Solar desalination

History

Solar distillation has been used for thousands of years. Early Greek mariners and Persian alchemists produced both freshwater and medicinal distillates. Solar stills were the first method used on a large scale to convert contaminated water into a potable form.[2]

In 1870 the first US patent was granted for a solar distillation device to Norman Wheeler and Walton Evans.[3] Two years later in Las Salinas, Chile, Swedish engineer Charles Wilson began building a solar distillation plant to supply freshwater to workers at a saltpeter and silver mine. It operated continuously for 40 years and distilled an average of 22.7 m3 of water a day using the effluent from mining operations as its feed water.[4]

Solar desalination in the United States began in the early 1950s when Congress passed the Conversion of Saline Water Act, which led to the establishment of the Office of Saline Water (OSW) in 1955. OSW's main function was to administer funds for desalination research and development projects.[5] One of five demonstration plants was located in Daytona Beach, Florida. Many of the projects were aimed at solving water scarcity issues in remote desert and coastal communities.[4] In the 1960s and 1970s several distillation plants were constructed on the Greek isles with capacities ranging from 2000 to 8500 m3/day.[2] In 1984 a plant was constructed in Abu-Dhabi with a capacity of 120 m3/day that is still in operation.[4] In Italy, an open source design called "the Eliodomestico" by Gabriele Diamanti was developed for personal costing $50.[6]

Of the estimated 22 million m3 daily freshwater produced through desalination worldwide, less than 1% uses solar energy.[2] The prevailing methods of desalination, MSF and RO, are energy-intensive and rely heavily on fossil fuels.[7] Because of inexpensive methods of freshwater delivery and abundant low-cost energy resources, solar distillation has been viewed as cost-prohibitive and impractical.[2] It is estimated that desalination plants powered by conventional fuels consume the equivalent of 203 million tons of fuel a year.[2]

Methods
The status of renewable-powered desalination technologies.[8]

In the direct (distillation) method, a solar collector is coupled with a distilling mechanism.[9] Solar stills of this type are described in survival guides, provided in marine survival kits, and employed in many small desalination and distillation plants. Water production is proportional to the area of the solar surface and solar incidence angle and has an average estimated value of 3–4 litres per square metre (0.074–0.098 US gal/sq ft).[2] Because of this proportionality and the relatively high cost of property and material for construction, distillation tends to favor plants with production capacities less than 200 m3/d (53,000 US gal/d).[2]

Indirect desalination employs a solar collection array, consisting of photovoltaic and/or fluid-based thermal collectors, and a separate conventional desalination plant.[9] Many arrangements have been analyzed, experimentally tested and deployed. Categories include multiple-effect humidification (MEH), multi-stage flash distillation (MSF), multiple-effect distillation (MED), multiple-effect boiling (MEB), humidification–dehumidification (HDH), reverse osmosis (RO), and freeze-effect distillation.[7]

Indirect solar desalination systems using photovoltaic (PV) panels and reverse osmosis (RO) have been in use since 2009. Output by 2013 reached 1,600 litres (420 US gal) per hour per system, and 200 litres (53 US gal) per day per square metre of PV panel.[10][11] Utirik Atoll in the Pacific Ocean has been supplied with fresh water this way since 2010.[12]

Indirect solar desalination by a form of humidification/dehumidification is in use in the seawater greenhouse.

Indirect

Large solar desalination plants typically use indirect methods.[13] Indirect solar desalination processes are categorized into single-phase processes (membrane based) and phase change processes (non-membrane based).[14] Single-phase desalination use photovoltaics to produce electricity that drive pumps.[15] Phase-change (or multi-phase) solar desalination is not membrane-based.[16]

Single-phase desalination processes include reverse osmosis and membrane distillation, where membranes filter water from contaminants.[14][16] As of 2014 reverse osmosis (RO) made up about 52% of indirect methods.[13][17][18] Pumps push salt water through RO modules at high pressure.[14][17] RO systems depend on pressure differences. A pressure of 55–65 bar is required to purify seawater. An average of 5 kWh/m3 of energy is typically required to run a large-scale RO plant.[17] Membrane distillation (MD) utilizes pressure difference from two sides of a microporous hydrophobic membrane.[17][19] Fresh water can be extracted through four MD methods: Direct Contact (DCMD), Air Gap (AGMD), Sweeping Gas (SGMD) and Vacuum (VMD).[17][19] An estimated water cost of $15/m3 and $18/m3 support medium-scale solar-MD plants.[17][20] Energy consumption ranges from 200 to 300 kWh/m3.[21]

