Lao Wenjian
Southern California Coast Water Research Project, Costa Mesa 92626, CA. USA.
Se Pu. 2013 Jul;31(7):667-73. doi: 10.3724/sp.j.1123.2013.06030.
Toxaphene quantification incorporating gas chromatography/negative chemical ionization mass spectrometry (GC/NCI-MS) offers improved sensitivity and specificity. The U. S. Environmental Protection Agency (USEPA) recently released a GC/NCI-MS method (Method 8276) for the measurement of technical toxaphene and eight specific congeners (Hx-Sed, Hp-Sed, P26, P41, P40, P44, P50 and P62). However, there is still lack of a practical and complete analytical method including sample extraction, clean up, instrumental analysis, and data analysis. The goal of this work was to develop a ready-to-use method for the quantification of total toxaphene and the eight congeners. Sediment and salmon fish tissue were selected as sample matrices and extracted with methylene chloride using an accelerated solvent extraction system. The sample extracts were cleaned up with active copper powder or gel permeation chromatography, and finally silica/alumina combination column. Separation was performed on a DB-XLB column. GC/NCI-MS was operated under selected ion monitoring mode with an identical set of confirmation and quantitation ions for total toxaphene and the eight congeners. Oxygen reaction of polychlorinated biphenyls (PCB) was monitored by PCB204, an internal calibration standard, and the reaction level was kept below 1%. Average relative response factors were used in quantitation. Quantitation of total toxaphene employed the sum of all detectable (S/N > or = 3) 6-C1 to 10-Cl homolog peak areas, while the individual congeners were quantified followed the standard procedures for single analytes. Multi-point calibration solutions ranged from 0. 5 (5 for P62) to 500 microg/L for the individual congeners, and 50 to 500 microg/L for technical toxaphene, with the lowest calibration levels as lower limits of quantitation. Average congener recovery was (90.8 +/- 17.4)% (n =10) in spiked sediment with relative standard deviations of 5.4% - 12.8% (n =10), underscoring an excellently accurate and precise method. The method was applied to analyze sediment and fish tissue sample.
采用气相色谱/负化学电离质谱法(GC/NCI-MS)进行毒杀芬定量分析,可提高灵敏度和特异性。美国环境保护局(USEPA)最近发布了一种GC/NCI-MS方法(方法8276),用于测定工业用毒杀芬和8种特定同系物(六氯-Sed、七氯-Sed、P26、P41、P40、P44、P50和P62)。然而,目前仍缺乏一种实用且完整的分析方法,包括样品萃取、净化、仪器分析和数据分析。本研究的目的是开发一种现成可用的方法,用于定量分析总毒杀芬和8种同系物。选择沉积物和鲑鱼组织作为样品基质,使用加速溶剂萃取系统用二氯甲烷进行萃取。样品提取物用活性铜粉或凝胶渗透色谱法净化,最后用硅胶/氧化铝组合柱净化。在DB-XLB柱上进行分离。GC/NCI-MS在选择离子监测模式下运行,对总毒杀芬和8种同系物使用一组相同的确认离子和定量离子。通过内部校准标准物多氯联苯(PCB)204监测多氯联苯的氧反应,反应水平保持在1%以下。定量分析中使用平均相对响应因子。总毒杀芬的定量采用所有可检测到的(信噪比≥3)6个氯原子至10个氯原子同系物峰面积之和,而单个同系物则按照单分析物的标准程序进行定量。单个同系物的多点校准溶液浓度范围为0.5(P62为5)至500μg/L,工业用毒杀芬为50至500μg/L,最低校准水平作为定量下限。在加标沉积物中,同系物的平均回收率为(90.8±17.4)%(n = 10),相对标准偏差为5.4% - 12.8%(n = 10),突出了该方法具有极高的准确性和精密度。该方法应用于分析沉积物和鱼类组织样品。