Automatic condensed oil remover

Information

  • Patent Grant
  • 6527821
  • Patent Number
    6,527,821
  • Date Filed
    Thursday, February 28, 2002
    22 years ago
  • Date Issued
    Tuesday, March 4, 2003
    21 years ago
Abstract
An automatic condensed oil remover for an intercooler of a diesel engine has a flow restrictor that is positioned between the intercooler and the diesel engine, an oil sump in the intercooler, and an oil tube carrying condensed oil from the oil sump to the diesel engine. The flow restrictor creates a pressure drop sufficient to force the oil to flow from the oil sump through the oil tube to the diesel engine.
Description




BACKGROUND OF THE INVENTION




This invention relates to droplet aerosol collection by electrostatic precipitation, and methods that improve efficiency for particle collection. The improvements include one or more of the use of multiple, thin wire discharge electrodes; the use of a conductive porous medium as a collecting surface; the use of high voltage electrostatic shield to prevent particle deposition on the insulator for the components; and the use of heated insulator to prevent vapor condensation and particle deposition by thermophoresis.




Electrostatic precipitation is one of the most widely used methods for removing suspended particulate matter from a gas for gas cleaning or air pollution control. In comparison with other particulate collecting devices, such as cyclones, wet scrubbers, filters, and the like, an electrostatic precipitator has the advantage of low pressure drop, high collection efficiency and requiring relatively small amounts of electrical power for its operation. The low pressure drop


6


f the electrostatic precipitator makes the device most advantageous with large volumetric flow rates of the gas flow needing treatment. Electrostatic precipitation have been used extensively for large scale industrial applications, such as removing fly ash from power plants, controlling particulate emission from smelters, steel and cement making and other similar industries, and general purpose air cleaning for building ventilation. A typical electrostatic precipitator may operate at several hundred cubic feet per minute of flow in small systems, to several million cubic feet per minute for large industrial installations.




The first laboratory demonstration of electrostatic precipitation was made by Hohifeld in 1824, according to credible sources. The first U.S. patent on electrostatic precipitation was issued to Walker in 1886 as U.S. Pat. No. 342,548. Numerous other electrostatic precipitator patents have been issued over the years. Those considered the most significant include U.S. Pat. No. 895,729 to Cottrell on the use of rectified alternating current for electrostatic precipitation, and the invention of the liquid film precipitator by Bums as shown in patent U.S. Pat. No. 1,298,088; the fine wire electrode and two-stage precipitation system of Schmidt, U.S. Pat. No. 1,329,285; the low-ozone air-cleaning precipitator of Penney U.S. Pat. No. 2,000,654; and pulse energizing of precipitators disclosed in U.S. Pat. No. 2,509,548 to White, among others.




The fundamental design of the electrostatic precipitator has remained relatively unchanged over the years. In its simplest form for a single stage precipitator, a high voltage electrode is placed in the center of a grounded tube. A high DC voltage on the small diameter center electrode causes a corona discharge to develop between the electrode and the interior surface of the tube. As the gas containing suspended particles flows between the electrode and the wall of the tube, the particles are electrically charged by the corona ions. The charged particles are then precipitated electrostatically by the electric field onto the interior surface of the collecting tube.




One disadvantage of the electrostatic precipitator is its relatively large physical size. According to Deutsch (W. Deutsch, Ann. der Physik, Volume 68, p. 335, 1922), the basic equation governing the operation of the electrostatic precipitator is:






η=1


−e




−A w/Q








The Deutsch equation relates the precipitator collection efficiency, η, to the collecting area of the precipitator, A, the volumetric flow rate, Q, through the precipitator, and the electrical migration velocity, w, of the particles is the constant, 2.718, the base of natural logarithms. For a specific application, the collecting area of the precipitator, A, is determined when the required volumetric gas flow rate, Q, is known. To reduce the overall physical size of the precipitator, closely spaced precipitating plates can be used. However, there is a limit on this approach to reducing physical size. When the resulting physical size of the precipitator is still too large for the application, an electrostatic precipitator is then considered unfeasible.




Several applications have developed in recent years where a significant reduction in the overall physical size of the electrostatic precipitator is needed. One application is the removal of the suspended particulate matter from the blowby gas from a Diesel engine. In Diesel engines, the high temperature, high pressure combustion gas in the engine cylinder has a tendency to leak past the piston rings into the crankcase. This is usually referred to as the blowby gas. This blowby gas contains lubricating oil droplets from the lubricating oil films atomized by the highs velocity blowby gas flowing from the high pressure cylinder into the crankcase. It also contains Diesel exhaust particulates, which result from the incomplete combustion of the Diesel fuel in the engine cylinder. The amount of blowby gas is relatively small for new engines, but will increase over time as the engines age, and the piston rings no longer provides a good seal. This blowby gas usually has a flow rate of few cubic feet per minute to perhaps as high as 20 cfm for engines in good operating condition.




The Diesel blowby gas is currently being exhausted directly into the atmosphere. In order to protect the environment, there is a need to remove suspended oil droplets and Diesel exhaust particulates in the blowby gas so that the blowby gas can be returned to the fresh air intake side of the Diesel engine for further combustion. This “blowby gas recirculation system” is practical only when the suspended particulate matter is removed to avoid contaminating the components and equipment located on the air intake side of the Diesel engine. One such component is the turbo charger or compressor used to supercharge the Diesel engine to increase its power output and efficiency.




For application in the blowby gas recirculation system, the electrostatic precipitator must be compact and reliable. It is also desirable that the operating voltage of the precipitator be relatively low so that very a high supply voltage is not needed.




Another application for an electrostatic precipitator that is reduced in size from existing precipitators is for removing suspended oil and grease particles in the exhaust gas from commercial kitchens, including kitchens in fast-food, as well as conventional, restaurants.




