2. TOPICS OF PRESENTATION
INTRODUCTION
what is it?
why is it?
where is it?
VARIOUS METHODS OF DESALINATION
THERMAL BASED –Multi-Stage Flash distillation (MSF), Multi-Effect Distillation (MED),
Vapour compression(VC)
MEMBRANE BASED –Reverse Osmosis (RO), Electro-Dialysis (ED), Electro-dialysis Reversal
(EDR)
PREFERRRED TECHNOLOGIES IN SEA WATER DESALINATION
MFD & RO
why is it preferred
STATE OF THE ART
Reverse osmosis technology
Pretreatment
Post treatment
Chemical cleaning
Reject handling
Energy recovery
3. INTRODUCTION
WHAT IS DESALINATION?
Desalination refers to the various processes that removes excess salt and other minerals from water in
order to make it suitable for human consumption , irrigation and industrial application.
desalination can be :
Sea water desalination
Brackish groundwater desalination
WHY DESALINATION?
Makes water suitable for human consumption and
Irrigation
Makes water suitable for industrial application
Scarcity of fresh surface water in the world
Hazardous contamination of groundwater
Abundance of sea water
4. INTRODUCTION
As per data from WORLD WATER BALANCE AND WATER RESOURCES OF
THE EARTH, UNESCO 1975, following are some percentages of total water
available on earth:
96.5% of earths water are oceans and seas which are saline in nature and are not fit for any usage in
its natural form
0.93% of earths water are saline ground water which are unfit for usage without treatment
0.006% of total earth’s water are saline lake water and are not usable in its untreated form.
Therefore nearly 97.5% of earth’s total water cannot be used directly into most of the applications and uses
of humans which amount to a quantity of 1351 Million cubic kilometres.
WHERE DESALINATION IS USED?
Arid areas with scarcity of fresh water , contaminated ground water or brackish groundwater
Sea water as source of raw water
Power availability in abundance and cost of power is low
renowned desalination projects of the world
desalination plant table.pdf
some major ro based desalination project in INDIA
-nemmeli-chennai-100mld
-minjur-chennai-100mld
5. METHODS OF SEA WATER DESALINATION
THERMAL BASED SEA WATER DESALINATION
Includes heat transfer
Includes phase change of water to vapour
heating
evaporation
condensation
Includes operation at pressure lower than atmospheric pressure to reduce energy consumption
for vaporizing water
Different thermal processes are
Multi-stage flash distillation
Multi -effect distillation
Vapour compression
MEMBRANE BASED SEA WATER DESALINATION
Includes use of very thin special plastics which acts as special barriers for selected particles
Includes the reverse principle of osmosis
Includes high pressure operations
Includes the principle of electrolysis with ionic movement towards preferred electrodes.
Different membrane based process:
Electro dialysis & Electro dialysis reversal
Reverse Osmosis
6. MULTISTAGE FLASH DISTILLATION
MORE THAN HALF OF WORLDS DESALINATION PLANTS ARE BASED ON
THIS PROCESS
THE PROCESS INVOLVES
Feeding of sea water into the system
Preheating of sea water while passing through heat exchange tubes
Heating of preheated sea water in a brine heater at normal pressure
Passing of heated sea water through a series of closed vessel with progressively lower internal
pressure called ‘stages’
Sudden boiling of heated sea water in the stages with progressively lower internal pressures
called ‘flashing or exploding into steam’
Steam formed is passed over the heat exchange tubes carrying the incoming cold sea water
causing it to condense
Collection of the condensate as pure water on a tray under the tube
Blowdown of stage chambers with concentrate.
operating temperature varies from 90-120 degrees centigrade
number of stages can be from 4- 40 stages
power consumption figure varies from 23-27 kwh/cubic meter of distilled water production
7.
8. MULTISTAGE FLASH DISTILLATION
ADVANTAGES:
Large production capacity (4000-30000 cum/day)
Has flexibility in regards of quality of water
More energy efficient with respect to other thermal processes
Proven reliability
Better quality of water is achievable than membrane processes
Well developed construction and operation experience over other thermal processes
Less pretreatment to feed water required
DRAWBACKS:
Operating cost high as it has both electromechanical equipments as well as requirement of fuel
to generate heat
Maintenance cost high due to high level of scale formations and corrosion due to high operating
temperature
9. REVERSE OSMOSIS
DEFINING RO
Reverse osmosis is a filtration process which works by using pressure to force a solution
through a semi permeable selective membrane, retaining the solute on one side and allowing the pure
solvent to pass to the other side. This is the reverse of the normal osmotic process, which is the natural
movement of solvent from an area of low solute concentration, through a membrane, to an area of high
solute concentration when no external pressure is applied to balance the free energy available in the high
concentration area. Osmotic pressure is driven by chemical potential which is a thermodynamic
parameter.
