CN114350352A - Novel carbon materials based on coffee beans and methods for detecting lead ions and PPi - Google Patents

Novel carbon materials based on coffee beans and methods for detecting lead ions and PPi Download PDF

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CN114350352A
CN114350352A CN202111570633.2A CN202111570633A CN114350352A CN 114350352 A CN114350352 A CN 114350352A CN 202111570633 A CN202111570633 A CN 202111570633A CN 114350352 A CN114350352 A CN 114350352A
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刘意
严志红
姚微
冯冰洁
何晓婷
汪子琨
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Meijianji Bioengineering Technology Guangzhou Co ltd
Guangdong Pharmaceutical University
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Guangdong Pharmaceutical University
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Abstract

本发明公开了一种基于咖啡豆的新型碳材料及检测铅离子、PPi的方法,属于纳米级碳材料技术及其荧光检测应用领域。包括以下步骤:(1)将咖啡豆粉末、氢氧化钠溶解于水中,得溶液A;(2)溶液A高温下水热反应,得到溶液B;(3)溶液B经透析,得到溶液C;(4)将溶液C过滤、干燥后,得CQDs。本发明通过一步水热法合成的碳量子点作为荧光探针,该荧光探针能通过荧光淬灭效应高灵敏度地检测Pb2+,再通过荧光恢复现象检测PPi,具有合成方法绿色简单、检测快速方便、结果准确的优点,具有较高的生物医学领域应用价值。

Figure 202111570633

The invention discloses a novel carbon material based on coffee beans and a method for detecting lead ions and PPi, belonging to the nanometer carbon material technology and the application field of fluorescence detection. The method comprises the following steps: (1) dissolving coffee bean powder and sodium hydroxide in water to obtain solution A; (2) hydrothermally reacting solution A at high temperature to obtain solution B; (3) dialysis of solution B to obtain solution C; ( 4) After the solution C was filtered and dried, CQDs were obtained. In the present invention, the carbon quantum dots synthesized by one-step hydrothermal method are used as fluorescent probes. The fluorescent probes can detect Pb2+ with high sensitivity through the fluorescence quenching effect, and then detect PPi through the fluorescence recovery phenomenon. The synthesis method is green and simple, and the detection is fast and convenient. , The advantages of accurate results have high application value in the field of biomedicine.

Figure 202111570633

Description

基于咖啡豆的新型碳材料及检测铅离子、PPi的方法Novel carbon materials based on coffee beans and methods for detecting lead ions and PPi

技术领域technical field

本发明属于纳米级碳材料技术及其荧光检测应用领域,具体涉及一种基于咖啡豆的新型碳材料及检测铅离子、PPi的方法。The invention belongs to the nanoscale carbon material technology and the application field of fluorescence detection thereof, and particularly relates to a novel carbon material based on coffee beans and a method for detecting lead ions and PPi.

背景技术Background technique

重金属污染已严重威胁环境和人类健康,如何有效监测环境中有毒重金属离子的浓度已成为一个日益重要的问题。铅是最常见的有毒重金属之一,广泛应用于颜料、水管、蓄电池、防腐涂料、合金等领域,广泛存在于环境的各个领域。同时,由于Pb2+的非生物降解性,当暴露在受污染的空气和水源中时,Pb2+很容易积聚在人类的神经和心血管系统中。当血液中Pb2+浓度高于5μM时,可导致贫血、生殖功能障碍、神经系统功能障碍和发育障碍等,而过高的Pb2+浓度甚至可导致死亡。因此,有必要建立快速、灵敏的痕量Pb2+测定方法。Heavy metal pollution has seriously threatened the environment and human health. How to effectively monitor the concentration of toxic heavy metal ions in the environment has become an increasingly important issue. Lead is one of the most common toxic heavy metals, widely used in pigments, water pipes, batteries, anti-corrosion coatings, alloys and other fields, and widely exists in various fields of the environment. Meanwhile, due to the non-biodegradability of Pb 2+ , Pb 2+ easily accumulates in the human nervous and cardiovascular systems when exposed to polluted air and water sources. When the concentration of Pb 2+ in the blood is higher than 5μM, it can lead to anemia, reproductive dysfunction, nervous system dysfunction and developmental disorders, etc., and excessive Pb 2+ concentration can even lead to death. Therefore, it is necessary to establish a rapid and sensitive method for the determination of trace Pb 2+ .

阴离子在整个生物系统中无处不在,在广泛的化学和生物过程中发挥着重要作用。作为一种阴离子,焦磷酸盐(PPi)在细胞条件下三磷酸腺苷水解为一磷酸腺苷时被释放。它是生物能量循环和DNA合成的一部分,也是几个结晶反应的抑制剂。因此,近年来有许多人致力于发展PPi的非生物传感器,这些工作在医学、生物学、环境和营养学中变得重要。Anions are ubiquitous throughout biological systems and play important roles in a wide range of chemical and biological processes. As an anion, pyrophosphate (PPi) is released when adenosine triphosphate is hydrolyzed to adenosine monophosphate under cellular conditions. It is part of the bioenergy cycle and DNA synthesis and is an inhibitor of several crystallization reactions. Therefore, many efforts have been devoted to developing non-biosensors for PPi in recent years, and these works have become important in medicine, biology, environment, and nutrition.