A third application of an electrostatic precipitator of reduced size is to remove cutting fluid droplets from the machine shop environment. During machining of metal parts, a cutting fluid is usually directed at the tool and the parts being machined to provide cooling as well as lubrication. Some of this cutting fluid is aerosolized to form small droplets by the higher speed rotary cutting tool. This cutting fluid aerosol presents a heath hazard to the workers and must be filtered to remove the suspended droplets. Conventional fibrous filters are not suitable for this application, because the collected droplets tend to clog the filter and produce excessive pressure drop in a short time. The inherent advantage of the small compact physical size and the inherent flame arresting properties of the precipitator of the present invention makes it particularly suited for these applications.




It should be noted the term “compact size” is used here in a relative sense to indicate that the size of the precipitator designed on the basis of this invention is smaller or more compact in comparison with electrostatic precipitators of a conventional design at the same flow rate and at the same efficiency level. By necessity, as a diesel blowby particle collector, the electrostatic precipitator must be sufficiently small to fit under the hood of a truck powered by a diesel engine. The overall volume of the collector must be no more than a few liters, preferably below two liters. On the other hand, an electrostatic precipitator designed for kitchen exhaust applications will need to be considerably larger because of the high flow rate of the exhaust gas to be treated. Such a collector can also be called compact even though the collector is several cubic feet in total volume so long as the collector of the conventional design is even larger, perhaps by as much as 50 or 100%.




SUMMARY OF THE INVENTION




The present invention is an electrostatic precipitator that has improved operating efficiency while being smaller in physical size than existing devices that handle similar flow rates. The present device uses multiple electrical wire discharge electrodes which permit reducing the length of the precipitator. An electrically conductive porous medium is preferably used as the collecting surface. A further aspect of the invention is an electrostatic shield used to reduce or prevent particle deposition on the insulators for high voltage components. A further aspect of the invention is use of heated electrodes which prevent vapor condensation and also prevent particle deposition by thermophoresis.




All aspects of the invention cooperate to increase efficiency and reduce physical size for a given flow rate. These improvements have made it possible to significantly reduce the overall physical size of the precipitator. The small, compact physical size has in turn made it practical to use electrostatic particle collection for the above applications where small physical size is important. Treating diesel blowby exhaust to remove suspended oil droplets and particulate matter permits the blowby exhaust gas to be discharged to the ambient with minimal amount of particulate air pollutant, or to be returned to the air intake side of the diesel engine for exhaust gas recirculation. When used to remove oil and grease particles contained in the exhaust of commercial kitchens the organic particulate matter will be removed. Another application is collecting droplet aerosols of cutting-fluid in machine shops where sprayed liquids enter the atmosphere.




While the present invention was primarily developed for applications such as those described above, the small compact size of the new precipitator makes the device suitable for a variety of other applications, even in those cases where small physical dimensions are not a primary requirement.




For the purpose of this disclosure, Aerosol is defined as small particles suspended in a gas. The particles can be a solid, a liquid, or a mixture of both. The particle size can range from approximately 0.001 μm to 100 μm, with 0.01 μm to 20 μm being the size range of the greatest interest. For the present application, most of the mass of aerosol particles to be collected is concentrated in the latter size range. Droplet aerosol is defined as an aerosol in which the suspended particles are primarily in a droplet form and having a spherical shape. However, the liquid droplets need not be a pure liquid, and may contain suspended solid particles within each droplet.











BRIEF DESCRIPTION OF THE DRAWINGS





FIG. 1

is a schematic cross sectional view of a compact electrostatic precipitator made according to the.,present invention;





FIG. 2

is a sectional view taken on horizontal line


2





2


in

FIG. 1

;





FIG. 3A

is a schematic sectional view of a modified form of the electrode support and high voltage shield used with the precipitator of

FIG. 1

;





FIG. 3B

is a further modified form of a electrode support and high voltage shield used with the precipitator of

FIG. 1

;





FIG. 4

is a transverse sectional view of a precipitator made according to the present invention but having a rectangular configuration;





FIG. 5

is a schematic representation of an ultrasonic generator used for introducing aerosols into the electrostatic precipitator in the present invention;





FIG. 6

is a cross sectional view of a modified compact precipitator using a different style of electrode assembly from that shown in

FIG. 1

;





FIG. 7

is sectional view taken on line


7





7


in

FIG. 6

;





FIG. 8

is a sectional view of a still further modified form of a electrostatic precipitator of the compact electrostatic precipitator of the present invention;





FIG. 9

is a sectional view taken on the line


9





9


in

FIG. 8

;





FIG. 10

is a schematic block diagram of a blowby gas recirculation system used in a diesel engine;





FIG. 10A

is a modified recirculation system similar to that shown in

FIG. 10

;





FIG. 11

is a further modified block diagram of a blowby gas recirculation system used in a diesel engine;





FIG. 12

is a block diagram similar to

FIG. 11

with a controlled flow restrictor on the outlet of the intercooler;





FIG. 13

is a cross sectional view of a modified support for the electrode wire;





FIG. 14

is a vertical sectional view of a further modified compact electrostatic precipitator;





FIG. 15

is a sectional view taken on line


15





15


in

FIG. 14

;





FIG. 16

is a cross sectional view of a modified support for the electrode wire as it would be taken along the line


15





15


of

FIG. 14

;





FIG. 17

is a cross sectional view of a modified support for the electrode wire as would be taken along the line


17





17


of

FIG. 14

; and





FIG. 18

is a flat layout of a cylindrical electrode support unrolled to a flat surface to reveal a modified pattern for the electrode wire supported on the electrode surface.











DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS





FIG. 1

is a schematic cross sectional view of an electrostatic precipitator


10


made according to the present invention. A housing


12


has a discharging electrode assembly


14


to produce the corona discharge. The high voltage DC power supply


16


applies a high voltage (several thousand volts), to the electrode assembly


14


on a wire surrounded by an insulator bushing


18


. The bushing


18


is surrounded by a high voltage shield


20


, made of suitable conducting material.




An electric heater


22


is in contact with the insulator bushing


18


to keep the insulator bushing at a sufficiently high temperature to prevent vapor condensation and particle deposition on the bushing


18


.




