如何建立多层次HSE管理体系的PDCA循环模式

PDCA循环模式是HSE管理体系运行的最基本方式,也是实现体系绩效螺旋式上升的重要手段.在体系运行的过程中,经过PDCA等各个环节以及各环节涉及到的诸多要素的不断发展与完善,体系的目标与方针得以实现.从管理体系实际运行的角度来看,整个体系运行过程中的PDCA循环又可以分为以下层次:单要素间某几个管理方面的相互影响与作用;几个要素之间形成的PDCA循环;大部分要素(关键要素)之间的作用;整个体系的PDCA循环.这几层次的循环模式也是相互交叉相互作用的.现以表1所涉及的工作为例,探讨这几个层次PDCA循环的相关性.     

阻止杭州湾海底输油管线穿孔、溢油的设想

对海底管线穿孔后如何阻止溢油、减少海上.油污染,提出了采用负压保护的可行性方案.     

浅析电子废弃物回收利用及危害解决办法

随着高科技的发展和人们需求的增长,电子产品不断推陈出新,电子废弃物成为世界上数量增长最快的垃圾."电子垃圾",主要包括各种使用后废弃的电脑、通信设备、电视机、电冰箱、洗衣机等电子电器产品.电子废弃物不规范回收处理易造成污染.电子废弃物中含有很多可回收再利用的有色金属、黑色金属、玻璃等物质.严格意义上讲,这些电子废弃物,不应称其为电子垃圾,而应称作电子旧货.伴随着电子工业的高速发展,电子废弃物污染不可避免地摆在了我们面前.电子废弃物具有危害性和可利用性.     

水电站项目生态用水工程措施设计

电站引水发电以及堤坝式电站调峰运行将使坝下河段减(脱)水,调水、引水和供水等河道以外用水水利工程也将造成下游河道减(脱)水,水文将对水生生态、生产和生活用水、河道景观等产生一系列的不利影响.为维护河流的基本生态需求,水利水电工程必须下泻一定的生态流量,将其纳入工程水资源配置统筹考虑,使河流水电动能经济规模和水资源配备向"绿色"方向发展.本文以火溪河阴坪水电站为例,简述水电工程下泄生态流量确定的主要方法和下泄生态流量的工程措施设计.     

发现和消除未遂事件保障装置安全生产——洛阳分公司2006年未遂事件、事故隐患统计分析

统计了洛阳分公司2006年度事故隐患情况,从未遂事件、事故隐患的时间段、后果、性质、直接原因等方面进行了深入细致的分析,找出影响洛阳分公司安全生产的主要隐患,提出了相应对策措施和建议.     

石化污水处理场浮选剂的优化

对几种浮选剂在荆门石化污水处理场的处理效果进行了对比,结果表明岳阳云溪XY-Ⅱ和江苏武进PAFC比现有PAC浮选剂的处理效果佳,且运行成本低.     

A new captorhinid reptile, Gansurhinus qingtoushanensis, gen. et sp. nov., from the Permian of China

Captorhinids, a clade of Paleozoic reptiles, are represented by a rich fossil record that extends from the Late Carboniferous into the Late Permian. Representatives of this clade dispersed from the equatorial regions of Laurasia into the temperate regions of Pangea during the Middle and Late Permian. This rich fossil record shows that there was an evolutionary trend from faunivorous to omnivorous and herbivorous feeding habits within this clade. The discovery of well-preserved captorhinid materials in the Middle Permian of China allows us to determine that the new taxon, Gansurhinus qingtoushanensis, gen. et sp. nov, is a member of Moradisaurinae, a clade of captorhinids with multiple tooth rows arranged in parallel. The presence of this moradisaurine in the Middle Permian of south central Asia leads us to suggest that paleogeographic changes during the Permian, with part of what is today China becoming a large peninsula of Pangea, allowed these early reptiles as well as other terrestrial vertebrates to extend their geographic ranges to this region of the Late Paleozoic supercontinent.     

