Barriers To Thermal Desalination In The United States

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Desalination and Water Purification Researchand Development Program Report No. 144Barriers to Thermal Desalinationin the United StatesU.S. Department of the InteriorBureau of ReclamationMarch 2008

REPORT DOCUMENTATION PAGEForm ApprovedOMB No. 0704-0188Public reporting burden for this collection of information is estimated to average 1 hour per response, including the time for reviewing instructions, searching existing data sources, gathering and maintainingthe data needed, and completing and reviewing this collection of information. Send comments regarding this burden estimate or any other aspect of this collection of information, including suggestions forreducing this burden to Department of Defense, Washington Headquarters Services, Directorate for Information Operations and Reports (0704-0188), 1215 Jefferson Davis Highway, Suite 1204, Arlington, VA22202-4302. Respondents should be aware that notwithstanding any other provision of law, no person shall be subject to any penalty for failing to comply with a collection of information if it does not display acurrently valid OMB control number. PLEASE DO NOT RETURN YOUR FORM TO THE ABOVE ADDRESS.1. REPORT DATE (DD-MM-YYYY)T2. REPORT TYPETTMarch 20083. DATES COVERED (From - To)TTTFinalOctober 2005 – December 20074. TITLE AND SUBTITLE5a. CONTRACT NUMBERTBarriers to Thermal Desalination in the United StatesAgreement No. 04-FC-81-11545b. GRANT NUMBER5c. PROGRAM ELEMENT NUMBER6. AUTHOR(S)5d. PROJECT NUMBERJohn Tonner5e. TASK NUMBERTask B5f. WORK UNIT NUMBER7. PERFORMING ORGANIZATION NAME(S) AND ADDRESS(ES)8. PERFORMING ORGANIZATION REPORTNUMBERWater Consultants International10201 N. Concord DriveMequon, Wisconsin 530979. SPONSORING / MONITORING AGENCY NAME(S) AND ADDRESS(ES)10. SPONSOR/MONITOR’S ACRONYM(S)U.S. Department of the InteriorBureau of ReclamationDenver Federal CenterPO Box 25007, Denver CO 80225-000711. SPONSOR/MONITOR’S REPORTNUMBER(S)DWPR Report No. 14412. DISTRIBUTION / AVAILABILITY STATEMENTAvailable from the National Technical Information ServiceOperations Division, 5285 Port Royal Road, Springfield VA 2216113. SUPPLEMENTARY NOTESTReport can be downloaded from Reclamation Web html14. ABSTRACT (Maximum 200 words)This report quantifies where thermal desalination processes should be competitive, citing examples and documentingregulations and practices that are impeding the implementation of thermal desalination in the United States. This wasaccomplished through the following series of steps: Investigating our domestic power market regulations and practices (both State and national) Summarizing the Federal Energy Regulatory Commission’s (FERC) cogeneration policies Profiling existing industrial and dual-purpose power/water cogeneration projects Discussing carbon footprint and prime energy consumption of various desalination processes Outlining target criteria for future cogeneration applications Discussing exergistic analyses of single-purpose and dual-purpose desalination plantsNote: Exergistic analysis involves a detailed review of all energy consumed in a process and all products or services theprocess provides. This is in contrast to simpler methods which focus on conversion of fuel into a single product (e.g.,electricity) and does not consider that additional products can be cogenerated from the same primary source and quantityof energy.15. SUBJECT TERMSBrackish Water Treatment, Carbon Footprint, Cogeneration, Desalting, Distiller, Evaporator, Exergy, HybridDesalination, Multi-Stage Flash Distillation, Multi-Effect Distillation, Reverse Osmosis, Seawater Treatment, ThermalDesalination, Thermal Energy, Vapor Compression, Waste Heat16. SECURITY CLASSIFICATION OF:17. LIMITATIONOF ABSTRACTULa. REPORTULb. ABSTRACTULc. THIS PAGEULSAR18. NUMBER 19a. NAME OF RESPONSIBLE PERSONOF PAGESHarry RemmersT5319b. TELEPHONE NUMBER (include area code)303-445-2261S Standard Form 298 (Rev. 8/98)P Prescribed by ANSI Std. 239-18

