• 专利附录
  • 专利说明
  • 权利要求
  • 类似技术
  • 同族专利
  • 引用文献
  • 法律状态
  • 优先权
    • 专利摘要:
    The invention relates to a process for the inertization of heavy metals, chlorides and other salt formers and soluble solids and metallic contaminants in ashes and / or waste from combustion processes or other thermal, chemical, mechanical processes. A major problem in landfilling is the formation of heavy metals, chlorides and other salt formers, as well as metallic contaminants and other readily dissolvable substances. These can enter the landfill site and, through the presence of appropriate reactants and conditions, favor other toxic compounds and contaminants. The invention is therefore characterized in that the incineration or the thermal, chemical, mechanical process is followed by a piece preparation, for example granulation. Under appropriate conditions can here a chemical / mineral inerting / stabilization of above-mentioned problem substances by integration and fixation and shaping and dimensional stability in terms of promotion, storage and transport can be achieved.
    公开号:AT512693A1
    申请号:T444/2012
    申请日:2012-04-13
    公开日:2013-10-15
    发明作者:Gerald Dipl Ing Fraissler；Kurt Dipl Ing Kaufmann；Sebastian Dipl Ing Dr Kaiser；Guenter Dipl Ing Jaritz
    申请人:Andritz Energy & Environment Gmbh；
    IPC主号:
    专利说明:

    »·» «· ···· · * ·· • '* · · * · · · ·····»
    The invention relates to a process for the inertization of heavy metals, chlorides and other Salzbildnem and soluble solids and metallic contaminants in ashes and / or waste from combustion processes or other thermal, chemical, mechanical processes.
    Slags, flyashes, dusts and reaction products from incineration, especially of refuse derived fuel (EBS) burning fluidized bed boilers have high pollutant contents. Of course, other waste materials from thermal, chemical or mechanical processes such as e.g. Sludges, slags, dross, dusts from the metal industry and the rock iron industry or other industries are treated. Depending on the legal requirements, their current disposal with regard to top and / or underground storage or other utilization is often very costly for plant operators.
    A major problem in landfilling is heavy metals, chlorides and other salt formers, as well as soluble solids and metallic contaminants. These may get into the landfill and, through the presence of suitable reactants and conditions, may favor other toxic compounds and contaminants.
    A method for inerting ash is e.g. from DE 697 01 128 T2 (EP 0 883 585 Bl). In this method, the ash is added phosphoric acid or phosphates, the resulting mass then annealed. The annealed mass is then added hydraulic binder and the resulting hydraulic mortar treated in a rotary tube dryer and then stored for several days for maturation and setting. Such a method is very complex in terms of apparatus and time and can only bind heavy metals to a limited extent.
    The aim of the invention is therefore to provide a recovery process for the inerting of existing heavy metals, chlorides and other salt formers as well as metallic contaminants and soluble solids in wet or dry incineration ashes or other thermal, chemical, mechanical processes. This method should also work from an economic point of view (investment, operating, disposal costs in terms of transport and landfill). Another aim with regard to disposal is to improve further handling with regard to conveying, storage and transport.
    The invention is therefore characterized in that the incineration or the thermal, chemical or mechanical process is followed by a piece preparation, for example granulation. Under appropriate conditions, a chemical / mineral stabilization of the aforementioned problem substances by incorporation and fixation and shaping and dimensional stability in terms of promotion, storage and transport can be achieved here.
    A favorable development of the invention is characterized in that the water content in the ash / waste mixture as a function of the ash / Abfallbesch monkey unit and that for the 1
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    Inertization / stabilization required addition amount of reaction chemicals is set. The amount and type of reaction chemicals / binder added depends on the chemical and / or alkaline properties of the waste / ash.
    High present alkalinity at pH> 11 and the presence of aluminosilicate phases cause their activation to form hydrate gels which lead to crosslinking (geopolymerization / condensation) involving incorporation / fixation of the above problematic substances.
    In addition, the presence of hydraulic phases on hydration leads to their activation and formation of CASH phases, which also serve to incorporate / fix the aforementioned problem substances. Particularly advantageous for the binding of Salzbildnem have proven high levels of CA phases. Unlike geopolymers, however, CASH phases are only partially resistant to heat and acid.
    By deliberately increasing the hydrate gels activated aluminosilicate and / or hydraulic Phasenanteüe in the form of binders of the binding effect can be reinforced with respect to inerting / stabilization of critical problem substances and optimized with respect to the respective criteria for disposal.
    If the alkalinity in the wet waste / ash is not sufficient for the formation of the hydrate gels, alkaline reaction chemicals, e.g. Base, water glass or even alkaline industrial wastes (e.g., red mud) may be added.
