CN116855247A - Preparation, processing method and application of carbon nanodots - Google Patents
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Abstract
Description
技术领域Technical field
本发明涉及一种碳纳米点的制备、处理方法及应用,属于纳米材料技术领域。The invention relates to a preparation, processing method and application of carbon nanodots, and belongs to the technical field of nanomaterials.
背景技术Background technique
双模式检测(Dual-mode detection)通过两种不同的检测方法同时对样品进行检测,提供的结果相互认证,提高了测量的可靠性和准确性。3,3',5,5'-四甲基联苯胺(TMB)是双模式检测中常用的显色底物,在检测过程中被氧化,生成的产物(oxTMB或diimineoxTMB)在可见光区域显示出较强的吸光度。然而,研究人员发现,氧化产物在很多工作条件下都不稳定,产物颜色在反应完成几分钟后即变淡甚至消失(ChemPlusChem.87(2022)e202200090;J.Histochem.Cytochem.47(1999)265–272)。这种现象会严重影响检测的灵敏度、准确度和精度,为了解决这个问题,分析工作者做了很多尝试,比如,Li等人(ACSOmega.4(2019)5459–5470)在反应体系中加入适量的烷基咪唑四氟硼酸根离子液体和表面活性剂十二烷基硫酸钠,两者形成胶束后,TMB氧化产物在胶束中能比较稳定地存在。但是,在反应体系中引入与测量无关的化学物质(如上述的烷基咪唑四氟硼酸根离子液体和表面活性剂十二烷基硫酸钠)通常会使体系的性质更加复杂,可控性变差,而且,本例中引入的化学物质都有一定的细胞毒性,不适合于生物体中成分的检测。Dual-mode detection uses two different detection methods to detect samples at the same time, providing results that are mutually authenticated, improving the reliability and accuracy of measurement. 3,3',5,5'-Tetramethylbenzidine (TMB) is a commonly used chromogenic substrate in dual-mode detection. It is oxidized during the detection process, and the generated product (oxTMB or diimineoxTMB) displays in the visible light region. Strong absorbance. However, researchers found that the oxidation product is unstable under many working conditions, and the color of the product becomes lighter or even disappears a few minutes after the reaction is completed (ChemPlusChem.87(2022)e202200090; J.Histochem.Cytochem.47(1999)265 –272). This phenomenon will seriously affect the sensitivity, accuracy and precision of detection. In order to solve this problem, analysts have made many attempts. For example, Li et al. (ACSOmega.4 (2019) 5459–5470) added an appropriate amount of After the alkyl imidazole tetrafluoroborate ionic liquid and the surfactant sodium dodecyl sulfate form micelles, the TMB oxidation product can exist relatively stably in the micelles. However, the introduction of chemicals unrelated to measurement (such as the above-mentioned alkyl imidazole tetrafluoroborate ionic liquid and surfactant sodium dodecyl sulfate) into the reaction system usually makes the properties of the system more complex and the controllability becomes worse. Poor, and the chemicals introduced in this example all have certain cytotoxicity and are not suitable for the detection of components in organisms.
碳纳米点(Carbon Dots,CDs)是一类直径小于10nm的碳纳米颗粒,由于量子限域效应和表面/边缘态效应,CDs广泛应用于双模式检测中。CDs具有丰富的表面官能团,如多芳环结构、羧基、羟基、氨基和环氧化物等。因此,作为双模式检测的光致发光探针,CDs容易与另一种探针相互作用。例如,TMB很容易吸附在CDs表面(Carbon.179(2021)692–700),且吸附之后溶液的紫外吸收强度显著降低(J.Mol.Struct.1268(2022)133723)。另一方面,尽管CDs的表面官能团的性质可以通过氧化、酸化和化学反应功能化来改变,但是目前鲜有对CDs表面基团进行改性并应用于双模式检测的报道。由于基于TMB和CDs的双模式检测在分析科学中应用广泛,对CDs表面进行改性来提高检测性能具有良好的应用价值。Carbon Dots (CDs) are a type of carbon nanoparticles with a diameter less than 10 nm. Due to the quantum confinement effect and surface/edge state effect, CDs are widely used in dual-mode detection. CDs have abundant surface functional groups, such as polyaromatic ring structures, carboxyl groups, hydroxyl groups, amino groups, and epoxides. Therefore, as photoluminescent probes for dual-mode detection, CDs easily interact with another probe. For example, TMB is easily adsorbed on the surface of CDs (Carbon. 179 (2021) 692–700), and the UV absorption intensity of the solution is significantly reduced after adsorption (J. Mol. Struct. 1268 (2022) 133723). On the other hand, although the properties of the surface functional groups of CDs can be changed through oxidation, acidification, and chemical reaction functionalization, there are currently few reports on the modification of CDs surface groups and their application in dual-mode detection. Since dual-mode detection based on TMB and CDs is widely used in analytical science, modifying the surface of CDs to improve detection performance has good application value.
