US20030040651A1 - Apparatus and method for chemically reducing waste materials - Google Patents

Apparatus and method for chemically reducing waste materials Download PDF

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Publication number
US20030040651A1
US20030040651A1 US10/263,043 US26304302A US2003040651A1 US 20030040651 A1 US20030040651 A1 US 20030040651A1 US 26304302 A US26304302 A US 26304302A US 2003040651 A1 US2003040651 A1 US 2003040651A1
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United States
Prior art keywords
vessel
interior
waste
temperature
alkaline
Prior art date
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Abandoned
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US10/263,043
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English (en)
Inventor
Joseph Wilson
Gordon Kaye
Robert Hahn
Peter Weber
Kevin Morris
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Digestor LLC
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Individual
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First worldwide family litigation filed litigation Critical https://patents.darts-ip.com/?family=33298131&utm_source=google_patent&utm_medium=platform_link&utm_campaign=public_patent_search&patent=US20030040651(A1) "Global patent litigation dataset” by Darts-ip is licensed under a Creative Commons Attribution 4.0 International License.
Priority claimed from US09/171,447 external-priority patent/US6472580B2/en
Application filed by Individual filed Critical Individual
Priority to US10/263,043 priority Critical patent/US20030040651A1/en
Assigned to WASTE REDUCTION BY WASTE REDUCTION INC. reassignment WASTE REDUCTION BY WASTE REDUCTION INC. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: KAYE, GORDON I., HAHN, ROBERT L., MORRIS, KEVIN A., WEBER, PETER B., WILSON, JOSEPH H.
Publication of US20030040651A1 publication Critical patent/US20030040651A1/en
Priority to JP2004570934A priority patent/JP2006507940A/ja
Priority to KR1020057005643A priority patent/KR20050053723A/ko
Priority to EP03816212A priority patent/EP1578545A4/fr
Priority to UAA200502885A priority patent/UA85375C2/ru
Priority to MXPA05004274A priority patent/MXPA05004274A/es
Priority to PCT/US2003/031184 priority patent/WO2004091820A2/fr
Priority to EA200500569A priority patent/EA200500569A3/ru
Priority to AU2003304046A priority patent/AU2003304046C1/en
Priority to CA002500811A priority patent/CA2500811C/fr
Priority to CNA2003801023867A priority patent/CN1735442A/zh
Priority to BR0315019-4A priority patent/BR0315019A/pt
Priority to ZA200503168A priority patent/ZA200503168B/en
Priority to US11/457,342 priority patent/US7910788B2/en
Assigned to BIOSAFE ENGINEERING, LLC reassignment BIOSAFE ENGINEERING, LLC ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: WASTE REDUCTION BY WASTE REDUCTION, INC.
Assigned to DIGESTOR, LLC reassignment DIGESTOR, LLC ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: BIOSAFE ENGINEERING, LLC
Assigned to OLD NATIONAL BANK, N.A. reassignment OLD NATIONAL BANK, N.A. SECURITY AGREEMENT Assignors: BIOSAFE ENGINEERING, LLC, DIGESTOR, LLC, STI BIOSAFE, LLC, STI PATENT, LLC
Priority to US12/364,012 priority patent/US7829755B2/en
Priority to US12/913,830 priority patent/US20110040138A1/en
Priority to JP2011033590A priority patent/JP2011156531A/ja
Priority to US13/053,927 priority patent/US20110171073A1/en
Abandoned legal-status Critical Current

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    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/30—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
    • A62D3/35—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by hydrolysis
    • A—HUMAN NECESSITIES
    • A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61L—METHODS 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
    • A61L11/00—Methods specially adapted for refuse
    • A—HUMAN NECESSITIES
    • A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61L—METHODS 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
    • A61L2/00—Methods or apparatus for disinfecting or sterilising materials or objects other than foodstuffs or contact lenses; Accessories therefor
    • A61L2/02—Methods or apparatus for disinfecting or sterilising materials or objects other than foodstuffs or contact lenses; Accessories therefor using physical phenomena
    • A61L2/04—Heat
    • A—HUMAN NECESSITIES
    • A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61L—METHODS 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
    • A61L2/00—Methods or apparatus for disinfecting or sterilising materials or objects other than foodstuffs or contact lenses; Accessories therefor
    • A61L2/16—Methods or apparatus for disinfecting or sterilising materials or objects other than foodstuffs or contact lenses; Accessories therefor using chemical substances
    • A61L2/18—Liquid substances or solutions comprising solids or dissolved gases
    • A—HUMAN NECESSITIES
    • A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61L—METHODS 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
    • A61L2/00—Methods or apparatus for disinfecting or sterilising materials or objects other than foodstuffs or contact lenses; Accessories therefor
    • A61L2/24—Apparatus using programmed or automatic operation
    • 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
    • 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
    • B09B3/0075—Disposal of medical waste
    • 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
    • B09B3/40—Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • G—PHYSICS
    • G21—NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21F—PROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00—Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28—Treating solids
    • G21F9/34—Disposal of solid waste
    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/02—Chemical warfare substances, e.g. cholinesterase inhibitors
    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/04—Pesticides, e.g. insecticides, herbicides, fungicides or nematocides
    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20—Organic substances
    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20—Organic substances
    • A62D2101/28—Organic substances containing oxygen, sulfur, selenium or tellurium, i.e. chalcogen
    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2203/00—Aspects of processes for making harmful chemical substances harmless, or less harmful, by effecting chemical change in the substances
    • A62D2203/10—Apparatus specially adapted for treating harmful chemical agents; Details thereof

Definitions

  • This invention relates to the field of waste disposal and, more particularly, to a system and method for the digestion and sanitary disposal of waste material, such as infectious waste material and other hazardous, biohazardous, or radioactive waste.
  • waste may include surgical and pathological tissues, animal tissues, cadavers, blood and other bodily fluids, disposable matter exposed to blood, and other potentially infectious or dangerous body fluids of patients or animals.
  • regulated medical waste RMW
  • LLRW animal carcasses containing compounds labeled with 14 C or 3 H or other radioisotopes are classified as LLRW. Because state and federal guidelines regulate the disposal of LLRW, special precautions must be followed in their disposal. Currently, the two methods commonly used in disposing of this type of waste are incineration and land burial. Presently, federal law allows for incineration only when the animal carcass contains a radioisotope concentration below a certain level. However, even when radioisotope concentrations are below this level, incineration may be further limited by state and local agencies. When the levels of radioactivity in the animal carcasses are below acceptable de minimis levels as defined by federal, state, and local authorities, the disposal thereof is not subject to any additional regulation as a radioactive waste.
  • this radioactive material is disposed of through the general sewage system because the level of the radioactive materials discharged by the body into the sewer system is sufficiently diluted such that it no longer poses any hazard to public health and safety. This process is well within the state and federal disposal regulations for LLRW disposal. However, LLRW contained in animal remains are not readily capable of disposal through such means because the animals are naturally solid waste.
