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CN116626136A - A method for the detection of different chromium ion species based on group interaction - Google Patents

A method for the detection of different chromium ion species based on group interaction Download PDF

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CN116626136A
CN116626136A CN202310619347.3A CN202310619347A CN116626136A CN 116626136 A CN116626136 A CN 116626136A CN 202310619347 A CN202310619347 A CN 202310619347A CN 116626136 A CN116626136 A CN 116626136A
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黄行九
黄聪聪
杨猛
宋宗银
陈石华
李培华
李慧泉
崔玉民
吴珍汉
于信誉
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Hefei Institutes of Physical Science of CAS
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Abstract

The invention discloses a method for realizing detection of different chromium ion forms based on radical interaction, which comprises the steps of carrying out electrochemical action on a functionalized material modified electrode and a chromium-containing solution under the induction of an electric field; the functional material is amino modified cobalt-based graphene and/or carboxylated modified cobalt-based graphene. The invention further fixes HCrO by electrostatic attraction and group interaction under the action of an electric field 4 And Cr (OH) 2+ The detection lower limit is 0.10 mug/L and 0.12 mug/L respectively, the detection sensitivity is 19.46 mug/L and 13.44 mug/L respectively, and the detection lower limit is improved by 2-3 orders of magnitude compared with the detection lower limit of the traditional spectrometry, the operation process is simple and mild, the cost is low, and the method has good application prospect.

Description

一种基于基团相互作用的不同铬离子形态检测方法A method for the detection of different chromium ion species based on group interaction

技术领域technical field

本发明涉及重金属铬的形态分析检测技术领域,具体地,本发明涉及一种基于基团相互作用的不同铬离子形态检测方法。The invention relates to the technical field of speciation analysis and detection of heavy metal chromium, in particular, the invention relates to a method for detecting the speciation of different chromium ions based on group interaction.

背景技术Background technique

近年来,重金属离子引起的环境污染受到越来越多的关注。不同形态的重金属离子对应着不同的生物利用度和生理毒性,因此,将重点放在对不同形态的快速准确检测上,而不是全面检测,具有重要意义。目前重金属污染物的灵敏可靠检测在很大程度上仍依赖于传统光学仪器方法,例如原子吸收光谱法、电感耦合等离子体质谱法等。但大多具有设备庞大、运行成本高、对操作人员技术要求高等特点。此外,电化学技术和激光诱导击穿光谱技术(LIBS)也被用于重金属离子的检测1-3,但存在常依赖于强酸电解质或贵金属催化、常用于单一形态分析的特点问题。In recent years, environmental pollution caused by heavy metal ions has received more and more attention. Different forms of heavy metal ions correspond to different bioavailability and physiological toxicity. Therefore, it is of great significance to focus on the rapid and accurate detection of different forms rather than comprehensive detection. At present, the sensitive and reliable detection of heavy metal pollutants still largely relies on traditional optical instrument methods, such as atomic absorption spectrometry, inductively coupled plasma mass spectrometry, etc. However, most of them have the characteristics of huge equipment, high operating costs, and high technical requirements for operators. In addition, electrochemical techniques and laser-induced breakdown spectroscopy (LIBS) have also been used for the detection of heavy metal ions1-3 , but there are characteristic problems that often rely on strong acid electrolytes or noble metal catalysis, and are often used for single-species analysis.

发明内容Contents of the invention

本发明提出了一种在电场诱导下,基于目标离子含氧基团与功能材料特殊相互作用的机制,从而可实现对具有不同形态铬的超低限、准确、快速检测的目的。为实现该目的,本发明采用下述技术方案:The invention proposes a mechanism based on the special interaction between oxygen-containing groups of target ions and functional materials under electric field induction, so as to achieve the purpose of ultra-low limit, accurate and rapid detection of chromium with different forms. To achieve this goal, the present invention adopts the following technical solutions:

一种基于基团相互作用的不同铬离子形态检测方法,其是在电场诱导下,将功能化材料修饰电极与含铬溶液进行电化学作用;所述功能化材料为氨基化修饰的钴基石墨烯和/或羧基化修饰的钴基石墨烯。A method for detecting different forms of chromium ions based on group interactions, which involves electrochemically interacting a functionalized material-modified electrode with a chromium-containing solution under the induction of an electric field; the functionalized material is cobalt-based graphite modified by amination ene and/or carboxylated cobalt-based graphene.

上述所述的方法中,优选的,可采用将钴基石墨烯Co3O4-rGO进行氨基化修饰得到NH2-Co3O4/rGO,将钴基石墨烯Co3O4 rGO进行羧基化修饰得到COOH-Co3O4/rGO。其中,所述氨基化修饰可以是将Co3O4 rGO溶于乙醇和水中,加入氨水和氨丙基三甲氧基硅烷(APTMS),超声振荡。所述氨基化修饰方法是常见常用的处理工艺。所述羧基化修饰是将Co3O4 rGO溶于乙醇和水中,加入羧基化石墨烯(COOHGO),超声振荡。所述Co3O4-rGO可采用已知报道的相关文献方法如RSC Adv.,2015,5,88567得到。所述羧基化石墨烯(COOHGO)也可通过常用的石墨烯羧基化方法得到或者直接购自专业的生产商。In the method described above, preferably, the cobalt-based graphene Co 3 O 4 -rGO can be aminated to obtain NH 2 -Co 3 O 4 /rGO, and the cobalt-based graphene Co 3 O 4 rGO can be carboxylated COOH-Co 3 O 4 /rGO was obtained through modification. Wherein, the amination modification may be dissolving Co 3 O 4 rGO in ethanol and water, adding ammonia water and aminopropyltrimethoxysilane (APTMS), and ultrasonically vibrating. The amination modification method is a common and commonly used treatment process. The carboxylation modification comprises dissolving Co 3 O 4 rGO in ethanol and water, adding carboxylated graphene (COOHGO), and ultrasonically vibrating. The Co 3 O 4 -rGO can be obtained by using known and reported related literature methods such as RSC Adv., 2015, 5, 88567. The carboxylated graphene (COOHGO) can also be obtained by a common graphene carboxylation method or directly purchased from a professional manufacturer.

