首页> 外文期刊>Environment protection engineering >MODELLING OF MASS TRANSPORT IN WATERCOURSES CONSIDERING MASS TRANSFER BETWEEN PHASES IN UNSTEADY STATES. PART II. MASS TRANSPORT DURING ABSORPTION AND ADSORPTION PROCESSES
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MODELLING OF MASS TRANSPORT IN WATERCOURSES CONSIDERING MASS TRANSFER BETWEEN PHASES IN UNSTEADY STATES. PART II. MASS TRANSPORT DURING ABSORPTION AND ADSORPTION PROCESSES

机译:考虑非稳态状态下相之间的传质的水流中的传质建模。第二部分吸附和吸附过程中的质量运输

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摘要

Equations describing the rate of adsorption and absorption processes and those based on Whitman's model have been analyzed. In the case of unstable states, the mass flux penetrating to the layer of the river sediment and calculated by means of these equations differs from the mass flux calculated from the mass diffusion equation. In order to minimize the discrepancies between the flux determined by Whitman's model and a real flux, the correction factor has been introduced into the concentration gradient equation originated from Whitman's model. This correction factor can be expressed as a time dependence of the product of a certain parameter and the concentration derivative at the phase boundary (solid phase side). The corrected equation for the concentration gradient has been used to derive another equation, describing a general rate of the absorption and adsorption processes at the linear interfacial equilibrium and the chemical reactions occurring in the liquid and solid phases; the chemical reactions follow the first order monomolecular mechanism in unstable states with reference to the liquid phase. Knowing the general rate of the earlier mentioned processes it is possible to construct an advective-dispersion model of mass transport in a river including these particular processes. Such a model contains a term defined as a correction factor referring to the time dependence of the concentration derivative with respect to time. The described model may be also used for simulation of the transport of pollutants undergoing adsorption and absorption in the layer river sediment; the processes occur with a finite and infinitely large rate through the equilibrium states.
机译:分析了描述吸附和吸收过程速率的方程以及基于惠特曼模型的方程。在不稳定状态下,渗透到河流沉积物层并通过这些方程式计算的质量通量不同于从质量扩散方程式计算的质量通量。为了使惠特曼模型确定的通量与实际通量之间的差异最小化,已将校正因子引入了源自惠特曼模型的浓度梯度方程。该校正因子可以表示为某一参数与相边界(固相侧)上的浓度导数的乘积的时间依赖性。校正后的浓度梯度方程式已用于推导另一个方程式,描述了线性界面平衡下吸收和吸附过程的一般速率以及液相和固相中发生的化学反应。化学反应遵循不稳定状态下相对于液相的一阶单分子机理。了解了前面提到的过程的总体速率,就可以构建包括这些特定过程在内的河流中物质运输的对流扩散模型。这种模型包含定义为校正因子的术语,是指浓度导数相对于时间的时间依赖性。所描述的模型还可以用于模拟在层状河沉积物中吸附和吸收的污染物的运输。在平衡状态下,过程以有限且无限大的速率发生。

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  • 来源
    《Environment protection engineering》 |2011年第4期|p.71-89|共19页
  • 作者

    ANDRZEJ BIELSKI;

  • 作者单位

    Cracow University of Technology, Department of Environmental Engineering, ul. Warszawska 24,31-155 Cracow, Poland;

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  • 正文语种 eng
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  • 入库时间 2022-08-18 00:06:17

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