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Combining submerged membrane technology with anaerobic and ...

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Tertiary <strong>membrane</strong> filtration of industrial wastewater using granular or flocculent biomass SBRs3.3.1.2. Cleaning strategyFigure 3.2. Membrane module.Physical cleaning of the <strong>membrane</strong> module was performed by rinsing <strong>with</strong> tap water.Chemically enhanced backwashing was not used during the experiments. Chemicalrecovery cleaning was conducted when TMP in the <strong>membrane</strong>s was higher than 30 kPa orpermeability value was below 50 L·m -2·h -1·bar -1 . The cleaning procedure was:- Soak in chlored water (2000 ppm Cl 2:l) for 2 h.- Backwashing <strong>with</strong> chlored water (2000 ppm Cl 2:1) for 1 h.3.3.1.3. Influent <strong>and</strong> operating strategyIndustrial wastewater from a fish freezing industry was treated during the study. Theraw wastewater contained 50-300 mg·L -1 ammonia <strong>and</strong> 1000-6300 mg·L -1 total COD. Totalphosphorous ranged between 70 <strong>and</strong> 190 mg·L -1 of which 60-70% was orthophosphate.Soluble COD represented around 85% total COD. Lots of the industrial wastewater weretaken <strong>and</strong> diluted <strong>with</strong> tap water to obtain the desired OLR <strong>and</strong> COD values in the influent.The soluble COD values varied from 100 to 1100 mg·L -1 . The dissolved total nitrogen(DTN) concentration ranged from 20 to 180 mg·L -1 , <strong>and</strong> the total phosphorus concentrationranged from 20 to 110 mg·L -1 .An exchange volume ratio of 50 % <strong>and</strong> a cycle length of 3 hours were fixed asoperating parameters. The two SBR were operated <strong>with</strong> constant <strong>and</strong> similar HRTs <strong>and</strong>SRTs during all the operation. The lengths of the feeding, reaction, settling <strong>and</strong> <strong>with</strong>drawal89

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