Gas containing suspended droplets and other particulate matter from a source


23


is directed to flow through an inlet opening


24


of the housing


12


and passes through a porous medium


26


in the inlet. The porous medium


26


is a relatively inefficient droplet collector to keep out large contaminants, so that most of the droplets in the aerosol are carried by the gas into the electrostatic electrode region or chamber


28


above.




The input gas then flows around the electrode assembly


14


to expose the droplet particles in the gas to the high electric field around the electrode assembly. The discharge electrode assembly


14


includes a central rigid support


30


for two support discs


32


and


34


on opposite ends of the central support. The upper disc


32


may be attached to the insulator bushing


18


and thus support the discs


32


and


24


from the housing


12


. A plurality of holes


35


(see

FIG. 2

) are formed in each disc


32


and


34


and a fine metal wire,


36


is strung between them. The sectional view

FIG. 2

, through the compact electrostatic precipitator electrode


14


shows there are eight holes in each of the support discs. A fine metal wire


36


is threaded through the holes to form eight straight, parallel discharge electrodes


36


. By way of example, if the distance between the two support discs is 8 inches, the fine wire electrode


36


extending between them will each be 8 inches in length for a total discharge electrode length of 64 inches. More holes can be used in the support discs


32


and


34


to create more discharge electrodes, or fewer holes can be used if less length of the discharge electrodes is needed. With the above mentioned distance of 8 inches between the support disks, an electrode circle diameter of 3 inches, the diameter of the housing


12


is approximately 5 inches, and its length, approximately 10 inches. Using the conventional design of a single discharge electrode in the center of a tube, the total length of the electrostatic precipitator is more than 64 inches. The advantage of the present electrode design in reducing the size of the precipitator and making it compact over the conventional design thus becomes obvious.




The gas (aerosol) flows around the wires


36


and ions are produced in the corona discharge. The ions collide with the droplets to cause the droplets to be charged. The charged droplets are then carried by the gas flow through an electrically conducting, grounded porous medium


40


as the gas flows to an outlet


42


. The droplets are collected by electrostatic precipitation onto the grounded collecting elements in the medium.




The clean gas then flows out of the annular space


41


between the porous medium


40


and the outer housing


12


to the outlet


42


. The collected oil droplets flow down the inside surface of the porous medium


40


as a thin film which is returned by gravity to an oil reservoir or sump


44


.




As shown in

FIG. 1

, all parts of the system are grounded except for the high voltage electrode assembly and the high voltage shield


20


.




Using a thin wire of a uniform diameter in the above electrode arrangement, and in other embodiments disclosed, it is important to keep the distance between each wire segment and the adjacent collector electrode the same for all the wire segments on the support structure. By keeping the distance uniform and using the same high voltage potential on all the wire segments, a uniform corona discharge can be maintained. This will insure that all particles flowing through the device will be charged uniformly and to the same maximum possible extent to insure high collection efficiency for the device.




In designing an electrostatic precipitator using the above electrode assembly, the spacing, S, between the wire segments must bear a proper relationship to the distance, D, between the wire segment and the adjacent collector electrode surface. (see FIG.


2


). Too small a spacing, S, will cause the closely spaced wire segments to interfere with each other, thereby reducing the maximum current that can be obtained from each wire. Too large a spacing will cause some empty spots on the collector electrode surface to appear. Within these empty spots, there are no corona current flow. Particles flowing over these empty spots will not encounter corona ions and thus remain uncharged. From experience, it has been found that the ratio, S/D, must be kept between the limits of 0.1 and 10, preferably between 0.3 and 3, for the electrode assembly to function properly and avoid-degradation in performance.




For application in a Diesel blowby gas recirculation system, the inlet housing


24


is connected to an opening in the crankcase, which is represented at


23


, and the collected oil film is also returned directly to the crankcase. The outlet


42


can be open to the atmosphere to allow the cleaned blowby gas to be discharged to the atmosphere, or the outlet


42


can be connected to the intake of the Diesel engine for exhaust gas recirculation.




The total discharge electrode length is greatly increased from that of the conventional precipitator with a single discharge electrode in the center of a tube. The corona current that can be maintained between the discharge electrode and the collecting tube is generally proportional to the total electrode length. The approach described here makes it possible to greatly increase the electrode length and hence the total corona current, thereby increasing the efficiency for both droplet particle charging and precipitation of the charged droplets or particles. A laboratory prototype device has demonstrated the practicality of this approach. As many as sixteen discharge electrodes have been used leading to approximately a factor of sixteen increase in total corona current in laboratory prototypes.




Another purpose of the electrode design shown is to allow the discharge electrode to be circumferentially supported on a circle. A large diameter circle of the electrode length mounting will bring the discharge electrodes (the wires) closer to the porous medium


40


collecting surface, thereby reducing the voltage needed to maintain the corona discharge between the electrode and the grounded porous collecting surface. A lower operating voltage from existing precipitators is desirable for the applications described above, to reduce the need for very high voltage insulation. When using a lower voltage, the leakage current through the insulator bushing


18


can be reduced. Using a lower voltage also reduces the cost and complexity of the power supply


16


, thus making the device more economical to produce. In the present device, voltages of between 5,000 to 10,000 volts are most preferred, but voltages up to 20,000, volts DC can be used.




Using a circle of electrode lengths spaced from the center rod also forces the gas flowing radially outward toward the porous collecting surface to be exposed to the very high electric field surrounding each discharge electrode. Generally, the electric field strength according to Gauss's law tends to decrease with increasing distance from the discharge electrode. The closely spaced wires forming the discharge electrodes forces the gas to pass through the high field region between the electrodes and to be exposed to the high electric field around the wires. Each droplet or particle can thus be charged to a higher level than is possible with the conventional single length electrode design, thereby gaining a higher electrical charge and allowing droplets to be more easily removed by electrostatic precipitation.




Although a porous collector electrode


40


is shown in

FIG. 1

as the collector electrode, the basic design of the discharge electrode assembly


14


works well also when the collector electrode is made of a solid conducting material, in which case the housing


12


itself can be the collector. The oil droplets will be collected on the interior surface of the housing walls. The collected oil droplets will then flow down the walls and be returned to the oil sump or the crankcase of the diesel engine, eliminating the porous collector electrode will make the device less efficient, but the overall size, the complexity, and the cost of the device will also be reduced.




