US3734988A - Use of composted refuse to make construction products - Google Patents

Use of composted refuse to make construction products Download PDF

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US3734988A
US3734988A US3734988DA US3734988A US 3734988 A US3734988 A US 3734988A US 3734988D A US3734988D A US 3734988DA US 3734988 A US3734988 A US 3734988A
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refuse
percent
water
nitrogen
maintaining
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A Aintablian
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INTERNA SYSTEMS MANAGEMENT COR
INTERNA SYSTEMS MANAGEMENT CORP US
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    • AHUMAN NECESSITIES
    • A61MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61LMETHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
    • A61L11/00Methods specially adapted for refuse
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/30Mixed waste; Waste of undefined composition
    • C04B18/305Municipal waste
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B26/00Compositions of mortars, concrete or artificial stone, containing only organic binders, e.g. polymer or resin concrete
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Definitions

  • ABSTRACT A process for converting mun' [52] U.S.Cl. ..264/82,7l/9,7l/14, products such as building ,a -board, and 106/1 1 106/1 106/137 building bricks which consists of the steps of reducing [5 l -C --C C04) 5f 9/ 0 the size of the refuse to a chip size by shredding; [58] Field of Search ..264/32, 332, 109; decomposing the refuse in the presence of nitrogen,
  • a Japanese process compacts refuse into blocks and coats them with tar.
  • the Japanese blocks are unstable and cannot be used in building and have been found unsatisfactory in roads.
  • the gist of the present invention is a process for quickly converting municipal refuse into useful products which can be used to construct buildings. Accordingly, an object of the present invention is to provide a technically feasible and cost effective process for converting typical municipal refuse in urban areas into a dense, hard stable, odor-free material which can be produced in many forms such as cylinders, blocks having physical characteristics similar to commercial cement blocks and sheets for a variety of building paving and decorating applications.
  • Another object is to stop the microbiology and chemical reactions quickly so as to effect decomposition in a matter of days instead of the usual several months.
  • a further object is to produce inert, sterile building construction materials from refuse in an essentially continuous process, and which will retain its construc tion characteristics and integrity over a long period of time.
  • FIG. I is a schematic drawing of the equipment used in the process of the present invention.
  • FIG. 2 is a flow diagram of the present invention.
  • Receiving Municipal refuse is delivered by trucks 1 or other means and dumped into a receiver 2.
  • the receiver holds the refuse from approximately two normal size (36 cubic yard) collection trucks.
  • the largest piece size is an object that will fit in a residential garbage can or an approximate maximum of l A feet.
  • Incoming refuse is approximately 74 cubic yards with a density of approximately 270 pounds per cubic yard.
  • the receiver holds about 10 tons of refuse which is about 40 percent by weight water.
  • Refuse larger than 12 X 12 inches is screened mechanically by a screen graded belt 3 and the smaller classified refuse falls into a receiving hopper and is conveyed to a magnetic separator.
  • the hopper facilitates fly, rodent and odor control.
  • the larger pieces of refuse are sorted for metal or other reuseable product recovery.
  • Magnetic Separator Refuse is conveyed to a magnetic drum or a magnetic belt where ferrous metals are extracted and conveyed to a metal bin for salvaging. Iron separation may also be accomplished with a cross belt pickup.
  • Shredder The refuse remaining after the preceding separations is then conveyed by belts 4 to a shredder which may be of conventional design.
  • the shredder reduces all items to about 1 X 1 inch size chips.
  • the density of the refuse increases approximately 3.5 times and gives a discharge volume of slightly over cubic feet per hour.
  • the waste is then delivered by conveyers 7 to deconditioning or composting tanks, 8,9, 10,11 and 12 for accelerated biological decomposition. Three days to a week is required for decomposition. Consequently five or more tanks are needed.
  • Refuse delivered to the deconditioning tank is a mixture of wet material chemically and bacteriologically active.
  • de-conditioning is a biological process.
  • the environmental factors influence the activities of the organisms in determining the speed and the course of the decomposition cycle.
  • the important factors are: particle size, moisture content, aeration, hydrogen ion concentration, temperature and initial carbon-nitrogen ratio.
  • Nitrogen is added periodically. The amount of nitrogen to be added depends upon the carbon content of the material. The ratio of carbon content (C) to nitrogen content (N) to be added is C/N between 20 to 50 percent by weight.
  • Composting reduces the particle size of most of the material and consequently increases the density to approximately 40 pounds per cubic foot. Moisture content of the material will be approximately 50 percent.
  • the material is moved by conveyers 13 and 14 and dried by a gas fired heater 16 to render it biologically inert to facilitate grinding to a fine powder and to permit uniform compounding of the final product. Between 60 to percent moisture of the composted material is removed in several hours by the gas fired dryer at a temperature of between to 210 F. The dried material is then conveyed by conveyer 17 to the grinder 18.
  • the dry material is ground to a fine powder form. To achieve the mesh size needed (approximately 80 mesh size) two passes of the grinding process are required.
  • the ground-up material is then conveyed by conveyer 19 to a mixing tank 21.
  • the fine powdered form material is mixed with additives and binders to provide the required physical characteristics. Dry materials are fed from overhead storage tanks 22 and 23 by proportioning feeders 24 and 25 to the mixer.
  • the basic ingredients of the mixture are as follows:
  • Portland Cement 0% to 30% 7. Water 25% to 110%
  • the meaning for Portland Cement in the specification and claims is a kind of cement that hardens under water, and is basically made by burning a mixture of limestone and clay, shale, blast furnace slag, marl, iron ore and gypsum.
