艾比湖湖周生境恶化及其恢复对策

艾比湖是新疆第二大咸水湖，湿地内分布着多种植被类型。自20世纪60年代开始，湖水水位急剧下降，造成湖盆大面积裸露，在当地强风作用下成为巨大风沙之源，从而成为困扰新疆地区的严重生态问题。通过有关资料对艾比湖及其毗邻地区环境恶化的现象进行剖析，提出保护、恢复的相关对策。     

对地铁工程风险评估体系框架的研究

地铁工程同一般建设项目相比,受不可预见的水文地质条件、社会环境、施工技术的可靠度、经济发展的程度等多方面因素的影响较重;就必然使地铁工程成为高风险的工程建设项目,然而目前对其风险评估工作还停留在简单的定性和定量的评估水平上。为此,笔者在研究系统论的基础上,从动态系统风险评估的观点出发,运用动态控制的原理,着重研究适合于地铁工程风险评估体系的理论框架,及建立理论框架时应考虑的诸多问题;同时对动态系统风险评估、评价因素可靠性分析技术、各种风险评估方法及评估技术的运用做了简要论述。该框架体系不仅适用于地铁工程的风险评估,同样适用于其他复杂的工程系统的风险评估评价。     

可移动危险源动态安全监控的探索与展望

简述近年来可移动危险源的严重事故及惨痛教训,究其重要原因之一就是缺乏对可移动危险源的动态安全监控,指出开展可移动危险源动态安全监控的迫切性;从而对建立可移动危险源动态安全监控体系的指导思想与功能设计进行了比较深入的探索,利用全球移动通信系统(GSM),全球定位系统(GPS),地理信息系统(GIS)和计算机网络技术相结合,对可移动危险源实施动态安全监控,以实现对其严重事故的有效控制,并对完善可移动危险源动态安全监控体系作了进一步的展望。     

矿井电网动态安全分析系统的研究

随着国民经济的迅速发展,各行各业对煤矿资源的需求越来越大,然而矿难事故的频繁发生,煤矿安全已成为迫切需要解决的首要问题。笔者针对目前的矿井供电系统存在的不足而导致的安全隐患问题,进行了深入的理论研究和技术分析。根据煤矿供电系统的实际情况,对其供电系统的动态安全分析问题进行了较全面的探讨和论述;介绍了矿井电网动态安全分析系统的功能要求、主要组成部分和结构;对各部分的实现和需要注意的问题进行了分析;给出了矿井电网动态安全分析系统的框图及系统最终要反映的信息要求。     

炼油污水的深度处理

对炼油污水深度处理常用技术——过滤、膜分离、化学氧化技术进行了详细的论述，并结合中试试验，对动态砂滤系统、PAN膜处理系统和高级氧化系统处理炼油厂二级排放水的适用性进行了论证。     

客户关系生命周期管理及其策略

客户关系生命周期理论的提出对服务经济时代的企业产生了巨大的影响,该理论在强调了客户关系存在周期性的同时,也提出了对客户关系应当进行阶段性管理;阐述了客户关系生命周期理论,并在此基础上提出了客户关系动态发展模型,旨在帮助管理人员更清楚地认识到客户关系的长期价值和对客户关系的各个阶段进行良好的管理.     

Conservation implications of anthropogenic impacts on visual communication and camouflage

Anthropogenic environmental impacts can disrupt the sensory environment of animals and affect important processes from mate choice to predator avoidance. Currently, these effects are best understood for auditory and chemosensory modalities, and recent reviews highlight their importance for conservation. We examined how anthropogenic changes to the visual environment (ambient light, transmission, and backgrounds) affect visual communication and camouflage and considered the implications of these effects for conservation. Human changes to the visual environment can increase predation risk by affecting camouflage effectiveness, lead to maladaptive patterns of mate choice, and disrupt mutualistic interactions between pollinators and plants. Implications for conservation are particularly evident for disrupted camouflage due to its tight links with survival. The conservation importance of impaired visual communication is less documented. The effects of anthropogenic changes on visual communication and camouflage may be severe when they affect critical processes such as pollination or species recognition. However, when impaired mate choice does not lead to hybridization, the conservation consequences are less clear. We suggest that the demographic effects of human impacts on visual communication and camouflage will be particularly strong when human‐induced modifications to the visual environment are evolutionarily novel (i.e., very different from natural variation); affected species and populations have low levels of intraspecific (genotypic and phenotypic) variation and behavioral, sensory, or physiological plasticity; and the processes affected are directly related to survival (camouflage), species recognition, or number of offspring produced, rather than offspring quality or attractiveness. Our findings suggest that anthropogenic effects on the visual environment may be of similar importance relative to conservation as anthropogenic effects on other sensory modalities.     