  • the present invention relates to a system for degrading, digesting or neutralizing undesirable materials by subjecting them to a controlled alkaline hydrolysis cycle.
  • the system includes an apparatus having means for receiving the undesirable materials, such as a closeable reaction vessel.
  • the apparatus further includes means for controlling the operation of the system.
  • the apparatus also includes means for introducing water within the interior of the vessel in a predetermined amount based on the maximum volume of the vessel and means for introducing an alkali compound within the interior of said vessel in predetermined amount based on the maximum volume of the vessel.
  • the apparatus includes means for heating the interior of the vessel to a first predetermined temperature level after the introduction of water and alkali compound into the interior of the vessel for a duration sufficient to produce a safely disposable resultant.
  • the method provided by the invention generally comprises the steps of providing a sealable vessel, filling the vessel with a highly alkaline solvent, immersing the waste matter containing the undesirable elements within the highly alkaline solvent, and heating the highly alkaline solvent.
  • the waste matter is allowed to remain within the highly alkaline solvent until the hydrolyzable matter is degraded or digested (i.e., substantially hydrolyzed), thereby forming a sterile solution and sterile solid waste.
  • aqueous solution and any resultant solid waste may then be disposed of through conventional means, such as a sanitary sewer, anaerobic fermentor, local landfill facility, or, if appropriate, by land application as fertilizer (either in liquid or solid form) or by mixing with peat, compost, or other cellulosic material.
  • conventional means such as a sanitary sewer, anaerobic fermentor, local landfill facility, or, if appropriate, by land application as fertilizer (either in liquid or solid form) or by mixing with peat, compost, or other cellulosic material.
  • One object of the present invention is to provide an improved system, method and apparatus for disposing of hydrolyzable waste matter. Related objects and advantages of the present invention will be apparent from the following description.
  • FIG. 1 is a schematic representation of the system provided by a currently preferred embodiment of the invention.
  • FIG. 2 is a flowchart representation of the method provided by a currently preferred embodiment of the invention.
  • FIGS. 3A, 3B and 3 C are side, top and bottom elevations, respectively, of a holding container according to a first embodiment of the present invention for receiving and storing the waste matter within the vessel chamber interior during the digestion cycle;
  • FIG. 4A shows an exploded elevation of a unique vacuum balancer device provided by the invention
  • FIGS. 4B and 4C show the vacuum balancer of FIG. 4A in its open and closed states, respectively;
  • FIGS. 5 A- 5 D show various views of agitating injector means provided by this invention.
  • FIGS. 6 A- 6 C are top, front and side elevations, respectively, of a vessel chamber according to a second embodiment of the present invention for receiving and storing waste matter therewithin during a hydrolytic digestion cycle;
  • FIG. 6D shows an exploded perspective view of the embodiment of FIGS. 6 A- 6 C;
  • FIG. 6E is a plumbing schematic of the embodiment of FIGS. 6 A- 6 C;
  • FIGS. 7 A- 7 C are top, side and end elevations, respectively, of a vessel chamber according to a third embodiment of the present invention.
  • FIG. 7D is a plumbing/electrical schematic of the embodiment of FIGS. 7 A- 7 C.
  • This invention involves a system and method for treating and safely disposing of waste matter containing undesirable agents or elements, such as but not limited to animal carcasses, animal tissue, organic material, organophosphate pesticides and nerve gasses, nitric esters and aromatic nitro-compounds, chemotherapeutic agents and related alkylating agents (such as sulfur mustards, nitrogen mustards, and phosgene), antibiotics, plant, animal, and bacteriological toxins, non-protein toxins (such as aflatoxin and tetrodotoxin), animal venoms (such as snake, spider, scorpion, fish and amphibian venoms), plant catechols, polyphenols, infectious, biohazardous, hazardous, and radioactive materials.
  • the system and method of this invention is designed and intended to comply with all federal, state, and local laws or regulations presently in existence applicable to the disposal of such waste.
  • the method of the invention comprises the steps of providing a sealable vessel, providing a highly alkaline solvent, immersing the waste matter containing the undesirable elements within the solvent within the interior of the vessel, heating the solvent and the waste matter, and allowing the waste matter to remain within the solvent until digested or degraded, thereby forming a sterile aqueous solution and sterile solid waste.
  • the extent of digestion or degradation of the waste matter may be increased by treating the waste under pressures above one atmosphere, by adding catalytic agents to the solvent bath, or both.
  • the post-digestion end product may then be directly disposed of through conventional disposal means, such as a sanitary sewer or landfill, or even used as a fertilizing agent in land use applications.
  • the post-digestion stage may also include rinsing or flushing of the resultant waste product and the interior of the vessel.
  • the system and method of this invention also substantially reduce the amount of post-digestion solid waste to be disposed of.
  • the inventors herein have determined that completeness of degradation/digestion (time vs. temperature curves) may be determined by measuring the rate of production of amino acids as the digestion process proceeds. When that process reaches an asymptote, digestion is considered complete.
  • the waste matter such as animal carcasses or remains, for example
  • the waste matter is placed within a holding container that is then placed within the interior of the vessel.
  • the lid of the vessel is then secured by way of conventional lid clamps.
  • the load of waste matter placed in the vessel for digestion should be at least 10% of the capacity of the vessel (by weight) but not more than 60% of the total weight of the capacity of the vessel.
  • the digestion cycle is then initiated, ultimately resulting in the waste matter being completely immersed in the highly basic solvent.
  • a “highly alkaline solvent” or “highly basic solvent” may include a 1 - 2 molar (M) aqueous solution of an alkali metal hydroxide, an alkaline earth metal hydroxide or an alkaline earth metal oxide.
  • this solvent should have a pH of at least above 13, preferably in the range of 13 to 14.
  • An aqueous solution of sodium hydroxide (NaOH—also commonly known as caustic soda or sodium hydrate) or potassium hydroxide (KOH—also commonly known as caustic potash or potassium hydrate) is preferred.
  • aqueous solutions of NaOH or KOH solutions containing calcium oxide (CaO—also commonly known as burnt lime, calx or caustic lime), ammonium hydroxide (NH 4 OH—also commonly known as aqua ammonia) or magnesium hydroxide are also suitable for some applications.
  • a suitable highly basic solvent may consist of a 0.1 M to 2.5 M solution of NaOH in water, or approximately 0.4%-10% sodium hydroxide (by weight) in water.
  • the hydrolyzable material should be immersed in a sufficient amount of solvent such that the material may be degraded or digested.
  • One ratio assuring excess base to carry out the digestion of the waste matter to completion, particularly animal tissue, is a 1:10 ratio of alkali metal hydroxide to wet tissue weight.
  • a further expression of this ratio is 40 kilograms of NaOH dissolved in 900 liters of water added to 100 kilograms dry weight protein or 40 kilograms of NaOH in 500 L H 2 O added to 500 kilograms fresh or frozen waste matter by weight.
  • the highly basic solvent should be heated to a temperature of at least about 90° C., and preferably 110° C. to 150° C.
