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Reverse Osmosis Technology

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Reverse Osmosis Technology

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In this presentation, we tried to cover all the information regarding Reverse Osmosis technology. We have discussed its different types, major parts of Reverse Osmosis i.e Activated Carbon Bed, Ion Exchange Unit, Cartridge Filter and then at the end design steps of Reverse Osmosis.

In this presentation, we tried to cover all the information regarding Reverse Osmosis technology. We have discussed its different types, major parts of Reverse Osmosis i.e Activated Carbon Bed, Ion Exchange Unit, Cartridge Filter and then at the end design steps of Reverse Osmosis.

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Reverse Osmosis Technology

  1. 1. REVERSE OSMOSIS SYESTEM (University of Engineering and Technology, Lahore)
  2. 2. Presenters • Awais Yaqoob(2011-ch-32) • Mujahad Ali(2011-ch-24) 1 • Engineer Haq Nawaz(2011-ch-44) • Adeel Matloob(2011-ch-46) 2 • Rizwan Liaquat(2011-ch-72) • Hafeez-ur-Rehman(2011-ch-80) 3
  3. 3. Synopsis Ion-Exchange Unit Reactions Involved Merits and Demerits Activated Carbon Bed Factors Affecting its Performance Regeneration of Bed Introduction to Reverse osmosis Key Terms RO arrangements
  4. 4. Advantages And Disadvantages of RO Comparison b/w RO and other purification techniques Conclusion Basic Equations for RO Calculations RO System Design Guidelines Steps to Design RO Membrane System Cartridge Filter Flow Meters Conductivity Meters
  5. 5. Reverse Osmosis • Reverse Osmosis is a technology used to remove majority of contaminants from water by pushing water under high pressure through a semi permeable membrane • It is a process where you demineralize or deionize water
  6. 6. Osmosis • To understand purpose and process of RO, you must first understand naturally occurring process of Osmosis • It is a process where a weaker saline solution will tend to migrate to a stronger saline solution • For example, Plant root absorbs water from soil & Kidney absorbs water from blood • In diagram, salts are more concentrated in salty water so natural flow of salts will be from right side to left side and water will flow from right side to left side
  7. 7. Reverse Osmosis • RO is other way round of naturally occurring Osmosis • Water is pushed through semi permeable membrane under high pressure, thus leaving behind contaminants • Pressure depends upon salt concentration of feed water. • More the salts, more will be the applied pressure
  8. 8. Cont.… • Two types of water coming out of RO – Permeate (containing less contaminants) – Concentrate, reject or brine (containing more contaminants) • Ro system employs cross filtration rather than standard filtration where the Contaminants are collected within the filter media.
  9. 9. Salt Rejection % • It tells you how effective the RO membranes are removing contaminants. • A well designed RO system with properly functioning RO membranes will reject 95% to 99% of most feed water contaminants s𝑎𝑙𝑡 𝑅𝑒𝑗𝑒𝑐𝑡𝑖𝑜𝑛 % = 𝐶𝑜𝑛𝑑𝑢𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑜𝑓 𝐹𝑒𝑒𝑑 − 𝐶𝑜𝑛𝑑𝑢𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑜𝑓 𝑝𝑒𝑟𝑚𝑒𝑎𝑡𝑒 𝐶𝑜𝑛𝑑𝑢𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑜𝑓 𝐹𝑒𝑒𝑑 • The higher the salt rejection, the better the system is performing • The lower the salt rejection meaning either filter needs to be cleaned or replaced
  10. 10. Salt Passage % • It is the inverse of Salt rejection. • It tells the amount of salt passing through RO system Salt Passage % = (1-Salt rejection%)
  11. 11. Recovery % • It is the amount of water that is being recovered as permeate Recovery % = 𝑃𝑒𝑟𝑚𝑒𝑎𝑡𝑒 𝑓𝑙𝑜𝑤 𝑟𝑎𝑡𝑒 (𝑔𝑝𝑚) 𝐹𝑒𝑒𝑑 𝑓𝑙𝑜𝑤 𝑟𝑎𝑡𝑒 (𝑔𝑚𝑝) * 100 • Industrial RO typically run anywhere from 50% to 85%
  12. 12. Concentration Factor • The concentration factor is related to RO system recovery • The more water you collect as permeate, the more concentrated salts you collect in concentrate stream which may lead to scaling and fouling Concentration Factor = 1 1−𝑅𝑒𝑐𝑜𝑣𝑒𝑟𝑦 %
  13. 13. 1 & 2 Stage RO System • In 1 stage RO system, feed enters RO system as one stream and leaves as concentrate and permeate. • In 2 stage, concentrate from 1st becomes the feed water to the 2nd stage. Permeate water from 1st stage is collected and mixed with permeate water from 2nd stage.
