅拌加热至沸腾,快速加入20mL质量分数1%柠檬酸钠的水溶液,反应15分钟后,加入30mL0.1mM的4'-氨基-苯并-18-冠醚-6的DMF溶液和30mL0.15mM的3-巯基丙酸的乙醇溶液,得反应混合物溶液,反应混合物溶液的pH值用HCl调控为10,溶液颜色由浅黄色变为红色,静置冷却至室温,制得金纳米粒子。将制得金纳米粒子进行TEM测试,其形貌如图1所示。Add 10 mL of 6mM aqueous chloroauric acid solution to the round-bottomed flask, stir and heat to boiling, quickly add 20 mL of 1% sodium citrate aqueous solution, and after 15 minutes of reaction, add 30 mL of 0.1 mM 4'-amino-benzo- The DMF solution of 18-crown-6 and the ethanol solution of 30 mL of 0.15 mM 3-mercaptopropionic acid were used to obtain a reaction mixture solution. The pH value of the reaction mixture solution was adjusted to 10 with HCl, and the color of the solution changed from light yellow to red. Set to cool to room temperature to obtain gold nanoparticles. The obtained gold nanoparticles were tested by TEM, and their morphologies were shown in Figure 1.
实施例2Example 2
在圆底烧瓶中加入20mL3mM的氯金酸水溶液,搅拌加热至沸腾,快速加入20mL质量分数1%柠檬酸钠的水溶液,反应5分钟后,加入20mL0.1mM的4'-氨基-苯并-18-冠醚-6的DMF溶液和30mL0.15mM3-巯基丙酸的乙醇溶液,得反应混合物溶液,用HCl调控其pH值为13,溶液颜色由浅黄色变为红色,静置冷却至室温,制得金纳米粒子。Add 20 mL of 3mM aqueous solution of chloroauric acid to the round-bottomed flask, stir and heat to boiling, quickly add 20 mL of aqueous solution of 1% sodium citrate by mass, and after 5 minutes of reaction, add 20 mL of 0.1 mM 4'-amino-benzo-18 -DMF solution of crown ether-6 and 30mL of ethanol solution of 0.15mM 3-mercaptopropionic acid to obtain a reaction mixture solution, the pH value of which was adjusted with HCl to 13, the color of the solution changed from light yellow to red, and it was left to cool to room temperature. gold nanoparticles.
实施例3Example 3
在圆底烧瓶中加入20mL5mM浓度的氯金酸水溶液,搅拌加热至沸腾,快速加入30mL质量分数1%柠檬酸钠的水溶液,反应10分钟后,加入40mL 0.1mM的4'-氨基-苯并-18-冠醚-6的DMF溶液和40mL0.15mM3-巯基丙酸的乙醇溶液,反应混合物溶液的pH值用HCl调控为12,溶液颜色由浅黄色变为红色,静置冷却至室温,制得金纳米粒子。Add 20 mL of 5mM aqueous chloroauric acid solution to the round-bottomed flask, stir and heat to boiling, quickly add 30 mL of 1% sodium citrate aqueous solution, and after 10 minutes of reaction, add 40 mL of 0.1 mM 4'-amino-benzo- DMF solution of 18-crown-6 and 40mL of ethanol solution of 0.15mM 3-mercaptopropionic acid, the pH value of the reaction mixture solution was adjusted to 12 with HCl, the color of the solution changed from light yellow to red, and it was left to cool to room temperature to obtain Gold Nanoparticles.
