Patent Application
20110096618
The present invention relates to a method and apparatus for aerating or oxygenating a liquid. In particular, the present invention relates to a method and apparatus for aerating or oxygenating a liquid for example but not limited to wastewaters and more particularly for the treatment of wastewaters by a biological process.
Biological processes are often used for the removal of Chemical Oxygen Demand (COD) and other nutrients such as ammonia and phosphate from wastewaters. The efficiency of such processes is usually limited by the rates at which oxygen may be transferred to the micro-organisms present in the wastewaters.
For example, in the treatment of sewage by the so-called activated sludge process, the energy used to provide the oxygen by aeration accounts for over half of the energy consumption of the treatment plant.
Two of the most commonly used methods of aeration are:
(i) the use of surface aerators; and
(ii) membrane diffusers.
Surface aerators are low cost but operate with an aeration efficiency of only 1.0-1.5 kg O2/kWh in activated sludge applications. On the other hand, membrane diffusers are more costly but have better efficiency with values at 1.5-2.0 kg O2/KWh. However, in terms of energy usage, such values still represent less than 15% energy efficiency.
It is desirable to obtain as high a rate of oxygen transfer to the wastewater whilst using as little energy as possible.
Many attempts have been made to try and improve the efficiency of the aeration process. For example, Hines et al (U.S. Pat. No. 4,253,949) describes a sewage treatment apparatus wherein, the sewage containing dissolved air is circulated around a system comprising a down-corner and a riser. Part of the mixture in the riser is introduced into a flotation chamber in which the hydrostatic pressure gradually decreases as the mixture flows upwards, with consequent release from solution of air bubbles that carry the micro-organisms to the top of the mixture.
The devices of the invention taught by Hines et al, are commonly known as air-lift reactors and they have been used predominantly for fermentation processes such as the ICI™ single cell protein production.
Nonetheless, a number of systems known as “deep shaft” reactors use such processes for wastewater treatment. The aeration efficiency of ‘deep shaft’ processes is of the order of 5-8 kg O2/kWh.
Following the original development of the deep shaft reactor technology, there have been other improvements in long vertical shaft reactor systems for wastewater treatment. For example, U.S. Pat. No. 4,466,928 (Kos) discloses a system that includes an apparatus for dissolving gas in the liquid.
The apparatus comprises an inlet for introducing a liquid into the apparatus, means for injecting a gas into the apparatus to produce a gas-liquid mixture, a contact chamber for maintaining the mixture at elevated pressure, a flow distributor at the upper end of the contact chamber having a plurality of nozzles extending in a downstream direction forming an upper gas trap, the contact chamber being of essentially uniform cross-section so that a constant velocity of the gas-liquid mixture is maintained therein. A gas disengagement chamber at the lower end of the contact chamber forming a lower gas trap, a recycle conduit external to the lower gas trap so that the gas in lower gas trap is injected into said upper gas trap by the differential pressure for further dissolution in the liquid, and an outlet to permit the treated liquid to exit the disengagement chamber. The Kos systems are more suitable for use with pure oxygen and are not suitable for use with air as would be the case with the invention of Hines et al.
Despite their substantially improved oxygen transfer efficiencies, the processes of Kos and Hines et al. have not achieved significant commercial success due to the inherent problem of constructing such a large reactor, and moreover such a large reactor which is substantially deep underground. The operation of these processes also requires high-pressure gas compressors to enable gas injection to take place at great depths, with the associated problems of installation and high running costs.
A more recent development in aerating methodology has been disclosed by Dyson (U.S. Pat. No. 7,121,534). The Dyson method involves passing a liquid to be aerated down a surface in the presence of air and into standing liquid. The surface has at least one change in gradient to provide a surface for the development of turbulence that is essential in drawing air into the liquid.
According to Dyson, one side of the flowing liquid must be bounded by a wall of a column that extends into the standing liquid and the other side of the liquid is bounded by an interface with air that occupies the rest of the column such that gas is drawn into the standing liquid. The movement of the liquid over the surface of the column is such as to generate turbulence in the liquid that is passed along a plane surface of progressively increasing gradient for at least part of its downward flow into the standing liquid. The method of Dyson is both simple and elegant. It has few moving parts and is very economical to construct. However, with a claimed aeration efficiency of only 1.5-2.5 kg O2/KWh, it has not been successful in displacing the more traditional aeration methods in wastewater treatment. The poor energy efficiency of the Dyson method arises from the fact that the liquid has to be raised by about 0.5 m above the standing liquid to achieve flow and the turbulence necessary for the generation of the air bubbles.