Effects of irrigation,fertilization and crop straw management on nitrous oxide and nitric oxide emissions from a wheat–maize rotation field in northern China

One-year winter wheat–summer maize rotation is the most popular double cropping system in north-central China, and this highly productive system is an important source of nitrous oxide (N₂O) and nitric oxide (NO) emissions due to the high fertilizer N and irrigation water inputs. To sustain the high crop production and mitigate the detrimental impacts of N₂O and NO emissions, improved management practices are extensively applied. The aim of this study is therefore to evaluate the effects of an improved management practice of irrigation, fertilization and crop straw on grain yield and N₂O and NO emissions for a wheat–maize rotation field in northern China. Using automated and manual chamber measuring systems, we monitored N₂O and NO fluxes for the conventional (CT, 2007–2008), improved (IT, 2007–2008), straw-amended (WS, 2008–2009), straw-not-amended (NS, 2008–2009), and no N-fertilizer treatments (WS–NN, 2008–2009), respectively, for one rotation-year. The grain yields were determined for CT and IT for three rotation-years (2005–2008) and for WS, NS and WS–NN for one rotation-year (2008–2009). The improved management of irrigation and fertilization reduced the annual N fertilization rate and irrigation amount by 17% and 30%, respectively; increased the maize yield by 7–14%; and significantly decreased the N₂O and NO emissions by 7% (p < 0.05) and 29% (p < 0.01), respectively. The incorporation of wheat straw increased the cumulative N₂O and NO emissions in the following maize season by 58% (p < 0.01) and 13%, respectively, whereas the effects of maize straw application were not remarkable. The N₂O and NO emission factors of applied N were 2.32 ± 2.32% and 0.42 ± 1.69% for wheat straw and 0.67 ± 0.23% and 0.54 ± 0.15% for chemical N-fertilizers, respectively. Compared to conventional management practices using high application rates of irrigation water and chemical N-fertilizer as well as the field burning of crop straw, the improved management strategy presented here has obvious environmentally positive effects on grain yield and mitigation of N₂O and NO emissions.     

自然保护区生态补偿定量方案研究——基于“虚拟地”计算方法

自然保护区生态补偿的“补给谁”和“补多少”在理论和实践上都是生态补偿中的重点和难点所在。传统的通过计量保护区正外部性以确定生态补偿数量的方法存在两个主要问题：一是违背经济学原理,二是与管理体制不符且法理不足。据此,并考虑到中国相当数量的保护区“没有保护好”的主要因素是保护区社区居民生产生活的干扰,论文认为应通过控制保护区社区的负外部性来达成对保护区的生态补偿。通过生产函数理论分析,发现通常情况下保护区社区的经济产出与土地面积单调正相关,因此在没有生态补偿的情况下,保护区的划建会使周边社区居民经济收入减少,解决周边社区对保护区干扰的根本途径是利用生态补偿资金发展替代产业以提高单位面积土地的经济产出。以此认识为基础,文章提出了“虚拟地”概念并发展了定量方法来确定保护区的生态补偿最低标准,采用武夷山保护区的数据进行了这一方法的案例分析。     

Risk assessment on disinfection by-products of drinking water of different water sources and disinfection processes

The occurrences of trihalomethanes (THMs) and haloacetics (HAAs) in the water supply in Beijing and Canada were investigated. The concentrations of THMs and HAAs in Beijing and Canada were below the maximum contaminant levels specified by the USEPA and WHO standards. The multi-pathway risk assessment (assessed through oral ingestion, dermal absorption and inhalation exposure to drinking water) was used to assess the cancer risk and the hazard index of THMs and HAAs from fifteen waterworks in Beijing, China and three treatment plants using different disinfection processes in Canada. Residents in Beijing and residents who were served by three treatment plants using different disinfection processes in Canada had a higher risk of cancer through oral ingestion than through the other two pathways. The cancer risk resulted from disinfection by-products (DBPs) was 8.50E-05(for males), 9.25E-05(for females) in Beijing, China, while it was 1.18E-04, 1.44E-04 in Canada. The risk was higher when water treatment plants used surface water source than when they used ground water source and mixture water source in Beijing. The risk showed different changes in three treatment plants using different disinfection processes in Canada. The lifetime cancer risk for THMs followed the order: Plant 2>Plant 1>Plant 3. And, the lifetime cancer risk for HAAs was: Plant 1>Plant 2>Plant 3.