城市污水中PCBs的分析及其QA/QC研究

报道了一种城市污水中痕量PCBs的分析方法,并进行了QA/QC研究,采用二氯甲烷萃取剂对城市污水进行液-液萃取,联合运用浓硫酸和硅胶层析柱将PCBs与杂质分离,以毛细管GC-ECD和内标法对PCBs定量.空白加标回收试验得出,PCBs的回收率为58%～125%,标准偏差为0.00173～0.00778μg/L,相对标准偏差为1.58%～12.43%.以实际城市污水作为加标基质,得出加入污水中的19种PCBs的分析方法回收率为57.6%～129.2%,方法的检测限为0.010～0.056μg/L,满足了US EPA对PCBs回收率要求.经过3次平行测定,测得实际城市污水中PCBs含有9种PCBs,PCBs总量的平均值为0.0235μg/L,相对标准偏差为9.63%,该分析方法所需的仪器简便、容易操作.     

吉林省公主岭市青少年头发中多氯联苯污染水平的研究

应用气相色谱-质谱（GC-MS）分析了23份采自吉林省公主岭市青少年（12～18岁）头发样品中的30种多氯联苯（PCBs）,并对头发样品中PCBs的构成和来源进行了解析,对其与性别的相关性进行了分析.结果表明,头发样品中PCBs的检出率为100%,PCBs总含量ΣPCBs为（68.85±36.72）ng.g-1,含量范...     

珠三角地区冬季大气中PCBs的空间分布

为了考察珠三角地区冬季大气中PCBs的空间分布,于2001年12月24日至2002年1月16日在广州的市区、郊区和背景区进行连续的空气样品采样.采用GC-MS-SIM模式进行PCBs分析.结果表明,空气中PCBs的总浓度按照距离市区从近到远的次序依次降低.市区PCBs平均浓度是郊区的1.61倍,是背景区的2.54倍.PCBs各单体化合物的浓度分布表现出明显的地区差异.低氯取代PCBs的市区浓度比郊区和背景区的浓度高出很多,而高氯取代PCBs的空间差异不明显.在不同氯数PCB浓度之和对PCBs总浓度的百分贡献率分布中,市区、郊区和背景区都表现为三氯和四氯取代PCBs的贡献最大,而且不同地区两者的贡献率之和非常接近.市区和郊区空气中三氯和四氯取代PCBs的贡献比较接近;而背景区空气中四氯取代PCBs的贡献高达52.79%,是三氯贡献的近2倍.郊区和背景区空气中五氯取代PCBs的平均贡献率分别是9.65%和10.87%.仅就颗粒相而言,其PCBs平均贡献率在市区、郊区和背景区表现出非常好的一致性.对市区、郊区和背景区空气中log Kp与log PLo进行回归分析,其斜率mr分别是-0.60、-0.42和-0.45,都明显地偏离空气中气/固分配的理想平衡状态.     

珠江广州段水体、沉积物及底栖生物中的多氯联苯

对珠江广州江段水体、沉积物及底栖生物体内多氯联苯有机污染物进行了初步的调查研究.结果表明,广州江段7个样点水体中多氯联苯类有机污染物平均含量为2.3ng/L,各点含量无显著差异;沉积物中多氯联苯类有机污染物平均含量为31.52g/kg,各点有显著差异,其中以广州江段南航道y03样点最高,达65.31g/kg;底栖生物体内多氯联苯含量平均为181.77g/kg,其中也以y03样点最高,达317.37g/kg.多氯联苯在水体、沉积物及生物体3者之间存在明显的富集和放大作用.     

典型污染地区底泥和土壤中残留多氯联苯（PCBs）的情况调查

为了解PCBs在生态系统中的分布,利用毛细管气相色谱对受PCBs污染地区的土壤、底泥进行实际环境样品的调查。在底泥和土壤样品中测定近50个同属物的含量,并对其分市规律进行了探讨。指出在实际环境样品中PCBs的同属物分布和工业产品有明显不同。通过不同深度底泥样品测定,证明PCBs在底泥中的渗透作用较弱。     

衡山大气中PCBs的浓度水平及来源分析

为研究我国高山地区大气中多氯联苯(PCBs)的含量情况,于2009年4月~5月在衡山气象站采集了气相及颗粒相样品.以气相色谱法测得该地区大气中7种指示性PCB(Indicator-PCBs)的平均浓度为180.51pg/m3,含量最多的为PCB52.与国外高山站点相比,衡山的PCBs含量处于较高水平.通过后推气流轨迹分析了气流来向对PCBs含量的影响,结果显示,来自北方的气流携带较多的PCBs.主因子分析的结果表明,该地区PCBs的来源可以归结为3类,分别为:国外的PCBs产品;焚烧炉排放、造纸漂白等工业生产过程以及国产的变压器油等PCBs产品;含PCBs的油漆添加剂等.     

