JP2008291497A - Method of using coal ash for ground material - Google Patents
Method of using coal ash for ground material Download PDFInfo
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- JP2008291497A JP2008291497A JP2007137616A JP2007137616A JP2008291497A JP 2008291497 A JP2008291497 A JP 2008291497A JP 2007137616 A JP2007137616 A JP 2007137616A JP 2007137616 A JP2007137616 A JP 2007137616A JP 2008291497 A JP2008291497 A JP 2008291497A
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- 239000010883 coal ash Substances 0.000 title claims abstract description 52
- 238000000034 method Methods 0.000 title claims abstract description 36
- 239000000463 material Substances 0.000 title claims abstract description 24
- 239000002245 particle Substances 0.000 claims abstract description 44
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 34
- 238000005406 washing Methods 0.000 claims abstract description 30
- 239000004094 surface-active agent Substances 0.000 claims abstract description 23
- 239000012736 aqueous medium Substances 0.000 claims abstract description 18
- 239000002002 slurry Substances 0.000 claims abstract description 16
- 238000002156 mixing Methods 0.000 claims abstract description 8
- 238000000926 separation method Methods 0.000 claims description 16
- 239000004568 cement Substances 0.000 claims description 8
- 238000003756 stirring Methods 0.000 claims description 8
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 7
- 229910052799 carbon Inorganic materials 0.000 claims description 7
- 239000002994 raw material Substances 0.000 claims description 4
- 238000005119 centrifugation Methods 0.000 claims description 3
- 239000012190 activator Substances 0.000 claims description 2
- 239000010419 fine particle Substances 0.000 abstract description 18
- 239000011573 trace mineral Substances 0.000 abstract description 10
- 235000013619 trace mineral Nutrition 0.000 abstract description 10
- ZOXJGFHDIHLPTG-UHFFFAOYSA-N Boron Chemical compound [B] ZOXJGFHDIHLPTG-UHFFFAOYSA-N 0.000 description 8
- 229910052796 boron Inorganic materials 0.000 description 8
- 239000011362 coarse particle Substances 0.000 description 7
- 238000010828 elution Methods 0.000 description 7
- 239000007787 solid Substances 0.000 description 6
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 4
- 239000011737 fluorine Substances 0.000 description 4
- 229910052731 fluorine Inorganic materials 0.000 description 4
- 239000003245 coal Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000010881 fly ash Substances 0.000 description 3
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 2
- 241000196324 Embryophyta Species 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 239000003945 anionic surfactant Substances 0.000 description 2
- 229910052785 arsenic Inorganic materials 0.000 description 2
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 229910052602 gypsum Inorganic materials 0.000 description 2
- 239000010440 gypsum Substances 0.000 description 2
- 238000002386 leaching Methods 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 238000010008 shearing Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 235000021419 vinegar Nutrition 0.000 description 2
- 239000000052 vinegar Substances 0.000 description 2
- 235000017166 Bambusa arundinacea Nutrition 0.000 description 1
- 235000017491 Bambusa tulda Nutrition 0.000 description 1
- 241001330002 Bambuseae Species 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 229920001732 Lignosulfonate Polymers 0.000 description 1
- 235000015334 Phyllostachys viridis Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 238000004380 ashing Methods 0.000 description 1
- 239000011425 bamboo Substances 0.000 description 1
- WUKWITHWXAAZEY-UHFFFAOYSA-L calcium difluoride Chemical compound [F-].[F-].[Ca+2] WUKWITHWXAAZEY-UHFFFAOYSA-L 0.000 description 1
- 229910001634 calcium fluoride Inorganic materials 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 230000003100 immobilizing effect Effects 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- PSZYNBSKGUBXEH-UHFFFAOYSA-M naphthalene-1-sulfonate Chemical compound C1=CC=C2C(S(=O)(=O)[O-])=CC=CC2=C1 PSZYNBSKGUBXEH-UHFFFAOYSA-M 0.000 description 1
- 239000002736 nonionic surfactant Substances 0.000 description 1
- 239000005077 polysulfide Substances 0.000 description 1
- 229920001021 polysulfide Polymers 0.000 description 1
- 150000008117 polysulfides Polymers 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- AKHNMLFCWUSKQB-UHFFFAOYSA-L sodium thiosulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=S AKHNMLFCWUSKQB-UHFFFAOYSA-L 0.000 description 1