  • reaction it is preferable to allow the reaction to proceed in a closed reaction vessel after the waste matter has been immersed within the solvent. Reducing the amount of CO 2 available to the reaction is beneficial in order to maintain the ideal rate and stoichiometry of the reaction. This may be done by simply removing or limiting any contact that the highly basic solvent has with the environment.
  • One way to increase the speed of the reaction process is to heat the solvent, preferably to temperatures of 110° C. to 150° C. Conducting the reaction in a sealed vessel under increased atmospheric pressure also reduces the reaction time needed to digest the animal tissue.
  • a preferred mode includes heating the solvent to a temperature of about 150° C. for a duration of about three (3) hours at a pressure of about 55 PSIG (or about 3.8 atmospheres).
  • detergents to a concentration of up to 1% to the solvent, examples being sodium lauryl sulfate or deoxycholate, may also be added to increase the rate of digestion, if desired. It should also be noted that addition of detergents to the solvent also has the added advantage of dispersing nonsaponifiable lipids, and aiding in the sterilization of biological materials.
  • the reaction rate will depend on specific variables such as: the temperature of the solvent, pressure in the reaction vessel, the nature and volume of the waste matter, i.e., the physical size of the carcasses or waste tissue, and the ratio of waste matter to the volume of the highly basic solvent. As the reaction rate will vary, the time that the waste matter must remain immersed in the solvent will also vary. However, regardless of the reaction rate, the waste matter should remain completely immersed within the solvent until solubilized and hydrolyzed. Allowing the waste matter to remain within the solvent until digestion is achieved will also help produce a more sterile solution.
  • the first type of debris consists of rubber, plastic, or cellulosic materials that a lab animal may have ingested, as well as debris remaining from experimental or surgical procedures, such as surgical clips, sutures, glass, and bits of plastic or paper. Solid items such as these never incorporate the radioactive isotopes. Once sterilized, such solid items are also not considered biomedical waste in most jurisdictions. This type of debris may often be simply disposed of as ordinary sterile solid waste upon being isolated from the solution and washed.
  • the second type of solid debris remaining undissolved includes inorganic portions of an animal's skeletal structure and teeth. Unless a radioisotope capable of incorporation into the inorganic portion of bones and teeth is used, the inorganic component of the skeletal remains will not contain the radioactive isotope and may be disposed of as solid sterile waste. The skeletal remains, when removed from the solvent and washed, are extremely friable.
  • the solution may comprise a diluted concentration of radioactive isotopes that meet the MPC requirements under the federal regulations, as well as an alkaline mixture of alkai metal salts of amino acids and peptides, sugar acids, nucleotides, small peptides, fatty acids from lipids, phosphates from lipid and nucleic acid breakdown, soluble calcium salts, pigments, sugars, sugar alcohols, hydrocarbons, and inorganic acids derived from the electrolytes normally within solution in body fluids.
  • the solution contains compounds that are non-toxic and are biodegradable by bacteria or fungi found in soil and sewage treatment systems, and possibly a very dilute amount of radioactive solute.
  • the solution at the end of the digestion cycle contains only non-toxic biodegradable materials and the water released from the animal tissue, further dilution of the solution may not be required for safe disposal. Further dilution to reduce the alkalinity of the solution will be accomplished, however, by the rinsing of the vessel and the inorganic remains with excess water, by the temperature regulating co-flush for the effluent, and the general daily effluent volume of the site, institution, or company. (Deliberate dilution of soluble radioactive waste is usually not permitted by the applicable local, state, federal and national regulations.) Further, carbon dioxide may be injected into the solution at this stage to adjust its pH down to between about 7.5 and 10. At this stage, however, the concentration of radioisotope in the solution should be well within the level that may be safely released to a sanitary sewer.
  • This sterile, neutral, aqueous solution that contains the breakdown products of cells and tissues, and may contain remnants of radioisotopically labeled solutes may be safely disposed of utilizing methods commonly used to dispose of everyday nontoxic and biodegradable substances. It is entirely safe to dispose of this solution using disposal means such as sanitary sewage systems and other disposal means appropriate for the disposal of these simple biodegradable compounds.
  • FIG. 1 a preferred system 10 for carrying out the invention is shown schematically, comprising a closed reaction chamber or vessel 12 capable of containing the solvent solution and the waste matter such as the animal tissue or carcass or regulated medical waste.
  • a portion of vessel 12 is defined by a double-walled structure for purposes discussed below.
  • the vessel must be constructed from material capable of withstanding the pH levels, temperatures, and pressures employed in this invention. Suitable materials include certain formulations of stainless steel.
  • Vessel 12 must also be capable of being closed in an air tight fashion to provide the necessary environment within the vessel interior 14 for the controlled alkaline hydrolysis cycle to be carried out to completion.
  • the lid or cover 16 of the vessel 12 must be capable of being closed tightly, pressure and air tight, to withstand the temperatures and pressures of the digestion cycle and prevent the inadvertent introduction of atmosphere (particularly carbon dioxide) into the vessel interior or, more importantly, prevent the escape or inadvertent exhausting of the contents of the vessel interior to atmosphere.
  • Such closure of the vessel may be achieved by conventional lid clamps well known in the industry (not shown).
  • control means preferably includes an information screen, a disk drive for the automation program software, a disk drive or like recording means for recording process parameters and data during operation, and a keyboard for alternative manual input or operation.
  • System 10 further includes a weight transducer 18 (shown schematically) coupled to one or more of the legs of the vessel 12 for determining the weight of the waste matter received within the vessel and for generating an output signal indicating such weight data.
  • the transducer is preset such that the weight of the vessel without contents equals zero weight.
  • the contents weight data is then inputted to the PLC control means for, based on the weight output data, determining the appropriate amounts of water and solvent to introduce into the interior of the vessel, utilizing a water supply 20 , via conduit 20 a , and a spray ball or nozzle 20 e located within the vessel interior, and solvent supply 22 , via solvent loop conduit 24 and pump 26 .
  • Solvent is injected into the interior of vessel 12 via injector means 28 , which are shown schematically in FIG. 1 and in more detail in FIGS. 5A through 5D.
  • injector means 28 mixes and agitates the contents of the vessel interior 14 and enhances the interaction between the highly basic solvent and the waste matter being digested by directing the jet flow of the solvent solution upwardly at the bottom 62 of the container 60 (see FIG. 5A) to keep the vessel contents moving and to prevent waste matter from accumulating at the bottom of container 60 and not mixing thoroughly with the solvent. By doing so, the agitating injector means also shortens the digestion cycle time.
  • this invention is not limited to the agitating injector means described and shown herein but contemplates any means that introduces the solvent into the interior of the vessel.
  • the mere introduction of solvent into the vessel will “mix” the alkali-water solution with the waste matter. Introducing heat also induces mixing.
  • agitation of the contents may be achieved by various means, including external mechanisms coupled to the vessel, such as a rocking or shaking assembly that physically moves the vessel. All such alternative means of mixing or agitating the vessel contents are contemplated by this invention.
