WO1992016317A1 - Synthetic cover for waste piles - Google Patents
Synthetic cover for waste piles Download PDFInfo
- Publication number
- WO1992016317A1 WO1992016317A1 PCT/US1992/002318 US9202318W WO9216317A1 WO 1992016317 A1 WO1992016317 A1 WO 1992016317A1 US 9202318 W US9202318 W US 9202318W WO 9216317 A1 WO9216317 A1 WO 9216317A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- waste piles
- mixture
- binder
- piles according
- percent
- Prior art date
Links
- 239000002699 waste material Substances 0.000 title claims abstract description 88
- 239000000203 mixture Substances 0.000 claims abstract description 79
- 239000011230 binding agent Substances 0.000 claims abstract description 50
- 239000000835 fiber Substances 0.000 claims abstract description 43
- 239000007788 liquid Substances 0.000 claims abstract description 43
- 229920003043 Cellulose fiber Polymers 0.000 claims abstract description 36
- 239000004033 plastic Substances 0.000 claims abstract description 35
- 229920003023 plastic Polymers 0.000 claims abstract description 35
- 239000000428 dust Substances 0.000 claims abstract description 26
- 239000011398 Portland cement Substances 0.000 claims abstract description 18
- 239000004568 cement Substances 0.000 claims abstract description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 239000000123 paper Substances 0.000 claims abstract description 14
- 239000000440 bentonite Substances 0.000 claims abstract description 13
- 229910000278 bentonite Inorganic materials 0.000 claims abstract description 13
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 claims abstract description 13
- 239000010881 fly ash Substances 0.000 claims abstract description 12
- 239000004575 stone Substances 0.000 claims abstract description 8
- 238000004519 manufacturing process Methods 0.000 claims description 12
- 238000000034 method Methods 0.000 claims description 12
- 239000000149 chemical water pollutant Substances 0.000 claims description 10
- 229920002522 Wood fibre Polymers 0.000 claims description 7
- 239000002025 wood fiber Substances 0.000 claims description 7
- 239000011248 coating agent Substances 0.000 claims description 6
- 238000000576 coating method Methods 0.000 claims description 6
- 238000005507 spraying Methods 0.000 claims description 5
- KKEYFWRCBNTPAC-UHFFFAOYSA-L terephthalate(2-) Chemical compound [O-]C(=O)C1=CC=C(C([O-])=O)C=C1 KKEYFWRCBNTPAC-UHFFFAOYSA-L 0.000 claims description 5
- 239000003153 chemical reaction reagent Substances 0.000 claims description 3
- -1 polyethylene terephthalate Polymers 0.000 claims description 2
- 229920000139 polyethylene terephthalate Polymers 0.000 claims description 2
- 239000005020 polyethylene terephthalate Substances 0.000 claims description 2
- 239000000470 constituent Substances 0.000 abstract description 30
- 241000238631 Hexapoda Species 0.000 abstract description 3
- 239000002023 wood Substances 0.000 abstract description 2
- 239000010842 industrial wastewater Substances 0.000 description 7
- 239000000463 material Substances 0.000 description 7
- 239000002362 mulch Substances 0.000 description 7
- 239000010813 municipal solid waste Substances 0.000 description 5
- 239000002689 soil Substances 0.000 description 3
- 239000007921 spray Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 244000025254 Cannabis sativa Species 0.000 description 2
- 235000012206 bottled water Nutrition 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 230000001419 dependent effect Effects 0.000 description 2
- 239000004615 ingredient Substances 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 238000003892 spreading Methods 0.000 description 2
- 239000013598 vector Substances 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 1
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 239000003086 colorant Substances 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 230000008014 freezing Effects 0.000 description 1
- 238000007710 freezing Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 238000009533 lab test Methods 0.000 description 1
- 235000020166 milkshake Nutrition 0.000 description 1
- 239000010812 mixed waste Substances 0.000 description 1
- 239000004570 mortar (masonry) Substances 0.000 description 1
- 238000005325 percolation Methods 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000004800 polyvinyl chloride Substances 0.000 description 1
- 229920000915 polyvinyl chloride Polymers 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000011343 solid material Substances 0.000 description 1
- 239000004071 soot Substances 0.000 description 1
- 238000007592 spray painting technique Methods 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B1/00—Dumping solid waste
- B09B1/004—Covering of dumping sites
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/20—Agglomeration, binding or encapsulation of solid waste
- B09B3/25—Agglomeration, binding or encapsulation of solid waste using mineral binders or matrix
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/008—Sludge treatment by fixation or solidification
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B22/00—Use of inorganic materials as active ingredients for mortars, concrete or artificial stone, e.g. accelerators, shrinkage compensating agents
- C04B22/002—Water
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/02—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing hydraulic cements other than calcium sulfates
- C04B28/04—Portland cements
-
- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K8/00—Compositions for drilling of boreholes or wells; Compositions for treating boreholes or wells, e.g. for completion or for remedial operations
- C09K8/42—Compositions for cementing, e.g. for cementing casings into boreholes; Compositions for plugging, e.g. for killing wells
- C09K8/46—Compositions for cementing, e.g. for cementing casings into boreholes; Compositions for plugging, e.g. for killing wells containing inorganic binders, e.g. Portland cement
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/30—Landfill technologies aiming to mitigate methane emissions
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/78—Recycling of wood or furniture waste
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Definitions
- This invention relates to the field of waste management. More particularly, the invention relates to a synthetic cover for waste piles.