- 235000019345 sodium thiosulphate Nutrition 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 230000008961 swelling Effects 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- VLCLHFYFMCKBRP-UHFFFAOYSA-N tricalcium;diborate Chemical compound [Ca+2].[Ca+2].[Ca+2].[O-]B([O-])[O-].[O-]B([O-])[O-] VLCLHFYFMCKBRP-UHFFFAOYSA-N 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 235000020681 well water Nutrition 0.000 description 1
- 239000002349 well water Substances 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B18/00—Use 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
- C04B18/04—Waste materials; Refuse
- C04B18/06—Combustion residues, e.g. purification products of smoke, fumes or exhaust gases
- C04B18/08—Flue dust, i.e. fly ash
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2103/00—Function or property of ingredients for mortars, concrete or artificial stone
- C04B2103/0003—Unintentionally added compounds, such as impurities in raw materials, e.g. alkali sulfates in construction grade cement
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2103/00—Function or property of ingredients for mortars, concrete or artificial stone
- C04B2103/40—Surface-active agents, dispersants
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2111/00—Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
- C04B2111/10—Compositions or ingredients thereof characterised by the absence or the very low content of a specific material
- C04B2111/1075—Chromium-free or very low chromium-content materials
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Ceramic Engineering (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Civil Engineering (AREA)
- Combustion & Propulsion (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Consolidation Of Soil By Introduction Of Solidifying Substances Into Soil (AREA)
- Investigation Of Foundation Soil And Reinforcement Of Foundation Soil By Compacting Or Drainage (AREA)
- Processing Of Solid Wastes (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
Abstract
Description
本発明は、石炭火力発電所や石炭焚ボイラ等から排出される石炭灰(フライアッシュ)に含まれる微量元素を除去して地盤材料として利用する石炭灰地盤材料化方法に関する。 The present invention relates to a coal ash ground materialization method for removing trace elements contained in coal ash (fly ash) discharged from a coal-fired power plant, a coal fired boiler, and the like and using it as a ground material.
石炭は植物の化石であることから、植物が土壌から吸収した微量元素を含有している。石炭を燃焼させたあとに15%程度の石炭灰が排出される。石炭灰の内、70%以上を占めるのがボイラ中を飛散するフライアッシュである。石炭灰中に微量元素が濃縮含有している。フライアッシュは細粒であるため、これが水に触れると微量元素が溶出し、場合によっては環境基準値を超してしまうことがあった。石炭灰は石炭火力発電所などから年間1000万トン以上排出され、その発生量は年々増加している。石炭灰の大部分はセメント原料として活用されている。しかし、セメントの消費量は徐々に減少している。そのため、石炭灰の盛土や道路の地盤材料としての活用が必須となっている。ここで問題になるのは溶出成分であり、特に六価クロムやホウ素、ヒ素などの制御が課題となっている。 Since coal is a fossil plant, it contains trace elements that the plant has absorbed from the soil. After burning coal, about 15% of coal ash is discharged. The fly ash that scatters in the boiler occupies 70% or more of the coal ash. Trace elements are concentrated in coal ash. Since fly ash is a fine particle, trace elements are eluted when it comes into contact with water, and in some cases, it may exceed the environmental standard value. More than 10 million tons of coal ash is discharged annually from coal-fired power plants, and the amount generated is increasing year by year. Most of the coal ash is used as a raw material for cement. However, cement consumption is gradually decreasing. For this reason, utilization as coal ash embankment and road ground material is essential. The problem here is the elution component, and in particular, control of hexavalent chromium, boron, arsenic and the like is a problem.
こうした溶出成分を固定化する技術として、セメントや石膏を添加するなど古くから用いられている方法に有効性が認められている。例えば、特開2004−148288号公報には、多硫化カルシウムやチオ硫酸ナトリウムの添加によって六価クロムの溶出を抑制する技術が開示されている。特開2004−97944号公報には、含水比を調整した石炭灰に石灰/石膏を添加し、ホウ素の溶出を抑制する技術が開示されている。特開2001−157884号公報には、木酢液や竹酢液によって重金属の溶出を抑制する技術が開示されている。また、溶出成分を除去する方法としては、古くから用いられている洗浄による方法が知られており、ここに添加剤を用いて除去効果の向上を図る方法が提案されている。例えば、特開2003−320342号公報には、酸性の水溶液で洗浄することによってホウ素を除去する技術が開示されている。
しかしながら、従来の固定化による溶出成分の制御の技術は、微量成分を除去するわけではなく、環境条件の変化によって微量元素が再溶出する可能性が残っている。又、洗浄による微量成分の除去する技術に関しては、洗浄にかかる労力が甚だ大きく、洗浄後の排水量も多大となるため現実的ではなかった。 However, the conventional technique for controlling the eluted components by immobilization does not remove the trace components, and there remains a possibility that the trace elements are re-eluted due to changes in environmental conditions. In addition, the technology for removing trace components by washing is not practical because the labor required for washing is very large and the amount of waste water after washing becomes large.