Concentration of DL-PCBs in fish from market of Parma city (north Italy): estimated human intake

The concentrations of 12 congeners of non-ortho and mono-ortho dioxin-like polychlorinated biphenyls (ΣDL-PCB) were measured in 30 fish samples from Parma markets by GC/MS technique. The samples were randomly purchased, choosing the species commonly found in supermarkets. The concentration of DL-PCBs estimated remained under the fixed Italian limit of 4 pg g⁻¹ ww WHO-TEQ (World Health Organization-Toxic Equivalent) in the major part of the samples, so the situation seems to be not at a level sufficient to pose a risk to human health of the Parma population. The medium daily intake for DL-PCBs for Italian consumers (Parma) was also estimated. This value generally resulted minor than 2 pg g⁻¹ ww WHO-TEQ kg⁻¹ body weight, exceeding only in four cases: eel, smooth hound, starry smooth hound and tuna.     

Concentration of Organochlorine Pollutants in Surface Waters of the Central European Biosphere Reserve Krivoklatsko (8 pp)

Background, Aim and Scope The article is focused on dioxin, furan, PCB and organochlorine pesticide monitoring in the surface waters of the Central European, protected natural reserve Krivoklatsko, under the UNESCO programme Man and Biosphere. Persistent compounds are presently transported via different means throughout the entire world. This contamination varies significantly between sites. This raises the question of what constitutes the naturally occurring background levels of POPs in natural, unpolluted areas, but which are close to industrialised regions. Information of real background POP contamination can be of high value for risk assessment management of those sites evidently polluted and for the defining of de-contamination limits. Preserved areas should not be seen as isolated regions in which the impacts of human activities and natural factors are either unexpected or overlooked. Every ambient region, even those protected by a law or other means, are still closely connected to neighbouring human developed and impacted areas, and are therefore subject to this anthropogenic contamination. These areas adjacent to natural reserves are sources of diverse substances, via entry of air, water, soil and/or biota. After an extended period of industrial activities, organochlorine pollutants, even those emitted in trace concentrations have reached detectable levels. For future research and for the assessment of environmental changes, present levels of contamination would be of high importance. This work publishes data of the contamination with organochlorine pollutants of this natural region, where biodiversity and ecological functions are of the highest order. Materials and Methods: Semipermeable membrane devices (SPMDs) were utilised as the sampling system. SPMDs were deployed in two small creeks and one water reservoir selected in the central part of the Krivoklatsko Natural Reserve, where it could be expected that any possible contamination by POPs would be lowest. The exposed SPMDs were analysed both for chemical contents of POPs and for toxicity properties. The chemical analyses of dibenzo-dioxins, dibenzo-furans, PCBs and OCPs were analysed by GC/MS/MS on GCQ or PolarisQ (Thermoquest). Toxicity bioassays were performed on the alga Desmodesmus subspicatus, bacteria Vibrio fischeri and crustacean Daphnia magna. All toxicity data were expressed as the effective volume Vtox. Vtox is a toxicity parameter, the determination of which is independent of SPMD deployment time and pre-treatment dilution (unlike, for example, the EC50 of the SPMD extract). Results: The following chemical parameters were monitored: 1) tetra, penta, hexa and hepta dibenzo-p-dioxins and furans; 2) all those detectable from tri- through deca-polychloriated biphenyls (PCBs) and 3) a group of organochlorine pesticides: hexachlorobenzene and isomers of hexachlorocyclohexane, DDE, DDD and DDT. The concentrations of dioxins and furans on the assessed sites varied from under detection levels up to 7 pg.l-1; PCBs were detected in a sum concentration up to 2.8 ng.l-1; and organochlorine pesticides up to 346 pg.l-1. The responses of bioassays used were very low, with the values obtained for Vtox being under 0.03 l/d. Discussion: Toxicity testing showed no toxicity responses, demonstrating that the system used is in coherence with the ecological status of the assessed sites. Values of Vtox were under the critical value – showing no toxicity. The PCA of chemical analysis data and toxicity responses resulted in no correlations between these two groups of parameters. This demonstrated that the present level of contamination has had no direct adverse effects on the biota. Conclusions: The concentration values of six EPA-listed, toxic dioxins and sums of tetra-hepta dioxins; nine EPA toxic dibenzofurans and the sums of tetra-hepta bibenzofurans are presented together with all tri-deka PCBs and organochlorine pesticides (alfa-, beta-, gama-, delta-HCH, HCB, opDDE, ppDDE, opDDD, ppDDD, opDDT, ppDDT). These values represent possible current regional natural background values of these substances monitored within the Central European region, with no recorded adverse effects on the freshwater ecosystem (up until the present time). Recommendations and Perspectives: Assessment of dioxins, furans and other organochlorine compounds within natural reserves can be important for the monitoring of human-induced impacts on preserved areas. No systematic monitoring of these substances in areas not directly affected by industry has generally been realised. There is a paucity of data of the presence of any of these substances within natural regions. Further monitoring of contamination of both soil and biota by dioxins and furans in preserve regions is needed and can be used for future monitoring of man-made activities and/or accidents. Semipermeable membrane devices proved to be a very good sampling system for the monitoring of trace concentrations of ambient organochlorine compounds. Toxicity evaluation using the Vtox concept demonstrated that those localities assessed expressed no toxicity.     