Pb2+的传统测定方法很多,如原子吸收光谱法(AAS)、阳极溶出伏安法(ASV)、电感耦合等离子体原子发射光谱法(ICP-AES)和电感耦合等离子体质谱法(ICP-MS)。然而,这些方法通常需要昂贵和复杂的仪器、耗时和复杂的样品预处理程序。另一方面,在迄今为止报道的众多PPi传感器中,只有少数几个例子是在100%的PPi水溶液中能有效检测PPi的荧光传感器。大多数报道都集中在它们在非水溶剂中的行为上,这些方法大多基于有机小分子探针的合成,复杂且耗时,需要有机溶剂作为反应介质。There are many traditional methods for the determination of Pb 2+ , such as atomic absorption spectrometry (AAS), anodic stripping voltammetry (ASV), inductively coupled plasma atomic emission spectrometry (ICP-AES) and inductively coupled plasma mass spectrometry (ICP- MS). However, these methods often require expensive and complex instrumentation, time-consuming and complicated sample pretreatment procedures. On the other hand, among the numerous PPi sensors reported so far, only a few examples are fluorescent sensors that can effectively detect PPi in 100% PPi aqueous solution. Most reports have focused on their behavior in non-aqueous solvents, and these methods are mostly based on the synthesis of organic small molecule probes, which are complex and time-consuming and require organic solvents as reaction media.

近年来,碳量子点(CQDs)作为一种新的荧光纳米粒子,引起了研究者的极大兴趣。CQDs通常为球形结构,粒径小于10nm,具有较强且稳定的荧光,与有机染料、量子点和贵金属纳米颗粒相比,CQDs具有优异的水溶性、良好的光稳定性、超强的生物相容性和低毒性,这使得碳量子点可以有效地应用于化学传感器和生物传感器的实际应用中。根据文献调研显示,利用不同的原料为碳源(如柠檬酸,树叶,柠檬等)通过水热法制备CQDs具有简单、易操作、成本低等优点,目前已成为制备CQDs最常用的方法之一,合成的CQDs表面通常带有羟基、羧基或氨基,可以与金属离子和重金属离子配位从而引起荧光的变化。In recent years, carbon quantum dots (CQDs) have attracted great interest from researchers as a new type of fluorescent nanoparticles. Compared with organic dyes, quantum dots and noble metal nanoparticles, CQDs have excellent water solubility, good photostability, and superior biological phase. Capacitance and low toxicity, which make carbon quantum dots effective for practical applications in chemical sensors and biosensors. According to the literature survey, using different raw materials as carbon sources (such as citric acid, leaves, lemons, etc.) to prepare CQDs by hydrothermal method has the advantages of simplicity, easy operation and low cost, and has become one of the most commonly used methods for preparing CQDs. , the surface of synthesized CQDs usually has hydroxyl, carboxyl or amino groups, which can coordinate with metal ions and heavy metal ions to cause fluorescence changes.

基于对新型碳量子点制备的迫切需求,本申请以咖啡豆为原料,与一定浓度的碱(NaOH)相互作用,通过一步水热法合成碳量子点,并以其作为荧光探针,快速检测Pb2+和PPi。Based on the urgent need for the preparation of novel carbon quantum dots, the present application uses coffee beans as raw materials, interacts with a certain concentration of alkali (NaOH), and synthesizes carbon quantum dots by one-step hydrothermal method, and uses them as fluorescent probes for rapid detection. Pb 2+ and PPi.

发明内容SUMMARY OF THE INVENTION

本发明的目的在于提供一种基于咖啡豆的新型碳材料及检测Pb2+、PPi的方法,具体为基于荧光“开-关”效应检测Pb2+和PPi的方法,以咖啡豆为原料,通过一步水热法合成的碳量子点作为荧光探针,该荧光探针能通过荧光淬灭效应高灵敏度地检测Pb2+,再通过荧光恢复现象检测PPi,具有合成方法绿色简单、检测快速方便、结果准确的优点,克服了传统铅离子和焦磷酸盐检测方法设备成本高、操作复杂等问题。The object of the present invention is to provide a novel carbon material based on coffee beans and a method for detecting Pb 2+ and PPi, specifically a method for detecting Pb 2+ and PPi based on fluorescence "on-off" effect, using coffee beans as raw materials, The carbon quantum dots synthesized by one-step hydrothermal method are used as fluorescent probes. The fluorescent probes can detect Pb 2+ with high sensitivity through the fluorescence quenching effect, and then detect PPi through the fluorescence recovery phenomenon. The synthesis method is green and simple, and the detection is fast and convenient. , The advantages of accurate results overcome the problems of high equipment cost and complicated operation of traditional lead ion and pyrophosphate detection methods.