石炭灰中の微量成分の含有形態を調査研究した結果、(1)石炭灰表面に強く吸着している成分、(2)石炭灰の主成分であるシリカやアルミナなどの中に固溶している成分の2種類があることが判明した。溶出が問題になるのは、前記(1)のケースであるが、この除去が困難であった。検討の結果、除去の困難さは、微量成分が石炭灰の微細粒子や未燃カーボン粒子に強く吸着しており、これらの微細粒子は粗い石炭灰粒子に強く配位(凝集)しているためであることが判明した。このため、こうした微細粒子を効果的に除去することが微量成分を除去する上で重要な問題であり、微細粒子を除去したものは地盤材料として利用できることが判明した。 As a result of investigating and studying the content of trace components in coal ash, (1) components strongly adsorbed on the surface of coal ash, (2) dissolved in silica, alumina, etc., which are the main components of coal ash It was found that there are two types of ingredients. The elution becomes a problem in the case (1), but this removal is difficult. As a result of the examination, the difficulty of removal is that the trace components are strongly adsorbed to the fine particles of coal ash and unburned carbon particles, and these fine particles are strongly coordinated (aggregated) to the coarse coal ash particles. It turned out to be. For this reason, it has been found that effective removal of such fine particles is an important problem in removing trace components, and those from which fine particles have been removed can be used as a ground material.
本発明は、前記従来技術の問題を解決する、簡単な構成で効率良く微細粒子を分離して微量元素を除去し石炭灰を無害化して地盤材料として利用する石炭灰の地盤材料化方法を提供することを目的とする。 The present invention provides a method for converting coal ash into a ground material that solves the problems of the prior art, efficiently separates fine particles with a simple structure, removes trace elements, renders coal ash harmless, and uses it as a ground material. The purpose is to do.
本第1発明は、前記課題を解決するために、石炭灰の地盤材料化方法において、石炭灰に界面活性剤と水性媒体を加えて攪拌混合してスラリーとするスラリー化工程と、前記スラリーを分級・分離手段により5μm以上の粒子を分級・分離する分級・分離工程と、分級・分離した5μm以上の粒子を清浄な水で洗浄する洗浄工程を有することを特徴とする。 In order to solve the above-mentioned problems, the first invention of the present invention is a method for making coal ash into a ground material. A slurrying step is performed by adding a surfactant and an aqueous medium to coal ash, stirring and mixing the slurry, It comprises a classification / separation step of classifying / separating particles of 5 μm or more by a classification / separation means, and a washing step of washing the classified / separated particles of 5 μm or more with clean water.
本第2発明は、本第1発明の石炭灰の地盤材料化方法において、前記スラリー化工程は、石炭灰に対して0.2〜3重量%の界面活性剤を添加し、石炭灰に対して100〜150重量%の水を加えることを特徴とする。 This 2nd invention is the ground materialization method of the coal ash of this 1st invention, The said slurrying process adds 0.2 to 3weight% of surfactant with respect to coal ash, 100 to 150% by weight of water is added.
本第3発明は、本第1又は第2発明の石炭灰の地盤材料化方法において、前記スラリー化工程において、最初に最終添加量の2/3の水性媒体を加えて攪拌混合する予備混合工程を備えることを特徴とする。界面活性剤は、2/3の水性媒体に添加しても良いし、後に添加する1/3の水性媒体に添加しても良い。 The third invention is a premixing step in which, in the slurry ashing method of the first or second invention of the first or second invention, first, a final addition amount of 2/3 of an aqueous medium is added and stirred and mixed. It is characterized by providing. The surfactant may be added to a 2/3 aqueous medium or may be added to a 1/3 aqueous medium to be added later.
