The present invention generally relates to water treatment systems, and more particularly to a closed loop water treatment system that is particularly suited for surface cleaning apparatus.
Water treatment describes those processes used to make water more acceptable for a desired end-use. These can include use as drinking water, industrial processes, medical and many other uses. The goal of all water treatment processes is to remove existing contaminants in the water, or reduce the concentration of such contaminants so the water becomes fit for its desired end-use. One such use can be returning water that has been used back into the natural environment without adverse ecological impact.
The processes that have been suggested for use in treating water for solids separation include physical processes such as settling and filtration, and chemical processes such as disinfection and coagulation.
Biological processes have also been employed in the treatment of water, and these processes may include, for example, aerated lagoons, activated sludge or slow sand filters.
Surface cleaning apparatus such as pressure washers are useful for cleaning a variety of objects. Such devices require a clean supply of water for proper operation, but create wastewater by entraining solids from the cleaned surface into the used source water. Although there are many types of pressure washing systems, a typical system utilizes an engine that powers a pump. The inlet side of the pump is connected to a low pressure water source such as a tank or a municipal water supply, while the high pressure side of the pump is connected to a high pressure hose and wand for controlling the flow of high pressure water generated by the pump. The high pressure water is directed at a surface to dislodge dirt, paint and the like, and the water is generally allowed to drain into the storm sewer.
Ultra-high pressure washers, supplying more than 25,000 P.S.I. are also known. These systems include a large engine, typically diesel, which operates a large multi-cylinder pump to generate high volumes of water at ultra-high pressures. The ultra-high pressure water is directed through piping and/or hoses to various types of blast heads suitable for controlling the flow and direction of the ultra-high pressure water. One particular use for ultra-high pressure water devices is the removal of stripes or other markings from road surfaces. When polymers such as paint or plastic are used for roadway marking, the surface of the pavement is penetrated from ⅛-⅜ inch; whereby water blasting is the only known method of removing the stripe material from below the surface without removing a portion of the roadway surface. Ultra-high pressure water washers are also utilized for removing paint from ships, cleaning industrial facilities, removing graffiti, removing rubber from aircraft runways and demolition.
One problem associated with both low and ultra-high pressure water cleaning equipment is maintaining an adequate supply of clean water for continuous operation of the system. Dirty or contaminated water causes numerous problems with water cleaning equipment such as excessive pump wear, clogged filters, nozzles, screens and the like. Because cleaning often needs to take place away from municipal water supplies, water is often transported to the cleaning site. Because the water cleaning equipment requires large volumes of water to be effective, additional equipment is needed to haul in tanks of water. Alternatively, cleaning must be stopped so that additional water may be obtained.
Recovery and disposal of the water is another problem facing water cleaning equipment users. Demolition or even the mere cleaning of surfaces results in the water becoming contaminated with dirt and debris. This problem is particularly exacerbated with ultra high pressure water cleaning equipment which breaks dirt and debris up into particles small enough to remain suspended within the water indefinitely. Therefore, the contaminated water should be properly recovered and thereafter cleaned or contained before it can be disposed of.
Industrial systems that utilize filter belts are also known to be used for solid/liquid separation processes, particularly the dewatering of sludges in the chemical industry, mining and water treatment. The process of filtration is primarily obtained by passing a pair of filtering cloths and belts through a system of rollers. The feed sludge to be dewatered is introduced from a hopper between two filter cloths (supported by perforated belts) which pass through a convoluted arrangement of rollers. As the belts are fed through the rollers, water is squeezed out of the sludge. When the belts pass through the final pair of rollers in the process, the filter cloths are separated and the filter cake is scraped off into a suitable container. Water sprays are typically utilized to clean the filter cloth before it is reused. The water spray is reclaimed to be reprocessed or diverted to a drain for disposal. However, in these systems it is typically the solid filter cake that the user is interested in recovering and not the water that was carrying the solid particles, and thus the water typically remains dirty and is discarded to the drain.
Therefore, there is a need in the art for a water recirculation system that is suitable for applications such as high pressure or ultra-high pressure water cleaning equipment. The water recirculation system should provide a predetermined amount of clean water to start the cleaning operation. The water recirculation system should recover the dirty and contaminated water expelled during the cleaning process for removal of dirt and debris so that the water can be recirculated through the pressure cleaning equipment. The water recirculation system should be efficient enough to recirculate a sufficient volume of water for continuous operation of the water cleaning system. The water recirculation system should retain the dirt and debris for proper disposal. The water recirculation system should be compact enough to fit on a mobile frame that may also contain the high or ultra-high pressure water cleaning equipment.
There is also a need in the art for a water filtration system that is suitable for municipal, industrial and private uses. The water filtration system should utilize a continuous filter belt in combination with a settling tank for water containing a coagulant. The filter belt should be submerged within the settling tank a predetermined distance to control the hydrostatic head pressure utilized to push the debris containing water through the filter belt to limit the adhesion of the particles to the filter belt so that vacuum can be utilized to clean the filter belt for continuous use. The filter belt should be sized and the head pressure selected to provide a desired volume of cleaned water. The water can then be used as is or supplied to additional equipment or processes for further cleaning.