上述所述的方法中,优选的,可通过采用NH2-Co3O4/rGO对电极进行修饰,施加正电压对含铬溶液HCrO4 -进行检测;采用COOH-Co3O4/rGO对电极进行修饰,施加负电压对含铬溶液Cr(OH)2+进行检测。所述电极采用常见的金属电极如铝片电极即可,当然也可以采用其他金属比如铜箔电极、钛电极、银电极或者采用非金属电极如石墨电极,研究发现,相比于石墨电极,铝片电极有更优越的电化学富集效果,这可能是铝片的导电性更好的原因。另外,在对电极进行修饰时,工作电极一般需要经过前处理比如用砂纸打磨至光亮状态,然后再将4-6mg/ml NH2-Co3O4/rGO和1-3mg/ml COOH-Co3O4/rGO均匀旋涂至电极表面,干燥后待用。优选5mg/ml NH2-Co3O4/rGO、1.5mg/ml COOH-Co3O4/rGO进行旋涂。所述电极可采用便于更换的旋转电极,这样便于调整更换电极。发明人研究发现,旋涂的溶液浓度过大会造成滴涂材料过厚,会覆盖电极表面活性位点,影响与目标离子的相互作用;而旋涂溶液浓度过低则不足以提供足够多的功能化基团与目标离子发生相互作用,减弱了光谱信号的产生。In the method described above, preferably, the electrode can be modified by using NH 2 -Co 3 O 4 /rGO, and a positive voltage can be applied to detect the chromium-containing solution HCrO 4 - ; COOH-Co 3 O 4 /rGO can be used to detect The electrode is modified, and a negative voltage is applied to detect Cr(OH) 2+ in chromium-containing solution. The electrode can be a common metal electrode such as an aluminum sheet electrode. Of course, other metals such as copper foil electrodes, titanium electrodes, silver electrodes or non-metal electrodes such as graphite electrodes can be used. It is found that compared with graphite electrodes, aluminum The sheet electrode has a superior electrochemical enrichment effect, which may be the reason for the better conductivity of the aluminum sheet. In addition, when modifying the electrode, the working electrode generally needs to be pre-treated, such as sanded to a bright state, and then 4-6mg/ml NH 2 -Co 3 O 4 /rGO and 1-3mg/ml COOH-Co 3 O 4 /rGO was evenly spin-coated onto the surface of the electrode and dried for use. Preferably 5 mg/ml NH 2 -Co 3 O 4 /rGO, 1.5 mg/ml COOH-Co 3 O 4 /rGO for spin coating. The electrode can adopt a rotating electrode that is easy to replace, so that it is convenient to adjust and replace the electrode. The inventors have found that too much concentration of the spin-coating solution will cause the dripping material to be too thick, which will cover the active sites on the electrode surface and affect the interaction with the target ions; while the concentration of the spin-coating solution is too low to provide enough functions. The interaction between the cation group and the target ion weakens the generation of spectral signal.

更优选的,本发明用于不同铬离子形态检测及富集的方法,可采用下述步骤:More preferably, the method for detecting and enriching different forms of chromium ions according to the present invention may adopt the following steps:

(1)取8-12mg Co3O4 rGO溶于25-35mL乙醇和1-3mL去离子水中,加入2-6mL氨水和200-300μL APTMS,超声处理2-4h后在室温200rpm下振荡6-8h;用乙醇和水多次洗涤后,得到NH2-Co3O4/rGO;(1) Dissolve 8-12mg Co 3 O 4 rGO in 25-35mL ethanol and 1-3mL deionized water, add 2-6mL ammonia water and 200-300μL APTMS, sonicate for 2-4h and shake at room temperature at 200rpm for 6- 8h; after washing with ethanol and water several times, NH 2 -Co 3 O 4 /rGO was obtained;

(2)当采用COOHGO替换APTMS时,将获得COOH-Co3O4/rGO;具体的:取8-12mgCo3O4rGO溶于25-35mL乙醇和1-3mL去离子水中,加入200-300μL COOHGO,超声处理2-4h后在室温200rpm下振荡6-8h;用乙醇和水多次洗涤后,得到COOH-Co3O4/rGO。(2) When COOHGO is used to replace APTMS, COOH-Co 3 O 4 /rGO will be obtained; specifically: take 8-12mg Co 3 O 4 rGO and dissolve it in 25-35mL ethanol and 1-3mL deionized water, add 200-300μL COOHGO, sonicated for 2-4h, shaken at room temperature 200rpm for 6-8h; after washing with ethanol and water several times, COOH-Co 3 O 4 /rGO was obtained.

(3)采用NH2-Co3O4/rGO对电极进行修饰,施加正电压对含铬溶液HCrO4 -进行检测;采用COOH-Co3O4/rGO对电极进行修饰,施加负电压对含铬溶液Cr(OH)2+进行检测。(3) The electrode is modified with NH 2 -Co 3 O 4 /rGO, and a positive voltage is applied to detect the chromium-containing solution HCrO 4 - ; the electrode is modified with COOH-Co 3 O 4 /rGO, and a negative voltage is applied to detect the Chromium solution Cr(OH) 2+ for detection.