    Alternatively, if the alkalinity is insufficient, silicatic binders such as e.g. Water glass, silanol, silica are added. With regard to hydraulically acting binders, for example, alumina cement with high proportions of CA phases has proven itself. With a correspondingly high alkalinity in the ash / waste, the addition of aluminosilicate-rich substances with a high specific surface area and as a consequence of high reactivity, such as, for example, is sufficient. Bed ash, kaolin, metakaolin, brick chippings and other wastes from the construction and quarrying industry or other industries, since the formation of the hydrate gels is already taking place during the seasoning, for example granulation.
    If no high alkalinity is present, silicate-active and / or hydraulically acting binders, z, B. Water glass or alumina cement are added.
    Alumosilicate additives or silicate-active binders with a silicate content of> 50% by mass and / or hydraulically active binders with a calcium aluminate content of> 50 m% have proved to be particularly advantageous.
    It has proven to be particularly favorable when the preparation of pieces, for example granulation, is preceded by a wet-chemical, alkaline treatment.
    A favorable development of the invention is characterized in that the Stückigmachung, for example granulation, a calcination is connected downstream. 2
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    The invention will now be described by way of example with reference to the drawings, in which FIG. 1 is a flow chart of the method according to the invention,
    2 shows a possible system diagram of the method according to the invention in a combustion plant,
    3 shows a variant of method steps according to the method according to the invention.
    Fig. 1 shows schematically the inventive method, starting from an incinerator / thermal, chemical / mechanical process there accumulating ash / waste, which is loaded with heavy metals, chlorides and other Salzbildnem and metallic contaminants and soluble solids, a subsequent treatment step for granulation is subjected. Of course, other waste materials from thermal, chemical, mechanical processes such as e.g. Sludges, slags, dross, dusts, filter cakes from the metal industry and the rock or other industries treated. The primary objective of granulation is the stabilization of heavy metals, chlorides and other salt formers as well as other soluble solids and the fixation of further metallic contaminants by inclusion in the solid binder matrix formed by crystallization and cross-linking. Another aim with regard to disposal is to improve further handling with regard to conveying, storage and transport.
    In the absence of base metal phases in the ash from a combustion process or in waste from thermal, chemical, mechanical processes no pretreatment is required.
    The Stückigmachung, for example, granulation, incineration ash or waste from thermal, chemical, mechanical processes leads by crystallization and / or crosslinking of alkali-activated aluminosilicate-rich phases in the form of hydrate gels and hydraulic phases for chemical / mineral inerting / stabilization of existing heavy metals, chlorides and other salt formers as well as metallic contaminants and soluble solids. In the absence of these phases, binders must be added.
    Additives or silicate-active binders having a silicate content of> 50% by mass and / or hydraulically acting binders having a calcium aluminate content of> 50 m% have proved to be particularly advantageous. 3
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    The water content shall be optimized in terms of waste / ash composition and the nature and amount of the binder for complete surface wetting, as well as the provision of water for the hydration of these binder phases.
    2 shows a simplified system diagram for carrying out a variant of the method according to the invention with reference to an incinerator.
    The incineration plant is shown here as a circulating fluidized bed boiler 1 with cyclone 2, afterburner chamber 3 and dust collectors 4 including multicyclone 5. The contaminated, untreated fly ash 6 is passed through a buffer tank 7 in a mixer / kneader 8 for wet chemical treatment. With the addition of water 9 and other alkaline reactants as described here e.g. Base 10 and / or nitrate 11 is here the wet-chemical treatment. Due to the hydration / oxidation of base metal phases, hydrogen / ammonia is released depending on their content in the fly ash. Accordingly, the formation of an explosive atmosphere in the mixer / kneader 8 and in its immediate vicinity by gas purging must be prevented. The necessary amount of purge gas supplied is based on the fuel gas oxygen ratio in the generated exhaust gas, so that an explosive atmosphere is prevented in any case. Gas monitoring measurements must be used accordingly. The purge gas used preferably has a lower, at best no oxygen content. Flue gas 12 branched off from the combustion process with a low residual oxygen content may therefore be considered for use. The fuel gas contained in the exhaust gas is recycled to the energy use in the combustion chamber 1. An upstream scrubber 20 is used for the separation of valuable ammonia, which can be used for denitrification in the combustion process or recycled.
    After completion of the mechanical stress in the mixer / kneader 8 and discharge there is a risk that upon further handling, the moist thixotropic mixture by crystallization and / or polymerization / condensation of existing binder phases within a short time uncontrolled sets and forms a solid mass. The aim of subsequent Stückigmachung / granulation is therefore in terms of conveying, storage and transport technology optimal shape and dimensional stability and to achieve optimum granule shape and strength for the downstream Kalzinierschritt. After the mixer / kneader 8, the product 13 is used from the wet chemical treatment in a granulator 14 for mixing and shaping. The granulator preferably operates on the continuous or quasi-continuous principle.