  14. 14. 1 stage RO
  15. 15. 2 Stage RO
  16. 16. Single Pass RO & Double Pass RO • In double pass RO, permeate from 1st pass becomes the feed to 2nd pass • By going through 2 RO systems, a much higher quality permeate can be achieved • It also removes Carbon Dioxide by injecting Caustic Soda between 1st and 2nd pass • By adding Caustic Soda, we convert CO2 to carbonates and bicarbonates which are removed in 2nd pass.
  17. 17. Single Pass RO
  18. 18. Double Pass RO
  19. 19. Activated Carbon Bed Presented By: Mujahad Ali(2011-ch-24)
  20. 20. Activated Carbon Bed • Activated carbon is a form of carbon processed to have small, low-volume pores that increase the surface area available for adsorption. • Due to its high degree of micro-porosity, just one gram of activated carbon has a surface area in excess of 500 m2
  21. 21. Activated Carbon Bed • Active charcoal carbon filters are most effective at removing chlorine, sediment, volatile organic compounds (VOCs), taste and odor from water. • They are not effective at removing minerals, salts, and dissolved inorganic compounds. • Typical particle sizes that can be removed by carbon filters range from 0.5 to 50 micrometers.
  22. 22. Factors Affecting the Operation • Molecular weight • pH • Contaminant concentration • Particle size • Flow rate • Temperature
  23. 23. Molecular Weight • As the molecular weight increases, the activated carbon adsorbs more effectively because the molecules are less soluble in water. • The pore structure of the carbon must be large enough to allow the molecules to migrate within. • A mixture of high and low molecular weight molecules should be designed for the removal of the more difficult species.
  24. 24. pH • Most organics are less soluble and more readily adsorbed at a lower pH • As the pH increases, removal decreases. • Increase the size of the carbon bed by twenty percent for every pH unit above neutral.
  25. 25. Contaminant Concentration • The higher the contaminant concentration, the greater the removal capacity of activated carbon. • The contaminant molecule is more likely to diffuse into a pore and become adsorbed. • Higher contaminant concentration may require more contact time with the activated carbon.
  26. 26. Particle Size • Activated carbon bed is commonly available in 8 by 30 mesh (largest), 12 by 40 mesh (most common), and 20 by 50 mesh (finest). • The finer mesh gives the best contact and better removal, but at the expense of higher pressure drop. • 8 by 30 mesh gives two to three times better removal than the 12 by 40, and 10 to 20 times better kinetic removal than the 8 by 30 mesh.
  27. 27. Flow Rate • The lower the flow rate, the more time the contaminant will have to diffuse into a pore and be adsorbed. • Adsorption by activated carbon is almost always improved by a longer contact time. • Whenever considering higher flow rates with finer mesh carbons, watch for an increased pressure drop.
  28. 28. Temperature • Higher water temperatures decrease the solution viscosity and increase diffusion rate. • Higher temperatures can also disrupt the adsorptive bond. • Generally, lower temperatures seem to favor adsorption.
