Landfill leachate is a dangerous and polluting solution formed by a very complex sequence of physical, chemical and biological processes modifying the rainwater that percolates through waste (Bogner et al.,1996). Migration of the pollutants from the waste material into the percolating water is another important phenomenon requiring attention (Mora-Naranjo et al., 2004). The resulting leachate is a solution containing dissolved organic matter, inorganic macrocomponents, heavy metals and xenobiotic organic compounds and is characterized by reducing redox state (Christensen et al., 2001). Migration is a long-term and continuous process and the leachate may evolve and pollute the surrounding environment for hundred of years (Ustohalova et al., 2006).
Landfill leachate is often a dangerous solution with a very complex matrix, produced from biodegradation processes that can last for hundreds of years; during this period changes may take place in the composition and chemical, physical and structural characteristics of the containment system. The aim of this study is to investigate the main interactions taking place in the leachate-clayey barrier system and whether these interactions are capable of modifying solid phase porosity and creating an unconfined leachate plume, since, after mixing with pore water of the surrounding barrier, this leachate plume could pollute soil and groundwater. Numerical models of contaminant transport through porous media are now commonly used to make quantitative predictions of pollutant migration. The chemical and physical processes involved, and the alteration related to the migration of leachate into the clayey barrier of Buriano Landfill (Montecatini Val di Cecina, Tuscany) have been investigated using a one-dimensional model that simulates reactive diffusion. The numerical simulator used in this study is TOUGHREACT.
Copyright: | © IWWG International Waste Working Group | |
Quelle: | Specialized Session E (Oktober 2007) | |
Seiten: | 12 | |
Preis inkl. MwSt.: | € 12,00 | |
Autor: | C. Geloni M. Guidi B. Raco M. Cervelli | |
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BEHAVIOR OF MERCURY FROM USED BATTERIES IN LANDFILLS OVER 20 YEARS
© IWWG International Waste Working Group (10/2007)
In Japan, used batteries are collected as incombustible municipal waste, and the majority is landfilled. In 1983, it was determined that the used batteries in daily life contained mercury, and the fact the mercury-containing batteries, which were disposed of as waste raised fears of environmental mercury pollution.
EVALUATION OF ELUSION RATE OF ALKALINITY FROM BOTTOM ASH FOR A LONG TERM PERIOD
© IWWG International Waste Working Group (10/2007)
The pH in a landfill layer affects many phenomena such as dissolution/precipitation and adsorption/desorption of heavy metals, activities of microorganisms, CO2 absorption/emission etc. However, because of a lack of knowledge about the leachate characteristics after closing a landfill site, some inhabitants around a landfill site that has been constructed or is under consideration are anxious about the environmental safety of the landfill site, and often oppose the construction of a new landfill site. Therefore, it is very important to predict the pH change for a long term period for the management of a landfill site after closing. In order to predict the pH in a landfill layer, it is necessary to know the total amount of alkali and acid and their supply and consumption rates.
CLONIC: CLOSING THE NITROGEN CYCLE FROM LANDFILL LEACHATES. A BIOLOGICAL PROCESS WITH PARTIAL NITRITATION AND ANAMMOX FOLLOWED BY THERMAL DRY TREATMENT.
© IWWG International Waste Working Group (10/2007)
CESPA, being part of the Ferrovial Group, is a leader in waste management and urban services in Spain. CESPA has a long experience in landfill construction and management, having a total of 37 landfills either in property or in exploitation. As one of the legal and environmental requirements, a suitable leachate treatment must be applied before the discharge to the receiving media. Thus, the decision to choose for an specific leachate treatment depends on different parameter such as: the landfill site location, physical location of the leachate treatment plant, the leachate quality, the discharge requirements and the best technologies available.
TREATMENT OF LEACHATE FROM A LARGE HAZARDOUS WASTE LANDFILL SITE IN SOUTH AFRICA
© IWWG International Waste Working Group (10/2007)
The Vissershok Waste Management Facility is a privately owned hazardous waste landfill site, located to the north of Cape Town in South Africa. The joint owners are South African waste management companies, Enviroserv Waste Management and The Wasteman Group (partly owned by Suez Environment). Forty hectares of the site is permitted to receive H:H (high hazard rating) waste and has been in operation since 1974. It has an anticipated life to between 2020 and 2025. The facility presently receives about 300 000t of waste per annum of which some 23 percent is hazardous. The site provides disposal and treatment facilities for many types of hazardous waste. In addition there is an encapsulation process for wastes that cannot be treated or disposed of onto the landfill.
IRON AND MANGANESE SURVEY IN AQUIFERS SURROUNDING LANDFILLS IN WALLONIA (BELGIUM)
© IWWG International Waste Working Group (10/2007)
The groundwater biogeochemistry around waste disposal facilities has been widely studied since twenty years (Christensen & al, 2001). It is well known that leachates produced by water percolation through waste solid often contain high concentrations of dissolved Fe and Mn (Christensen & al, 1997). Fe(III) and Mn(IV) also enter in the composition of aquifers matrix (silts, sand, rocks). It constitutes a second reserve of electrons acceptors for further anaerobic biodegradation in aquifer environment.