污染地块土壤多氯联苯风险筛选值研究

污染地块土壤多氯联苯（PCBs）污染主要来自含PCBs电力设备封存点的泄漏及非故意产生源,建立土壤PCBs筛选标准是开展PCBs污染地块调查、评估和修复的基础.本研究通过文献分析统计了典型PCBs单体的占比,并基于人体健康风险评估模型推导了污染地块土壤PCBs风险筛选值.结果表明,不同商用PCBs混合物中共平面PCBs总量（∑Co-PCBs）占比为0.01%~16.10%,难以代表PCBs的总体风险水平.研究建立了PCBs总量、指示性PCBs总量（∑Id-PCBs）及∑Co-PCBs等3个指标共同作为土壤PCBs筛选值体系,敏感用地和非敏感用地情景下,PCBs总量、∑Id-PCBs、∑Co-PCBs分别为2.10、0.24、0.03 mg·kg^-1和6.20、0.71、0.09 mg·kg^-1.通过6个含PCBs电容器地下封存点485个污染土壤样品的分析,进一步证明了仅控制∑Co-PCBs将低估PCBs污染风险,采用本研究提出的3个指标进行筛选能够更有效地识别和评估PCBs污染地块的风险.     

滨海城市大气中多氯联苯的污染特征

选取滨海城市厦门的城区、郊区、工业区和背景区为研究对象,于2008年10月至2009年9月对厦门市大气进行了为期四个季节的采样工作,用GC-MS对气相和颗粒相中的28种多氯联苯(PCBs)同系物进行测定。研究结果表明,厦门市PCBs具有明显的时空分布特征,PCBs的含量在66.94～689.59 pg/m3之间,平均值...     

环境样品中多氯联苯的分析技术

作为一种持久性有机污染物,多氯联苯在地球上的分布十分广泛。然而由于多氯联苯在环境样品中残留浓度低、干扰物质多且组成复杂,必须对环境样品进行预处理。目前较为常用的含多氯联苯样品的前处理技术有：溶剂萃取技术、固相萃取技术、固相微萃取技术、超临界萃取技术、微波萃取技术和加速溶剂萃取技术等,分析经过技术处理以后的样品常用的方法有化学分析方法和生物分析方法,化学方法包括气相色谱法,气相色谱质谱分析法等;生物方法有生物传感器测定法、表面胞质团共振检测、以Ah受体为基础的生物分析法和酶联免疫检测法。中国在这方面的研究投入不够,应加大人力、财力和物力的支持,提高环境样品中多氯联苯的检测水平。     

城市不同功能区径流中PCBs的污染特征及毒性评价

选取温州不同城市功能区小区路面、停车场、汇流口、小区屋面以及交通干道作为研究对象,采集径流样品测定了14种多氯联苯(PCBs)的浓度,并对其进行多元统计分析,探讨了其可能的污染来源.结果表明,不同城市功能区径流中PCBs含量和检出率有所差别但变化不大,其中小区屋面要高于交通干道、汇流口、停车场和小区路面(均值分别为337.9, 306.3, 240.1, 193.2, 172.7ng/L);径流中以五氯代PCBs为主,占到总量31.4%~56.2%;径流中PCBs跟SS浓度相关性较差;由多元统计分析结果可以看出,高低氯代PCBs污染来源不同;TEQs在汇流口、小区路面、停车场径流中浓度相对较大,分别达到4.4, 4.1, 4.0ng/L,这跟其径流中CB126含量较高有关.     

手性多氯联苯在电子垃圾拆解地鱼类体内的分布及累积规律

电子垃圾拆解活动已造成当地鱼类多氯联苯（Polychlorinated Biphenyls,简称PCBs）污染,但手性PCBs在鱼类体内的分布特征和选择性富集则较少有报道.本研究采集了广东省清远市龙塘镇某电子垃圾拆解区附近水塘的鱼类样品,研究鱼肉样品中手性PCBs污染水平、分布规律和对映体选择性.结果表明,在电子垃圾拆解区鱼肉样品中均检测到7种手性PCBs,总PCBs（ΣPCBs）含量为386.7~602.8 ng·g^-1（湿重）,证实当地鱼类已受到手性PCBs的污染.PCB45、PCB91、PCB95、PCB132、PCB136和PCB174在鱼类样品的对映体分数（EF值）与沉积物具有显著差异,表明这些手性PCBs在鱼类体内可能具有对映体选择性富集和代谢作用.不同种类的鱼肉样品中EF值不同,说明它们对PCBs的富集能力不同.鲮鱼、鲫鱼和乌鳢对PCBs的生物/沉积物富集因子（BSAF）分别为0.31~1.71、0.30~1.86和0.50~2.64.根据乌鳢/鲮鱼和乌鳢/鲫鱼食物关系计算的生物放大因子（BMF）范围分别为1.35~4.51和2.17~5.10,表明乌鳢对手性PCBs具有生物放大作用.     

