欧拉观测的大气扩散参数计算方法探析及应用

根据湍流扩散统计理论，讨论了利用欧拉观测的风速资料求解正态扩散模式中大气扩散参数的计算方法及其实现，并以海南洋埔开关区各稳定度大气扩散参数的计算为实例作了分析。     

湿式氧化技术处理炼油厂碱渣废水

考察了湿式氧化法处理运行过程 ,以及相关参数的控制方案。在实现装置出水、废气达标排放的前提下 ,稳定控制装置运行是可以实现的。如后续有酸化除酚工艺和SBR工艺进行再处理 ,则应选用温度 (14 5± 5 )℃ ,压力控制在 0 6～ 0 .7MPa的湿式氧化法     

氢氧同位素交换动力学及其地质意义

氢氧同位素交换动力学是同位素地球化学学科的前沿。它使同位素地球化学的研究由静态向动态、定性向定量、封闭体系向开放体系发展 ;为各种天然地质过程的研究定量提供有关的时间、温度、作用机制、演化途径及地质体的冷却史等重要信息。本文概述了氢氧同位素交换动力学参数、同位素交换动力学模式、在地学研究中的应用及实验测试新技术等。     

含PVA印染废水的生化动力学研究及其应用

通过对含有聚乙烯醇(PVA)印染废水的生化降解动力学的研究,确定表征微生物生长繁殖、自身氧化等的动力学参数,以此作为生化处理工艺设计的重要依据,使之更符合废水的水质特点,从而提高处理效率;同时,通过掌握其处理过程的规律,为工艺管理、运行效果预测,提供比较明确的控制量。     

活性污泥数学模型中进水易降解有机物的测定

ASM系列模型 (ASMs)自推出以来在欧美得到广泛应用。要想利用ASMs对特定污水处理过程进行准确的模拟 ,首先必须得到该过程污水的水质特性参数。介绍了连续式OUR计量法、序批式OUR计量法和絮凝过滤物理化学法等 3种测定ASMs中进水易降解有机物的方法 ,通过分析比较指出了各自的优缺点及适用情况。     

装甲钢自然环境试验与人工加速试验的相关性

对某型装甲钢在酸雨大气环境下自然暴露与人工模拟加速试验的相关性进行了研究。利用腐蚀机理对比、Spearman秩相关系数、灰色关联度、加速转换因子等方法进行了相关性的定性定量评价。评价结果表明模拟加速试验与自然环境暴露试验有较好相关性。     

铅芯橡胶支座等效线性分析模型参数的研究

针对目前铅芯橡胶支座等效线性分析模型动力参数选取不够合理的现状 ,笔者通过对铅芯橡胶支座水平动态试验分析 ,系统研究了铅芯橡胶支座等效线性分析模型参数与其几何结构及外加动力荷载特性的关系。研究结果表明 :铅芯橡胶支座等效线性分析模型参数 (水平耗能、等效刚度及等效阻尼比 )主要由其本身的几何构造及组成材料决定 ,且在往复加、卸载循环过程中具有较好的稳定性。笔者对试验数据进行数学统计分析 ,归纳出一些经验公式 ,为其等效线性化动力分析模型参数的合理选取提供了计算方法 ,从而提高其动力分析结果的安全性。     

METHODOLOGIES FOR CALIBRATION AND PREDICTIVE ANALYSIS OF A WATERSHED MODEL1

ABSTRACT: The use of a fitted parameter watershed model to address water quantity and quality management issues requires that it be calibrated under a wide range of hydrologic conditions. However, rarely does model calibration result in a unique parameter set. Parameter nonuniqueness can lead to predictive nonuniqueness. The extent of model predictive uncertainty should be investigated if management decisions are to be based on model projections. Using models built for four neighboring watersheds in the Neuse River Basin of North Carolina, the application of the automated parameter optimization software PEST in conjunction with the Hydrologic Simulation Program Fortran (HSPF) is demonstrated. Parameter nonuniqueness is illustrated, and a method is presented for calculating many different sets of parameters, all of which acceptably calibrate a watershed model. A regularization methodology is discussed in which models for similar watersheds can be calibrated simultaneously. Using this method, parameter differences between watershed models can be minimized while maintaining fit between model outputs and field observations. In recognition of the fact that parameter nonuniqueness and predictive uncertainty are inherent to the modeling process, PEST's nonlinear predictive analysis functionality is then used to explore the extent of model predictive uncertainty.     

Specific Contributions of Politics,Economics, and Toxicology in Setting Socially Consensual Limit Values

/ Limit values are legal limits for the concentrations of substances in the environment. They must be agreed upon in a consensual procedure between science, economics/technology, and political forces. This is a crucial political precondition for their social acceptance. The arguments put forward to justify their expediency and numerical level are based not only on risk-benefit considerations but also on the aspect of the technical avoidability of direct and indirect exposure. The critical assessment of the direct benefit of specified exposures falls within the responsibility of economics/technology, whereas criteria for their potential adverse effects (direct and indirect) are provided by medicine/biochemistry and/or ecology. Within this concept, the avoidance of nonbeneficial-even if not openly adverse-exposure is the essential aim of environmental hygiene and should be promoted by politics/science. In general, society or segments thereof reject adverse, accept beneficial, and tolerate unavoidable exposure. Conflicts of interest arise when different groups of society simultaneously define a given exposure as being adverse, beneficial, and unavoidable. Therefore, from the viewpoint of society as a whole, an optimal exposure lies as far as reasonably achievable at a level lower than known or plausible adverse effect thresholds (as defined by toxicology or ecology). This optimal level of exposure must be determined using a transparent and, hence, public procedure.KEY WORDS: Legal limit values; Benefit threshold; Social acceptance; Social tolerability; Adverse effect threshold; Avoidable exposure; Tolerance threshold; Environmental hygiene