发明内容Contents of the invention
本发明解决的技术问题在于提供一种碳纳米点的制备、处理方法,发明人发现,采用本方法制备以及处理的碳纳米点与TMB检测体系混合之后,不仅没有对TMB或氧化之后的oxTMB以及diimine oxTMB产生吸附,而且,能使TMB的氧化产物在溶液中稳定存在。有鉴于此,本发明提供一种碳纳米点的制备、处理方法,其特征是,包括以下步骤:The technical problem solved by the present invention is to provide a method for preparing and processing carbon nanodots. The inventor found that after the carbon nanodots prepared and processed by this method are mixed with the TMB detection system, not only are there no effects on TMB or oxTMB after oxidation, but also Diimine oxTMB produces adsorption and can stabilize the oxidation products of TMB in the solution. In view of this, the present invention provides a method for preparing and processing carbon nanodots, which is characterized by including the following steps:
(1)将15g芒果肉切碎后与10mL三次蒸馏水混合,170℃高温反应后,9000转/分离心10min去除沉淀,再用0.45μm滤膜滤除大颗粒物质,滤液70℃加热烘干得碳纳米点;(1) Chop 15g of mango pulp and mix it with 10mL of triple distilled water. After high temperature reaction at 170℃, centrifuge at 9000 rpm for 10min to remove the precipitate. Then use a 0.45μm filter membrane to filter out large particulate matter. The filtrate is heated and dried at 70℃ to obtain carbon nanodots;
(2)称取4mg碳纳米点分散于500μL NaOH溶液中,加热到70℃后通入臭氧进行处理,用截留分子量为50kDa的超滤膜离心超滤后取滤液,将滤液用截留分子量为3kDa的超滤膜离心超滤后取上层碳纳米点。(2) Weigh 4 mg of carbon nanodots and disperse them in 500 μL of NaOH solution. Heat to 70°C and add ozone for treatment. Use an ultrafiltration membrane with a molecular weight cutoff of 50kDa to centrifuge and ultrafiltrate and take the filtrate. Use a filter with a molecular weight cutoff of 3kDa to take the filtrate. After centrifugal ultrafiltration of the ultrafiltration membrane, the upper layer of carbon nanodots is taken.
优选的,步骤(1)中所述高温反应时间为3~7h。Preferably, the high-temperature reaction time in step (1) is 3 to 7 hours.
优选的,步骤(2)中所述NaOH溶液中NaOH浓度为50~200mM。Preferably, the NaOH concentration in the NaOH solution described in step (2) is 50-200mM.
优选的,步骤(2)中所述通入臭氧处理时间为1.5~3.5h。Preferably, the ozone treatment time described in step (2) is 1.5 to 3.5 hours.
优选的,步骤(2)中所述通入臭氧的流速为4.0~8.0mL/min。Preferably, the flow rate of ozone introduced in step (2) is 4.0-8.0 mL/min.
本发明还提供一种比率荧光-比色法双模式检测方法,探针由碳纳米点和3,3',5,5'-四甲基联苯胺构成,比率荧光法测量时,分别以360nm和500nm电磁波激发测量溶液,测得探针450nm和540nm处发射强度分别为I450和I540,以荧光强度的比率I450/I540对待测样品进行定量分析;比色法测量时,以测量溶液450nm处的紫外吸光度A450进行定量分析。The invention also provides a ratiometric fluorescence-colorimetric dual-mode detection method. The probe is composed of carbon nanodots and 3,3',5,5'-tetramethylbenzidine. When measured by the ratiometric fluorescence method, the probe is measured at 360 nm. and 500nm electromagnetic wave to excite the measurement solution. The measured emission intensity of the probe at 450nm and 540nm is I 450 and I 540 respectively. The sample to be measured is quantitatively analyzed with the ratio of fluorescence intensity I 450 /I 540 ; when measuring by colorimetric method, The UV absorbance A 450 of the solution at 450 nm was used for quantitative analysis.