Phase-change (or multi-phase) solar desalination[16][18][22] includes multi-stage flash, multi-effect distillation (MED), and thermal vapor compression (VC).[16] It is accomplished by using phase change materials (PCMs) to maximize latent heat storage and high temperatures.[23] MSF phase change temperatures range 80–120 °C, 40–100 °C for VC, and 50–90 °C for the MED method.[16][22] Multi-stage flash (MSF) requires seawater to travel through a series of vacuumed reactors held at successively lower pressures.[18] Heat is added to capture the latent heat of the vapor. As seawater flows through the reactors, steam is collected and is condensed to produce fresh water.[18] In Multi-effect distillation (MED), seawater flows through successively low pressure vessels and reuses latent heat to evaporate seawater for condensation.[18] MED desalination requires less energy than MSF due to higher efficiency in thermodynamic transfer rates.[18][22]

Direct

Direct methods use thermal energy to vaporize the seawater as part of a 2-phase separation. Such methods are relatively simple and require little space so they are normally used on small systems. However, they have a low production rate due to low operating temperature and pressure, so they are appropriate for systems that yield 200 m3/day.[24]

Single-effect

This uses the same process as rainfall. A transparent cover encloses a pan where saline water is placed. The latter traps solar energy, evaporating the seawater. The vapor condenses on the inner face of a sloping transparent cover, leaving behind salts, inorganic and organic components and microbes.

The direct method achieves values of 4-5 L/m2/day and efficiency of 30-40%.[25] Efficiency can be improved to 45% by using a double slope or an additional condenser.[26]

In a wick still, feed water flows slowly through a porous radiation-absorbing pad. This requires less water to be heated and is easier to change the angle towards the sun which saves time and achieves higher temperatures.

A diffusion still is composed of a hot storage tank coupled to a solar collector and the distillation unit. Heating is produced by the thermal diffusion between them.

Increasing the internal temperature using an external energy source can improve productivity.

Multi-stage flash distillation (MSF)
Main article: Multi-stage flash distillation

The multi-stage flash (MSF) method is a widely used technology for desalination, particularly in large-scale seawater desalination plants. It is based on the principle of utilizing the evaporation and condensation process to separate saltwater from freshwater.

In the MSF desalination process, seawater is heated and subjected to a series of flashings or rapid depressurizations in multiple stages. Each stage consists of a series of heat exchangers and flash chambers. The process typically involves the following steps:

  1. Preheating: Seawater is initially preheated to reduce the energy required for subsequent stages. The preheated seawater then enters the first stage of the MSF system.
  2. Flashing: In each stage, the preheated seawater is passed through a flash chamber, where its pressure is rapidly reduced. This sudden drop in pressure causes the water to flash into steam, leaving behind concentrated brine with high salt content.
  3. Condensation: The steam produced in the flash chamber is then condensed on the surfaces of heat exchanger tubes. The condensation occurs as the steam comes into contact with colder seawater or with tubes carrying cool freshwater from previous stages.
  4. Collection and extraction: The condensed freshwater is collected and collected as product water. It is then extracted from the system for storage and distribution, while the remaining brine is removed and disposed of properly.
  5. Reheating and repetition: The brine from each stage is reheated, usually by steam extracted from the turbine that drives the process, and then introduced into the subsequent stage. This process is repeated in subsequent stages, with the number of stages determined by the desired level of freshwater production and the overall efficiency of the system.

The multi-stage flash (MSF) method, known for its high energy efficiency through the utilization of latent heat of vaporization during the flashing process, accounted for approximately 45% of the world's desalination capacity and a dominant 93% of thermal systems as recorded in 2009.[2]

In Margherita di Savoia, Italy a 50–60 m3/day MSF plant uses a salinity gradient solar pond. In El Paso, Texas a similar project produces 19 m3/day. In Kuwait a MSF facility uses parabolic trough collectors to provide solar thermal energy to produce 100 m3 of fresh water a day.[7] And in Northern China an experimental, automatic, unmanned operation uses 80 m2 of vacuum tube solar collectors coupled with a 1 kW wind turbine (to drive several small pumps) to produce 0.8 m3/day.[27]