为实现上述发明目的,本发明技术方案如下:In order to realize the above-mentioned purpose of the invention, the technical scheme of the present invention is as follows:

一方面,本发明提供一种基于咖啡豆的新型碳材料的制备方法,包括以下步骤:In one aspect, the present invention provides a method for preparing a novel carbon material based on coffee beans, comprising the following steps:

(1)将咖啡豆粉末、氢氧化钠溶解于水中,得溶液A;(1) coffee bean powder and sodium hydroxide are dissolved in water to obtain solution A;

(2)溶液A高温下反应,得到溶液B;(2) solution A reacts at high temperature to obtain solution B;

(3)溶液B经透析,得到溶液C;(3) solution B is dialyzed to obtain solution C;

(4)将溶液C过滤、干燥后,得CQDs。(4) After the solution C was filtered and dried, CQDs were obtained.

优选地,步骤(1)中,所述咖啡豆粉末由咖啡豆粉碎得到,粉碎的方式包括但不限于研磨、碾碎、超微粉碎、气流粉碎等方式。Preferably, in step (1), the coffee bean powder is obtained by pulverizing coffee beans, and the pulverizing methods include but are not limited to grinding, grinding, ultra-fine pulverizing, jet pulverizing, and the like.

优选地,步骤(1)中,所述咖啡豆粉末和氢氧化钠的质量比为2~4:7.2~16.8。Preferably, in step (1), the mass ratio of the coffee bean powder and sodium hydroxide is 2-4:7.2-16.8.

此反应中,氢氧化钠溶液充当催化剂和分解剂的作用,对于终产品的制备至关重要。氢氧化钠不仅可以使咖啡豆中的高分子(如蛋白质、纤维素等)在碱性条件下发生降解,进而提供生成碳量子点的原料,而且也参与了碳源生成量子的系列化学反应。此过程是咖啡中含有的聚合物(多糖类、蛋白质等)在含有氢氧化钠的高温条件下,能够催化分解形成胺类和羧酸类小分子含碳化合物,所得小分子含碳物质在高温高压的条件下发生反应形成碳量子点。In this reaction, sodium hydroxide solution acts as a catalyst and a decomposer, which is crucial for the preparation of the final product. Sodium hydroxide can not only degrade the macromolecules (such as protein, cellulose, etc.) in coffee beans under alkaline conditions, thereby providing raw materials for the formation of carbon quantum dots, but also participate in a series of chemical reactions in which carbon sources generate quantum. This process is that the polymers (polysaccharides, proteins, etc.) contained in coffee can be catalytically decomposed to form amines and carboxylic acid small carbon-containing compounds under high temperature conditions containing sodium hydroxide, and the obtained small molecular carbon-containing substances are in The reaction occurs under high temperature and high pressure conditions to form carbon quantum dots.

优选地,步骤(1)中,所述咖啡豆粉末和水的的质量比为1:50~200。Preferably, in step (1), the mass ratio of the coffee bean powder to water is 1:50-200.

优选地,步骤(1)中,所述水为纯水。Preferably, in step (1), the water is pure water.

优选地,步骤(1)中,通过超声使其充分溶解。Preferably, in step (1), it is fully dissolved by ultrasound.

优选地,步骤(2)中,所述反应的温度为150~200℃,反应的时间为240~480min。Preferably, in step (2), the temperature of the reaction is 150-200° C., and the reaction time is 240-480 min.

优选地,步骤(2)中,所述反应不锈钢反应釜中的聚四氟乙烯内衬中进行。Preferably, in step (2), the reaction is carried out in a polytetrafluoroethylene lining in the stainless steel reaction kettle.

优选地,步骤(3)中,所述透析在纯水、1000~12000D的透析袋中进行,透析时间为24~72h。Preferably, in step (3), the dialysis is performed in a dialysis bag of pure water and 1000-12,000 D, and the dialysis time is 24-72 hours.

优选地,步骤(4)中,所述干燥的方式为冷冻干燥。Preferably, in step (4), the drying method is freeze-drying.

再一方面,本发明提供按照上述制备方法制备得到的基于咖啡豆的新型碳材料。In yet another aspect, the present invention provides a novel carbon material based on coffee beans prepared according to the above preparation method.

再一方面,本发明提供上述基于咖啡豆的新型碳材料在检测Pb2+和PPi中的应用。In yet another aspect, the present invention provides the application of the above-mentioned novel carbon material based on coffee beans in the detection of Pb 2+ and PPi.

再一方面,本发明提供一种快速检测Pb2+的方法,包括以下步骤:In another aspect, the present invention provides a method for rapidly detecting Pb 2+ , comprising the following steps:

S1、将上述制备方法得到的CQDs溶于超纯水中,得溶液D,将溶液D和超纯水混合后测试其荧光强度为F0S1, the CQDs obtained by the above preparation method are dissolved in ultrapure water to obtain solution D, and the fluorescence intensity of solution D and ultrapure water is mixed and tested to be F 0 ;

S2、将不同浓度的Pb2+溶液分别与溶液D混合,获得混合溶液,对混合溶液进行荧光测试,分别获得各混合溶液的荧光强度值F;S2. Mix different concentrations of Pb 2+ solutions with solution D respectively to obtain a mixed solution, perform a fluorescence test on the mixed solution, and obtain the fluorescence intensity value F of each mixed solution;