加速溶剂萃取-气相色谱质谱法测定海洋沉积物中多氯联苯残留

样品采用加速溶剂萃取,萃取液依次经复合硅胶和石墨化炭黑柱净化后,采用GC-MS法测定样品中的多氯联苯残留。结果表明,方法检出限为(0.005～0.038)×10-9(湿重),样品加标回收率为68.5%～108.4%,RSD为2.1%～11.8%。本方法具有提取效率高,净化效果好,回收率高,准确灵敏等优点,可应用于海洋沉积物中多氯联苯等持久性有机污染物残留的监测。     

加速溶剂萃取和净化-气相色谱-串联质谱法测定典型污染场地土壤中多氯联苯残留

建立了加速溶剂萃取同步净化-气相色谱-三重四极杆串联质谱法测定污染场地土壤中7种指示性多氯联苯的方法。对加速溶剂萃取、净化、色谱柱、串联质谱离子对、碰撞电压等条件进行了优化。萃取和净化过程合二为一,串联质谱法提高了7种多氯联苯的灵敏度。7种多氯联苯在0.1～100μg/L质量浓度范围内线性良好,线性相关系数为0.999 80～0.999 99,方法检出限为0.004～0.010μg/kg,回收率为84.8%～97.3%,相对标准偏差为2.4%～8.5%。运用网格法采集了华东某典型污染场地土壤中31个土壤样品,分析了该场地7种指示性多氯联苯的残留特征。7种多氯联苯的检出率为100%,检出范围为0.096～3 661μg/kg,各点平均值为307μg/kg。各采样点中多氯联苯的残留程度存在很大差异,局部点位受到了较重污染,与封存点相近的部分点位残留较外围位置高。土壤中多氯联苯同系物以三氯联苯、四氯联苯、五氯联苯为主,占同系物总量的98.2%。该污染场地土壤多氯联苯主要是低氯代联苯污染,土壤中多氯联苯的毒性效应评估处于中等水平,污染以点源污染为主,且已有较大程度扩散。     

Dechlorination of 2,2＇,4,4＇,5,5＇-hexachlorobiphenyl by thermal reaction with activated carbon-supported copper or zinc

Activated carbon （AC）-supported copper or zinc made from ion exchange resin （IRCu-C and IRZn-C） have an increased metal load of 557.3 mg·g^-1 and 502.8 mg·g^-1 compared to those prepared by the traditional method involving impregnation with AC and copper （II） citrate or zinc citrate solution （LaCu-C and LaZn-C） of 12.9 mg·g^-1 and 46.0 mg·g^-1 respectively. When applied to decompose 2,2＇,4,4＇,5,5＇-hexachlorobiphenyl at 250 ℃, IRCu-C achieved higher activity of 99.0% decomposition efficiency than LaCu-C of 84.7%, IRZn-C of 90.5% and LaZn-C of 62.7%. When the reaction temperature rose to 350 ℃, all the four kinds of reactants can decompose PCB- 153 with efficiency above 90%. Further, X-ray photoelec- tron spectroscopy characterization of IRCu-C before and after the reaction indicated transformation of 19.1% of Cu atoms into Cu^2＋, illustrating that Cu is the active ingredient or electron donor promoting the decomposition of PCB- 153. The mechanism underlying this process differs from a traditional H donor. However, there is no significant change on the surface of IRZn-C before and after the reaction, suggesting that Zn acts as catalyst during the process of PCB-153 decomposition.     

Characterization studies of a semi‐automated separation method for analysis of non‐ortho substituted polychlorinated biphenyl (PCB) congeners in environmental samples

Non‐ortho substituted polychlorinated biphenyl (PCB) congeners can account for the majority of the dioxin‐like toxicity in environmental samples, yet analysis for these congeners is difficult because other PCB congeners co‐elute with them in most Chromatographic methods. An automated method was developed which incorporates a porous graphitic carbon (PGC) column which is commercially available. Non‐ortho substituted congeners were successfully separated from interfering PCB congeners. Recoveries of non‐ortho substituted congeners were consistently reproducible (CV < 9%) when chicken eggs were fortified with individual congeners.     

Medium ‐ pressure ‐ liquid ‐ extraction (MPLE) of selected polychlorinated biphenyls from soil (MPLE II) 1

The extraction of PCBs from spiked soils using the Medium‐Pressure Liquid‐Extraction method showed good recovery rates. Comparison of MPLE and Soxhlet extraction of naturally contaminated soil showed similar results. However, too large quantities of solvents have to be used in MPLE procedure and the elution profile makes it unlikely, that the aspired separation from PAHs would be sufficient.