优选的,测量溶液中碳纳米点与3,3',5,5'-四甲基联苯胺的质量浓度之比为(8~32):1Preferably, the ratio of the mass concentrations of carbon nanodots and 3,3',5,5'-tetramethylbenzidine in the measured solution is (8-32): 1
优选的,所述测量溶液的pH值为1~2。Preferably, the pH value of the measurement solution is 1-2.
采用本发明提供的碳纳米点构建的比率荧光-比色法双模式检测探针用于肌氨酸检测时,检测限分别为0.046和0.0014μM,远远优于现有的技术。When the ratiometric fluorescence-colorimetric dual-mode detection probe constructed using the carbon nanodots provided by the invention is used for sarcosine detection, the detection limits are 0.046 and 0.0014 μM respectively, which is far superior to the existing technology.
附图说明Description of the drawings
图1CDs的透射电镜图。Figure 1 TEM image of CDs.
图2CDs粒径分布图。Figure 2 CDs particle size distribution chart.
图3臭氧处理之前的CDs XPS能谱图。Figure 3 XPS spectrum of CDs before ozone treatment.
图4臭氧处理之后的CDs XPS能谱图。Figure 4 XPS spectrum of CDs after ozone treatment.
图5臭氧处理之前CDs的荧光光谱图。Figure 5 Fluorescence spectra of CDs before ozone treatment.
图6臭氧处理之后CDs荧光发射光谱图。Figure 6 Fluorescence emission spectrum of CDs after ozone treatment.
图7(A)测量体系1不同时间的紫外吸收光谱图;(B)对应的吸光度随时间的变化曲线。Figure 7 (A) UV absorption spectra of measurement system 1 at different times; (B) Corresponding absorbance change curve with time.
图8(A)测量体系2不同时间的紫外吸收光谱图;(B)对应的吸光度随时间的变化曲线。Figure 8 (A) Measurement system 2 UV absorption spectra at different times; (B) Corresponding absorbance change curve with time.
图9(A)测量体系3不同时间的紫外吸收光谱图;(B)对应的吸光度随时间的变化曲线。Figure 9 (A) UV absorption spectra of measurement system 3 at different times; (B) Corresponding absorbance change curve with time.
图10(A)360nm激发时系统对不同浓度肌氨酸的荧光响应;(B)500nm激发时系统对不同浓度肌氨酸的荧光响应;(C)对应的比率荧光线性关系图。Figure 10 (A) Fluorescence response of the system to different concentrations of sarcosine when excited at 360nm; (B) Fluorescence response of the system to different concentrations of sarcosine when excited at 500nm; (C) Corresponding ratio fluorescence linear relationship diagram.
图11(A)系统对不同浓度肌氨酸的比色法响应;(B)对应的线性关系图。Figure 11 (A) Colorimetric response of the system to different concentrations of sarcosine; (B) Corresponding linear relationship graph.
具体实施方式Detailed ways
本发明提供一种碳纳米点的制备、处理方法,包括以下两个步骤:The invention provides a method for preparing and processing carbon nanodots, which includes the following two steps:
(1)将15g芒果肉切碎后与10mL三次蒸馏水混合,170℃高温反应后,9000转/分离心10min去除沉淀,再用0.45μm滤膜滤除大颗粒物质,滤液70℃加热烘干得碳纳米点;(1) Chop 15g of mango pulp and mix it with 10mL of triple distilled water. After high temperature reaction at 170℃, centrifuge at 9000 rpm for 10min to remove the precipitate. Then use a 0.45μm filter membrane to filter out large particulate matter. The filtrate is heated and dried at 70℃ to obtain carbon nanodots;
(2)称取4mg碳纳米点分散于500μL NaOH溶液中,加热到70℃后通入臭氧进行处理,用截留分子量为50kDa的超滤膜离心超滤后取滤液,将滤液用截留分子量为3kDa的超滤膜离心超滤后取上层碳纳米点。(2) Weigh 4 mg of carbon nanodots and disperse them in 500 μL of NaOH solution. Heat to 70°C and add ozone for treatment. Use an ultrafiltration membrane with a molecular weight cutoff of 50kDa to centrifuge and ultrafiltrate and take the filtrate. Use a filter with a molecular weight cutoff of 3kDa to take the filtrate. After centrifugal ultrafiltration of the ultrafiltration membrane, the upper layer of carbon nanodots is taken.
