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Overall, the concentration of EV throughout the WWTP remained relatively stable for the eight-month sampling period. 05) seasonal variation was observed during the current study for EV quantification. 1. 3. 10. Log removal Following the quantification of viruses, the overall log removal achieved by the MBR and the entire WWTP’s was calculated using equations (3) and (4) for HAdV, EV and NoV.   Membrane Influent Concentration Log Removal¼log10 Membrance Effluent Concentration (3)   Influent Concentration Log Removal ¼ log10 Effluent Concentration (4) For membrane and post-secondary treatment samples that were below the detection limit, the log removal values were calculated by using the detection limit of the individual assays.

Hydrobiologia 540, 79e104. , 2004. Modelling bacterial water quality in streams draining pastoral land. Water Research 38, 700e712. , 2004. Use of macrocosms to determine persistence of Escherichia coil in recreational coastal water and sediment and validation with in situ measurements. Journal of Applied Microbiology 96, 922e930. , 2000. The fate of stormwaterassociated bacteria in constructed wetland and water pollution control pond systems. Journal of Applied Microbiology 89, 349e360. , 1995.

Fig. 8a shows the simulated timeseries at Temse, showing the reduced concentrations and variability. The remaining variability is related to the upstream discharge (average daily discharges are prescribed). Fig. 8c shows the daily water discharge at Melle (see Fig. 1 for location) and there is indeed a clear similarity with the concentration timeseries at Temse. High concentrations at Temse generally coincide with high discharge periods. The concentrations at Uitbergen are overall less influenced by the tide.

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Water Research Volume 45 Issue 9 by Mark van Loosdrecht

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