The high-voltage insulator bushing


18


, if unprotected, will be exposed to the suspended droplets or particles in the gas, as well as any condensable vapor which may be present. Over time, the accumulation of deposited and condensed material on the insulator will render it ineffective. The insulator is heated by contact with the electrical heating element


22


to a high enough temperature to prevent vapor condensation on the insulator bushing.




To prevent the precipitation of droplets or particles on the insulator bushing surface, a conductive shroud or shield


20


surrounds the insulator. This conductive shroud


20


is connected to the same high voltage source as the discharge electrodes


36


so that a high electric field is created in the region between the shroud and the nearby grounded surfaces of the porous medium


40


or housing


12


. The charged droplets or particles present in the gas will thus be precipitated onto the grounded surfaces and not on the high voltage insulation bushing.




Design variations of conductive shroud


20


are shown in

FIGS. 3A and 3B

. By using a small gap spacing between the bottom plate of the shield or shroud and the nearby grounded surface, a high electric field can be created in this gap space to also precipitate droplets or particles in the gas.




In

FIG. 3A

, the modified high voltage shield as indicated at


50


, and as shown has a base plate


50


A, and the surrounding wall


50


B that surrounds the insulator bushing


18


. The grounded housing


12


has a cap portion


52


that comes up from a top wall


54


and defines an opening near the upper end of the insulator


18


, as shown. The surrounding wall


5


OB is spaced from the wall over cap


52


, and terminates short of the upper end wall of the cap. Thus there is a gap shown at


56


between the shield wall


50


B and the housing wall


52


around the insulator. The support shown at


56


supports a top plate


32


of the electrode assembly. The central support and the lower electrode plate


34


can be provided as before.




In

FIG. 3B

, the high voltage shield comprises a flat disc


60


that is fixed to the lower end of the insulator bushing


18


, and the insulator bushing


18


in this case is also surrounded by a sleeve or cap


62


of the housing, which is grounded.




The top wall


64


of the housing is spaced from the plate


60


, to form a gap


66


between the housing wall


64


, which is a top wall, and the plate


60


which is a shielding disc. The support


68


can be used for supporting a top plate


32


of the electrode assembly as before.




Each of these forms of conductive shroud shows a gap between the high voltage shield or shroud and a portion of the grounded housing. The gap is relatively narrow, and will provide for precipitation of charged particles that come near the high voltage shield, to the walls of the grounded housing.




Creating a long pathway in the gap space as shown in

FIG. 3A and 3B

, the charged droplets or particles in the gas can be efficiency precipitated in the regions surrounding the insulator bushing


18


to provide improved protection of the high voltage insulator from particulate contamination.




In spite of the efficient high voltage insulator shield design of this invention, there is the possibility that some droplets or particles in the gas may remain uncharged. These uncharged particles, will be capable of penetrating through the gap space


56


or


66


between the shroud and the nearby grounded surface to deposit on the insulator. The precipitation of these uncharged particles on the insulator can be prevented by utilizing the phenomena of thermophoresis.




Thermophoresis refers to the movement of aerosol particles in the direction of a decreasing temperature gradient due to the radiometric force acting on the particles. For effective thermophoretic motion of the particles to prevent particle precipitation on the insulator the insulator must he held at a sufficiently high temperature. The insulator temperature must be 10° C. or more than the surrounding gas temperature. In contrast, to prevent vapor condensation, the insulator only needs to be held above the dew point of the condensable species in the gas. Usually at least a few degree C above the gas temperature would be sufficient




To be effective, the porous medium


40


must be made of a conductive material, usually metal. It can be made of a perforated metal, a porous, sintered metal, one or more layers of wire mesh material rolled into the desired cylindrical shape, a pad of metal fiber or wires formed into a cylinder, and similar configurations. As the gas flows into the porous medium, particles are brought to close proximity to the surface of the conducting elements in the medium, thus allowing the charged particles to be effectively deposited onto the surface of the conducting elements of the porous medium. In comparison, in the conventional electrostatic precipitator using solid collecting electrodes, such as a solid tube surrounding the center electrodes, the charged particles must be precipitated by electrical force through the fluid boundary layer adjacent to the inner surface of the surrounding tube.




Depending on the gas flow velocity, the relatively stagnant boundary layers adjacent to the solid collecting surfaces may be a centimeter or more in thickness. The particles must be precipitated through this centimeter thick stagnant gas layer to be deposited on the surface. In comparison, using a porous collecting electrode, as shown here, the gas is forced to flow between the closely spaced conducting elements in the porous medium, thereby greatly reducing the distance the particles must travel to reach the collecting surface. This will increase the efficiency of the precipitator and reduce the overall physical size of the device.




Not all electrically conducting porous material can be used with the compact electrostatic precipitator described in this invention. In order to handle the high gas flow rate per unit of collecting surface intended for this application, the porous material must not produce excessive pressure drop at the required high gas flow. In addition, the collected oil drops must drained off easily by gravity and not be collected in the porous medium to clog the medium or produce excessive high pressure drops. Depending on the structure of the porous medium, and the surface tension and viscosity of the liquid droplets being collected, the distance between the conducting elements of the porous medium must be kept above a critical limit. Too small a distance will allow the collected droplets to form surface films bridging neighboring elements and block the flow. For the usual liquid such as lubricating oils, the mean distance between the conductive elements in the medium must be larger than about 5 microns, and preferably larger than 10 μm. The mean distance between the elements in a porous medium is also referred to as the mean pore diameter which can be measured by a commercial poremeter. A mean pore diameter greater than 5 μm, preferably greater than 10 μm, is generally necessary for the medium to work successfully as the porous collecting electrode of the droplet collecting precipitator described herein.




