Wikipedia

Membrane distillation

Water desalination
Methods

Membrane distillation (MD) is a thermally driven separation process in which separation is driven by phase change. A hydrophobic membrane presents a barrier for the liquid phase, allowing the vapour phase (e.g. water vapour) to pass through the membrane's pores.[1] The driving force of the process is a partial vapour pressure difference commonly triggered by a temperature difference.[2][3]

Principle of membrane distillation

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Capillary depression of water on a hydophobic membrane
 
Temperature and pressure profile through the membrane considering temperature polarisation

Most processes that use a membrane to separate materials rely on static pressure difference as the driving force between the two bounding surfaces (e.g. reverse osmosis - RO), or a difference in concentration (dialysis), or an electric field (ED).[4] The selectivity of a membrane can be due to the relation of the pore size to the size of the substance being retained, or its diffusion coefficient, or its electrical polarity. Membranes used for membrane distillation (MD) inhibit passage of liquid water while allowing permeability for free water molecules and thus, for water vapour.[1] These membranes are made of hydrophobic synthetic material (e.g. PTFE, PVDF or PP) and offer pores with a standard diameter between 0.1 and 0.5 μm (3.9×10−6 and 1.97×10−5 in). As water has strong dipole characteristics, whilst the membrane fabric is non-polar, the membrane material is not wetted by the liquid.[5] Even though the pores are considerably larger than the molecules, the high water surface tension prevents the liquid phase from entering the pores. A convex meniscus develops into the pore.[6] This effect is named capillary action. Amongst other factors, the depth of impression can depend on the external pressure load on the liquid. A dimension for the infiltration of the pores by the liquid is the contact angle Θ=90 – Θ'. As long as Θ < 90° and accordingly Θ' > 0° no wetting of the pores will take place. If the external pressure rises above the so-called liquid entry pressure, then Θ = 90°resulting in a bypass of the pore. The driving force which delivers the vapour through the membrane, in order to collect it on the permeate side as product water, is the partial water vapour pressure difference between the two bounding surfaces. This partial pressure difference is the result of a temperature difference between the two bounding surfaces. As can be seen in the image, the membrane is charged with a hot feed flow on one side and a cooled permeate flow on the other side. The temperature difference through the membrane, usually between 5 and 20 K, conveys a partial pressure difference which ensures that the vapour developing at the membrane surface follows the pressure drop, permeating through the pores and condensing on the cooler side.[7]

Membrane distillation techniques

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Schematic AGMD arrangement

Many different membrane distillation techniques exist. The basic four techniques mainly differ by the arrangement of their distillate channel or the manner in which this channel is operated. The following technologies are most common:

  • Direct Contact MD (DCMD)
  • Air Gap MD (AGMD)
  • Vacuum MD (VMD)
  • Sweeping Gas MD (SWGMD)
  • Vacuum multi-effect membrane distillation (V-MEMD)
  • Permeate Gap MD (PGMD)

Direct-contact MD

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In DCMD, both sides of the membrane are charged with liquid- hot feed water on the evaporator side and cooled permeate on the permeate side. The condensation of the vapour passing through the membrane happens directly inside the liquid phase at the membrane boundary surface. Since the membrane is the only barrier blocking the mass transport, relatively high surface related permeate flows can be achieved with DCMD.[8] A disadvantage is the high sensible heat loss, as the insulating properties of the single membrane layer are low. However, a high heat loss between evaporator and condenser is also the result of the single membrane layer. This lost heat is not available to the distillation process, thus lowering the efficiency.[9] Unlike other configurations of membrane distillation, in DCMD the cooling across the membrane is provided by permeate flow rather than feed preheating. Therefore, an external heat exchanger is also needed to recover heat from the permeate, and the high flow rate of the feed must be carefully optimized.[10]

Air-gap MD

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Droplet condensation regimes seen in AGMD.[11][12]

In air-gap MD, the evaporator channel resembles that in DCMD, whereas the permeate gap lies between the membrane and a cooled walling and is filled with air. The vapour passing through the membrane must additionally overcome this air gap before condensing on the cooler surface. The advantage of this method is the high thermal insulation towards the condenser channel, thus minimizing heat conduction losses. However, the disadvantage is that the air gap represents an additional barrier for mass transport, reducing the surface- related permeate output compared to DCMD.[13] A further advantage over DCMD is that volatile substances with a low surface tension such as alcohol or other solvents can be separated from diluted solutions, due to the fact that there is no contact between the liquid permeate and the membrane with AGMD. AGMD is especially advantageous compared to alternatives at higher salinity.[14] Variations on AGMD can include hydrophobic condensing surfaces[15] or porous condensers[16] for improved flux and energy efficiency. In AGMD, uniquely important design features include gap thickness, condensing surface hydrophobicity, gap spacer design, and tilt angle.[17]