本第4発明は、本第1〜第3発明のいずれかの石炭灰の地盤材料化方法において、分級・分離された5μm以上の粒子をさらに50μm以上の粒子を分級・分離する第2分級・分離工程を備えることを特徴とする。 The fourth aspect of the present invention is the second classifying / classifying method according to any one of the first to third aspects of the present invention, wherein the classified and separated particles of 5 μm or more are further classified and separated by 50 μm or more. A separation step is provided.
本第5発明は、本第1〜第4発明のいずれかの石炭灰の地盤材料化方法において、洗浄工程の残余の水から水面に浮遊する浮遊粒子、未燃カーボンを分離し、その後残余の水から遠心分離により5μm以下の粒子を分離してセメント原料とし、固形分が分離された水は界面活性剤を添加して前記スラリー化工程の界面活性材水溶液として使用することを特徴とする。 The fifth aspect of the present invention is the method for converting a ground material of coal ash according to any one of the first to fourth aspects of the invention to separate floating particles and unburned carbon floating on the water surface from the remaining water in the washing step, and then It is characterized in that particles having a size of 5 μm or less are separated from water by centrifugation to obtain a cement raw material, and the water from which the solid content has been separated is added as a surfactant and used as a surfactant aqueous solution in the slurrying step.
本発明の石炭灰に界面活性剤と水性媒体を加えて攪拌混合してスラリーとするスラリー化工程と、前記スラリーを分級・分離手段により5μm以上の粒子を分級・分離する分級・分離工程と、分級・分離した5μm以上の粒子を清浄な水で洗浄する洗浄工程を備える構成により、スラリー化工程で粗い粒子に強く凝集していた微細粒子が分離されて界面活性剤水溶液中に分散し、続く分級・分離工程で微細粒子が5μm以上の粒子から分離され、さらに、洗浄工程で5μm以上の粒子に付着していた微細粒子と浮遊粒子、未燃カーボンが除去されるので、微量元素を多く含有する微細粒子を効率良く分離できる。
スラリー化工程において、最初に最終添加量の2/3の水性媒体を加えて攪拌混合する予備混合工程を備える構成により、強いせん断力を生じさせることができ、この時に微粒分を引き剥がすことができる。界面活性剤は、この予備混合水に添加しても良いし、残余の混合水に添加しても良い。
分級・分離された5μm以上の粒子をさらに50μm以上の粒子を分級・分離する第2分級・分離工程を備える構成により、地盤材料としての用途に応じた粒度の異なる石炭灰を用意できる。
洗浄工程の残余の水から水面に浮遊する浮遊粒子、未燃カーボンを分離し、その後残余の水から遠心分離により5μm以下の粒子を分離してセメント原料とし、固形分が分離された水は界面活性剤を添加して前記スラリー化工程の界面活性材水溶液として使用する構成により、洗浄水を無駄なく使用でき後処理が容易になる。微量元素の濃度が濃くなった洗浄後の水で再度スラリー化工程を実施しても、その後の洗浄工程で微量元素を除去できる。
A slurrying step of adding a surfactant and an aqueous medium to the coal ash of the present invention and stirring and mixing to form a slurry; and a classification / separation step of classifying / separating particles of 5 μm or more by the classification / separation means of the slurry; With a structure comprising a washing step of washing the classified and separated particles of 5 μm or more with clean water, the fine particles strongly agglomerated into the coarse particles in the slurrying step are separated and dispersed in the surfactant aqueous solution, followed by Fine particles are separated from particles of 5 μm or more in the classification / separation process. Furthermore, fine particles, floating particles, and unburned carbon adhering to the particles of 5 μm or more are removed in the cleaning process, so it contains a large amount of trace elements. Can be separated efficiently.
In the slurrying process, a configuration including a premixing process in which an aqueous medium having a final addition amount of 2/3 is first added and stirred and mixed can generate a strong shearing force. At this time, fine particles can be peeled off. it can. The surfactant may be added to this premixed water or may be added to the remaining mixed water.
Coal ash having a different particle size according to the use as the ground material can be prepared by a configuration including a second classification / separation step of classifying / separating the classified / separated particles of 5 μm or more and further separating / separating particles of 50 μm or more.
Floating particles floating on the water surface and unburned carbon are separated from the remaining water in the washing process, and then the particles of 5 μm or less are separated from the remaining water by centrifugation to make cement raw material. With the configuration in which the activator is added and used as the surfactant aqueous solution in the slurrying step, the cleaning water can be used without waste and the post-treatment is facilitated. Even if the slurrying process is carried out again with the water after washing in which the concentration of the trace element is increased, the trace element can be removed in the subsequent washing process.