其中,步骤(1)中所述高温反应时间为3~7h;步骤(2)中所述NaOH溶液中NaOH浓度为50~200mM,所述通入臭氧处理时间为1.5~3.5h,所述通入臭氧的流速为4.0~8.0mL/min。Wherein, the high-temperature reaction time in step (1) is 3-7h; the NaOH concentration in the NaOH solution in step (2) is 50-200mM, the ozone treatment time is 1.5-3.5h, and the ozone treatment time is 1.5-3.5h. The flow rate of ozone is 4.0~8.0mL/min.
另外,本发明还提供一种比率荧光-比色法双模式检测方法,探针由碳纳米点和3,3',5,5'-四甲基联苯胺构成,比率荧光法测量时,分别以360nm和500nm电磁波激发测量溶液,测得探针450nm和540nm处发射强度分别为I450和I540,以荧光强度的比率I450/I540对待测样品进行定量分析;比色法测量时,以测量溶液450nm处的紫外吸光度A450进行定量分析。In addition, the present invention also provides a ratiometric fluorescence-colorimetric dual-mode detection method. The probe is composed of carbon nanodots and 3,3',5,5'-tetramethylbenzidine. When measured by the ratiometric fluorescence method, respectively The measurement solution is excited by electromagnetic waves of 360nm and 500nm, and the emission intensities of the probe at 450nm and 540nm are measured to be I 450 and I 540 respectively. The sample to be tested is quantitatively analyzed with the ratio of fluorescence intensity I 450 /I 540 ; when measuring by colorimetry, Quantitative analysis was performed by measuring the UV absorbance A 450 of the solution at 450 nm.
测量溶液中碳纳米点与3,3',5,5'-四甲基联苯胺的质量浓度之比为(8~32):1;所述测量溶液的pH值为1~2。The ratio of the mass concentrations of carbon nanodots to 3,3',5,5'-tetramethylbenzidine in the measurement solution is (8-32):1; the pH value of the measurement solution is 1-2.
为进一步理解本发明,下面结合实施例对本发明提供的一种碳纳米点的制备、处理方法及应用进行详细说明,本发明的保护范围不受以下实施例的限制。In order to further understand the present invention, the preparation, processing method and application of the carbon nanodots provided by the present invention will be described in detail below with reference to the examples. The protection scope of the present invention is not limited by the following examples.
下属实施例中所述实验方法,如无特殊说明,均为常规方法;所述试剂和材料,如无特殊说明,均可从商业途径购得。The experimental methods described in the following examples, unless otherwise specified, are all conventional methods; the reagents and materials, unless otherwise specified, can be purchased from commercial sources.
实施例1:碳纳米点的制备Example 1: Preparation of carbon nanodots
将超市购得的成熟芒果外皮剥下,去除芒果核,将芒果肉切成约5mm×5mm的小粒,放入70℃的真空干燥箱中恒温至恒重。取15.0g芒果肉放入50mL聚四氟乙烯高压反应釜内胆(西安仪表厂,西安),加入10mL三次蒸馏水,拧紧高压反应釜,放入烘箱加热至170℃,反应3h后自然冷却至室温。用药匙取出内容物,纱布过滤。将滤液加入离心管去除沉淀,9000转/分离心10min后取上清液,用0.45μM滤膜(九鼎高科,北京)过滤上清液,滤液70℃加热烘干得到CDs产物。Peel off the skin of ripe mangoes purchased from the supermarket, remove the mango core, cut the mango flesh into small pieces of about 5 mm × 5 mm, and place them in a vacuum drying oven at 70°C at constant temperature until constant weight. Take 15.0g of mango pulp and put it into the inner tank of a 50mL polytetrafluoroethylene high-pressure reactor (Xi'an Instrument Factory, Xi'an), add 10mL of triple distilled water, tighten the high-pressure reactor, put it in an oven and heat it to 170°C, react for 3 hours and then naturally cool to room temperature. . Remove the contents with a medicine spoon and filter with gauze. Add the filtrate into a centrifuge tube to remove the precipitate, centrifuge at 9000 rpm for 10 min, take the supernatant, filter the supernatant with a 0.45 μM filter membrane (Jiuding High-tech, Beijing), and heat and dry the filtrate at 70°C to obtain the CDs product.
