饱和带有机污染物的厌氧反硝化微生物降解

以卤代烃和芳香烃为代表,通过室内实验模拟饱和带厌氧反硝化环境,对地下饱和带中有机污染物的厌氧反硝化可生物降解性,降解机理,降解动力学方程等进行了研究。实验结果表明,芳香烃较卤代烃易被微生物降解,在有低学葡萄糖存在时有 机物的最大生物降解速率Ｃ６Ｈ６：Ｌｍａｘ＝１７ｍｇ／（ｍ＾２．ｄ）,Ｃ７Ｈ８：Ｌｍａｘ＝４６ｍｇ／（ｍ＾２．ｄ）,ＣＣｌ４;Ｌｍａｘ＝７ｍｇ／（ｍ＾２．ｄ）,ＣＨＣｌ３：Ｌｍａｘ＝６     

易降解有机物对氯代芳香化合物好氧生物降解性能的影响

利用测定微生呼吸耗氧量的方法,从生物氧化程度出发,研究易降解有机物对氯代芳香化合物生物解性能的影响。结果表明,易降解有机物的存在有利于受试物的降解,生物氧化率的增加值与所投易降解ＢＯＤ５浓度的关系具有类似米－门公式的形式。     

运用回归分析与人工神经网络预测含硫芳香族化合物好氧生物降解速率常数

为了研究人工神经网络预测有机化合物生物降解的性能,运用多元线性回归方法和误差反向传递人工神经网络模型以基团代码作为结构描述符,分别拟合、预测了一批含硫芳香族化合物的一级好氧生物降解速率常数．结果表明,由于神经网络自动考虑了基团间的交互作用,它对生物降解这类复杂问题有极高的求解能力,预测的均方误差为０．００１０２,远低于线性回归模型的预测误差０．０１５９１     

苯并[a]芘和1-羟基芘诱导人胚胎干细胞分化心肌细胞ROS、CYP基因表达和DNA损伤

多环芳烃(PAHs)化合物中的苯并[a]芘和PAHs暴露检测标志物1-羟基芘与心脏功能障碍有关,但其生物学机制尚不清楚。为研究苯并[a]芘和1-羟基芘对心脏的毒性作用,基于人胚胎干细胞分化心肌细胞(hESC-CM)研究了苯并[a]芘和1-羟基芘对心肌细胞活性氧(ROS)生成、CYP基因表达和DNA损伤等的影响。结果表明,苯并[a]芘和1-羟基芘对h ESC-CM活性无影响,但能显著增强细胞ROS水平,诱导DNA损伤。此外,苯并[a]芘还能诱导细胞线粒体促凋亡基因的表达。研究表明,苯并[a]芘和1-羟基芘能通过诱导氧化应激和DNA损伤事件导致h ESC-CM损伤,在一定程度上解释了多环芳烃暴露导致心脏疾病的分子机制。     

Transmembrane transport of polycyclic aromatic hydrocarbons by bacteria and functional regulation of membrane proteins

• Explaintheadsorption, uptake and transmembrane transport of PAHs by bacteria. • Analyze functional regulation of membrane proteins inthe transmembrane transport. • Proteomics technology such as iTRAQ labeling was used to access expressed proteins. • Single cell analysis technology wereused to study the morphological structure. In recent years, increasing research has been conducted on transmembrane transport processes and the mechanisms behind the microbial breakdown of polycyclic aromatic hydrocarbons (PAHs), including the role of membrane proteins in transmembrane transport and the mode of transmission. This article explains the adsorption, uptake and transmembrane transport of PAHs by bacteria, the regulation of membrane protein function during the transmembrane transport. There are three different regulation mechanisms for uptake, depending on the state and size of the oil droplets relative to the size of the microbial cells, which are (i) direct adhesion, (ii) emulsification and pseudosolubilization, and (iii) interfacial uptake. Furthermore, two main transmembrane transport modes are introduced, which are (i) active transport and (ii) passive uptake and active efflux mechanism. Meanwhile, introduce the proteomics and single cell analysis technology used to address these areas of research, such as Isobaric tags for relative and absolute quantitation (iTRAQ) technology and Nano Secondary ion mass spectrometry (Nano-SIMS). Additionally, analyze the changes in morphology and structure and the characteristics of microbial cell membranes in the process of transmembrane transport. Finally, recognize the microscopic mechanism of PAHs biodegradation in terms of cell and membrane proteins are of great theoretical and practical significance for understanding the factors that influence the efficient degradation of PAHs contaminants in soil and for remediating the PAHs contamination in this area with biotechnology.     

