2018
DOI: 10.1038/s41545-018-0021-y
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Membrane-based technologies for post-treatment of anaerobic effluents

Abstract: Anaerobic digestion-based processes for converting wastewater into clean water and energy are attracting ever-growing industrial interest. However, apart from the microbial digestion step, current technologies require further progress from an integrated process point of view, including post-treatment steps. Anaerobic effluents normally undergo extensive post-treatment steps to meet stringent discharge standards, while valuable nutrients are rarely recovered. Additionally, a significant portion of the produced … Show more

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Cited by 38 publications
(25 citation statements)
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“…According to the literature (Hansen et al, 2007;Pelendridou et al, 2014;Rongwong et al, 2018;Yoo, 2018), the cost of typical treatment technologies such as a coagulation-flocculation process for wastewater treatment, is in the range from 0.35-8.5 EUR/m 3 ; for membrane-based technologies -from 2 EUR/m 3 ; for conventional biological treatmentfrom 0.035 to 1 EUR/m 3 while the fungal treatment growth and operation costs may vary from 200 to 2000 EUR/m 3 . The fungal treatment costs highly depend on fungal growth requirements (temperature, incubation time, electricity of shaking, composition of media).…”
Section: Cost Evaluation Of Fungal Treatmentmentioning
confidence: 99%
“…According to the literature (Hansen et al, 2007;Pelendridou et al, 2014;Rongwong et al, 2018;Yoo, 2018), the cost of typical treatment technologies such as a coagulation-flocculation process for wastewater treatment, is in the range from 0.35-8.5 EUR/m 3 ; for membrane-based technologies -from 2 EUR/m 3 ; for conventional biological treatmentfrom 0.035 to 1 EUR/m 3 while the fungal treatment growth and operation costs may vary from 200 to 2000 EUR/m 3 . The fungal treatment costs highly depend on fungal growth requirements (temperature, incubation time, electricity of shaking, composition of media).…”
Section: Cost Evaluation Of Fungal Treatmentmentioning
confidence: 99%
“…However, in D-CH 4 recovery, the residual pollutants such as suspended solids and organics in the feed solution should also be considered together during the selection of the flow configuration. For example, Cookney et al, Henares et al, and Rongwong et al supplied the liquid to the shell side for the high organic content anaerobic effluents such as UASB and vice versa for low organic-containing effluents such as AnMBR [13,[37][38][39]. Even though the lumen side operational mode offers the better CH 4 recovery efficiency, a higher risk of membrane clogging limits such operation mode.…”
Section: Influensive Parameters Of Hollow Fiber Mcs For D-ch 4 Recoverymentioning
confidence: 99%
“…More importantly, although membrane wetting and fouling seem to be two separate issues that can be possibly dealt with one by one, those two are mostly related to each other. For example, highly hydrophobic membranes that are capable of preventing pore wetting are generally vulnerable to membrane fouling [13]. Thus, many researchers have studied to mitigate or eliminate such problems to increase the overall productivity in MCs for the biomethane recovery.…”
Section: Technical Challenges and Recent Efforts To Address Themmentioning
confidence: 99%
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