实施例4Example 4
“矿泉水”中Cd2+、Ba2+、Pb2+离子的检测Detection of Cd 2+ , Ba 2+ , Pb 2+ ions in "mineral water"
(a)取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Cd2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“矿泉水”等体积的待检测溶液分别加入到所述的两份金纳米粒子水溶液中,形成混合液A和混合液B;反应15分钟后,对比混合液B与混合液A的颜色,若颜色变化,则待检测的“矿泉水”溶液中存在Cd2+离子,若不存在颜色变化,则待检测的“矿泉水”溶液中不存在Cd2+离子,或者对比计算混合液B与混合液A的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“矿泉水”溶液中存在Cd2+离子,若没有发生变化,则待检测的“矿泉水”溶液中不存在Cd2+离子。(a) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution without Cd ions (within the detection range) as a comparison solution, mix the comparison solution and "mineral water" equal volumes of The detection solution was added to the two aqueous solutions of gold nanoparticles to form mixed solution A and mixed solution B; after 15 minutes of reaction, the colors of mixed solution B and mixed solution A were compared. There are Cd 2+ ions in the "mineral water" solution, if there is no color change, there is no Cd 2+ ions in the "mineral water" solution to be detected, or compare and calculate the UV-visible absorption intensity of mixed solution B and mixed solution A and Peak, if its absorption intensity and peak value change, there are Cd 2+ ions in the “mineral water” solution to be detected. If there is no change, there is no Cd 2+ ion in the “mineral water” solution to be detected.
(b)取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Ba2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“矿泉水”等体积的待检测溶液分别加入到所述的两份金纳米粒子水溶液中,形成混合液C和混合液D;反应15分钟后,对比混合液D与混合液C的颜色,若颜色变化,则待检测的“矿泉水”溶液中存在Ba2+离子,若不存在颜色变化,则待检测的“矿泉水”溶液中不存在Ba2+离子,或者对比计算混合液D与混合液C的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“矿泉水”溶液中存在Ba2+离子,若没有发生变化,则待检测的“矿泉水”溶液中不存在Ba2+离子。(b) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution without Ba ions (within the detection range) as a comparison solution, mix the comparison solution and "mineral water" with equal volumes of the The detection solution was added to the two aqueous solutions of gold nanoparticles to form mixed solution C and mixed solution D; after 15 minutes of reaction, the colors of mixed solution D and mixed solution C were compared. There are Ba 2+ ions in the "mineral water" solution. If there is no color change, then there are no Ba 2+ ions in the "mineral water" solution to be detected. If the absorption intensity and peak value change, there are Ba 2+ ions in the “mineral water” solution to be detected. If there is no change, there are no Ba 2+ ions in the “mineral water” solution to be detected.
(c))取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Pb2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“矿泉水”等体积的待检测溶液分别加入到所述的两份金纳米粒子的水溶液中,形成混合液E和混合液F;反应15分钟后,对比混合液F与混合液E的颜色,若颜色变化,则待检测的“矿泉水”溶液中存在Pb2+离子,若不存在颜色变化,则待检测的“矿泉水”溶液中不存在Pb2+离子,或者对比计算混合液F与混合液E的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“矿泉水”溶液中存在Pb2+离子,若没有发生变化,则待检测的“矿泉水”溶液中不存在Pb2+离子。(c)) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution without Pb 2+ ions (within the detection range) as a contrast solution, mix the contrast solution and "mineral water" equal volumes of The solution to be detected is respectively added to the two aqueous solutions of gold nanoparticles to form mixed solution E and mixed solution F; after 15 minutes of reaction, the colors of mixed solution F and mixed solution E are compared, if the color changes, then to be detected There are Pb 2+ ions in the "mineral water" solution of the sample, if there is no color change, then there is no Pb 2+ ions in the "mineral water" solution to be detected, or compare and calculate the UV-visible absorption of the mixed solution F and the mixed solution E Intensity and peak value, if the absorption intensity and peak value change, there is Pb 2+ ion in the “mineral water” solution to be detected, if there is no change, then there is no Pb 2+ ion in the “mineral water” solution to be detected .