RO FEATURES AND MEMBRANES
Involves high pressure operations (40-80 bars of pressure)
Type of membranes can be cellulose acetate type or polyamide type.
In sea water application polyamide membranes are used as these membranes can handle temperatures
above 35 deg C.
Spiral wound membrane is the most commonly used membrane construction in sea water reverse
osmosis process
Semi permeable membranes used has dense barrier layer in polymer matrix
Spirally wound membrane picture MEMBRANE.jpg & spiral wound membrane.gif
13. REVERSE OSMOSIS
ADVANTAGES:
Suitable for desalinating both sea water as well as brackish ground water
Flexible in regards of quantity and quality
Requires less energy than thermal processes
Flexible in regards of starting and stopping of pumps
Easy operation with full automation
Flexible in the matters of increasing the capacity of plant size by adding new membrane units
Operating cost comparatively low with respect to thermal processes
DRAWBACKS:
More pretreatment required
Water quality achievable is in the tune of 250-500 ppm
Maintenance cost high
14. PRE-TREATMENT TO DESALINATION
PRE-TREATMENT HIGHLIGHTS
WHY PRETREATMENT OF RO IS REQUIRED
No regular backwashing of the membranes are done due to the spiral wound characteristic of the membrane as
effective cleaning of the membrane cannot be achieved
Fouling in the membrane caused due to various factors results in loss of productivity of the system
Membrane life gets hampered due to biological, organic and other deposits reducing the performance level
For adjustment of Oxidation-reduction potential, PH and SDI of inlet feed water.
For separating out the maximum of solid particles to make RO efficient. e.g.. cartridge filtration to remove 1-5
micrometer sized particles. and ultrafiltration to remove particles below <1 micron
STAGES OF PRETREATMENT BEFORE RO PROCESS:
Course and fine screen arrangement for physically separating larger sized wastes e.g. plastic, shoes, rags, sticks,
sea weeds etc. in the sea water intake area.
In presence of oil, oil removal systems like API, TPI and DAF are required for physical separation of oil by
floatation and skimming technique
Suspended solid separation by coagulation ,flocculation and settling process in clariflocculators, clarifiers
Application of chlorine and sodium meta-bisulphate for prevention of biological fouling and necessary surface
adsorption membranes for removing residual oxidizing agents.
PH correction process for avoiding extreme PH conditions for prevention of RO membranes from corrosive
atmosphere
Various micro filtration processes viz. ultrafiltration, cartridge filtration, Nano filtration based on the type of RO
membrane selected and final water quality requirement. primary purpose of pre filtration is to lower the particle
size of the feed water and also take care of colloidal silica and reduction of SDI below 4.
15. PRE-TREATMENT TO DESALINATION
DIFFERENT TYPES OF FOULING WITH NECESSARY PRETREATMENTS
Fouling Cause Appropriate Pre-treatment
Biological fouling Bacteria, microorganisms, viruses,
protozoan
Chlorination + Micro filtration
Particle fouling sand, clay (turbidity, suspended solids) Flocculation & sedimentation +
Filtration
Colloidal fouling Organic and inorganic complexes,
colloidal particles, micro-algae
Chlorination +Flocculation &
Sedimentation+ Micro Filtration
Organic fouling Natural Organic Matter (NOM) : humic
and fulvic acids, biopolymers
Coagulation + Filtration + Activated
carbon adsorption
Coagulation+ Micro filtration
Mineral fouling Calcium, Magnesium Barium or
Strontium sulfates and carbonates
Antiscalant dosing
Acidification and Post PH correction
Oxidant fouling Chlorine, Ozone, KMnO4 Oxidant scavenger dosing:
Sodium (meta)bilsulfite
Granulated Activated Carbon
16. PUMPING SYSTEM IN DESALINATION
THE BASIC GROUP OF PUMPS AND TYPICAL TYPES IN A SWROP ARE:
PUMPS TYPES
Sea water intake pumps Vertical Turbine pumps, Depressed pit Horizontal
centrifugal Pumps
Pre-treatment Filter feed pumps Horizontal centrifugal Pumps
Microfiltration Filter feed pumps Multi Stage Pumps
RO high pressure feed pumps Multi Stage Pumps
RO low pressure feed pumps Multi Stage Pumps
Filter backwashing pumps (for backwashing filters of
pretreatment system)
Horizontal centrifugal Pumps
Flushing pumps Positive Displacement pumps
Energy recovery drive pumps (booster pumps) Horizontal centrifugal Pumps
Product water pumps Horizontal centrifugal Pumps
Chemical cleaning pumps Positive Displacement pumps, progressive cavity type
or diaphragm type.