Desalination and Water Purification Researchand Development Program Report No. 144Barriers to Thermal Desalinationin the United StatesPrepared for Reclamation Under Agreement No. 04-FC-81-1154byJohn TonnerWater Consultants InternationalMequon, WisconsinU.S. Department of the InteriorBureau of ReclamationTechnical Service CenterWater and Environmental Services DivisionWater Treatment Engineering Research TeamDenver, ColoradoMarch 2008

MISSION STATEMENTSThe mission of the Department of the Interior is to protect and provideaccess to our Nation’s natural and cultural heritage and honor our trustresponsibilities to Indian tribes and our commitments to islandcommunities.The mission of the Bureau of Reclamation is to manage, develop, andprotect water and related resources in an environmentally andeconomically sound manner in the interest of the American public.DisclaimerThe views, analysis, recommendations, and conclusions in this report are those ofthe authors and do not represent official or unofficial policies or opinions of theUnited States Government, and the United States takes no position with regard toany findings, conclusions, or recommendations made. As such, mention of tradenames or commercial products does not constitute their endorsement by theUnited States Government.

AcknowledgementsWater Consultants International wishes to thank the Bureau of Reclamation andits Desalination and Water Purification Research (DWPR) Program forsponsoring this project as well as the following individuals for their guidance andassistance throughout the project:Frank Leitz – Program Manager, DWPR ProgramHarry Remmers – Grant and Cooperative Agreement Officer’s TechnicalRepresentativeiii

KGRAkWhe/m3kWhth/m3lb of H20m3/dMEDMGD or mgdMIGDMSFMVCMWOPEXPG&EAbu Dhabi Water and Electricity AuthorityAtlantic MethanolAfvalverwerking (Dutch for “Treatment of Waste”)build/own/operateBritish thermal units per poundcapital costsChicago Climate Exchangeclean development mechanismCode of Federal edesign/build/own/operate/transferDesalination and Water Purification ResearchFederal Energy Regulatory CommissionGulf Cooperation Council (Bahrain, Kuwait, Oman, Qatar,Saudi Arabia and the United Arab Emirates)gained output ratiogallons per daygallons per minuteGulf Total Tractebel Power Companyheat recovery steam generatorindependent systems operatorsindependent water producerindependent water and power producerkilograms of waterknown geothermal resource areakilowatthours (electric) per cubic meterkilowatthours (thermal) per cubic meterpounds of watercubic meters per daymultiple effect distillationmillion gallons per daymillion Imperial gallons per daymultistage flashmechanical vapor compressionmegawattsoperating costsPacific Gas and Electricv

Glossary Ot/hTDATDSTVCUNFCCwater stressWEBWEDWPAviPennsylvania, Jersey, Maryland Power Pool, an RTO whichhas expanded to other States since it was createdPerformance Ratiopounds per square inch gaugeterepthalic acidPublic Utility Regulatory Policy Act of 1978photovoltaicPower and Water Purchase Agreementqualifying facilityreverse osmosisRegulatory Services Bureau (UAE)regional transmission organizationsspecial purpose companyseawater reverse osmosistons per hourU.S. Trade and Development Agencytotal dissolved solidsthermal vapor compressionUnited Nations Framework Convention on Climate ChangeWater stress occurs when the demand for water exceeds theamount available during a certain period or when poorquality restricts its use (UNEP definition).Water en Energieberifj, ArubaWater and Electricity Authority, Abu DhabiWater Purchase Agreement

Table of ContentsPageGlossary .1Executive Summary .2Relevant Definitions .3Discussion of Findings.3.1 Minimum Energy of Separation.3.2 Cogeneration .3.3 Maximum Thermal Efficiency Not Always Justified.3.4 Waste Heat .3.5 Cogeneration in Practice .3.6 U.S. Power and Cogeneration.3.7 Public-Owned Treatment Works or Long-TermPurchase of Water? .3.8 Heat Rate, Exergy, and Cogeneration Policy.3.9 Carbon Footprint and Potential Use of RenewableEnergy Sources .3.10 Potential Application Guidance and Recommendations.v12667111415172427Appendix A—Al Taweelah Desalination Facility (UAE) .Appendix B—Shuweihat Desalination Plant (UAE).31392123List of TablesTable1 Power-to-Water Ratio (MSF) .2 Power-to-Water Ratio (MED).1011List of FiguresFigure12345678910Distillation Energy Consumption .Block Diagrams for Generic Desalination of Seawater .Block Diagram for Waste Heat Thermal Desalination .Power Generation Utilizing Steam Turbine.Power Generation Utilizing Combined Cycle .Distiller GOR Versus Capital Expenditures (CAPEX)and Operating Expenditures (OPEX).AVR Rotterdam Waste Incinerator .Fujairah, UAE Hybrid Cogeneration .Exergy Cost Allocations .Generic Diagram for Solar (or Geothermal) Powerand Water Production .581010101316162425vii

