Assimlable Organic Carbon (AOC) Criteria to Control Bactrium Regrowth in Drinking Water Distribution System

2012 ◽  
Vol 461 ◽  
pp. 440-443 ◽  
Author(s):  
Deng Ling Jiang ◽  
Xiao Liu ◽  
Guo Wei Ni

Relation between AOC concentration and bacterium regrowth in drinking water network was investigated to obtain biostability criteria. Comparably obvious linear relationship was found between the maximum HPC and the maximum content of AOC of the distribution system. By extrapolation of the line,HPC would decline to 0 when AOC was 57µg/L. That result showed that substrates cannot support bacterium growth when AOC was less than 57µg/L. Similar obvious linear relationship was also derived between the maximum AOC content and the maximum AOC consumption (∆AOC) of the distribution system. AOC consumption (∆AOC) would decline to 0 when AOC content was 43.8µg/L. it also showed that bacteria cannot growth and AOC do not be utilized when AOC was less than 43.8µg/L. Some researchers had proposed biostability criterias, i.e. Van der Kooij’s criteria of 10µg/L and LeChevallier’s criteria of 50~100µg/L. We proposed that the biostability criteria under chlorine disinfection was AOC <40µg/L.

2009 ◽  
Vol 43 (20) ◽  
pp. 5005-5014 ◽  
Author(s):  
Jeffrey G. Szabo ◽  
Christopher A. Impellitteri ◽  
Shekar Govindaswamy ◽  
John S. Hall

2007 ◽  
Vol 2007 (1) ◽  
pp. 449-467
Author(s):  
Stacia L. Thompson ◽  
Elizabeth Casman ◽  
Paul Fischbeck ◽  
Mitchell J. Small ◽  
Jeanne M. VanBriesen

Author(s):  
Pirjo-Liisa Rantanen ◽  
Ilkka Mellin ◽  
Minna Keinänen-Toivola ◽  
Merja Ahonen ◽  
Riku Vahala

We studied the seasonal variation of nitrite exposure in a drinking water distribution system (DWDS) with monochloramine disinfection in the Helsinki Metropolitan Area. In Finland, tap water is the main source of drinking water, and thus the nitrite in tap water increases nitrite exposure. Our data included both the obligatory monitoring and a sampling campaign data from a sampling campaign. Seasonality was evaluated by comparing a nitrite time series to temperature and by calculating the seasonal indices of the nitrite time series. The main drivers of nitrite seasonality were the temperature and the water age. We observed that with low water ages (median: 6.7 h) the highest nitrite exposure occurred during the summer months, and with higher water ages (median: 31 h) during the winter months. With the highest water age (190 h), nitrite concentrations were the lowest. At a low temperature, the high nitrite concentrations in the winter were caused by the decelerated ammonium oxidation. The dominant reaction at low water ages was ammonium oxidation into nitrite and, at high water ages, it was nitrite oxidation into nitrate. These results help to direct monitoring appropriately to gain exact knowledge of nitrite exposure. Also, possible future process changes and additional disinfection measures can be designed appropriately to minimize extra nitrite exposure.


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