  • the preferred process requires that the solvent solution be heated in order to accelerate the digestion process to completely dissolve the animal tissue, carcasses, or medical waste.
  • a heating means preferably defined by a stainless steel steam jacket 30 arranged circumferentially about the vertical sides and base of vessel 12 for heating the interior of the vessel to a first predetermined temperature level after the introduction of water and solvent into the vessel interior 14 . Heated water or steam is circulated between the walls of the double walled vessel 12 . While the steam jacket defines a preferred embodiment, any heating means commonly known and used for heating solutions could be utilized in this invention.
  • Steam is supplied to jacket 30 by a steam supply 32 and conduit 32 a provided with a cut-off valve 32 b and a regulating valve 32 c .
  • the system further includes a vent 34 , which is disposed in the open state upon initiation of the cycle and thereafter closed by PLC control means when the temperature within the vessel reaches a predetermined first temperature.
  • the temperature within the vessel 12 is gauged by a vessel thermocouple 36 a
  • the pressure within the vessel is gauged by a PSI transducer 38 .
  • the temperature within the solvent loop is gauged by a loop thermocouple 36 b.
  • an eductor apparatus 40 is utilized for creating a vacuum within the vessel interior 14 .
  • vent 34 When vent 34 is open and flushing water is admitted to the eductor by the water supply 20 via conduit 20 b , the action of the eductor draws the air and any odorous gas from within the interior of the vessel through conduit 34 a , whereupon the air and odorous gas is eventually entrapped with the flushing water at eductor 40 to, in turn, be removed from the system via drain conduit 42 a to sanitary drain 42 .
  • the temperature of the fluid at the drain may be gauged by a thermocouple 44 to monitor the effluent temperature prior to disposal in a sanitary sewer system.
  • the vacuum-creating eductor substantially reduces the odorous gases that may escape from rotting carcasses while the vessel is filling, before the vent valve 34 is closed.
  • a vacuum balancing device 46 shown and discussed below in relation to FIGS. 4 A- 4 C is provided that selectively admits ambient air to the vessel interior when the internal vacuum pressure reaches or exceeds the threshold pressure of the vacuum balancer 46 . While the vacuum balancer shown and discussed herein is of a unique design, any vacuum balancing device that will not leak fluid or collect condensed fluid may be suitable for the effective operation of this invention.
  • vacuum balancer 46 is shown in detail comprising a vacuum clamp 47 , a vacuum plug 48 , an annular end cap 49 , a vacuum gasket 50 , an O-ring 51 , a flat washer 52 , a socket head cap screw 53 , an upper ferrule portion 54 , a lower ferrule portion 55 , a spring 56 and a thermometer cap 57 .
  • spring 56 urges the cap screw 53 , washer 52 and the vacuum plug 48 upwardly such that O-ring 51 abuttingly engages the vacuum gasket 50 , thereby preventing any air from passing therethrough.
  • the preferred system further includes a permeable container capable of holding the waste tissue or remains or medical waste within the vessel interior 14 during the digestion cycle to completely immerse the waste material within the solvent solution.
  • a permeable container capable of holding the waste tissue or remains or medical waste within the vessel interior 14 during the digestion cycle to completely immerse the waste material within the solvent solution.
  • a container preferably includes a cylindrical article 60 defined by a steel mesh screen 62 having an upper rim portion 64 , a lower rim portion 66 , and a lid 68 to enclose the waste tissue within the container 60 .
  • Attached to the lid 68 is preferably a handle 68 a . As shown in FIGS.
  • both the lid 68 and the bottom of the container include the stainless steel mesh 62 , which is preferably constructed from stainless steel screen mesh having about 3 mm to about 6 mm (one-eighth (1 ⁇ 8) to one-quarter (1 ⁇ 4) inch) screen mesh.
  • the lid 68 may be releasably secured to the body 61 of the container via conventional means.
  • Handle 68 a may be equipped with an eyelet-like portion 68 b to receive attachment means for lowering and raising the container into and out of the vessel interior.
  • the permeable container 60 may be hoisted out of the vessel 12 , or removed out of another port arranged in the side of the vessel 12 during a “clean side” removal as discussed below, thereby removing the undigested solid debris remaining within the container 60 .
  • the height “h” (FIG. 3A) and diameter “d” (FIG. 3C) of the container may be varied to accommodate varying amounts of waste tissue or carcasses of animals of varying sizes, or of medical waste of varying volume or quantity.
  • the preferred embodiment includes agitating injector means 28 shown in FIGS. 5 A- 5 D to accelerate the reaction rate between the solvent solution and the waste tissue by keeping the solvent in motion while the reaction is occurring.
  • One such means is accomplished by circulating the solvent via loop 24 and pump 26 (FIG. 1) and introducing the solvent into the interior of the vessel by injecting it via multiple jet ports at varying angles generally aimed at the bottom of the holding container 60 (see FIG. 5A).
  • Such an arrangement keeps the solvent moving within the vessel interior, as well as keeping waste matter from accumulating on the bottom of the container 60 , which can result in the prolonging or slowing of the digestion process.
  • Agitating injector means 28 preferably comprise a plurality of concentric flow reducers or nozzles 28 a coupled to respective elbow members 28 b , which in turn are coupled to respective tube members 28 c , which finally are coupled to respective cross members 28 d .
  • Each cross member 28 d is connected to a screw-coupling member 28 e for affixing the injector means to the upper end of the inflow conduit 24 a .
  • Nozzles need not be conical as illustrated in FIGS. 5 A-D, but may vary in shape and size to suit particular applications.
  • the opposing nozzles 29 a are disposed at an included angle A of about 22.5 degrees (FIG.
  • angles A and B may be varied to suit particular applications.
  • the inflow conduit 24 a delivering solvent to injector 28 extends into and, in a coaxial fashion, extends upwardly through the outflow conduit 24 b .
  • Inflow conduit 24 a is smaller in diameter than outflow conduit 24 b such that the aqueous interior contents of the vessel 12 may drain downwardly into outflow conduit 24 b as shown by the reference arrows “a” in FIG. 5A.
  • Outflow conduit 24 b carries the solvent back to the solvent loop 24 and pump 26 (see FIG. 1) and when necessary, through drain valve 41 to the sanitary drain 42 . It will be understood by those skilled in the art that the points of connection “b” shown in FIG.
  • the injector means may include separate injector nozzles disposed in fixed arrangements about the interior of the vessel to direct solvent at the waste matter. Such a configuration is useful in larger applications involving large diameter containers and large-volume waste matter. Such separate fixed injections may be utilized in lieu of or in addition to the injector assembly 28 shown and described herein.
  • FIG. 2 presents a flowchart depicting the cycle process of this invention.
  • the waste matter is weighed and the weight and water and solvent ratios automatically determined by the PLC control means (box a).
  • the appropriate amount of water (box b) and solvent (box c) is then introduced into the interior of the vessel based on the weight calculations made by the PLC control means.
  • Water is typically added at the rate of 60% water to 40% tissue by weight, but may be added in other amounts according to the requirements of particular load amounts and types of waste.
