MAE/GC-MS测定底泥中PCBs的研究

采用微波辅助萃取、气相色谱柱分离、质谱检测器检测底泥中PCBs的含量.通过实验对微波辅助参数优化,研究表明优化后的微波辅助萃取法不仅能够取得与索氏萃取法相当的效果,而且它还具有溶剂用量少、提取时间短等优点,是提取底泥中PCBs较好的方法.     

多氯联苯对我国土壤微生物的生态毒理效应

作为持久性有机污染物(POPs),多氯联苯(PCBs)一旦进入土壤将长期存留并对土栖生物产生潜在危害。土壤微生物是土壤生态系统重要组成部分,研究外源PCBs对土壤微生物的生态毒理效应,筛选出指示PCBs污染的敏感指标并获取可靠的生态毒理数据十分重要。研究以江西红壤和天津潮土为供试土壤,在室内25℃连续培养28 d的条件下进行了生态毒理实验,选择了微生物量碳、呼吸强度、代谢熵、硝化作用、脱氢酶活性、脲酶活性和微生物群落功能多样性为微生物指标。结果显示:1)在28 d培养时间内,多氯联苯(PCBs)的毒性作用随培养时间的延长而增强,且在红壤中的毒性作用强于在潮土中,表明PCBs对土壤微生物的毒性作用存在时间效应并受土壤性质的影响。2)各微生物指标的敏感性不同,微生物量碳、脲酶活性和微生物功能多样性对PCBs污染反应不够敏感,而土壤呼吸强度、代谢熵、硝化作用和脱氢酶活性对PCBs污染反应敏感。3)14 d时,红壤中PCBs对脱氢酶活性、呼吸强度和代谢熵的EC10值分别为1.20、3.18和1.09 mg·kg-1,而在潮土中分别为6.31、4.73和50 mg·kg-1;28 d时,红壤中PCBs对硝化作用、脱氢酶活性、呼吸强度和代谢熵的EC10值分别为2.32、0.77、0.51和0.71mg·kg-1,而在潮土中分别为5.91、1.65、3.00和50 mg·kg-1。综合考虑经济和实际需要等因素,建议将呼吸强度、硝化作用和脱氢酶活性作为PCBs污染土壤生态毒理评价中的首选敏感指标,并建议培养时间设置为28 d。     

几类有机污染物的微塑料/水分配系数的线性溶解能关系模型

水体中的微塑料会吸附其中的有机污染物,影响有机污染物和微塑料的环境归趋和生态毒性。研究微塑料对有机污染物的吸附行为,对于评价有机污染物和微塑料的环境赋存、迁移及生物有效性有重要意义。污染物在微塑料与水之间的平衡分配系数(Kd),是表征微塑料对有机污染物吸附能力的重要参数。实验方法难以逐个测定众多有机污染物的Kd值,有必要发展其预测模型。本研究搜集了有机污染物的线性溶解能关系(LSER)参数及Kd值,构建了可预测有机污染物在聚丙烯微塑料与海水、聚乙烯微塑料与海水、聚乙烯微塑料与淡水之间Kd值的LSER模型。模型具有良好的拟合优度(R2adj介于0.794~0.903)、稳健性(Q2LOO和Q2BOOT分别介于0.763~0.863和0.720~0.804)和预测能力(R2ext和Q2ext分别介于0.886~0.971和0.825~0.954),能够用于预测多氯联苯、多环芳烃、六氯环已烷和氯苯类有机污染物的Kd值。     

天津塘沽海滨浴场沉积物中POPs的垂直分布

应用GC-MS对渤海湾潮间带天津塘沽海滨浴场沉积物中的多环芳烃、有机氯农药、多氯联苯和多溴联苯醚等持久性有机污染物的垂直分布进行了研究.4类污染物的污染水平依次为PAHs>OCPs>PCBs>PBDEs,其质量分数范围分别为113.1～1 040.0和7.6～118.1 ng/g,715.0～7 048.3和10.0～158.2 pg/g(以干质量计). 在0～50 cm深度,w(PAHs)相对较高且变化较大,50 cm以下深度,w(PAHs)逐渐降低且变化较小.在测定的16种PAHs中w(菲)最高,并随深度的增加而降低.污染源解析表明,PAHs的污染主要来自石油输入和煤、木炭等的燃烧. OCPs的垂直分布与PAHs类似,在定量的20种OCPs中,w(HCB)最高,其次是w(HCHs)和w(DDTs);研究表明HCHs和DDT没有新的输入. 在0～70 cm深度,w(PCBs)低且变化小,70～80 cm深度突增1个数量级. w(PBDEs)较w(PCBs)低1个数量级,在5～10 cm深度污染水平最高.      

Thirty year monitoring of PCBs, organochlorine pesticides and tetrabromodiphenylether in eel from The Netherlands

Because of their excellent properties as a biomonitor, yellow eels (Anguilla anguilla) have been used for time-trend monitoring of polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs) and tetrabrominated diphenylether (tetra-BDE). The program has now lasted for thirty years and has delivered valuable information on trends and spatial differences of these compounds in the delta of the rivers Rhine and Meuse and other Dutch canals, rivers and lakes. Specific local PCB, HCH and dieldrin contaminations were identified. Temporal trends show a slow decrease of PCB concentrations since 1977. Eels from the rivers Rhine and Meuse still exceed present European maximum residue limits for dioxin-like PCBs. Apart from some exceptions, OCP and tetra-BDE concentrations have also decreased, and more than those of PCBs. Fat contents of eel have decreased from an average of 21 to ca. 13%. This decrease in fat contents, coincides with the strong reduction of the European eel stock.     