实施例2:碳纳米点的臭氧处理Example 2: Ozone treatment of carbon nanodots
称取4mg碳纳米点分散于500μL 50mM NaOH溶液中,将溶液装入2mL聚丙烯离心管,置于水浴70℃水浴中,开启GN-S2S臭氧发生器(安泽电子、安徽省),将产生的臭氧通入碳纳米点溶液中,流速为4.0mL/min。处理2h后,在14000转/分下进行超滤处理,超滤分两步进行,先用截留分子量为50kDa的超滤膜离心超滤后取滤液,再将滤液用截留分子量为3kDa的超滤膜离心超滤后取上层碳纳米点。Weigh 4 mg of carbon nanodots and disperse them in 500 μL of 50 mM NaOH solution. Put the solution into a 2 mL polypropylene centrifuge tube, place it in a 70°C water bath, and turn on the GN-S2S ozone generator (Anze Electronics, Anhui Province) to generate ozone was passed into the carbon nanodot solution at a flow rate of 4.0 mL/min. After treatment for 2 hours, perform ultrafiltration at 14,000 rpm. Ultrafiltration is performed in two steps. First, use an ultrafiltration membrane with a molecular weight cutoff of 50kDa to centrifuge and ultrafiltrate, then take the filtrate, and then filter the filtrate with an ultrafiltration membrane with a molecular weight cutoff of 3kDa. After membrane centrifugation and ultrafiltration, the upper layer of carbon nanodots was collected.
实施例3:碳纳米点的透射电子显微镜表征Example 3: Transmission electron microscopy characterization of carbon nanodots
碳纳米点的形貌由Talos F200S透射电子显微镜(TEM,赛默飞世尔科技有限公司,美国)测量,测试前将CDs产物溶于三次蒸馏水,超声处理20min后滴在超薄碳膜上,在室温下干燥过夜后进行分析。TEM的结果显示,CDs呈球形(图1),由粒径分布图可知(图2),其粒径在4~11nm间,平均粒径7.5nm。The morphology of carbon nanodots was measured by a Talos F200S transmission electron microscope (TEM, Thermo Fisher Scientific Co., Ltd., USA). Before the test, the CDs product was dissolved in triple distilled water, treated with ultrasonic for 20 min, and then dropped on the ultra-thin carbon film. Analysis was performed after drying overnight at room temperature. The TEM results show that CDs are spherical (Figure 1). From the particle size distribution diagram (Figure 2), the particle size ranges from 4 to 11 nm, with an average particle size of 7.5 nm.
实施例4:碳纳米点的X射线光电子能谱表征Example 4: X-ray photoelectron spectroscopy characterization of carbon nanodots
碳纳米点的X射线光电子能谱(XPS)用ESCALAB 250Xi X射线光电子能谱仪(赛默飞世尔科技有限公司,美国)表征。臭氧处理之前和处理之后的CDs的XPS能谱图分别见图3和图4。两个谱图C1s谱中284.8、286.4、287.9以及289.3eV处出现了四个峰,分别对应C-C或C-H(C1)、C-O(C2)、C=O或O-C-O(C3)以及O-C=O(C4)。臭氧处理之后,C1的含量增加,从33.3%增加到39.3%,而C2的含量从51.2%增加到46.5%,表明CDs表面有一小部分羟基被氧化为C=O或O-C-O;此外,结果显示CDs表面对应羧基数量的C4含量下降,说明臭氧处理导致碳纳米点表面含氧官能团发生分解。X-ray photoelectron spectroscopy (XPS) of carbon nanodots was characterized using an ESCALAB 250Xi X-ray photoelectron spectrometer (Thermo Fisher Scientific, Inc., USA). The XPS spectra of CDs before and after ozone treatment are shown in Figures 3 and 4 respectively. In the two spectra C1s spectrum, four peaks appeared at 284.8, 286.4, 287.9 and 289.3eV, corresponding to C-C or C-H(C1), C-O(C2), C=O or O-C-O(C3) and O-C=O(C4 ). After ozone treatment, the content of C1 increased from 33.3% to 39.3%, while the content of C2 increased from 51.2% to 46.5%, indicating that a small part of the hydroxyl groups on the surface of CDs were oxidized to C=O or O-C-O; in addition, the results showed that CDs The C4 content corresponding to the number of carboxyl groups on the surface decreases, indicating that ozone treatment causes the decomposition of oxygen-containing functional groups on the surface of carbon nanodots.