  • Portland cement is readily attainable as the type ordinarily used in making concrete in building construction. Portland Cement for construction is identified by ASTM NO. C-150. Quick setting cements may also be used such as by (1) heating bauxite and lirnestone and then grinding to a fine powder, (2) tricalcium silicate or (3) oxychloride cements (BMgOMgCI lOl'LO).
  • Example 1 Mixture Ratio of Mixture (per cent by weight) 1. De-conditioned material 100% 2. Plaster of Paris 20% to 60% 3. Silica (sand) 25% to 80% 4. Water 26% to 110% Example 2 l. Deconditioned material 100% 2. Plaster of Paris 20% to 60% 3. Portland cement to 30% 4. Water 25% to l 10% Example 3 1. De-conditioned material 100% 2. Plaster of Paris 25% to 50% 3. Portland cement 10% to 30% 4. Lime 25% to 60% 5. Silica (sand) 30% to 80% 6. Water 25% to 110% The correct amount of liquid is controlled by the feeder. Operation of the mixer is continuous and retention time within the mixing chamber is variable.
  • the mixture which is prepared in the mixing tank is conveyed to a press 27 for molding into block form 20.
  • the molding pressure will vary between a load of 15,000 pounds to 75,000 pounds. The pressure is held for about 1 minute or longer to insure that the blocks will be stabilized. Higher pressures are required for larger blocks.
  • the blocks are stacked in a curing room 29 with high moisture content.
  • Water spray as overhead fixtures, provides suspended water spray continuously.
  • the blocks are cured between 1 day to 10 days.
  • the blocks are then ready for use and are stacked in the open air in a yard.
  • the blocks may be coated with plastic as by dipping in a tank 30 to give them the desired architectural characteristics. Further examples and testing results Sample No. 1 Series Sample 1A Deconditioned material 300 grams Plaster of Paris 150 grams Portland Cement grams Water 400 grams Sample 18 same as 1A except water 350 grams Sample 1C same as [A except water 300 grams Sample ID same as 1A except water 250 grams Test results of Sample No. 1 Series Block sixe for the samples in series 1 was 1 X1 X4 inches.
  • Sample No. 2 Series 1n a second series of test samples, the same formulation as the sample No. 1 series was used except that 400 grams of water was added and the curing time was increased.
  • the test results showed a dramatic increase in compressive strength as indicated by tests by Twining Laboratories of Southern California, Inc. as follows: Test results of Sample No. 2 Series (1 1% diameter cylinders) Specimen Load Compressive Strength No. 1 3,720 lbs. 2,105 psi. No. 2 3,260 lbs. 1,845 psi. No. 3 3,420 lbs. 1,935 psi. No. 4 3.120 lbs. 1,766 psi.
  • Sample No. 3 Series De-conditioned material 45% Silica (sand) 75% Plaster of Paris 1 1.2% Portland Cement 6.8% Water 25 to 30% Test results of Sample No. 3 series The average compressive failure was 1,400 psi.
  • Sample No. 4 Series Specimen Decondi- Plaster Portland 11,0 Molding tioned Mixture of Paris Cement gr. Pressure grams grams grams grams lbs.
  • Deconditioned material 100 grams Silica (sand) 100 grams Lime 10 grams Water grams Bacteriological Tests Tests for bacteriological activity and for pH reading were conducted by the Orange Coast College in Costa Mesa, California and the results are shown below:
  • nitrogen may be introduced in the form of ammonium sulfate, (NI-M 50 nitrogen tri-oxide, N 0 ammonium nitrate, NH NO sodium nitrate, NaNO or equivalent.
  • FIG. 2 a flow diagram is shown for the operation of a plant having a capacity of 100 tons of refuse per day.
  • This refuse has a volume of 740 cubic yards and a water content of 40 percent.
  • the density and water content will of course vary but a typical density is about 270 pounds per cubic yard.
  • Such a plant should have a receiver having a capacity to take 12.5 tons of refuse per hour with a volume of 2,500 cubic feet per hour. Density is about 10 pounds per cubic foot with a water content still at 40 percent and still containing the large pieces.
  • the product is fed through a standard shredder which has a capacity of 12.5 tons per hour and processes 715 cubic feet per hour.
  • the density is raised by shredding to 35 pounds per cubic foot.
  • the size is reduced to about 1 inch and the water content remains at 40 percent.
  • the de-conditioner nitrogen in the form of ammonium nitrate or the other compounds of nitrate set forth above are added in the amounts above specified.
  • the de-conditioner should have a capacity of about 690 cubic feet per hour with a weight capacity of 13.8 tons per hour. Density again increases to 40 pounds per cubic foot and the water content is raised by the addition of water to 50 percent. Size is now reduced to ls-l inch.
  • Water 1.1 tons per hour, 35.3 cubic feet per hour with a density of 62.4 pounds per cubic foot.
  • Lime 1.1 tons per hour at a volume of 33.9 cubic feet per hour and a density of 65 pounds per cubic foot.
  • Size is ASTM 100.
  • Silica is added at the rate of 7.5 tons per hour at a volume of 188 cubic feet per hour and having a density of 80 pounds per cubic foot and a size of ASTM 100.
  • Portland cement may be added at the rate of 1.8 tons per hour having a volume of 45 cubic feet per hour at 94 pounds per cubic foot.
  • the de-conditioned product added to the mixer at this point in the process is 7.5 tons per hour with a volume of 300 cubic feet per hour. Density is 50 pounds per cubic foot and water content is 3 per cent. Size is 0.006 to 0.01 inches (ASTM 100 50).
  • the above process makes about 32,500 blocks per day in a molder which subjects each block to 31,200 psi. at a rate of 1,980 blocks per hour working 17 hours per day.
  • Wall board is made by taking dry de-conditioned material in a ratio of about to 90 percent from the dryer and mixing it with 10 to 25 percent Elmers Glue or equivalent (such as Resorcinol water proof glue by U.S. Plywood or any marine glue used by companies to make plywood) and pressing between two sheets for forming. The wall board is then dried for about 24 hours.
