EP3003587A1 - Facility and procedure for treatment of waste with choice of quality of output products - Google Patents

Facility and procedure for treatment of waste with choice of quality of output products

Info

Publication number
EP3003587A1
EP3003587A1 EP13752662.0A EP13752662A EP3003587A1 EP 3003587 A1 EP3003587 A1 EP 3003587A1 EP 13752662 A EP13752662 A EP 13752662A EP 3003587 A1 EP3003587 A1 EP 3003587A1
Authority
EP
European Patent Office
Prior art keywords
heat
solidificate
waste
treatment
quality
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
EP13752662.0A
Other languages
German (de)
English (en)
French (fr)
Inventor
Milli Spanovic
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to EP18208147.1A priority Critical patent/EP3513885B1/en
Publication of EP3003587A1 publication Critical patent/EP3003587A1/en
Ceased legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/02Compositions 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/20Agglomeration, binding or encapsulation of solid waste
    • B09B3/25Agglomeration, binding or encapsulation of solid waste using mineral binders or matrix
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/02Agglomerated materials, e.g. artificial aggregates
    • C04B18/021Agglomerated materials, e.g. artificial aggregates agglomerated by a mineral binder, e.g. cement
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/02Agglomerated materials, e.g. artificial aggregates
    • C04B18/023Fired or melted materials
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/008Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for liquid waste
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00017Aspects relating to the protection of the environment
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00474Uses not provided for elsewhere in C04B2111/00
    • C04B2111/00767Uses not provided for elsewhere in C04B2111/00 for waste stabilisation purposes
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2203/00Furnace arrangements
    • F23G2203/20Rotary drum furnace
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/20Waste processing or separation
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Definitions

  • This invention falls into the following areas:
  • E04 B (C03, C04), E04 C; E04 D; E04 F; B29 G, and: G21 F and G21 K.
  • Such procedures reduce the harmfulness of material for at least one MAC (maximum allowable concentration) level. Also, the material is transformed into a dry, powdery solidificate with more favourable chemical and physical characteristics.
  • CaC0 3 MgO.
  • Ca(OH) 2 + CaO is typically a good and cost-effective way to achieve solidification. Some sorts of waste require only CaO, while others need only Ca(OH) 2 . We select reactants by analysing the waste.
  • solidificate treated with less calcium oxide contains high levels of moisture, which decreases its quality and further industrial use.
  • Cost is often the reason why waste is not treated this way, but instead by using other methods that do not meet basic ecological criteria.
  • Solidification transformation of liquid, oily and muddy materials into powder
  • solidification is a simpler and cheaper procedure, many opt for incineration because such waste contains certain amounts of energy, which improves cost-effectiveness of incineration.
  • New regulations and European directives do not support incineration of such waste because of uncontrolled air pollution (dioxins, furans, hydrocarbons, nitrogen compounds, etc.)
  • Other procedures that need other additives are no longer in frequent use because of their price and large quantities of solidificate coming from the process.
  • Illustration 1 Layout of the facility
  • Illustration 2 Blueprint of the facility
  • Illustration 3 Regenerator for obtaining calcium oxide and ash from solidificate Drawings are marked as follows:
  • This invention focuses on communal or industrial waste.
  • waste usually contains chemical compounds with carbon, different compounds with hard metals, alkyl compounds, alkaline and / or acidic content as well as numerous nitrogen, chlorine and other compounds.
  • Waste undergoes preparation to become a material of equal granulation (0-20 mm).
  • Useful components are being recycled (metal, glass, plastic, paper) and the rest is chopped up and crushed to become a material awaiting treatment.
  • Air pump is installed in the pipeline and placed in front of Injector, Air pump blows in the warm air and that is how the warm air comes into direct contact with incoming waste.
  • Ozone circulates in 1-2 g/s and decomposes organic contents.
  • Organic contents break down, molecular and physical water separate, physical characteristics (colour, granulation) change. This contributes to better molecular dissociation in Second reactor's line.
  • Dissociation device conducts the initial ion separation from molecule's atoms into anions (especially OH ) and cations (especially H + ). This is followed by ionic dissociation of hard metals and carbon portion of organic fraction. This depends on the surrounding available energy and negative electric potential of ions in dissociated parts.
  • Electromagnet is placed underneath the reactor's line and it creates a magnetic field. Electromagnet has a rounded shape as it follows the curvature of reactor's external surface. (Author has a registered Patent pertaining to this: HR/P20080004) g) Device for chopping up particles (9)
  • Device for chopping up particles is placed between the first and second reactors' lines. It serves as a so-called micronizer as it chops up the particles.
  • Parallel oxide encapsulators (12) are inside the second reactor's line (11). Particles need to be chopped up to less than 10 ⁇ m .
  • Encapsulated performs the function of pozzolamic impact on atoms coming from dissociated molecules under the conditions of vacuum space.
  • Vacuum space is located inside the whirlwind surrounded by steam and gases. This is followed by encapsulation of cations (especially heavy metals and non-carbons of the organic fraction) which depends on available surrounding energy.
  • Filtration system for cleansing of gas, steam and particles consists of:
  • Scrubber is a device for chemical treatment of gaseous content. Sediment containing mostly hydroxide is taken out, shaped as mud, and returned back into the process.
  • Increased temperature of the filter is added to the Heat exchange system as a part of total accumulated heat energy needed for treatment.
  • Gasses exiting scrubber consist of water steam, C0 2 and N 2 .
  • Mud in the baggy filter and scrubber contain sulphate salts and together with mud from water filter, they are reintroduced to the process.
  • Increased temperature inside scrubber is added to the Heat exchange system as a part of total accumulated heat energy needed for treatment.
  • a small ozone exposure (1 g/s) is sufficient for waste with high portion of organic compounds. Transformation, oxidation, physical and chemical decomposition of organic compounds happens quickly regardless of temperature differences.
  • Final product is defined on output transporters (24, 25).
  • One transporter is for basic treatment without additional changes to the final product.
  • Second output is designed for additional integration, including special additives, depending on product's further use.
  • Product (E) leaving the facility after basic treatment is a so-called Neutral product. It has standard qualities expected from solidificate (according to Patent HR/P20100575 A2 by same Author).
  • Adjusted final product can be the one intended for production of silicate granulates (Patent P20100300, same Author) or gascement (Patent HR/P20100325, same Author).
  • Solidificate as the final product of basic treatment, is taken by transporter (35) into Regenerator's rotary kiln (36).
  • Transporter (35) into Regenerator's rotary kiln (36).
  • burner (37) to break down solidificate.
  • Heat exchanger (39) to distribute heat for further use,
  • Solidificate to be transformed into calcium oxide has the following content:
  • So-called Calciner is a device for regeneration of solidificate. We use it to obtain calcium oxide as follows: transporter (35) takes solidificate to be roasted and then decomposed in regenerator's rotary kiln (36).
  • Ash (41) collects in cyclone, while Heat exchanger (39) distributes hot air (VI). Some of hot air goes into burner to increase the use of heat energy. Function of ozone is shown by describing its influence on organic contents in waste. Here are the most common chemical reactions:
  • Ozone breaks down organic carbon in amount of 0.55 g/s. If material has ⁇ 50% of organic content, ozone will penetrate the organic content in amount of 3 kg/h. Ozone will get through the organic content in amount of 0.55 g/s (ozone 0.02%) when the treatment capacity is 1.5 kg/s (5.4 t/h). The remaining ozone quickly transforms into O 2 This procedure lowers the amount of calcium oxide needed for treatment.
  • Material awaiting treatment (communal and / or industrial waste) is chopped up to equal granulation and analysed.
  • This total energy in MJ/kg is compared to energy needed to transform waste into a dry solidificate.
  • Level of moisture in solidificate has to be ⁇ 10%.
  • Temperature in reactors' lines has to be 100-125 °C.
  • Temperature of output material has to be 75-85 °C. Losses pertain to energy taken within the process (endothermic reactions) and heat lost through facility's openings and surface.
  • Quality of the final product determines the speed of the process. Calculation of energy balance tells us about needed treatment capacity. If we do not need solidificate as the final product, then the energy shortage can be solved by using heat released during its regeneration, temperatures of hot air being ⁇ 600 °C.
  • Temperature of input waste can be 10-15% lower than temperature of gases and steam exiting reactors' lines. This depends on insulation of heat exchangers as well as length of the pipeline.
  • Treatment is cost-effective because we harmonise all energy values in different phases of the process and utilise energy obtained through that same process.

