Full‐Scale Experience for Nitrogen Removal from Piggery Waste

The nitrogen‐removal performances of three full‐scale piggery wastewater treatment plants, with different organic and nitrogen loads, at the capacity ranges of 95 to 130 m3/d, were compared in this study. Plants 1 and 2 can be characterized as the modification of anoxic–aerobic operating systems, while an anaerobic and anoxic–aerobic system was used in plant 3. The influent piggery wastewater concentration for plant 1 was relatively lower, but with higher organic and nitrogen loads, resulting in higher chemical oxygen demand (COD) and ammonium‐nitrogen in effluent. Plant 2 was operated with strong piggery wastewater, resulting in a higher operating temperature. The high temperature could inhibit the nitrifying activity in plant 2. Although plant 3 was operated with a higher influent total COD‐to‐total Kjeldahl nitrogen ratio (TCOD:TKN), an additional external carbon source was required to polish the final effluent to remove nitrogen. Influent COD in plant 3 was used in the anaerobic–anoxic reactor for both methane (CH4) production and denitrification. Based on various mass balances, including caloric, COD, and alkalinity, the key elements for the successful nitrogen removal from the piggery waste were reactor temperature (less than 35°C), influent TCOD:TKN (greater than 6), and alkalinity‐to‐TKN ratio (greater than 3).

[1]  F J Humenik,et al.  Environmentally superior technologies for swine waste management. , 2004, Water science and technology : a journal of the International Association on Water Pollution Research.

[2]  Jin-young Jung,et al.  Enhanced nitrite build-up in proportion to increasing alklinity/NH4+ ratio of influent in biofilm reactor , 2000, Biotechnology Letters.

[3]  E. Choi,et al.  Application of piggery waste to nightsoil plant towards sustainable development. , 2003, Water science and technology : a journal of the International Association on Water Pollution Research.

[4]  Z. Yun,et al.  The nomographic design approach to recycled water reatment by the nitritation process. , 2002, Water science and technology : a journal of the International Association on Water Pollution Research.

[5]  E. Choi,et al.  Optimization of nitrogen removal from piggery waste by nitrite nitrification. , 2002, Water science and technology : a journal of the International Association on Water Pollution Research.

[6]  J. H. Ho,et al.  NITROGEN REMOVAL FROM PIGGERY WASTE BY NITRITE NITRIFICATION , 2000 .

[7]  S. Sözen,et al.  The effect of residual microbial products on the experimental assessment of the particulate inert COD in wastewaters , 1999 .

[8]  James E. Alleman,et al.  Thermophilic aerobic biological wastewater treatment , 1999 .

[9]  Awwa,et al.  Standard Methods for the examination of water and wastewater , 1999 .

[10]  I. Svoboda,et al.  Intermittent aeration of pig slurry – farm scale experiments for carbon and nitrogen removal , 1995 .

[11]  G. Bortone,et al.  Nitrification, Denitrification and Biological Phosphate Removal in Sequencing Batch Reactors Treating Piggery Wastewater , 1992 .

[12]  Takashi Osada,et al.  Removal of nitrogen and phosphorus from swine wastewater by the activated sludge units with the intermittent aeration process , 1991 .

[13]  R. Loehr,et al.  Inhibition of nitrification by ammonia and nitrous acid. , 1976, Journal - Water Pollution Control Federation.