- waste may be concentrated into piles within landfills, compost windrows, sludge heaps, etc.
- waste piles When waste is concentrated into piles, it is often necessary to cover waste piles to minimize their odor, prevent fires, prevent the movement of the waste, and prevent vectors such as birds, flies, and other insects from feeding thereon.
- waste piles are covered by spreading a layer of dirt over the exposed portions of the waste piles. For example, in landfills, piles of municipal solid waste are covered by spreading a layer of dirt thereon. The thickness of the layer depends upon the length of time the pile is to remain covered.
- a waste pile which is to be covered for a short period of time, for example, overnight may require, for example, a six-inch layer.
- a twelve-inch layer may be required.
- For a permanent cover generally a layer of dirt of approximately two foot thickness or more may be required.
- the invention includes a mixture for creating a synthetic cover for waste piles.
- the mixture comprises a liquid, a binder, cellulose fibers, and plastic fibers.
- the invention also incorporates a method of making a synthetic cover for waste piles comprising mixing cellulose fibers and plastic fibers with a liquid to form a pre-mixture, and mixing a binder reagent to form a final mixture, wherein the final mixture has a thick-viscous consistency which will harden after it is applied to cover waste piles.
- the mixture may comprise approximately thirty eight percent to forty five percent by weight liquid, approximately fifty four percent to sixty percent by weight binder, approximately one half percent to two percent by weight cellulose fibers, and approximately one-tenth of a percent or less by weight plastic fibers.
- the liquid may comprise water, landfill leachate, and/or industrial waste water.
- the binder may comprise cement kiln dust; and/or cement kiln dust with bentonite.
- the amount of bentonite may be approximately five percent, by weight of the total mixture.
- the binder may comprise fly ash, and/or fly ash with portland cement.
- the amount of Portland cement may comprise about ten to fifteen percent of the mixture, by weight.
- the cellulose fibers may include shredded paper and/or finely shredded wood fibers.
- the plastic fibers may comprise polyethylene terephthalate fiber.
- the invention also incorporates a method of covering waste piles comprising mixing a binder, cellulose fibers, plastic fibers and liquid together to form a mixture; coating a waste pile with the mixture; and allowing the coating to harden as a cover on the waste pile.
- the mixing of the binder, cellulose fibers, plastic fibers and liquid may comprise mixing cellulose fibers and plastic fibers into a liquid? thereafter, adding the binder thereto; and mixing the binder therein. Mixing the fibers, liquid and binder may occur within a mixing tank.
- the coating of a waste pile with the mixture may comprise spraying the mixture on the waste pile.
- the synthetic cover for waste piles in accordance with the present invention may be used to cover a variety of waste piles such as, for example, composte windrows, sludge heaps, and municipal solid waste piles in landfills. However, implementation of the synthetic cover for waste piles will be described in conjunction with its use to cover municipal solid waste piles in landfills.
- a seed and mulch applicator is normally used to mix water, grass seed, and mulch and then spray the mixture onto a ground area to provide a vegetative cover, from which grass will eventually grow.
- a typical seed and mulch applicator contains a mixing tank with an agitator, a liquid pump capable of passing a high content of solid material therethrough, and a spray hose with a nozzle. The capacity of the mixing tanks ranges from approximately 500 to 3,000 gallons.
- the agitator and pump are powered by a diesel or gasoline engine.
- the entire seed and mulch applicator apparatus may be mounted on a trailer that could be towed by a truck or other powered means.
- the seed and mulch applicator apparatus may be mounted on the bed of a truck or mounted on a track unit to be guided to different areas of the landfill.
- the synthetic cover for waste piles has been effectively mixed and applied using seed and mulch applicator equipment, it is possible to mix the ingredients to form the synthetic cover in other types of mixing equipment which have a sufficient mixing and spraying capacity.