实施例5:碳纳米点的荧光光谱表征Example 5: Fluorescence spectrum characterization of carbon nanodots
荧光性质用FS5荧光光谱仪(英国爱丁堡仪器有限公司,英国)进行研究,将CDs溶于三次蒸馏水,激发波长范围为250nm~550nm,发射波长范围为300nm~700nm,入射狭缝和出射狭缝均为5nm。实验结果(图5、图6)显示,臭氧处理前后CDs的荧光发射光谱波长没有发生明显变化,峰的形状极为相似,不同的是处理之后发射强度明显提高。上述现象说明臭氧处理之后CDs表面的晶格缺陷增加,也说明臭氧处理之后的CDs用于荧光探针时,检测灵敏度将大大提高。The fluorescence properties were studied using a FS5 fluorescence spectrometer (Edinburgh Instruments Ltd., UK). CDs were dissolved in triple distilled water. The excitation wavelength range was 250 nm to 550 nm, and the emission wavelength range was 300 nm to 700 nm. Both the incident slit and the exit slit were 5nm. The experimental results (Figure 5 and Figure 6) show that the wavelength of the fluorescence emission spectrum of CDs does not change significantly before and after ozone treatment, and the shapes of the peaks are very similar. The difference is that the emission intensity increases significantly after treatment. The above phenomenon shows that the lattice defects on the surface of CDs increase after ozone treatment. It also shows that when CDs after ozone treatment are used as fluorescent probes, the detection sensitivity will be greatly improved.
实施例6:臭氧处理对双模式检测性能的影响Example 6: Effect of ozone treatment on dual-mode detection performance
本实施例以肌氨酸的检测为例,采用CDs为荧光探针,3,3',5,5'-四甲基联苯胺(TMB)为比色探针,说明本发明合成、处理的CDs的性能。This example takes the detection of sarcosine as an example, using CDs as the fluorescent probe and 3,3',5,5'-tetramethylbenzidine (TMB) as the colorimetric probe to illustrate the synthesis and processing of the present invention. Performance of CDs.
CDs的合成:步骤同实施例1,不同之处在于,合成时烘箱加热至170℃,反应7h后自然冷却至室温,得本实施例的初始CDs。Synthesis of CDs: The steps are the same as in Example 1, except that during synthesis, the oven is heated to 170°C, and after 7 hours of reaction, it is naturally cooled to room temperature to obtain the initial CDs of this example.
对于本实施例中所用的未经臭氧处理的CDs,需要对得到的初始CDs在14000转/分下进行超滤处理,超滤分两步进行,先用截留分子量为50kDa的超滤膜离心超滤后取滤液,再将滤液用截留分子量为3kDa的超滤膜离心超滤后取上层碳纳米点。For the CDs without ozone treatment used in this example, the obtained initial CDs need to be subjected to ultrafiltration at 14,000 rpm. The ultrafiltration is performed in two steps. First, use an ultrafiltration membrane with a molecular weight cutoff of 50kDa, centrifuge and ultrasonic. After filtration, take the filtrate, centrifuge and ultrafiltrate the filtrate with an ultrafiltration membrane with a molecular weight cutoff of 3 kDa, and then take the upper layer of carbon nanodots.
对于本实施例中所用的臭氧处理的CDs,用臭氧对初始CDs进行处理,步骤同实施例2,不同之处在于,NaOH溶液中NaOH浓度为200mM,臭氧处理时,流速为8.0mL/min,处理时间为1h。For the ozone-treated CDs used in this example, the initial CDs were treated with ozone. The steps were the same as in Example 2. The difference was that the NaOH concentration in the NaOH solution was 200mM. During ozone treatment, the flow rate was 8.0mL/min. The processing time is 1h.
测量体系1:将150μL 10μM肌氨酸溶液(溶于50mM磷酸盐缓冲溶液,pH 7.4)和20μL20U/mL的肌氨酸氧化酶溶液混合,在37℃孵育10min后冷却至室温,然后加入10μL2mM的TMB溶液和5μL 30U/mL辣根过氧化酶溶液,室温避光孵育5min后加入5M盐酸调节pH值为1.0,终止反应。Measurement system 1: Mix 150 μL of 10 μM sarcosine solution (dissolved in 50 mM phosphate buffer solution, pH 7.4) and 20 μL of 20 U/mL sarcosine oxidase solution, incubate at 37°C for 10 min, cool to room temperature, and then add 10 μL of 2mM sarcosine oxidase solution. TMB solution and 5 μL of 30 U/mL horseradish peroxidase solution were incubated at room temperature for 5 min in the dark, then 5 M hydrochloric acid was added to adjust the pH to 1.0 to terminate the reaction.