Sweeping-gas MD

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Sweeping-gas MD, also known as air stripping, uses a channel configuration with an empty gap on the permeate side. This configuration is the same as in AGMD. Condensation of the vapour takes place outside the MD module in an external condenser. As with AGMD, volatile substances with a low surface tension can be distilled with this process.[18] The advantage of SWGMD over AGMD is the significant reduction of the barrier to the mass transport through forced flow. Hereby higher surface-related productwater mass flows can be achieved than with AGMD. A disadvantage of SWGMD caused by the gas component and therefore the higher total mass flow, is the necessity of a higher condenser capacity. When using smaller gas mass flows there is a risk of the gas heating itself at the hot membrane surface, thus reducing the vapour pressure difference and therefore the driving force. One solution of this problem for SWGMD and for AGMD is the use of a cooled walling for the permeate channel, and maintaining temperature by flushing it with gas.[19]

Vacuum MD

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Vacuum MD contains an air gap channel configuration. Once it has passed through the membrane, the vapour is sucked out of the permeate channel and condenses outside the module as with SWGMD. VCMD and SWGMD can be applied for the separation of volatile substances from a watery solution or for the generation of pure water from concentrated salt water. One advantage of this method is that undissolved inert gasses blocking the membrane pores are sucked out by the vacuum, leaving a larger effective membrane surface active.[20] Furthermore, a reduction of the boiling point results in a comparable amount of product at lower overall temperatures and lower temperature differences through the membrane. A lower required temperature difference leaves a lower total- and specific thermal energy demand. However, the generation of a vacuum, which must be adjusted to the salt water temperature, requires complex technical equipment and is therefore a disadvantage to this method. The electrical energy demand is a lot higher as with DCMD and AGMD. An additional problem is the increase of the pH value due to the removal of CO2 from the feed water. For vacuum membrane distillation to be efficient, it is often run in multistage configurations.[21]

Permeate-gap MD

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In the following, the principle channel configuration and operating method of a standard DCMD module as well as a DCMD module with separate permeate gap shall be explained. The design in the adjacent image depicts a flat channel configuration, but can also be understood as a schema for flat-, hollow fibre - or spiral wound modules.

The complete channel configuration consists of a condenser channel with inlet and outlet and an evaporator channel with inlet and outlet. These two channels are separated by the hydrophobic, micro porous membrane. For cooling, the condenser channel is flooded with fresh water and the evaporator e.g. with salty feed water. The coolant enters the condenser channel at a temperature of 20 °C (68 °F). After passing through the membrane, the vapour condenses in the cooling water, releasing its latent heat and leading to a temperature increase in the coolant. Sensible heat conduction also heats the cooling water through the surface of the membrane. Due to the mass transport through the membrane the mass flow in the evaporator decreases whilst the condenser channel increases by the same amount. The mass flow of pre-heated coolant leaves the condenser channel at a temperature of about 72 °C (162 °F) and enters a heat exchanger, thus pre-heating the feed water. This feed water is then delivered to a further heat source and finally enters the evaporator channel of the MD module at a temperature of 80 °C (176 °F). The evaporation process extracts latent heat from the feed flow, which cools down the feed increasingly in flow direction. Additional heat reduction occurs due to sensible heat passing through the membrane. The cooled feed water leaves the evaporator channel at approximately 28 °C. Total temperature differences between condenser inlet and evaporator outlet and condenser inlet and evaporator outlet are about equal. In a PGMD module, the permeate channel is separated from the condenser channel by a condensation surface. This enables the direct use of a salt water feed as coolant, since it does not come into contact with the permeate. Considering this, the cooling-or feed water entering the condenser channel at a temperature T1 can now also be used to cool the permeate. Condensation of vapour takes place inside the liquid permeate. Pre-heated feed water that was used to cool the condenser can be conducted directly to a heat source for final heating, after leaving the condenser at a temperature T2. After it has reached temperature T3 it is guided into the evaporator. Permeate is extracted at temperature T5 and the cooled brine is discharged at temperature T4.