MSF solar distillation has an output capacity of 6–60 L/m2/day versus the 3-4 L/m2/day standard output of a solar still.[7] MSF experience poor efficiency during start-up or low energy periods. Achieving highest efficiency requires controlled pressure drops across each stage and steady energy input. As a result, solar applications require some form of thermal energy storage to deal with cloud interference, varying solar patterns, nocturnal operation, and seasonal temperature changes. As thermal energy storage capacity increases a more continuous process can be achieved and production rates approach maximum efficiency.[28]

Freezing

Although it has only been used on demonstration projects, this indirect method based on crystallization of the saline water has the advantage of the low energy required. Since the latent heat of fusion of water is 6,01 kJ/mole and the latent heat of vaporization at 100 °C is 40,66 kJ/mole, it should be cheaper in terms of energy cost. Furthermore, the corrosion risk is lower too. There is however a disadvantage related with the difficulties of mechanically moving mixtures of ice and liquid. The process has not been commercialized yet due to cost and difficulties with refrigeration systems.

The most studied way of using this process is the refrigeration freezing. A refrigeration cycle is used to cool the water stream to form ice, and after that those crystals are separated and melted to obtain fresh water. There are some recent examples of this solar powered processes: the unit constructed in Saudi Arabia by Chicago Bridge and Iron Inc. in the late 1980s, which was shut down for its inefficiency.

Nevertheless, there is a recent study for the saline groundwater [29] concluding that a plant capable of producing 1 million gal/day would produce water at a cost of $1.30/1000 gallons. Being this true, it would be a cost-competitive device with the reverse osmosis ones.

Problems with thermal systems

Inherent design problems face thermal solar desalination projects. First, the system's efficiency is governed by competing heat and mass transfer rates during evaporation and condensation.[1]

Second, the heat of condensation is valuable because it takes large amounts of solar energy to evaporate water and generate saturated, vapor-laden hot air. This energy is, by definition, transferred to the condenser's surface during condensation. With most solar stills, this heat is emitted as waste heat.

Solutions

Heat recovery allows the same heat input to be reused, providing several times the water.[1]

One solution is to reduce the pressure within the reservoir. This can be accomplished using a vacuum pump, and significantly decreases the required heat energy. For example, water at a pressure of 0.1 atmospheres boils at 50 °C (122 °F) rather than 100 °C (212 °F).[30]

Solar humidification–dehumidification
Main article: Solar humidification

The solar humidification–dehumidification (HDH) process (also called the multiple-effect humidification–dehumidification process, solar multistage condensation evaporation cycle (SMCEC) or multiple-effect humidification (MEH)[31] mimics the natural water cycle on a shorter time frame by distilling water. Thermal energy produces water vapor that is condensed in a separate chamber. In sophisticated systems, waste heat is minimized by collecting the heat from the condensing water vapor and pre-heating the incoming water source.[32]

Single-phase solar desalination

In indirect, or single phase, solar-powered desalination, two systems are combined: a solar energy collection system (e.g. photovoltaic panels) and a desalination system such as reverse osmosis (RO). The main single-phase processes, generally membrane processes, consist of RO and electrodialysis (ED). Single phase desalination is predominantly accomplished with photovoltaics that produce electricity to drive RO pumps. Over 15,000 desalination plants operate around the world. Nearly 70% use RO, yielding 44% of desalination.[33] Alternative methods that use solar thermal collection to provide mechanical energy to drive RO are in development.

Reverse osmosis

RO is the most common desalination process due to its efficiency compared to thermal desalination systems, despite the need for water pre-treatment.[34] Economic and reliability considerations are the main challenges to improving PV powered RO desalination systems. However, plummeting PV panel costs make solar-powered desalination more feasible.

Solar-powered RO desalination is common in demonstration plants due to the modularity and scalability of both PV and RO systems. An economic analysis[35] that explored an optimisation strategy[36] of PV-powered RO reported favorable results.