There are a number of devices using a porous medium to collect charged particles. One such device is the electrically augmented bag filter described by Penney in U.S. Pat. No. 3,910,779. In Penney's device, the particles are charged in a corona charger. The charged particles are then carried by the gas flow through a fabric medium and deposited on the surface of the fabric. The particles to be deposited must be a dry solid material, so that the deposited particles on the fabric will form a porous cake. Since a cake will also form on the fabric in the absence of an electrical charge, electrostatics charges are used by Penney to modify the property of this cake namely to increase the pore size of the cake and reduce the pressure drop. The textile fabric used in a fabric filter is usually not electrically conductive, so that it is not possible to maintain a corona discharge directly between the corona electrode and the fabric. A separate corona charger is used upstream of the fabric filter to charge the particles for subsequent filtration by the fabric.




Another device using a porous filter media is what is usually referred to as electrostatically enhanced fibrous filter such as that described by Carr in U.S. Pat. No. 3,999,964. A conventional fibrous filter media made of glass, polymeric and other non-conducting fibers is sandwiched between two sets of electrical grids. A potential difference is established between the grids to create an electric field in the medium to enhance the efficiency of the medium for particle collection by electrostatic attraction. The device is most effective when the particles are electrically charged. If the particles are not charged, a corona ionizer can be used upstream of the filter to charge the particles to increase the efficiency of the filter for particle collection.




A further version of the electrostatically enhanced fibrous filter is that of Argo et al in U.S. Pat. No. 4,222,748. In Argo's device, a corona charger is used upstream to charge the particles. As the charged particles are collected in the fiber bed, which is made of a non-conductive material, charge will build up in the bed to raise its electrical potential. To prevent the continuous buildup of charge in the bed, the bed is continuously irrigated by water to make the bed conductive. Particles collected in the bed are also carried away by the flowing water.




The electrostatic precipitator of the present invention is very efficient and can be made into a small compact size. For many applications, such as diesel blowby filtration, the cylindrical geometry with a circular cross section is the most convenient. However, it is not necessary that the cross section shape be a circle to take advantage of many of the features of this invention. Rectangular, elliptical, and other cross sectional shapes can be easily adapted to the design of an electrostatic precipitator described by the method described in the present invention.





FIG. 4

represents a transverse sectional view through a rectangular precipitator. The electrode assembly


72


including a pair of spaced corona wire supports


74


(only one is shown) would be made as before with the two supports


74


spaced along a support rod


76


with wire


77


forming electrodes extending between the supports. The wires


77


are shown in the cross over portions for threading through the holes. A conductive porous medium collecting electrode


78


, surrounds the high voltage electrode assembly


72


, and the porous medium, and the grounded outer housing


79


have a generally rectangular cross-sectional shape.




In designing such a rectangular precipitator, it is important to keep the individual corona wire lengths between the support


74


at approximately the same distance from the porous collecting electrode


78


. This will insure that the corona discharge between the high voltage corona wire


76


and the collecting electrode


78


will be uniform at the same applied voltage on the wires. As before, the lateral distance between the wire lengths and the porous collecting electrode


78


can be reduced to lower the required operating voltage of the precipitator.




Although the precipitator described in this invention is intended for droplet aerosol collection, it can also be used to collect aerosols containing only dry solid particles. To prevent the build up of solid particles in the porous collecting electrode which will cause plugging of the pores, liquid droplets, usually water, can be added to the aerosol before it is introduced into the precipitator.

FIG. 5

shows an ultrasonic droplet generator


80


used in conjunction with an electrostatic precipitator


82


for droplet addition. As aerosol flows from source


84


through the ultrasonic generator


80


, it picks up droplets in the space


86


above an agitated liquid


88


produced by ultrasonic agitation using an ultrasonic transducer


89


. The dry particulate matter will be precipitated along with the added liquid droplets in the precipitator


82


and be carried away by the liquid stream resulting from the collected droplets, thereby preventing the build up of dry solid material on the collecting electrode in the precipitator. Other droplet generating devices, such as compressed air atomizer, bubblers, and the like can also be used. The electrostatic precipitator can be made as shown in any of the forms disclosed




Because of the small droplet size and the large surface area of the droplets produced by ultrasonic agitation or a compressed air atomizer, the combined wet electrostatic precipitator and droplet generator described above will have excellent gas absorptive properties, and can be used as a combined gas and particle scrubber. The combined gas and particle, scrubber will have a variety of applications in air pollution control. For instance, in the semiconductor industry, the exhaust gas from the vacuum pump downstream of a semiconductor process equipment often contains both toxic gases as well as fine particulate matter. One such gas is fluorine, which is used at the end of a process cycle to clean the process chamber. Fluorine is very reactive to water and will be efficiently scrubbed by water droplets in the combined droplet generator and wet electrostatic precipitator. Similarly, various acidic vapors such as hydrogen fluoride (HF) and hydrogen chloride (HCl) can be absorbed by water droplets or by an aqueous solution of KOH and other basic; solutions. By combining a droplet generator with appropriate chemical scrubbing solutions and the wet electrostatic precipitator, a highly efficient combined gas and particle scrubber can be obtained.





FIGS. 6 and 7

show a compact two-stage electrostatic precipitator


98


in which an electrode assembly


100


including a short corona-discharge electrode


102


that is attached to a cylindrical precipitating electrode


104


, and both are held at the same high DC voltage from a voltage or power source


106


. The short corona-discharge electrode


102


has a pair of spaced support discs


108


and


110


held together with a central support


112


. The discs support a fine wire


113


carrying a high voltage to produce a corona-discharge. The cylindrical electrode


104


is a tubular cylinder with a conducting surface. This cylindrical electrode


104


together with the surrounding porous metal media collector


114


form a precipitating region in which the charged particles are precipitated.




In this two-stage design, the relatively short corona wire lengths


113


A forming electrodes produce a corona discharge to charge the droplets or particles moving past the corona-discharge electrode


102


. The short length of electrode


102


reduces the corona output from the wires, hence the required current output from the power source


106


is reduced, in turn reducing its physical size, and cost. The design also makes it possible to vary the radius of the circle of the corona wire lengths


113


A independently from that of the radius of the tubular cylinder electrode


104


. By changing these two radii, both the corona discharge electrode


102


, which is an ionizer, and the precipitating cylinder electrode


104


can be independently optimized, leading to improved overall operation of the system.




