养鸭场对环境影响的调查与评价

介绍了应用卫生学现场观察测量等方法,对滇池周边养鸭场周围大气及纳污水体滇池进行调查监测,并根据监测结果,对养鸭场周边受污染的空气环境质量和滇池水质进行环境健康评价,表明养鸭场对周边大气和水体的污染程度的范围,并提出相应的控制养鸭场污染的对策措施。     

风向变化对城市大气污染的影响及试验分析

针对城市大气污染的复杂多变状况，在理论分析的基础上，通过风洞实验对城市大气污染扩散模型进行了模拟试验研究，建立了适合一定条件下城市大气污染物扩散的数学和物理模型，并对城市大气污染状况的影响因素进行了分析，在得到特定条件下城市大气污染扩散普遍规律的同时，重点讨论了风向变化对城市大气污染的影响，该方法同时还可以应用于城市大气污染物扩散浓度的估算。     

四川盆地近地面风场及污染物输送通道统计分析

利用2017年四川盆地18个城市PM_2.5小时浓度数据、欧洲气象中心ERA-Interim再分析资料对四川盆地污染特征及不同季节近地面风场特征进行统计分析.通过分异指数和相关性分析各城市PM_2.5逐小时浓度，结合近地面风场特征分析出四川盆地污染物变化趋势最相似的城市组合，探索污染物传输特征.研究发现，分异指数和相关性分析得到的传输通道城市组合与地面风场基本相符.四川盆地污染物输送途径可能包括以下3条路径，第1条"川西通道"：污染物随气流沿广元→绵阳东南部→德阳→成都、眉山北部→雅安流动；第2条"川中通道"：污染物随气流沿巴中→南充北部→遂宁北部、绵阳东南部→资阳北部→眉山东部→乐山北部流动；第3条"川东通道"：污染物随气流沿重庆北部→达州、广安→南充南部→遂宁中部→资阳东部→内江、自贡→宜宾、泸州流动.川西通道城市污染排放量大，容易引起连片污染，对应城市群应实施联防联控；川东通道末端在川南城市群和重庆形成风场辐合，造成污染物的滞留和累积，因此，建议在中长期产业布局中减少川南城市群的重污染企业.     

中国风电的时空分布特征和发展趋势

利用1990-2005年中国和英国风电发展数据,对两国风电的时空分布特征和发展趋势进行了比较分析。据英国风电发展的阶段性,把中国风电发展划分为试验性发展、规模发展、过渡发展3个阶段,并预测到2007年步入大规模发展阶段。因此,未来几年,中国风电场数目和规模将会快速增长,并且由集中走向高密度集中分布。据对影响风电场省级时空分布的自然、市场和政策共8个选择因子的主成分分析和系统聚类分析结果,将中国风电场按省级划分为3个区域和8个亚区域,对聚类结果进行逐步判别回判,结果表明准确率达92.6%。     

一个研究街道峡谷流场及浓度场特征的三维数值模式

目前，研究街道峡谷内流场及机动车排放污染物的扩散行为特征所采用的主要方法为：采用野外测试法和物理模拟法，而采用三维数值模拟方法研究此问题的工作很少。本文创建了一个研究微尺度街道峡谷内流场及机动车排放污染物扩散特征的三维数值模式，即首次采用伪不定常方法，利用K——E闭合方案，建立了一个模拟城市街道峡谷内流场及污染物扩散特征与街道峡谷风场、街道几何结构及两侧建筑物高度对称性之间的复杂关系的三维数值模式。经过与实际监测资料及风洞实验对比，结果表明此三维模式具有较好的模拟精度，能够很好模拟峡谷内的风场及街谷几何结构对街道峡谷内流场及浓度场特征的影响，有很强的实用性。     

国有林场安全生产依法管理措施探讨

本文从林场安全生产管理实际出发，论述了国有林场如何贯彻实施(安全生产法)，提高林场安全生产依法管理水平的内容与措施。     

The Relation Between Sandstorms and Strong Winds in Xinjiang,China

With observational data spanning 1961–1999 from 90 meteorological stations in Xinjiang, China, the spatial and temporal characteristics of sandstorms and strong winds, and the contribution of strong winds to the occurrence of sandstormsare analyzed. Moreover, the dominant wind direction and minimumwind speeds during sandstorm periods are discussed. The research shows that although possessing similar climatic trends, sandstorms and strong winds in Xinjiang have opposite geographical distributions, i.e. places with more sandstorms show fewer strong winds. The contribution of strongwinds to sandstorms in northern Xinjiang is larger than that insouthern Xinjiang. The dominant wind directions clearly indicatethe paths of the weather systems that introduced the sandstorms.The minimum wind speeds in the sandstorms were over 10 ms^-1in northern and eastern Xinjiang and in the Turpan and Yanqi Basins of southern Xinjiang. In Tarim Basin of southern Xinjiang,however, the minimum wind speed was about 6–8 ms^-1, and even 6 ms^-1 at its southern edge.     

QUALITY OF HYDROMETEOROLOGICAL DATA IN COLD REGIONS1

ABSTRACT: Many users of hydrometeorological records are not aware of the number of inconsistencies and biases that occur in hydrometeorological records. Examples are presented illustrating how the exposures of sites for measurement of precipitation, wind, snow on the ground, and evaporation determine to a large extent how useful the records are for estimating areal conditions. For areas where precipitation in the form of snow produces a significant portion of the runoff, a smaller number of quality records may be more valuable for modeling than a much larger number of records of lower quality. Information is presented to show that the overall value of an operational hydrometeorological network is dependent upon how consistent and representative of average conditions the collected records are, especially for mountainous areas in cold regions.     

台风湍流积分尺度与脉动风速谱——基于实测数据的分析

基于4个台风过程中的长时间序列风速、风方向观测数据，分析研究了近地台风的湍流积分尺度和脉动风速谱等脉动特性。介绍了湍流积分尺度的几种常见的计算方法，基于实测台风数据，分析研究了台风过程中湍流积分尺度的变化以及不同计算方法的稳定性。根据实测数据计算了纵向脉动风速谱，并与Von-Karman谱、Davenport谱、Simiu谱和Harris谱等经验谱进行了比较，给出了最适合描述台风纵向脉动风速谱的经验谱。还计算了横向脉动风速功率谱，并与基于各向同性湍流理论推导出的水平横向脉动风速谱进行了对比。     

Human Diets and Animal Welfare: the Illogic of the Larder

Few moral arguments have been made against vegetarian diets. One exception is the “Logic of the Larder:” We do animals a favor by purchasing their meat, eggs, and milk, for if we did not purchase these products, fewer animals would exist. This argument fails because many farm animals have lives that are probably not worth living, while others prevent a significant number of wild animals from existing. Even if this were not so, the purchase of animal products uses resources that could otherwise be used to bring a much greater number of animals into existence.