Environmental impact of an urban landfill on a coastal aquifer (El Jadida, Morocco)

• Published in: Journal of African earth sciences (1994) 2004-06, Vol.39 (3), p.509-516
• Main Authors: Chofqi, Amina, Younsi, Abedelkader, Lhadi, El Kbir, Mania, Jacky, Mudry, Jacques, Veron, Alain
• Format: Article
• Language: English
• Subjects: Coastal aquifer; Groundwater pollution; Landfill leachate; Morocco; Semi-arid region; Uncontrolled urban landfill
• ISSN: 1464-343X; 1879-1956
• DOI: 10.1016/j.jafrearsci.2004.07.013

The El Jadida landfill is one among many uncontrolled dumping sites in Morocco with no bottom liner. About 150 tons/day of solid wastes from mixed urban and industrial origins are placed directly on the ground. At the site of this landfill, the groundwaters circulate deeply (10–15 m) in the Cenomanian rock (calcareous–marl), which is characterised by an important permeability from cracks. The soil is sand–clay characterized by a weak coefficient of retention. The phreatic water ascends to the bottom of three quarries, which are located within the landfill. These circumstances, along with the lack of a leachate collection system, worsen the risks for a potential deterioration of the aquifer. To evaluate groundwater pollution due to this urban landfill, piezometric level and geochemical analyses have been monitored since 1999 on 60 wells. The landfill leachate has been collected from the three quarries that are located within the landfill. The average results of geochemical analyses show an important polluant charge vehiculed by landfill leachate (chloride = 5680 mg l −1, chemical oxygen demand = 1000 mg l −1, iron = 23 000 μg l −1). They show also an important qualitative degradation of the groundwater, especially in the parts situated in the down gradient area and in direct proximity to the landfill. In these polluted zones, we have observed the following values: higher than 4.5 mS cm −1 in electric conductivity, 1620 and 1000 mg l −1 respectively in chlorides and sulfate ( SO 4 2 - ), 15–25 μg l −1 in cadmium, and 60–100 μg l −1 in chromium. These concentrations widely exceed the standard values for potable water. Several determining factors in the evolution of groundwater contamination have been highlighted, such as (1) depth of the water table, (2) permeability of soil and unsaturated zone, (3) effective infiltration, (4) humidity and (5) absence of a system for leachate drainage. So, to reduce the pollution risks of the groundwater, it is necessary to set a system of collection, drainage and treatment of landfill leachates and to emplace an impermeable surface at the site of landfill, in order to limit the infiltration of leachate.