优选的,所述含铬溶液pH=4-5为佳。该pH范围内时,六价铬和三价铬分别是以HCrO4-和Cr(OH)2+形式存在,对于六价铬一般都是以含氧基团形式存在,对于三价铬,在pH为4-5情况下以含氧基团Cr(OH)2+的形式存在(Int.J.Environ.An.Ch.2019,1051)。从而可利用两种含氧基团所带电荷的差异进行电化学分析。当然,含铬溶液可采用缓冲溶液进行调配到适合的pH。所述施加正电压0.5~2V为佳,0.8-1.5V更佳,1.0V最佳;施加负电压-0.5~-2V为佳,-0.8~-1.5V更佳,-0.9V最佳;施加电压过大容易导致电极表面析氢,产生气泡影响纳米材料对目标离子的吸附和相互作用,而电压过小则不能提供足够的电场下的牵引力,影响电富集效率。步骤(3)检测结合采用LIBS定量分析法为佳。本发明通过电场下的电压调控和氨基或羧基化基团的化学结合作用在电极表面固定HCrO4 -或Cr(OH)2+,即可进行定量分析。Preferably, the pH of the chromium-containing solution is preferably 4-5. Within this pH range, hexavalent chromium and trivalent chromium exist in the form of HCrO4 - and Cr(OH) 2+ respectively. For hexavalent chromium, they generally exist in the form of oxygen-containing groups. For trivalent chromium, at pH In the case of 4-5, it exists in the form of oxygen-containing group Cr(OH) 2+ (Int.J.Environ.An.Ch.2019, 1051). Thus, the difference in charge of the two oxygen-containing groups can be used for electrochemical analysis. Of course, the chromium-containing solution can be adjusted to a suitable pH with a buffer solution. The applied positive voltage is preferably 0.5-2V, 0.8-1.5V is better, and 1.0V is the best; the negative voltage is -0.5--2V is better, -0.8--1.5V is better, and -0.9V is the best; If the voltage is too high, it will easily lead to hydrogen evolution on the surface of the electrode, and the generation of bubbles will affect the adsorption and interaction of nanomaterials with target ions, while if the voltage is too small, it will not be able to provide sufficient traction force under the electric field, which will affect the efficiency of electrical enrichment. The detection in step (3) is preferably combined with the LIBS quantitative analysis method. The invention fixes HCrO 4 - or Cr(OH) 2+ on the surface of the electrode through the voltage regulation under the electric field and the chemical combination of the amino group or the carboxylation group, so as to perform quantitative analysis.

根据本发明,以四氧化三钴和石墨烯为介质,通过氨基和羧基功能化来制备功能化钴基石墨烯复合材料载体,不仅能通过过渡金属钴的价态循环提升电子转移能力,还能通过含氧基团与功能化基团的相互作用实现目标离子的选择性和抗干扰检测。According to the present invention, using tricobalt tetroxide and graphene as the medium, functionalized cobalt-based graphene composite material carrier is prepared by functionalizing amino group and carboxyl group, which can not only improve the electron transfer ability through the valence cycle of the transition metal cobalt, but also through the oxygen-containing The interaction between the group and the functionalized group realizes the selective and anti-interference detection of the target ion.

本发明提出了一种电场调控和氨基、羧基化基团相互作用下,高灵敏高选择性检测ppb量级的不同形态铬的新方法。与传统的光谱方法相比,该方法可以将检测限和灵敏度提高两个数量级,并进一步解释了选择性和灵敏检测的作用机制是“电场诱导”和“化学结合”的共同作用。在钴基石墨烯表面分别进行氨基化和羧基化基团的修饰,在pH为4.0-5.0尤其4.0的缓冲溶液中,氨基基团质子化形成NH3 +与HCrO4 -在正电场1.0V作用下发生静电吸引和化学结合的共同作用,促使LIBS高灵敏高选择性地识别了HCrO4 -的光谱信号。羧基化基团去质子化形成COO-与Cr(OH)2+在负电场0.9V作用下发生静电吸引和化学结合的共同作用,促使LIBS高灵敏高选择性地识别了Cr(OH)2+的光谱信号。通过TEM、XPS和XANES解释了本工作中新方法的高灵敏检测机理。它从基团相互作用的微观角度提出一种选择性检测的新方法,为水环境中重金属污染物的快速精确分析提供了一种新的思路。The invention proposes a new method for highly sensitive and selective detection of chromium in different forms at the ppb level under electric field regulation and the interaction of amino groups and carboxylation groups. Compared with traditional spectroscopic methods, this method can improve the detection limit and sensitivity by two orders of magnitude, and further explains the mechanism of selective and sensitive detection as the combined effect of "electric field induction" and "chemical binding". Amination and carboxylation groups are respectively modified on the surface of cobalt-based graphene. In a buffer solution with a pH of 4.0-5.0, especially 4.0, the amino group is protonated to form NH 3 + and interact with HCrO 4 - in a positive electric field of 1.0V Under the combined effect of electrostatic attraction and chemical combination, LIBS can identify the spectral signal of HCrO 4 - with high sensitivity and high selectivity. The deprotonation of the carboxylation group to form COO - and Cr(OH) 2+ under the action of a negative electric field of 0.9V have electrostatic attraction and chemical combination, which promotes the highly sensitive and selective recognition of Cr(OH) 2+ by LIBS the spectral signal. The highly sensitive detection mechanism of the new method in this work is explained by TEM, XPS and XANES. It proposes a new selective detection method from the microscopic point of group interaction, and provides a new idea for the rapid and accurate analysis of heavy metal pollutants in the water environment.