Reject handling pumps Multi Stage Pumps
17. PUMPING SYSTEM IN DESALINATION
The feed pumps supplies the pressure needed to push water through the membrane, while the
membrane rejects the passage of salt through it.
Typical pressures for sea water feed pumps ranges from 60 to 80 bars (high pressure operations)
efficiency of pumps are high for lower power consumption
Corrosion resistant material of construction to handle sea water
Wide range of flow (rpm varies 700 to 3450)
Centrifugal pumps for smaller and positive displacement pumps for comparatively larger systems
Corrosion resistant material of construction to handle sea water are used. e.g. Duplex stainless
steel, Titanium etc.
18. POST TREATMENT IN DESALINATION
Depending on the treated water application the reverse osmosis permeate shall be reconditioned
before end usage
Usual permeate Character
has an acidic PH
TDS varying from 100-350mg/lt
2-6 mg/lt of calcium and magnesium content
Boron content 0.5 to 1.2mg/lt based on the raw water salinity and temperature
End usage can be human consumption, irrigation or industrial process water.
FACTORS DRINKING
WATER
IRRIGATION WATER PROCESS WATER
SODIUM CHLORIDE <450MG/LT AS PER SAR & EC
OPTIMIZATION
MINIMUM
CALCIUM AND MAGNESIUM 6-10MG/LT AS PER SAR & EC
OPTIMIZATION
MINIMUM
PH 6.5-8.5 6.5-8.5 6.5-8.5
BORON <0.5 MG/LT CROP DEPENDANT -
DISINFECTION REQUIRED NOT REQUIRED NOT REQUIRED
19. POST TREATMENT IN DESALINATION
POST TREATMENT SUMMARY
PROCESS DRINKING
WATER
IRRIGATION
WATER
PROCESS
WATER
TO REMOVE SODIUM
CHLORIDE
2ND PASS RO - 2ND PASS RO
TO REMOVE CALCIUM
AND MAGNESIUM
REMINERALISAT
ION
REMINERALISATION -
TO NEUTRALIZE TO PH
+/-7
NAOH/HCL
INJECTION
NAOH/HCL
INJECTION
NAOH/HCL
INJECTION
TO REMOVE BORON NAOH+2ND PASS
RO
SPECIFIC BORON
REMOVAL PROCESS
-
DISINFECTION HYPOCHLORITE
ADDITION
NOT REQUIRED NOT REQUIRED
20. CHEMICAL CLEANING IN DESALINATION
Seawater flows tangentially along the membrane, creating a boundary layer on the membrane
surface.
Membranes have to cleaned typically when:
- Normalized permeate flow varies by 10-15%
- Normalized feed pressure varies by 10-15%
- Normalized permeate conductivity varies by 10-15%
- Pressure drop between feed and concentrate varies by 10-15%
Normalized values take into account temperature and salinity variations in feed water.
In order to ease cleaning, systems can be equipped with cleaning in place (CIP) station, readily
connected to the membranes rack
The CIP station, depending on the plant size includes a chemical tank with mechanical or manual
stirrer, a CIP pump and a fine filter to avoid debris to enter the membranes. the chemical tank
depends on the number of membranes to be cleaned at the same time.
Alkaline and acid cleaning solutions are recirculated around the membranes for at least 30 minutes.
21. REJECT HANDLING IN DESALINATION
Reject of sea water desalination plant are discharged 2-3 kms deep inside the sea through marine
pipelines
The pressure available in the reject is utilized in the feed system with energy recovery devices for
reducing power consumption
Rejects can be also taken into another RO system at a higher pressure for maximum utilization
Rejects can be put into incinerators to produce salts as the solid waste by evaporation of the liquid. it
helps in attaining zero discharge concept
ENERGY RECOVERY IN DESALINATION
The power required to drive the high pressure pumps is the largest component of operating cost in SWRO
membrane system. Most of energy imparted into the feed water flowing to the SWRO membranes leaves
with the membranes in the brine reject water. A number of devices have been developed to recover pressure
energy from the brine reject stream. Effectivity of an energy recovery device can be judged by quantifying the
power consumption of a high pressure pumping system with the device and without the device. Energy
recovery devices can be divided into two general categories.
CENTRIFUGAL : Captures brine pressure with a turbine and transfer it to an impeller spinning in the sea
water Francis turbines, Pelton wheels and turbochargers
ISOBARIC : The device accomplish a direct transfer of pressure from the brine to the sea water in constant
pressure chambers pressure exchangers where number of free pistons operate to balance and transmit
pressure from the brine side to the sea water feed side.