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    田露, 陈学国, 吴浩天, 安国策. 基于玉米芯生物炭的磁性固相萃取-气相色谱-质谱法测定环境水中13种三嗪类除草剂的含量[J]. 理化检验-化学分册, 2024, 60(8): 749-757. DOI: 10.11973/lhjy-hx230664
    引用本文: 田露, 陈学国, 吴浩天, 安国策. 基于玉米芯生物炭的磁性固相萃取-气相色谱-质谱法测定环境水中13种三嗪类除草剂的含量[J]. 理化检验-化学分册, 2024, 60(8): 749-757. DOI: 10.11973/lhjy-hx230664
    TIAN Lu, CHEN Xueguo, WU Haotian, AN Guoce. Determination of 13 Triazine Herbicides in Environmental Water by Gas Chromatography-Mass Spectrometry with Magnetic Solid Phase Extraction Based on Corn Cob Biochar[J]. PHYSICAL TESTING AND CHEMICAL ANALYSIS PART B:CHEMICAL ANALYSIS, 2024, 60(8): 749-757. DOI: 10.11973/lhjy-hx230664
    Citation: TIAN Lu, CHEN Xueguo, WU Haotian, AN Guoce. Determination of 13 Triazine Herbicides in Environmental Water by Gas Chromatography-Mass Spectrometry with Magnetic Solid Phase Extraction Based on Corn Cob Biochar[J]. PHYSICAL TESTING AND CHEMICAL ANALYSIS PART B:CHEMICAL ANALYSIS, 2024, 60(8): 749-757. DOI: 10.11973/lhjy-hx230664

    基于玉米芯生物炭的磁性固相萃取-气相色谱-质谱法测定环境水中13种三嗪类除草剂的含量

    Determination of 13 Triazine Herbicides in Environmental Water by Gas Chromatography-Mass Spectrometry with Magnetic Solid Phase Extraction Based on Corn Cob Biochar

    • 摘要: 以玉米芯为母体,通过化学沉淀法制备磁性玉米芯生物炭材料,并采用扫描电子显微镜、透射电子显微镜和红外光谱仪表征。取环境水样5.0 mL,加入150 mg磁性玉米芯生物炭材料,涡旋4 min,在试管底部外壁放置磁铁,吸附磁性玉米芯生物炭材料,将上层清液全部弃去。加入1.0 mL水,涡旋1 min,弃去溶液。加入1.0 mL乙酸乙酯(洗脱剂),涡旋4 min,收集乙酸乙酯洗脱液,按照气相色谱-质谱法测定。结果显示,合成的磁性玉米芯生物炭材料具有丰富的孔隙结构,近似球形的Fe3O4颗粒均匀分布在玉米芯生物炭的表面,对三嗪类除草剂的吸附过程符合朗缪尔等温吸附模型,其吸附机理为单层吸附,最大理论吸附容量为0.604 mg·g−1。13种三嗪类除草剂的质量浓度分别在0.05~10.00 mg·L−1(脱乙基莠去津、莠去通、莠去津、敌草净、嗪草酮、西草净、莠灭净、扑草净、特丁净、异丙净和氰草津)和0.02~10.00 mg·L−1(特丁通和环嗪酮)内和峰面积呈线性关系,检出限(3S/N)为0.01~0.02 mg·L−1;按照标准加入法进行回收试验,回收率为87.1%~110%,测定值的相对标准偏差(n=6)为1.8%~5.6%(日内精密度试验结果)和2.9%~7.9%(日间精密度试验结果)。方法用于疑似投毒环境水样的分析,检出了扑草净,检出量为5.3 g·L−1

       

      Abstract: Magnetic corn cob biochar material was prepared by chemical precipitation method using corn cob as the parent material, and characterized by scanning electron microscopy, transmission electron microscopy, and infrared spectroscopy. The 5.0 mL of environmental water sample was taken, and 150 mg of magnetic corn cob biochar material was added. After vortex for 4 min, a magnet on the outer wall of the bottom of the test tube was placed to adsorb the magnetic corn cob biochar material, and all the upper clear liquid was discarded. Then 1.0 mL of water was added, and the mixture was vortexed for 1 min. The solution was discarded, and 1.0 mL of ethyl acetate (eluant) was added. The mixture was vortexed for 4 min, and the ethyl acetate eluate was collected, and determined by gas chromatography-mass spectrometry. It was shown that the synthesized magnetic corn cob biochar material had a rich pore structure, and approximately spherical Fe3O4 particles evenly distributed on the surface of the corn cob biochar. The adsorption process of triazine herbicides conformed to the Langmuir isotherm adsorption model, and its adsorption mechanism was single-layer adsorption, with the maximum theoretical adsorption capacity of 0.604 mg·g−1. Linear relationships between values of the mass concentration and the peak area of 13 triazine herbicides were kept in the ranges of 0.05-10.00 mg·L−1 (altrazinedesethyl, atraton, atrazine, desmetryn, metribuzin, simetryn, ametryn, prometryn, terbutryn, dipropetryn, and cyanazine) and 0.02-10.00 mg·L−1 (terbumeton and hexazinone), with detection limits (3S/N) in the range of 0.01-0.02 mg·L−1. Test for recovery was made according to the standard addition method, giving recoveries in the range of 87.1%-110%, and RSDs (n=6) of the determined values were found in the ranges of 1.8%-5.6% (results for test of intra-day precision) and 2.9%-7.9% (results for test of inter-day precision). The proposed method was used for the analysis of suspected toxic environmental water samples, and prometryn was detected with the detected amount of 5.3 g·L−1.

       

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