PV converts solar radiation into direct-current (DC) electricity, which powers the RO unit. The intermittent nature of sunlight and its variable intensity throughout the day complicates PV efficiency prediction and limits night-time desalination. Batteries can store solar energy for later use. Similarly, thermal energy storage systems ensure constant performance after sunset and on cloudy days.[37]

Batteries allow continuous operation. Studies have indicated that intermittent operations can increase biofouling.[38]

Batteries remain expensive and require ongoing maintenance. Also, storing and retrieving energy from the battery lowers efficiency.[38]

Reported average cost of RO desalination is US$0.56/m3. Using renewable energy, that cost could increase up to US$16/m3.[33] Although renewable energy costs are greater, their use is increasing.

Electrodialysis

Both electrodialysis (ED) and reverse electrodialysis (RED) use selective ion transport through ion exchange membranes (IEMs) due either to the influence of concentration difference (RED) or electrical potential (ED).

In ED, an electrical force is applied to the electrodes; the cations travel toward the cathode and anions travel toward the anode. The exchange membranes only allow the passage of its permeable type (cation or anion), hence with this arrangement, diluted and concentrated salt solutions are placed in the space between the membranes (channels). The configuration of this stack can be either horizontal or vertical. The feed water passes in parallel through all the cells, providing a continuous flow of permeate and brine. Although this is a well-known process electrodialysis is not commercially suited for seawater desalination, because it can be used only for brackish water (TDS < 1000 ppm).[33] Due to the complexity for modeling ion transport phenomena in the channels, performance could be affected, considering the non-ideal behavior presented by the exchange membranes.[39]

The basic ED process could be modified and turned into RED, in which the polarity of the electrodes changes periodically, reversing the flow through the membranes. This limits the deposition of colloidal substances, which makes this a self-cleaning process, almost eliminating the need for chemical pre-treatment, making it economically attractive for brackish water.[40]

The use ED systems began in 1954, while RED was developed in the 1970s. These processes are used in over 1100 plants worldwide. The main advantages of PV in desalination plants is due to its suitability for small-scale plants. One example is in Japan, on Oshima Island (Nagasaki), which has operated since 1986 with 390 PV panels producing 10 m3/day with dissolved solids (TDS) about 400 ppm.[40]

