Nitrification of anaerobically pretreated municipal landfill leachate (270-
1000 mg COD l(-1), 53-270 mg NH4-N l(-1)) was studied in laboratory-scale a
ctivated sludge reactors without (AS) and with (ASC) the addition of plasti
c carrier material. The reactors were run at 10 degrees C (149 d), 7 degree
s C (21 d) and 5 degrees C (16 d). With a loading rate of 0.027 g NH4-N g M
LVSS-1 d(-1) and a hydraulic retention time of ca. 3 d, at 10 degrees C, co
mplete nitrification was obtained in both reactors. At 7 degrees C, and in
loading rate of 0.023 g NH4-N g MLVSS-1 d(-1), both reactors appeared to be
overloaded and ammonium removal was only ca. 93%. At 5 degrees C, with a l
ower loading rate of 0.010 g NH4-N g MLVSS-1 d(-1), complete nitrification
was obtained in the ASC reactor but in the AS reactor only 61% of ammonium
was removed. Aerobic posttreatment produced effluent with 150-500 mg COD l(
-1), less than 7 mg BOD7 l(-1), and, on average, less than 13 mg NH4-N l(-1
).
In batch assays at 24 and 10 degrees C, maximum nitrification rates were 0.
13 and 0.03 g NO3-N g MLVSS-1 d(-1), respectively, while ammonium removal r
ates were twice as high. The nitrification rates were higher with than with
out carrier material, suggesting that a large fraction of nitrifying micro-
organisms was attached on the surface of the carrier material.
The results show that nitrification of anaerobically treated leachate is fe
asible at temperatures down to 5-10 degrees C. Benefits of the carrier reac
tor were evident only at low temperatures and under varying loading conditi
ons. (C) 2000 Elsevier Science Ltd. All rights reserved.