垃圾转运站污水回用处理工艺设计

垃圾转运站污水回用处理采用了膜 -生物反应器处理工艺 ,它具有高效、稳定、工艺流程简单、设备占地面积小和投资少等优点 ,且处理后出水可用于自身站内所需 ,即冲车、喷洒道路、冲厕、绿化、冲刷车间地面等多种用途 ,实现了污水处理后再利用的目的。     

合成氨装置重点部位的安全管理及防范措施

对安庆分公司化肥厂合成氨装置 4年以来的运行及安全管理情况作了综述 . 对装置的重点 监督部位加强技术型管理 , 并实行了一系列行之有效的安全防范措施 , 使之达到了国内同类 型装置先进水平 .     

输气场站工艺安全风险分析

针对输气场站HAZOP风险评估出的天然气泄漏风险进行工艺安全量化分析,通过天然气泄漏喷射火模拟,对天然气泄漏风险进行量化,为输气场站的安全管理提供有效的技术支持。通过量化,分析出对天然气泄漏喷射火造成后果大小的影响因素,提高了HAZOP风险分析的准确性和科学性,对输气场站的风险管理具有参考意义。     

Environmental impact of China''''s village and township industry(1988-1992): a comparison with urban industry

１ＩｎｔｒｏｄｕｃｔｉｏｎＶｉｌａｇｅａｎｄｔｏｗｎｓｈｉｐｉｎｄｕｓｔｒｙ（ＶＴＩ）ｉｓｂｅｃｏｍｉｎｇａｖｅｒｙｉｍｐｏｒｔａｎｔｃｏｍｐｏｎｅｎｔｏｆＣｈｉｎａｓｅｃｏｎｏｍｙａｎｄｅｎｖｉｒｏｎｍｅｎｔ．Ｉｎ１９９２，ＶＴＩｐｒｏｄｕｃｅｄ...     

火车站环境污染及防治措施

火车站候车室内的粉尘，烟尘 气溶胶 有毒有害气体危害人体健康，人群集中，流动量大易恶化空气质量，传播疾病，应围绕改善空气质量，控制疾病传播建立和实施严格的管理制度，以防治火车站的环境污染。     

移动通信基站的环境电磁辐射测量与分析

选择设于上海市区及郊区的５座典型移动通信基站，对其一半电磁波辐射强度进行了规范布点监测经数据计算分析及与国家有关电磁辐射防标准比较认为，移动基站周围环境中是磁辐射强度随着离基站天线距离增加大而减少小，在人群可能到达的距天线最近的地方，辐射水平最大值为１．５Ｖ／ｍ，未超过国家标准限值。     

高压变电站改造的安全监督管理

以茂名分公司动力厂南110kV变电站改造项目为例，从组织措施，安全教育，施工准备，现场安全管理等方面，阐述对高压变电站改造项目的安全监督管理。     

输油管道的泥土封堵与蒸汽置换动火技术

介绍了输油管道检修中的泥土封堵动火与蒸汽置换动火技术方法。详细阐述了应用泥土封堵更换一段管道动火、管道改流程并在天窗两边加盲板动火、更换污水管线弯头动火、应用蒸汽置换更换一段管道动火和管道改流程动火的实施例。在实际应用中，可根据动火检修管道的具体情况，选用其中的一种或两种方法并用。     

胜利石油局配气站噪声治理

本文对配气站管网系统作了噪声源分析，提出了在节流降压阀下游加装消声器，对管道作重点隔声包扎和简易隔声包扎、加装阀门局部隔声罩的方案。方案实施后，管网噪声由１２１ｄＢＡ降至８０ｄＢＡ，效果十分显著。     

Carbon Budget Implications of the Transition from Natural to Managed Disturbance Regimes in Forest Landscapes

Land-use change from an unmanaged to a managed forested landscape in northern forests is associated with a reduction of the area annually affected by natural disturbances (wildfires and forest insects) and the introduction of harvesting as a new disturbance. This study examined the impacts of changes in the disturbance regime-the frequency and type of disturbance-on landscape-level carbon (C) content and fluxes. The Carbon Budget Model of the Canadian Forest Sector was used to assess these impacts in six representative landscapes (100,000 ha each) with a range of disturbance regimes that are characteristic of conditions in coastal British Columbia, the interior of British Columbia, and the eastern boreal forest in Canada. The model was used to simulate ecosystem C fluxes during a period of natural disturbances, a 50-year transition period during which harvesting replaced natural disturbances, followed by 150 years of harvesting. The initial landscape-level biomass C content under natural disturbance regimes in the six example landscapes was 22 to 75% of their potential maximum content which is often used as the reference or baseline case. After 200 years of forest management, the C stored in the landscape plus the C retained in forest products manufactured from harvested biomass was between 58 and 101% of the landscape C content prior to the onset of harvesting. Landscape-level ecosystem C content was found to be affected by changes in the disturbance frequency, the age-dependence of the disturbance probabilities, and the disturbance-specific impacts on ecosystem C content. The results indicate that using the potential maximum C content of a landscape as the baseline always overestimates the actual C release due to land use change. A more meaningful procedure would be to assess the actual differences in landscape-level C content between the natural and the managed disturbance regime.