  • the alkali is added at the predetermined concentration based on the tissue weight. This is typically equivalent to a solution of 50% NaOH added by weight at a ratio of 15 to 20% of the total tissue weight.
  • the heating means 30 (FIG.
  • System 10 then heats the vessel interior (box d) to the digestion cycle temperature while closing the vent 34 (box e).
  • System 10 then maintains that elevated temperature for a predetermined duration (box f) as calculated by the PLC control means based on the weight of the waste matter placed in the vessel for digestion.
  • the system typically maintains the digestion temperature at about 150° C. (302° F.) for about 3 hours, or if operated at a lower temperature, for an appropriate time for that temperature based on a theoretical full digestion time of 16 hours at 100 degrees Celsius and halving the digestion cycle time for each 10 degrees Celsius increase in temperature, in accordance with the thermodynamics equation discussed above. More preferably, an appropriate safety factor is added to the theoretical digestion time at a given temperature to accommodate differences arising from variations in load size, composition, distribution, and the like.
  • the system goes into the cooling cycle after digestion whereupon cooling water is admitted to the steam jacket interior 30 from water supply 20 (FIG. 1) via conduit 20 c to lower the temperature of the vessel interior (box g). This continues until the internal pressure within the vessel reaches about atmospheric pressure (101.3 kilopascals/14.7 pounds per square inch (PSI)), shown as a reading of zero on the pressure gauge or transducer, which measures pressure above 1.0 atmosphere.
  • PSI pounds per square inch
  • the vessel is drained to the sewer (sanitary drain 42 ) by the control means opening the vent 34 (box h) and drain valve 41 (box i) to drain the liquid contents from within the vessel interior down to a predetermined point, at which point drain valve 41 is closed (box j) while flushing water is continued to be introduced to flush the vessel interior (box k) until the interior is preferably about half full.
  • the vessel interior is sprayed with rinsing liquid and the contents are circulated through the injectors 28 for a predetermined time before the drain is again opened to rinse away any residual materials remaining within the interior of the vessel (boxes l and m).
  • This invention also presents a method for digesting or neutralizing waste matter comprising organic tissue or infectious, biohazardous, hazardous, or radioactive agents, by subjecting the waste matter to a controlled alkaline hydrolysis cycle and generating a sterile resultant suitable for conventional sanitary disposal.
  • the preferred method compromises the steps of:
  • fill levels discussed above may be modified as a function of waste material load size, with larger loads requiring higher fill levels. In other words, enough liquid should be added such that the waste material is completely submerged for reduction by the alkaline solution.
  • an additional feature of the closed vessel is to allow the solid waste remains to be removed from a secondary opening (not shown) arranged on the vertical side of the vessel.
  • This feature allows the vessel to be positioned in such a configuration that the primary opening may be located within a contaminated portion of the facility, while the remaining portions of the system are located within a clean portion of the facility. This would allow contaminated materials to be processed and sterilized, then for the sterile solid waste remains to be removed from the secondary opening as sterile remains into a clean area for final disposal. Thereafter, the secondary opening would be sealed prior to the opening of the primary opening for the loading of waste for another processing cycle. Such a configuration is referred to as “dirty side feed/clean side removal.” Such an embodiment would alter step (u) above to read as follows:
  • the lid of the vessel Prior to filling the vessel with, for example, animal carcasses containing infectious or hazardous agents, the lid of the vessel is closed in order to “zero” the load scale. The lid is then opened and the vessel filled with waste matter to the desired volume. Preferably, the load should be at least 20% of the vessel's capacity (by weight) but not more than the weight capacity of the vessel, in which case the system will not operate and the excess weight must be removed.
  • the vessel lid is then closed and secured.
  • the PLC controller is then activated to initiate the digestion process by first determining the weight of the waste matter within the vessel. The digestion cycle is then initiated whereby water is preferably added at the rate of 60% water to 40% tissue by weight, alkali is added at the predetermined concentration based on the tissue weight. Such concentration is normally equivalent to a solution of 50% NaOH added by weight at a ratio of 15 to 20% of the total tissue weight.
  • the heating step is then initiated to raise the temperature of the interior of the vessel to the predetermined first digestive cycle temperature for a predetermined duration to completely digest the carcasses.
  • the cycle holds the digestion temperature to at least 110° C., preferably about 130° C., and most preferred about 150° C. At 150° C., the digestion cycle is normally about 3 hours in duration.
  • the PLC control means initiates the cooling cycle, utilizing cold water flushed through the sleeve jacket 30 of the vessel. Once the vessel has cooled sufficiently, the vessel is drained to the sewer, then partially refilled with cold water and the interior rinsed. The vessel is then drained again, partially refilled again and this second rinse solution heated if desired. After this hot rinse, the vessel is then drained and it contents sprayed with a final spray rinse. The cooling cycle is then complete and the system shuts down while the drain is opened to empty completely the interior of the vessel.
  • the vessel may at that point be opened and the waste-carrying basket removed and emptied. The basket is then replaced, making the system ready for a new cycle.
  • the operator should initiate the spray rinse cycle for a short duration, preferably about 30 seconds.
  • the vessel may be opened and the waste safely disposed of.
  • FIGS. 6 A- 6 E illustrate another preferred embodiment of the present invention, a chemical waste reduction system 110 for chemically reducing masses of hydrolyzable waste materials ranging up to about 25 pounds.
  • the system 110 includes a closeable reaction chamber or vessel 112 capable of containing a highly alkaline solvent solution and a volume of waste matter (such as animal tissue or carcasses, regulated medical waste, contamination on surgical instruments, and the like).
  • waste matter such as animal tissue or carcasses, regulated medical waste, contamination on surgical instruments, and the like.
  • the hydrolyzable waste materials may be organic contamination on medical instruments not specifically limited to surgical instruments.
  • a portion of the vessel 112 is defined by a double-walled structure.
  • the vessel interior 114 should be coated with an alkaline resistant material, such as stainless steel or a ceramic material.
  • the vessel 112 is constructed from a material capable of withstanding the combination of pH levels, temperatures, and pressures it may be subjected to during a hydrolysis operation. Suitable materials include certain formulations of stainless steel.
  • the vessel 112 is preferably capable of being closed in an air tight fashion to provide the necessary environment within the vessel interior 114 for the controlled alkaline hydrolysis cycle to be carried out to completion, as well as to prevent the highly alkaline solvent and waste materials from escaping into the environment.
  • the lid or cover 116 of the vessel 112 is preferably capable of being closed tightly and sealed shut to withstand the temperatures and pressures of the digestion cycle and prevent the inadvertent introduction of atmosphere (particularly carbon dioxide) into the vessel 112 interior and, more importantly, prevent the escape or inadvertent exhausting of the contents of the vessel 112 interior to atmosphere.
  • Such closure of the vessel 112 may be achieved by conventional lid clamps well known in the industry (not shown), or by any convenient closure means available to one of ordinary skill in the art.