本発明の石炭灰の地盤材料化方法を工程順に説明する。スラリー化工程では、石炭灰に界面活性剤と水性媒体を加えて攪拌混合してスラリーにする工程である。水性媒体としては、水道水、井戸水、雨水等入手が容易なもを使用する。使用する界面活性剤としては、陰イオン系界面活性剤、非イオン系界面活性剤などである。ナフタレンスルホン酸塩やリグニンスルホン酸塩などの陰イオン系界面活性剤が安価で好適である。 The method for converting coal ash into a ground material according to the present invention will be described in the order of steps. In the slurrying step, a surfactant and an aqueous medium are added to coal ash and mixed with stirring to form a slurry. As the aqueous medium, tap water, well water, rain water, etc., which are easily available are used. Examples of the surfactant used include an anionic surfactant and a nonionic surfactant. Anionic surfactants such as naphthalene sulfonate and lignin sulfonate are inexpensive and suitable.
石炭灰に対して界面活性剤は0.2〜3重量%、好ましくは0.5〜1.5重量%添加する。0.2重量%以下では界面活性剤添加効果がほとんど得られず、3重量%以上では石炭灰中の未燃カーボンが溶出し、スラリーが黒濁化し後処理が困難となる。石炭灰に対して水性媒体は100〜150重量%加える。水性媒体の量が100重量%以下であると粘性が高くなり分級、分離効果が悪化し、150重量%以上では石炭灰の沈殿が生じやすく、プロセス上での閉塞を生じたり、排水処理量が嵩む等の問題が生じる。また、後述のように、フッ素、ホウ素の沈殿物を効果的に作るために必要である。 The surfactant is added in an amount of 0.2 to 3% by weight, preferably 0.5 to 1.5% by weight, based on the coal ash. If it is 0.2% by weight or less, the effect of adding a surfactant is hardly obtained, and if it is 3% by weight or more, unburned carbon in coal ash is eluted and the slurry becomes blackish and post-treatment becomes difficult. The aqueous medium is added in an amount of 100 to 150% by weight based on the coal ash. When the amount of the aqueous medium is 100% by weight or less, the viscosity becomes high, and the classification and separation effect deteriorates. When the amount is 150% by weight or more, coal ash is likely to precipitate, causing clogging in the process or wastewater treatment amount. Problems such as swelling occur. Further, as will be described later, it is necessary to effectively produce a precipitate of fluorine and boron.
石炭灰は、粗大粒子表面に微細粒子が強力に凝集している。微細粒子を分級・分離するためには、粗大粒子表面に凝集している微細粒子を分離する必要がある。そのため、本発明では、石炭灰に界面活性剤と水性媒体を加えて攪拌・混合してスラリーとする。界面活性剤を添加した水中で攪拌・混合する過程で、粗大粒子表面に強力に凝集していた微細粒子が分離し、界面活性剤水溶液中に均一に分散したスラリーとなる。 Coal ash has fine particles strongly aggregated on the surface of coarse particles. In order to classify and separate the fine particles, it is necessary to separate the fine particles aggregated on the surface of the coarse particles. Therefore, in this invention, surfactant and an aqueous medium are added to coal ash, and it stirs and mixes to make a slurry. In the process of stirring and mixing in the water to which the surfactant is added, fine particles that have been strongly aggregated on the surface of the coarse particles are separated to form a slurry uniformly dispersed in the aqueous surfactant solution.
スラリー化工程において、石炭灰に対して、最終添加量の2/3程度の水性媒体を加えて攪拌混合する予備混合工程を実施しても良い。界面活性剤は、2/3の水性媒体に添加しても良いし、後に添加する1/3の水性媒体に添加しても良い。必要最終添加量の2/3に相当する予備混合水と石炭灰を混合し、予備攪拌することで、強いせん断力を生じさせることができ、この時に微粒分を引き剥がすことができる。 In the slurrying step, a preliminary mixing step may be performed in which an aqueous medium having a final addition amount of about 2/3 is added to the coal ash and stirred. The surfactant may be added to a 2/3 aqueous medium or may be added to a 1/3 aqueous medium to be added later. By mixing premixed water and coal ash corresponding to 2/3 of the required final addition amount and pre-stirring, a strong shearing force can be generated, and fine particles can be peeled off at this time.