  • Elmers Glue or equivalent such as Resorcinol water proof glue by U.S. Plywood or any marine glue used by companies to make plywood
  • Other glues which may be used are Plyobord Super Glue by Goodyear and two component epoxy glues.
  • Floor tile is best made using 75 to 90 percent deconditioned material and 10 to 25 percent Plyobord Super Glue or Elmer's Glue.
  • a process for converting municipal refuse that is chemically and bacteriologically active to building construction blocks comprising:
  • de-conclitioning said shredded refuse for approximately 3 to 7 days in a de-conditioning tank including the steps of:
  • additives and binders selected from the group consisting of plaster of paris, lime, silica, portland cement, calcium in a form selected from the group consisting of gypsum, selenite, alabaster, satin, and spar, and water and mixing;
  • a process as defined in claim 1 comprising:
  • a process as defined in claim 1 comprising:
  • a process as defined in claim 1 comprising:
  • a process as defined in claim 1 comprising:
  • a process as defined in claim 1 comprising:
  • a process as defined in claim 1 comprising:
  • said binders and additives consisting of plaster of paris and silica.
  • said binders and additives consisting of plaster of paris and portland cement.
  • a process as defined in claim 1 comprising:
  • said binders and additives consisting of plaster of paris, portland cement, lime and silica.
  • a process as defined in claim 1 comprising:
  • said binders and additives consisting of plaster of paris, lime, silica, calcium (in a form selected from the group consisting of gypsum, selenite, alabaster, satin, or spar), and portland cement.
  • a process as defined in claim 1 comprising:
  • a process for converting municipal refuse that is chemically and bacteriologically active to building wall board comprising the steps of:
  • de-conditioning said shredded refuse for approximately three to seven days in a deconditioning tank including the steps of:
  • a process for converting municipal refuse that is chemically and bacteriologically active to building floor tile comprising the steps of:
  • deconditioning said shreeded refuse for approximately three to 7 days in a deconditioning tank including the steps of:

Abstract

A process for converting municipal refuse into useable products such as building blocks, wall board, and building bricks which consists of the steps of reducing the size of the refuse to a chip size by shredding; decomposing the refuse in the presence of nitrogen, water and air; drying the chemically processed material in a gas fired dryer to render it biologically inert; grinding the dried material to a fine powder; mixing the powder with fillers and binders such as hydraulic setting cements and glues; adding water and other chemicals as required; forming the blocks or other building materials by pressing; and curing the product until a specified strength has been achieved.

Description

c -zz-va AU 116 EX Aintablian 1 May 22, 1973 USE OF COMPOSTED REFUSE TO 3,344,217 9/1967 Mogg et a1 l06/l22 MAKE CONSTRUCTION PRODUCTS 3,419,377 /1968 3,579,320 /1971 1 Inventor: Avedis Ainublim, Santa Clara 3,653,871 4/1972 Tempe ..71/14 Calif.
[73] Assignee: International Systems Management OTHER PUBLICATIONS Corporation Santa Clara Calif Business Week, July 12, 1969, page 145 [22] Filed: Nov. 8, 1971 Primary Examiner-Lorenzo B. Hayes 1. N 196 7 7 [211 App 0 6 Assistant ExaminerJohn H. Miller Related US. Application Data Att0rney-James R. Cypher [63] Continuation-impart of Ser. No. 119,564, March 1,
1971, abandoned. [57] ABSTRACT A process for converting mun' [52] U.S.Cl. ..264/82,7l/9,7l/14, products such as building ,a -board, and 106/1 1 106/1 106/137 building bricks which consists of the steps of reducing [5 l -C --C C04) 5f 9/ 0 the size of the refuse to a chip size by shredding; [58] Field of Search ..264/32, 332, 109; decomposing the refuse in the presence of nitrogen,
water and air; drying the chemically processed material in a gas fired dryer to render it biologically inert; [56] Referenm C ted grinding the dried material to a fine powder; mixing the powder with fillers and binders such as hydraulic UNITED STATES PATENTS setting cements and glues; adding water and other 516,112 3/1894 Ransome ..106/119 chemicals as required; forming the blocks or other 1,777,449 l Rath 26 building materials by pressing; and curing the product 1 1 1927 Robens,
l 19 until a specified strength has been achieved. 1,941,817 H1934 Sweeney et ...92/14 2,798,800 7/1957 Geraghty et a1.... ..71/ 14 13 Claims, 2 Drawing Figures 3,243,327 3/1966 Hoppeler 264/37 3,236,604 2/1966 Pierson ..71/9 3,236,605 2/1966 Pierson ..7l/9
GOMPOSTING RECElVlNG SORTING SHREDDIN'G s 7 n a 9 1o 11 12 4 DRYING 5 smuome /Q 23 V 5124 19, w
COMPOUNDING COATING SHIPPING Patented May 22, 1973 2 Sheets-Sheet l OZEEIw QZEMOLSOO OZEQwmIm wzrrmow INVENTOR USE OF COMPOSTED REFUSE TO MAKE CONSTRUCTION PRODUCTS The present application is a continuation in part of my prior co-pending US. Pat. application Ser. No. 119,564 filed Mar. 1, 1971 and now abandoned.
BACKGROUND OF THE INVENTION Disposal of urban refuse is a critical, nationwide problem and extensive analysis and research are underway to find viable solutions. The time-honored solution to refuse disposal, atmospheric burning, has ceased in all metropolitan areas. Open burning has usually been replaced with earth burial using cut and-fill techniques. Nationally, this is a temporary solution since the large quantities of refuse produced in urban areas are rapidly consuming available sites. Incineration has been tried, but is is expensive and contributes significantly to air pollution. Many costal cities dump refuse at sea but this method must soon cease since there is evidence that refuse contaminants are poisoning the local marine life.