在这里,发明人提出一种基于不同含氧基团与功能化基团在外加电场诱导下相互作用的机制,并以辅助激光诱导击穿光谱(LIBS)检测水中不同形态铬的新方法。由于重金属污染物形态分布随溶液pH的变化而变化,通过调节电化学参数,利用两种铬离子的电荷差异实现选择性富集,然后通过LIBS技术进行定量分析。利用具有优良电导率的Co3O4纳米颗粒和较大表面积的rGO构建电化学敏感界面,该复合材料在阻止石墨烯片层团聚的同时,提升了电导率和电化学富集效率,降低了LIBS检测下限。氨基和羧基修饰的Co3O4-rGO分别选择性富集HCrO4 -和Cr(OH)2+,然后被LIBS定量检测。结果表明,该方法具有较好的抗干扰性和实际水样分析效果。FTIR、XPS和XANES表明,优异的检测性能归因于薄层石墨烯的强吸附能力、功能化基团(氨基和羧基)对不同形态铬离子的选择性吸附和化学相互作用、以及Co3O4纳米颗粒中Co(II)/(III)价态循环的协同作用,本发明中对Co3O4纳米颗粒粒径不做要求,它主要起到增强导电性以及价态循环促进电子转移的作用。Here, the inventors proposed a new method based on the interaction mechanism of different oxygen-containing groups and functional groups induced by an applied electric field, and assisted by laser-induced breakdown spectroscopy (LIBS) to detect different forms of chromium in water. Since the speciation distribution of heavy metal pollutants changes with the change of solution pH, by adjusting the electrochemical parameters, the charge difference of the two chromium ions is used to achieve selective enrichment, and then quantitative analysis is carried out by LIBS technology. Using Co 3 O 4 nanoparticles with excellent conductivity and rGO with a large surface area to construct an electrochemically sensitive interface, the composite material not only prevents the agglomeration of graphene sheets, but also improves the conductivity and electrochemical enrichment efficiency, reducing the LIBS lower limit of detection. Amino- and carboxyl-modified Co 3 O 4 -rGO were selectively enriched in HCrO 4 - and Cr(OH) 2+ , respectively, and then quantitatively detected by LIBS. The results show that the method has good anti-interference and real water sample analysis effect. FTIR, XPS, and XANES indicated that the excellent detection performance was attributed to the strong adsorption capacity of thin-layer graphene, the selective adsorption and chemical interaction of functionalized groups (amino and carboxyl groups) for different morphological chromium ions, and the Co3O 4 synergy of Co(II)/(III) valence state cycle in the nanoparticle, in the present invention Co3O4 nanoparticle size is not required, it mainly plays the role of enhancing electrical conductivity and valence state cycle to promote electron transfer effect.

发明人研究发现,Co3O4纳米颗粒增强了复合材料的导电性,防止了石墨烯基底材料层间团聚,提高富集效率。DFT差分电荷密度图中揭示了COO--Co3O4/rGO与Cr(OH)2+作用时,电子从Co位点流向Cr(OH)2+中的Cr位点,NH3 +-Co3O4/rGO与HCrO4 -作用时,电子从Co位点流向HCrO4 -的O位点,如图3。XPS表明功能化钴基石墨烯吸附铬离子后,Co(II)比例降低,Co(III)比例升高。通过Co(II)/(III)价态循环促进电子转移。如图5。The inventors found that the Co 3 O 4 nanoparticles enhanced the electrical conductivity of the composite material, prevented interlayer agglomeration of the graphene base material, and improved the enrichment efficiency. The DFT differential charge density map reveals that when COO - -Co 3 O 4 /rGO interacts with Cr(OH) 2+ , electrons flow from Co sites to Cr sites in Cr(OH) 2+ , and NH 3 + -Co When 3 O 4 /rGO interacts with HCrO 4 - , electrons flow from the Co site to the O site of HCrO 4 - , as shown in Figure 3. XPS showed that the proportion of Co(II) decreased and the proportion of Co(III) increased after functionalized Co-based graphene adsorbed chromium ions. Electron transfer is facilitated through the Co(II)/(III) valence cycle. Figure 5.

本发明通过在不同电场下用功能化材料修饰电极来实现选择性电化学富集Cr(OH)2+和HCrO4 -,并发生特异性的化学相互作用,是提升检测灵敏度和选择性的关键因素,在材料表面修饰特定的官能团(氨基和羧基),在电场作用下,通过静电吸引和基团相互作用进一步固定HCrO4 -和Cr(OH)2+,得到的检测下限分别为0.10μg/L和0.12μg/L,检测灵敏度分别为19.46μg/L和13.44μg/L,较传统激光诱导击穿光谱法4-8(检测下限100μg/L-1000μg/L)提高了2-3个数量级。操作过程简洁温和,成本低廉,显示出良好的应用前景。高灵敏度检测的机制是预富集过程中的电场诱导以及功能化基团与目标离子的相互作用。结果表明,氨基基团质子化NH3 +与HCrO4 -发生静电吸引和化学结合的共同作用的同时,在正电场下规避了阳离子的干扰(静电斥力)和其他以简单形式(没有含氧基团)存在的阴离子的干扰。羧基化基团去质子化形成COO-与Cr(OH)2+发生静电吸引和化学结合的共同作用的同时,在负电场下规避了阴离子的干扰(静电斥力)和其他以简单形式(没有含氧基团)存在的阳离子的干扰。且具有优良导电性的Co3O4纳米颗粒协同提高了电富集和电子转移的效率,促使LIBS高灵敏高选择性地进行了不同形态铬的检测。本发明为重金属离子形态分析的电化学方法提供了新的思路。The invention achieves selective electrochemical enrichment of Cr(OH) 2+ and HCrO 4 - by modifying electrodes with functionalized materials under different electric fields, and produces specific chemical interactions, which is the key to improving detection sensitivity and selectivity Factors, modify specific functional groups (amino and carboxyl) on the surface of the material, under the action of an electric field, further immobilize HCrO 4 - and Cr(OH) 2+ through electrostatic attraction and group interaction, and the lower detection limits obtained are 0.10 μg/ L and 0.12μg/L, the detection sensitivities are 19.46μg/L and 13.44μg/L, which is 2-3 orders of magnitude higher than the traditional laser-induced breakdown spectroscopy 4-8 (lower detection limit 100μg/L-1000μg/L) . The operation process is simple and gentle, and the cost is low, showing good application prospects. The mechanism of high-sensitivity detection is the electric field induction during the pre-enrichment process and the interaction between functionalized groups and target ions. The results show that the amino group protonated NH 3 + and HCrO 4 - have electrostatic attraction and chemical combination, and at the same time avoid the interference of cations (electrostatic repulsion) and other simple forms (without oxygen-containing group) the interference of anions present. The carboxylation group is deprotonated to form COO - and Cr(OH) 2+ has electrostatic attraction and chemical combination, and at the same time, it avoids the interference of anions (electrostatic repulsion) and other simple forms (without containing Oxygen group) the presence of cation interference. And the Co 3 O 4 nanoparticles with excellent conductivity synergistically improved the efficiency of electrical enrichment and electron transfer, which promoted the detection of different forms of chromium with high sensitivity and selectivity by LIBS. The invention provides a new thought for the electrochemical method of heavy metal ion speciation analysis.