スライー化工程で生成されたスラリーは、水しや篩い分けなどによる分級分離工程で、5μm以上の粒子とそれ以下の粒子が分級分離される。均一に微細粒子、粗大粒子が分散したスラリーとなっているので、分級分離工程で粉塵が発生することがない。分級分離された5μm以下の粒子が分散したスラリーは、遠心分離装置で5μm以下の粒子が分離され、分離された5μm以下の粒子はセメント材料として使用される。固形分が除去された界面活性剤水溶液は再度スラリー化工程で使用される。 The slurry produced in the slurrying step is classified and separated into particles having a particle size of 5 μm or more and particles having a particle size of less than 5 μm in a classification and separation step such as watering or sieving. Since it is a slurry in which fine particles and coarse particles are uniformly dispersed, dust is not generated in the classification and separation step. From the classified and separated slurry in which particles of 5 μm or less are dispersed, particles of 5 μm or less are separated by a centrifugal separator, and the separated particles of 5 μm or less are used as a cement material. The aqueous surfactant solution from which the solid content has been removed is used again in the slurrying step.
粗大粒子が多く含有する石炭灰の場合は、分級分離された5μm以上の粒子を第2分級分離工程で、50μm以上と5〜50μmとに分級分離される。粗大粒子は地盤材料として使いやすいので、50μm以上と5〜50μmの粒子を別々に洗浄工程で洗浄し、粒度の異なる地盤材料としても良い。 In the case of coal ash containing a large amount of coarse particles, the classified and separated particles of 5 μm or more are classified and separated into 50 μm or more and 5 to 50 μm in the second classification separation step. Since coarse particles are easy to use as a ground material, particles having a particle size of 50 μm or more and 5 to 50 μm may be separately washed in a washing step to obtain ground materials having different particle sizes.
分級分離された5μm以上の粒子は、洗浄工程により洗浄される。洗浄工程は、5μm以上の粒子の表面に残った微細粒子や微量成分を洗浄分離すると共に、比重の軽い浮遊成分や未燃カーボンを洗浄水表面に浮かせて分離する機能を有する。洗浄水の量は、スラリー化工程で添加した水性媒体の30〜50%である。洗浄後の5μm以上の粒子は地盤材料として利用する。 The classified and separated particles of 5 μm or more are washed by a washing step. The washing step has a function of washing and separating fine particles and trace components remaining on the surface of particles of 5 μm or more, and floating and separating light floating components and unburned carbon on the washing water surface. The amount of wash water is 30-50% of the aqueous medium added in the slurrying step. The particles of 5 μm or more after washing are used as the ground material.
洗浄後の洗浄水には、5μm以上の粒子の表面から洗浄分離された5μm以下の粒子と微量成分が存在する。洗浄後の洗浄水を遠心分離装置に投入し、5μm以下の固形粒子を分離し、分離された5μm以下の固形粒子はセメント材料として利用する。固形分が分離された洗浄後の洗浄水には微量成分が残存しているが、界面活性剤を添加し、スラリー化工程で再利用する。洗浄後の洗浄水中の微量成分は、スラリー化工程の後の洗浄工程で簡単に洗浄分離できるので問題にならない。洗浄水を再利用することで使用水量を減らすことができ、後処理の処理量を減らすことができる。 The washing water after washing contains particles having a size of 5 μm or less and trace components separated from the surface of the particles having a size of 5 μm or more. The washed water after washing is put into a centrifugal separator to separate solid particles of 5 μm or less, and the separated solid particles of 5 μm or less are used as a cement material. Although trace components remain in the washed water after the solid content is separated, a surfactant is added and reused in the slurrying step. The trace component in the wash water after washing can be easily washed and separated in the washing process after the slurrying process, so that there is no problem. By reusing washing water, the amount of water used can be reduced, and the amount of post-treatment can be reduced.
以下の表1に種類の異なるA、B、C、D4種の石炭灰に対して、本発明の石炭灰の地盤材料化方法を実施した結果を示す。 Table 1 below shows the results of carrying out the method for converting the ground material of coal ash of the present invention to different types of A, B, C, and D4 types of coal ash.