测量体系2:向测量体系1最终溶液中加入5μL未经臭氧处理的CDs,此时,溶液中碳纳米点与3,3',5,5'-四甲基联苯胺的质量浓度之比为8:1。Measurement system 2: Add 5 μL of CDs without ozone treatment to the final solution of measurement system 1. At this time, the ratio of the mass concentrations of carbon nanodots to 3,3',5,5'-tetramethylbenzidine in the solution is 8:1.
测量体系3:向测量体系1最终溶液中加入5μL臭氧处理的CDs,此时,溶液中碳纳米点与3,3',5,5'-四甲基联苯胺的质量浓度之比为8:1。Measurement system 3: Add 5 μL of ozone-treated CDs to the final solution of measurement system 1. At this time, the mass concentration ratio of carbon nanodots to 3,3',5,5'-tetramethylbenzidine in the solution is 8: 1.
测量体系1的结果显示,TMB氧化的最终产物diimine oxTMB在450nm产生一个明显的吸收峰(图7A),但是,吸光度随着时间逐渐降低,从0min的0.17逐渐降低到60min的0.16(图7B)。The results of measurement system 1 show that diimine oxTMB, the final product of TMB oxidation, produces an obvious absorption peak at 450 nm (Figure 7A). However, the absorbance gradually decreases with time, from 0.17 at 0 min to 0.16 at 60 min (Figure 7B) .
测量体系2的结果显示,在测量体系1的最终溶液中加入未经臭氧处理的CDs之后,TMB氧化的最终产物diimine oxTMB在450nm产生的吸收峰仍然清晰可辩(图8A),但是,吸光度随着时间快速降低,从0min的0.14逐渐降低到60min的0.112(图8图7B)。The results of measurement system 2 show that after adding CDs without ozone treatment to the final solution of measurement system 1, the absorption peak at 450 nm of diimine oxTMB, the final product of TMB oxidation, is still clearly discernible (Figure 8A). However, the absorbance increases with the The burning time decreased rapidly, gradually decreasing from 0.14 at 0 min to 0.112 at 60 min (Figure 8 Figure 7B).
测量体系3的结果显示,在测量体系1的最终溶液中加入经臭氧处理的CDs之后,TMB氧化的最终产物diimine oxTMB在450nm产生的吸收峰仍然清晰可辩(图9A),而且,吸光度基本不随着时间变化,在0min到60min时间范围内,维持在0.157~0.158之间(图9B),在测量误差允许的范围内可以认为不发生变化。The results of measurement system 3 show that after adding ozone-treated CDs to the final solution of measurement system 1, the absorption peak at 450nm of diimine oxTMB, the final product of TMB oxidation, is still clearly discernible (Figure 9A), and the absorbance basically does not vary. It changes with time and remains between 0.157 and 0.158 in the time range from 0 min to 60 min (Figure 9B). It can be considered that there is no change within the allowable range of the measurement error.
上述实验结果表明,采用本发明制备的CDs,经过臭氧处理之后,用作荧光-比色法双模式检测时,不仅对比色法的检测不发生干扰,而且能稳定TMB氧化的最终产物diimineoxTMB,从而极大地提高检测性能。The above experimental results show that when the CDs prepared by the present invention are used for fluorescence-colorimetric dual-mode detection after ozone treatment, they not only do not interfere with the detection of the contrastive colorimetric method, but also stabilize diimineoxTMB, the final product of TMB oxidation, thus extremely Dramatically improve detection performance.