以Pb2+浓度为横坐标,荧光淬灭率即1-F/F0为纵坐标,进行线性拟合,获得回归方程y1=k1x1+b1,其中y1为荧光淬灭率,x1为Pb2+浓度,k1值为斜率,b1值为截距;Taking the concentration of Pb 2+ as the abscissa and the fluorescence quenching rate, namely 1-F/F 0 as the ordinate, perform linear fitting to obtain the regression equation y 1 =k 1 x 1 +b 1 , where y 1 is the fluorescence quenching rate, x 1 is the Pb 2+ concentration, k 1 is the slope, and b 1 is the intercept;

S3、将待测样品与溶液D混合,得混合溶液;测试所得混合溶液的荧光强度值,进而得到荧光淬灭率,代入步骤S2中的线性回归方程y1=k1x1+b1,得到Pb2+的浓度。S3. Mix the sample to be tested with solution D to obtain a mixed solution; test the fluorescence intensity value of the obtained mixed solution to obtain the fluorescence quenching rate, and substitute it into the linear regression equation y 1 =k 1 x 1 +b 1 in step S2, The concentration of Pb 2+ was obtained.

优选地,步骤S1中,所述溶液D的质量浓度为5~10mg/ml,溶液D和超纯水混合的比例为1:39。Preferably, in step S1, the mass concentration of the solution D is 5-10 mg/ml, and the mixing ratio of the solution D and the ultrapure water is 1:39.

优选地,步骤S2中,所述Pb2+溶液的浓度范围为12~260μM。Preferably, in step S2, the concentration range of the Pb 2+ solution is 12-260 μM.

优选地,步骤S2中,Pb2+溶液分别与溶液D以39:1的比例混合。Preferably, in step S2, the Pb 2+ solution is mixed with the solution D in a ratio of 39:1, respectively.

优选地,步骤S3中,所述待测样品和溶液D混合时的质量比为29~49:1,最优选为39:1。Preferably, in step S3, the mass ratio when the sample to be tested and the solution D are mixed is 29-49:1, most preferably 39:1.

最后,本发明提供一种快速检测PPi的方法,包括以下步骤:Finally, the present invention provides a method for rapidly detecting PPi, comprising the following steps:

S1、将上述制备方法得到的CQDs溶于超纯水中,得溶液D。S1. The CQDs obtained by the above preparation method are dissolved in ultrapure water to obtain solution D.

S2、将Pb2+溶液与溶液D混合,得混合溶液E,对混合溶液E进行荧光测试,获得的荧光强度值F0;将不同浓度的PPi加入到混合溶液E中,进行荧光测试,得荧光强度值F,以PPi浓度为横坐标,荧光增长率即F/F0-1为纵坐标,进行线性拟合,获得回归方程y2=k2x2+b2,其中y2为荧光增长率,x2为PPi的浓度,k2值为斜率,b2值为截距;S2. Mix the Pb 2+ solution with the solution D to obtain a mixed solution E, carry out a fluorescence test on the mixed solution E, and obtain the fluorescence intensity value F 0 ; add PPi of different concentrations into the mixed solution E, carry out a fluorescence test, and obtain The fluorescence intensity value F, with the concentration of PPi as the abscissa, and the fluorescence growth rate, namely F/F0-1, as the ordinate, perform linear fitting to obtain the regression equation y 2 =k 2 x 2 +b 2 , where y 2 is the fluorescence increase rate, x 2 is the concentration of PPi, k 2 is the slope, and b 2 is the intercept;

S3、将待测样品与Pb2+溶液、溶液D混合,得混合溶液,测试所得混合溶液的荧光强度值,代入步骤S2中的线性回归方程y2=k2x2+b2,得到PPi的浓度。S3. Mix the sample to be tested with Pb 2+ solution and solution D to obtain a mixed solution, test the fluorescence intensity value of the obtained mixed solution, and substitute it into the linear regression equation y 2 =k 2 x 2 +b 2 in step S2 to obtain PPi concentration.

优选地,步骤S1中,所述的溶液D的质量浓度为5~10mg/ml。Preferably, in step S1, the mass concentration of the solution D is 5-10 mg/ml.

优选地,步骤S2中,所述的Pb2+溶液浓度为12~260μM。Preferably, in step S2, the concentration of the Pb 2+ solution is 12-260 μM.

优选地,步骤S2中,所述的不同浓度的PPi浓度范围为37.5~125μM。Preferably, in step S2, the PPi concentration range of the different concentrations is 37.5-125 μM.

优选地,步骤S2中,Pb2+溶液与溶液D以39:1的比例混合。Preferably, in step S2, the Pb 2+ solution and the solution D are mixed in a ratio of 39:1.

优选地,步骤S3中,待测样品与Pb2+溶液、溶液D按照38:1:1的比例混合。Preferably, in step S3, the sample to be tested is mixed with the Pb 2+ solution and the solution D in a ratio of 38:1:1.

优选地,步骤S3中,所述Pb2+浓度为10mM。Preferably, in step S3, the Pb 2+ concentration is 10 mM.