  29. 29. Regeneration of Bed • The economics of the adsorption process greatly depend on the reuse of activated carbon. Various regeneration techniques are used such as; • Thermal regeneration • Chemical regeneration • Wet air oxidation
  30. 30. Presented By: 2011-ch-44 32 Water Softener
  31. 31. 33 • What is ion exchanger? • Applications • Formation of ion exchanger • Hardness types and removal • Resins types • Regeneration • Advantages & Disadvantages of ion exchanger Water Softener/Ion Exchanger
  32. 32. 34 Ion exchange is an adsorption phenomenon where the mechanism of adsorption is electrostatic. What is ION Exchange?
  33. 33. 35 • Ca , Mg (hardness removal) exchange with Na or H. • Fe, Mn removal from groundwater. • Demineralization (exchange all Cations for H all anions for OH) Applications
  34. 34. 36 Resins are formed by polymerization process . • Typical procedures involve heating aqueous solutions of alumina and silica with sodium hydroxide. • Equivalent reagents include sodium aluminate and sodium silicate. Formation of Resins
  35. 35. 37 1) Temporary hardness 2) Permanent hardness Hardness
  36. 36. Removal of Temporary Hardness 38 (1)Boiling Method: Ca ( HCo3)2 ---> CaCo3 + Co2 + H2o Mg ( HCo3)2 ---> MgCo3 + Co2 + H2o (2)Clark’s Method: Ca (HCo3)2+ (Ca(OH)2 ---> 2CaCo3+ 2 H2o
  37. 37. Removal of Permanent Hardness 39 (1)Reaction with Washing Soda Na2Co3 + Caso4 ---> CaCo3 + Na2so4 (2) Ion Exchange Method: Caso4 + Na2 – zeolite ---> Ca - zeolite + Na2so4
  38. 38. Resin Classification 40  Cationic resin  Anionic resin
  39. 39. Cationic Resin Vs. Anionic Resins 41 • Those that exchange positive ions, called cation exchange resins.e.g Ca+2, Mg+2 • Those that exchange negative ions, called anion exchange resins.e.g Cl-1, SO4-2,
  40. 40. 42 Regeneration and its Types Counter-current Regeneration Co-current Regeneration
  41. 41. Co-current Regeneration 43
  42. 42. Counter-current Regeneration 44
  43. 43. Regeneration Reaction 45 Ca- zeolite + NaCl ---> Na2 – zeolite + CaCl2
  44. 44. Advantages of Soft Water 46 • Longer appliance life for washing machines • Less use of household cleaning products, such as detergents. • Your clothes last longer and remain brighter longer if they are washed in soft water. • Your plumbing will last longer. Hard water can cause a build up of scale from mineral deposits • Your skin is softer when you bathe with soft water
  45. 45. Advantages of Ion Exchange Column 47 • It is compact and has a low capital cost • The chemicals used are safer for the operator to handle and operation • It can be almost totally automated • It can be used for production of good quality water
  46. 46. Disadvantages 48 • Adsorption of Organic Matter • Iron Fouling • Bacterial Contamination
  47. 47. Cartridge Filter
  48. 48. Cartridge Filter • Fabric or Polymer-Based • To remove Particulate material • Designed along a central core • Pleats/ Foldings
  49. 49. Top Cap Bottom Cap Pleated Media
  50. 50. Working of Cartridge Filter • Pressurized Fluid • Passage through the Pore • Suspended Solid material • Clogging • Pressure drop
  51. 51. Application • Filtration of surface water or ground water under the influence of surface water. • Prefiltration prior to subsequent treatment. • Solids removal.