    In this granulator 14 binders 15 are additionally introduced. With correspondingly high alkalinity, e.g. after the susceptible wet-chemical treatment, the addition of fine bed ash with a high aluminosilicate content and high specific surface is sufficient
    7243-B AT «· t Μ ·· k · ·« Φ ** »» ·
    Formation of the hydrate gels required for setting, which already takes place during the preparation, for example granulation. In addition, fine bed ash has high proportions of hydraulically acting phases. In any case, in downstream calcination additives which lead to the formation of geopolymers, due to their good thermal stability in contrast to hydraulically acting additives.
    In addition, a fine bed pocket has the advantage that its problematic contents can be determined e.g. Chlorides and other salt formers, heavy metals and soluble solids as well as metallic contaminations are often negligible.
    An optimal shaping / dimensional stability in terms of conveying, storage and transport can ensure that the product does not uncontrollably set after the wet-chemical treatment with thixotropic properties and presence of hydrated binder phases and forms a solid mass, but continues to be fordable, storable and transportable is.
    The safety and monitoring measures are based on the possibility of non-depleted metallic aluminum or other base metal phases with existing reaction potential to form explosive gaseous hydrogen in accordance with the wet-chemical treatment.
    The product 16 from the granulation step is additionally supplied to a calcination furnace 17 by way of example. This can be, for example, a multi-level oven, whereby the process parameters temperature and dwell time can be varied per oven (floor). The deck oven also offers good circulation and flow through the bed and consequently the desired contact with the furnace atmosphere. The mechanical stress during the calcining step should be kept as low as possible on the product, in order to avoid abrasion and breakage and, as a consequence, a build-up of dust, since this has adverse effects on the process and the costs.
    The heating of the calcination furnace 17 is here convection with flue gas 18 in countercurrent. However, it can also be used in combination with other drying methods, e.g. Radiation drying and contact drying happen. The invention is not limited to the use of a multiple-hearth furnace, but equivalent thermoreactors with corresponding properties may also be used, e.g. Drum dryer, belt dryer, etc. The exhaust gas 19 is then returned to the heat recovery in the combustion chamber 1, which leads to energy savings.
    Fig. 3 shows the process stage Stückigmachung / granulation separately. This can be followed by the combustion or the thermal, chemical, mechanical process without intermediate step, if the ash has no base metal phases, which at 5
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    Humidification by hydration / oxidation release explosive hydrogen. Otherwise, a wet chemical treatment should be added.
    Starting from an incinerator / thermal, chemical, mechanical process, the resulting ash / waste, which is loaded with heavy metals, chlorides and other Salzbildnem and metallic contaminants and soluble solids, subjected to a downstream treatment step for granulation. The primary objective of granulation is the chemical stabilization of heavy metals, chlorides and other salt formers as well as other soluble solids and the fixation of further metallic contaminants by inclusion in the solid binder matrix formed by crystallization and cross-linking. Another aim is to improve the disposal in terms of disposal, further handling in terms of promotion, storage and transport and to achieve optimum granule shape and strength for an optional downstream calcination.
    The granulation (preparation) is preferably carried out under alkaline conditions at a pH of> 1 1.
    The ash / waste 13 is fed to a granulator 14, for example. If appropriate, water 9 and suitable binder 15 are added here. Further, purge gas 12 is supplied, which may be optionally supplied as a waste gas 21 to a scrubber.
    The Stückigmachung, for example, granulation, incineration ash or waste from thermal, chemical, mechanical processes leads by crystallization and / or crosslinking of alkali-activated aluminosilicate-rich phases and hydraulic phases for chemical / mineral inerting / stabilization of existing heavy metals, chlorides and other Salzbildnem and metallic contaminants and soluble solids. In the absence of these phases, suitable binders 15 must be added.
    Additives or silicate-active binders having a silicate content of> 50% by mass and / or hydraulically acting binders having a calcium aluminate content of> 50 m% have proved to be particularly advantageous.
    The water content is to be optimized with regard to the waste ash quality and a complete surface wetting for the hydration / oxidation of these phases.
    The recycling process according to the invention is followed, for example, by a combustion process or another thermal, chemical, mechanical process and can be operated as a connected or independent plant, the technical necessity of a wet-chemical treatment and / or calcining step being dependent on the ash / waste properties of the educt with regard to further handling (Promotion, storage, disposal) is dependent. 6
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    ·· mm ···· * · ···· I »· ·« · # »Μ * ·· * · · t · V · · · · · ·
    The invention is not limited by the drawings and description. Thus, the granulation can be used separately or following a wet-chemical treatment and / or followed by calcination. 7
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    权利要求:
    Claims (8)
    [1]
    1. A process for the inerting of heavy metals, chlorides and other Salzbildnem and soluble solids and metallic contaminants in ashes and / or waste from combustion processes or other thermal, chemical, mechanical processes, characterized in that the combustion or the thermal, chemical, mechanical process a piece preparation, for example, granulation, preferably with continuous or quasi-continuous operation, is connected downstream.
