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串联四极杆质谱(GC-QqQ-MS/MS)测定土壤中的有机氯农药和多氯联苯 总被引:6,自引:1,他引:5
建立了用加速溶剂萃取仪(ASE)萃取、凝胶渗透色谱(GPC)净化、气相色谱/串联四极杆质谱多反应监测、同时测定土壤中17种有机氯农药和19种多氯联苯的方法.加标浓度在3.3μg/kg时的平均回收率在79.6%~93.2%之间,相对标准偏差在2.9%~13.0%之间,定量限在0.01~0.51μg/kg之间.在检测土壤样品中的有机氯农药和多氯联苯残留方面,Gc-QqQ-MS/MS相对于气相色谱/电子捕获检测器(GC-ECD)和GC-MS的选择离子检测(SIM)模式具有非常明显的优势,尤其是在低浓度水平的定性和定量方面. 相似文献
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气相色谱法同时分析测定土壤中15种有机氯农药残留 总被引:4,自引:1,他引:3
采用石油醚+丙酮(3+1,V/V)作为提取溶剂、硫酸钠溶液与弗罗里藻土净化,气相色谱法同时测定贵州150个土壤背景点15种有机氯农药残留.峰面积与保留时间的精密度分别为1.14~5.15,0.01~0.09;线性关系均在0.99以上;加标回收率为84.3%~127.8%;方法检出限为0.003~0.025ng/g.该方法适用于土壤背景点有机氯农药残留量的分析. 相似文献
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超声波萃取-气相色谱/质谱法测定土壤中15种Pops类有机氯农药 总被引:2,自引:1,他引:1
用探头式超声波萃取仪、己烷/丙酮混合溶剂提取土壤中的15种Pops类有机氯农药(包括六氯苯、七氯、六六六、氯丹、艾氏剂、狄氏剂、异狄氏剂、灭蚁灵、滴滴涕),萃取溶液经氟罗里硅土柱净化、氮吹浓缩,用气相色谱/质谱仪(GC-MS)进行测定。方法检出限0.4~1.4μg/kg,空白样品有机氯农药加标回收率为52.8%~118%、有机氯标记替代物回收率为71.0%~122%,RSD为6.8%~16.5%。 相似文献
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采用气相色谱法对北京市官厅水库沉积物表层中持久性有机氯农药(OCPs)的残留状况进行了调查,并对有机氯农药污染水平和生态风险作出评价。结果表明:沉积物中有机氯农药总含量为8.48 ng/g~24.40 ng/g,其中HCHs和DDTs的含量较高,分别为1.11 ng/g~7.73 ng/g和2.97 ng/g~10.52 ng/g,其组分特征为来自环境的残留。与沉积物风险评估低值(ERL)和风险评估中值(ERM)对比评价沉积物中有机污染物的风险程度,官厅水库沉积物表层中的有机氯农药存在一定的生态风险。 相似文献
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采用固相萃取-气相色谱-质谱法(SPE-GC-MS)同时测定水中26种有机氯农药和8种氯苯类化合物,通过选择合适的SPE小柱、优化固相萃取和仪器检测的条件,使该方法在0.050 0 mg/L~1.00 mg/L范围内线性良好。各目标物的方法检出限为0.021μg/L~0.069μg/L,空白水样的加标回收率为36.6%~133%,RSD为0.5%~12.4%。 相似文献
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采用固相萃取(SPE)技术,结合气相色谱/质谱(GC-MS)选择离子检测法(SIM)对水样中26种有机氯农药(OCPs)进行提取、净化、浓缩前处理,优选了固相萃取小柱填料及萃取、净化条件,优化了GC-MS的工作参数,建立了地下水中26种有机氯农药的SPE-GC-MS分析方法。针对不同的组分,本法加标回收率为76.422%~112.512%,相对标准偏差为4.905%~15.524%,检出限为0.014~0.089μg/L。该方法操作简单,消耗费用低,分析速度快,具有较高的灵敏度和回收率。 相似文献
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采用快速溶剂提取-Florisil固相萃取柱净化-气相色谱法测定土壤中多氯联苯单体,探讨了有机氯农药对测定的干扰。方法在0ug/L-100ug/L范围内线性良好,19种多氯联苯单体的检出限为0.06ug/kg-0.36ug/kg,基体加标回收率为78.6%-120%,RSD为0.2%-5.1%。 相似文献
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论述了气相色谱法测定水中微量多氯联苯及有机氯农药的方法步骤,该方法灵敏度、准确度均能达到微量分析的要求.整个测定过程需60min,所测组分共15种,检出限在1~8ng/L范围内. 相似文献
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针对目前室内环境监测工作出现的种种问题,就如何规范的开展室内环境监测工作,更好地为社会提供真实、准确、有效的监测数据,本文提出相关的探讨。 相似文献
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Peter Timmerman 《Environmental monitoring and assessment》1998,49(2-3):111-122
The social and economic implications of atmospheric change on biodiversity need to be seen in a global context of major shifts in the conceptualization and management of our relationship with nature. Traditionally, we have conceptualized the atmosphere and the other creatures of the biosphere as separate from the human, but their quasi-autonomy is now becoming subject to more and more human management. This raises not only economic issues, but social, political, and ethical concerns that will have substantial influence on public policy. Among these are the commodification of genetic material; the privatization of traditional knowledge; and the management of information. In this broader context, the paper examines an array of current and proposed strategies of response to changes in biodiversity as a result of climatic and other stresses. 相似文献
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Canada responded to the Global Biodiversity Convention by completing the Canadian Biodiversity Strategy in 1995. At the same time, Environment Canada also completed a national Science Assessment on Biodiversity. During this period, the Smithsonian Institution, in partnership with Parks and Environment Canada, initiated the implementation of a global biodiversity monitoring program in Canada. Under the auspices of the United Nations Man and the Biosphere Program, the SI/MAB monitoring protocols and plots have spread across Canada at an unprecedented rate. National champions in the science and educational sectors, working within an inter-disciplinary ecological framework, have guided the development, education, quality control and sharing of atmosphere-biodiversity observations electronically.Atmospheric-Biodiversity Networks and Networking have traditionally operated within separate mandates with little degree of integration. Air-Bio Networks were designed within an integrated framework to better understand the atmospheric stress on biodiversity and the adaptation actions, nationally and regionally. Detailed examples of the cumulative effects of climate change, stratospheric ozone depletion, acid deposition, ground-level ozone, suspended particulate matter and hazardous air pollutants on biodiversity will be discussed using a Southern Ontario case study. In addition, recommendations will be presented for future paired SI/MAB plots, linked networks and networking for adaptation within the context of climate, chemical and ecological gradients. 相似文献
