Apparatus for aeration without significant agitation to deplete and biodegrade sludge

Abstract
An improved method and apparatus for aeration of septic tanks and the like. Because of the interrelationship of the rotating impeller, an air plate and the horsepower of the unit in comparison with the volumetric size of the sludge tank, the unit disperses extremely small reduced pressure microbubbles adjacent the area of the impeller. These reduced pressure microbubbles are thereafter dispersed throughout the wastewater by Brownian movement without agitating the sludge. As a result, there is substantially increased lateral oxygen transfer to replace the oxygen used by the aerobic bacteria. The sludge is therefore efficiently digested without the need for huge, expensive and energy inefficient equipment.
Description




FIELD OF THE INVENTION




This invention relates to vacuum aeration units with improved construction and methodology in comparison with those of our earlier U.S. Pat. No. 5,951,867 issued Sep. 14, 1999.




BACKGROUND OF THE INVENTION




As explained in our earlier-above referenced U.S. Patent, there is a continuing need for the development of improved bacterial breakdown of sewage waste material. This invention relates to an improvement on our earlier patented device. It allows for enhancing the lateral oxygen transfer to allow aerobic bacterial to sufficiently and efficiently decompose waste material, often without objectionable odors.




Prior devices, including the device of our earlier U.S. Pat. No. 5,951,867 depended upon substantial agitation of all of the sludge materials in tanks to enhance the rate and efficiency of aerobic bacterial decomposition. As a result, large horsepower units and energy expenditures were often required in order to achieve sufficient agitation to enhance lateral oxygen transfer.




In accordance with the improvement of the present invention, a unit has been developed which is not dependant upon high horsepower and high energy consumption. This goal has been achieved by understanding the relationship between the configuration of the air plate of the unit, the impeller design and the horsepower in relation to the ratio of volume in the tank.




Accordingly, it is a primary objective of the present invention to provide a sewage aeration unit which is low in energy consumption, which has a high degree of lateral oxygen transfer to replace the oxygen used by the aerobic bacteria during the digestion process, and which enhances the production of reduced pressure microbubbles capable of dispersing themselves throughout the wastewater in the septic tank by Brownian movements, all without agitating the sludge in the tank.




The method and means of accomplishing the above objectives and advantages as well as others will become apparent from the detailed description of the invention which follows hereinafter.




SUMMARY OF THE INVENTION




An improved method and apparatus for aeration of septic tanks and the like. Because of the interrelationship of the rotating impeller, an air plate and the horsepower of the unit in comparison with the volumetric size of the wastewater tank, the unit disperses extremely small reduced pressure microbubbles adjacent to the impeller area. These reduced pressure microbubbles are thereafter dispersed throughout the wastewater by Brownian movement without agitating the sludge. As a result, there is substantially increased lateral oxygen transfer to replace the oxygen used by the aerobic bacteria. The sludge is therefore efficiently digested without the need for huge, expensive and energy inefficient equipment.











BRIEF DESCRIPTION OF THE DRAWINGS





FIG. 1

is a perspective view of the aeration device of the present invention.





FIG. 2

is an exploded view of the aeration device of FIG.


1


.





FIG. 2A

is a front view of the aeration device.





FIG. 3

is a bottom view of the aeration device of the present invention.





FIG. 4

is a top view of the aeration device of the present invention.





FIG. 5

shows a plan view of the construction of the air plate.





FIG. 5A

shows a side view of the air plate.





FIG. 6

is a side view of the impeller showing the angles of the blade with respect to a horizontal plane.





FIGS. 7 & 8

show schematically the microbubbles and the agitation generated in the surrounding area adjacent the impeller.











DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT




The unit, best illustrated in overall perspective in

FIG. 1

, is a device which may be fitted in a conventional septic tank. The aeration device


10


is operated by motor


12


, energized via electrical hookup


14


. As seen in

FIG. 2

, the unit


10


has air intake lines,


16


and


18


, which draw ambient air. Motor


12


is mounted to motor mount plate


20


which is attached to circular housing wall


22


. Mounted inside of circular housing wall


22


, and attached to motor


12


is drive shaft


24


. Mounted to circular housing


22


, opposite motor


12


is air plate


26


. Below air plate


26


and spaced apart therefrom, is impeller


28


. Impeller


28


is held adjacent to the air plate


26


by a hex nut


30


attached to the end of drive shaft


24


as best illustrated in FIG.


3


. Air intake tubes


32


and


34


are shown, adjacent the side wall of housing


22


.




The configuration of air plate


26


is best illustrated in

FIG. 5

which depicts a plan view of the unit. As seen in

FIG. 5

, air plate


26


has a series of generally parallel concentrically positioned apertures


35


with a plurality of curved or arcuate slots


36


crossing the concentric rings in a manner that matingly matches the shape of the trailing edge of the impeller


28


. Air plate


26


is preferably made of a polymeric plastic material such as an alpha olefin polymer. The air plate


26


configuration, together with the concentrically positioned rings of air holes


35


and the arcuate air slot


36


enhance the preparation of vacuum microbubbles in the liquid adjacent impeller


28


.




The impeller


28


is configured of four distinct blades,


38


,


40


,


42


, and


44


(FIG.