It is therefore the aim of the present invention to provide an improved method for aerating a liquid that overcomes the disadvantages of current methods as described above.
It is a further aim of the present invention is provide an improved apparatus for aerating a liquid, that is of higher efficiency and more economical to construct than the currently available apparatus as described above.
Therefore, according to a first aspect of the present invention there is provided:
In accordance with a second aspect of the present invention there is provided an apparatus suitable for use in aerating a liquid in a reactor, the apparatus comprising:
In the method according to the first aspect of the present invention the liquid velocity is preferably in the range of 5 cm/s to 100 cm/s, more preferably in the range of 20 cm/s to 75 cm/s.
It is also preferred that the contact period is preferably in the range of 5 seconds to 500 seconds, more preferably, in the range of 10 seconds to 300 seconds.
In accordance with the method the size range of the air bubbles is preferably 0.2 to 5.0 mm in diameter.
The air bubbles are preferably generated within 50 cm of the liquid surface. More preferably, the air bubbles are preferably generated within 5 cm of the liquid surface.
According to the present invention the hydrostatic pressure is preferably defined by the product of the down flow liquid velocity and the air liquid contact period in the vertical pipe.
That is:
HM=(down flow liquid velocity)×(air liquid contact period)
wherein:
It should be noted that the actual contact time between the bubbles and the liquid is not a fixed quantity as it depends on the size of the bubbles which would have a distribution.
The bubbles generated according to the present invention preferably comprise oxygen-enriched air.
The air-water mixture of the method preferably comprises 3 to 30% air by volume under normal atmospheric conditions. More preferably the air-water mixture comprises 5 to 25% air by volume under normal atmospheric condition.
In a first embodiment of the second aspect of the present invention suitable for use but not limited to a high-pressure arrangement, the length of vertical pipe is preferably in the range 1 metre to 100 metres, more preferably in the range 2 metres to 90 metres. Even more preferably the length of the length of vertical pipe is preferably in the range 10 metres to 90 metres and most preferably the length of vertical pipe is in the range 25 metres to 75 metres.
In an alternative embodiment of the second aspect of the present invention for use in for example but not limited to a low-pressure arrangement, the length of vertical pipe is preferably in the range 1 metre to 10 metres. More preferably, the length of vertical pipe is preferably in the range 2 metres to 6 metres.
In accordance with the second aspect of the present invention the position of the vertical pipe may be varied. For example, the vertical pipe may be completely submerged within the reactor. Alternatively, the vertical pipe may be disposed completely on the outside the reactor.
It is also possible for a bottom portion of the vertical pipe to be disposed underneath the reactor.
The bubbles generated during the method according to a first aspect of the present invention or in the apparatus according to a second aspect of the present invention are preferably generated by a means selected from the group comprising: overflow weirs, rotating impellers, membrane diffusers, coarse diffusers and nozzles in conjunction with air blowers or compressors.
The means for drawing the liquid down the pipe preferably comprises a liquid moving device such as for example but not limited to one or more marine impellers or helical screws.
It should be understood that the term liquid refers to any wastewater, sludge or fermentation media that is to be treated biologically. The terms air or gas refer to any gaseous medium containing some oxygen or complete oxygen.
Air contains about 20% oxygen and has a density of 1.3 kg/m3 under normal atmospheric condition. Also under normal atmospheric conditions water can become saturated at a concentration of 10 g O2/m3 water. This means that 38.5 litres (L) of air would contain enough oxygen to cause saturation in a cubic metre of water under normal atmospheric condition. The air/water ratio at the oxygen saturation point is therefore 3.7% by volume and by introducing more air bubbles into the water any excess air would represent waste energy. According to Henry's law, the solubility of a gas in water is proportional to the gas pressure. Thus, it should be possible to raise the saturation concentration by increasing the air water contact pressure.
It has been found that it is possible to generate an air water mixture of about 20-30% by volume under normal atmospheric conditions. Mixtures with a greater proportion of air are not stable because the bubbles would coalesce rapidly. An air water mixture of 25% would contain enough oxygen to produce a saturation concentration of 86 g O2/m3 water. However, such a saturation level would require an air water contact pressure of 8.6 atmospheres according to Henry's law. The prior art, for example Hines et al, suggests that a contact pressure of 8.6 atmospheres could be achieved by injecting air at 8.6 atmospheres into a liquid column at a depth of 86 m. However, as already mentioned injection of air to such a depth would require a very high energy level.