本发明的有益效果为:The beneficial effects of the present invention are:

1.本发明基于该碳量子点“开-关”荧光效应用于Pb2+和PPi含量的检测方案,具有灵敏度高、选择性好、光谱干扰少、成本较低等优点,且该碳量子点是以咖啡豆为原料合成,不仅合成方案绿色环保,且生物相容性较好,具有用于生物成像的潜力。1. The present invention is used for the detection scheme of Pb 2+ and PPi content based on the "on-off" fluorescence effect of the carbon quantum dots, which has the advantages of high sensitivity, good selectivity, less spectral interference, and low cost, and the carbon quantum dots The point is synthesized from coffee beans, which is not only green and environmentally friendly, but also has good biocompatibility and has the potential for bioimaging.

2.本发明技术方案制备的碳量子点具有动力学和热力学性能优越、物理化学稳定性、水溶性良好、生物相容性好、对环境危害小、对铅离子灵敏度高等优势。2. The carbon quantum dots prepared by the technical solution of the present invention have the advantages of superior kinetic and thermodynamic properties, physical and chemical stability, good water solubility, good biocompatibility, little environmental harm, and high sensitivity to lead ions.

3.本发明以咖啡豆为原料,通过一步水热法合成的碳量子点作为荧光探针,合成绿色简单。3. In the present invention, coffee beans are used as raw materials, and carbon quantum dots synthesized by one-step hydrothermal method are used as fluorescent probes, and the synthesis is green and simple.

附图说明Description of drawings

图1不同实施例和对比例的产物CQDs检测Pb2+灵敏度的对比图;The comparison diagram of the sensitivity of the product CQDs of Fig. 1 different embodiment and comparative example to detect Pb 2+ ;

图2实施例1产物CQDs的FTIR图;The FTIR diagram of the product CQDs of Fig. 2 embodiment 1;

图3为CQDs的溶血率柱状图;Figure 3 is a histogram of the hemolysis rate of CQDs;

图4为预处理前CQDs检测Pb2+的选择性柱状图;Figure 4 is a histogram of the selectivity of CQDs to detect Pb 2+ before pretreatment;

图5为预处理后CQDs检测Pb2+的选择性柱状图;Figure 5 is a histogram of the selectivity of CQDs to detect Pb 2+ after pretreatment;

图6为CQDs的荧光强度变化与Pb2+浓度之间的关系图;Figure 6 is a graph showing the relationship between the change of fluorescence intensity of CQDs and the concentration of Pb 2+ ;

图7为CQDs荧光恢复的强度变化与PPi浓度之间的关系图;Figure 7 is a graph showing the relationship between the intensity change of CQDs fluorescence recovery and the concentration of PPi;

图8为CQDs检测PPi的选择性柱状图。Figure 8 is a bar graph of the selectivity of CQDs to detect PPi.

具体实施方式Detailed ways

以下非限制性实施例可以使本领域的普通技术人员更全面的理解本发明,但不以任何方式限制本发明。下述内容仅仅是对本申请要求保护的范围的示例性说明,本领域技术人员可以根据所公开的内容对本申请的发明作出多种改变和修饰,而其也应当属于本申请要求保护的范围之中。The following non-limiting examples may enable those of ordinary skill in the art to more fully understand the present invention, but do not limit the present invention in any way. The following content is only an exemplary description of the scope of protection claimed in the application, and those skilled in the art can make various changes and modifications to the invention of the application according to the disclosed content, and it should also belong to the scope of protection claimed in the application. .

下面以具体实施例的方式对本发明作进一步的说明。本发明实施例中所使用的各种化学试剂如无特殊说明均通过常规商业途径获得。The present invention will be further described below by way of specific embodiments. Various chemical reagents used in the examples of the present invention are obtained through conventional commercial channels unless otherwise specified.

下述实施例中,咖啡豆粉均由咖啡豆研磨得到。In the following examples, coffee bean powder is obtained by grinding coffee beans.

实施例1Example 1

1)将3g的咖啡豆粉溶解于30mL纯水中,再加入氢氧化钠7.2g(6mM),得到混合溶液A;1) Dissolve 3g of coffee bean powder in 30mL of pure water, then add 7.2g (6mM) of sodium hydroxide to obtain mixed solution A;

2)将溶液A转移到聚四氟乙烯内衬中,再装入不锈钢反应釜中在200℃下反应480min,得到溶液B;2) Transfer the solution A to the polytetrafluoroethylene lining, then load it into the stainless steel reactor and react for 480 min at 200° C. to obtain the solution B;

3)将溶液B转移到12000D的透析袋中,透析48h得到溶液C;3) Transfer solution B to a 12000D dialysis bag, and dialyze for 48h to obtain solution C;

4)将溶液C用0.22μm的有机系滤膜抽滤,接着在-60℃下冷冻4h,抽取真空干燥12h后,得到棕黑色粉末状CQDs,2~8℃下保存备用。4) The solution C was filtered through a 0.22 μm organic filter membrane, then frozen at -60°C for 4 hours, and vacuum-dried for 12 hours to obtain brown-black powdery CQDs, which were stored at 2-8°C for later use.

实施例2Example 2

与实施例1不同的是,添加2g的咖啡豆粉,其余皆相同。The difference from Example 1 is that 2 g of coffee bean powder was added, and the rest were the same.

