Membranes are becoming increasingly popular for production of potable drinking water from ground, surface and seawater sources, as well as for the advanced treatment of wastewater and desalination. These technologies have been one of the most used technologies for the treatment of water over the last two decades. It is a very high performing system.
Advantages and Disadvantages
- High performance
- Compact units: less space needed than conventional treatment schemes
- Simple operation
- Membranes available can be used to separate many kinds of contaminants
- Disinfection can be performed without chemicals
- Membrane fouling
- Production of polluted water (from backwashing)
- Membranes have to be replaced on a regular basis
Today there are many different types of membranes that allow the passage of solutes and others depending on their nature, ionic charge or size.
|DIVISION FACTOR||DRIVING FORCE||TYPE – OPERATION|
|Size / Difussion||Pressure / Concentration||Reverse Osmosis|
|Ion Charge / Difussion||Electric field||Electrodialysis|
|Temperature (Hydrophobic membrane)||Steam pressure||Membrane distillation|
In this case the classification is based on Division factor, then there are the most important types like to describe the main types according to this criteria:
- SIZE: Microfiltration / Ultrafiltration / Nanofiltration / Reverse Osmosis
- ELECTRIC FIELD: Electrodialysis / Reversal Electrodialysis
- TEMPERATURE: Membrane distillation
MICROFILTRATION / ULTRAFILTRATION /NANOFILTRATION
Micro-filtration membranes have a pore size of 0.1-10 µm, enough to restrain all types of bacteria, turbidity, macromolecules, colloidals, etc. These are used during cold sterilization of liquid food and pharmaceutical products, water microorganism reduction, water pretreatment for nano-filtration and reverse osmosis, etc.
By means of ultra-filtration, particles with a size of 0.001-0.1 µm are removed. All viruses, macroproteins, antibiotics, etc, are restrained in these membranes. These have application in the removal of harmful organic substances from food and drink industries, in the removal of trihalomethanes from water, in the treatment of wastewaters and in the textile industry, amongst others.
By means of nano-filtration, particles with a size of 0.1 nm-0.001 µm are restrained, allowing water separation from most molecules, although low molecular weight particles are partially restrained in the membrane. Nano-filtration is used for water-softening, wastewater heavy metal elimination, wastewater decontamination, pretreatment for reverse osmosis, nitrates elimination, colour removal, etc.
Reverse osmosis uses a procedure whereby through a semipermeable membrane the chemical potentials of two dilutions located one on each side of the membrane tend to equalize, making it operate in reverse.
Reverse osmosis consists of pumping water charged with dissolved ions to a tank where it’s subjected to pressure against a membrane. During this process, water is transferred from one side of the membrane to the other. Ions are left in the feed water thereby generating a concentrate in the water that has not yet passed through the membrane and a purified water flow if it has passed through the membrane.
The concentrate generated should be eliminated from direct contact with the membrane to prevent an increase in ion concentration that can precipitate salts on the membrane surface. This provokes a loss of effectiveness of the process in addition to increased maintenance costs. It is also important to perform pretreatment to prevent clogging.
Electrodialysis consists of the elimination of electrically charged ions, those of which are dissolved in water. To carry out this elimination phase, a pair of distinctly charged electrodes are introduced into the feed water so that the dissolved ions will be attracted to the electrodes of opposite sign to their own. This achieves moving the ions from one place to another in the dissolution.
The alternating use of anion and cation selective membranes is essential for the feed water to continue losing negative and positive ions after passing through the separation zone.
Most interestingly is alternately placing the membranes so that in some of the channels solutes are concentrated in water called concentrate. In other channels the feed water circulates, gradually losing its contaminants until it finishes the process with a very low salt concentration.
In this case, the polarities of the electrodes are periodically altered so that water flows temporarily change direction receiving purified water from those conduits carrying the concentrate and vice versa.
This method eliminates the risk of formation of precipitates, fouling and clogging of the membranes thanks to the periodic change of water flow direction which facilitates cleaning pipes and membranes and avoids the emergence of slime and other deposits in the plant.
The treatment of saline and briny effluents is not possible using conventional processes. The only technology that offers a complete solution is vacuum evaporation, given that reverse osmosis or electrodialysis generate a discharge effluent that must be managed. And conventional distillation entails costs that make it financially unviable.
However, there is a technology that, though the first patent dates from 1963, its use is currently beginning to emerge harnessing all the developments in membrane engineering. It is membrane distillation.
Membrane distillation consists of a thermal process in which only steam molecules can pass through the membrane, which is hydrophobic. The feed that is to be treated is in direct contact with one of the surfaces of the membrane, but it does not penetrate through the pores of the membrane since the latter is hydrophobic. The driving force for the separation is steam pressure through the membrane, not the total pressure as in reverse osmosis. On increasing the temperature of the deed, the steam pressure increases and, therefore, the steam pressure gradient that is the driving force also increases.
From the commercial point of view, it is a technology that has been widely implemented for the
- The thermal efficiency of the process is low due to the heat loss because of the conductivity of the membranes that occurs.
- Concentration and temperature polarisation effects occur that decrease the flow of permeate through the membrane.
- The wetting effect occurs, which consists of the penetration of impurities in the feed into the pores of the membrane, thus reducing the flow of permeate.