  • the system 110 further includes an electronic controller 117 , such as the conventional programmable logic controller (PLC) means described above.
  • the system 110 further includes a weight sensor or transducer 118 (shown schematically) operationally coupled to the vessel 112 and electrically coupled to the electronic controller 117 for determining the weight of the waste matter received within the vessel 112 and for generating an output signal to the controller 117 including such weight data.
  • the transducer 118 is normally preset such that the weight of the vessel 112 without contents equals zero weight. The contents weight data may then be inputted to the electronic controller 117 for, based on the weight output data, determining the appropriate amounts of water and solvent to introduce into the interior of the vessel 112 .
  • a predetermined amount of alkaline solvent (formulated to digest the maximum waste material load of the vessel 112 ) may be preferred for use with any amount of waste material up to the maximum load of the vessel 112 .
  • the weight data may instead be used to disable the system 110 if the maximum capacity of the vessel 112 is exceeded.
  • the system 110 further includes connecting a water supply 120 operationally connected to the vessel 112 , such as via conduit 120 a .
  • the highly alkaline solvent is produced in the vessel 112 by mixing water and dry alkaline earth, alkali hydroxides, or alkali metal oxides therewith to form a highly alkaline solution. Alternately, a highly alkaline solution may first be prepared and then added into the vessel 112 .
  • FIG. 6E illustrates the plumbing of the system in greater detail.
  • Conduit 120 a connects through valves 124 to water inlet 126 and/or injector means 128 for introducing water into the vessel 112 .
  • the system 110 preferably includes a heater 130 operationally connected to and positioned in thermal communication with the vessel 112 . More preferably, the heater 130 is an electric hot plate in thermal contact with the base of the vessel 112 capable of heating the interior of the vessel 112 to a first predetermined temperature level after the introduction of water and solvent into the vessel interior 114 . Alternately, any convenient type of heater 130 may be used to heat the vessel 112 , such as the steam jacket described in the previous embodiment or any other heating means known to one of ordinary skill in the art.
  • Electricity is supplied to the heater 130 by a power supply 132 via conduit 132 a .
  • a temperature sensor 119 (such as a thermocouple or the like) is positioned in thermal communication with the interior of the vessel 114 such that the temperature of the interior of the vessel 114 may be continuously monitored or queried upon demand.
  • the heater 130 and the temperature sensor 119 are both connected in electric communication with electronic controller 117 , such that electronic controller 117 may regulate the output of the heater 130 to maintain the temperature of the interior of the vessel 114 according to a predetermined or desired time/temperature profile.
  • the system 110 also preferably includes a vent 140 (discussed in greater detail below), which is preferably disposed in the open state upon initiation of the cycle and thereafter is preferably closed by the electronic controller 117 when the temperature within the vessel 112 reaches a predetermined first temperature.
  • the temperature within the vessel 112 is gauged by the vessel thermocouple 119 , while the pressure within the vessel 112 may be measured by a pressure sensor (not shown) such as a PSI transducer.
  • the system 110 also preferably includes agitation means 133 for circulating and mixing solvent and partially dissolved waste matter.
  • Agitation means 133 is preferably magnetic, such as a magnetic stirrer 135 positioned such that a magnetic field may be generated within the vessel 112 and used to rotate one or more magnetic stir rods 137 positioned within the vessel 112 .
  • the magnetic stirrer 135 may be functionally combined with the heater 130 , such as in a hot plate/stirrer combination readily known to one of ordinary skill in the art. While a magnetic stirrer 135 is preferred, agitation means 133 may include any convenient stirring means familiar to one of ordinary skill in the art to mix and agitate the contents of the vessel interior 114 .
  • Such agitation enhances the interaction between the highly alkaline solvent and the dissolving waste matter to keep the vessel contents moving and to prevent waste matter from accumulating at the bottom of container 112 .
  • a further benefit of agitation is the reduction of digestion cycle time. Agitation of the contents may be achieved by various means, including external mechanisms coupled to the vessel 112 , such as rocking or shaking assembly that physically moves the vessel 112 . All such alternative means of mixing or agitating the vessel contents are contemplated by this invention.
  • the system 110 also includes a ventilation system for relieving excess pressure from the vessel interior 114 when the vessel 112 is closed.
  • a fluid conduit 142 connects the vent 140 to a drain line 144 .
  • a check valve 146 is connected between the 140 and the drain line 144 to prevent contamination of the vessel 112 .
  • the drain line 144 is also connected to a water outlet 148 formed in the vessel 112 for drainage of the solvent solution and any dissolved waste matter.
  • the system may also include an eductor 150 connected between the water outlet 148 and the drain line 144 . Flushing water is admitted to the eductor 150 by the water supply 120 via conduit 120 b . The action of the eductor 150 draws the air and any odorous gas from within the interior of the vessel 112 through fluid conduit 142 , whereupon the air and odorous gas is eventually entrapped with the flushing water at eductor 150 to, in turn, be removed from the system via drain conduit 144 .
  • the temperature of the fluid at the drain may be gauged by a thermocouple (not shown) to monitor the effluent temperature prior to disposal in a sanitary sewer system.
  • the vacuum-creating eductor 150 substantially reduces the odorous gases that may escape from rotting carcasses while the vessel 112 is filling, and may also be actuated to draw gasses from the vessel 112 while or after the waste is being hydrolyzed, if desired.
  • the interior of the vessel may be rinsed with cold water via water inlet 128 with the water outlet 148 open. After a few minutes, the water outlet 148 is closed to allow the vessel 112 to begin to fill with water.
  • the vessel 112 is now considered ready for another hydrolysis cycle, and may be filled with waste for reduction. Once the vessel 112 is filled with a predetermined amount of water (at least enough such that the waste matter is covered) a predetermined amount the highly alkaline powder is added and combined with the water to form a highly alkaline solvent solution.
  • the contents are then agitated by the magnetic stirrer 135 and stir rod 137 , and the contents are heated to about 98 degrees Celsius for a predetermined period of time to chemically reduce the waste material.
  • the vessel 112 is then allowed to cool, and the water outlet 148 is opened and rinse water is introduced into the vessel 112 .
  • the water outlet may be closed to allow rinse water to accumulate and rinse any remaining solids.
  • the water outlet 148 is then re-opened and the liquid contents of the vessel 112 are allowed to drain. Thereafter, if desired or necessary, the water outlet 148 is closed for a second time and the vessel 112 is allowed to again fill with water. Heat may then be applied again to the vessel 112 to heat the liquid within the vessel to approximately 95° C. (203° F.), whereupon an enhanced rinse/diffusion is initiated.
  • the time and temperature used in this post-digestion heating stage may vary.
  • the preferred system further includes a liquid permeable container 160 , such as a basket, capable of holding the waste material within the vessel interior 114 during the waste reduction operation to completely immerse the waste material within the solvent solution.
  • a liquid permeable container 160 such as a basket, capable of holding the waste material within the vessel interior 114 during the waste reduction operation to completely immerse the waste material within the solvent solution.