实施例7:比率荧光-比色法双模式检测肌氨酸Example 7: Ratio fluorescence-colorimetric dual-mode detection of sarcosine
将150μL不同浓度的肌氨酸溶液(溶于50mM磷酸盐缓冲溶液,pH 7.4)和20μL 20U/mL的肌氨酸氧化酶溶液混合,在37℃孵育10min后冷却至室温,然后加入10μL 2mM的TMB溶液和5μL 30U/mL辣根过氧化酶溶液,室温避光孵育5min后加入5M盐酸,调节pH为2.0,终止反应,然后加入20μL经臭氧处理的CDs得测量溶液,此时,测量溶液中碳纳米点与3,3',5,5'-四甲基联苯胺的质量浓度之比为32:1。Mix 150 μL of sarcosine solution of different concentrations (dissolved in 50mM phosphate buffer solution, pH 7.4) and 20 μL of 20 U/mL sarcosine oxidase solution, incubate at 37°C for 10 min, cool to room temperature, and then add 10 μL of 2mM sarcosine oxidase solution. TMB solution and 5 μL of 30 U/mL horseradish peroxidase solution were incubated for 5 minutes at room temperature in the dark, then 5 M hydrochloric acid was added to adjust the pH to 2.0 to terminate the reaction, and then 20 μL of ozone-treated CDs were added to obtain a measurement solution. At this time, the measurement solution The mass concentration ratio of carbon nanodots to 3,3',5,5'-tetramethylbenzidine is 32:1.
定量分析:比率荧光法测量时,分别以360nm和500nm电磁波激发测量溶液,测得探针450nm和540nm处发射强度分别为I450和I540,以荧光强度的比率I450/I540对待测样品进行定量;比色法测量时,以测量溶液450nm处的紫外吸光度A450进行定量。Quantitative analysis: When measuring by the ratiometric fluorescence method, the measurement solution is excited by electromagnetic waves of 360nm and 500nm respectively. The measured emission intensities of the probe at 450nm and 540nm are I 450 and I 540 respectively. The sample to be tested is measured based on the ratio of fluorescence intensity I 450 /I 540 . For quantification; when measuring by colorimetry, measure the UV absorbance A 450 of the solution at 450nm for quantification.
实验结果显示,在肌氨酸浓度从0增加到30μM时,I450和I540逐渐降低(图10A,图10B),荧光比率I450/I540与浓度呈良好的线性关系(图10C),荧光比率法的检出限为0.046μM。比色法检测时,系统在450nm处的吸光度随着肌氨酸浓度的增高而逐渐增大(图11A),在0~30μM范围内呈良好的线性关系,比色法的检出限为0.0014μM。The experimental results show that when the sarcosine concentration increases from 0 to 30 μM, I 450 and I 540 gradually decrease (Figure 10A, Figure 10B), and the fluorescence ratio I 450 /I 540 has a good linear relationship with the concentration (Figure 10C). The detection limit of the fluorescence ratiometric method is 0.046 μM. During colorimetric detection, the absorbance of the system at 450nm gradually increased as the sarcosine concentration increased (Figure 11A), showing a good linear relationship in the range of 0 to 30 μM. The detection limit of the colorimetric method was 0.0014 μM.
经文献检索,本发明对肌氨酸的检测限优于目前的报道(表1)。After literature search, the detection limit of sarcosine of the present invention is better than the current reports (Table 1).
表1现有技术的肌氨酸检出限Table 1 Detection limits of sarcosine in the prior art
备注,表中对应的参考文献:Note, the corresponding references in the table:
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[10]J.de Cássia L.R.da Rocha,T.B.Capelari,M.C.Prete,P.N.Angelis,M.G.Segatelli,C.R.T.Tarley,Design and performance of novelmolecularly imprinted biomimetic adsorbent for preconcentration of prostatecancer biomarker coupled to electrochemical determination by using multi-walled carbon nanotubes//>/Ni(OH)2-modified screen-printed electrode,Journal of Electroanalytical Chemistry.878(2020)114582.https://doi.org/10.1016/j.jelechem.2020.114582.[10]J. de Cássia LRda Rocha,TBCapelari,MCPrete,PNAngelis,MGSegatelli,CRTTarley,Design and performance of novelmolecularly imprinted biomimetic adsorbent for preconcentration of prostatecancer biomarker coupled to electrochemical determination by using multi-walled carbon nanotubes//> /Ni(OH)2-modified screen-printed electrode,Journal of Electroanalytical Chemistry.878(2020)114582.https://doi.org/10.1016/j.jelechem.2020.114582.
以上实施例只是用于帮助理解本发明的方法及其核心思想。应当指出,对于本技术领域的专业技术人员来说,在不脱离本发明原理的前提下,还可以对本发明进行若干改进和修饰,这些改进和修饰也落入本发明权利要求的保护范围内。The above embodiments are only used to help understand the method and its core idea of the present invention. It should be noted that for those skilled in the art, several improvements and modifications can be made to the present invention without departing from the principles of the present invention, and these improvements and modifications also fall within the protection scope of the claims of the present invention.
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