The air bubbles may be generated by any known means. For example air bubbles may be produced by passing a liquid over a weir, blowing air through a membrane diffuser or by agitating the surface of a liquid with a mechanical device such as an impeller. It has been found that these surface bubbles are mostly in the size range of 0.2-5 mm diameter for an air water system and surprisingly they require very little energy to generate.
Air bubbles in a liquid have a tendency to rise and would accelerate to a steady state velocity known as the terminal velocity. It has been found that in order to overcome the bubble terminal velocity and to entrain the mentioned surface bubbles, the liquid must be induced to flow at a minimum velocity of 5 cm/s. A more suitable velocity would be in the range 10 to 100 cm/s. Preferably the liquid velocity should be in the range 20 cm/s to 75 cm/s. The air water contact time is determined by the liquid velocity and the length of the vertical pipe. For example, if the pipe length is 100 m and the liquid velocity is 50 cm/s the contact time would be 200 seconds. At such a depth a contact time of 200 seconds is adequate to achieve oxygen saturation.
It has been discovered that the mentioned surface air bubbles can be entrained by a liquid as it flows vertically down a pipe and surprisingly as the air bubbles are taken to a greater depth more oxygen is dissolved by the increasing hydrostatic pressure. Importantly it has been found that high levels of dissolved oxygen, as much as 86 g O2/m3 water can be achieved without the need for air or oxygen injection at high pressure.
For a better understanding of the present invention and to show more dearly how it may be carried into effect, the invention will now be described in further details with reference to and by way of example only, to the accompanying examples and drawings in which:
FIG. 1—is a diagrammatic sketch of an apparatus according, to the first embodiment of the present invention; and
FIG. 2—is a diagrammatic sketch of an apparatus according to the second embodiment of the present invention.
Referring to
As the liquid is drawn down the vertical pipe it leaves a void in the bell mouth that becomes a weir as more water falls over its edge to fill the void and thus create a high density of surface bubbles within the bell mouth. Bubbles that are small enough are entrained and carried by the liquid flow and dissolve in the liquid as they move towards the bottom of the pipe where the hydrostatic pressure is greatest. Larger bubbles rise back to the liquid surface where they are broken to smaller sizes by the forces of the falling water.
The first embodiment of the present invention is suitable for air liquid contact at pressures of up to 6 m of hydrostatic head. Alternatively, if required, air liquid contact pressure up to 100 m of hydrostatic head may be achieved, as illustrated in
Referring to
The apparatus comprises a reactor 1 for storing a liquid to be treated, a vertical pipe 2 suspended in reactor 1 and extending through the bottom of the reactor 1 deep into the underground below, a surface agitator as a means for bubble generation 3, means for inducing flow 4, and a concentric pipe 5 enclosing the first vertical pipe 2 as a means for returning aerated liquid back to the reactor 1.
In the case of the second embodiment of the present invention, the liquid flow is induced by a suction pressure that is drawn on the liquid return line.
A person skilled in the art will appreciate that most of the energy used in the operation of the present invention is expended in inducing the liquid flow. There are many types of known devices in use for inducing liquid flow but it is important to select the most energy efficient device that is appropriate for this application. It has been found that the most suitable type of flow inducer for the present invention is the marine impeller of the type commonly used for propelling ships and boats
Alternatively helical screw type devices are also suitable. It should be noted that the flow of liquid also serves another important function in providing effective mixing of the contents of the reactor. In most situations, the return flow from the apparatus of the present invention provides the necessary mixing and distribution of the aerated liquid throughout the reactor without any further energy input.
It will be appreciated that many modifications and enhancements may be made to the basic treatment system outlined herein. For instance, the methods of pumping the liquid and of agitating the liquid may be varied. The total number of reactors can vary to suite any particular application, as can the relative size of the reactor to the size of the aerator. The aerated liquid may also be used for applications other than biological treatment, for example but not limited to the dissolved air flotation for solid liquid separation.
Other possible modifications or applications will be readily apparent to the appropriately skilled person.
A sewage treatment plant operating a conventional activated sludge process was equipped with an aerator as illustrated by
The aerator in example 1 was replaced with an aerator as illustrated by
| Number | Date | Country | Kind |
|---|---|---|---|
| 0715909.8 | Aug 2007 | GB | national |
| Filing Document | Filing Date | Country | Kind | 371c Date |
|---|---|---|---|---|
| PCT/GB08/02497 | 7/8/2008 | WO | 00 | 2/12/2010 |
