KR20160108764A - The method of neutralization phospho-gypsum using Fluidized bed boiler Fly ash and use thereof - Google Patents

The method of neutralization phospho-gypsum using Fluidized bed boiler Fly ash and use thereof Download PDF

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KR20160108764A
KR20160108764A KR1020150031679A KR20150031679A KR20160108764A KR 20160108764 A KR20160108764 A KR 20160108764A KR 1020150031679 A KR1020150031679 A KR 1020150031679A KR 20150031679 A KR20150031679 A KR 20150031679A KR 20160108764 A KR20160108764 A KR 20160108764A
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fly ash
gypsum
fluidized bed
bed boiler
phosphoric acid
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KR101881459B1 (en
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김병권
김원석
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쌍용양회공업(주)
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    • 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
    • C04B28/14Compositions 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 calcium sulfate cements
    • C04B28/16Compositions 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 calcium sulfate cements containing anhydrite, e.g. Keene's 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
    • C04B18/04Waste materials; Refuse
    • C04B18/06Combustion residues, e.g. purification products of smoke, fumes or exhaust gases
    • C04B18/061Ashes from fluidised bed furnaces
    • 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
    • C04B18/04Waste materials; Refuse
    • C04B18/06Combustion residues, e.g. purification products of smoke, fumes or exhaust gases
    • 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
    • C04B18/04Waste materials; Refuse
    • C04B18/06Combustion residues, e.g. purification products of smoke, fumes or exhaust gases
    • C04B18/08Flue dust, i.e. fly ash
    • 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
    • C04B22/00Use of inorganic materials as active ingredients for mortars, concrete or artificial stone, e.g. accelerators, shrinkage compensating agents
    • C04B22/08Acids or salts thereof
    • C04B22/16Acids or salts thereof containing phosphorus in the anion, e.g. phosphates
    • 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
    • C04B2103/00Function or property of ingredients for mortars, concrete or artificial stone
    • C04B2103/20Retarders
    • 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

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Combustion & Propulsion (AREA)
  • Civil Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Processing Of Solid Wastes (AREA)
  • Curing Cements, Concrete, And Artificial Stone (AREA)

Abstract

Disclosed is a manufacturing method of a cement setting retarder using fly ash from a fluidized bed boiler. According to the present invention, the manufacturing method of a cement setting retarder comprises the following steps of: preparing phosphogypsum, as a starting material, having pH of 4.0 at most generated in a process of extracting phosphoric acid; and neutralizing the phosphogypsum to have pH of at least 7.0 by mixing the phosphogypsum with fly ash obtained from circulating fluidized bed boiler. According to the present invention, neutralized phosphogypsum applicable as a cement setting retarder can be obtained. Through the present invention, discarded or stowed resources can be usefully used to resolve problems of waste and stowage, and can be reused.

Description

유동층 보일러 비산회를 활용한 인산석고 중화 방법 그의 활용 {The method of neutralization phospho-gypsum using Fluidized bed boiler Fly ash and use thereof}The fluidized-bed boiler Fly ash and use of the method of neutralizing phosphate gypsum using the fluidized-bed boiler fly ash

본 발명은 유동층 보일러에서 발생하는 비산회를 활용하여 인광석으로부터 인산을 회수하는 공정에서 발생하는 인산석고를 중화하여 시멘트용 응결지연제로 재활용하는 방법에 관한 것으로, 보다 상세하게는 인광석으로부터 인산 추출 공정에서 발생하는 산성의 인산석고에 순환유동층 보일러에서 황을 제거하기 위해 투입하는 석회석과 반응하여 발생되는 알칼리성의 비산회를 직접 또는 수화처리 후 혼합하고 숙성시킴으로써 중화 및 수용성의 인산을 불용성의 인산으로 안정화 시키는 방법이다. 또한 이렇게 안정화 된 중화 인산석고를 시멘트 클링커에 첨가하여 분쇄함으로써 시멘트 응결지연제로 재활용하는 방법에 관한 것이다.The present invention relates to a method for neutralizing phosphoric acid gypsum generated in a process for recovering phosphoric acid from phosphorus by utilizing fly ash generated in a fluidized bed boiler and recycling it as a caking retarder for cement. More particularly, Which is reacted with limestone added to the acidic phosphate gypsum to remove sulfur from the circulating fluidized bed boiler, is directly or hydrated and then mixed and aged to stabilize the neutralized and soluble phosphoric acid with insoluble phosphoric acid . The present invention also relates to a method of recycling this stabilized neutralized phosphoric acid gypsum as a cement retarding agent by adding it to a cement clinker and crushing it.