表1に示されるように、本発明の石炭灰の地盤材料化方法によって、大幅に溶出成分が石炭灰から分離している状況がわかる。ただし、D種のヒ素に関しては、特異的に溶出濃度が高いため二次処理を行う必要がある。なお、ホウ素とフッ素に関しては、A種とC種でマスバランスが合っていない。これは、高固形分濃度下での分級分離処理過程で、自成分間の化学反応が生じたためである。すなわち、石炭灰に含まれているカルシウムは高pH下でホウ素、フッ素と反応し、それぞれホウ酸カルシウムとフッ化カルシウムを生成して沈殿したため溶出が抑えられた結果である。添加水量が多くなると沈殿量が少なくなり、ホウ素等の溶出量を下げることができない。 As shown in Table 1, it can be seen that the leaching component is largely separated from the coal ash by the method for converting the ground material of coal ash according to the present invention. However, since D-type arsenic has a specifically high elution concentration, it is necessary to perform secondary treatment. In addition, regarding boron and fluorine, mass balance does not match between A type and C type. This is because a chemical reaction between the components occurred in the classification separation process under a high solid content concentration. That is, the calcium contained in the coal ash reacts with boron and fluorine under high pH to generate and precipitate calcium borate and calcium fluoride, respectively. When the amount of added water increases, the amount of precipitation decreases, and the amount of elution of boron and the like cannot be reduced.
以上のように、本発明の石炭灰の地盤材料化方法によって、極めて高い分離効率が達成できるとともに、副次的にホウ素、フッ素の溶出を抑制でき、分離された5μm以上の粒子は地盤材料として十分利用できる。 As described above, the coal ash ground materialization method of the present invention can achieve extremely high separation efficiency, and secondary elution of boron and fluorine can be suppressed, and the separated particles of 5 μm or more can be used as the ground material. Fully available.
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Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS58159885A (en) * | 1982-03-17 | 1983-09-22 | Shimizu Constr Co Ltd | Manufacture of coal ash slurry |
JPS6219260A (en) * | 1985-07-17 | 1987-01-28 | Junko Ishizu | Process and device for sorting and recycling of excavated earth in construction work from sludge |
JPS6265756A (en) * | 1985-09-17 | 1987-03-25 | Catalysts & Chem Ind Co Ltd | Wet classifying method for granular particle |
JPS63234085A (en) * | 1987-03-20 | 1988-09-29 | Shimizu Constr Co Ltd | Artificial basement material consisting of fly ash |
JPH09125395A (en) * | 1995-11-01 | 1997-05-13 | Pub Works Res Inst Ministry Of Constr | Device and method for adjusted muddy water treatment |
JPH09225441A (en) * | 1996-02-26 | 1997-09-02 | Chichibu Onoda Cement Corp | Treatment of fly ash and application thereof |
JP3505000B2 (en) * | 1995-03-17 | 2004-03-08 | 太平洋セメント株式会社 | Coal ash treatment method |
JP2005246323A (en) * | 2004-03-05 | 2005-09-15 | Arumaare Engineering Kk | Recycling apparatus and method for soil generated by construction |
-
2007
- 2007-05-24 JP JP2007137616A patent/JP5024608B2/en active Active
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS58159885A (en) * | 1982-03-17 | 1983-09-22 | Shimizu Constr Co Ltd | Manufacture of coal ash slurry |
JPS6219260A (en) * | 1985-07-17 | 1987-01-28 | Junko Ishizu | Process and device for sorting and recycling of excavated earth in construction work from sludge |
JPS6265756A (en) * | 1985-09-17 | 1987-03-25 | Catalysts & Chem Ind Co Ltd | Wet classifying method for granular particle |
JPS63234085A (en) * | 1987-03-20 | 1988-09-29 | Shimizu Constr Co Ltd | Artificial basement material consisting of fly ash |
JP3505000B2 (en) * | 1995-03-17 | 2004-03-08 | 太平洋セメント株式会社 | Coal ash treatment method |
JPH09125395A (en) * | 1995-11-01 | 1997-05-13 | Pub Works Res Inst Ministry Of Constr | Device and method for adjusted muddy water treatment |
JPH09225441A (en) * | 1996-02-26 | 1997-09-02 | Chichibu Onoda Cement Corp | Treatment of fly ash and application thereof |
JP2005246323A (en) * | 2004-03-05 | 2005-09-15 | Arumaare Engineering Kk | Recycling apparatus and method for soil generated by construction |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2020056270A (en) * | 2018-10-04 | 2020-04-09 | 日本基礎技術株式会社 | Liquefaction countermeasure method |
JP7199190B2 (en) | 2018-10-04 | 2023-01-05 | 日本基礎技術株式会社 | Liquefaction countermeasure method |
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