An advantage of PGMD over DCMD is the direct use of feed water as cooling liquid inside the module and therefore the necessity of only one heat exchanger to heat the feed before entering the evaporator. Hereby heat conduction losses are reduced and expensive components can be cut. A further advantage is the separation of permeate from coolant. Therefore, the permeate does not have to be extracted later in the process and the coolant's mass flow in the condenser channel remains constant. The low flow velocity of the permeate in the permeate gap is a disadvantage of this configuration, as it leads to a poor heat conduction from the membrane surface to the condenser walling. High temperatures on the permeate side's membrane bounding surface are the result of this effect (temperature polarisation), which lowers the vapour pressure difference and therefore the driving force of the process. However, it is beneficial, that the heat conduction losses through the membrane are also lowered by this effect. This poor gap heat conduction challenge is largely removed with a variant of PGMD called CGMD, or conductive gap membrane distillation, which adds thermally conductive spacers to the gaps.[22][23] Compared to AGMD, in PGMD or CGMD, a higher surface related permeate output is achieved, as the mass flow is not additionally inhibited by the diffusion resistance of an air layer.[7]

Vacuum multi-effect membrane distillation

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The hydrophobic membranes (or PP foils) are welded at both sides of the memsys frame. This frame are designed to combine and distribute vapor, feed, non condensable gas and distillate flows.
 
Different numbers of memsys frame are vibration welded as memsys module (e.g. steam raiser, membrane stage and condenser). GOR and capacity of memsys module can be easily modified deponding on the application or customer's needs.
 
Diagram of memsys V-MEMD process

The typical vacuum multi-effect membrane distillation (e.g. the memsys brand[clarification needed] V-MEMD) module consists of a steam raiser, evaporation–condensation stages, and a condenser. Each stage recovers the heat of condensation, providing a multiple-effect design. Distillate is produced in each evaporation–condensation stage and in the condenser.[24]

Steam raiser: The heat produced by the external heat source (e.g. solar thermal or waste heat) is exchanged in the steam raiser. The water in the steam raiser is at lower pressure (e.g. 400 hPa), compared to the ambient. The hot steam flows to the first evaporation–condensation stage (stage 1).

Evaporation–condensation stages: Stages are composed of alternative hydrophobic membrane and foil (Polypropylene, PP) frames. Feed (e.g. seawater) is introduced into stage 1 of the module. Feed flows serially through the evaporation–condensation stages. At the end of last stage, it is ejected as brine.

Stage 1: Steam from the evaporator condenses on a PP foil at pressure level P1 and corresponding temperature T1. The combination of a foil and a hydrophobic membrane creates a channel for the feed, where the feed is heated by the heat of condensation of the vapour from the steam raiser. Feed evaporates under the negative pressure P2. The vacuum is always applied to the permeate side of the membranes.

Stage [2, 3, 4, x]: This process is replicated in further stages and each stage is at a lower pressure and temperature.

Condenser: The vapour produced in the final evaporation–condensation stage is condensed in the condenser, using the coolant flow (e.g. seawater).

Distillate production: Condensed distillate is transported via the bottom of each stage by pressure difference between stages.

Design of memsys module: Inside each memsys frame, and between frames, channels are created. Foil frames are the ‘distillate channels’. Membrane frames are the ‘vapour channels’. Between foil and membrane frames, ‘feed channels’ are created. Vapour enters the stage and flows into parallel foil frames. The only option of for the vapour entering the foil frames is to condense, i.e. vapour enters a ‘dead-end’ foil frame. Although it is called a ‘dead-end’ frame, it does contain a small channel to remove the non-condensable gases and to apply the vacuum.

The condensed vapour flows into a distillate channel. The heat of condensation is transported through the foil and is immediately converted into evaporation energy, generating new vapour in the seawater feed channel. The feed channel is limited by one condensing foil and a membrane. The vapour leaves the membrane channels and is collected in a main vapour channel. The vapour leaves the stage via this channel and enters the next stage. Memsys has developed a highly automated production line for the modules and could be easily extended.[clarification needed] As the memsys process works at modest low temperatures (less than 90 °C or 194 °F) and moderate negative pressure, all module components are made of polypropylene (PP). This eliminates corrosion and scaling and allows large-scale cost efficient production.