    [2]
    2. The method according to claim 1, characterized in that the required water content in the ash mixture is adjusted depending on the ashability and the required addition amount of reaction chemicals / binder for the inertization.
    [3]
    3. The method according to any one of claims 1 or 2, characterized in that in the Stückigmachung, for example granulation, the addition of alkali-activatable aluminosilicate additives with high specific surface area such. Bed ash, metakaolin, kaolin, brick chippings or binder in the form of a silicate binder having a silicate content of> 50% by weight, such as e.g. Waterglass, silanol, silicic acid and / or in the form of a hydraulic binder with a calcium aluminate content of> 50% by weight, e.g. Alumina cement takes place.
    [4]
    4. The method according to claim 3, characterized in that the addition of aluminosilicate additives, the pH in the wet waste / ash mixture> 11.
    [5]
    5. The method according to any one of claims 1 to 4, characterized in that to increase the pH at insufficient alkalinity alkaline reaction chemicals such. Base, alkali or industrial wastes such. Red mud, to be added.
    [6]
    6. The method according to any one of claims 1 to 5, characterized in that the Stückigmachung, for example, granulation, a wet-chemical treatment is connected upstream.
    [7]
    7. The method according to any one of claims 1 to 6, characterized in that the Stückigmachung, for example granulation, a calcination is followed.
    [8]
    8,7243-B AT
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    同族专利:
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    引用文献:
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    EP0335024A1|1988-03-31|1989-10-04|Wheelabrator Environmental Systems Inc.|Immobilization of lead and cadmium in solid residues from the combustion of refuse using lime phosphate|
    DE3909060A1|1989-03-18|1990-09-20|Pahl Ekke Dipl Ing|Process for the making inert of combustion residues and also natural and industrial sediments|
    US5416252A|1991-12-27|1995-05-16|Ciments Lafarge|Waste incineration residues and the products obtained|
    US6132355A|1996-02-28|2000-10-17|Solvay |Ash inerting method|
    EP1918031A1|2006-10-30|2008-05-07|ASH DEC Umwelt AG|Method of detoxification and utilization of fly ash|
    EP2087947A2|2008-02-08|2009-08-12|Depuracque Sviluppo S.R.L.|Method for reclaiming soil, sediment and sludge dredged from watercourses contaminated by heavy metals and by dangerous and toxic organic compounds|
    EP0313016B1|1987-10-21|1993-08-04|Förster, Fritz|Inorganic, insoluble industrial raw material producible from waste, method for its production and use|
    DE3924565C2|1989-07-25|1992-06-25|Gebr. Knauf Westdeutsche Gipswerke Kg, 8715 Iphofen, De|
    US5573576A|1994-10-24|1996-11-12|International Solidification, Inc.|Method of treating steel mill waste|
    AT409350B|2000-06-28|2002-07-25|Kostjak Michael Dipl Ing Dr Te|METHOD FOR DETACHING METALLIC ALUMINUM FROM ALUMINUM-CONTAINING SOLID WASTE|
    DE10229697A1|2002-07-02|2004-01-29|Ati Nuklear Ag|A process for stabilization of solid waste with immobilization of the waste by encapsulation useful for stabilization of solid waste, e.g. chemical and radioactive waste material prior to disposal|
    US8522720B2|2009-09-15|2013-09-03|Ceramatec, Inc.|Environmentally-friendly animal litter|AT516407B1|2014-11-20|2016-05-15|Andritz Ag Maschf|Process for the use of hydrated sorbents in thermal process plants|
    IT201900011970A1|2019-08-09|2021-02-09|Gianfranco Gonella|Apparatus for the inertization of ashes and dangerous dust by means of the sintering technique|
    法律状态:
    2015-09-15| PC| Change of the owner|Owner name: ANDRITZ AG, AT Effective date: 20150721 |
    优先权:
    申请号 | 申请日 | 专利标题
    ATA444/2012A|AT512693B1|2012-04-13|2012-04-13|Process for the inerting of heavy metals, chlorides and other salt formers as well as soluble solids and metallic contaminants|ATA444/2012A| AT512693B1|2012-04-13|2012-04-13|Process for the inerting of heavy metals, chlorides and other salt formers as well as soluble solids and metallic contaminants|
    EP13001754.4A| EP2650057B1|2012-04-13|2013-04-05|Method for the inertisation of heavy metals, chlorides and other salt-forming compounds and soluble solids and metallic contaminations|
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