实施例3Example 3

碳量子点的制备方法参照实例1,改变氢氧化钠的量,具体步骤如下:The preparation method of carbon quantum dots changes the amount of sodium hydroxide with reference to example 1, and the concrete steps are as follows:

与实施例1不同的是,加入氢氧化钠12g,其余皆相同。The difference from Example 1 is that 12 g of sodium hydroxide was added, and the rest were the same.

实施例4Example 4

与实施例1不同的是,将溶液A转移到聚四氟乙烯内衬中,再装入不锈钢反应釜中在150℃下反应480min,得到溶液B,其余皆相同。The difference from Example 1 is that solution A was transferred to a polytetrafluoroethylene liner, and then loaded into a stainless steel reactor to react at 150° C. for 480 min to obtain solution B, and the rest were the same.

实施例5Example 5

与实施例1不同的是,透析袋的规格为1000D,其余皆相同。Different from Example 1, the specification of the dialysis bag is 1000D, and the rest are the same.

对比例1Comparative Example 1

与实施例1不同的是,不添加氢氧化钠,其余皆相同。The difference from Example 1 is that no sodium hydroxide is added, and the rest are the same.

灵敏度测试:Sensitivity test:

以上实施例和对比例中的产物CQDs,均配制成10mg/mL的D溶液,将D溶液和纯水按照1:39的比例混合,测试初始荧光强度记为F0,再将D溶液和250μM的Pb2+溶液以1:39的比例混合,测试淬灭后的荧光强度,记为F。以F/F0的值为灵敏度的检测指标(图1),即F/F0的值越低,表明淬灭程度越高、灵敏度越高。可以看出,对比例1制备的CQDs实施效果较差。综合结果以实施例1的产物CQDs为后续检测例1和检测例2的检测材料。The product CQDs in the above examples and comparative examples were all prepared into 10 mg/mL D solution, the D solution and pure water were mixed in a ratio of 1:39, and the initial fluorescence intensity of the test was recorded as F 0 , and then the D solution and 250 μM The Pb 2+ solution was mixed at a ratio of 1:39, and the fluorescence intensity after quenching was measured, denoted as F. Taking the value of F/F 0 as the detection index of sensitivity (Fig. 1), that is, the lower the value of F/F 0 , the higher the degree of quenching and the higher the sensitivity. It can be seen that the implementation effect of the CQDs prepared in Comparative Example 1 is poor. Comprehensive results The product CQDs of Example 1 was used as the detection material of the subsequent detection example 1 and detection example 2.

CQDs检测Pb2+的选择性测试:Selectivity test for detection of Pb 2+ by CQDs:

将实验所涉及的各种金属离子的最终浓度设计为250μM进行选择性测试,可以看出Cu2+、Hg2+、Fe3+对Pb2+的检测有干扰,但以谷胱甘肽和抗坏血酸作为螯合剂和还原剂处理Cu2+、Hg2+、Fe3+后干扰消失,其中金属离子的最终浓度为50μM,谷胱甘肽的最终浓度为0.08mg/mL,抗坏血酸的最终浓度为0.5mg/mL。图4-5表明,CQDs对Pb2+的检测作用稳定不受影响,选择性较高。The final concentration of various metal ions involved in the experiment is designed to be 250 μM for selective testing. It can be seen that Cu 2+ , Hg 2+ , Fe 3+ interfere with the detection of Pb 2+ , but glutathione and Ascorbic acid was used as a chelating agent and a reducing agent to treat Cu 2+ , Hg 2+ , Fe 3+ and the interference disappeared. The final concentration of metal ions was 50 μM, the final concentration of glutathione was 0.08 mg/mL, and the final concentration of ascorbic acid was 0.5 mg/mL. Figures 4-5 show that the detection of Pb 2+ by CQDs is stable and unaffected, with high selectivity.

检测例1Test Example 1

利用本发明上述实施例1所得CQDs,以荧光光谱法用于检测铅离子含量,所述方法步骤如下:Utilize the CQDs obtained in the above-mentioned embodiment 1 of the present invention to detect lead ion content by fluorescence spectroscopy, and the method steps are as follows:

1)将粉末状CQDs溶于超纯水中,配置成10mg/mL的D溶液,将D溶液和纯水按照1:39的比例混合,测试其荧光强度为10100.5,记为F01) Dissolve the powdered CQDs in ultrapure water, configure it into a 10 mg/mL D solution, mix the D solution and pure water in a ratio of 1:39, and test its fluorescence intensity as 10100.5, denoted as F 0 ;

2)将浓度为12,35,55,86,110,130,170,210,260μM的Pb2+溶液分别与D溶液按照39:1的比例混合,分别获得混合溶液,对混合溶液进行荧光测试,获得各混合溶液的荧光强度值分别为9578.3,8856.2,8415.5,8171.5,6977.9,6860.2,5649.7,4660.6,3270.5,记为F;2) Mix Pb 2+ solutions with concentrations of 12, 35, 55, 86, 110, 130, 170, 210, and 260 μM with D solution in a ratio of 39:1, respectively, to obtain a mixed solution, and perform a fluorescence test on the mixed solution , the fluorescence intensity values obtained for each mixed solution are 9578.3, 8856.2, 8415.5, 8171.5, 6977.9, 6860.2, 5649.7, 4660.6, 3270.5, denoted as F;

