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Treatment of Sanitary Landfill Leachate : Biological Treatment
H.-J. Ehrig
Instittit für Stadtbauwesen, TU Braunschweig, Postfach 3329, 3300 Braunschweig, West Germany
In most cases leachates from sanitary landfills are highly polluted (COD, BOD5, ammonium) and must be treated before discharge. Treatment experiments with aerated lagoons, activated sludge plants and rotating biological contactors in laboratory and technical scale are described. Treatment with full degradation of organics and oxydation of ammonium (nitrification) are possible with attention to some special problems of leaching treatment such as high ammonium concentrations, the BOD5/N-ratio, precipitation of inorganics, cooling, foaming etc. From aerated lagoons BOD5-effluents 50 mg l-1 could be obtained at volumetric loadings 20 g BOD5 m -3 day-1. Shorter retention times in activated sludge plants result in lower BOD levels ( 25 mg l-1) at loading rates between 0.02 and 0.05 kg BOD5 kg MLSS- 1 day-1 provided that the BOD5/N-ratio > 1. In all other cases the dimension parameter for activated sludge plants is ammonium load 0.03 kg N kg MLSS-1 day- 1. Similar results are obtained with rotating biological contactors also with ammonium as the critical loading value, here as an area loading 2 g N m-2 day-1. In all cases ammonium is the dominate parameter and careful operation is necessary because nitrification is a very sensitive process. Operation problems could result in serious water pollution problems with discharges of high concentrations of ammonium or nitrite.
Key Words: Municipal solid waste sanitary landfill leachate pollution potential biological treatment nitrification aerated lagoon activated sludge rotating biological contactor
Waste Management & Research, Vol. 2, No. 1,
131-152 (1984)
DOI: 10.1177/0734242X8400200116

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Hamidi Abdul Aziz, S. Alias, F. Assari, and Mohd Nordin Adlan
The use of alum, ferric chloride and ferrous sulphate as coagulants in removing suspended solids, colour and COD from semi-aerobic landfill leachate at controlled pH
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