Thus, the present invention provides a water recirculation system for stationary or mobile applications and is particularly suited for surface cleaning apparatus and the like which overcomes the disadvantages of the prior art systems.
The present invention relates generally to an environmentally sensitive mobile cleaning system, and more specifically relates to a closed loop water recirculation system for high or ultra-high pressure mobile cleaning apparatus. The water recirculation system works in combination with a mobile pressure cleaning apparatus for cleaning surfaces while minimizing water usage and containing contaminants before they enter a storm water drain system. The system includes a water tank sized to contain an established volume of fluid sufficient to circulate through the system, a pump to pressure the fluid to a cleaning head, a vacuum system to return the contaminated fluid to the system, and a filter means to remove the contaminants from the fluid so that clean fluid can be reintroduced to the cleaning head. The method comprises the steps of increasing the pressure of a fixed volume of fluid in a closed-loop system, jetting or blasting the surface with the pressurized fluid, vacuuming the blasted fluid into the system, and removing the contaminants from the fluid.
Accordingly, it is an objective of the present invention to provide an environmentally sensitive cleaning system.
It is a further objective of the present invention to provide a mobile water recirculation system for surface cleaning apparatus.
It is yet a further objective of the present invention to provide a mobile water recirculation system for surface cleaning apparatus that reduces particulate size within the recirculated water to less than 1 micron.
It is another objective of the instant invention to provide a novel sediment tank arrangement.
It is yet another objective of the instant invention to provide a mobile water recirculation system for surface cleaning apparatus that includes a coagulant injection system.
It is still yet another objective of the instant invention to provide a mobile water recirculation system for surface cleaning apparatus that includes a continuous belt type filter.
It is yet a further objective of the instant invention to provide a method of continuously cleaning water to remove suspended solids therefrom.
Other objectives and advantages of this invention will become apparent from the following description taken in conjunction with the accompanying drawings wherein are set forth, by way of illustration and example, certain embodiments of this invention. The drawings constitute a part of this specification and include exemplary embodiments of the present invention and illustrate various objects and features thereof.
While the present invention is susceptible of embodiment in various forms, there is shown in the drawings and will hereinafter be described a presently preferred embodiment with the understanding that the present disclosure is to be considered an exemplification of the invention and is not intended to limit the invention to the specific embodiments illustrated.
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It should noted that while aluminum chlorhydrate is the preferred coagulant, other coagulants such as but not limited to aluminum chloride, aluminum sulfate, ferric chloride, ferric sulfate, poly aluminum chloride, clays, sodium aluminate, ULTRA-FLOC, WESTCHLOR, inorganic/polymer blends and suitable combinations thereof, may be utilized without departing from the scope of the invention. It should also be noted that these coagulants may include or be combined to carry iron to create a magnetic flocculent or coagulant.
This application is a continuation in part and claims the priority of U.S. Patent Application No. 61/147,158, entitled “Mobile Water Recirculation System For Surface Cleaning Apparatus”, filed Jan. 26, 2009, the contents of which are incorporated herein in their entirety. This application is related to U.S. Pat. No. 7,255,116, entitled “Stripe Removal System”, issued Aug. 14, 2007, U.S. patent application Ser. No. 11/340,738, entitled, “Transportable Holding Tank For Stripe Removal System”, filed Jan. 26, 2006, and U.S. patent application Ser. No. 11/340,104, entitled “Mobile Mark Removal System”, filed Jan. 26, 2006, the contents of which are incorporated herein by reference.
Number | Name | Date | Kind |
---|---|---|---|
