几种不同浓缩技术回收水中病毒的效果

实验表明,即使病毒剂量低到一个感染性病毒也可使人感染,并可在人群间造成传播。因此,水环境的病毒污染深为人们关切。 水中的致病性病毒主要来自人和动物的排泄物及医院废水。目前已从各种水体中检测出120多种危及人类健康的肠道病毒和其它病毒。 世界卫生组织要求,用最灵敏的方法试验,在100—1000L饮用水中应不含病毒。因此,病毒的浓缩技术是监测水中病毒的前提。 现在国内外使用的浓缩技术方法很多,但都不甚理想。我们用几种不同的方法回收自来水和污水厂出水中实验性污染的病毒,以便选择具有快速、简便、适用性广泛、浓缩水样体积大和回收病毒效率高的技术。     

牛赶冲矿段地质构造研究及其意义

本文主要对洋水磷矿区牛赶冲矿段下盘矿的断裂和褶皱构造的产状、形态、位置、对矿体的破坏程度及其形成机制等进行了综合研究,并对研究结果在矿山生产实践中的指导意义进行了阐述。     

关于锅炉大气污染物排放标准的思考

多年来锅炉大气污染物排放标准,一直沿用以锅炉排放污染物的浓度来评价的方法.由于锅炉燃烧的方式,锅炉运行、维护等方面的管理上存在很大的差异,目前低温连续供热的理念地提出,都给锅炉排放污染物的评价带来新的考验.本文主要探讨,锅炉大气污染物的评价指标以污染物排放量还是以浓度为标准,更能体现锅炉运行的实际状况,更准确地反映污染源源强.     

两种方法监测近岸大气NOX浓度的比较

分别用常规法和离子色谱法对近岸海域大气ＮＯＸ 进行同步监测，并对两方法间的相关性和测定结果的换算进行了研究。结果表明： 两者呈极显著的正相关，相关系数达０－８３５（ｎ＝ ９） ，其测定结果是可换算的。为此，建立了采用离子色谱法测定气溶胶ＮＯ－３ 浓度预测近岸大气ＮＯＸ 浓度的方法。     

4—氯苯甲酸钠的光催化氧化降解及其影响因素

本试验采用P－25TiO2，光催化剂，对4－氯苯甲酸钠的光催化氧化降解及污染物初始浓度，催化剂投加量和入射光强等因素的影响进行了研究，研究发现污染物初始降解速率与其初始浓度的关系遵循Langmuir-Hinshelwood模式，其中半饱和浓度常数Ks不仅是催化剂和污染物种类的函数，而且也是入射光强的函数，催化剂投加量存在一限值，当低于此限值时，污染物降解速率由于催化剂浓度的不足受到影响而下降，当高于此限值时，污染物降解速率受催化剂投加量的影响变小，在本试验4－CBA－Na浓度为0.15-0.6mmol／L时该催化剂限值浓度大约为0.4g/L，在入射光强为1-7mW/cm^2和催化剂浓度为0.4g／L下，污染物降解速率与光强成0.67次幂关系，经估算其量子效率为6．3％。     

水泥土桩复合地基桩土应力参数研究

本文首先通过理论分析，认为桩土应力比、桩土荷载分担比等是反映水泥土桩复合地基工作性状的重要参数。然后通过现场试验，研究桩土应力比、桩土荷载分担比随荷载变化的规律。结果认为：随着荷载增加，桩土应力比逐渐减小，当比值达到某一特征值后，不再发生明显变化；桩土应力比、桩土荷载分担比不为常数，其变化是桩土变形协调的结果。最后得出有一定参考价值的结论。     

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。     

BUILDUP,WASHOFF, AND EVENT MEAN CONCENTRATIONS1

ABSTRACT: Most watershed water quality simulation models require the user to specify pollutant buildup and washoff rate parameters for pollutants, by land use. Buildup and washoff rates are difficult to measure directly, and only limited guidance and few observed data are available from the literature. Many studies, however, report storm event mean concentrations (EMCs). These EMCs must arise as a result of the buildup and washoff processes, but typically represent the net contribution from a variety of pervious and impervious surfaces. This paper explores the relationship between EMCs and buildup/washoff parameters. An assumption of the mathematical form of the buildup/washoff relationship gives an algebraic expression for the EMC consistent with model assumptions. This yields techniques to separate observed EMCs into contributions from different land uses and from pervious and impervious surfaces. Given this relationship, numerical optimization may be used to estimate site specific values of buildup and washoff parameters from observed storm EMCs for use in modeling. Use of this approach helps ensure that model parameters are consistent with observed data, providing a rational starting point for final model calibration. Several site examples demonstrate use of the method.     

Effect of soil solids concentration in batch tests on the partition coefficients of organic pollutants in landfill liner-soil materials

 The effect of the soil solids concentration in batch tests on the measured values of the partition coefficient (K _p) of organic pollutants in landfill liner-soil material was investigated. Since this study was based on the results of batch and column tests conducted independently, there were limitations to the conclusions derived. The organic compounds tested were benzene, methylene chloride, toluene, trichloroethylene, and p-xylene. The results of this study showed that as soil solids concentrations increased, the measured K _p values of these organic compounds strongly decreased. The observed values of K _p stabilized when the soil solids concentration was above a certain value. Typical K _p values obtained from batch tests conducted under high soil solids concentrations were close to those obtained from column tests. It was concluded that the K _p values of organic compounds measured under low soil solids concentrations, i.e., less than 100 g/l, may not correctly simulate the field situation. Consequently, the values of K _p obtained with low soil solids concentrations can result in an overestimation of the retardation factor of the landfill liner material. Received: March 14, 2002 / Accepted: August 25, 2002     

80m烟囟排放放射性气溶胶连续自动监测

本文介绍采用德国进口的ＬＢ９１００Ｄ监测系统对８０ｍ烟囟排放的α放射性气溶胶浓度进行连续、自动监测。并与国产ＦＪ－３６７，ＦＨ－４６３Ａ装置进行了对比则量，两套装置的测量结果符合得较好。