PHYSICAL AND CHEMICAL TREATMENT OF A NITRIFIED LEACHATE FROM A MUNICIPAL LANDFILL

Citation
U. Welander et T. Henrysson, PHYSICAL AND CHEMICAL TREATMENT OF A NITRIFIED LEACHATE FROM A MUNICIPAL LANDFILL, Environmental technology, 19(6), 1998, pp. 591-599
Citations number
21
Categorie Soggetti
Environmental Sciences
Journal title
ISSN journal
09593330
Volume
19
Issue
6
Year of publication
1998
Pages
591 - 599
Database
ISI
SICI code
0959-3330(1998)19:6<591:PACTOA>2.0.ZU;2-Z
Abstract
Leachate from a Swedish municipal landfill in the methanogenic phase w as nitrified and then treated by various physical and chemical methods : oxidation with Fenton's reagent and with ozone, precipitation with f erric chloride and with aluminum sulphate and adsorption onto activate d carbon. The leachate was analyzed by measuring the COD (chemical oxy gen demand), the BOD, (biochemical oxygen demand) and the TOC (total o rganic carbon). Specific organic compounds were analyzed by GC/MS (gas chromatography and mass spectrometry) while the molecular weight of t he organic matter was determined by ultrafiltration. The nitrification process resulted in 20-30% of the COD being removed. The maximum COD removed after nitrification and oxidation was 80% using Fenton's reage nt and 54% using ozone. The combination of nitrification and precipita tion gave a maximum COD removal of 68% using ferric chloride and 54% u sing aluminum sulphate, while nitrification and adsorption onto activa ted carbon gave a maximum COD removal of 76%. A combination of nitrifi cation, precipitation with ferric chloride and adsorption on activated carbon gave a TOC removal of 96%. The ultrafiltrations showed that ni trification and adsorption onto activated carbon were the most efficie nt processes for the removal of low molecular weight compounds. The GC /MS analyses showed that, for instance, C-3-substituted benzenes and C -2-C-4 substituted phenol isomers were degraded during the nitrificati on process, while phthalates were unaffected even after treatment with Fenton's reagent or by adsorption onto activated carbon.