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1976年7月10日工业事故后在塞韦索检测2,3,7,8-四氯二苯并对二噁英的分析程序。

Analytical procedures to detect 2,3,7,8-TCDD at Seveso after the industrial accident of July 10, 1976.

作者信息

Cattabeni F, di Domenico A, Merli F

出版信息

Ecotoxicol Environ Saf. 1986 Aug;12(1):35-52. doi: 10.1016/0147-6513(86)90005-9.

Abstract

The analytical procedures used at Seveso (Milan, Italy) for the determination of 2,3,7,8-TCDD, and some isomers, in biological and environmental samples are reviewed in this paper. During the emergency period, up until the first 10 days of August, the extracts, mostly from soil or vegetation samples, were evaporated to dryness and then mixed with less than or equal to 10-ml solvent. Of these solutions, aliquots up to 10 microliter were injected into a low-resolution gas chromatograph (GC) combined with a low-resolution mass spectrometer (MS). Analytical sensitivity for vegetation and soil was less than 10 ppb and approximately 100 ppt, respectively--sufficient for the early mapping of the most heavily contaminated territory. After the emergency period, the greatest improvement in environmental sample analysis was the introduction of cleanup procedure which greatly reduced the presence of unwanted material in samples. Cleanup was followed by the complete removal of the solvent. Dry samples could be taken up with rather small volumes (greater than or equal to 0.1 ml) of solvent, of which an aliquot was used for GC-MS analysis. The instrumental setup was kept as above. For animal samples, extraction entailed preliminary alkaline digestion followed by a number of cleanup steps. The final dry sample was taken to desired volume by adding solvent (greater than or equal to 0.1 ml), of which a few microliters were injected in GC-MS apparatuses. Detection thresholds improved markedly and were less than 10 ppt for agricultural soil and sediment, less than or equal to 0.05 ppt for water, in the range of 60 to 200 ppt for air dust, less than 10 ng/m2 and 10 ppt for wipe and scrape tests, respectively, less than 50 ppt for vegetation, and 250 ppt for biological substrata. Major later improvements in TCDD assay were the use of high-resolution gas chromatography (hrGC-MS), in some cases combined with high-resolution mass spectrometry (hrGC-hrMS). This provided greater specificity, sometimes accompanied by a very marked increase in detection sensitivity.

摘要

本文回顾了意大利米兰塞韦索用于测定生物和环境样品中2,3,7,8-四氯二苯并二恶英及某些异构体的分析程序。在应急期间,直到8月的前10天,提取物(主要来自土壤或植被样品)被蒸发至干,然后与体积小于或等于10毫升的溶剂混合。从这些溶液中,取至多10微升的等分试样注入与低分辨率质谱仪(MS)联用的低分辨率气相色谱仪(GC)中。植被和土壤的分析灵敏度分别小于10 ppb和约100 ppt——足以对污染最严重的区域进行早期测绘。应急期过后,环境样品分析最大的改进是引入了净化程序,这大大减少了样品中不需要物质的存在。净化后将溶剂完全去除。干燥的样品可用相当少量(大于或等于0.1毫升)的溶剂溶解,取其中一份等分试样用于GC-MS分析。仪器设置保持如上所述。对于动物样品,提取需要先进行碱性消化,然后进行一系列净化步骤。最终的干燥样品通过加入溶剂(大于或等于0.1毫升)达到所需体积,取几微升注入GC-MS仪器中。检测限显著提高,农业土壤和沉积物的检测限小于10 ppt,水的检测限小于或等于0.05 ppt,空气粉尘的检测限在60至200 ppt范围内,擦拭和刮擦试验的检测限分别小于10 ng/m²和10 ppt,植被的检测限小于50 ppt,生物基质的检测限为250 ppt。后来,TCDD测定的主要改进是使用高分辨率气相色谱(hrGC-MS),在某些情况下与高分辨率质谱(hrGC-hrMS)联用。这提供了更高的特异性,有时还伴随着检测灵敏度的显著提高。

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