1. Executive SummaryThe Bureau of Reclamation (Reclamation) awarded a project to WaterConsultants International to study “Barriers to Thermal Desalination in theUnited States.” The purpose of the study was to objectively quantify wherethermal desalination processes should be competitive, citing examples, anddocumenting regulations and practices that impede the implementation ofthermal desalination in the United States.This report presents the results and explains various cogeneration techniquesthat are used internationally, highlighting the significant differences thesehave from definitions and expectations of “cogeneration” within the UnitedStates. Thermal desalination is often erroneously compared to other desaltingprocesses based on the heat being produced by the direct combustion of fossilfuels. In fact, most thermal desalination systems operating internationallyutilize heat from secondary sources, such as waste or byproduct heat whichwould otherwise be discarded.Initially, this project had the following objectives as they relate to thesubject – “Barriers to Thermal Desalination in the United States”: Investigate our domestic power market regulations and practices (bothState and national) Summarize Federal Energy Regulatory Commission’s (FERC)Cogeneration Policy Profile existing industrial and dual-purpose power/water cogenerationprojects Outline target criteria for future cogeneration applicationsThese objectives were later modified to also include exergistic analyses ofsingle-purpose and dual-purpose desalination plants. Exergistic analysesinvolve a detailed review of all energy consumed in a process and all productsor services the process provides; this is in contrast to simpler methods thatfocus on conversion of fuel into a single product (e.g., electricity) and does notconsider that additional products can be cogenerated from the same primarysource and quantity of energy.1

2. Relevant DefinitionsWhat is thermal desalination and what is a distiller?Thermal desalination is a process that involves changing saline water intovapor. This vapor, or steam, is generally free of the salt, minerals, and othercontaminants that were in the saline water. When condensed, this vapor formsa high-purity distilled water. There are several different methods of achievingthis distillation. The quality of water produced and the heat consumed in itsproduction can both be defined when the system is designed. The efficiencyof these systems covers an order of magnitude. The selected efficiency isproject-specific and reflects the increased capital cost for higher efficiencydesigns that is offset by a lower operating (energy) cost. Conversely, wherelow cost or low-grade thermal energy is utilized, there is economicjustification in utilizing lower efficiency designs.A distiller produces distilled water. When water must be re-mineralized forpotability, there may be no advantage in producing high-quality distillate.When water is required for industrial purposes, there is an economic andprocess gain obtained from using distilled water rather than reverse osmosis(RO) permeate (which often must be treated further by RO and/or polished byanother treatment process).Distillation is, from a practical perspective, a macroscopic process. Vaporchambers are large enough for inspections by groups of people. Tubes can bevisually inspected with the naked eye as can most other components. This isin contrast to the active surfaces of a membrane process such as RO thatoperates on a microscopic level and can only be inspected as part of adestructive autopsy. Distillers require simple screening as pretreatment and aremore tolerant to changes in intake water quality. Oxidants such as chlorinecan cause problems in distillers, but this is orders of magnitude lower than thepotential impact they have on current RO membranes.How is thermal desalination different from membrane processes like RO?There are a few RO plants that operate using fossil-fuel-driven pumps, usuallydiesel-engine pumps in remote locations. There is talk about a large ROproject at the low elevation of the Dead Sea being fed with water flowingdownhill from the Red Sea; the elevation difference reportedly is adequate tocover most or all of the pressure required to drive the RO process. However,for the most part, all RO systems utilize electric-driven motors; they use aprime source of energy that could otherwise be used elsewhere or notgenerated in the first place. Even when these electric RO plants are connectedto renewable energy sources such as wind farms, they are consuming primeenergy that otherwise could be used elsewhere.2