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Ceramic Engineering (AREA)
  • Civil Engineering (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Processing Of Solid Wastes (AREA)
  • Pretreatment Of Seeds And Plants (AREA)
  • Disintegrating Or Milling (AREA)
  • Crystals, And After-Treatments Of Crystals (AREA)
EP13752662.0A 2013-06-07 2013-06-17 Facility and procedure for treatment of waste with choice of quality of output products Ceased EP3003587A1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
EP18208147.1A EP3513885B1 (en) 2013-06-07 2013-06-17 Facility and procedure for treatment of a solidificate

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
HRP20130502 2013-06-07
PCT/HR2013/000018 WO2014195740A1 (en) 2013-06-07 2013-06-17 Facility and procedure for treatment of waste with choice of quality of output products

Related Child Applications (1)

Application Number Title Priority Date Filing Date
EP18208147.1A Division EP3513885B1 (en) 2013-06-07 2013-06-17 Facility and procedure for treatment of a solidificate

Publications (1)

Publication Number Publication Date
EP3003587A1 true EP3003587A1 (en) 2016-04-13

Family

ID=49029127

Family Applications (2)

Application Number Title Priority Date Filing Date
EP13752662.0A Ceased EP3003587A1 (en) 2013-06-07 2013-06-17 Facility and procedure for treatment of waste with choice of quality of output products
EP18208147.1A Active EP3513885B1 (en) 2013-06-07 2013-06-17 Facility and procedure for treatment of a solidificate

Family Applications After (1)

Application Number Title Priority Date Filing Date
EP18208147.1A Active EP3513885B1 (en) 2013-06-07 2013-06-17 Facility and procedure for treatment of a solidificate

Country Status (7)

Country Link
EP (2) EP3003587A1 (sr)
CN (1) CN105473245A (sr)
EA (1) EA201592181A1 (sr)
ES (1) ES2842000T3 (sr)
HR (1) HRP20202060T1 (sr)
RS (1) RS61353B1 (sr)
WO (1) WO2014195740A1 (sr)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2766454C1 (ru) * 2021-03-22 2022-03-15 Леонид Александрович Аминов Способ переработки органических отходов

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Also Published As

Publication number Publication date
EA201592181A1 (ru) 2016-07-29
HRP20202060T1 (hr) 2021-02-19
WO2014195740A1 (en) 2014-12-11
ES2842000T3 (es) 2021-07-12
EP3513885B1 (en) 2020-10-07
CN105473245A (zh) 2016-04-06
EP3513885A1 (en) 2019-07-24
RS61353B1 (sr) 2021-02-26

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