Determination of Trace Pb2+ and Cd2+ in Water by Electrochemical Method Based on Glassy Carbon Electrode Modified with COF@CNTs/Bi
摘 要
建立了基于COF@CNTs/Bi修饰玻碳电极的电化学法测定水中痕量Pb2+和Cd2+的方法。称取单壁碳纳米管(CNTs)0.1 g,加入25 mL二甲基亚砜,超声10 min;再加入对苯二甲酸二醛0.02 g和1,3,5-三(4-氨基苯基)苯0.035 g,超声5 min;接着加入2 mL 12 mol·L-1乙酸溶液,超声10 min。用10 mL N,N-二甲基甲酰胺和10 mL无水乙醇重复洗涤3次,干燥,得到COF@CNTs。称取1 mg COF@CNTs,加入5 mL N,N-二甲基甲酰胺,超声5 min,得到悬浮液。移取5 μL悬浮液,滴涂在活化好的玻碳电极表面,得到COF@CNTs工作电极。以COF@CNTs为工作电极,Ag/AgCl为参比电极,铂丝为辅助电极,将该三电极系统置于Bi3+、Pb2+、Cd2+的标准溶液中,于-1.4 V下富集Bi3+、Pb2+、Cd2+ 360 s,得到COF@CNTs/Bi电极,再于-1.4~-0.2 V内进行扫描,记录Pb2+和Cd2+的溶出峰电流。结果显示,Pb2+和Cd2+的质量浓度在500 μg·L-1以内与其对应的溶出峰电流呈线性关系,检出限(3S/N)均为0.33 μg·L-1;基于COF@CNTs/Bi电极对100 μg·L-1 Pb2+和Cd2+混合标准溶液平行测定5次,测定值的相对标准偏差(RSD)为3.9%;对自来水和湖水进行加标回收试验,Pb2+和Cd2+的回收率分别为96.2%~108%和95.3%~105%。
Abstract
A method for the determination of trace Pb2+ and Cd2+ in water by electrochemical method based on glassy carbon electrode modified with COF@CNTs/Bi was established. Single-wall carbon nanotubes of 0.1 g was taken, dimethyl sulfoxide of 25 mL was added, and the mixture was treated for 10 min with ultrasonic. Dialdehyde terephthalate of 0.02 g and 1,3,5-tri(4-aminophenyl) benzene of 0.035 g were added for ultrasonic treatment of 5 min. Then 12 mol·L-1 acetic acid solution of 2 mL was added for ultrasonic treatment of 10 min. After washing 3 times repeatedly with N,N-dimethylformamide of 10 mL and anhydrous ethanol of 10 mL and drying, COF@CNTs was obtained. N,N-dimethylformamide of 5 mL was added to COF@CNTs of 1 mg for ultrasonic treatment of 5 min to get the suspension. The suspension of 5 μL was dropped onto the activated glassy carbon electrode surface to obtain COF@CNTs working electrode. Using COF@CNTs as the working electrode, Ag/AgCl as the reference electrode and platinum wire as the auxiliary electrode, the three-electrode system was placed in standard solution of Bi3+, Pb2+ and Cd2+. Bi3+, Pb2+ and Cd2+ were enriched for 360 s at -1.4 V to prepare COF@CNTs/Bi electrode. The stripping peak currents of Pb2+ and Cd2+ were recorded in the range of -1.4--0.2 V. As shown by the results, linear relationships between values of mass concentration of Pb2+ and Cd2+ and their stripping peak current were kept within 500 μg·L-1, with detection limits (3S/N) of 0.33 μg·L-1. Pb2+ and Cd2+ mixed standard solution of 100 μg·L-1 was determined 5 times in parallel based on COF@CNTs/Bi electrode, and RSDs of the determined values was 3.9%. Recovery test was made on tap water and lake water, giving results in the range of 96.2%-108% and 95.3%-105%, respectively.
