The floc blanket formed by the Clari–DAF system.
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Treatment Results
The plant was built and commenced operation in 2003. Currently, the coagulant chemical feed is polyaluminum chloride and lime, averaging 12 mg/L and 2 mg/L respectively. The G value, which defines the amount of mixing taking place and is calculated uses power input, volume and viscosity of liquid (where the higher the value, the more violent the mixing), in the flocculators is 70 sec–1 in the first stage, and 50 sec– in the second stage. The loading rate is 16.3 m/hr (6.7 gpm/ft2) based on collector area, while the recycle rate is 10% in the summer and 7% during the other nine months. Since start–up of the facility, the average raw turbidity has been 5 NTU, DAF system effluent 0.3 NTU, and filter effluent 0.04 NTU. Rain events have resulted in raw water turbidities ranging from 64 to 430 NTU. During those times, 2.3 to 16.5 NTU turbidity remained in the effluent from the pre–sedimentation process. This turbidity was reduced by the DAF system to 0.14 – 1.1 NTU and then by the filter to 0.02 – 0.09 NTU producing a stable water quality.
When removing organics in the raw water, K–Water has elected to reduce the level of chlorinated by–products below the criteria mandated in Korea and the United States as listed in Table 1.
Table 1. Chlorinated DBPs removed at Songjeon facility vs. U.S. and Korean mandates | Units : mg/L | Parameter | Korea | USA | K-Water |
TTHMs | < 0.1 | < 0.08 | < 0.064 |
HAA2 | < 0.1 | < 0.06 | < 0.048 |
CH | < 0.03 | | < 0.024 |
To help the plant meet the goals, PAC was fed prior to the addition of the coagulant. Table 2 summarizes the average concentrations of chlorinated by–products in the effluent water with PAC addition from April 2005 to March 2006 and without PAC addition from April 2004 to March 2005.
Table 2. Average concentrations of chlorinated DBPs in effluent with PAC addition and without. | Units : mg/L | Parameter | w/o PAC | w PAC | Goal |
TTHMs | 0.022 | 0.022 | < 0.064 |
HAA2 | 0.029 | 0.020 | < 0.048 |
CH | 0.006 | 0.007 | < 0.024 |
With PAC, concentrations of TTHMs and CH were all unchanged, but HAA2 was reduced by 9 ug/L. This is significant because, of the three chlorinated by–products, HAA2 has been the biggest problem in most Korean potable water treatment plants. During this study, the pre–sedimentation basin observed an increase in turbidity when feeding PAC, while the DAF system showed excellent efficiency for removing turbidity. While feeding PAC, and with raw water turbidity of 3.5 NTU, the pre–sedimentation basin average effluent went from 1.9 NTU to 2.8 NTU, while the DAF system effluent yielded a slight increase from 0.15 to 0.23 NTU. Plant personnel continue to investigate additional methods to further reduce chlorinated by–products.