2022
DOI: 10.1016/j.seppur.2022.120744
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Submerged hollow-fiber-ultrafiltration for harvesting microalgae used for bioremediation of a secondary wastewater

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Cited by 11 publications
(4 citation statements)
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“…A subsequent evaluation of these resistances R f and R p could provide a better understanding of fouling mechanisms and provide further theoretical support in the industrial optimization of the process. J p may be defined as the material amount that passes through the membrane surface in the time (Kukučka & Kukučka, 2013) (Wang et al ., 2022): JP=QPAm where Q p is the permeate volumetric flowrate; A m is the membrane surface of the membrane, may be calculated differently, depending on what the pressure operation is internal or external: Amin=π*ditalicin*l*Nitalicfibers Amex=π*ditalicex*l*Nitalicfibers where A m‐in is the membrane area for the hollow‐fibre membrane with internal pressure operation, that is IN‐to‐OUT filtration mode; A m‐ex is the membrane area for the hollow‐fibre membrane with external pressure operation, that is OUT‐to‐IN filtration mode; d in and d ex are the internal and external diameters for a fibre; l is the length for a fibre; and N fibers is the number of fibres. Through TMP , hydraulic membrane permeability is defined: LP=QPitalicTMP which may be expressed in the function of the membrane resistances: LP=1μ*Ritalictot J p can also be expressed in function of the permeability: JP=LP*TMP The membrane permeability can vary during the tests; the average J p versus the TMP value has been graphed (Mohammadi et al ., 2005) for three consecutive tests performed at three different TMP values, bypassing a straight line through these points, the origin.…”
Section: Methodsmentioning
confidence: 99%
“…A subsequent evaluation of these resistances R f and R p could provide a better understanding of fouling mechanisms and provide further theoretical support in the industrial optimization of the process. J p may be defined as the material amount that passes through the membrane surface in the time (Kukučka & Kukučka, 2013) (Wang et al ., 2022): JP=QPAm where Q p is the permeate volumetric flowrate; A m is the membrane surface of the membrane, may be calculated differently, depending on what the pressure operation is internal or external: Amin=π*ditalicin*l*Nitalicfibers Amex=π*ditalicex*l*Nitalicfibers where A m‐in is the membrane area for the hollow‐fibre membrane with internal pressure operation, that is IN‐to‐OUT filtration mode; A m‐ex is the membrane area for the hollow‐fibre membrane with external pressure operation, that is OUT‐to‐IN filtration mode; d in and d ex are the internal and external diameters for a fibre; l is the length for a fibre; and N fibers is the number of fibres. Through TMP , hydraulic membrane permeability is defined: LP=QPitalicTMP which may be expressed in the function of the membrane resistances: LP=1μ*Ritalictot J p can also be expressed in function of the permeability: JP=LP*TMP The membrane permeability can vary during the tests; the average J p versus the TMP value has been graphed (Mohammadi et al ., 2005) for three consecutive tests performed at three different TMP values, bypassing a straight line through these points, the origin.…”
Section: Methodsmentioning
confidence: 99%
“…Microalgae are appealing from both an economic and environmental standpoint, as during their cultivation and processing, CO 2 emissions from burning may be captured, and wastewater may be treated [56][57][58]. Due to their low costs and associated environmental advantages, the high-potential method for tertiary treatment in wastewater treatment facilities is microalgae-based systems (WWTPs) (Table 2) [59][60][61][62][63][64][65][66][67][68][69][70].…”
Section: Nutrient Removal and Wastewater Treatmentmentioning
confidence: 99%
“…and Coelastrella sp. have been cultured in a submerged membrane-based filtration device using anaerobic membrane bioreactor-treated secondary effluent as the culturing medium [118]. Based on the different fractions of the microalgal suspension, it was observed that the fouling mechanisms and fouling reversibility of the polyvinylidene fluoride (PVDF) ultrafiltration membrane were strongly dependent on the stages of microalgal growth.…”
Section: Membrane Fouling In Microalgae-wastewater Mediummentioning
confidence: 99%