Assessment of population exposure to particulate matter pollution in Chongqing, China

To determine the population exposure to PM(10) in Chongqing, China, we developed an indirect model by combining information on the time activity patterns of various demographic subgroups with estimates of the PM(10) concentrations in different microenvironments (MEs). The spatial and temporal variations of the exposure to PM(10) were illustrated in a geographical information system (GIS). The population weighted exposure (PWE) for the entire population was 229, 155 and 211 microg/m(3), respectively, in winter, summer and as the annual average. Indoor PM(10) level at home was the largest contributor to the PWE, especially for the rural areas where high pollution levels were found due to solid fuels burning. Elder people had higher PM(10) exposure than adults and youth, due to more time spent in indoor MEs. The highest health risk due to particulate was found in the city zone and northeast regions, suggesting that pollution abatement should be prioritized in these areas.     

Anaerobic degradation behavior of nonylphenol polyethoxylates in sludge

Anaerobic biodegradation behavior of nonylphenol polyethoxylates (NPEOs) was investigated. Results showed that terminal electron acceptors, organic matters, initial concentration, and temperature had great influence on the anaerobic biodegradation of NPEOs. Anaerobic biodegradation of NPEOs could be enhanced by adding sulfate or nitrate while this process could be inhibited by adding organic matters. The maximum removal rate increased 1.24 microM d(-1) for each ten micromoles increase in initial concentration. The decrease in temperature caused a sharp decrease in the removal efficiency of NPEOs. The temperature coefficient (PHI) for the anaerobic biodegradation of NPEOs was 0.01 degrees C(-1). Nonylphenol (NP), the typical intermediate of NPEOs, could inhibit the anaerobic biodegradation of NPEOs only at high concentration. However, these environmental factors had no effect on the anaerobic biodegradation pathway of NPEOs. The accumulation of NP and short-chain NPEOs during NPEO biodegradation led to a significant increase in the estrogenic activity during the biodegradation period.     

青藏高原湖泊细菌种群结构的研究综述

青藏高原东北地区位于我国东部季风区、西北干旱区和青藏高原高寒区的交汇地带，人为影响较少，是研究人为影响与生物种群组成的理想场所。随着分子生物学技术的迅速发展，高原湖泊菌种群结构多样性研究越来越受到人们的重视并取得了重要成果。本文从青藏高原上应用的技术方法、细菌种群结构研究成果以及区域性的重要影响因素3个方面概述了湖泊细菌种群结构多样性研究在青藏高原上取得的进展。简单地讨论了种群多样性和影响因素的关系，对比发现，微生物种群结构的主要限制性因素会随着环境的变化发生改变。同时，微生物种群结构随着环境的变化实际上是其生理结构适应的结果。     

1—硝基芘对斜生栅藻的毒性研究

酿要用评价化学品对藻类毒性的标准实验方法，研究了１－硝基芘对斜生栅藻生长的影响，得到了１－ＮＰ抑制斜生栅藻生长的ＥＣ５０（９６ｈ）为０．１８２４ｍｇ．１＾－１，实验结果还表明，１－ＮＰ对藻生长的抑制作用随时间的延长而增加，抑制物性表现为特久且强度大，抑制机理为不可逆性抑制。     

Ecological Function Zoning for Environmental Planning at Different Levels

Environmental planning at different levels has been called for by environmental departments in China during last years to integrate environment consideration to economic development. Based on the accomplished environmental planning practice in Xiamen China, the paper suggests a general environmental planning process with ecological function zoning as its key steps, at the same time an effective method for ecological function zoning was formulated. The case studies of Dongfu suburban town environmental planning and Xiamen eco-city conceptual planning indicate that scientifically sound results of ecological function zoning can contribute to improving not only the adaptability and acceptability of environmental planning, also the environmental management and the decision-making. The experience shows that the ecological function zoning methods should be applied according to the principles of adaptive management, resource-based and community-based, so that it can integrate science into decision-making process, avoiding both narrow-minded viewpoints of planners and natural resource use conflicts among variety of stakeholders. Problems to be resolved in the future are also pointed out in the ending part.     

应用D412螯合树脂治理含镍电镀废水的研究

本文研究了Ｄ４１２螯合树脂对Ｎｉ（Ⅱ）离子静态和动态的吸收性能，并且研究了使用Ｄ４１２树脂除去和回收电镀废水中镍的最佳条件。     

ABR反应器的启动研究

研究了添加填料对折流式厌氧反应器(ABR)启动性能的影响.反应器启动时,控制COD负荷为0.15 kg/(m3*d),逐渐提升至0.6 kg/(m3*d).未加填料的反应器经过约60 d,加入填料的反应器经过约35 d的连续运行,出水COD去除率稳定,启动基本完成.研究表明,添加填料的复合式反应器启动速度明显快于普通ABR,且运行稳定性更好,COD去除率较高,能够较好地截留污泥,有利于反应器生物效应的形成.     

丁苯橡胶生产过程中不稳定因素分析及对策

针对丁二烯自聚物闪燃爆炸和后处理胶粒塑化着火的形成机理、形成条件、影响因素进行了分析,并提出了防范措施和应急处理办法。     

Size-fractionation and characterization of landfill leachate and the improvement of Cu2+ adsorption capacity in soil and aged refuse

Leachate was collected from an anaerobic lagoon at Shanghai Laogang refuse landfill, the largest landfill in China, and the sample was separated into six fractions using micro-filtration membranes, followed by ultra-filtration membranes. Several parameters of the samples were measured, including chemical oxygen demand (COD), total organic carbon (TOC), total solids (TS), pH, total phosphate (TP), total nitrogen (TN), fixed solids (FS), NH4+, orthophosphate, color, turbidity, and conductivity. These parameters were then quantitatively correlated with the molecular weight cutoff of the membrane used. Organic matter in the dissolved fraction (MW<1kDa) predominated in the leachate, accounting for 65% of TOC. Thermal infrared spectroscopy was used to characterize the filter residues. Asymmetric and symmetric stretching of methyl and methylene groups, and of functional groups containing nitrogen and oxygen atoms, were observed. In addition, the ability of two different samples to adsorb heavy metals was tested. Cu2+ was chosen as the representative heavy metal in this study, and the samples were soil; aged refuse, which had spent 8 years in a conventional sanitary landfill; and samples of soil and aged refuse treated for 48h with leachate in the ratio of 5g of sample per 50ml of leachate. Cu2+ uptake by the raw soil was approximately 4.60microg/g, while uptake by the leachate-contacted soil and leachate-contacted aged refuse were 5.66 and 5.11microg/g, respectively. These results show that the organic matter in the leachate enhanced the capacity of aqueous solutions to adsorb Cu2+.