See also

References
  1. J H Lienhard, G P Thiel, D M Warsinger, L D Banchik (2016). "Low Carbon Desalination: Status and Research, Development, and Demonstration Needs". Report of a Workshop Conducted at the Massachusetts Institute of Technology in Association with the Global Clean Water Desalination Alliance, MIT Abdul Latif Jameel World Water and Food Security Lab, Cambridge, Massachusetts.{{cite journal}}: CS1 maint: multiple names: authors list (link)
  2. Kalogirou, S.A. (2013). Solar Energy Engineering: Processes and Systems. Elsevier Science. ISBN 978-0-12-397256-9. Retrieved 2023-10-05.
  3. US patent 102633, Wheeler, N. & Evans, W., "Improvements in Evaporating and Distilling by Solar Heat", published 1870
  4. Delyannis, E. (2003). "Historic background of desalination and renewable energies". Solar Energy. Elsevier BV. 75 (5): 357–366. Bibcode:2003SoEn...75..357D. doi:10.1016/j.solener.2003.08.002. ISSN 0038-092X.
  5. "Records of the office of Saline Water". National Archives. 2016-10-12.
  6. Eric Spooner; Lisa VanBladeren. Solar Distillation in Rajasthan, India (PDF) (Report).
  7. Qiblawey, Hazim Mohameed; Banat, Fawzi (2008). "Solar thermal desalination technologies". Desalination. 220 (1–3): 633–44. doi:10.1016/j.desal.2007.01.059.
  8. Ahmadi, Esmaeil; McLellan, Benjamin; Ogata, Seiichi; Mohammadi-Ivatloo, Behnam; Tezuka, Tetsuo (2020). "An Integrated Planning Framework for Sustainable Water and Energy Supply". Sustainability. 12 (10): 4295. doi:10.3390/su12104295.
  9. García-Rodríguez, Lourdes; Palmero-Marrero, Ana I.; Gómez-Camacho, Carlos (2002). "Comparison of solar thermal technologies for applications in seawater desalination". Desalination. 142 (2): 135–42. doi:10.1016/S0011-9164(01)00432-5.
  10. ""Trunk size solar desalination unit"" (PDF). Archived from the original (PDF) on 2016-03-03. Retrieved 2014-02-27.
  11. ""Container size solar desalination unit"" (PDF).
  12. "Utrik RO unit a big success". marshallislandsjournal.com. January 17, 2014. Archived from the original on 2014-03-03.
  13. Deniz, Emrah (2015-10-28). "Solar-Powered Desalination". Desalination Updates. doi:10.5772/60436. ISBN 978-953-51-2189-3.
  14. Delyannis, E.-E (1987). "Status of solar assisted desalination: A review". Desalination. Elsevier BV. 67: 3–19. doi:10.1016/0011-9164(87)90227-x. ISSN 0011-9164.
  15. Attia, Ahmed A.A. (2012). "Thermal analysis for system uses solar energy as a pressure source for reverse osmosis (RO) water desalination". Solar Energy. Elsevier BV. 86 (9): 2486–2493. Bibcode:2012SoEn...86.2486A. doi:10.1016/j.solener.2012.05.018. ISSN 0038-092X.
  16. Sarwar, J.; Mansoor, B. (2016). "Characterization of thermophysical properties of phase change materials for non-membrane based indirect solar desalination application". Energy Conversion and Management. Elsevier BV. 120: 247–256. doi:10.1016/j.enconman.2016.05.002. ISSN 0196-8904.
  17. Ali, Muhammad Tauha; Fath, Hassan E.S.; Armstrong, Peter R. (2011). "A comprehensive techno-economical review of indirect solar desalination". Renewable and Sustainable Energy Reviews. Elsevier BV. 15 (8): 4187–4199. doi:10.1016/j.rser.2011.05.012. ISSN 1364-0321.
  18. Li, Chennan; Goswami, Yogi; Stefanakos, Elias (2013-03-01). "Solar assisted sea water desalination: A review". Renewable and Sustainable Energy Reviews. 19: 136–163. doi:10.1016/j.rser.2012.04.059. ISSN 1364-0321.
  19. Zaragoza, G.; Andrés-Mañas, J. A; Ruiz-Aguirre, A. (2018-10-30). "Commercial scale membrane distillation for solar desalination". npj Clean Water. 1 (1). doi:10.1038/s41545-018-0020-z. ISSN 2059-7037.
  20. Banat, Fawzi; Jwaied, Nesreen (2008). "Economic evaluation of desalination by small-scale autonomous solar-powered membrane distillation units". Desalination. Elsevier BV. 220 (1–3): 566–573. doi:10.1016/j.desal.2007.01.057. ISSN 0011-9164.
  21. Banat, Fawzi; Jwaied, Nesreen; Rommel, Matthias; Koschikowski, Joachim; Wieghaus, Marcel (2007). "Performance evaluation of the "large SMADES" autonomous desalination solar-driven membrane distillation plant in Aqaba, Jordan". Desalination. Elsevier BV. 217 (1–3): 17–28. doi:10.1016/j.desal.2006.11.027. ISSN 0011-9164.
  22. Alhaj, Mohamed; Mabrouk, Abdelnasser; Al-Ghamdi, Sami G. (2018-09-01). "Energy efficient multi-effect distillation powered by a solar linear Fresnel collector". Energy Conversion and Management. 171: 576–586. doi:10.1016/j.enconman.2018.05.082. ISSN 0196-8904. S2CID 102703212.