实施例5Example 5
“自来水”中Cd2+、Ba2+、Pb2+离子的检测Detection of Cd 2+ , Ba 2+ , Pb 2+ ions in "tap water"
(a)取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Cd2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“自来水”等体积的待检测溶液分别加入到所述的两份金纳米粒子的水溶液中,形成混合液A和混合液B;反应15分钟后,对比混合液B与混合液A的颜色,若颜色变化,则待检测的“自来水”溶液中存在Cd2+离子,若不存在颜色变化,则待检测的“自来水”溶液中不存在Cd2+离子,或者对比计算混合液B与混合液A的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“自来水”溶液中存在Cd2+离子,若没有发生变化,则待检测的“自来水”溶液中不存在Cd2+离子。(a) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution that does not contain Cd ions (within the detection range) as a comparison solution, and use the comparison solution and "tap water" equal volumes of the to-be-detected The solutions were added to the two aqueous solutions of gold nanoparticles to form mixed solution A and mixed solution B; after 15 minutes of reaction, compare the colors of mixed solution B and mixed solution A. There are Cd 2+ ions in the "tap water" solution, if there is no color change, then there are no Cd 2+ ions in the "tap water" solution to be detected, or compare and calculate the UV-visible absorption intensity and peak value of mixed solution B and mixed solution A, If its absorption intensity and peak value change, Cd 2+ ions exist in the “tap water” solution to be detected. If there is no change, there are no Cd 2+ ions in the “tap water” solution to be detected.
(b)取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Ba2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“自来水”等体积的待检测溶液分别加入到所述的两份金纳米粒子的水溶液中,形成混合液C和混合液D;反应15分钟后,对比混合液D与混合液C的颜色,若颜色变化,则待检测的“自来水”溶液中存在Ba2+离子,若不存在颜色变化,则待检测的“自来水”溶液中不存在Ba2+离子,或者对比计算混合液D与混合液C的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“自来水”溶液中存在Ba2+离子,若没有发生变化,则待检测的“自来水”溶液中不存在Ba2+离子。(b) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution without Ba ions (within the detection range) as a comparison solution, mix the comparison solution and "tap water" equal volumes of the solution to be detected The solutions were added to the two aqueous solutions of gold nanoparticles to form mixed solution C and mixed solution D; after 15 minutes of reaction, compare the colors of mixed solution D and mixed solution C. There are Ba 2+ ions in the "tap water" solution, if there is no color change, then there are no Ba 2+ ions in the "tap water" solution to be detected, or compare and calculate the UV-visible absorption intensity and peak value of mixed solution D and mixed solution C, If its absorption intensity and peak value change, there are Ba 2+ ions in the "tap water" solution to be detected. If there is no change, there are no Ba 2+ ions in the "tap water" solution to be detected.
(c))取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Pb2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“自来水”等体积的待检测溶液分别加入到所述的两份金纳米粒子的水溶液中,形成混合液E和混合液F;反应15分钟后,对比混合液F与混合液E的颜色,若颜色变化,则待检测的“自来水”溶液中存在Pb2+离子,若不存在颜色变化,则待检测的“自来水”溶液中不存在Pb2+离子,或者对比计算混合液F与混合液E的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“自来水”溶液中存在Pb2+离子,若没有发生变化,则待检测的“自来水”溶液中不存在Pb2+离子。(c)) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution without Pb ions (within the detection range) as a comparison solution, mix the comparison solution and "tap water" equal volumes of The detection solution is respectively added to the two aqueous solutions of gold nanoparticles to form mixed solution E and mixed solution F; after 15 minutes of reaction, compare the colors of mixed solution F and mixed solution E, if the color changes, then the There are Pb 2+ ions in the "tap water" solution, if there is no color change, then there are no Pb 2+ ions in the "tap water" solution to be detected, or compare and calculate the UV-visible absorption intensity and peak value of the mixed solution F and the mixed solution E , if its absorption intensity and peak value change, there is Pb 2+ ion in the "tap water" solution to be detected, if there is no change, there is no Pb 2+ ion in the "tap water" solution to be detected.