以Pb2+浓度为横坐标,荧光淬灭率(1-F/F0)为纵坐标,进行线性拟合,获得回归方程y1=0.00241x1-0.0321,其中y1为荧光淬灭率,x1为Pb2+的浓度;Taking the concentration of Pb 2+ as the abscissa and the fluorescence quenching rate (1-F/F 0 ) as the ordinate, perform linear fitting to obtain the regression equation y 1 =0.00241x 1 -0.0321, where y 1 is the fluorescence quenching rate , x 1 is the concentration of Pb 2+ ;

3)将待测含一定浓度铅离子(50μM)的湖水样本与D溶液按照39:1的比例混合,获得混合溶液;进行荧光测试,得到的荧光强度值代入线性回归方程y1=0.00241x1-0.0321,计算得到铅离子的平均浓度为51.7μM(n=3),平均回收率为103.4%(n=3)。所用荧光测试中荧光的激发波长为370nm。3) Mix the lake water sample containing a certain concentration of lead ions (50 μM) and the D solution according to the ratio of 39:1 to obtain a mixed solution; carry out the fluorescence test, and substitute the obtained fluorescence intensity value into the linear regression equation y 1 =0.00241× 1 -0.0321, the average concentration of lead ions was calculated to be 51.7 μM (n=3), and the average recovery rate was 103.4% (n=3). The excitation wavelength of fluorescence in the fluorescence assay used was 370 nm.

检测例2Test example 2

利用本发明上述实施例1所得CQDs,再以荧光光谱法用于检测PPi含量,所述方法步骤如下:Utilize the CQDs obtained in the above-mentioned embodiment 1 of the present invention, and then use fluorescence spectroscopy to detect the PPi content, and the method steps are as follows:

1)将粉末状CQDs溶于超纯水中,配置成10mg/mL的D溶液;1) Dissolve the powdered CQDs in ultrapure water to prepare a 10 mg/mL D solution;

2)将250μM的Pb2+溶液与D溶液按照39:1的比例混合,获得混合溶液E,对混合溶液E进行荧光测试,获得的荧光强度值为2070.2,记为F0;将37.5,50,62.5,75,87.5,100,112.5,125μM的PPi溶液和溶液E按照1:39的比例混合,进行荧光测试,获得的荧光强度值分别为2243.3,2733.5,3227.4,3676.8,4360.9,4866.4,5358.7,5679.2,记为F,以PPi浓度为横坐标,荧光增长率(F/F0-1)为纵坐标,进行线性拟合,获得回归方程y2=0.02051x2+0.7250,其中y2为荧光增长率,x2为PPi的浓度;2) Mix the 250 μM Pb 2+ solution with the D solution in a ratio of 39:1 to obtain a mixed solution E, carry out a fluorescence test on the mixed solution E, and the obtained fluorescence intensity value is 2070.2, denoted as F 0 ; , 62.5, 75, 87.5, 100, 112.5, 125 μM of PPi solution and solution E were mixed in a ratio of 1:39, and the fluorescence intensity was measured. , 5679.2, denoted as F, take the PPi concentration as the abscissa and the fluorescence growth rate (F/F 0 -1) as the ordinate, perform linear fitting to obtain the regression equation y 2 =0.02051x 2 +0.7250, where y 2 is Fluorescence growth rate, x 2 is the concentration of PPi;

3)将待测含PPi的溶液(50μM)与Pb2+溶液(10mM)、溶液D按照38:1:1的比例混合,获得PPi-Pb-CQDs混合溶液;进行荧光测试,得到的荧光强度值,代入线性回归方程y2=0.02051x2+0.7250,计算得到PPi的平均浓度为50.6μM,平均回收率为101.2%。3) Mix the PPi-containing solution (50 μM) to be tested with Pb 2+ solution (10 mM) and solution D in a ratio of 38:1:1 to obtain a PPi-Pb-CQDs mixed solution; perform a fluorescence test to obtain the fluorescence intensity value, substituted into the linear regression equation y 2 =0.02051× 2 +0.7250, the average concentration of PPi was calculated to be 50.6 μM, and the average recovery rate was 101.2%.

可以看出,本发明方法的测试结果准确、可靠,且测试步骤方便快速。It can be seen that the test results of the method of the present invention are accurate and reliable, and the test steps are convenient and fast.

以上所述仅为本发明的较佳实施例而已,并不用以限制本发明,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present invention shall be included in the scope of the present invention. within the scope of protection.