The discs


108


and


110


are held together with a central support


112


. The fine wire


113


is threaded between the discs


108


and


110


, and carries the high voltage from the source


106


. The high voltage again is carried by wire through an insulator bushing


118


, which is surrounded by high voltage carrying shield


120


. An end plate


104


A on tube


104


carries the voltages to the tube


104


. The tube


104


in turn is connected to the disc


108


for powering the corona discharge electrode


102


. The flow of gas is from an inlet


116


of housing


12


to an outlet


117


, which discharges clean gas.





FIGS. 8 and 9

show a modified electrode design that can be used with the single-stage and the two-stage precipitators shown in

FIGS. 1 and 6

. In this case, a plurality of support rods


120


are attached to the support discs


122


and


124


to form an assembly. A single corona fine wire


126


is spirally wound around the support rods


120


to extend from one disc to the other, and this forms a plurality of segments of conductive wire carrying current for supporting a corona discharge for charging particle in the droplet aerosol introduced through an inlet


128


. The porous media collector


129


is shown in

FIG. 1

with a coarse filter formed at a bottom panel


130


, and selected porosity on a cylindrical electrically conductive porous side wall media


132


. The cylindrical side wall


132


acts to precipitate charged droplets and particles as previously shown. The cylindrical wall


132


is grounded, as is the housing


12


. An outlet


134


from the housing discharges clean gas. The insulator bushing


18


, heater


22


and voltage source are the same as shown before.




The compact electrostatic precipitator described herein can be used to remove suspended particles in the blowby gas from a diesel engine or other internal combustion engines. The blowby gas with the suspended particulate matter removed can be discharged directly into the atmosphere, or can be recirculated into the engine.

FIGS. 10 and 11

described below are both suitable for use for any electrostatic precipitator, including that of the conventional design.





FIG. 10

shown one arrangement for blowby gas recirculation using an electrostatic precipitator, preferably one made according to the present invention. The diesel engine


135


has a crankcase


136


and blowby gas from the engine crankcase


136


first flows along a passage through an electrostatic precipitator


137


designed as show previously to remove suspended droplets or particles. The clean gas then flows into the inlet section of a T-connector


138


which has a orifice plate


138


A in an outlet section. The gas flows through an orifice


140


in the plate


138


A and into the intake of a turbo charger


142


. The side inlet section


136


D of the T-connector


138


is open to atmosphere.




This T-connector constitutes a crankcase pressure regulating device when an electrostatic precipitator is used to remove particles from the blowby gas for recirculation into the diesel intake. Its operation is as follows. The T-connector


138


inlet


138


B is open to the atmosphere, and thus the outlet of the precipitator


137


is also at atmospheric pressure. The crankcase pressure Pc relative to atmospheric pressure Pa is thus Pc−Pa=ΔP, where ΔP is the pressure drop of the blowby gas through the precipitator


137


. This pressure drop is usually quite low, on the order of a few inches of water or less. The crankcase pressure is thus limited to a few inches of water above atmospheric. In an internal combustion engine, the crankcase pressure must not be allowed to vary by more than a few inches above or below atmospheric to prevent leakage of crankcase oil to the outside, and other operational difficulties. This design makes it possible to achieve crankcase pressure regulation with a simple connection and at low cost.




In a diesel engine using a turbo-charger or turbo-compressor to increase the engine power output, as shown in

FIG. 10

, a filter


144


is used at the air intake of the turbo-charger


142


to remove suspended particles in the ambient air. The pressure drop through


64


the filter


144


causes the pressure Pt at the turbo-charger, intake to be below atmospheric. The diameter of the orifice


140


in the outlet section of the T-connector


138


is chosen such that the pressure drop across the orifice


140


(ΔP=Pa−Pt) is just sufficient to cause the gas flow through the orifice


140


to be the same as the blowby gas flow Q


1


during normal engine operation, and when the engine intake air filter


144


is new. When the intake filter


144


becomes partially clogged, its pressure drop increases. This increases the gas flow through the orifice Q


2


. The difference, Q


3


=Q


2


−Q


1


is made up by the air flow coming from the ambient through the side inlet section


138


B of the T-connector


138


.




Alternatively, as shown in

FIG. 10A

, a modified orifice housing


139


can be made as a straight through flow tube with no side inlet for atmospheric air. An atmospheric inlet


139


A can be connected to an opening in the diesel engine crankcase


136


.




In both the arrangements shown in

FIGS. 10 and 10A

, the blowby gas passing through the electrostatic precipitator


137


is at a relatively high temperature. It also contains oil vapor which is not removed by electrostatic precipitation. This oil vapor will condense on the heat transfer surfaces of an intercooler


146


used at the outlet of the turbo-charger


142


. Over time, the condensed oil will flood the intercooler


146


to cause a drop in the intercooler efficiency and the power output of the diesel engine if not handled or removed.




To automatically remove this accumulated oil from the intercooler


146


, an oil sump


148


is provided in the intercooler to allow the condensed oil to flow into the sump by gravity. The airflow from the intercooler


134


is directed through a flow restriction


150


, such as a nozzle or an orifice to create a pressure drop to remove the oil from the intercooler


146


and be carried by the airflow into the engine intake. The oil collected in the oil sump


148


can also be fed to the intake manifold


131


of the engine


135


, by the back pressure created by the flow restriction


150


.





FIG. 11

shows a second arrangement for recirculating the blowby gas into a diesel engine


135


. The crankcase


137


is connected to the electrostatic precipitator


137


as before, but the T-connector


138


is removed and the flow from the precipitator


137


is directed to a filter intake plenum


154


and allowed to pass through the filter


144


along with the intake airflow. No crankcase pressure limiting arrangement is needed in this case. Since the precipitator outlet is always at atmospheric pressure, the crankcase pressure will thus be automatically limited to that needed to maintain the blowby gas flow through the precipitator


137


.