附图说明Description of drawings

图1为制备的氨基和羧基化钴基石墨烯的TEM图。Figure 1 is a TEM image of the prepared amino and carboxylated cobalt-based graphene.

图2为检测原理图。不同形态铬的检测分为电化学分离富集和LIBS定量分析两部分。电催化吸附在可更换的旋转电极进行,之后这两种电极进行原位LIBS定量分析。通过光谱信号结果建立线性方程,获得不同形态铬的分析结果。Figure 2 is a schematic diagram of the detection. The detection of different forms of chromium is divided into two parts: electrochemical separation and enrichment and LIBS quantitative analysis. Electrocatalytic adsorption was performed on a replaceable rotating electrode, after which both electrodes were used for in situ LIBS quantification. The linear equation was established through the spectral signal results to obtain the analysis results of different forms of chromium.

图3为DFT吸附构型图(附吸附能)。Figure 3 is the DFT adsorption configuration diagram (adsorption energy).

(a)Co3O4/rGO,(b)NH3 +-Co3O4/rGO对HCrO4 -在1V时的吸附构型和吸附能;(c)Co3O4/rGO,(d)COO--Co3O4/rGO对Cr(OH)2+在-0.9V的吸附构型和吸附能。(a) Co 3 O 4 /rGO, (b) NH 3 + -Co 3 O 4 /rGO adsorption configuration and adsorption energy of HCrO 4 - at 1V; (c) Co 3 O 4 /rGO, (d )COO--Co 3 O 4 /rGO adsorption configuration and adsorption energy for Cr(OH) 2+ at -0.9V.

图4为实施例中a)NH2-Co3O4/rGO对HCrO4 -的LIBS响应图,插图为对应的线性拟合图,b)COOH-Co3O4/rGO对Cr(OH)2+的LIBS响应图,插图为对应的线性拟合图。(50-500ppb)Figure 4 is a) the LIBS response diagram of NH 2 -Co 3 O 4 /rGO to HCrO 4 - in the example, the inset is the corresponding linear fitting diagram, b) COOH-Co 3 O 4 /rGO to Cr(OH) 2+ LIBS response plot, inset is the corresponding linear fitting plot. (50-500ppb)

图5为实施例中制备的a)-e)NH2-Co3O4/rGO和COOH-Co3O4/rGO吸附Cr前后各元素XPS高分辨谱对比,f)Cr foil,CrO3,Cr(OH)2+/COOH-Co3O4/rGO,Cr2O3,HCrO4 -/NH2-Co3O4/rGO的Cr K边近边谱比较,插图是局部放大图。Figure 5 is a comparison of XPS high-resolution spectra of each element before and after adsorption of Cr on a)-e) NH 2 -Co 3 O 4 /rGO and COOH-Co 3 O 4 /rGO prepared in the example, f) Cr foil, CrO 3 , Comparison of Cr(OH) 2+ /COOH-Co 3 O 4 /rGO, Cr 2 O 3 , HCrO 4 - /NH 2 -Co 3 O 4 /rGO Cr K-edge and near-edge spectra. The inset is a partially enlarged view.

图6单纯电场诱导对于100ppb(a)HCrO4 -和(b)Cr(OH)2+的光谱信号。Fig. 6 Spectral signals for 100ppb (a) HCrO 4 - and (b) Cr(OH) 2+ induced by pure electric field.

图7选择性和抗干扰试验。Figure 7 Selectivity and anti-interference test.

图8NH3 +-Co3O4/rGO在1V时对(a)HCrO4-和(b)Cr(OH)2+的吸附构型和吸附能;COO-Co3O4/rGO在-0.9V时对(c)Cr(OH)2+和(d)HCrO4 -的吸附构型和吸附能。Fig.8 Adsorption configuration and adsorption energy of (a) HCrO 4- and (b) Cr(OH) 2+ by NH 3 + -Co 3 O 4 /rGO at 1V ; COO-Co 3 O 4 /rGO at -0.9 The adsorption configuration and adsorption energy of (c) Cr(OH) 2+ and (d) HCrO 4 - at V.