3


). Each blade has an arcuate short trailing edge


46


and a longer forward edge such as at


48


. Looking at the blade as illustrated in

FIG. 6

, it does not dwell in a single horizontal plane but rather in moving from trailing edge


46


it curves up and away from the horizontal plane as one moves from trailing edge


46


to forward edge


48


. The blade rotates as indicated by directional arrow


50


(looking up from the bottom). As impeller


28


rotates in the direction indicated by arrow


50


, air is pulled through the concentrically positioned apertures in the manner illustrated in FIG.


7


. In particular, air is pushed through air intakes


16


since the atmospheric pressure is greater than the partial vacuum created, and also through air tubes


32


and


34


through air plate


26


as impeller


28


rotates in the manner shown by directional arrow


50


, air above air plate


26


goes through the concentrically positioned rings. Vortexes


52


are constantly being disrupted by larger volumes of air pushed through slots


36


which disrupt the air bubbles tending to make them even smaller. The smaller bubbles then transfer down into the water adjacent and around the area of the impeller as illustrated in FIG.


7


. Because the bubbles are so small (sized generally of 100 microns to 500 microns) and are also low pressure air bubbles, they move like colloidal particles via Brownian movement throughout the wastewater tank to enhance lateral oxygen transfer. In this way, the invention results are achieved.




It has been found important there be a proper horsepower ratio with respect to the volume of unit. For example, one does not want to agitate or disturb all of the sludge/liquid in the septic tank. If you do this, it requires too much energy and the amount of oxygen transfer to the bacteria is decreased. Correspondingly, if only the vacuum air bubbles are moving via Brownian movement, the chances of interaction with water for dissolved oxygen transfer are substantially increased thereby increasing transfer of oxygen to bacteria. Generally speaking, the ratio of the volume of the tank to horsepower should be 5000 gallons or less per horsepower to move or mix. If more than 5000 gallons of water per horsepower, it will not move the water. In actual operation, the unit for example can operate at about 3,000 rpm. The forward edge of the impeller blade


28


when it crosses the slot creates the whirlpool effect and the angle of pitch above the horizontal plane from the trailing edge


46


to the forward edge


48


of the blade is about 6°. Ideally the unit should operate at from six inches to twelve inches below the water surface in the tank.




While not wishing to be bound by theory, it is believed the unit works as follows. Bacterial cell respiration produces the energy for growth and division. This energy is supplied by what we call wet combustion, the oxidation of organic chemical compounds broken down by the bacteria in the presence of dissolved oxygen.




Bacterial growth and multiplication must take place in a aqueous medium possessing carbon and nitrogen compounds in a form capable of being assimilated to provide energy for the cells respiration process. Nutrient ingestion by bacteria must take place through a cell wall and membrane which require minute particles of molecular size dispersed in solution for ready transport.




These conditions are met here in an aqueous medium with minimal or no mixing so that oxygen, food, and bacteria have the most effective interface for assimilation and digestion.




The prime mover of the water (impeller


28


) moves the water out of the air chamber which will cause the air to enter, and when the water completely evacuates the space above the air plate


26


, the air is pushed into the space (air tube), through the holes provided in the air plate. The water below the impeller replaces or fills the space above the impeller. As the air above the air plate is pushed down into the recirculating water from below, the air streams from the several air holes in the plate make empty cylinder in the water or vortexes (vortices) which are periodically cut or terminated and reformed by the blades of the impeller. Thus, forming smaller and smallest voids in the water leaving the end of the air chamber. The water space formed, at a uniform time and distance, have a volume with air at a lower pressure than the water. Therefore, the volume will reduce, until the air is compressed. The size of the bubble will be smaller than the diameter of the vortex that was formed at the air plate. The air plate therefore sets the size of the bubble that forms.



Claims
  • 1. An apparatus for aeration of septic tank wastewater comprising:a motive power means; an impeller operatively connected to the motive power means; an air plate positioned between said motive power means and said impeller; said air plate having a series of concentrically positioned apertures, periodically interrupted with crossing arcuate air slots, wherein the concave side of the arcuate air slots faces in the direction of roatation of the impeller.
  • 2. The apparatus of claim 1, wherein the impeller has a plurality of blades, having a forward edge and a pitched upwardly inclined trailing edge.
US Referenced Citations (26)
Number Name Date Kind
3630498 Bielinski Dec 1971 A
3662890 Grimshaw May 1972 A
3677229 Blough et al. Jul 1972 A
3778233 Blough et al. Dec 1973 A
3810548 Blough May 1974 A
4244531 Szegvari Jan 1981 A
4333796 Flynn Jun 1982 A
4519959 Takeuchi et al. May 1985 A
4620925 Allen Nov 1986 A
4646714 Bolin Mar 1987 A
4732682 Rymal Mar 1988 A
4988630 Chen et al. Jan 1991 A
5194144 Blough Mar 1993 A
5403088 Killmer et al. Apr 1995 A
5403473 Moorehead et al. Apr 1995 A
5413765 Smith et al. May 1995 A
5458816 Ebner et al. Oct 1995 A
5490187 VanSiclen et al. Feb 1996 A
5690976 Nakayama Nov 1997 A
5727403 Na Mar 1998 A
5840276 Apfel Nov 1998 A
5919289 Misawa et al. Jul 1999 A
5951867 Blough et al. Sep 1999 A
6245237 Blough et al. Jun 2001 B1
20010013666 Nomura et al. Aug 2001 A1
20010022755 Holtzapple et al. Sep 2001 A1