There have been numerous attempts to economically produce building blocks from refuse. One process creates bricks out of the ashes of incinerated refuse. Incineration, however, as previously stated, adds greatly to the particle and thermal pollution of the air.
A Japanese process compacts refuse into blocks and coats them with tar. Thus far the Japanese blocks are unstable and cannot be used in building and have been found unsatisfactory in roads.
BRIEF SUMMARY OF THE INVENTION The gist of the present invention is a process for quickly converting municipal refuse into useful products which can be used to construct buildings. Accordingly, an object of the present invention is to provide a technically feasible and cost effective process for converting typical municipal refuse in urban areas into a dense, hard stable, odor-free material which can be produced in many forms such as cylinders, blocks having physical characteristics similar to commercial cement blocks and sheets for a variety of building paving and decorating applications.
Another object is to stop the microbiology and chemical reactions quickly so as to effect decomposition in a matter of days instead of the usual several months.
. A further object is to produce inert, sterile building construction materials from refuse in an essentially continuous process, and which will retain its construc tion characteristics and integrity over a long period of time.
BRIEF DESCRIPTION OF THE DRAWINGS FIG. I is a schematic drawing of the equipment used in the process of the present invention.
FIG. 2 is a flow diagram of the present invention.
DESCRIPTION OF THE PREFERRED EMBODIMENTS OF THE INVENTION Receiving Municipal refuse is delivered by trucks 1 or other means and dumped into a receiver 2. The receiver holds the refuse from approximately two normal size (36 cubic yard) collection trucks. The largest piece size is an object that will fit in a residential garbage can or an approximate maximum of l A feet. Incoming refuse is approximately 74 cubic yards with a density of approximately 270 pounds per cubic yard. Thus the receiver holds about 10 tons of refuse which is about 40 percent by weight water. Refuse larger than 12 X 12 inches is screened mechanically by a screen graded belt 3 and the smaller classified refuse falls into a receiving hopper and is conveyed to a magnetic separator. The hopper facilitates fly, rodent and odor control. The larger pieces of refuse are sorted for metal or other reuseable product recovery.
Magnetic Separator Refuse is conveyed to a magnetic drum or a magnetic belt where ferrous metals are extracted and conveyed to a metal bin for salvaging. Iron separation may also be accomplished with a cross belt pickup.
Shredder The refuse remaining after the preceding separations is then conveyed by belts 4 to a shredder which may be of conventional design. The shredder reduces all items to about 1 X 1 inch size chips. The density of the refuse increases approximately 3.5 times and gives a discharge volume of slightly over cubic feet per hour.
Chemical Processing The waste is then delivered by conveyers 7 to deconditioning or composting tanks, 8,9, 10,11 and 12 for accelerated biological decomposition. Three days to a week is required for decomposition. Consequently five or more tanks are needed.
Refuse delivered to the deconditioning tank is a mixture of wet material chemically and bacteriologically active. Basically, de-conditioning is a biological process. The environmental factors influence the activities of the organisms in determining the speed and the course of the decomposition cycle. The important factors are: particle size, moisture content, aeration, hydrogen ion concentration, temperature and initial carbon-nitrogen ratio.
To accelerate the decomposition, the following steps are involved:
1. Turning the material at least once a day. The turning process will provide aeration (oxygenation) 2. Maintaining a moisture content between 40-70 percent. Water is sprayed periodically on the material to maintain this moisture range.
3. Warm air is supplied periodically to maintain the temperature of the material between 50 C. to C.
4. Nitrogen is added periodically. The amount of nitrogen to be added depends upon the carbon content of the material. The ratio of carbon content (C) to nitrogen content (N) to be added is C/N between 20 to 50 percent by weight.
5. When the material has a pH of 6 or less, calcium carbonate or other base acid is added periodically to raise the pH slightly.
6. Composting reduces the particle size of most of the material and consequently increases the density to approximately 40 pounds per cubic foot. Moisture content of the material will be approximately 50 percent.
Drying After the chemical or deconditioning process, the material is moved by conveyers 13 and 14 and dried by a gas fired heater 16 to render it biologically inert to facilitate grinding to a fine powder and to permit uniform compounding of the final product. Between 60 to percent moisture of the composted material is removed in several hours by the gas fired dryer at a temperature of between to 210 F. The dried material is then conveyed by conveyer 17 to the grinder 18.
Grinder The dry material is ground to a fine powder form. To achieve the mesh size needed (approximately 80 mesh size) two passes of the grinding process are required. The ground-up material is then conveyed by conveyer 19 to a mixing tank 21.
Mixing Tank In the mixing tank 21, the fine powdered form material is mixed with additives and binders to provide the required physical characteristics. Dry materials are fed from overhead storage tanks 22 and 23 by proportioning feeders 24 and 25 to the mixer. The basic ingredients of the mixture are as follows:
Mixture Ratio of Mixture (per cent by weight) 1. De-conditioned material 100% 2. Plaster of Paris to 50% 3. Lime 0% to 50% 4. Silica, as in the form of sand 0% to 60% 5. Calcium as in the form of gypsum (selenite, alabaster, satin or spar) 0% to 50% 6. Portland Cement 0% to 30% 7. Water 25% to 110% The meaning for Portland Cement in the specification and claims is a kind of cement that hardens under water, and is basically made by burning a mixture of limestone and clay, shale, blast furnace slag, marl, iron ore and gypsum. Portland cement is readily attainable as the type ordinarily used in making concrete in building construction. Portland Cement for construction is identified by ASTM NO. C-150. Quick setting cements may also be used such as by (1) heating bauxite and lirnestone and then grinding to a fine powder, (2) tricalcium silicate or (3) oxychloride cements (BMgOMgCI lOl'LO).