具体实施方式Detailed ways

下述实施例是对于本发明内容的进一步说明以作为对本发明技术内容的阐释,但本发明的实质内容并不仅限于下述实施例所述,本领域的普通技术人员可以且应当知晓任何基于本发明实质精神的简单变化或替换均应属于本发明所要求的保护范围。The following examples are a further description of the content of the present invention as an explanation of the technical content of the present invention, but the essential content of the present invention is not limited to the following examples, those of ordinary skill in the art can and should know any Simple changes or replacements of the essential spirit of the invention shall fall within the scope of protection required by the present invention.

实施例1Example 1

(1)功能材料制备过程如下:首先,Co3O4 rGO(10mg)溶于乙醇(30mL)和去离子水(2mL)中,加入氨水(5mL)和APTMS(200μL),超声处理2h后在室温(200rpm)下振荡6h。用乙醇和水多次洗涤后,得到NH2-Co3O4/rGO;(1) The preparation process of functional materials is as follows: First, Co 3 O 4 rGO (10 mg) was dissolved in ethanol (30 mL) and deionized water (2 mL), ammonia (5 mL) and APTMS (200 μL) were added, and after ultrasonic treatment for 2 h, the Shake at room temperature (200rpm) for 6h. After multiple washes with ethanol and water, NH 2 -Co 3 O 4 /rGO was obtained;

在上述步骤中当APTMS替换成COOHGO时,可获得COOH-Co3O4/rGO。具体的,取Co3O4rGO(10mg)溶于乙醇(30mL)和去离子水(2mL)中,加入COOHGO(300μL),超声处理3h后在室温(200rpm)下振荡8h。用乙醇和水多次洗涤后,得到COOH-Co3O4/rGO。图1给出实施例中制备的氨基化和羧基化钴基石墨烯的TEM图。When APTMS is replaced by COOHGO in the above steps, COOH-Co 3 O 4 /rGO can be obtained. Specifically, Co 3 O 4 rGO (10 mg) was dissolved in ethanol (30 mL) and deionized water (2 mL), COOHGO (300 μL) was added, sonicated for 3 h and then shaken at room temperature (200 rpm) for 8 h. After multiple washes with ethanol and water, COOH-Co 3 O 4 /rGO was obtained. Fig. 1 shows the TEM figure of amination and carboxylation cobalt-based graphene prepared in the embodiment.

(2)当溶液的pH=4,Cr(VI)以HCrO4 -的形式存在,Cr(III)以Cr(OH)2+的形式存在。根据两种离子所携带电荷的不同,施加不同电压。电化学分离富集可描述为以下步骤:采用电化学工作站,施加正电压时,经NH2-Co3O4/rGO修饰的电极作为工作电极,COOH-Co3O4/rGO修饰的电极作为参比电极/对电极;施加负电压时,COOH-Co3O4/rGO修饰的电极作为工作电极,经NH2-Co3O4/rGO修饰的电极作为参比电极/对电极。具体的,NH2-Co3O4rGO修饰铝片作为工作电极1施加正电压,形成一个正电区,通过电场诱导和质子化NH3 +对六价铬酸根离子的化学结合用于HCrO4 -的转移,被固定在NH2-Co3O4rGO电极上;当负电压作用于COOH-Co3O4rGO修饰的铝电极时,负电场的迁移辅助Cr(OH)2+聚焦在工作电极2周围,Cr(OH)2+在负电场和去质子化COO-的作用下被固定在COOH-Co3O4rGO电极上,LIBS激光对可旋转的电化学电极片进行原位分析,获得光谱信号。(2) When the pH of the solution is 4, Cr(VI) exists in the form of HCrO 4 - , and Cr(III) exists in the form of Cr(OH) 2+ . Depending on the charge carried by the two ions, different voltages are applied. Electrochemical separation and enrichment can be described as the following steps: using an electrochemical workstation, when a positive voltage is applied, the electrode modified by NH 2 -Co 3 O 4 /rGO is used as the working electrode, and the electrode modified by COOH-Co 3 O 4 /rGO is used as the Reference electrode/counter electrode; when a negative voltage is applied, the electrode modified by COOH-Co 3 O 4 /rGO is used as the working electrode, and the electrode modified by NH 2 -Co 3 O 4 /rGO is used as the reference electrode/counter electrode. Specifically, the NH 2 -Co 3 O 4 rGO modified aluminum sheet is used as the working electrode 1 to apply a positive voltage to form a positive charge area, and the chemical combination of hexavalent chromate ions by electric field induction and protonation NH 3 + is used for HCrO 4 The transfer of - is immobilized on the NH 2 -Co 3 O 4 rGO electrode; when a negative voltage is applied to the COOH-Co 3 O 4 rGO modified aluminum electrode, the migration of the negative electric field assists Cr(OH) 2+ to focus on the work Around the electrode 2, Cr(OH) 2+ was immobilized on the COOH-Co 3 O 4 rGO electrode under the action of negative electric field and deprotonated COO-, and the LIBS laser performed in-situ analysis on the rotatable electrochemical electrode sheet, Obtain spectral signals.

(3)DFT计算验证了功能化基团的引入增强了基底材料与目标离子的相互作用,促使产生了对不同铬离子高选择性和高灵敏检测的机制。图3给出了功能化基团存在和不存在的两种情况下,基底材料对目标离子的吸附构型和吸附能数值的对比。(3) DFT calculations verified that the introduction of functional groups enhanced the interaction between the substrate material and the target ions, resulting in the mechanism of high selectivity and high sensitivity detection of different chromium ions. Figure 3 shows the comparison of the adsorption configuration and adsorption energy value of the substrate material for the target ion in the presence and absence of functional groups.