Distillers also require pumping, but depending upon the distillation process,this can be one-third of the electric power required by RO (when consideringseawater desalting). Distillers need heat in addition to pumping power. Iffossil fuels are burned to provide the heat for thermal desalination, it willnever be economically competitive with other desalting processes like RO. Ifthermal desalination units are heated with the byproduct of electricitygeneration – heat that is often discharged to the environment via heatexchangers or cooling towers – then the economics and efficiency can fall infavor of distillers.Why cogenerate power and water?Most all power and water cogeneration facilities have a common thread nomatter where they are located globally: the offtaker accepts both products,and the regulatory framework of the country was developed for water andpower simultaneously under the auspices of a single government agency.From Aruba (in the Caribbean) to Saudi Arabia and points in between, waterand power are systematically linked. Water-En Energiebedrijf (WEB), whichis Aruba’s electricity and water authority, celebrated 75 years of cogenerationin 2007, while neighboring Curaçao will celebrate 80 years of cogeneration in2008. The Arabian Peninsula nations have cogenerated for over 40 years, ashave the United States Virgin Islands.The lure of cogeneration is quite simply to try to use the heat from burningfuel for two purposes: first to turn turbines and make electricity, secondly tocondense in a desalination plant and make water. Even with single-purposepower generation, the steam must be condensed and the heat dissipated to theenvironment, typically via cooling towers or condensers cooled by surfacewater. The attraction is then obvious: instead of throwing the heat away,utilize it in a linked process – desalination.There have been many detailed analyses of cogeneration from an efficiencyperspective, which will be covered later in detail. An exergistic analysis iswhen the First Law of Thermodynamics is used to analyze the efficiency of aprocess. All exergistic analyses show that cogeneration is significantly moreefficient than generating power and water in two disconnected processes.Cogeneration should, therefore, be more economical and environmentallyfriendly than the alternative (this statement assumes that desalination isrequired for any case being studied).Desalination processes require significant quantities of feedwater and energy.Co-locating the desalination process with a power generation facility,therefore, is a practical benefit, even if the two production processes are notintrinsically linked.3

Why are the terms Gained Output Ratio and Performance Ratio importantdesign parameters for a thermal desalination system?Gained Output Ratio (GOR) is a measure of how much thermal energy isconsumed in a desalination process, typically defined as the number ofkilograms of distilled water produced per kilogram of steam consumed, i.e.,Obviously, the GOR value is the same when the United States (U.S.)customary units of pounds are used (figure 1).The value of GOR generally ranges from 1 to 10:1. Lower values are typicalof applications where there is a high availability of low-value thermal energy.Higher values, as high as 18:1, have been associated with situations wherelocal energy values are very high, when the local value or need for water ishigh, or a combination of both.GOR should be considered at the design stage of a desalination system whenthe quantity and economic value of energy and water can be used to comparethe capital and operating costs of units with different GORs. Typically, higherGOR systems cost more but consume less energy and, therefore, have loweroperating costs (at least the energy component of operating cost is lower).Performance Ratio (PR) is a closely related measurement, but slightly moretechnically defined. PR was developed from the U.S. version of GOR, (i.e.,lbs of water per lb of steam). It is not uncommon to assume each pound ofsteam has an average enthalpy of 1,000 British thermal units (Btu), hence:The metric version has been adopted by industry to be:4

5.06.07.08.09.010.011.012.0013.0GORkWh/TMED effectsMED-TC effectsMSF stagesFigure 1. Distillation Energy Consumption.5Stages or EffectskWhth/m325800