Three main categories of mixtures are listed below: Example 1 Mixture Ratio of Mixture (per cent by weight) 1. De-conditioned material 100% 2. Plaster of Paris 20% to 60% 3. Silica (sand) 25% to 80% 4. Water 26% to 110% Example 2 l. Deconditioned material 100% 2. Plaster of Paris 20% to 60% 3. Portland cement to 30% 4. Water 25% to l 10% Example 3 1. De-conditioned material 100% 2. Plaster of Paris 25% to 50% 3. Portland cement 10% to 30% 4. Lime 25% to 60% 5. Silica (sand) 30% to 80% 6. Water 25% to 110% The correct amount of liquid is controlled by the feeder. Operation of the mixer is continuous and retention time within the mixing chamber is variable.
Molding The mixture which is prepared in the mixing tank is conveyed to a press 27 for molding into block form 20. The molding pressure will vary between a load of 15,000 pounds to 75,000 pounds. The pressure is held for about 1 minute or longer to insure that the blocks will be stabilized. Higher pressures are required for larger blocks.
Curing The blocks are stacked in a curing room 29 with high moisture content. Water spray, as overhead fixtures, provides suspended water spray continuously. The blocks are cured between 1 day to 10 days. The blocks are then ready for use and are stacked in the open air in a yard.
Coating As required, the blocks may be coated with plastic as by dipping in a tank 30 to give them the desired architectural characteristics. Further examples and testing results Sample No. 1 Series Sample 1A Deconditioned material 300 grams Plaster of Paris 150 grams Portland Cement grams Water 400 grams Sample 18 same as 1A except water 350 grams Sample 1C same as [A except water 300 grams Sample ID same as 1A except water 250 grams Test results of Sample No. 1 Series Block sixe for the samples in series 1 was 1 X1 X4 inches.
Sample No. 2 Series 1n a second series of test samples, the same formulation as the sample No. 1 series was used except that 400 grams of water was added and the curing time was increased. The test results showed a dramatic increase in compressive strength as indicated by tests by Twining Laboratories of Southern California, Inc. as follows: Test results of Sample No. 2 Series (1 1% diameter cylinders) Specimen Load Compressive Strength No. 1 3,720 lbs. 2,105 psi. No. 2 3,260 lbs. 1,845 psi. No. 3 3,420 lbs. 1,935 psi. No. 4 3.120 lbs. 1,766 psi.
Sample No. 3 Series De-conditioned material 45% Silica (sand) 75% Plaster of Paris 1 1.2% Portland Cement 6.8% Water 25 to 30% Test results of Sample No. 3 series The average compressive failure was 1,400 psi. Sample No. 4 Series Specimen Decondi- Plaster Portland 11,0 Molding tioned Mixture of Paris Cement gr. Pressure grams grams grams lbs. A 100 40 20 122 15,000 13 100 40 20 100 20,000 C 100 40 2O 60 30.000 D 100 40 20 25,000 E 40 20 40 35,000 F 100 40 20 122 15,000 6 Deconditioned material 100 grams Silica (sand) 100 grams Lime 10 grams Water grams Bacteriological Tests Tests for bacteriological activity and for pH reading were conducted by the Orange Coast College in Costa Mesa, California and the results are shown below:
neg neg neg neg neg pH Tests All pl-l tests were performed by dissolving 1 gram of material in milliliters of pH 7.0 buffer. Results are based on the average of three readings.
The foregoing test show that blocks having compressive strength of 1,450 psi are obtainable which is in excess of the compressive strength of commercial cement blocks which is between 800 and 1,240 psi. Further the bacteriological tests show that the block is inert and may in fact be more inert than commercial cement block because it is essentially non-porous and therefore bacteria has a difficult time growing in the present block.
In the deconditioning step of the process it has been found that nitrogen may be introduced in the form of ammonium sulfate, (NI-M 50 nitrogen tri-oxide, N 0 ammonium nitrate, NH NO sodium nitrate, NaNO or equivalent.
Referring to FIG. 2, a flow diagram is shown for the operation of a plant having a capacity of 100 tons of refuse per day. This refuse has a volume of 740 cubic yards and a water content of 40 percent. The density and water content will of course vary but a typical density is about 270 pounds per cubic yard. Such a plant should have a receiver having a capacity to take 12.5 tons of refuse per hour with a volume of 2,500 cubic feet per hour. Density is about 10 pounds per cubic foot with a water content still at 40 percent and still containing the large pieces.
The product is fed through a standard shredder which has a capacity of 12.5 tons per hour and processes 715 cubic feet per hour. The density is raised by shredding to 35 pounds per cubic foot. The size is reduced to about 1 inch and the water content remains at 40 percent.
In the de-conditioner, nitrogen in the form of ammonium nitrate or the other compounds of nitrate set forth above are added in the amounts above specified. The de-conditioner should have a capacity of about 690 cubic feet per hour with a weight capacity of 13.8 tons per hour. Density again increases to 40 pounds per cubic foot and the water content is raised by the addition of water to 50 percent. Size is now reduced to ls-l inch.
in the dryer which has a capacity of 7.5 tons per hour and a volume of 470 pounds per cubic foot the density is increased to 32 pounds per cubic foot and the water content is negligible. Size is further reduced to oneeight inch to 1 inch.
After grinding, the following materials in batch quantities are added. Water, 1.1 tons per hour, 35.3 cubic feet per hour with a density of 62.4 pounds per cubic foot. Lime, 1.1 tons per hour at a volume of 33.9 cubic feet per hour and a density of 65 pounds per cubic foot. Size is ASTM 100. Silica is added at the rate of 7.5 tons per hour at a volume of 188 cubic feet per hour and having a density of 80 pounds per cubic foot and a size of ASTM 100.