  • a container preferably includes a cylindrical article 60 defined by a steel mesh screen 62 having an upper rim portion 64 , a lower rim portion 66 , and a lid 68 to enclose the waste tissue within the container 60 .
  • Attached to the lid 68 is preferably a handle 68 a .
  • the container 60 is sized to fit within the interior of the vessel 114 .
  • both the lid 68 and the bottom of the container include the stainless steel mesh 62 , which is preferably constructed from stainless steel screen mesh having about 3 mm to about 6 mm (one-eighth (1 ⁇ 8) to one-quarter (1 ⁇ 4) inch) screen mesh.
  • the lid 68 may be releasably secured to the body 61 of the container via conventional means.
  • Handle 68 a may be equipped with an eyelet-like portion 68 b to receive attachment means for lowering and raising the container into and out of the vessel interior. After the waste reduction operation has completed, the container 60 may be hoisted out of the vessel 112 , thereby removing the undigested solid debris remaining within the container 60 .
  • the method of using the system 110 is similar to that of the first embodiment discussed above, and includes the elements of providing a substantially alkaline-resistant vessel, providing a highly alkaline solvent, providing an amount of waste matter having a mass less than or equal to a predetermined maximum mass, immersing the waste matter in the solvent within the interior of the vessel, heating the solvent and the waste matter, and allowing the waste matter to remain within the solvent until digested to form an aqueous solution with residual solid waste matter.
  • the waste matter remains in the solvent for a predetermined length of time calculated to substantially completely dissolve a predetermined maximum mass of waste matter at a predetermined operating temperature.
  • the predetermined operating temperature is between about 95 and about 98 degrees Celsius.
  • hydrolysis may be achieved at lower temperatures (i.e., 90 degrees Celsius or even lower) by increasing the cycle time according to the Q10 Rule, as discussed above.
  • the extent of digestion or degradation of the waste matter may be increased by lengthening the amount of time the waste matter is immersed in the solvent at the predetermined temperature, increasing the temperature of the solvent and waste matter, adding a catalyst material, or some combination of the above.
  • the post-digestion end product may then be directly disposed of through conventional disposal means, such as a sanitary sewer or landfill, used as a fertilizing agent in land use applications, or the like.
  • the post-digestion stage may also include rinsing or flushing of the resultant waste product and the interior of the vessel.
  • the system and method of this invention also substantially reduce the amount of post-digestion solid waste to be disposed of.
  • FIGS. 7 A- 7 D illustrate still another preferred embodiment of the present invention, a chemical waste reduction system 210 for chemically reducing masses of hydrolyzable waste materials ranging up to about 3000 pounds or more.
  • the system 210 includes a closeable reaction chamber or vessel 212 capable of containing a highly alkaline solvent solution and a volume of waste matter (such as animal tissue or carcasses, regulated medical waste, and the like).
  • the vessel 212 is defined by a double-walled container structure.
  • the vessel interior 214 should be coated with an alkaline resistant material, such as a suitable stainless steel or a ceramic material.
  • the entire vessel 212 is constructed from a material capable of withstanding the combination of pH levels, temperatures, and pressures it may be subjected to during a hydrolysis operation, such as certain formulations of stainless steel.
  • the vessel 212 is preferably capable of being closed in an air tight fashion to provide the necessary environment within the vessel interior 214 for the controlled alkaline hydrolysis cycle to be carried out to completion as well as to prevent the highly alkaline solvent and waste materials from escaping into the environment.
  • the lid or cover 216 of the vessel 212 is preferably capable of being closed tightly and sealed shut to withstand the temperatures and pressures of the digestion cycle and prevent the inadvertent introduction of atmosphere (particularly carbon dioxide) into the vessel 212 interior and, more importantly, prevent the escape or inadvertent exhausting of the contents of the vessel 212 interior to atmosphere.
  • Such closure of the vessel 212 may be achieved by conventional lid clamps well known in the industry (not shown), or by any convenient closure means available to one of ordinary skill in the art.
  • the system 210 further includes an electronic controller 217 , such as the conventional programmable logic controller (PLC) means described above.
  • the system 210 further includes a weight sensor or transducer 218 (shown schematically) operationally coupled to the vessel 212 and electrically coupled to the electronic controller 217 for determining the weight of the waste matter received within the vessel 212 and for generating an output signal to the controller 217 including such weight data.
  • the transducer 218 is normally preset such that the weight of the vessel 212 without contents equals zero weight. The contents weight data may then be inputted to the electronic controller 217 for, based on the weight output data, determining the appropriate amounts of water and solvent to introduce into the interior of the vessel 212 .
  • a predetermined amount of alkaline solvent (formulated to digest fixed increments of waste material load) may be preferred for use with any amount of waste material up to the maximum load of the vessel 212 .
  • the weight data may instead be used to disable the system 210 if the maximum capacity of the vessel 212 is exceeded.
  • the system 210 further includes connecting a water supply 220 to the vessel 212 , such as via conduit 220 a .
  • the highly alkaline solvent is produced in the vessel 212 by mixing water and dry alkaline earth, alkali hydroxides, or alkali metal oxides therewith to form a highly alkaline solvent solution.
  • Conduit 220 a connects through valves 224 to water inlet 226 and/or injector means 228 for introducing water into the vessel 212 .
  • the system 210 preferably includes a heater 230 operationally connected to and positioned in thermal communication with the vessel 212 or immersed in the liquid contents of the vessel 212 .
  • the heater 230 is a burner (such as a natural gas burner, and oil burner, or the like) extending below the vessel 212 and in thermal communication therewith or inserted into the vessel 212 and in direct thermal communication with the vessel contents.
  • the burner is preferably adapted to generate sufficient thermal energy to heat the interior of the vessel 214 to a first predetermined temperature level after the introduction of water and alkaline solvent thereinto.
  • any convenient type of furnace or heater 230 may be used to heat the vessel 212 , such as the steam jacket described in the previous embodiment or any other heating means known to one of ordinary skill in the art.
  • a temperature sensor 219 (such as a thermocouple) is positioned in thermal communication with the interior of the vessel 214 such that the temperature of the interior of the vessel 214 may be continuously monitored or queried upon demand. More preferably, the heater 230 and the temperature sensor 219 are both connected in electric communication with electronic controller 217 , such that electronic controller 217 may regulate the output of the heater 230 to maintain the temperature of the interior of the vessel 214 according to a predetermined or desired temperature profile.
  • the system 210 may also optionally include agitation means for circulating and mixing solvent and partially dissolved waste matter.
  • the system 210 may also preferably include a vent 240 , which is preferably disposed in the open state upon initiation of the cycle and thereafter is preferably closed by the electronic controller 217 when the temperature within the vessel 212 reaches a predetermined first temperature.
  • a fluid conduit 242 connects the vent 240 to a fluid drain line or flue 244 .
  • the temperature within the vessel 212 is gauged by the vessel thermocouple 219 , while the pressure within the vessel 212 may be measured by a pressure sensor (not shown) such as a PSI transducer.