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Xiangyun Liu Yan Yang Ying Cui Huijun Zhu Xiong Li Zhining Li Kankan Zhang Deyu Hu 《Environmental monitoring and assessment》2014,186(8):5307-5313
A simple and accurate method of determining metalaxyl and cymoxanil in pepper and soil was developed by ultra-performance liquid chromatography–photodiode array detection. The limits of detection were 0.015 mg/kg for metalaxyl and 0.003 mg/kg for cymoxanil. The limits of quantification were 0.05 mg/kg for metalaxyl in pepper and soil as well as 0.01 mg/kg for cymoxanil in pepper and soil. Recoveries of pepper and soil were investigated at three spiking levels and ranged within 77.52 to 102.05 % for metalaxyl and 87.15 to 103.21 % for cymoxanil, with relative standard deviations below 9.30 %. For field experiments, the half-lives of metalaxyl were 3.2 to 3.9 days in pepper and 4.4 to 9.5 days in soil at the three experimental locations in China. At harvest, pepper samples were found to contain metalaxyl and cymoxanil well below the maximum residue limit MRLs of the European Union (EU) following the recommended dosage and the interval of 21 days after last application. 相似文献
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Junxue Wu Hongyan Zhang Kai Wang Chengju Wang 《Environmental monitoring and assessment》2014,186(2):1195-1202
A simple and accurate method for the determination of bismerthiazol and its metabolite 2-amino-5-mercapto-1,3,4-thiadiazole was developed in Chinese cabbage and soil by high-performance liquid chromatography-diode array detection in this study. The limits of detection were 0.06 mg/kg for bismerthiazol and 0.03 mg/kg for 2-amino-5-mercapto-1,3,4-thiadiazole, respectively. Recoveries of cabbage and soil were investigated at three spiking levels and were in the range of 84.0–96.0 % for bismerthiazol and 71.0–74.6 % for 2-amino-5-mercapto-1,3,4-thiadiazole, with relative standard deviations below 7.0 %. For field experiments, the half-life of bismerthiazol was 2.4–2.5 days in Chinese cabbage and 2.5–4.8 days in soil at the two experimental locations in China. Dissipation residues of 2-amino-5-mercapto-1,3,4-thiadiazole were lower than 0.72 mg/kg. Terminal residues of bismerthiazol and its metabolite were less than 3.0 and 0.3 mg/kg in Chinese cabbage, respectively. No bismerthiazol or metabolite residues were detected in soil on days 5, 7, 10, and 14 after the last spraying at the two dosage levels. 相似文献
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Lin Wang Wenming Li Puyu Li Minghui Li Shuo Chen Lijun Han 《Environmental monitoring and assessment》2014,186(11):7793-7799
A simple residue analytical method using the quick, easy, cheap, effective, rugged, and safe (QuEChERS) procedure for the determination of trifloxystrobin and its metabolite trifloxystrobin acid (CGA321113) in tomato and soil was developed using high-performance liquid chromatography-tandem mass spectrometry (HPLC-MS/MS). The limits of detection were 0.0005 mg/kg for trifloxystrobin and 0.001 mg/kg for trifloxystrobin acid, respectively. The average recoveries in tomato and soil ranged from 73–99 % for trifloxystrobin and 75–109 % for trifloxystrobin acid, with relative standard deviations below 15 %. The method was then used to study the dissipation and residues in tomato and soil. The dissipation half-lives of trifloxystrobin in tomato were 2.9 days (Beijing) and 5.4 days (Shandong), while in soil were 1.9 days (Beijing) and 3.0 days (Shandong), respectively. The final results showed that the major residue compound was trifloxystrobin in tomato whereas it was its metabolite, trifloxystrobin acid, in soil. The final residues of total trifloxystrobin (including trifloxystrobin acid) were below the EU maximum residue limit of 0.5 mg kg?1 in tomato 3 days after the treatment. 相似文献