For extra strength Portland cement may be added at the rate of 1.8 tons per hour having a volume of 45 cubic feet per hour at 94 pounds per cubic foot.
The de-conditioned product added to the mixer at this point in the process is 7.5 tons per hour with a volume of 300 cubic feet per hour. Density is 50 pounds per cubic foot and water content is 3 per cent. Size is 0.006 to 0.01 inches (ASTM 100 50).
The above process makes about 32,500 blocks per day in a molder which subjects each block to 31,200 psi. at a rate of 1,980 blocks per hour working 17 hours per day.
Wall board is made by taking dry de-conditioned material in a ratio of about to 90 percent from the dryer and mixing it with 10 to 25 percent Elmers Glue or equivalent (such as Resorcinol water proof glue by U.S. Plywood or any marine glue used by companies to make plywood) and pressing between two sheets for forming. The wall board is then dried for about 24 hours. Other glues which may be used are Plyobord Super Glue by Goodyear and two component epoxy glues.
Floor tile is best made using 75 to 90 percent deconditioned material and 10 to 25 percent Plyobord Super Glue or Elmer's Glue.
It is to be understood that the process described above and the sizes given are exemplary only. By changing the size and proportions of the formulas a plant can handle anywhere from 100 tons a day to a 1,000 tons a day or more.
1 claim:
1. A process for converting municipal refuse that is chemically and bacteriologically active to building construction blocks comprising:
a. shredding said refuse and reducing it to approximately 1 inch chip size;
b. de-conclitioning said shredded refuse for approximately 3 to 7 days in a de-conditioning tank including the steps of:
1. adding nitrogen in a form selected from the group consisting of ammonium sulfate, nitrogen tri-oxide, ammonium nitrate and sodium nitrate, periodically so that the ratio of carbon content to nitrogen content is between 20 and 50 by weight,
2. adding water so that the moisture content is between 40 and 70 percent,
3. maintaining a temperature between 50 and 4. aerating the deconditioned material as by turning periodically,
5. maintaining a pH of slightly more than 6,
c. drying said de-conditioned material and removing 60 to percent of the water;
d. grinding said dried de-conditioned material to a fine powder form:
e. adding additives and binders selected from the group consisting of plaster of paris, lime, silica, portland cement, calcium in a form selected from the group consisting of gypsum, selenite, alabaster, satin, and spar, and water and mixing;
f. compressing the mixture into a pre-selected mold;
and
g. curing the molded product in a moist atmosphere until the desired strength has been achieved.
2. A process as defined in claim 1 comprising:
a. said nitrogen being added in the form of ammonium sulfate.
3. A process as defined in claim 1 comprising:
a. said nitrogen being added in the form of nitrogen tri-oxide.
4. A process as defined in claim 1 comprising:
a. said nitrogen being added in the form of ammonium nitrate.
5. A process as defined in claim 1 comprising:
a. said nitrogen being added in the form of sodium nitrate.
6. A process as defined in claim 1 comprising:
a. said pH being maintained by the addition of calcium carbonate.
7. A process as defined in claim 1 comprising:
a. said binders and additives consisting of plaster of paris and silica.
8. A process as defined in claim 1 comprising:
a. said binders and additives consisting of plaster of paris and portland cement.
9. A process as defined in claim 1 comprising:
a. said binders and additives consisting of plaster of paris, portland cement, lime and silica.
10. A process as defined in claim 1 comprising:
a. said binders and additives consisting of plaster of paris, lime, silica, calcium (in a form selected from the group consisting of gypsum, selenite, alabaster, satin, or spar), and portland cement.
11. A process as defined in claim 1 comprising:
a. said compression step being held for at least about I minute.
12. A process for converting municipal refuse that is chemically and bacteriologically active to building wall board comprising the steps of:
a. shredding said refuse and reducing it to approximately 1 inch chip size;
b. de-conditioning said shredded refuse for approximately three to seven days in a deconditioning tank including the steps of:
1. adding nitrogen periodically so that the ratio of carbon content to nitrogen content is between 20 and 50 by weight,
2. adding water so that the moisture content is between 40 and percent,
3. maintaining a temperature between 50 and 4. aerating the de-conditioned material as by tuming periodically 5. maintaining a pH of slightly more than 6 c. drying said de-conditioned material and removing 60 to percent of the water;
d. adding a glue binder and mixing; and
e. compressing the mixture of de-conditioned material and glue additive into a sheet; and
f. curing said sheet until the desired strength has been achieved.
13. A process for converting municipal refuse that is chemically and bacteriologically active to building floor tile comprising the steps of:
a. shredding said refuse and reducing it to approximately 1 inch chip size;
b. deconditioning said shreeded refuse for approximately three to 7 days in a deconditioning tank including the steps of:
1. adding nitrogen periodically so that the ratio of carbon content to nitrogen content is between 20 and 50 percent by weight,
2. adding water so that the moisture content is between 40 and 70 percent,
3. maintaining a temperature between 50 and 80 4. aerating the deconditioned material as by turning periodically,
5. maintaining a pH of slightly more than 6,
c. drying said deconditioned material and removing 60 to 90 percent of the water;
d. adding 10 to 25 percent by weight of a glue binder and mixing; and
e. compressing the mixture of deconditioned material and glue additive into a sheet; and
f. curing said sheet until the desired strength has been achieved.
* t t i

Claims (24)

  1. 2. A process as defined in claim 1 comprising: a. said nitrogen being added in the form of ammonium sulfate.
