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After a contact time of 2 h, the sludge was dewatered with the flocculant.
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Sodium cacodylate buffer (0.1 mol/L) was applied to wash the fixed granules and then samples were dewatered with a graded ethanol series, i.e. 10, 25, 50, 75, 90 and 100%%.
In a third WWTP (no. 6), anaerobic digested sludge was dewatered; yet, the dewatering process resulted in only minor removal for TCC and 3-Cl′-TCC, while no significant changes were observed for the other carbanilides.
Raw FS coming from household and public toilets at a ratio of 2 1 (v/v) was dewatered on sand drying beds to obtain DFS.
Flocculation was carried out using a Ti-salt flocculant and the collected sludge was dewatered and incinerated at 600 °C to produce TiO2 nanoparticles.
Red mud (RM), the digestion by-product of bauxite processing from "Aluminum Hellas", was dewatered by means of a filter press.
The material was dewatered, neutralized, acid impregnated, and pretreated.
In the first step harvested fermentation broth was dewatered by continuous disc stack centrifugation.
At one site (no. 6), the digested sludge was dewatered after anaerobic digestion.
The wet corn stover was dewatered after 30 minutes in a press (Tinkturenpressen HP5M, Fischer Maschinenfabrik GMBH, Germany) of capacity 3 litres.
The mixed impregnated feedstock was dewatered using a horizontal tapered screw-press to 60% total solids prior to pretreatment, and then mixed again by coning and quartering.
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