Applications

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Typical applications of membrane distillation are:

Solar-powered membrane distillation

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Plant design of a compact system
 
Plant design of a two loop system

Membrane distillation is very suitable for compact, solar powered desalination units providing small and medium range output less than 10,000 litres per day (2,600 US gal/d).[25] Especially the spiral wound design patented by GORE in the year 1985 suits this application. Within the MEMDIS project, which kicked off in 2003, the Fraunhofer Institute for Solar Energy Systems ISE began developing MD modules as well as installing and analysing two different solar powered operating systems, together with other project partners. The first system type is a so-called compact system, designed to produce a drinking water output of 100–120 litres per day (26–32 US gal/d) from sea-or brackish water. The main aim of the system design is a simple, self-sufficient, low maintenance and robust plant for target markets in arid and semi-arid areas of low infrastructure. The second system type is a so-called two-loop plant with a capacity of around 2,000 litres per day (530 US gal/d). Here, the collector circuit is separated from the desalination circuit by a saltwater resistant heat exchanger.[7] Based on these two system types, a various number of prototypes were developed, installed and observed.

The standard configuration of today's (2011) compact system is able to produce a distillate output of up to 150 litres per day (40 US gal/d). The required thermal energy is supplied by a 6.5 m2 (70 sq ft) solar thermal collector field. Electrical energy is supplied by a 75 W PV-module. This system type is currently being developed further and marketed by the Solar Spring GmbH, a spin-off of the Fraunhofer Institute for Solar Energy Systems. Within the MEDIRAS project, a further EU-project, an enhanced two-loop system was installed on the Island of Gran Canaria. Built inside a 6.1 m (20 ft) container and equipped with a collector aray size of 225 m2 (2,420 sq ft), a heat storage tank makes a distillate output of up to 3,000 litres per day (790 US gal/d) possible. Further applications with up to 5,000 litres per day (1,300 US gal/d) have also been implemented, either 100% solar powered or as hybrid projects in combination with waste heat.[citation needed]

Exemplary systems

Challenges

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The operation of membrane distillation systems faces several major barriers that may impair operation, or prevent it from being a viable option. The principal challenge is membrane wetting, where saline feed leaks through the membrane, contaminating the permeate.[1] This is especially caused by membrane fouling, where particulates, salts, or organic matter deposit on the membrane surface.[26] Techniques to mitigate fouling include membrane superhydrophobicity,[27][28] air backwashing to reverse[1] or prevent wetting,[29] choosing non-fouling operating conditions,[30] and maintaining air layers on the membrane surface.[29]

The single biggest challenge for membrane distillation to be cost effective is the energy efficiency. Commercial systems have not reached competitive energy consumption compared to the leading thermal technologies such as Multiple-effect distillation, although some have been close,[31] and research has shown potential for significant improvements on energy efficiency.[22]