  52. 52. Rotameter
  53. 53. Rotameter • Variable area meters • Cross Sectional area • Floating
  54. 54. Working of Rotameter • Volumetric Flow rate increases drag force • Cone shaped area decreases the buoyancy force • Equilibrium with the float
  55. 55. Why to use Cartridge Filter and Rotameter
  56. 56. Cartridge Filters Cartridge Filters are less expensive then the other sediment filters Minimum maintenance is involved Can filter out anything about 5 to 10 micrometre in size Can be both the surface and depth type filters Ease in cleaning
  57. 57. Rota Meter Relatively Simple Device to manufacture Requires no External power or fuel to run Scale of rotameter is almost linear Clear glass is used which is highly resistant to shock
  58. 58. RO System
  59. 59. REVERSE OSMOSIS SYSTEM DESIGN Presented By: Rizwan Liaquat(2011-ch-72)
  60. 60. Basic Equations for RO Calculations Water Transport Solute Transport Correlation of Operating Conditions
  61. 61. Water Transport • Water transport through the membrane is expressed as a permeate flux. • The permeate flux is proportional to the net driving pressure (NDP). Where
  62. 62. CONTD… • The product flow rate can be obtained by multiplying the permeate flux by total membrane area. • The pressure drop is calculated by the average flow rate (feed and concentrate) as follows: In which a and b are coefficients, specific for element and feed spacer configuration. The values for these coefficients are obtained experimentally.
  63. 63. Solute Transport • Solute transport through an RO membrane is expressed as a solute flux. • This solute flux is proportional to the concentration difference across the membrane. • The average feed concentration (feed and concentrate) is used in the feed side to calculate solute transport. • And the rate of solute transport is defined by rejection or salt passage as follows: In which: B, solute permeability, R, rejection, SP, salt passage
  64. 64. Correlation of Operating Conditions • RO membrane system performance (flux and rejection or salt passage) is influenced by operating conditions such as operating pressure, temperature, feed concentration etc. • AS = Specific flux at operating conditions, • An= Specific flux at nominal conditions • SPS= Salt passage at operating conditions, • SPn= Salt passage at nominal conditions • (JV) S= Permeate flux at operating conditions, (JV) n,= Permeate flux at nominal conditions • TCF = Correlation factor of temperature (1; on specific flux, 2; on salt passage) • SCF= Correlation factor of feed concentration (1; on specific flux, 2; on salt passage) • FF= Fouling factor
  65. 65. RO System Design Guidelines Fouling Tendency with Operating Conditions Recommended Range of Element Operating Conditions (Design Guideline)
  66. 66. Fouling Tendency with Operating Conditions • Membrane fouling is caused by particles and colloidal materials which are present in the feed water and become concentrated at the membrane surface. • The Silt Density Index (SDI) of pretreated feed water is an index of the fouling potential of particle or colloidal materials in the RO system. • The concentration of the fouling materials at the membrane surface increases with increasing permeate flux, increasing element recovery and decreasing concentrate flow rate. • Therefore the average permeate flux of the RO system should be low if a strong fouling environment is anticipated.
  67. 67. Recommended Range of Element Operating Conditions The maximum lead element permeate flux The maximum average permeate flux The maximum recovery (system and element) The maximum feed flow rate The minimum concentrate flow rate
  68. 68. Steps to Design RO Membrane System System Design Information and Feed Water Selection of Element Type and Average Permeate Flux Calculation of Number of Total RO Elements Decision of Recovery Rate Decision of Number of Stages Decision of Number of RO Elements per Pressure Vessel Decision of Element Arrangement Relations between Nominal Performances and Field Results
  69. 69. System Design Information and Feed Water Water source and pretreatment required Customer/process required product flow rate Application of water being treated Expected recovery rate Annual water temperature Required product water quality, operating pressure limit, etc.
