We chose to evaluate the ME
removal within 4 h, taking into account that the treated wastewaters
remain in the Milano-Nosedo WWTP for about 24 h; thus,
the selected time seemed to be a fair compromise in view of
integrating the conventional treatment with limited dimensional
requirements. To check the practicability of such assumptions, we
carried out further
final tests in single for a period of 24 h, taking
only two samples, one at the beginning and one at the end of the
tests. The tests were conducted with an initial
flow rate
corresponding to 3500 L/h, which would imply 18 min contact
time, recirculating the effluent in the pilot-plant 84 times to obtain
an overall 24 h contact time. After each test, the entire pilot-plant
was washed with tap water, to avoid memory-effects related to the previous tests. For this reason, to minimize this problem, as well as
to decrease the bivalve stress, the test schedule started with the
most diluted waste (100% outlet) and gradually increased its
concentration until 100% inlet. We monitored the wastewater
temperature both at the beginning and at the end of each test in
order to take into account its possible interference with the
filtration activity of zebra mussels. The wastewater temperature
within the pilot-plant during the spring season ranged from 14 to
24 C, comparable with the optimal values for D. polymorpha
filtration activity (10–20 C)
We chose to evaluate the MEremoval within 4 h, taking into account that the treated wastewatersremain in the Milano-Nosedo WWTP for about 24 h; thus,the selected time seemed to be a fair compromise in view ofintegrating the conventional treatment with limited dimensionalrequirements. To check the practicability of such assumptions, wecarried out furtherfinal tests in single for a period of 24 h, takingonly two samples, one at the beginning and one at the end of thetests. The tests were conducted with an initialflow ratecorresponding to 3500 L/h, which would imply 18 min contacttime, recirculating the effluent in the pilot-plant 84 times to obtainan overall 24 h contact time. After each test, the entire pilot-plantwas washed with tap water, to avoid memory-effects related to the previous tests. For this reason, to minimize this problem, as well asto decrease the bivalve stress, the test schedule started with themost diluted waste (100% outlet) and gradually increased itsconcentration until 100% inlet. We monitored the wastewatertemperature both at the beginning and at the end of each test inorder to take into account its possible interference with thefiltration activity of zebra mussels. The wastewater temperaturewithin the pilot-plant during the spring season ranged from 14 to24 C, comparable with the optimal values for D. polymorphafiltration activity (10–20 C)
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