环境工程设计质量保障体系探讨

以污水处理工程为例，阐明环境工程设计质量保障体系的构成，概述设计原则以及每一设计步骤所需注意的问题，对验证、确保设计质量的后续工作过程作了简要的介绍。     

茂名石化炼油废水处理扩建一期工程A/O系统改O/O工艺运行探索

茂名石化炼油废水A/O系统改O/O工艺运行后,出水水质各项指标均达到国标和地标排放。为期两个月的工业试运行,为工艺操作与管理提供了经验和依据,同时也为二期工程的设计、施工和管理奠定了基础。     

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

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

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。     

固定化微生物技术在环境工程中的应用

固定化微生物技术是一种新技术，与普通生物处理法相比有许多优点，对固定化微生物技术、微生物的固定化方法、固定化栽体及固定化技术在环境工程中的应用和研究进展状况进行了综述，并对其发展问题做了探讨。     

绿色设计方法——设计领域发展的新趋势

 简要地介绍了设计领域发展的新趋势—绿色设计的基本思想，综述了绿色设计各主要研究领域的现状和问题以及发展趋势，阐明了我国开展绿色设计的研究与应用的必要性与可行性．     

石油石化企业环境工程设计的质量保证及其注意事项

简要论述了建立健全石油石化企业环境工程设计质量保证体系的必要性和重要性，以及由此涉及到的设计原则、设计方案、设计程序和设计规范等事项，指出了其中应注意的主要问题。     

安全工程专业本科教育培养模式的探讨

本文分析了当前安全工程专业本科教育存在的一些问题，如本科基础知识教育欠系统和规范，知识结构的行业限制性过重，课程设置不甚合理等，这些问题对培养高素质安全科学人才及本专业自身的发展不利，笔者就合理的培养模式作了探讨，提出本科教育应有明确的目标，业务能力应有具体要求，专业知识结构应划分为四个层次。     

大庆红岗生态工业园区创建的现有条件

生态工业园是根据循环经济理念和工业生态学原理而设计建立的一种新型工业组织形态,在园区内通过废物交换、循环利用、清洁生产等手段,实现资源利用的最大化和废物排放的最小化.文章通过对大庆市石油、石油化工产业链现状分析及产品代谢和废物代谢分析,说明大庆红岗具有创建生态工业园区的区位和资源优势,园区所在区域内现已经初步形成了石油开采、石油化工、轻烃加工和化工建材产业(品)代谢连及废油、废水回注等废物代谢链的生态工业雏形,为创建大庆红岗生态工业(石化)示范园区奠定了一定的基础.     

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.