  70. 70. CONTD… • The RO membrane system highly depends on the available feed water. • Therefor, the System design information should be thoroughly studied and considered in selection of the RO system design. • If the required permeate water quality is so high that the quality cannot be achieved by 1pass RO system, and then a 2 pass RO system should be considered. • As an alternative to the 2 pass RO, an ion exchange resin system may also be a viable design option
  71. 71. Selection of Element Type and Average Permeate Flux • According to the feed water source, pretreatment and feed water salinity, the type of RO membrane element is selected. • Once the water source, pretreatment and RO element type are fixed by the designer, the recommended value of the average permeate flux (also called “design flux”) is determined by pilot experiment data or customer’s experience.
  72. 72. Calculation of Number of Total RO Elements • The relationship between the number of total elements, the product flow rate and the average permeate flux is expressed as follow equation: • In Which: • NE= Total element numbers • Qp= Product flow rate • JV,ave= Average permeate flux • (MA)E= Membrane area of element
  73. 73. Decision of Recovery Rate • In an RO membrane system, a recovery rate as high as possible is desirable • A high recovery rate can also cause some problems as follows:  Possibility of scale formation increase because of the increase of concentration factor  Osmotic pressure increase because of the increase of concentration factor  Concentrate flow rate decrease  Permeate water quality deterioration because of average feed concentration increase
  74. 74. CONTD… • Generally recovery rate is decided by scale formation and by feed pressure limit.
  75. 75. Decision of Number of Stages • The number of RO stages defines how many pressure vessels are in series in the RO membrane system. • Every stage consists of a certain number of pressure vessels in parallel. • The number of stages is a function of the system recovery rate, the number of elements per vessel, and the feed water quality
  76. 76. CONTD…
  77. 77. Decision of Number of RO Elements per Pressure Vessel • RO membrane elements can be coupled together in series in the pressure vessel, typically 1-8 elements per one pressure vessel. • In deciding the number of RO elements per pressure vessel, plant size is usually considered first. • In a large-scale plant (> 40 m3/h), 6-8 elements per pressure vessel are usually adopted, and in a smaller plant, 3-5 elements per pressure vessel. • In all cases, the space required to install or remove the RO elements should be considered in the plant design.
  78. 78. CONTD… • By increasing the number of RO elements per pressure vessel, almost all RO design parameters will change.
  79. 79. Decision of Element Arrangement • For the decision of element arrangement, the system design parameters should be consistent with the design flux guideline. • To decide the array, several calculations for case study should be done by computer program and these results should be compared.
  80. 80. Relations between Nominal Performances and Field Results • A higher nominal flow rate element will require lower feed pressure. • At different test conditions and /or different membrane area, feed pressure will be defined by water permeability. • A higher salt rejection element will produce a permeate of lower salinity. • A lower relative salt passage element (multiplier of nominal permeate flux by nominal salt passage) will produce a permeate of lower salinity.
  81. 81. Advantages And Disadvantages of RO Advantages: 1. Low Energy Requirements. RO performs a separation without a phase change. Thus, the energy requirements are low 2. Less Space requirements. RO systems are compact, and space requirements are less than with other desalting systems, e.g. distillation 3. Easy to Understand RO equipment is standardized - pumps, motors, valves, flowmeters, pressure gages, etc. Thus, the learning curve for unskilled labor is short.
  82. 82. 4. Little labor required:- Many RO systems are fully automated and designed to start-up and shutdown automatically through interlocks. Thus, RO plants usually require little labor. 5. Easy maintenance:- Due to their modular design, maintenance is easy. maintenance can be performed without shutting down the plant. Also the expansion of plant is an easy option. 6. Remove unpleasant smell:- RO removes dissolved minerals and other contaminants that cause to smell unpleasant.
  83. 83. 7. Efficient for plumbing system:- Removal of dissolved minerals, metals and other particles benefits plumbing systems, Nothing in the water to corrode pipes. 8. Removes bacteria and pathogens in drinking water Biological contaminants present in tap water are harmful bacteria that can cause diseases. And if you happen to drink the water, you may acquire fatigue, diarrhea, excessive gas, bloating, loss of interest in food and weight loss. 9. Better taste and smell In this process, 98% of chemicals are removed from your drinking water so it will not taste of chlorine anymore.