(4)以氨基化和羧基化钴基石墨烯材料为基底,通过电化学富集和基团间的相互作用,基于LIBS方法实现不同形态铬的定量分析。结果表明,在电场作用下,通过静电吸引固定HCrO4 -和Cr(OH)2+,得到的检测下限分别为0.10μg/L和0.12μg/L,检测灵敏度分别为19.46μg/L和13.44μg/L,较传统光谱法的检测下限提高了2-3个数量级。图4给出了所制备复合材料对于(a)HCrO4 -和(b)Cr(OH)2+的光谱检测信号图。(4) Using aminated and carboxylated cobalt-based graphene materials as substrates, the quantitative analysis of different forms of chromium was realized based on LIBS method through electrochemical enrichment and interaction between groups. The results show that under the action of an electric field, HCrO 4 - and Cr(OH) 2+ are immobilized by electrostatic attraction, the lower detection limits are 0.10μg/L and 0.12μg/L, and the detection sensitivities are 19.46μg/L and 13.44μg, respectively /L, which is 2-3 orders of magnitude higher than the detection limit of traditional spectroscopic methods. Figure 4 shows the spectral detection signal diagrams of the prepared composite material for (a) HCrO 4 - and (b) Cr(OH) 2+ .

(5)XPS结果揭示了目标离子的含氧基团与功能化基团相互作用产生化学位移的机制,佐证了我们制备的功能化材料(复合材料)对于不同形态铬离子检测的抗干扰和选择性。图5给出了复合材料与目标离子的相互作用的XPS高分辨谱图。(5) The XPS results revealed the mechanism of the chemical shift produced by the interaction between the oxygen-containing groups of the target ions and the functionalized groups, which proved the anti-interference and selection of the functionalized materials (composite materials) we prepared for the detection of different forms of chromium ions sex. Figure 5 shows the XPS high-resolution spectrum of the interaction between the composite material and the target ion.

另外,发明人研究发现,如图6所示,在没有修饰功能化材料的情况下,单纯电场诱导对于HCrO4 -和Cr(OH)2+的光谱信号都很微弱。说明材料与目标离子的相互作用是提升光谱信号的关键因素。In addition, the inventors found that, as shown in FIG. 6 , the spectral signals of HCrO 4 - and Cr(OH) 2+ induced by a simple electric field are very weak in the absence of modified functionalized materials. It shows that the interaction between materials and target ions is the key factor to enhance the spectral signal.

同时,发明人还进行了相关干扰实验,结果如图7所示,一定浓度范围内的干扰离子对目标离子的光谱信号较小,这归因于1.0V的正电场诱导规避了其他阳离子的干扰,含氧基团HCrO4 -与质子化的NH3 +的化学结合和电场吸引的共同作用大于其他简单(不含氧)阴离子的电场吸附作用,因此其他阴离子对目标离子HCrO4 -的干扰较小。负0.9V的负电场诱导规避了阴离子的干扰,含氧基团Cr(OH)2+与去质子化的COO-的化学结合和电场吸引的共同作用大于其他简单(不含氧)阳离子的电场吸附作用,因此其他阳离子对目标离子Cr(OH)2+的干扰较小。At the same time, the inventor has also carried out related interference experiments, and the results are shown in Figure 7, the interference ions within a certain concentration range have a smaller spectral signal to the target ion, which is due to the positive electric field induction of 1.0V avoiding the interference of other cations , the joint effect of the chemical combination and electric field attraction of oxygen-containing group HCrO 4 - and protonated NH 3 + is greater than the electric field adsorption of other simple (oxygen-free) anions, so the interference of other anions on the target ion HCrO 4 - is less Small. Negative electric field induction at minus 0.9 V circumvents the interference of anions, and the combination of chemical combination and electric field attraction of oxygen-containing group Cr(OH) 2+ with deprotonated COO- is greater than that of other simple (oxygen-free) cations Adsorption, so other cations have less interference on the target ion Cr(OH) 2+ .

图8展示了通过DFT构型和吸附能的优化过程,可知,在外加电场1V时,NH3 +-Co3O4/rGO对HCrO4 -的吸附能大于对Cr(OH)2+的吸附能;外加电场负0.9V时,COO--Co3O4/rGO对Cr(OH)2+的吸附能大于对HCrO4 -的吸附能。两种不同形态铬离子存在时,质子化的NH3 +-Co3O4/rGO在正电场下倾向于吸附HCrO4 -并与之产生相互作用,去质子化的COO--Co3O4/rGO在负电场下倾向于吸附Cr(OH)2+并与之产生相互作用。上述结果说明了特异性基团对两种目标离子的选择性。Figure 8 shows the optimization process of DFT configuration and adsorption energy. It can be seen that the adsorption energy of NH 3 + -Co 3 O 4 /rGO on HCrO 4 - is greater than that on Cr(OH) 2+ when the applied electric field is 1V energy; when the applied electric field is minus 0.9V, the adsorption energy of COO - -Co 3 O 4 /rGO on Cr(OH) 2+ is greater than that on HCrO 4 - . In the presence of two different forms of chromium ions, the protonated NH 3 + -Co 3 O 4 /rGO tends to adsorb and interact with HCrO 4 - under positive electric field, and the deprotonated COO - -Co 3 O 4 /rGO tends to adsorb and interact with Cr(OH) 2+ under negative electric field. The above results illustrate the selectivity of the specific groups for the two target ions.