  2. 2. adding water so that the moisture content is between 40 and 70 percent,
  3. 2. adding water so that the moisture content is between 40 and 70 percent,
  4. 2. adding water so that the moisture content is between 40 and 70 percent,
  5. 3. maintaining a temperature between 50* and 80* C.,
  6. 3. maintaining a temperature between 50* and 80* C.,
  7. 3. maintaining a temperature between 50* and 80* C.,
  8. 3. A process as defined in claim 1 comprising: a. said nitrogen being added in the form of nitrogen tri-oxide.
  9. 4. A process as defined in claim 1 comprising: a. said nitrogen being added in the form of ammonium nitrate.
  10. 4. aerating the deconditioned material as by turning periodically,
  11. 4. aerating the deconditioned material as by turning periodically,
  12. 4. aerating the de-conditioned material as by turning periodically
  13. 5. maintaining a pH of slightly more than 6 c. drying said de-conditioned material and removing 60 to 90 percent of the water; d. adding a glue binder and mixing; and e. compressing the mixture of de-conditioned material and glue additive into a sheet; and f. curing said sheet until the desired strength has been achieved.
  14. 5. maintaining a pH of slightly more than 6, c. drying said de-conditioned material and removing 60 to 90 percent of the water; d. grinding said dried de-conditioned material to a fine powder form: e. adding additives and binders selected from the group consisting of plaster of paris, lime, silica, portland cement, calcium in a form selected from the group consisting of gypsum, selenite, alabaster, satin, and spar, and water and mixing; f. compressing the mixture into a pre-selected mold; and g. curing the molded product in a moist atmosphere until the desired strength has been achieved.
  15. 5. maintaining a pH of slightly more than 6, c. drying said deconditioned material and removing 60 to 90 percent of the water; d. adding 10 to 25 percent by weight of a glue binder and mixing; and e. compressing the mixture of deconditioned material and glue additive into a sheet; and f. curing said sheet until the desired strength has been achieved.
  16. 5. A process as defined in claim 1 comprising: a. said nitrogen being added in the form of sodium nitrate.
  17. 6. A process as defined in claim 1 comprising: a. said pH being maintained by the addition of calcium carbonate.
  18. 7. A process as defined in claim 1 comprising: a. said binders and additives consisting of plaster of paris and silica.
  19. 8. A process as defined in claim 1 comprising: a. said binders and additives consisting of plaster of paris and portland cement.
  20. 9. A process as defined in claim 1 comprising: a. said binders and additives consisting of plaster of paris, portland cemenT, lime and silica.
  21. 10. A process as defined in claim 1 comprising: a. said binders and additives consisting of plaster of paris, lime, silica, calcium (in a form selected from the group consisting of gypsum, selenite, alabaster, satin, or spar), and portland cement.
  22. 11. A process as defined in claim 1 comprising: a. said compression step being held for at least about 1 minute.
  23. 12. A process for converting municipal refuse that is chemically and bacteriologically active to building wall board comprising the steps of: a. shredding said refuse and reducing it to approximately 1 inch chip size; b. de-conditioning said shredded refuse for approximately three to seven days in a deconditioning tank including the steps of:
  24. 13. A process for converting municipal refuse that is chemically and bacteriologically active to building floor tile comprising the steps of: a. shredding said refuse and reducing it to approximately 1 inch chip size; b. deconditioning said shreeded refuse for approximately three to 7 days in a deconditioning tank including the steps of:
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Cited By (26)

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US4012231A (en) * 1974-02-15 1977-03-15 Gottfried Dreer Process for the manufacture of fillers from solid waste
US4013616A (en) * 1971-11-22 1977-03-22 Wallace Richard A Mixed polymeric structural material and method
US4402751A (en) * 1981-11-24 1983-09-06 Wilde Bryce B Building material and method of manufacturing same
US4552726A (en) * 1983-06-17 1985-11-12 Consiglio Nazionale Delle Ricerche Plant consisting of modular elements for degrading organic wastes by means of earth worms
US4744829A (en) * 1985-07-13 1988-05-17 Hubert Eirich Process for producing agglomerates which are resistant to leaching out
US4838489A (en) * 1987-08-18 1989-06-13 Multinorm B.V. Coupling device
US5037286A (en) * 1988-06-24 1991-08-06 Rolite, Inc. Incineration residue treatment apparatus
US5302331A (en) * 1992-11-30 1994-04-12 Jenkins Robert E Waste treatment process
US5422051A (en) * 1993-06-28 1995-06-06 Sawyers; John P. Method for recycling plastic into cementitions building products
ES2073356A2 (en) * 1993-07-15 1995-08-01 Antonio Casado Y Cia S A Process for the full utilization of wastes by agglomeration
US5525153A (en) * 1995-04-04 1996-06-11 Cosola; Michael Ready mixed cement product incorporating material from construction and demolition debris
ES2130086A1 (en) * 1997-10-03 1999-06-16 Villares Martin Mario Use of purifier sludges for roadway safety structures and acoustic panels
WO1999058261A1 (en) 1998-05-11 1999-11-18 Concha Estrada Ernesto De Ecological mixture for the construction industry and process for eliminating waste materials
US20020096796A1 (en) * 1998-05-11 2002-07-25 Ernesto De La Concha Estrada Ecological mixture for construction and method for waste disposal
US20030030168A1 (en) * 1997-05-07 2003-02-13 Raffaello Bernabei Process for the cold transformation of municipal refuses and/or sludge into inert materials, plant for carrying out said process and products obtained