  84. 84. 10. Reduces the risk of having diseases and illnesses Chlorine, asbestos, mercury and lead are some of the toxins that can be found in tap water. Reverse osmosis offers defense between the body and the other 2100 known toxins. 11. Children- friendly Drinking pure water is very important to children’s developing immune systems. Water filters such as reverse osmosis systems provide the healthiest water for them.
  85. 85. Disadvantages 1. Purification Limits Many RO systems come with carbon pre-filters. That’s because chlorine and Volatile Organic Chemicals (VOC’s) are smaller than water molecules so they can’t be filtered on the reverse osmosis membrane. 2. Speed and Efficiency These systems can only produce 15 (gpd). It works against standard osmotic pressure so the reverse osmosis process is fairly slow. And requires 3 to 10 gallons of untreated water to make a single gallon of purified water, which is wasteful and expensive.
  86. 86. 3. Maintenance:- The maintenance of RO system must be done regularly. its filters must be cleaned to avoid the fouling of the membranes. The pre-filters must be changed annually, while the RO membrane should be replaced every 2-3 years. 4. Pressure limitations:- The applied pressure must exceed the osmotic pressure to separate the solute from the solvent. The max pressure for seawater devices is 800 - 1000 psig, For brackish water varies from 400 - 600 psig. Due to the high pressure requirement RO is usually not applicable for concentrated solutions.
  87. 87. 5. Pretreatment Required:- Because all RO membranes and devices are susceptible to fouling, the RO process usually cannot be applied without pretreatment. 6. Compatibility of feed Stream:- RO feed streams must be compatible with the membrane and other materials of construction used in the devices.
  88. 88. 7. High Temperature Usually at high temperature the RO process is favorable but the problem at high temperature is the increase in pore size of the membrane so it requires optimum conditions for temperature. 8. High Conductivity As Conductivity is directly proportional to total dissolved solids so It means high conductivity liquids require more treatment and hence more time required for the RO purification system.
  89. 89. • Comparison b/w RO and other purification techniques The given below are some techniques comparable with Reverse Osmosis 1. Ion Exchange 2. Distillation 3. Activated Carbon 4. Precipitation 5. Ultraviolet Radiation 6. Boiling
  90. 90. Disease Element Causing Disease Reverse Osmosis RO Ion Exchange Distillation Activated Carbon Precipitation Ultra- Violet Boiling Cancer Initiation Chlorine # x B # x x X pH In-equilibrium Alkali Fume # A # x x x X Cancer Initiation Chloroform # x B # x x X Bacteria Infections Disease Bacteria # x # B x # # Virus Infections Disease Viruses # x # x x # # Intoxication, Liver Disease Agricultural Chemicals # x # # x x X Hepatitis Dioxin # x # B x x X
  91. 91. Cancer Radioactive Material A A B x x x X Anorexia Taste and Odor # x x # x x X Calculus, Enteritis Precipitate # x # B # x X Poisoning Organic Substances # x B # X x X Cancer Initiation Fluoride A A # x x x X Cancer Initiation Fluorescence # x x x x x X Neuritis Arsenic A A A x x x X Calculus Calcium A A A x x x X
  92. 92. Notalgia Cadmium A A A x x x X Nephrosis, Leading Poisoning Lead A A # X x x X Organic Phosphorus Poisoning Phosphorus A A # X x x X Electrolyte In-equilibrium Potassium A A A X x x X Hypersensitive Heart Disease Sodium A A # X x x X Digestive System Disease Sulphur A A A X x x X Digestive System Disease Magnesium A A # # x x X Where #=98-99% Removal ; A =96-99% Removal; B =Partial Removal; x =Can not Remove

Editor's Notes

  • We cannot add caustic soda on 1st stage, coz by adding it carbonates will be formed which will react with cations like calcium and will cause fouling.

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