Determination of 12 Antibiotics in Waste Water by Solid Phase Extraction-Liquid Chromatography-Tandem Mass Spectrometry
摘 要
取500 mL废水样品,用6 mol·L-1盐酸溶液调节溶液酸度至pH 2.0~4.0后,再加入150 mg抗坏血酸和250 mg乙二胺四乙酸二钠。采用HLB固相萃取柱富集净化,用10 mL甲醇分两次洗脱。将洗脱液氮吹至近干,加入25 μL内标溶液,用初始比例流动相定容至1.0 mL,经0.22 μm有机滤膜过滤,得待测液。以ZARBAX Eclipse Plus C18色谱柱为固定相,以不同体积比的甲酸-甲醇-乙腈-水的混合液为流动相进行梯度洗脱。质谱分析采用电喷雾正离子(ESI+)源和多反应监测(MRM)模式检测,内标法定量。结果显示:12种抗生素标准曲线的线性范围均为2.00~200 μg·L-1,检出限(3.143s)为0.001~0.007 μg·L-1;对空白样品进行3个浓度水平的加标回收试验,回收率为60.1%~125%,测定值的相对标准偏差(n=6)为2.8%~13%。方法用于实际水样分析,结果显示5个不同来源的水样中均不同程度地检出抗生素。
Abstract
Waste water sample (500 mL) was adjusted to pH 2.0-4.0 with 6 mol·L-1 hydrochloric acid solution, and 150 mg of ascorbic acid and 250 mg of ethylenediamine tetraacetic acid disodium were added. HLB solid phase extraction column was used for enrichment and purification, and 10 mL of methanol was used for elution twice. The eluate was dried by nitrogen blowing and internal standard solution (25 μL) was added. The solution was made its volume up to 1.0 mL with initial proportional mobile phase and filtered by 0.22 μm microporous membrane for test. ZARBAX Eclipse Plus C18 chromatographic column was used as the stationary phase, and a mixture of formic acid, methanol, acetonitrile and water at different volume ratios was used as the mobile phase for gradient elution. ESI+ and MRM mode were used in MS analysis, and internal standard method was used for quantitative analysis. As shown by the results, the linear ranges of standard curves for 12 antibiotics were all 2.00-200 μg·L-1, with detection limits (3.143s) in the range of 0.001-0.007 μg·L-1. Recovery test was made on the blank sample at 3 concentration levels by standard addition method, giving results in the range of 60.1%-125%, and RSDs (n=6) of the determined values were in the range of 2.8%-13%. This method has been applied to the analysis of actual water samples, and the results showed that antibiotics were detected in 5 water samples from different sources in varying degrees.
中图分类号 O657.63 DOI 10.11973/lhjy-hx202204003
所属栏目 工作简报
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收稿日期 2020/7/9
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备注郭文建,硕士,主要从事环境中有机物分析测试研究
引用该论文: GUO Wenjian,ZHANG Hui,WANG Guixun,ZHU Chen,LI Lin,LI Hongli,SUN Junling. Determination of 12 Antibiotics in Waste Water by Solid Phase Extraction-Liquid Chromatography-Tandem Mass Spectrometry[J]. Physical Testing and Chemical Analysis part B:Chemical Analysis, 2022, 58(4): 387~394
郭文建,张慧,王桂勋,朱晨,李琳,李红莉,孙俊玲. 固相萃取-液相色谱-串联质谱法测定废水中12种抗生素的含量[J]. 理化检验-化学分册, 2022, 58(4): 387~394
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参考文献
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【15】陈乾,刘洋,肖丽君,等.超高效液相色谱串联质谱法同时测定叶菜中13种抗生素[J].环境科学, 2020,41(2):952-961.
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【17】石奥,张建淼.固相萃取-超高效液相色谱-串联质谱法同时测定畜禽粪便中的23种抗生素残留[J].理化检验-化学分册, 2018,54(3):337-344.
【2】姚倩钰,贺德春,龚道新,等.高效液相色谱-串联质谱法测定废水中5种喹诺酮类抗生素[J].中国环境监测, 2017,33(3):139-146.
【3】王云鹏,马越.养殖业抗生素的使用及其潜在危害[J].中国抗生素杂志, 2008,33(9):519-523.
【4】周启星,罗义,王美娥.抗生素的环境残留、生态毒性及抗性基因污染[J].生态毒理学报, 2007,2(3):243-251.
【5】胡冠九,穆肃,赵永刚,等.南京典型县区饮用水源抗生素含量特征[J].环境化学, 2015,34(1):192-193.
【6】KVMMERER K. Significance of antibiotics in the environment[J]. Journal of Antimicrobial Chemotherapy, 2003,52(1):5-7.
【7】王琦,武俊梅,彭晶倩,等.饮用水系统中药物和个人护理用品的研究进展[J].环境化学, 2018,37(3):453-461.
【8】孙艳侠.高效液相色谱在乳品抗生素残留检测中的应用[J].山西农业科学, 2010,38(3):10-13.
【9】刘靖靖,林黎明,江志刚,等.高效液相色谱法同时检测8种喹诺酮类兽药残留量[J].分析试验室, 2007,26(8):5-9.
【10】高立红,史亚利,厉文辉,等.高效液相色谱-电喷雾串联质谱法检测环境水样中22种抗生素类药物[J].色谱, 2010,28(5):491-497.
【11】刘玉春,徐维海,余莉莉,等.固相萃取液相色谱-质谱/质谱联用测定河水中大环内酯类抗生素[J].分析测试学报, 2006,25(2):1-5.
【12】吴小莲,包艳萍,向垒,等.固相萃取-高效液相色谱-串联质谱法同时测定蔬菜中8种磺胺类抗生素[J].环境化学, 2013,32(6):1038-1044.
【13】钟冬莲,丁明,汤富彬,等.高效液相色谱-电喷雾串联质谱法测定畜禽粪便中四环素类抗生素[J].分析科学学报, 2014,30(3):433-436.
【14】罗庆,孙丽娜,胡筱敏.固相萃取-高效液相色谱法测定畜禽粪便中罗红霉素和3种四环素类抗生素[J].分析试验室, 2014,33(8):885-888.
【15】陈乾,刘洋,肖丽君,等.超高效液相色谱串联质谱法同时测定叶菜中13种抗生素[J].环境科学, 2020,41(2):952-961.
【16】陈小平,邓小娟,李文斌,等.固相萃取-超高效液相色谱-串联质谱法测定水中13种抗生素的含量[J].理化检验-化学分册, 2017,53(5):542-547.
【17】石奥,张建淼.固相萃取-超高效液相色谱-串联质谱法同时测定畜禽粪便中的23种抗生素残留[J].理化检验-化学分册, 2018,54(3):337-344.
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