When the hot blowby gas is directed this way into the filter intake


154


, the oil vapor will be quickly cooled as it comes in contact with the cool collecting filter elements of the filter


144


. The vapor will thus condense and be collected in the filter housing. At the same time, all submicron size particles, which may not be completely removed by the electrostatic precipitator, will also be subjected to the strong thermophoretic forces created by the temperature gradient in the boundary layer of the gas flow around the collecting elements of the filter


144


, this thermophoretic force can be effectively utilized to remove these submicron particles. Normal engine intake air filters are designed to collect particles larger than a few micron in diameter only. Small particles in the submicron size range are usually not collected. By utilizing the thermophoretic force, the fine particles in the blowby gas can also be collected, thus making the incoming air to the turbo-charger cleaner. With proper design, oil and fine particle accumulation in the intercooler can be reduced to very low level.





FIG. 12

is similar to FIG.


11


and the parts that are identical are identically numbered. In

FIG. 12

a controllable flow restrictor


158


is connected to the outlet of the intercooler


146


. The flow restrictor has a retractable vane or blade


158


A that can be introduced into the interior passage of the restrictor and which is controlled by a solenoid


159


. The solenoid


159


is connected to the vane or blade


158


A and will extend the blade into the flow passage when a signal is received by the solenoid. An oil level sensor


160


is provided on the oil sump


148


, and when the oil level in the sump reaches a set level, the signal is provided to energize the solenoid


159


. The vane or blade


758


A is moved into the flow passage in flow restrictor


158


to restrict flow through the outlet line.




This action increases the back pressure in the oil sump and forces the collected oil out a line


161


to the intake manifold


131


of the diesel engine. The solenoid controlled restrictor can be any desired form, such a as a valve that closed partially, or an orifice that is introduced into the flow passageway.





FIG. 13

is a sectional view of a modified version of typical electrode support


170


. It can be molded from plastic and has an outer wall


172


, with a plurality of projections or “prongs” shown at


174


which make the outer surface much like a serrated surface. A wire of suitable diameter indicated at


176


can be wound around the support


170


in a helical fashion, much as shown in

FIG. 8

, with the points of the serrations or projections supporting the wire


176


at closely spaced intervals depending on the spacing of the serrations to insure that the wire


176


is maintained in a proper position relative to the collector electrode.





FIG. 14

is a vertical cross-sectional view of a modified form of a compact electrostatic precipitator


199


. In this form of the invention, a conductive sleeve


200


forms a passage for fluid, with an inlet connection


202


for receiving an aerosol, and an outlet connection


203


. A flow passageway is defined by a plurality of openings


204


in a housing plate


206


that is supported on sleeve


206


A, which is positioned at the upper end of the conductive sleeve


200


, and is supported on a cap plate


208


on a flange


210


formed on the end of the outer sleeve


200


.




The support sleeve


206


A has an open center, and an end insulator portion


215


of a main electrode support


212


is mounted therein. The upper end insulator portion


215


of the support


212


is supported on the cover


208


in a suitable manner. The upper end insulator portion has a receptacle for a heater assembly


216


, which has heaters


218


mounted in a outer jacket


219


that is heat conducting and in contact with the insulator portion


215


. The outer jacket


219


can be made of copper, which is a very good heat conductor, to distribute the heat uniformly to its outer surface and keep the insulator surface


213


hot and clean from contamination by vapor condensation and particle deposition. The top plate


220


is a heat insulator to reduce the heating power required to operate the heater. The electrical power to operate the heater, usually 12 or 24 volts, is carried by the electrical leads


221


passing through the top plate


220


.




A power connection line


224


can be passed out through a central opening of a cap


222


. As shown, a power supply


226


to provide the high voltage for the discharge electrode can be potted in the cap


222


and the connector line or rod


225


can be within the precipitator and does not have to extend through the cap. The line


224


can be a relatively low voltage, for example, a 24-volt supply could be provided. The heaters


218


also would be connected generally to a 24-volt supply.




The main support


212


includes a hollow center electrode support


214


that can be, for example, injection molded as a single piece with the main support


212


. The electrode support


214


has an interior passageway in which the high voltage connection rod or line electrode


225


extends, and a thin electrode wire


227


can extend for connection directly to the electrode wire shown at


228


that, as shown, is helically wrapped around the insulating support


214


. The electrode wire


228


is shown larger than actual size and is a thin wire as previously explained. The insulating material sleeve


214


may be attached to the main support


212


with suitable screws threaded up into the support


212


. The upper part of the insulating support has a conducting sleeve


217


, which can be made of a metal and connected to the same high voltage electrode wire


226


. The insulating support


214


can have a cross section that is cylindrical, if desired, or as shown in

FIG. 15

, it could be rectangular with the outer collector electrode


200


also being rectangular with care being taken so that at the corners there was a uniform spacing between the wire


228


and the collector electrode.




The cross section can take any desired configuration, as long as the spacings are maintained for a corona discharge.




The aerosol flow would come in as shown by the arrow


234


, and flow up and around the passageway


235


between the high-voltage electrode wire


228


and the collector electrode


200


. In this case, the collector electrode.


200


is not a porous member, but is a solid member that can either be stainless steel, for example, or could be a conducting plastic. As the flow passes through the space between the electrode wire


228


and the collector


200


, the particles are charged by the corona ions produced by the wire electrode


228


. Some of these particles are precipitated onto the collector


200


in this region. The remaining particles are carried by the gas to the upper part of the assembly between the precipitator electrode


217


and the collector electrode


220


, where they are precipitated onto the collector


220


by virtual of the high voltage on the electrode


217


. The flow then goes up through the openings


204


, and out through the outlet


203


as shown. The main support


212


and the electrode support


214


can be injection molded as a single piece, if desired, with conductors formed as slip-fit jackets, or wrapped wires. The heaters


218


are easily installed to ,maintain the temperature of the insulator at a desired level.