  • the interior of the vessel may be rinsed with cold water via water inlet 228 with the water outlet 248 open. After a few minutes, the water outlet 248 is closed to allow the vessel 212 to begin to fill with water.
  • the vessel 212 is now considered ready for another hydrolysis cycle, and may be filled with waste for reduction. Once the vessel 212 is filled with a predetermined amount of water (at least enough such that the waste matter is covered) a predetermined amount the highly alkaline powder is added and combined with the water to form a highly alkaline solvent solution. Alternately, a concentrated alkaline solution may be added to the water to yield a highly alkaline solvent solution.
  • the contents are then agitated by a stirring means, such as by pumping the highly alkaline solvent solution through the vessel 212 , and the contents are heated to about 98 degrees Celsius for a predetermined period of time to chemically reduce the waste material.
  • the vessel 212 is then allowed to cool, and the water outlet 248 is opened and rinse water is introduced into the vessel 212 .
  • the water outlet may be closed to allow rinse water to accumulate and rinse any remaining solids.
  • the water outlet 248 is then re-opened and the liquid contents of the vessel 212 are allowed to drain. Thereafter, if desired or necessary, the water outlet 248 is closed for a second time and the vessel 212 is allowed to again fill with water. Heat may then be applied again to the vessel 212 to heat the liquid within the vessel to approximately 95° C. (203° F.), whereupon an enhanced rinse is initiated.
  • the time and temperature used in this post-digestion heating stage may vary.
  • the preferred system further includes a liquid permeable container 260 , such as a basket, capable of holding the waste material within the vessel interior 214 during the waste reduction operation to completely immerse the waste material within the solvent solution.
  • the container 260 is preferably a basket shaped to fit into the vessel 212 and is preferably formed of alkaline-resistant perforated stainless steel. The perforation is preferably defined as a pattern of 6 mm (3 ⁇ 8 inch) holes formed through the steel basket 260 . After the waste reduction operation has completed, the container 260 may be hoisted out of the vessel 212 , thereby removing the undigested solid debris remaining within the container 260 .
  • the method of using the system 210 is similar to that of the embodiments discussed above, and includes the elements of providing a substantially alkaline-resistant vessel, providing a highly alkaline solvent, providing an amount of waste matter having a mass less than or equal to a predetermined maximum mass, immersing the waste matter in the solvent within the interior of the vessel, heating the solvent and the waste matter, and allowing the waste matter to remain within the solvent until digested to form an aqueous solution with residual solid waste matter.
  • the waste matter remains in the solvent for a predetermined length of time calculated to substantially dissolve a predetermined maximum mass of waste matter at a predetermined operating temperature.
  • the predetermined operating temperature is between about 95 and about 98 degrees Celsius.
  • the extent of digestion or degradation of the waste matter may be increased by lengthening the amount of time the waste matter is immersed in the solvent at the predetermined temperature, increasing the temperature of the solvent and waste matter, adding a catalyst material, or some combination of the above.
  • the post-digestion end product may then be directly disposed of through conventional disposal means, such as a sanitary sewer or landfill, used as a fertilizing agent in land use applications, or the like.
  • the post-digestion stage may also include rinsing or flushing of the resultant waste product and the interior of the vessel.
  • the system and method of this invention also substantially reduce the amount of post-digestion solid waste to be disposed of.

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  • Health & Medical Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Epidemiology (AREA)
  • Engineering & Computer Science (AREA)
  • Animal Behavior & Ethology (AREA)
  • Public Health (AREA)
  • Veterinary Medicine (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Business, Economics & Management (AREA)
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  • Toxicology (AREA)
  • General Engineering & Computer Science (AREA)
  • High Energy & Nuclear Physics (AREA)
  • Thermal Sciences (AREA)
  • Processing Of Solid Wastes (AREA)
  • Accommodation For Nursing Or Treatment Tables (AREA)
  • Fertilizers (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
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US10/263,043 1996-04-22 2002-10-02 Apparatus and method for chemically reducing waste materials Abandoned US20030040651A1 (en)

Priority Applications (18)

Application Number Priority Date Filing Date Title
US10/263,043 US20030040651A1 (en) 1998-10-20 2002-10-02 Apparatus and method for chemically reducing waste materials
CNA2003801023867A CN1735442A (zh) 2002-10-02 2003-10-01 化学还原废料的装置和方法
KR1020057005643A KR20050053723A (ko) 2002-10-02 2003-10-01 폐기물의 화학적 감소 기기 및 이의 방법
BR0315019-4A BR0315019A (pt) 2002-10-02 2003-10-01 Aparelho e método para reduzir quimicamente materiais de sobras
AU2003304046A AU2003304046C1 (en) 2002-10-02 2003-10-01 Apparatus and method for chemically reducing waste materials
EA200500569A EA200500569A3 (ru) 2002-10-02 2003-10-01 Устройство и способ для химического уменьшения объемов отходов
CA002500811A CA2500811C (fr) 2002-10-02 2003-10-01 Appareil et procede de reduction chimique de dechets
EP03816212A EP1578545A4 (fr) 2002-10-02 2003-10-01 Appareil et procede de reduction chimique de dechets
UAA200502885A UA85375C2 (ru) 2002-10-02 2003-10-01 Система и способ для химического восстановления отходов
MXPA05004274A MXPA05004274A (es) 2002-10-02 2003-10-01 Aparato y metodo para reducir quimicamente materiales de desecho.
PCT/US2003/031184 WO2004091820A2 (fr) 2002-10-02 2003-10-01 Appareil et procede de reduction chimique de dechets
JP2004570934A JP2006507940A (ja) 2002-10-02 2003-10-01 廃棄物を化学的に減少させる装置及び方法
ZA200503168A ZA200503168B (en) 2002-10-02 2005-04-19 Apparatus and method for chemically reducing waste materials
US11/457,342 US7910788B2 (en) 1996-04-22 2006-07-13 System for treating infectious waste matter
US12/364,012 US7829755B2 (en) 1996-04-22 2009-02-02 System and method for treating infectious waste matter
US12/913,830 US20110040138A1 (en) 1996-04-22 2010-10-28 System and method for treating infectious waste matter
JP2011033590A JP2011156531A (ja) 2002-10-02 2011-02-18 廃棄物を化学的に減少させる装置及び方法
US13/053,927 US20110171073A1 (en) 1996-04-22 2011-03-22 System and method for treating infectious waste matter

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US09171447 Continuation-In-Part 1997-04-21
US09/171,447 Continuation-In-Part US6472580B2 (en) 1996-04-22 1997-04-21 Methods for treatment and disposal of regulated medical waste
US10/201,121 Continuation US7183453B2 (en) 1996-04-22 2002-07-23 Method for treating infectious waste matter
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US11/457,297 Continuation US20070038013A1 (en) 1996-04-22 2006-07-13 System and method for treating infectious waste matter
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CN107597818A (zh) * 2017-11-02 2018-01-19 上海森旗智能科技有限公司 一种生物安全实验室动物尸体无害化处理设备
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