1789425 | Cabrera | Jan 1931 | A |
2074623 | Schroth | Mar 1936 | A |
2267086 | Donohue | Dec 1941 | A |
3026966 | Asklof | Mar 1962 | A |
3151348 | Maasberg | Oct 1964 | A |
3166773 | Wyczalek | Jan 1965 | A |
3489679 | Davidson et al. | Jan 1970 | A |
3532070 | Lamarque | Oct 1970 | A |
3540073 | Issenmann et al. | Nov 1970 | A |
3619632 | Labombarde | Nov 1971 | A |
3639936 | Ashton | Feb 1972 | A |
3658589 | Shaddock | Apr 1972 | A |
3694033 | Rowley et al. | Sep 1972 | A |
3701426 | Wetzel | Oct 1972 | A |
3753777 | Thomsen et al. | Aug 1973 | A |
3787916 | Akagi et al. | Jan 1974 | A |
3812379 | Kaufman et al. | May 1974 | A |
3900969 | Diehn | Aug 1975 | A |
3959010 | Thompson et al. | May 1976 | A |
3977128 | Goff | Aug 1976 | A |
4007026 | Groh | Feb 1977 | A |
4158248 | Palmer | Jun 1979 | A |
4158575 | Townsend | Jun 1979 | A |
4199837 | Fisco, Jr. | Apr 1980 | A |
4227893 | Shaddock | Oct 1980 | A |
4290820 | Swisher, Jr. et al. | Sep 1981 | A |
4336671 | Nelson | Jun 1982 | A |
4340488 | Toth et al. | Jul 1982 | A |
4376358 | Shelton | Mar 1983 | A |
4377924 | Bergh | Mar 1983 | A |
4509963 | Jackson | Apr 1985 | A |
4578840 | Pausch | Apr 1986 | A |
4753052 | Dickson | Jun 1988 | A |
4819676 | Blehert et al. | Apr 1989 | A |
4839061 | Manchak Jr. et al. | Jun 1989 | A |
4935984 | Bryant et al. | Jun 1990 | A |
5002595 | Kehr | Mar 1991 | A |
5041165 | Urbani | Aug 1991 | A |
5060334 | Strauser et al. | Oct 1991 | A |
5076919 | Francisco, Jr. | Dec 1991 | A |
5108471 | Poborsky | Apr 1992 | A |
5224236 | Sallquist | Jul 1993 | A |
5236278 | Dickson | Aug 1993 | A |
5589080 | Cho et al. | Dec 1996 | A |
H0001660 | Herman et al. | Jul 1997 | H |
5704989 | Page | Jan 1998 | A |
5708989 | Ellis | Jan 1998 | A |
5826460 | Soncina et al. | Oct 1998 | A |
5961847 | Creps et al. | Oct 1999 | A |
5965020 | Pierson | Oct 1999 | A |
5979012 | Fritz | Nov 1999 | A |
6042726 | Anderson | Mar 2000 | A |
6073720 | Vanderlinden | Jun 2000 | A |
6082630 | Bohrer | Jul 2000 | A |
6113800 | Hopkins et al. | Sep 2000 | A |
6129094 | Moll et al. | Oct 2000 | A |
6221258 | Feke et al. | Apr 2001 | B1 |
6302967 | Rohrbacher et al. | Oct 2001 | B1 |
6328165 | Baker et al. | Dec 2001 | B1 |
6358406 | Hirs | Mar 2002 | B1 |
6393944 | Soncina et al. | May 2002 | B1 |
6402822 | Najm | Jun 2002 | B1 |
6495031 | Bratten | Dec 2002 | B1 |
6653265 | Rossi et al. | Nov 2003 | B2 |
6685830 | Hartleitner et al. | Feb 2004 | B2 |
6749666 | Meegan, Jr. | Jun 2004 | B2 |
6797158 | Feke et al. | Sep 2004 | B2 |
6835315 | Fox et al. | Dec 2004 | B2 |
6896742 | Geyer et al. | May 2005 | B2 |
7029579 | Tapp | Apr 2006 | B2 |
7029580 | Suzuki et al. | Apr 2006 | B2 |
7150779 | Meegan, Jr. | Dec 2006 | B2 |
7204365 | Behymer et al. | Apr 2007 | B2 |
7216397 | Tanner | May 2007 | B1 |
7255116 | Crocker | Aug 2007 | B2 |
7364652 | Middleton | Apr 2008 | B2 |
7625588 | Barker et al. | Dec 2009 | B2 |
7674158 | Crocker | Mar 2010 | B2 |
7798158 | Crocker | Sep 2010 | B2 |
7824547 | Reynders et al. | Nov 2010 | B2 |
8147689 | Cogar | Apr 2012 | B1 |
20020036173 | Feke et al. | Mar 2002 | A1 |
20020139722 | Bratten | Oct 2002 | A1 |
20030205242 | Gerber et al. | Nov 2003 | A1 |
20040050805 | Hartleitner et al. | Mar 2004 | A1 |
20040237247 | Nowak et al. | Dec 2004 | A1 |
20040262242 | Middleton | Dec 2004 | A1 |
20050067355 | Suzuki et al. | Mar 2005 | A1 |
20060000491 | Crocker | Jan 2006 | A1 |
20060185689 | Crocker | Aug 2006 | A1 |
20070051672 | Reynders et al. | Mar 2007 | A1 |
20070169797 | Crocker | Jul 2007 | A1 |
20070204889 | Crocker | Sep 2007 | A1 |
20070207711 | Crocker | Sep 2007 | A1 |
20080066781 | Crocker | Mar 2008 | A1 |
20090241999 | Crocker | Oct 2009 | A1 |
20090242003 | Crocker | Oct 2009 | A1 |
20100167339 | Clayton et al. | Jul 2010 | A1 |
20100200514 | Crocker | Aug 2010 | A1 |
Entry |
---|
Specialty Chemicals/Coagulants & Flocculants, Ecologix Environmental Systems, www.dcologixsystems.com/ ch—coag—floc.php. |
Potable and Process Water Chemical Applications, www.coynechemical.com/environmental, 2000 George S. Coyne Chemical Co., Inc. |
Johnson, Committee report: Characterization of inorganic coagulant/polymer blends using refractive index and specific gravity measurements, CAT.INIST, 2004, vol. 96, pp. 170-173, American Water Works Association, Denver, CO. |
Number | Date | Country | |
---|---|---|---|
20100200514 A1 | Aug 2010 | US |
Number | Date | Country | |
---|---|---|---|
61147158 | Jan 2009 | US |