- the synthetic cover for waste piles in accordance with the present invention is mixed by filling the mixing tank with a predetermined amount of liquid constituent such as water, landfill leachate, or industrial waste water. The proper amount of cellulose fibers and plastic fibers are then loaded into the mixer containing the liquid.
- a coloring agent such as LANSCO* (Landers Segal Color Corp) "Earthtone” mortar dye may be added if desired.
- the agitator is activated such that the cellulose fibers and plastic fibers are mixed with the liquid. Typically, it is necessary to activate the agitator for approximately a minute or longer to adequately mix the liquid, cellulose and plastic fibers together.
- the binder reagent is then placed into the mixer where it is thoroughly agitated with the liquid, cellulose fibers and plastic fibers.
- the mixing time necessary to yield a mixture with the proper consistency may vary depending upon the percentage of each constituent added to the mixture. Also, weather conditions such as temperature and humidity may affect the length of time that the binder must be mixed with the liquid, cellulose fibers and plastic fibers. However, the materials should be mixed until the mixture has a thick, viscid, "milk shake" type consistency.
- the spray applicator is moved to the working area and the mixture is sprayed onto the waste pile surface using a motion similar to spray painting. The mixture is sprayed in such a manner that a uniform layer approximately one-eighth to one-quarter of an inch thick exists. After the entire surface area of the waste pile has been sprayed in this manner, the material will harden if undisturbed.
- the mixture When the mixture is applied at the proper consistency it will resemble a clotty coagulant type of material which will adhere to the waste pile and cohere to itself. Typically, the material will dry and harden to resemble a stucco-type finish within 24 hours. After the entire waste pile has been covered, the applicator and mixing unit must be cleaned out thoroughly when not in use so that the mixture remaining within the apparatus does not harden. Typically, water will suffice in cleaning the apparatus. For convenience, cleaning may occur directly on the landfill itself.
- the liquid portion of the mixture may include water, landfill leachate, and/or industrial waste water. Any quality of water is acceptable for use in the present invention, including turbid, polluted and/or non-potable waters as well as landfill leachate and industrial waste water.
- the amount of liquid should be between 38 and 45 percent, by weight, of the total mixture.
- the binder used in the mixture may include cement kiln dust, fly ash with Portland cement, stone dust with portland cement, and/or cement kiln dust with bentonite.
- the amount of binder in the total mixture should be between 54 and 60 percent, by weight.
- the cellulose fiber may include shredded newspaper, shredded mixed paper, and/or finely shredded wood fiber.
- the total amount of the cellulose fiber in the mixture should be between k and 2 percent, by weight.
- the plastic fiber which may be used within the mixture includes polyethelene terephthalate (PET) fibers or other plastic fibers including recycled plastics.
- PET polyethelene terephthalate
- the amount of plastic fiber used is in the mixture may be up to one-tenth of a percent, or less, of the mixture by weight.
- each constituent i.e. liquid, binder, cellulose fibers, plastic fibers
- the exact percentage of each constituent, (i.e. liquid, binder, cellulose fibers, plastic fibers) used to create the mixture may depend upon the weather conditions which exist during mixing and application of the synthetic cover. For example, at relatively higher temperatures, the amount of liquid used in the total mixture will be higher than the amount of liquid used at lower temperatures.
- the total amount of water used within the mixture should be between 38 and 45 percent despite such weather variations. Therefore, for example, on a relatively hot day, the amount of liquid used will be closer to 45 percent of the mixture, by weight.
- the amount of liquid will be closer to 38 percent of the mixture. Also, if there is a high degree of rainfall which will contact the mixture, then the amount of water used should be decreased accordingly.
- the amount of binder used in the mixture will also be higher on a cold day compared to the amount of binder used in the mixture on a hot day. However, despite variations in rainfall and temperature, the amount of binder should remain between 54 and 60 percent of the total weight of the mixture.
- the amount of cellulose fiber used is also dependent upon rainfall. On a day where the rainfall is present, the amount of cellulose fiber should be closer to the 2 percent portion of the range of total weight of the mixture. Accordingly, the higher the rainfall, the higher the amount of cellulose fiber used. However, the amount of cellulose fiber should continue to remain between h and 2 percent of the mixture, by weight.
- the amount of plastic fiber used in the mixture is not dependent upon changes in weather conditions.
- the constituent used in liquid portion of the mixture may include water, landfill leachate, and/or industrial waste water.