3. Discussion of FindingsDesalination is becoming more widespread both domestically as well asglobally, particularly as water stress increases. Most of the newer desaltingprocesses, such as reverse osmosis (RO), are membrane-based. Reverseosmosis has gained wide acceptance and is considered to be energy efficient.It is well known that more energy is required to boil and distill salt water thanto operate a hyper-filtration RO process.3.1 Minimum Energy of SeparationAll desalination processes have the same target for the minimum amountof energy required to separate salt from water; it is defined by the laws ofphysics. For separating salt from seawater, the target is approximately0.7 kilowatthour (electric) per cubic meter (kWh/m3)1; this value considerssome practical factors, but assumes an ideal process – a theoretical concept.Boiling water requires about 650 kWh/m3, which is commonly expressed as1,000 British thermal units per pound (Btu/lb). This is the amount of energyrequired to boil water that is already heated to the point where it is about toboil. RO, on the other hand has demonstrated it can desalt seawater using aslittle as 1.6 kWh/m3.2 Why consider a distillation process requiring energyhundreds of times higher than the theoretical minimum in favor of RO, whichis approaching two times the theoretical minimum? The question is verysimple, but the answer requires the consideration of some practical issues.First, it is important to recognize some key points. RO is an efficient process, but for seawater, the electrical energyconsumption is more typically 2.25 to 2.75 kWh/m3. RO produces a permeate that contains slightly less than 1 percent (%) ofthe salt found in the saline water. For seawater, the permeate istypically 300 milligrams per liter (mg/L) total dissolved solids (TDS); ifbetter quality permeate is required, a second stage (second pass) ofRO treatment is typically incorporated. Several different types of distillation processes are used for desalination,but they all generally produce distillate (product water) between5 and 25 mg/L TDS and can achieve 2 mg/L TDS or better withfeedwater as saline as seawater. Distillers generally require 0.8 to 4.5 kilowatthour (electric) per cubicmeter (kWhe/m3) of electrical energy for process pumps, and an1There are many references that explain this theoretical calculation, including Speiglerand El Sayed, ISBN086689-034-3; Chapter 3.2Demonstrated by the Affordable Desalination Coalitionhttp://www.affordabledesal.com.6

additional 40 to 1,200 kilowatthour (thermal) per cubic meter(kWhth/m3) of thermal energy to operate the process.3These process differences are identified in figure 2. This figure shows thegeneric similarity between thermal and membrane processes as separationtechniques highlighting the fundamental differences. Energy is a primaryconcern for any desalination project, even with the highly efficientRO process. Recently projects in Perth and Sydney, Australia, have elected toutilize 100% renewable energy for their RO plants by contracting for powerfrom remote wind farms. An exciting possibility exists to enhance the overallcarbon footprint by utilizing thermal desalination.3.2 CogenerationDistillation processes include multi-stage flash (MSF), multiple-effectdistillation (MED), and mechanical or thermal vapor compression (MVC,TVC), and the facilities are often referred to as distillers, evaporators, orsimply thermal desalination units.Some distillation desalination processes use a relatively small quantity ofelectricity. These are primarily the thin-film processes such as MED, whichconsume between 0.8 and 1.25 kWhe/m3. If these processes are combinedwith existing sources of unused heat, then the overall carbon footprint will belower than using RO. Even if electricity is generated by 100% renewableenergy, using a distiller in this manner means that more renewable energy canbe sent to the grid to reduce fossil fuel generation elsewhere.As shown in figure 3, by combining a source of waste heat with a thin-filmdistiller, the value of prime energy required to drive the process is closer to theminimum energy of separation than any other desalting technique. Figure 3 isa theoretical configuration for discussion purposes, but it highlights whydistillation may not only be competitive with RO but may also have a lowercarbon footprint.Distillation techniques have long been popular in the countries of the GCC4 inthe Arabian Peninsula. The seas around the GCC countries have largeseasonal variations in temperature and salinity along with high organic loadsthat, until recently, proved challenging for RO desalination. Therefore, MSFhas been the backbone of water production in the GCC countries.3An explanation as to why distillers have a wide range of thermal energy requirements isprovided in the section titled “Maximum Thermal Efficiency Not Always Justified.”4Gulf Cooperation Council; Bahrain, Kuwait, Oman, Qatar, Saudi Arabia and the UnitedArab Emirates.7

tical minimum energy of separation 0.8 kWh/m3 for seawaterPermeate50 – 250 mg/LReverseOsmosisProcessElectricity1.6 – 3.0 kWh/m3SalineWaterConcentrate& slight heatPressureNoiseDistillate2 – 50 mg/LDistillationProcessesElectricity0.8 – 4.5 kWhe/m3Thermal energy40-1,200 kWhth/m3SalineWaterConcentrate& moderateheatHeatNoiseFigure 2. Block Diagrams for Generic Desalination of Seawater ( 35,000 mg/LTDS).8