大气颗粒物中多环芳烃的源解析方法

综述了用于大气颗粒物中多环芳烃（PAHs)源解析的主要定性、定量方法、并对其优缺点作了总结。比值法多用于定性解析，化学质量平衡法（CMB）要求源的成分谱较全面，而多元统计法则要求输入的数据较多。由于缺乏各污染源较完整的PAHs成分谱，且PAHs易发生化学反应，所以CMB法难以广泛推广，而多元统计法对源成分谱，且PAHs易发生化学反应，所以CMB法难以广泛推广，而多元统计不对源成分谱要求低，且不需要考虑PAHs的降解，因而具有推广价值。     

活性炭固定床吸附分离溶液中表面活性剂和多环芳烃

利用活性炭固定床吸附分离表面活性剂和多环芳烃(PAH)的混合溶液,选取了具代表性的表面活性剂(TX100)和PAH(菲(PHE)等)。实验结果表明,流量越低、活性炭填充量越多、表面活性剂浓度越高、PAH浓度越低,越有利于表面活性剂的回收和PAH的去除。定义了有效回收时间,该时间是指PAH穿透10%的时间与表面活性剂穿透90%的时间之差,该时间越长,越有利于表面活性剂的回收。采用BDST和Thomas模型对TX100和PHE进行了吸附模拟,效果均较好;BDST模型拟合结果表明,当活性炭对TX100的吸附接近饱和时仍对PHE有较强的吸附能力。活性炭固定床吸附分离法可节约运行成本0.06元/L。     

Biodegradation of anthracene and phenanthrene by bacteria isolated from oil-contaminated soil of Bangladesh

Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous environmental pollutants entering into the environment through natural and anthropogenic activities. Owing to their toxicity to various life forms including humans, detoxification of PAHs is crucial to reduce their effects on cells. In this study, we have isolated two bacteria capable of degrading two common PAHs, anthracene and phenanthrene, from contaminated soil samples by using selective enrichment culture supplemented with test PAHs as the sole source of carbon and energy. The isolated bacteria were identified and affiliated as Pseudomonas aeruginosa strain KD and Stenotrophomonas maltophilia strain RC based on their 16s rRNA gene sequences. The degradation of anthracene and phenanthrene was estimated indirectly by measuring the decolourisation extent of a redox indicator, 2, 6-dichlorophenolindophenol, incorporated into PAH-supplemented mineral salt media. In the case of anthracene, ≥90% decolourisation was recorded at 20 and 48 days for P. aeruginosa and S. Maltophilia, respectively. On the other hand, ≥94% decolourisation was recorded at 56 and 52 days for P. aeruginosa and S. maltophilia, respectively during the utilisation of phenanthrene.     

The Emissions of Major Aromatic Voc as Landfill Gas from Urban Landfill Sites in Korea

In this study, concentrations of major aromatic VOCs were determined from landfill gas (LFG) at a total of five municipal landfill sites in Korea including Nan Ji (NJ), Woon Jung (WJ), Sam Poong (SP), Hoei Chun (HC), and No Hyung (NH). The concentration levels of those VOC were found to be significantly different, mainly as a function of such a parameter as landfill aging. The VOC concentrations measured from the unclosed landfill sites (e.g., WJ) were characterized by exceedingly high values above a few tens of ppm. However, the results of the abandoned site (e.g., SP) were about three orders of magnitude lower than the others so as to merely exceed the typical ambient concentration levels. It was most striking to find a systematic dominance of toluene over other aromatic VOC under most circumstances. The LFG flux values of all aromatic VOC and the four specific major ones (termed as BTEX: benzene, toluene, ethylbenzene, and xylene) were also computed for each vent pipe from all study sites using their concentrations and the concurrently determined environmental parameters. The results, if calculated in terms of the average BTEX quantity emitted per vent pipe, showed that the magnitude of their emissions can vary substantially, with the values ranging from 0.05 (SP) to 49.2 kg yr⁻¹ (WJ in wintertime). The LFG flux values of aromatic VOC, when compared to the contribution of non-methane hydrocarbons (NMHC), were able to explain a constant, but minor, proportion of the LFG carbon budget.