Halasz A, Groom C, Zhou E, Paquet L, Beaulieu C, Deschamps S, Corriveau A, Thiboutot S, Ampleman G, Dubois C, Hawari Jalal
Biotechnology Research Institute, National Research Council Canada, Montreal, Quebec.
J Chromatogr A. 2002 Jul 19;963(1-2):411-8. doi: 10.1016/s0021-9673(02)00553-8.
Polynitro organic explosives [hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX), octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX) and 2,4,6-trinitrotoluene (TNT)] are typical labile environmental pollutants that can biotransform with soil indigenous microorganisms, photodegrade by sunlight and migrate through subsurface soil to cause groundwater contamination. To be able to determine the type and concentration of explosives and their (bio)transformation products in different soil environments, a comprehensive analytical methodology of sample preparation, separation and detection is thus required. The present paper describes the use of supercritical carbon dioxide (SC-CO2), acetonitrile (MeCN) (US Environmental Protection Agency Method 8330) and solid-phase microextraction (SPME) for the extraction of explosives and their degradation products from various water, soil and plant tissue samples for subsequent analysis by either HPLC-UV, capillary electrophoresis (CE-UV) or GC-MS. Contaminated surface and subsurface soil and groundwater were collected from either a TNT manufacturing facility or an anti-tank firing range. Plant tissue samples were taken fromplants grown in anti-tank firing range soil in a greenhouse experiment. All tested soil and groundwater samples from the former TNT manufacturing plant were found to contain TNT and some of its amino reduced and partially denitrated products. Their concentrations as determined by SPME-GC-MS and LC-UV depended on the location of sampling at the site. In the case of plant tissues, SC-CO2 extraction followed by CE-UV analysis showed only the presence of HMX. The concentrations of HMX (<200 mg/kg) as determined by supercritical fluid extraction (SC-CO2)-CE-UV were comparable to those obtained by MeCN extraction, although the latter technique was found to be more efficient at higher concentrations (>300 mg/kg). Modifiers such as MeCN and water enhanced the SC-CO2 extractability of HMX from plant tissues.
多硝基有机炸药[六氢-1,3,5-三硝基-1,3,5-三嗪(RDX)、八氢-1,3,5,7-四硝基-1,3,5,7-四氮杂环辛烷(HMX)和2,4,6-三硝基甲苯(TNT)]是典型的易分解环境污染物,它们可与土壤中的原生微生物发生生物转化,经阳光光解,并通过地下土壤迁移从而造成地下水污染。因此,为了能够测定不同土壤环境中炸药及其(生物)转化产物的类型和浓度,需要一种涵盖样品制备、分离和检测的综合分析方法。本文介绍了使用超临界二氧化碳(SC-CO₂)、乙腈(MeCN)(美国环境保护局方法8330)和固相微萃取(SPME)从各种水、土壤和植物组织样品中提取炸药及其降解产物,随后通过高效液相色谱-紫外检测(HPLC-UV)、毛细管电泳-紫外检测(CE-UV)或气相色谱-质谱联用(GC-MS)进行分析。受污染的地表和地下土壤以及地下水取自一个TNT制造工厂或一个反坦克靶场。植物组织样品取自温室实验中生长在反坦克靶场土壤中的植物。来自原TNT制造工厂的所有测试土壤和地下水样品均被发现含有TNT及其一些氨基还原和部分脱硝产物。通过SPME-GC-MS和LC-UV测定的它们的浓度取决于现场采样的位置。就植物组织而言,SC-CO₂萃取后进行CE-UV分析仅显示存在HMX。通过超临界流体萃取(SC-CO₂)-CE-UV测定的HMX浓度(<200 mg/kg)与通过MeCN萃取获得的浓度相当,尽管发现后一种技术在较高浓度(>300 mg/kg)时效率更高。乙腈和水等改性剂提高了SC-CO₂从植物组织中萃取HMX的能力。