Distillate2 – 50 mg/LDistillationProcessesElectricity0.8 – 1.2 kWhe/m3Prime ThermalEnergy 0 kWhth/m3SalineWaterConcentrateHeatFigure 3. Block Diagram for Waste Heat Thermal Desalination.There are several ways to generate power, all of which involve a minimum ofone thermodynamic cycle.5 Reciprocating engine-driven generators utilize theOtto or diesel-engine cycles. Steam turbine generators operate on the Rankinecycle, while gas turbines follow the Brayton cycle. Each of these cycles is awell understood ideal thermodynamic process; however, all equipment andfacilities based on these cycles are far from ideal; they have unavoidablethermodynamic losses that represent heat which can potentially be recoveredfor further use. In many cases, heat MUST be removed from the cycle, whichmeans equipment must be installed to keep the process cooled.The GCC countries usually combine their desalination and power facilities insuch a manner that the heat remaining after power generation is directed to theMSF units. MSF is a robust process relatively insensitive to the rugged andseasonally varied sea conditions. In chemical engineering terminology, MSFis a forced-circulation rather than thin-film process, with the result that itconsumes a similar quantity of electricity as RO.Examples of two such dual-purpose cogeneration facilities are Taweelah andShuweihat, which are profiled in appendices A and B, respectively. Theseprojects were chosen because Taweelah is currently the largest facility in theworld, while Shuweihat has the largest individual machines (for MSF or anyother process). If these plants are base-loaded and the heat is truly “waste,”then there is little or no net-energy footprint between RO and MSF. This is, ofcourse, a simplification; the processes have different capital and operatingcosts, are robust to different degrees, and produce water of slightly differentqualities. Perhaps more importantly, the plants are not always base loaded; ifinsufficient waste heat is provided from the powerplant’s turbine, then either5A thermodynamic cycle is a series of processes which returns a system to its initial state.The series of processes can be repeated the most commonly known being the Otto cyclewhich repeats every four revolutions, or strokes, of a gasoline engine.9

water must be taken from storage or auxiliary heat must be provided.Auxiliary heat is usually obtained by operating fuel burners installed after thegas turbine exhaust which is inefficient and expensive.For many years the efficiency of these large distillers has been defined not bywhat distillation technology can achieve but by the normal demand for waterand nominal quantity of heat available. The quantity of heat availabledepends upon the type of power generation utilized on the project.The facilities shown in figures 4 and 5 could both be configured to generate agiven quantity of electricity, say 500 megawatts (MW). Clearly, when all theelectricity is generated in a steam turbine (figure 4), there is a greater quantityof steam available than when part of the power is produced by a gas turbine(figure 5). If identical efficiency distillers are used, then a different quantityof water will be produced in either case. Numerous power generationconfigurations have been developed, and over the years, some ratios havebecome rules of thumb. Usually expressed as million Imperial gallons per day(MIGD)6 per installed MW, the ratios are shown in tables 1 and 2.Figure 4. Power Generation Utilizing Steam Turbine.Figure 5. Power Generation Utilizing CombinedCycle.Table 1. Power-to-Water Ratio (MSF)Power generating configurationBack-pressure steam turbine (MSF)Extraction steam turbine (MSF)Gas turbine (HRSG-MSF)Combined cycle back pressure turbine (MSF)Combined cycle condensing turbine (MSF)m3/d cubic meters per day.MW/MIGD51081619MW/(1,000 m3/d)1.12.21.763.524.186Million Imperial gallons per day, where an Imperial gallon 1.2 times larger than aU.S. gallon.10

Table 2. Power-to-Water Ratio (MED)Power generating configurationBack-pressure steam turbine (MED)Extraction steam turbine (MED)Gas turbine heat recovery steam generator(HRSG-MED)Combined cycle back pressure turbine (MED)Combined cycle condensing turbine (MED)m3/d cubic meters per day.MW/MIGD3.57MW/(1,000 m3/d)0.771.54610121.322.22.64With the backdrop of tough and variable seawater conditions and the provenreliability of distillers, one of the above configurations continues to beselected for most of the seawater desalination in the GCC. Whichconfiguration is selected depends upon many factors, most of which are notdirectly related to desalination at all. The main water consideration is simplyidentifying the total demand for water. Other factors, such as the total powerproduction and fuel available for the generation process, are what reallydetermine what configurations are possible, practical, and ultimately areselected.MED systems also have lower investment costs than MSF plants, whichmeans that as RO systems are proven reliable, there is a

Desalination, Multi-Stage Flash Distillation, Multi-Effect Distillation, Reverse Osmosis, Seawater Treatment, Thermal Desalination, Thermal Energy, Vapor Compression, Waste Heat 16. SECURITY CLASSIFICATION OF: UL 19a. NAME OF RESPONSIBLE PERSON T Harry Remmers a. REPORT UL b. ABSTRACT UL c. T

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