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- Publisher Website: 10.1016/j.watres.2013.03.020
- Scopus: eid_2-s2.0-84876134850
- PMID: 23541307
- WOS: WOS:000318051900028
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Article: The importance of laboratory water quality for studying initial bacterial adhesion during NF filtration processes
Title | The importance of laboratory water quality for studying initial bacterial adhesion during NF filtration processes |
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Authors | |
Keywords | Cell adhesion |
Issue Date | 2013 |
Citation | Water Research, 2013, v. 47, n. 8, p. 2909-2920 How to Cite? |
Abstract | Biofouling of nanofiltration (NF) and reverse osmosis (RO) membranes for water treatment has been the subject of increased research effort in recent years. A prerequisite for undertaking fundamental experimental investigation on NF and RO processes is a procedure called compaction. This involves an initial phase of clean water permeation at high pressures until a stable permeate flux is reached. However water quality used during the compaction process may vary from one laboratory to another. The aim of this study was to investigate the impact of laboratory water quality during compaction of NF membranes. A second objective was to investigate if the water quality used during compaction influences initial bacterial adhesion. Experiments were undertaken with NF 270 membranes at 15bar for permeate volumes of 0.5L, 2L, and 5L using MilliQ, deionized or tap water. Membrane autopsies were performed at each permeation point for membrane surface characterisation by contact angle measurements, profilometry, and scanning electron microscopy. The biological content of compacted membranes was assessed by direct epi-fluorescence observation following nucleic acid staining. The compacted membranes were also employed as substrata for monitoring the initial adhesion of Ps. fluorescens under dynamic flow conditions for 30min at 5min intervals. Compared to MilliQ water, membrane compaction using deionized and tap water led to decreases in permeate flux, increase in surface hydrophobicity and led to significant build-up of a homogeneous fouling layer composed of both living and dead organisms (>106cellscm-2). Subsequent measurements of bacterial adhesion resulted in cell loadings of 0.2×105, 1.0×105cellscm-2 and 2.6×105cellscm-2 for deionized, tap water and MilliQ water, respectively. These differences in initial cell adhesion rates demonstrate that choice of laboratory water can significantly impact the results of bacterial adhesion on NF membranes. Standardized protocols are therefore needed for the fundamental studies of bacterial adhesion and biofouling formation on NF and RO membrane. This can be implemented by first employing pure water during all membrane compaction procedures and for the modelled feed solutions used in the experiment. © 2013 Elsevier Ltd. |
Persistent Identifier | http://hdl.handle.net/10722/228153 |
ISSN | 2021 Impact Factor: 13.400 2020 SCImago Journal Rankings: 3.099 |
ISI Accession Number ID |
DC Field | Value | Language |
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dc.contributor.author | Semião, A. J C | - |
dc.contributor.author | Habimana, O. | - |
dc.contributor.author | Cao, H. | - |
dc.contributor.author | Heffernan, R. | - |
dc.contributor.author | Safari, A. | - |
dc.contributor.author | Casey, E. | - |
dc.date.accessioned | 2016-08-01T06:45:19Z | - |
dc.date.available | 2016-08-01T06:45:19Z | - |
dc.date.issued | 2013 | - |
dc.identifier.citation | Water Research, 2013, v. 47, n. 8, p. 2909-2920 | - |
dc.identifier.issn | 0043-1354 | - |
dc.identifier.uri | http://hdl.handle.net/10722/228153 | - |
dc.description.abstract | Biofouling of nanofiltration (NF) and reverse osmosis (RO) membranes for water treatment has been the subject of increased research effort in recent years. A prerequisite for undertaking fundamental experimental investigation on NF and RO processes is a procedure called compaction. This involves an initial phase of clean water permeation at high pressures until a stable permeate flux is reached. However water quality used during the compaction process may vary from one laboratory to another. The aim of this study was to investigate the impact of laboratory water quality during compaction of NF membranes. A second objective was to investigate if the water quality used during compaction influences initial bacterial adhesion. Experiments were undertaken with NF 270 membranes at 15bar for permeate volumes of 0.5L, 2L, and 5L using MilliQ, deionized or tap water. Membrane autopsies were performed at each permeation point for membrane surface characterisation by contact angle measurements, profilometry, and scanning electron microscopy. The biological content of compacted membranes was assessed by direct epi-fluorescence observation following nucleic acid staining. The compacted membranes were also employed as substrata for monitoring the initial adhesion of Ps. fluorescens under dynamic flow conditions for 30min at 5min intervals. Compared to MilliQ water, membrane compaction using deionized and tap water led to decreases in permeate flux, increase in surface hydrophobicity and led to significant build-up of a homogeneous fouling layer composed of both living and dead organisms (>106cellscm-2). Subsequent measurements of bacterial adhesion resulted in cell loadings of 0.2×105, 1.0×105cellscm-2 and 2.6×105cellscm-2 for deionized, tap water and MilliQ water, respectively. These differences in initial cell adhesion rates demonstrate that choice of laboratory water can significantly impact the results of bacterial adhesion on NF membranes. Standardized protocols are therefore needed for the fundamental studies of bacterial adhesion and biofouling formation on NF and RO membrane. This can be implemented by first employing pure water during all membrane compaction procedures and for the modelled feed solutions used in the experiment. © 2013 Elsevier Ltd. | - |
dc.language | eng | - |
dc.relation.ispartof | Water Research | - |
dc.subject | Cell adhesion | - |
dc.title | The importance of laboratory water quality for studying initial bacterial adhesion during NF filtration processes | - |
dc.type | Article | - |
dc.description.nature | link_to_subscribed_fulltext | - |
dc.identifier.doi | 10.1016/j.watres.2013.03.020 | - |
dc.identifier.pmid | 23541307 | - |
dc.identifier.scopus | eid_2-s2.0-84876134850 | - |
dc.identifier.volume | 47 | - |
dc.identifier.issue | 8 | - |
dc.identifier.spage | 2909 | - |
dc.identifier.epage | 2920 | - |
dc.identifier.eissn | 1879-2448 | - |
dc.identifier.isi | WOS:000318051900028 | - |
dc.identifier.issnl | 0043-1354 | - |