Abstract

A coupling kinetics model is developed to simulate the release and transport of landfill leachate pollutants in a deformable municipal solid waste landfill by taking into account of landfill settlement, seepage of leachate water, hydrolyse of insoluble and degradable organic pollutants in solid phase, biodegradation of soluble and degradable organic pollutants in solid phase and aqueous one, growth of aerobic and anaerobic microorganism, and consumption of dissolved oxygen. The release and transport of organic pollutants and microorganisms in landfills in the process of landfill settlement was simulated by considering no hydraulic effect. Simulation results demonstrated that the interaction between landfill settlement and the release, transport and biodegradation of landfill leachate pollutants was significant. Porosity and saturated hydraulic conductivity were not constants because of the landfill settlement, which affected the release, transport and biodegradation of landfill leachate pollutants, and furthermore acted on the landfill settlement. The simulation results accorded with the practical situation, which preliminarily verified the reliability of the mathematical model and the numerical program in this paper.

Highlights

  • The release and transport of landfill leachate is a complex process, affected by landfill settlement, fluid movement, biodegradation and temperature changes, so a complete model which describes the release and transport of landfill leachate pollutants must contain mechanical, hydraulic, gas transport, temperature and biodegradation models, but it is almost impossible to realize a five-field coupling simulation, so this is often simplified to two or three field coupling model.Many researchers have studied the multi-field coupling problems of landfill leachate transport, and new models have been developed based on more detailed mathematical descriptions of the landfill and incorporating other aspects of interest apart from hydrology, such as the biological and physicalchemical degradation and settlement

  • C mo c o where ROCc and RACc are the aerobic and anaerobic degradation rates of SDA, respectively [ML−3T−1]; RDCo is the consumption rate for dissolved oxygen (DO) [ML−3T−1]; YCmo / Cc and YCma / Cc are the stoichiometric yield coefficients for aerobic microorganism and anaerobic microorganism, respectively; YCo / Cc is the consumption coefficient of DO

  • The release and transport ofpollutants and microorganisme in a landfill was simulated by considering no hydraulic action

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Summary

Introduction

The release and transport of landfill leachate is a complex process, affected by landfill settlement, fluid movement, biodegradation and temperature changes, so a complete model which describes the release and transport of landfill leachate pollutants must contain mechanical, hydraulic, gas transport, temperature and biodegradation models, but it is almost impossible to realize a five-field coupling simulation, so this is often simplified to two or three field coupling model. Demirekler et al [1] developed a three-dimensional mathematical model to estimate the quality and quantity of the landfill leachate produced. Durmusoglu et al [8] developed a one-dimensional multiphase numerical model to simulate the vertical settlement involving liquid and gas flows in a deformable MSW landfill. A coupling kinetic model was developed to simulate the release and transport of leachate pollutants in a deformable MSW landfill taking into account of hydrolyse and dissolution of solid-phase pollutants, oxygen consumption and transition of aqueous-phase pollutant biodegradation from anaerobic stage to aerobic one, and other behaviors such as convection and hydrodynamic dispersion, adsorption/desorption and growth of microorganism. A case study was given by considering none hydraulic action for studying the change law of water quality and quantity, which preliminarily verified the reliability of the mathematical model by comprising with the practical situation

Basic Assumptions
Mass-Conservation Equation
Mechanical Model
Hydraulic Model
Conceptual Framework
Hydrolysis of IDS
Dissolution of SDS
Biodegradation
Governing Equations
Numerical Solution Method
Results and Discussion
Displacement
Porosity
Saturated Hydraulic Conductivity
Pressure Head
3.10. AM and DO
Conclusions
Full Text
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