中图分类号 O657.1 DOI 10.11973/lhjy-hx202110014
所属栏目 工作简报
基金项目 国家重点研发项目资助(2018YFF0215404)
收稿日期 2021/6/22
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联系人作者许贺(hexu@dhu.edu.cn)
备注贾旭峰,硕士,研究方向为环境电化学及分析应用
引用该论文: JIA Xufeng,ZHANG Duo,WU Xiaohong,CHENG Yuxiao,XIE Tao,XU He. Determination of Trace Pb2+ and Cd2+ in Water by Electrochemical Method Based on Glassy Carbon Electrode Modified with COF@CNTs/Bi[J]. Physical Testing and Chemical Analysis part B:Chemical Analysis, 2021, 57(10): 933~939
贾旭峰,张多,吴晓红,程欲晓,谢韬,许贺. 基于COF@CNTs/Bi修饰玻碳电极的电化学法测定水中痕量Pb2+和Cd2+[J]. 理化检验-化学分册, 2021, 57(10): 933~939
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【2】FATEMA K, SHOILY S S, AHSAN T, et al. Effects of arsenic and heavy metals on metabolic pathways in cells of human origin:Similarities and differences[J]. Toxicology Reports, 2021, 8:1109-1120.
【3】NIU S, ZHENG L J, KHAN A Q, et al. Laser-induced breakdown spectroscopic detection of trace level heavy metal in solutions on a laser-pretreated metallic target[J]. Talanta, 2018, 179:312-317.
【4】吴海华.电感耦合等离子质谱法快速检测豆类及其制品中铅镉等重金属残留的方法研究[J].食品安全导刊, 2021(12):79-80.
【5】金文斌, 赵鑫, 刘瑞华.甲基百里香酚蓝分光光度法测定大豆中微量锌的研究与应用[J].天津化工, 2021, 35(3):41-42.
【6】SUN J D, GAN Y, LIANG T, et al. Signal enhancement of electrochemical DNA biosensors for the detection of trace heavy metals[J]. Current Opinion in Electrochemistry, 2019, 17:23-29.
【7】WU W Q, JIA M M, ZHANG Z W, et al. Sensitive, selective and simultaneous electrochemical detection of multiple heavy metals in environment and food using a lowcost Fe3O4 nanoparticles/fluorinated multi-walled carbon nanotubes sensor[J]. Ecotoxicology and Environmental Safety, 2019, 175:243-250.
【8】GENG K, HE T, LIU R, et al. Covalent organic frameworks:Design, synthesis, and functions[J]. Chemical Reviews, 2020, 120(16):8814-8933.
【9】TANG M, JIANG C, LIU S Y, et al. Small amount COFs enhancing storage of large anions[J]. Energy Storage Materials, 2020, 27:35-42.
【10】WU M X, YANG Y W. Applications of covalent organic frameworks (COFs):From gas storage and separation to drug delivery[J]. Chinese Chemical Letters, 2017, 28(6):1135-1143.
【11】LI C Z, MA Y H, LIU H R, et al. Asymmetric photocatalysis over robust covalent organic frameworks with tetrahydroquinoline linkage[J]. Chinese Journal of Catalysis, 2020, 41(8):1288-1297.
【12】SUN Y F, XU L H, WATERHOUSE G I N, et al. Novel three-dimensional electrochemical sensor with dual signal amplification based on MoS2 nanosheets and high-conductive NH2-MWCNT@COF for sulfamerazine determination[J]. Sensors and Actuators B:Chemical, 2019, 281:107-114.
【13】SENGUPTA M, BAG A, GHOSH S, et al. CuxOy@COF:An efficient heterogeneous catalyst system for CO2 cycloadditions under ambient conditions[J]. Journal of CO2 Utilization, 2019, 34:533-542.
【14】LOFRANO G, CAROTENUTO M, LIBRALATO G, et al. Polymer functionalized nanocomposites for metals removal from water and wastewater:An overview[J]. Water Research, 2016, 92:22-37.
【15】LIU Y B, LIU F Q, DING N, et al. Recent advances on electroactive CNT-based membranes for environmental applications:The perfect match of electrochemistry and membrane separation[J]. Chinese Chemical Letters, 2020, 31(10):2539-2548.
【16】CHEN P H, SHI Y M, NIU P P, et al. Highly sensitive detection of 4-NP in real water with long stability and high anti-inteference ability based on GO-Ag2CrO4/GCE[J]. Journal of the Taiwan Institute of Chemical Engineers, 2019, 97:128-136.
【17】ALGHAMDI A F. Development and validation of anodic stripping voltammetry method for the determination of tretinoin in human urine and plasma using glassy carbon electrode[J]. Journal of King Saud University-Science, 2020, 32(5):2635-2640.
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