实施例6Example 6
“湖水”中Cd2+、Ba2+、Pb2+离子的检测Detection of Cd 2+ , Ba 2+ , Pb 2+ ions in "lake water"
(a)取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Cd2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“湖水”等体积的待检测溶液分别加入到所述的两份金纳米粒子的水溶液中,形成混合液A和混合液B;反应15分钟后,对比混合液B与混合液A的颜色,若颜色变化,则待检测的“湖水”溶液中存在Cd2+离子,若不存在颜色变化,则待检测的“湖水”溶液中不存在Cd2+离子,或者对比计算混合液B与混合液A的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“湖水”溶液中存在Cd2+离子,若没有发生变化,则待检测的“湖水”溶液中不存在Cd2+离子。(a) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution that does not contain Cd ions (within the detection range) as a comparison solution, and use the comparison solution and "lake water" equal volumes of the to-be-detected The solutions were added to the two aqueous solutions of gold nanoparticles to form mixed solution A and mixed solution B; after 15 minutes of reaction, compare the colors of mixed solution B and mixed solution A. There are Cd 2+ ions in the "lake water" solution, if there is no color change, then there is no Cd 2+ ions in the "lake water" solution to be detected, or compare and calculate the UV-visible absorption intensity and peak value of mixed solution B and mixed solution A, If its absorption intensity and peak value change, there are Cd 2+ ions in the “lake water” solution to be detected. If there is no change, there are no Cd 2+ ions in the “lake water” solution to be detected.
(b)取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Ba2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“湖水”等体积的待检测溶液分别加入到所述的两份金纳米粒子的水溶液中,形成混合液C和混合液D;反应15分钟后,对比混合液D与混合液C的颜色,若颜色变化,则待检测的“湖水”溶液中存在Ba2+离子,若不存在颜色变化,则待检测的“湖水”溶液中不存在Ba2+离子,或者对比计算混合液D与混合液C的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“湖水”溶液中存在Ba2+离子,若没有发生变化,则待检测的“湖水”溶液中不存在Ba2+离子。(b) Take two equal volumes of aqueous solutions of the prepared gold nanoparticles; prepare an aqueous solution without Ba ions (within the detection range) as a comparison solution, and use the comparison solution and "lake water" equal volumes of the to-be-detected The solutions were respectively added to the two aqueous solutions of gold nanoparticles to form mixed solution C and mixed solution D; after 15 minutes of reaction, compare the colors of mixed solution D and mixed solution C. There are Ba 2+ ions in the "lake water" solution, if there is no color change, then there are no Ba 2+ ions in the "lake water" solution to be detected, or compare and calculate the ultraviolet-visible absorption intensity and peak value of the mixture D and the mixture C, If its absorption intensity and peak value change, there are Ba 2+ ions in the "lake water" solution to be detected. If there is no change, there are no Ba 2+ ions in the "lake water" solution to be detected.
(c))取两份等体积相同的所制备的金纳米粒子的水溶液;配制不含Pb2+离子(在检测范围内)的水溶液作为对比溶液,将对比溶液和“湖水”等体积的待检测溶液分别加入到所述的两份金纳米粒子的水溶液中,形成混合液E和混合液F;反应15分钟后,对比混合液F与混合液E的颜色,若颜色变化,则待检测的“湖水”溶液中存在Pb2+离子,若不存在颜色变化,则待检测的“湖水”溶液中不存在Pb2+离子,或者对比计算混合液F与混合液E的紫外可见吸收强度和峰值,若其吸收强度和峰值发生变化,则待检测的“湖水”溶液中存在Pb2+离子,若没有发生变化,则待检测的“湖水”溶液中不存在Pb2+离子。(c)) Take two equal volumes of the same aqueous solution of the prepared gold nanoparticles; prepare an aqueous solution without Pb ions (within the detection range) as a comparison solution, mix the comparison solution and "lake water" equal volumes of the The detection solution is respectively added to the two aqueous solutions of gold nanoparticles to form mixed solution E and mixed solution F; after 15 minutes of reaction, compare the colors of mixed solution F and mixed solution E, if the color changes, then the There are Pb 2+ ions in the "lake water" solution. If there is no color change, then there are no Pb 2+ ions in the "lake water" solution to be detected, or compare and calculate the UV-visible absorption intensity and peak value of the mixed solution F and the mixed solution E. , if its absorption intensity and peak value change, there are Pb 2+ ions in the “lake water” solution to be detected; if there is no change, there is no Pb 2+ ion in the “lake water” solution to be detected.