The high temperature at the heaters keeps vapor that enters the space between the sleeve


206


A and the upper high voltage insulator portion


215


from condensing on the surface


213


of the high voltage insulator portion


215


in the region around the center portion


215


. The heaters also provide enough heat to tend to repel contaminant particles by the thermophoretic effect and prevent them from depositing on the surface


213


of the high voltage insulator portion


215


. The heaters


218


are in heat transfer, contacting relation to the insulator portion


215


and will maintain the temperature of the surface


213


sufficiently high to prevent contaminant particles from building up on the surface of the insulator portion. Preferably the temperature of the surface


213


of the insulator portion


215


is 10° or more than the temperature of the gas in the vicinity of the insulating surface


213


inside the precipitator housing.





FIG. 16

is a transverse cross sectional view of a modified electrode support


250


taken on the same line as FIG.


15


.

FIG. 17

is a vertical cross sectional view of the modified electrode support


250


. A wire


252


forming the electrode is in contact with the surface


254


of the electrode support


250


and in substantial conformity to it. The wire


252


can be wound around the support


250


as shown, and made to adhere to the surface


254


by using a suitable adhesive material. When adhesives are used the wire


252


can have various patterns.




One such pattern for the wire


252


is shown in

FIG. 18

at


258


. In

FIG. 18

a surface


262


of a support


260


has been unrolled to a flat surface to review the wire pattern on the surface


262


. The electrically conductive discharge wire


264


is in contact with the support surface


262


, which is made of an electrically insulating material, such as a plastic or ceramic. The wire electrode


264


is of a substantially uniform diameter and the distance between the wire segments and the adjacent collector electrode is substantially uniform along the length of the wire. With a uniform distance between the wire


264


and the collector electrode, a substantially uniform corona discharge can be maintained. All parts of the wire


267


can thus be utilized effectively to insure a high charging efficiency in a small compact overall physical size for the electrostatic droplet collector.




Another way of fabricating the thin wire discharge electrode is to use a flat, thin dielectric, generally plastic, having a thin film clad on the outer surface. The flat thin dielectric with a thin film on the outer surface can be similar to those used in fabricating flexible, electric circuit boards. The electrode wire pattern on the surface can be etched by photolithography. The thin film forming the pattern can then be applied to the surface of the support structure by an adhesive. In such a case, the wire will no longer have a circular cross section. The lateral dimension of the etched electrode, however, must be sufficiently small to sustain a corona discharge at the applied high voltage material.




The compact electrostatic precipitators shown are intended primarily for droplet aerosol collection. The high collection efficiency for the compact size also make the precipitators suitable for collecting dry particle aerosols. The collected dry particles will accumulate in the unit and the precipitators must be periodically shut down for cleaning and maintenance. This is usually acceptable for most applications.




The compact electrostatic precipitator described herein, though not necessary for the application, is particularly attractive because of its compact physical size and high collection efficiency.




The invention as described above is for the preferred embodiments. Others, who are skilled in the art, will see other possibilities and embodiments to accomplish the same objectives based on the principles and approaches described in the present specifications.



Claims
  • 1. An automatic condensed oil remover for an intercooler of a diesel engine comprising a flow restrictor between the intercooler and the diesel engine, an oil sump in the intercooler, and an oil tube to carry condensed oil from the oil sump to the diesel engine, said flow restrictor comprising means for creating a pressure drop sufficient to force the oil to flow from the oil sump through the oil tube to the diesel engine.
  • 2. The condensed oil remover of claim 1, wherein the flow restrictor a is selectively operated to create pressure drop sufficient to force the oils to flow from the oil sump through the oil tube to the diesel engine, and a control to selectively operate the flow restrictor.
  • 3. An automatic condensed oil removal system comprising the condensed oil system of claim 1, and an oil level sensor to provide the signal to actuate the flow restrictor and create a pressure drop sufficient to force the oil to flow from the oil sump through the oil tube to the diesel engine.
Parent Case Info

This is a Divisional Application of copending Application Ser. No. 09/829,386, filed Apr. 9, 2001, now U.S. Pat. No. 6,364,941 which a is Divisional Application of Application Ser. No. 09/199,894, filed Nov. 25, 1998, for COMPACT ELECTROSTATIC PRECIPITATOR FOR DROPLET AEOROSOL COLLETION, now U.S. Pat. No. 6,221,136, and priority on both Applications Ser. No. 09/829,386 and Ser. No. 09/199,894 is hereby claimed.

US Referenced Citations (35)
Number Name Date Kind
342548 Walker May 1886 A
895729 Cottrell Aug 1908 A
1204907 Schmidt Nov 1916 A
1250088 Burns Dec 1917 A
1329285 Brownlee Jan 1920 A
1605648 Cooke Nov 1926 A
1994259 Thorne Mar 1935 A
2085349 Wintermute Jun 1937 A
2129783 Penney Sep 1938 A
2142129 Hoss et al. Jan 1939 A
2509548 White May 1950 A
2731958 Robley Jan 1956 A
3246639 Oliver Apr 1966 A
3509967 Ballard May 1970 A
3754538 Ephraim, Jr. et al. Aug 1973 A
3910779 Penney Oct 1975 A
3977384 Jahn Aug 1976 A
3999964 Carr Dec 1976 A
4029482 Postma et al. Jun 1977 A
4222748 Argo et al. Sep 1980 A
4563983 Hayashi et al. Jan 1986 A
4578088 Linscheid Mar 1986 A
4708095 Luterek Nov 1987 A
4890455 Leonhard et al. Jan 1990 A
5006134 Knoll et al. Apr 1991 A
5024685 Torok et al. Jun 1991 A
5239972 Takeyama et al. Aug 1993 A
5547019 Iacullo Aug 1996 A
5942026 Erlichman et al. Aug 1999 A
6047670 Stella et al. Apr 2000 A
6055966 Zentgraf May 2000 A
6109346 Hill Aug 2000 A
6123144 Morman et al. Sep 2000 A
6221136 Liu et al. Apr 2001 B1
6364941 Liu et al. Apr 2002 B2
Foreign Referenced Citations (4)
Number Date Country
3702469 Aug 1988 DE
39 30 872 Mar 1991 DE
0 044 361 Jan 1982 EP
307656 Mar 1989 EP