Despite these drawbacks which, as the research progresses are overcome, the technology has a series of advantages that make it competitive in ever more applications. The most important advantages of membrane distillation are:
- As in evaporation, the process is not limited by the equilibrium, such that it is possible to achieve the necessary water and discharge concentration factors. Unlike reverse osmosis, there is no equilibrium that establishes a separation limit.
- The technology generally does not need pre-treatment of the feed to lengthen the life of the membrane.
- The efficiency of the system and the good quality of the water that is produced are practically independent of the feed salt.
- 100% discharge of non-volatile solutes.
- The possibility of treating corrosive and acidic effluents, which in conventional distillation is difficult due to the materials that are required.
- Operational flexibility since they are Independent modules.
The selection of the membrane is key for the process to function well. The characteristics of the membrane directly influence the process; the most important are: the porosity, the size of the pore, the thickness of the membrane, the thermal conductivity and the composition, which is related to the resistance to chemical attack.
The characteristics of membrane distillation make it a technology that may be satisfactorily applied in such varied areas as:
- Production of pure water.
- Brine treatment.
- Elimination of dyes and treatment of wastewater from the textile industry.
- Concentration of acids and corrosive substances, as well as separation of azeotropic mixtures in the chemical industry.
- Concentration of juices and processing of milk in the food industry.
Membrane distillation is a competitive technology in a wide variety of industrial sectors given that it makes it possible to treat complex effluents. It is a technique that, together with vacuum evaporation, are among the few technologies that make it possible to treat saline and briny effluents without producing, if necessary, a discharge flow, given that the separation is not limited by the equilibrium.
However, membrane distillation it still not a technology with high energy efficiency due to the heat loss resulting from the conductivity of the membrane. As such, its application is restricted to those applications in which conventional distillation or vacuum evaporation are not viable alternatives, as is the case when wishing to concentrate acids or corrosive substances.
As a standard result, reverse osmosis returns 80% purified water and 20% rejection.
There are four main types of traditional modules (1-4). To To resolve the most common problem of the membranes which is the sealing caused by the residue layers that accumulate on the surface of the membrane during the filtration process, vibratory membranes VR were developed some time ago (5):
This is the simplest configuration, consisting of two end plates, the flat sheet membrane, and spacers. In tubular modules, the membrane is often on the inside of a tube, and the feed solution is pumped through the tube.
2. SPIRAL WOUND
The most popular module in industry for nanofiltration or reverse osmosis membranes is the spiral wound module. This module has a flat sheet membrane wrapped around a perforated permeate collection tube. The feed flows on one side of the membrane. Permeate is collected on the other side of the membrane and spirals in towards the centre collection tube.
3. HOLLOW FINE FIBRES
Hollow fibre modules used for seawater desalination consist of bundles of hollow fibres in a pressure vessel. They can have a shell-side feed configuration where the feed passes along the outside of the fibres and exits the fibre ends. Hollow fibre modules can also be used in a bore-side feed configuration where the feed is circulated through the fibres. Hollow fibres employed for wastewater treatment and in membrane bioreactors are not always used in pressure vessels. Bundles of fibres can be suspended in the feed solution and the permeate is collected from one end of the fibres.
4. TUBULAR MEMBRANES
Porous tubes with inner diameters ranging from 5mm to 15mm are coated with micro-porous layers of PVDF or PES on either the inside or outside walls. Depending on the orientation of the micro-porous layer, tubular modules – consisting of individual tubular membranes fitted into a cylindrical housing – are either operated in outside-in (waste water stream flowing outside individual tubes) or inside-out (waste water stream flowing inside individual tubes) configurations.
5. VIBRATORY MEMBRANES
The big difference compared to traditional membranes is that the basic design is vertical instead of horizontal, which means that the space required per unit is less than for other separation systems.
These vibrating membranes are capable of filtering any type of wastewater and can treat effluents with a high load of solids. In addition, it is a technology that does not require chemicals for operation, apart from those that are necessary for periodic cleaning of the membrane.
In a VR Membranes system, the liquid to be treated is almost immobile, circulating slowly between the elements of the parallel membranes. The cleaning action of the shear is created by vigorously vibrating the elements of the membrane in tangential direction to the surface of the membranes. The shear waves produced by the vibration of the membrane, mean that the solids are made to rise to the surface of the membrane and that they are once again mixed with the material or effluent that moves inside the membrane. This intense shear allows the pores of the membrane to be cleaner, achieving a higher performance than conventional membranes.
Vibratory membranes allow you to recuperate around 90% of the treated water as clean water that can be emptied or reused.
The type of membrane that is used in VR systems varies depending on the effluent to be treated. A very general classification would be as follows:
- Reverse osmosis membranes for the separation of materials.
- Nanofiltration membranes for the treatment of wastewater and for concentration.
- Ultrafiltration membranes for oil separation and concentration.
- Microfiltration membranes to separate the biggest particles from a liquid phase.
Other important parameters are pressure, temperature, amplitude of the vibration and the time of residence of the material inside the membrane.
All of these parameters are optimized during initial tests and are then recorded in a PLC that controls the system automatically.
In addition to all of this, it must be added that this is a modular system that can be modified after installation, should it be necessary:
- It can be added easily to an existing system to improve the performance.
- It can be installed in areas where space is limited.
- It is easy to transport and can be moved from one plant to another.
- It can be installed in multiple systems or phases as a single step.
- More units can be added in accordance with the increase in production.