- landfill leachate created by percolation of water through the buried refuse at a landfill, may also be used as a liquid constituent. Since disposal and treatment of landfill leachate are troublesome and expensive, use of landfill leachate may provide an effective method of its disposal. It should be noted that use of landfill leachate and industrial waste water as the liquid constituent may require increased safety precautions.
- the constituents which may be used as cellulose fibers include shredded newspaper, mixed types of shredded paper and/or shredded wood fiber. These cellulose fiber constituents may be used separately or in various combinations. Preferably, shredded newspaper or shredded mixed waste paper should be used because of its absorbability and availability.
- Newspapers may be shredded into particles, preferably less than one-half inch in any dimension.
- the shredded newspaper should not have more than a 6 percent, by weight, moisture content prior to mixing with the liquid constituent.
- other finely shredded mixed papers useable as the cellulose fiber constituent should preferably be less than one-half inch in any dimension.
- These mixed paper fibers may include shredded magazines, phone books, corrugated containers, junk mail, office paper, etc. These shredded mixed papers should also be less than 6 percent by weight moisture content prior to mixing.
- Shredded wood fibers may also be used as a constituent provided that the wood fibers are finely shredded. The shredded wood fiber must be in a string or hair-like shape such as fine excelsior.
- Wood chips are not satisfactory for use as the cellulose fiber constituent.
- the constituents which may be used as plastic fibers include high density polyethelene, polyvinyl chloride as well as or other types of plastics shredded into thin hair-like fibers. These hair-like fibers should be between one-quarter to one-half inch in length.
- Polyethelene terephthalate fibers, such as PETROFLEX* type 401 fiber which are hair-like in diameter and between one-quarter to one-half inch long in length are preferred as the plastic constituent useable in the present invention. These fibers are manufactured from recycled products such as plastic soda containers.
- the constituents which may be used as binders in the present invention include cement kiln dust (CKD) , fly ash with portland cement, cement kiln dust with bentonite, or stone dust with portland cement.
- Cement kiln dust is the preferred binder used in the present invention.
- Cement kiln dust is captured during the manufacture of portland cement by air pollution control devices. Although the physical and chemical characteristics of cement kiln dust are much different than portland cement, cement kiln dust does bear a physical resemblance to portland cement.
- cement kiln dust is the preferred binder constituent, other pozzolonic binders may be used.
- bentonite may also be added to cement kiln dust to form the binder constituent.
- the bentonite enhances the smoothness and consistency of the mixture and also increases its tacitness and viscosity enabling it to better adhere to waste and cohere to itself.
- approximately 5 percent, by weight of the total mixture, of bentonite may be added.
- Fly ash and portland cement may also be used as the binder constituent.
- Fly ash are fine solid particles of ashes, dust and soot which evolve from burning fuel.
- the amount of portland cement used with the fly ash should be approximately 10 to 15 percent by weight of the total mixture.
- stone dust derived from commercial stone crushing operations, may be used along with portland cement as a binder constituent. Accordingly, the amount of portland cement used with stone dust should also be between 10 to 15 percent by weight of the total mixture.
- Test Results TEST 1 A laboratory test was conducted utilizing the constituents and parameters shown in the following table.
- the constituent amounts were mixed as discussed supra and the mixture was sprayed onto municipal solid waste using a Bowie Lancer 500 Hydromulcher*.
- the mixture hardened into a cover which withstood freezing temperatures and various weather conditions.