Confirmation of polychlorinated biphenyl (PCB) distribution in the blood and verification of simple quantitative method for PCBs based on specific congeners

We measured the concentration of each polychlorinated biphenyl (PCB) congener in whole blood, plasma and blood cells, and investigated the distribution of PCBs in human blood using high-resolution gas chromatography/high-resolution mass spectrometry (HRGC/HRMS). The PCB concentrations in plasma and whole blood in terms of lipid concentrations were almost equal, with a correlation coefficient of r = 0.972. In the blood, the ratio of PCBs in blood cells to those in plasma was generally about 1:9 and the congener distribution patterns in blood cells and plasma were similar.We performed verification of a simple mass screening method by obtaining information on the main PCB congeners for investigations on human accumulation and exposure. The total concentration of the seven PCB congeners (UNEP-7) proposed to the United Nations Environment Programme (UNEP) by Muir and Morita was about 50% of the total concentration of all PCB congeners, and UNEP-30 was about 80%. The seven main congeners in the blood (MCB-7) showed a value that was about 60%, and MCB-30 showed a value that was about 90%. Determinations with the main congeners in the blood showed a correlation of r = 0.990 or more between the main eight congeners (MCB-7 plus #74) and the total PCB concentration for all congeners. The results suggest that, although total PCB concentration can be effectively estimated from the main seven congeners, the main eight congeners would be preferable, and that the use of these congeners in the simple mass screening method would be effective for populations in areas uncontaminated by PCBs.     

Spatial distribution of organochlorine contaminants in soil, sediment, and fish in Bikini and Enewetak Atolls of the Marshall Islands, Pacific Ocean

Several nuclear tests were performed at Enewetak and Bikini Atolls in the Marshall Islands between 1946 and 1958. The events at Bikini Atoll involved several ships that were tested for durability during nuclear explosions, and 24 vessels now rest on the bottom of the Bikini lagoon. Nine soil samples were collected from different areas on the two islands of the atoll, and eighteen sediment, nine fish, and one lobster were collected in the vicinity of the sunken ships. Organochlorine pesticides (OCPs), polychlorinated biphenyls (PCBs), and polychlorinated terphenyls (PCTs) in these samples were analyzed using gas chromatography/ion trap mass spectrometry (GC/ITMS). The average recoveries ranged from 78% to 104% for the different PCB congeners. The limits of detection (LOD) for PCBs, PCTs, DDE, DDT, and dieldrin ranged 10-50 pg g⁻¹. Some fish from Enewetak contained PCBs at a concentration range of 37-137 ng g⁻¹, dry weight (dw), and most of the soils from Enewetak showed evidence of PCBs (22-392 ng g⁻¹ dw). Most of the Bikini lagoon sediment samples contained PCBs, and the highest was the one collected from around the Saratoga, an aircraft carrier (1555 ng g⁻¹ dw). Some of the fish samples, most of the soil samples, and only one of the sediment samples contained 2,2-bis(4-chlorophenyl)-1,1-dichloroethylene (DDE) and PCBs. In addition to PCBs, the soils from Enewetak Atoll contained PCTs. PCTs were not detected in the sediment samples from Bikini Atoll. The results suggest local pollution sources of PCBs, PCTs, and OCPs.     

Environmental site assessments and audits: Building inspection requirements

Environmental site assessment criteria were originally developed by organizations that focused, almost exclusively, on surface, subsurface, and pollution source contamination. Many of the hazards associated with indoor environments and building structures were traditionally not considered when evaluating sources and entities of environmental pollution. Since a large number of building materials are potentially hazardous, careful evaluation is necessary. Until recently, little information on building inspection requirements of environmental problems has been published. Traditionally, asbestos has been the main component of concern. The ever-changing environmental standards have dramatically expanded the scope of building surveys. Indoor environmental concerns, for example, currently include formaldehyde, lead-based paint, polychlorinated biphenyls, radon, and indoor air pollution. Environmental regulations are being expanded and developed that specifically include building structures. These regulatory standards are being triggered by an increased awareness of health effects from indoor exposure, fires, spills, and other accidents that have resulted in injury, death, and financial loss. This article discusses various aspects of assessments for building structures.     

Modeling urban films using a dynamic multimedia fugacity model

A thin film coats impervious urban surfaces that can act as a source or sink of organic pollutants to the greater environment. We review recent developments in the understanding of film and film-associated pollutant behavior and incorporate them into an unsteady-state version of the fugacity based Multimedia Urban Model (MUM), focusing on detailed considerations of surface film dynamics. The model is used to explore the conditions under which these atmospherically-derived films act as a temporary source of chemicals to the air and/or storm water. Assuming film growth of 2.1 nm d⁻¹ (Wu et al., 2008a), PCB congeners 28 and 180 reach air-film equilibrium within hours and days, respectively. The model results suggest that the film acts as a temporary sink of chemicals from air during dry and cool weather, as a source to air in warmer weather, and as a source to storm water and soil during rain events. Using the downtown area of the City of Toronto Canada, as a case study, the model estimates that nearly 1 g d⁻¹ of ∑₅PCBs are transferred from air to film to storm water.