Using empirical models of species colonization under multiple threatening processes to identify complementary threat‐mitigation strategies

Approaches to prioritize conservation actions are gaining popularity. However, limited empirical evidence exists on which species might benefit most from threat mitigation and on what combination of threats, if mitigated simultaneously, would result in the best outcomes for biodiversity. We devised a way to prioritize threat mitigation at a regional scale with empirical evidence based on predicted changes to population dynamics—information that is lacking in most threat‐management prioritization frameworks that rely on expert elicitation. We used dynamic occupancy models to investigate the effects of multiple threats (tree cover, grazing, and presence of an hyperaggressive competitor, the Noisy Miner (Manorina melanocephala) on bird‐population dynamics in an endangered woodland community in southeastern Australia. The 3 threatening processes had different effects on different species. We used predicted patch‐colonization probabilities to estimate the benefit to each species of removing one or more threats. We then determined the complementary set of threat‐mitigation strategies that maximized colonization of all species while ensuring that redundant actions with little benefit were avoided. The single action that resulted in the highest colonization was increasing tree cover, which increased patch colonization by 5% and 11% on average across all species and for declining species, respectively. Combining Noisy Miner control with increasing tree cover increased species colonization by 10% and 19% on average for all species and for declining species respectively, and was a higher priority than changing grazing regimes. Guidance for prioritizing threat mitigation is critical in the face of cumulative threatening processes. By incorporating population dynamics in prioritization of threat management, our approach helps ensure funding is not wasted on ineffective management programs that target the wrong threats or species.     

绿色全要素生产率省际空间学习效应实证

当前中国资源环境约束日益凸显,依靠全要素生产率成为解决这些问题的共识。然而仅仅依靠全要素生产率不能转变生产方式,关键在于区分绿色与非绿色偏向。研究使用中国省际面板数据,运用面板与动态空间面板模型方法,对比分析绿色全要素生产率、绿色"软技术"、绿色"硬技术"的影响机制。研究发现:1依靠全要素生产率驱动发展需要区别绿色与非绿色偏向;2必须注重绿色全要素生产率对绿色发展的作用及其运行机制;3不同偏向的绿色全要素生产率的省际空间学习效应不同;4绿色"软技术"对绿色发展贡献不充分。这就意味着,在当前中国资源环境约束日趋收紧的背景下,要区别绿色与非绿色全要素生产率的不同作用,否则将不能促进生产方式转变,实现绿色可持续发展。推动绿色可持续发展,一方面需要重视提升绿色全要素生产率的作用,另一方面需要重视绿色管理技术等绿色"软技术"对绿色发展的贡献。提升绿色全要素生产率,既要重视研发投入、人力资本投入,又要考虑技术市场、劳动智力结构、劳动者年龄结构的影响。提升绿色"软技术"的贡献率,改善绿色技术效率变动的吸纳能力。通过绿色全要素生产率的省际空间学习效应,实现中国省际区域间绿色可持续协同发展。此外,在引进吸收国外先进绿色技术时,既要重视对绿色"硬技术"的吸收,又要重视对绿色"软技术"的再学习。总之,"打铁还需自身硬",中国要继续鼓励支持绿色"硬技术"自主研发,巩固提升绿色"硬技术"对绿色发展的贡献。     

动态校准仪臭氧间接传递技术

对5台主流动态校准仪开展臭氧间接传递技术研究,对动态校准仪的准确性、可靠性、稳定性及臭氧传递的线性方程等性能参数进行了实验室考察。总体而言,发生型动态校准仪和分析型动态校准仪均可用于臭氧传递工作中。分析型动态校准仪可直接进行臭氧传递,发生型动态校准仪在臭氧传递前必须进行预校准。建议至少每3个月对发生型动态校准仪进行1次臭氧传递,每6个月对分析型动态校准仪进行1次臭氧传递。