References

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  1. ^ a b c d Warsinger, David M.; Servi, Amelia; Connors, Grace B.; Lienhard V, John H. (2017). "Reversing membrane wetting in membrane distillation: comparing dryout to backwashing with pressurized air". Environmental Science: Water Research & Technology. 3 (5): 930–939. doi:10.1039/C7EW00085E. hdl:1721.1/118392.
  2. ^ Deshmukh, Akshay; Boo, Chanhee; Karanikola, Vasiliki; Lin, Shihong; Straub, Anthony P.; Tong, Tiezheng; Warsinger, David M.; Elimelech, Menachem (2018). "Membrane distillation at the water-energy nexus: limits, opportunities, and challenges". Energy & Environmental Science. 11 (5): 1177–1196. doi:10.1039/c8ee00291f. ISSN 1754-5692.
  3. ^ Panagopoulos, Argyris; Haralambous, Katherine-Joanne; Loizidou, Maria (2019-11-25). "Desalination brine disposal methods and treatment technologies - A review". Science of the Total Environment. 693: 133545. Bibcode:2019ScTEn.693m3545P. doi:10.1016/j.scitotenv.2019.07.351. ISSN 0048-9697. PMID 31374511. S2CID 199387639.
  4. ^ Lawson, Kevin W.; Lloyd, Douglas R. (1997-02-05). "Membrane distillation". Journal of Membrane Science. 124 (1): 1–25. doi:10.1016/S0376-7388(96)00236-0.
  5. ^ Rezaei, Mohammad; Warsinger, David M.; Lienhard V, John H.; Duke, Mikel C.; Matsuura, Takeshi; Samhaber, Wolfgang M. (August 2018). "Wetting phenomena in membrane distillation: Mechanisms, reversal, and prevention". Water Research. 139: 329–352. doi:10.1016/j.watres.2018.03.058. hdl:1721.1/115486. ISSN 0043-1354. PMID 29660622. S2CID 4902941.
  6. ^ Lee, Jongho; Karnik, Rohit (2010-08-15). "Desalination of water by vapor-phase transport through hydrophobic nanopores". Journal of Applied Physics. 108 (4): 044315. Bibcode:2010JAP...108d4315L. doi:10.1063/1.3419751. hdl:1721.1/78853. ISSN 0021-8979.
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  11. ^ Warsinger, David M.; Swaminathan, Jaichander; Morales, Lucien L.; Lienhard V, John H. (2018). "Comprehensive condensation flow regimes in air gap membrane distillation: Visualization and energy efficiency". Journal of Membrane Science. 555. Elsevier BV: 517–528. doi:10.1016/j.memsci.2018.03.053. hdl:1721.1/115268. ISSN 0376-7388. S2CID 103774569.
  12. ^ Warsinger, David M (2017-11-20). "Thermodynamic Design and Fouling of Membrane Distillation Systems". arXiv.org. Retrieved 2024-12-24.
  13. ^ Warsinger, David; Swaminathan, Jaichander; Lienhard, John H. (2014). "Effect of Module Inclination Angle on Air Gap Membrane Distillation". Proceedings of the 15th International Heat Transfer Conference. doi:10.1615/ihtc15.mtr.009351. hdl:1721.1/100241. ISBN 978-1-56700-421-2. Paper No. IHTC15-9351.
  14. ^ Swaminathan, Jaichander; Chung, Hyung Won; Warsinger, David M.; Lienhard V, John H. (2018). "Energy efficiency of membrane distillation up to high salinity: Evaluating critical system size and optimal membrane thickness". Applied Energy. 211: 715–734. doi:10.1016/j.apenergy.2017.11.043. hdl:1721.1/113008. ISSN 0306-2619. S2CID 73650179.
  15. ^ Warsinger, David E.M.; Swaminathan, Jaichander; Maswadeh, Laith A.; Lienhard V, John H. (2015). "Superhydrophobic condenser surfaces for air gap membrane distillation". Journal of Membrane Science. 492: 578–587. doi:10.1016/j.memsci.2015.05.067. hdl:1721.1/102500. ISSN 0376-7388.
  16. ^ Fattahi Juybari, Hamid; Parmar, Harsharaj B.; Alshubbar, Ali D.; Young, Katherine L.; Warsinger, David M. (2023). "Porous condensers can double the efficiency of membrane distillation". Desalination. 545. Elsevier BV: 116129. doi:10.1016/j.desal.2022.116129. ISSN 0011-9164. S2CID 253087478.
  17. ^ Warsinger, David M.; Swaminathan, Jaichander; Morales, Lucien L.; Lienhard V, John H. (2018). "Comprehensive condensation flow regimes in air gap membrane distillation: Visualization and energy efficiency". Journal of Membrane Science. 555: 517–528. doi:10.1016/j.memsci.2018.03.053. hdl:1721.1/115268. ISSN 0376-7388. S2CID 103774569.