  23. Hasan, A.; McCormack, S.J.; Huang, M.J.; Norton, B. (2014). "Characterization of phase change materials for thermal control of photovoltaics using Differential Scanning Calorimetry and Temperature History Method". Energy Conversion and Management. Elsevier BV. 81: 322–329. doi:10.1016/j.enconman.2014.02.042. ISSN 0196-8904.
  24. García-Rodríguez, Lourdes (2002). "Seawater desalination driven by renewable energies: a review". Desalination. Elsevier BV. 143 (2): 103–113. doi:10.1016/s0011-9164(02)00232-1. ISSN 0011-9164.
  25. Mink, György; Aboabboud, Mohamed M.; Karmazsin, Étienne (1998). "Air-blown solar still with heat recycling". Solar Energy. Elsevier BV. 62 (4): 309–317. Bibcode:1998SoEn...62..309M. doi:10.1016/s0038-092x(97)00121-7. ISSN 0038-092X.
  26. Fath, Hassan E.S. (1998). "Solar distillation: a promising alternative for water provision with free energy, simple technology and a clean environment". Desalination. Elsevier BV. 116 (1): 45–56. doi:10.1016/s0011-9164(98)00056-3. ISSN 0011-9164.
  27. Chen, Zhili; Xie, Guo; Chen, Ziqian; Zheng, Hongfei; Zhuang, Chunlong (2012). "Field test of a solar seawater desalination unit with triple-effect falling film regeneration in northern China". Solar Energy. 86 (1): 31–9. Bibcode:2012SoEn...86...31C. doi:10.1016/j.solener.2011.08.037.
  28. Gude, Veera Gnaneswar; Nirmalakhandan, Nagamany; Deng, Shuguang; Maganti, Anand (2012). "Low temperature desalination using solar collectors augmented by thermal energy storage". Applied Energy. 91: 466–74. doi:10.1016/j.apenergy.2011.10.018.
  29. Task 21 - Evaluation of Artificial Freeze Crystallization and Natural Freeze-Thaw Processes for the Treatment of Contaminated Groundwater at the Strachan Gas Plant in Alberta, Canada - Sour Gas Remediation Technology R{ampersand}D (Report). Office of Scientific and Technical Information (OSTI). 1997-03-01. doi:10.2172/637784.
  30. "Large scale Solar Desalination using Multi Effect Humidification". Archived from the original on 2008-12-21. Retrieved 2008-11-05.
  31. The MEH-method (in German with english abstract): Solar Desalination using the MEH method, Diss. Technical University of Munich
  32. Rajvanshi, A. K. (April 30, 1980). "A scheme for large scale desalination of sea water by solar energy". Solar Energy. 24 (6): 551–560. Bibcode:1980SoEn...24..551R. doi:10.1016/0038-092X(80)90354-0. S2CID 17580673 – via Semantic Scholar.
  33. Esmaeilion, Farbod (March 2020). "Hybrid renewable energy systems for desalination". Applied Water Science. 10 (3): 84. Bibcode:2020ApWS...10...84E. doi:10.1007/s13201-020-1168-5. ISSN 2190-5487.
  34. Mohammad Abutayeh; Chennan Li, D; Yogi Goswami; Elias K. Stefanakos (January 2014). Kucera, Jane (ed.). "Solar Desalination". Desalination: 551–582. doi:10.1002/9781118904855.ch13. ISBN 9781118904855. S2CID 243368304.
  35. Fiorenza, G.; Sharma, V.K.; Braccio, G. (August 2003). "Techno-economic evaluation of a solar powered water desalination plant". Energy Conversion and Management. 44 (14): 2217–2240. doi:10.1016/S0196-8904(02)00247-9.
  36. Laborde, H.M.; França, K.B.; Neff, H.; Lima, A.M.N. (February 2001). "Optimization strategy for a small-scale reverse osmosis water desalination system based on solar energy". Desalination. 133 (1): 1–12. doi:10.1016/S0011-9164(01)00078-9.
  37. Gude, Veera Gnaneswar; Nirmalakhandan, Nagamany; Deng, Shuguang; Maganti, Anand (2012). "Low temperature desalination using solar collectors augmented by thermal energy storage" (PDF). Applied Energy. Elsevier BV. 91 (1): 466–474. doi:10.1016/j.apenergy.2011.10.018. ISSN 0306-2619.
  38. Lienhard, John; Antar, Mohamed A.; Bilton, Amy; Blanco, Julian; Zaragoza, Guillermo (2012). "Solar Desalination". Annual Review of Heat Transfer. Begell House. 15 (15): 277–347. doi:10.1615/annualrevheattransfer.2012004659. ISSN 1049-0787. S2CID 7845704.
  39. Tedesco, M.; Hamelers, H.V.M.; Biesheuvel, P.M. (2017). "Nernst-Planck transport theory for (reverse) electrodialysis: II. Effect of water transport through ion-exchange membranes". Journal of Membrane Science. Elsevier BV. 531: 172–182. arXiv:1610.02833. doi:10.1016/j.memsci.2017.02.031. ISSN 0376-7388. S2CID 99780515.
  40. Al-Karaghouli, Ali; Renne, David; Kazmerski, Lawrence L. (2010). "Technical and economic assessment of photovoltaic-driven desalination systems". Renewable Energy. Elsevier BV. 35 (2): 323–328. doi:10.1016/j.renene.2009.05.018. ISSN 0960-1481.
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