实施例7Example 7
鉴别区分Cd2+、Ba2+、Pb2+离子Identify and differentiate Cd 2+ , Ba 2+ , Pb 2+ ions
0.9mL的金纳米粒子的水溶液,在不同的样品管中分别加入0.1mL的0.1mM镉、钡、铅离子浓度的水溶液,混匀后,再加入10uL10μM的3-MPA-abc溶液,反应15min,进行紫外-可见吸收光谱测试,结果如图4所示,不同的测试组分紫外可见吸收强度、峰值不同以及它们的颜色变化不同,可实现鉴别区分Cd2+、Ba2+、Pb2+重金属离子。0.9mL aqueous solution of gold nanoparticles, add 0.1mL aqueous solution of 0.1mM cadmium, barium, lead ion concentration to different sample tubes, after mixing, add 10uL 10μM 3-MPA-abc solution, react for 15min, The UV-Vis absorption spectrum test was carried out, and the results are shown in Figure 4. Different test components have different UV-Vis absorption intensities, different peaks and different color changes, which can distinguish Cd 2+ , Ba 2+ , Pb 2+ heavy metals ion.
实施例8Example 8
利用紫外-可见吸收光谱仪,测定含Cd2+离子的待测样品的A695nm/A525nm比值为0.6,代入Cd2+离子溶液标准曲线的线性方程y=0.9937 X+0.1588,可以计算出X=0.4440,即得Cd2+离子的浓度为0.4440μM;Using ultraviolet-visible absorption spectrometer, the ratio of A 695nm /A 525nm of the sample to be tested containing Cd 2+ ions was determined to be 0.6, and substituted into the linear equation of the standard curve of Cd 2+ ion solution y=0.9937 X+0.1588, it can be calculated that X= 0.4440, that is, the concentration of Cd 2+ ions is 0.4440 μM;
实施例9Example 9
利用紫外-可见吸收光谱仪,测定含Ba2+离子的待测样品的A685nm/A525nm比值为0.6,代入Ba2+离子溶液标准曲线的线性方程y=0.0524 X+0.0289,可以计算出X=10.90,即得Ba2+离子的浓度为10.90μM;Using UV-Vis absorption spectrometer, determine the ratio of A 685nm /A 525nm of the sample containing Ba 2+ ions to be 0.6, and substitute it into the linear equation of the standard curve of Ba 2+ ion solution y=0.0524 X+0.0289, it can be calculated that X= 10.90, that is, the concentration of Ba 2+ ions is 10.90 μM;
实施例10Example 10
利用紫外-可见吸收光谱仪,测定含Pb2+离子的待测样品的A690nm/A525nm比值为0.6,代入Pb2+离子溶液标准曲线的线性方程y=0.0823 X+0.0213,可以计算出X=7.032,即得Pb2+离子的浓度为7.032μM;Using UV-Vis absorption spectrometer, the ratio of A 690nm /A 525nm of the sample to be tested containing Pb 2+ ions was determined to be 0.6, and substituted into the linear equation y=0.0823 X+0.0213 of the standard curve of the Pb 2+ ion solution, X= 7.032, that is, the concentration of Pb 2+ ions is 7.032 μM;
以上所述的实施例对本发明的技术方案进行了详细说明,应理解的是以上所述仅为本发明的具体实施例,并不用于限制本发明,凡在本发明的原则范围内所做的任何修改和改进等,均应包含在本发明的保护范围之内。The above embodiments describe the technical solutions of the present invention in detail. It should be understood that the above are only specific embodiments of the present invention and are not intended to limit the present invention. Anything done within the scope of the principles of the present invention Any modification and improvement, etc., should be included within the protection scope of the present invention.
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