本发明揭示了一种不同功能化基团与目标离子的不同含氧基团相互作用的机制,发现“含氧基团”的存在是基团特异性结合进而实现抗干扰检测的重要因素,含氧基团HCrO4 -与质子化的NH3 +的化学结合和1.0V的正电场诱导,规避了阳离子和其他阴离子离子的干扰,含氧基团Cr(OH)2+与去质子化的COO-的化学结合和-0.9V的负电场诱导,规避了阴离子和其他阳离子的干扰。此外,基底材料中Co(II)/(III)的价态循环促进了电子向Cr的转移,促使Cr在电极上的还原与固定,有利于获得增强的光谱信号。结合DFT理论计算和XPS表征进一步解析了目标离子的配位环境,提出一种“电场诱导”和“化学结合”的协同作用机制,实现不同形态铬离子的高灵敏高选择性检测的方法。The present invention reveals a mechanism of interaction between different functionalized groups and different oxygen-containing groups of target ions, and finds that the existence of "oxygen-containing groups" is an important factor for the specific combination of groups and the realization of anti-interference detection, including Oxygen group HCrO 4 - chemical combination with protonated NH 3 + and positive electric field induction of 1.0V avoids the interference of cations and other anion ions, oxygen-containing group Cr(OH) 2+ and deprotonated COO The chemical combination of - and the negative electric field induction of -0.9V avoid the interference of anions and other cations. In addition, the valence cycle of Co(II)/(III) in the substrate material promotes the transfer of electrons to Cr, promotes the reduction and immobilization of Cr on the electrode, and is beneficial to obtain enhanced spectral signals. Combined with DFT theoretical calculation and XPS characterization, the coordination environment of target ions was further analyzed, and a synergistic mechanism of "electric field induction" and "chemical binding" was proposed to realize the highly sensitive and selective detection of different forms of chromium ions.

应当说明的是,本发明的上述所述之技术内容仅为使本领域技术人员能够获知本发明技术实质而进行的解释与阐明,故所述之技术内容并非用以限制本发明的实质保护范围。本发明的实质保护范围应以权利要求书所述之为准。本领域技术人员应当知晓,凡基于本发明的实质精神所作出的任何修改、等同替换和改进等,均应在本发明的实质保护范围之内。It should be noted that the above-mentioned technical content of the present invention is only an explanation and clarification to enable those skilled in the art to understand the technical essence of the present invention, so the described technical content is not intended to limit the scope of the present invention. . The substantive protection scope of the present invention should be defined by the claims. Those skilled in the art should know that any modifications, equivalent replacements and improvements made based on the essential spirit of the present invention shall fall within the scope of the essential protection of the present invention.

参考文献:references:

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Claims (10)

1. the method for detecting different chromium ion forms based on group interaction comprises the steps of carrying out electrochemical action on a functionalized material modified electrode and a chromium-containing solution under the induction of an electric field; the functional material is amino modified cobalt-based graphene and/or carboxylated modified cobalt-based graphene.
2. The method according to claim 1, wherein cobalt-based graphene Co 3 O 4 Amination modification of rGO to NH 2 -Co 3 O 4 rGO, cobalt-based graphene Co 3 O 4 Carboxylation modification of rGO to give COOH-Co 3 O 4 /rGO。
3. The method of claim 2, wherein the amination modification is the modification of Co 3 O 4 -rGO was dissolved in ethanol and water, ammonia and APTMS were added and sonicated.
4. The method of claim 2, wherein the carboxylation repairThe decoration is Co 3 O 4 -rGO was dissolved in ethanol and water, COOHGO was added and sonicated.
5. The method of claim 2, wherein NH is employed 2 -Co 3 O 4 Modification of electrode by rGO, application of positive voltage to HCrO in chromium-containing solution 4 - Detecting; by COOH-Co 3 O 4 Modification of electrode/rGO, application of negative voltage to Cr (OH) in chromium-containing solution 2+ And (5) detecting.
6. The method of claim 1, wherein the chromium-containing solution has a pH = 4-5.
7. The method of claim 2, comprising the steps of:
(1) Taking 8-12mg Co 3 O 4 -rGO is dissolved in 25-35mL ethanol and 1-3mL deionized water, 2-6mL ammonia water and 200-300 mu L APTMS are added, and after ultrasonic treatment for 2-4h, the solution is oscillated at 200rpm at room temperature for 6-8h; washing with ethanol and water for several times to obtain NH 2 -Co 3 O 4 /rGO;
(2) When COOHGO is used for replacing APTMS, COOH-Co is obtained 3 O 4 rGO; specific: taking 8-12mg Co 3 O 4 rGO is dissolved in 25-35mL of ethanol and 1-3mL of deionized water, 200-300 mu L of COOHGO is added, and after ultrasonic treatment for 2-4 hours, the solution is oscillated for 6-8 hours at room temperature and 200 rpm; washing with ethanol and water for several times to obtain COOH-Co 3 O 4 /rGO;
(3) By NH 2 -Co 3 O 4 Modification of electrode/rGO, application of positive voltage to chromium-containing solution HCrO with ph=4-5 4 - Detecting; by COOH-Co 3 O 4 Modification of electrode/rGO, application of negative voltage to chromium-containing solution Cr (OH) at ph=4-5 2+ And (5) detecting.
8. The method of claim 6, wherein the positive voltage is applied at 0.5-2V and the negative voltage is applied at-0.5 to-2V.
9. The method of claim 6, wherein the electrode is a rotating electrode.
10. The method of claim 6, wherein step (3) employs NH 2 -Co 3 O 4 Modification of electrode/rGO, application of positive voltage 1V to chromium-containing solution HCrO with ph=4-5 4 - Detecting; by COOH-Co 3 O 4 Modification of electrode/rGO, application of negative voltage 0.9V to chromium-containing solution Cr (OH) with pH=4-5 2+ And (5) detecting.
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