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Inorganic Chemistry (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
Claims
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US07/674,864 US5161915A (en) | 1991-03-25 | 1991-03-25 | Synthetic cover for waste piles |
US674,864 | 1991-03-25 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO1992016317A1 true WO1992016317A1 (en) | 1992-10-01 |
Family
ID=24708201
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/US1992/002318 WO1992016317A1 (en) | 1991-03-25 | 1992-03-23 | Synthetic cover for waste piles |
Country Status (5)
Country | Link |
---|---|
US (2) | US5161915A (en) |
EP (1) | EP0577730A4 (en) |
AU (1) | AU1696392A (en) |
CA (1) | CA2101546C (en) |
WO (1) | WO1992016317A1 (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1994015886A1 (en) * | 1993-01-13 | 1994-07-21 | Nachtman Thomas J | Sprayable composition and method for forming a foamed outdoor protective cover layer |
EP0669145A1 (en) * | 1994-02-25 | 1995-08-30 | PELT & HOOYKAAS B.V. | Method for immobilizing ecologically harmful, organic or inorganic compounds |
GB2288598A (en) * | 1994-04-20 | 1995-10-25 | Geohess | Covering a landfill site for waste disposal |
US5863153A (en) * | 1993-11-09 | 1999-01-26 | Geohess (Uk) Limited | Waste treatment |
EP1076048A1 (en) * | 1999-08-10 | 2001-02-14 | Yprema | Process for using treated leachates and device for utilizing this process |
Families Citing this family (42)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5849364A (en) * | 1989-05-10 | 1998-12-15 | New Waste Concepts, Inc. | Self-foaming sprayable composition |
US6806298B1 (en) * | 1989-05-10 | 2004-10-19 | New Waste Concepts, Inc. | Sprayable composition and method for forming a foamed outdoor protective cover layer |
US5556033A (en) * | 1989-05-10 | 1996-09-17 | New Waste Concepts, Inc. | Apparatus for forming a foamed outdoor protective cover layer |
US5259698A (en) * | 1990-06-19 | 1993-11-09 | Maurice Garzon | Method for hiding from sight and protecting a dumping site |
US5265979A (en) * | 1991-03-25 | 1993-11-30 | Landfill Service Corporation | High efficiency waste placement system for municipal landfills |
US5385429A (en) * | 1991-03-25 | 1995-01-31 | Landfill Service Corporation | Synthetic cover for waste |
US5416251A (en) * | 1993-03-12 | 1995-05-16 | Monolith Technology Incorporated | Method and apparatus for the solidification of radioactive wastes and products produced thereby |
US5399048A (en) * | 1993-06-04 | 1995-03-21 | Chemical Lime Company | Method of capping exposed land areas and particulate materials deposited thereon |
US5486068A (en) * | 1993-11-03 | 1996-01-23 | Soil And Water Management, Inc. | Process for treating waste materials with concentrated acid and the product produced thereby |
DE4410728A1 (en) * | 1994-03-28 | 1995-10-05 | Sued Chemie Ag | Auxiliary for mineral binder systems |
US5503788A (en) * | 1994-07-12 | 1996-04-02 | Lazareck; Jack | Automobile shredder residue-synthetic plastic material composite, and method for preparing the same |
AU667021B1 (en) | 1994-10-28 | 1996-02-29 | Ecocover Holdings Limited | Mulch or seed mat |
US6004070A (en) * | 1996-07-08 | 1999-12-21 | Van Camp; John W. | Waste storage containment cell, method of operating, and apparatus therefore |
US6082929A (en) * | 1997-02-06 | 2000-07-04 | Williams; Jerald R. | Waste containment system and method for the reclamation of landfill and waste areas |
US5915881A (en) * | 1997-04-30 | 1999-06-29 | Reclamation Technology, Inc. | Method and composition of a clay slurry capping system for landfill and mineral waste areas |
US6071043A (en) * | 1998-03-13 | 2000-06-06 | Hunt; James R. | System for securing landfills |
US6136430A (en) | 1998-08-05 | 2000-10-24 | Cargill, Incorporated | Disposable water resistant cover for bulk salt |
US7140805B1 (en) | 1999-10-21 | 2006-11-28 | Fagan Dennis A | Method of treating municipal solid waste |
US6435770B1 (en) | 2000-10-20 | 2002-08-20 | Advanced Material Technologies Llc | Method of forming a synthetic cap on a bulk material pile |
US6767398B2 (en) * | 2000-10-30 | 2004-07-27 | James H. Trato | Cementitious compositions and cementitious slurries for permanently plugging abandoned wells and processes and methods therefor |
US20060008325A1 (en) * | 2003-05-19 | 2006-01-12 | Ianniello Peter J | Conversion of gypsum stacks to waste containment facilities and related construction & business methods |
ES2229914B2 (en) * | 2003-07-03 | 2007-03-16 | Josep Grau Almirall | INERTIZATION PROCEDURE OF INORGANIC WASTE. |
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WO1994015886A1 (en) * | 1993-01-13 | 1994-07-21 | Nachtman Thomas J | Sprayable composition and method for forming a foamed outdoor protective cover layer |
US5863153A (en) * | 1993-11-09 | 1999-01-26 | Geohess (Uk) Limited | Waste treatment |
EP0669145A1 (en) * | 1994-02-25 | 1995-08-30 | PELT & HOOYKAAS B.V. | Method for immobilizing ecologically harmful, organic or inorganic compounds |
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Also Published As
Publication number | Publication date |
---|---|
EP0577730A1 (en) | 1994-01-12 |
US5275508A (en) | 1994-01-04 |
US5161915A (en) | 1992-11-10 |
EP0577730A4 (en) | 1995-10-25 |
AU1696392A (en) | 1992-10-21 |
CA2101546C (en) | 1997-09-23 |
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