  18. ^ Karanikola, Vasiliki; Corral, Andrea F.; Jiang, Hua; Eduardo Sáez, A.; Ela, Wendell P.; Arnold, Robert G. (2015). "Sweeping gas membrane distillation: Numerical simulation of mass and heat transfer in a hollow fiber membrane module". Journal of Membrane Science. 483: 15–24. doi:10.1016/j.memsci.2015.02.010. ISSN 0376-7388.
  19. ^ Khayet, M.; Cojocaru, C.; Baroudi, A. (2012). "Modeling and optimization of sweeping gas membrane distillation". Desalination. 287: 159–166. doi:10.1016/j.desal.2011.04.070. ISSN 0011-9164.
  20. ^ Bandini, S.; Gostoli, C.; Sarti, G.C. (1992). "Separation efficiency in vacuum membrane distillation". Journal of Membrane Science. 73 (2–3): 217–229. doi:10.1016/0376-7388(92)80131-3. ISSN 0376-7388.
  21. ^ Chung, Hyung Won; Swaminathan, Jaichander; Warsinger, David M.; Lienhard V, John H. (2016). "Multistage vacuum membrane distillation (MSVMD) systems for high salinity applications". Journal of Membrane Science. 497: 128–141. doi:10.1016/j.memsci.2015.09.009. hdl:1721.1/105371. ISSN 0376-7388. S2CID 4200568.
  22. ^ a b Swaminathan, Jaichander; Chung, Hyung Won; Warsinger, David M.; Lienhard V, John H. (2016). "Energy efficiency of permeate gap and novel conductive gap membrane distillation". Journal of Membrane Science. 502: 171–178. doi:10.1016/j.memsci.2015.12.017. hdl:1721.1/105372. S2CID 4282677.
  23. ^ "Energy-efficient conductive-gap membrane distillation". Google Patents. 2015-09-15. Retrieved 2024-12-24. USA issued US9956528B2, Jaichander Swaminathan; David Warsinger & Hyung Won Chung et al., "Energy-efficient conductive-gap membrane distillation", published 2018-05-01 
  24. ^ Kharraz, Jehad; Farid, Muhammad Usman; An, Alicia Kyoungjin; von Eiff, David; Gao, Yonggang; Shi, Zhiwei (2020). HYBRID CONFIGURATION OF MEMBRANE DISTILLATION : VACUUM MULTI-EFFECT MEMBRANE DISTILLATION in Young Moo Lee, Enrico Drioli (Ed.) Membrane Distillation: Materials and Processes (1st ed.). Nova Science Publishers, Inc. pp. 213–236. ISBN 978-1-53617-448-9.
  25. ^ Zaragoza, G.; Ruiz-Aguirre, A.; Guillén-Burrieza, E. (2014). "Efficiency in the use of solar thermal energy of small membrane desalination systems for decentralized water production". Applied Energy. 130: 491–499. doi:10.1016/j.apenergy.2014.02.024. ISSN 0306-2619.
  26. ^ Rezaei, Mohammad; Alsaati, Albraa; Warsinger, David M.; Hell, Florian; Samhaber, Wolfgang M. (August 2020). "Long-Running Comparison of Feed-Water Scaling in Membrane Distillation". Membranes. 10 (8): 173. doi:10.3390/membranes10080173. PMC 7463528. PMID 32751820.
  27. ^ Rezaei, Mohammad (2016). "Wetting Behaviour of Superhydrophobic Membranes Coated with Nanoparticles in Membrane Distillation". Chemical Engineering Transactions. 47: 373–378. doi:10.3303/cet1647063.
  28. ^ Warsinger, David M.; Servi, Amelia; Van Belleghem, Sarah; Gonzalez, Jocelyn; Swaminathan, Jaichander; Kharraz, Jehad; Chung, Hyung Won; Arafat, Hassan A.; Gleason, Karen K.; Lienhard V, John H. (2016). "Combining air recharging and membrane superhydrophobicity for fouling prevention in membrane distillation" (PDF). Journal of Membrane Science. 505: 241–252. doi:10.1016/j.memsci.2016.01.018. hdl:1721.1/105438. ISSN 0376-7388. S2CID 4672323.
  29. ^ a b Rezaei, Mohammad; Warsinger, David M.; Lienhard V, John H.; Samhaber, Wolfgang M. (2017). "Wetting prevention in membrane distillation through superhydrophobicity and recharging an air layer on the membrane surface". Journal of Membrane Science. 530: 42–52. doi:10.1016/j.memsci.2017.02.013. hdl:1721.1/111972. ISSN 0376-7388. S2CID 54029099.
  30. ^ Warsinger, David M.; Tow, Emily W.; Swaminathan, Jaichander; Lienhard V, John H. (2017). "Theoretical framework for predicting inorganic fouling in membrane distillation and experimental validation with calcium sulfate". Journal of Membrane Science. 528: 381–390. doi:10.1016/j.memsci.2017.01.031. hdl:1721.1/107916.
  31. ^ Tarnacki, K.; Meneses, M.; Melin, T.; van Medevoort, J.; Jansen, A. (2012). "Environmental assessment of desalination processes: Reverse osmosis and Memstill®". Desalination. 296: 69–80. doi:10.1016/j.desal.2012.04.009. ISSN 0011-9164.

Literature

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