NITRIFICATION PATTERN IN A FLUCTUATING ANAEROBIC-AEROBIC POND ENVIRONMENT

被引:18
作者
DIAB, S [1 ]
KOCHBA, M [1 ]
AVNIMELECH, Y [1 ]
机构
[1] TECHNION ISRAEL INST TECHNOL,FAC AGR ENGN,HAIFA,ISRAEL
关键词
FISH POND; OXIDATION PONDS; STABILIZATION POND; NITRIFYING BACTERIA; OXIC AND ANOXIC CYCLES; ADAPTATION TO FLUCTUATING CONDITIONS;
D O I
10.1016/0043-1354(93)90027-F
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Nitrification does not occur in conventional fish ponds or in oxidation ponds. Yet, intensive nitrification occurs in continually aerated and mixed fish ponds and in activated sludge systems. In a combined fish pond system, water from a conventional pond is pumped through a continually aerated and mixed pond, with a 5 h average hydraulic residence time. Unlike other aerated ponds, nitrification did not occur in this case. The masons for nitrification inhibition were studied in laboratory and field experiments. Inhibited nitrification was not due to any factor associated with water composition and persisted even when the water was replaced. In addition, it was not limited by a lack of inoculum. Nitrification in a laboratory assay started immediately in samples taken from a continually aerated pond, while it started only following a 24-48 h lag period in water sampled from a conventional pond or from the combined pond system. Nitrifying bacteria have to adapt to the partial anoxic conditions in the conventional pond. It is assumed that the lag period is needed by the reverse process, adaptation to oxic conditions. The ecological and practical implications of this phenomenon are discussed. The lag period is needed when nitrifiers are transferred from anoxic to oxic conditions as a protective mechanism to ensure that nitrification will take place only if continuous or long-term oxic conditions prevail.
引用
收藏
页码:1469 / 1475
页数:7
相关论文
共 26 条
[1]   NITRIFYING BACTERIA IN WASTE-WATER RESERVOIRS [J].
ABELIOVICH, A .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1987, 53 (04) :754-760
[2]  
Alexander M., 1965, METHODS SOIL ANAL 2, V9, P1477, DOI 10.2134/agronmonogr9.2.c51
[3]   METABOLISM OF HYDROXYLAMINE TO NITRITE BY NITROSOMONAS [J].
ANDERSON, JH .
BIOCHEMICAL JOURNAL, 1964, 91 (01) :8-&
[4]   ESTIMATION OF NITRIC OXIDE FORMED FROM HYDROXYLAMINE BY NITROSOMONAS [J].
ANDERSON, JH .
BIOCHEMICAL JOURNAL, 1965, 94 (01) :236-&
[5]  
AVNIMELECH Y, 1986, Aquaculture and Fisheries Management, V17, P231, DOI 10.1111/j.1365-2109.1986.tb00109.x
[6]   USE OF NITRIFIER ACTIVITY MEASUREMENTS TO ESTIMATE THE EFFICIENCY OF VIABLE NITRIFIER COUNTS IN SOILS AND SEDIMENTS [J].
BELSER, LW ;
MAYS, EL .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1982, 43 (04) :945-948
[7]   FACTORS CONTROLLING THE SEASONAL-VARIATION OF NITRATE IN LAKE ERKEN [J].
BOSTROM, B .
INTERNATIONALE REVUE DER GESAMTEN HYDROBIOLOGIE, 1981, 66 (06) :821-836
[8]   NITRIFICATION POTENTIAL AND FACTORS GOVERNING RATE OF NITRIFICATION IN LAKE-KINNERET [J].
CAVARI, BZ .
OIKOS, 1977, 28 (2-3) :285-290
[9]  
COLT J, 1979, UNPUB NITROGEN TOXIC