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The results in Table 3 show that using the most conservative chloramine decay reaction, the <br />nitrite -N MCL of 1 mg/L could theoretically be exceeded if the chloramine dose is at 3 or 4 <br />mg/L (as total chlorine), and the C12:NH3-N ratio is less than 5:1. As the chlorine to ammonia -N <br />ratio decreases, more ammonia becomes available for the nitrification process. This calculation <br />is quite conservative as it is unlikely that 100% of chloramine decay will occur according to one <br />single pathway. <br />Valentine et al (1998) conducted a series of mass and redox balances on solutions of varying pH, <br />NOM concentration, and initial chloramine concentration. For all conditions that were studied, <br />the amount of nitrate formed as a percentage of monochloramine decay was less than 15 percent, <br />and for all but three cases the amount was less than 10 percent. The authors concluded that <br />although nitrate is an important decomposition product of monochloramine decay, it is not the <br />major nitrogen -containing decay species. <br />Using data from a survey of 40 utilities that use chloramine as a disinfectant and an earlier <br />survey by Hack (1984), Wilczak et al. (1996) indicate that nitrite and nitrate levels may increase <br />on the order of 0.005 to 0.5 mg/L, although increases of greater than 1 mg/L are possible. The <br />authors concluded that changes in nitrite and nitrate levels in drinking water usually caused by <br />nitrification are not substantial enough to exceed regulatory requirements as long as source <br />related levels are not near the regulatory MCLs. Nitrite levels during nitrification episodes have <br />been reported ranging from 0.005 to 0.5 mg/L as NOz - N, with levels more frequently ranging <br />from 0.015 to 0.1 mg/L (Wolfe et al. 2001). Figure 1 compares treatment plant effluent and <br />distribution system nitrite concentrations in nine chloraminating utilities (Kirmeyer et al. 1995). <br />This figure demonstrates that nitrite levels during nitrification events can vary from as little as <br />0.05 mg/L to as much as 1 mg/L. <br />01 <br />001 <br />Nitrite -nitrogen <br />8 0 <br />130 <br />O <br />O <br />8 - <br />Q B <br />O <br />O <br />O <br />001 .01 .1 <br />Concentration in plant effluent (mg/L) <br />Figure 1 <br />Comparison Between Plant Effluent and Distribution System Concentrations of Nitrite <br />Source: Kirmeyer et al. 1995 <br />Prepared by AWWA with assistance from Economic and Engineering Services, Inc. <br />E <br />N <br />T <br />O Winter Sampling <br />N <br />C <br />O <br />a <br />O Summer Sampling <br />m <br />Observations located above diagonal <br />�o rn <br />c E <br />indicate greater concentration in the <br />0 <br />distribution system than in treatment <br />plant effluent. <br />C <br />U <br />U <br />C <br />O <br />U <br />01 <br />001 <br />Nitrite -nitrogen <br />8 0 <br />130 <br />O <br />O <br />8 - <br />Q B <br />O <br />O <br />O <br />001 .01 .1 <br />Concentration in plant effluent (mg/L) <br />Figure 1 <br />Comparison Between Plant Effluent and Distribution System Concentrations of Nitrite <br />Source: Kirmeyer et al. 1995 <br />Prepared by AWWA with assistance from Economic and Engineering Services, Inc. <br />