US6843844B1 (en) * 2002-01-22 2005-01-18 Therm-O-Lite Construction Products, Inc. Modified cellulose aggregate material
US20050029428A1 (en) * 2002-03-20 2005-02-10 Joshua Mesinger Method for creating an infrastructure
US20050035480A1 (en) * 1999-12-02 2005-02-17 Raffaello Bernabei Process for the cold transformation of municipal refuses and/or sludge into inert materials, plant for carrying out said process and products obtained
US20060065608A1 (en) * 2004-09-29 2006-03-30 Choate Chris E Process and apparatus for generating useful biomass from organic waste streams
ES2258411A1 (en) * 2006-01-20 2006-08-16 Maria Nuria Tomas Giner Recycling waste material for manufacturing panels, furniture, or other diverse types of objects, by adding agglutinating material into waste to achieve desired proportions
US20070231877A1 (en) * 2003-04-30 2007-10-04 Norcal Waste Systems, Inc. Systems and processes for treatment of organic waste materials with a biomixer
US20070231885A1 (en) * 2005-12-09 2007-10-04 Norcal Waste Systems, Inc. Biomechanical device for producing a biomass
EP2072156A1 (en) * 2007-12-17 2009-06-24 Snaidero Rino S.p.A. Fabrication method for the production of a construction part, in particular for furniture pieces, construction part and related production apparatus
US7955839B2 (en) 2006-06-23 2011-06-07 Recology Inc. Systems and methods for converting organic waste materials into useful products
WO2014012756A3 (en) * 2012-06-27 2014-04-03 Jentschura, Rolf Synthetic spongy wood boards
US8809038B1 (en) 2003-04-30 2014-08-19 Recology Inc. Process for treatment of organic waste materials

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Cited By (29)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4013616A (en) * 1971-11-22 1977-03-22 Wallace Richard A Mixed polymeric structural material and method
US4012231A (en) * 1974-02-15 1977-03-15 Gottfried Dreer Process for the manufacture of fillers from solid waste
US4402751A (en) * 1981-11-24 1983-09-06 Wilde Bryce B Building material and method of manufacturing same
US4552726A (en) * 1983-06-17 1985-11-12 Consiglio Nazionale Delle Ricerche Plant consisting of modular elements for degrading organic wastes by means of earth worms
US4744829A (en) * 1985-07-13 1988-05-17 Hubert Eirich Process for producing agglomerates which are resistant to leaching out
US4838489A (en) * 1987-08-18 1989-06-13 Multinorm B.V. Coupling device
US5037286A (en) * 1988-06-24 1991-08-06 Rolite, Inc. Incineration residue treatment apparatus
US5302331A (en) * 1992-11-30 1994-04-12 Jenkins Robert E Waste treatment process
US5422051A (en) * 1993-06-28 1995-06-06 Sawyers; John P. Method for recycling plastic into cementitions building products
ES2073356A2 (en) * 1993-07-15 1995-08-01 Antonio Casado Y Cia S A Process for the full utilization of wastes by agglomeration
US5525153A (en) * 1995-04-04 1996-06-11 Cosola; Michael Ready mixed cement product incorporating material from construction and demolition debris
US20030030168A1 (en) * 1997-05-07 2003-02-13 Raffaello Bernabei Process for the cold transformation of municipal refuses and/or sludge into inert materials, plant for carrying out said process and products obtained
ES2130086A1 (en) * 1997-10-03 1999-06-16 Villares Martin Mario Use of purifier sludges for roadway safety structures and acoustic panels
US20020096796A1 (en) * 1998-05-11 2002-07-25 Ernesto De La Concha Estrada Ecological mixture for construction and method for waste disposal
WO1999058261A1 (en) 1998-05-11 1999-11-18 Concha Estrada Ernesto De Ecological mixture for the construction industry and process for eliminating waste materials
US20050035480A1 (en) * 1999-12-02 2005-02-17 Raffaello Bernabei Process for the cold transformation of municipal refuses and/or sludge into inert materials, plant for carrying out said process and products obtained
US6843844B1 (en) * 2002-01-22 2005-01-18 Therm-O-Lite Construction Products, Inc. Modified cellulose aggregate material
US20050029428A1 (en) * 2002-03-20 2005-02-10 Joshua Mesinger Method for creating an infrastructure
US7985577B2 (en) 2003-04-30 2011-07-26 Recology, Inc. Systems and processes for treatment of organic waste materials with a biomixer
US20070231877A1 (en) * 2003-04-30 2007-10-04 Norcal Waste Systems, Inc. Systems and processes for treatment of organic waste materials with a biomixer
US8809038B1 (en) 2003-04-30 2014-08-19 Recology Inc. Process for treatment of organic waste materials
US20060065608A1 (en) * 2004-09-29 2006-03-30 Choate Chris E Process and apparatus for generating useful biomass from organic waste streams
US20060124559A1 (en) * 2004-09-29 2006-06-15 Norcal Waste Systems, Inc. Process for generating useful biomass from organic waste streams
US20070231885A1 (en) * 2005-12-09 2007-10-04 Norcal Waste Systems, Inc. Biomechanical device for producing a biomass
ES2258411A1 (en) * 2006-01-20 2006-08-16 Maria Nuria Tomas Giner Recycling waste material for manufacturing panels, furniture, or other diverse types of objects, by adding agglutinating material into waste to achieve desired proportions
US7955839B2 (en) 2006-06-23 2011-06-07 Recology Inc. Systems and methods for converting organic waste materials into useful products
WO2009077564A1 (en) * 2007-12-17 2009-06-25 Snaidero Rino S.P.A. Fabrication method for the production of a construction part, in particular for furniture pieces, construction part and related production apparatus
EP2072156A1 (en) * 2007-12-17 2009-06-24 Snaidero Rino S.p.A. Fabrication method for the production of a construction part, in particular for furniture pieces, construction part and related production apparatus
WO2014012756A3 (en) * 2012-06-27 2014-04-03 Jentschura, Rolf Synthetic spongy wood boards

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