FeCl_3存在时六六六热解生成PCDD/Fs的研究

在开管体系中,于280℃时研究了六六六无效体在Fe,理体制FeCl_3存在时的热解,以及影响热解产物中PCDD/Fs生成量的因素.PCDD/Fs的生成主要取决于FeCl_3,而Fe的存在并不增加体系中PCDD/Fs的生成量.在封管体系中,研究结果表明PCSS/Fs的生成量随FeCl_3用量、反应时间和反应温度的增加而增加,但温度影响最大.实验还表明,氯苯、氨酚对PCDD/Fs的生成起决定作用.在250─280℃,PCDD/Fs的生成主要在于二者之间的缩合,而单独氯酚间的缩合则居次要地位.氯化对生成PCDD/Fs的种类及量影响很大.250─280℃时,低氯苯、氨酚在FeCl_3作用下氯代成高氯产物,进而缩合成 OCDD/F;但在 350℃以上时,氯酚反应活性增加,故低氯PCDD/Fs生成量增加,OCDD/F生成量相对降低.     

Recent survey and effects of cooking processes on levels of PCDDs,PCDFs and Co-PCBs in leafy vegetables in Japan

We report here the latest levels of polychlorinated dibenzo-p-dioxins/polychlorinated dibenzofurans (PCDD/Fs) and coplanar polychlorinated biphenyls (Co-PCBs) in leafy vegetables in Japan as well as the effect of cooking processes on the reduction of these contaminants. Three kinds of leafy vegetables (“komatsuna”, lettuce and spinach) from seven districts in Japan in 1998 were analyzed for the 2,3,7,8-chlorine substituted PCDD/Fs and three non-ortho-PCBs (#77, 126 and 169). The mean total TEQ levels (using the WHO-TEFs) in the komatsuna, lettuce and spinach were 0.094, 0.025 and 0.196 pg/g fresh weight, respectively. The TEQ levels are dominated by 2,3,7,8-TCDD, 1,2,3,7,8-PeCDD, 2,3,4,7,8-PeCDF and 3,3^′,4,4^′,5-PeCB in many of the samples. For one of these isomers, the 2,3,4,7,8-PeCDF TEQ levels showed good correlation with the total TEQ levels in the samples (r=0.957). This suggests that 2,3,4,7,8-PeCDF may be an indicator for dioxin contamination in the analysis of the leafy vegetables. Also, the effects of two cooking processes (washing and washing followed by boiling) on the dioxin levels in two types of spinach samples were investigated. On average, in both samples, the total concentrations of the PCDDs, PCDFs and Co-PCB were reduced to about 38%, 73% and 88% of the initial concentrations by washing, and to 21%, 35% and 61% of the initial concentrations by washing followed by boiling. The total TEQ levels were reduced to about 30% of the initial TEQ levels by washing followed by boiling. Significant reductions in the TEQ levels were observed in the cooked samples. Thus, the cooking processes may reduce the risk of dioxin intake from the leafy vegetables.