Claims (10)

1. A preparation method of a novel carbon material based on coffee beans is characterized by comprising the following steps:
(1) dissolving coffee bean powder and sodium hydroxide in water to obtain a solution A;
(2) reacting the solution A at a high temperature to obtain a solution B;
(3) dialyzing the solution B to obtain a solution C;
(4) filtering and drying the solution C to obtain CQDs.
2. The production method according to claim 1, wherein in the step (1), the mass ratio of the coffee bean powder to the sodium hydroxide is 2-4:7.2-16.8, and the mass ratio of the coffee bean powder to the water is 1: 50-200.
3. The method as claimed in claim 1, wherein the step (2) is performed in a polytetrafluoroethylene lining in the reaction stainless steel reactor, the temperature of the reaction is 150 ℃ and 200 ℃, and the reaction time is 240 ℃ and 480 min.
4. The method as claimed in claim 1, wherein the dialysis in step (3) is carried out in a dialysis bag of pure water, 1000-12000D for a dialysis time of 24-72 hours.
5. A novel coffee bean-based carbon material produced by the production method according to any one of claims 1 to 4.
6. Use of the novel coffee bean-based carbon material according to claim 5 for detecting Pb2+And use in PPi.
7. Rapid detection Pb2+The method is characterized by comprising the following steps:
s1, dissolving CQDs prepared by the preparation method of any one of claims 1 to 4 in ultrapure water to obtain solution D, mixing the solution D and ultrapure water, and testing the fluorescence intensity of the solution D as F0
S2, mixing Pb with different concentrations2+Respectively mixing the solution with the solution D to obtain mixed solutions, and performing fluorescence test on the mixed solutions to respectively obtain fluorescence intensity values F of the mixed solutions;
with Pb2+Concentration is abscissa, and fluorescence quenching rate is 1-F/F0Linear fitting is performed for the ordinate to obtain a regression equation y1=k1x1+b1Wherein y is1As fluorescence quenching rate, x1Is Pb2+Concentration, k1The value is the slope, b1The value is the intercept;
s3, mixing the sample to be detected with the solution D to obtain a mixed solution; testing the fluorescence intensity value of the obtained mixed solution to further obtain the fluorescence quenching rate, and substituting the fluorescence quenching rate into the linear regression equation y in the step S21=k1x1+b1Obtaining Pb2+The concentration of (c).
8. The method according to claim 7, wherein in the step S1, the mass concentration of the solution D is 5-10 mg/ml, and the mixing ratio of the solution D and the ultrapure water is 1: 39; in step S2, Pb is2+The concentration range of the solution is 12-260 mu M; in step S2, Pb2+Mixing the solution with the solution D at a ratio of 39: 1; in step S3, the sample and the solution to be testedD, mass ratio of the mixed materials is 29-49: 1.
9. a method for rapidly detecting PPi is characterized by comprising the following steps:
s1, dissolving CQDs prepared by the preparation method of any one of claims 1 to 4 in ultrapure water to obtain solution D;
s2, adding Pb2+Mixing the solution with the solution D to obtain a mixed solution E, and performing fluorescence test on the mixed solution E to obtain a fluorescence intensity value F0(ii) a Adding PPi with different concentrations into the mixed solution E, performing fluorescence test to obtain fluorescence intensity value F, and taking the concentration of PPi as abscissa, wherein the fluorescence growth rate is F/F0-1 is a vertical coordinate, linear fitting is carried out to obtain a regression equation y2=k2x2+b2Wherein y is2As the rate of increase in fluorescence, x2Is the concentration of PPi, k2The value is the slope, b2The value is the intercept;
s3, mixing the sample to be tested with Pb2+Mixing the solution and the solution D to obtain a mixed solution, testing the fluorescence intensity value of the mixed solution, and substituting the fluorescence intensity value into the linear regression equation y in the step S22=k2x2+b2The concentration of PPi was obtained.
10. The method according to claim 9, wherein in step S1, the mass concentration of solution D is 5-10 mg/ml; in step S2, Pb is2+The concentration of the solution is 12-260 mu M; in step S2, the concentration range of the PPi with different concentrations is 37.5-125 μ M; in step S2, Pb2+Mixing the solution with the solution D at a ratio of 39: 1; in step S3, the sample to be tested and Pb2+Mixing the solution and the solution D according to the ratio of 38:1: 1; in step S3, Pb is2+Is 10 mM.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115125001A (en) * 2022-08-23 2022-09-30 济南大学 Preparation method of green luminescent carbon dots
CN118703208A (en) * 2024-06-28 2024-09-27 山西大学 A method for preparing a fluorescent probe and its application in detecting tetracycline and pyrophosphate ions

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106629658A (en) * 2016-11-12 2017-05-10 兰州大学 Preparation method of fluorescent carbon quantum dot
CN108424769A (en) * 2017-02-15 2018-08-21 东北林业大学 A kind of environment-friendly preparation method thereof of bio-imaging carbon dots

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106629658A (en) * 2016-11-12 2017-05-10 兰州大学 Preparation method of fluorescent carbon quantum dot
CN108424769A (en) * 2017-02-15 2018-08-21 东北林业大学 A kind of environment-friendly preparation method thereof of bio-imaging carbon dots

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
YIFANG GAO等: "One-step synthesis of a dual-emitting carbon dot-based ratiometric fluorescent probe for the visual assay of Pb2+ and PPi and development of a paper sensor", vol. 7, pages 5502 - 5509 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115125001A (en) * 2022-08-23 2022-09-30 济南大学 Preparation method of green luminescent carbon dots
CN115125001B (en) * 2022-08-23 2023-04-28 济南大学 A kind of preparation method of green luminescent carbon dot
CN118703208A (en) * 2024-06-28 2024-09-27 山西大学 A method for preparing a fluorescent probe and its application in detecting tetracycline and pyrophosphate ions

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