유동층(Fluidized Bed) 보일러란 석탄을 적당하게 분쇄하여 만든 석탄입자를 유동매체의 혼합가루층에 적정속도로 공기로 불어 넣어 유동시켜 연소하는 방식의 보일러를 말하며, 석탄을 연소하기 위한 보일러로 일반적으로 발전에 많이 사용되고 있다. 이 방식은 톡특한 연소 원리 때문에 재래식 석탄연소 기술에 비해 석탄연소가 가지고 있는 문제점을 극복할 수 있다. Fluidized bed boiler refers to a boiler that burns coal particles made by appropriately pulverizing coal to the mixed powder layer of the fluidized medium by blowing air at an appropriate rate, and is generally used as a boiler for burning coal. It is widely used for power generation. This method overcomes the problems of coal combustion compared to conventional coal combustion technology due to its unique combustion principle.

이 보일러의 장점은 연소시 비교적 안정적으로 잘 유지시킬 수 있고 낮은 온도에서 연소가 가능하기 때문에 낮은 품위의 석탄도 연소가 가능하며 낮은 온도로 인해 환경오염 물질인 질소산화물 (NOx)의 발생이 줄어들게 된다는 점이다. The advantage of this boiler is that it can be maintained relatively stable during combustion and can be burned at low temperature, so it is possible to burn coal with low quality and the generation of NOx, which is an environmental pollutant, It is a point.

유동층 보일러에서 석탄을 연소시키는 경우 석탄 내 황 성분의 연소에 의해 발생하는 황산화물(SOx)의 제어를 위해 석회석을 투입하게 된다. 투입된 석회석은 생석회와 이산화탄소로 분해되고 이 때 발생한 생석회가 황산화물과 반응하여 석고 (CaSO4)가 생성되므로써 탈황이 된다. 이 과정을 통해 생성되어 비산된 분진은 집진설비에서 포집되는데, 이것이 바로 비산회이다. When coal is burned in a fluidized bed boiler, limestone is injected to control the sulfur oxides (SOx) generated by the combustion of the sulfur components in the coal. The limestone is decomposed into quicklime and carbon dioxide, and the lime is reacted with sulfur oxides to produce gypsum (CaSO 4 ), which is then desulfurized. The dust generated and scattered in this process is collected in the dust collector, which is a fly ash.

비산회의 주성분은 석고이며, 석회석이 분해되는 과정에서 생긴 생석회도 일부 존재한다. 이에 따라 비산회는 pH가 높은 알칼리 특성을 지니게 된다. The main component of the fly ash is gypsum, and some of the lime is formed during the process of limestone decomposition. As a result, the fly ash has an alkaline property with a high pH.

국내에서 발생되는 이 비산회는 약 80만톤이며, 향후 유동층 보일러 방식의 발전설비가 늘어날 것으로 예상되기 때문에 비산회의 발생량은 꾸준히 증가될 것으로 판단되고 있다.The amount of fly ash generated in Korea is about 800,000 tons. It is expected that the amount of fly ash will be steadily increased because the power generation facilities of the fluidized bed boiler type are expected to increase in the future.

한편, 인산석고는 아래 반응식 1에 나타낸 바와 같이, 인광석과 황산을 이용해 인산 제조시부산되는 석고로 원료인 인광석에 황산을 처리하는 습식공정에서 발생한다. On the other hand, as shown in the following reaction formula (1), the gypsum gypsum is generated in a wet process in which sulfuric acid is treated in phosphorus as a raw material by using gypsum which is used in the production of phosphoric acid by using phosphate or sulfuric acid.

(반응식 1)(Scheme 1)

Ca10(PO4)6F2(s)+10H2SO4+20H2O Ca 10 (PO 4 ) 6 F 2 (s) + 10 H 2 SO 4 + 20 H 2 O

→ 10CaSO4ㆍ2H2O(s)+6H3PO4+ 2HF
→ 10CaSO 4 and 2H 2 O (s) + 6H 3 PO 4 + 2HF

국내에서는 2008년에 1,836천톤이 발생되었으나 재활용율이 낮아 잉여분이 발생하였고 2009년도 기준 2000만톤에 달하는 양이 적치되어 있다. In Korea, 1,836,000 tons were generated in 2008, but surplus was generated due to low recycling rate.

이에 비산회 및 인산 석고의 활용 방안에 대한 새로운 방법이 필요하다.Therefore, a new method for utilization of fly ash and phosphate gypsum is needed.

이상과 같이, 석고는 일반적으로 시멘트용 응결지연제로 사용될 수 있으나,비산회에 포함되어 있는 석고의 량이 적기 때문에 비산회 단독으로 응결지연제로 사용하는 것은 곤란하며, 인산 제조시 부산물로 생성되는 인산 석고는 pH가 2.5정도로 강산성을 나타내어시멘트 강도를 떨어뜨리고 수용성 P2O5 같은 성분에 의해 응결이 너무 지연되어 시멘트가 굳지 않는 문제가 발생할 수 있다.As described above, gypsum can be generally used as a coagulation retarding agent for cement, but it is difficult to use it as a coagulation retardant alone because the amount of gypsum contained in the fly ash is small. Phosphate gypsum produced as a by- Is strongly acidic to about 2.5, so that the strength of the cement is lowered and the condensation is delayed too much by the component such as water-soluble P 2 O 5 , so that the cement may not be hardened.

이에 본 발명의 발명자들은, 유동층 보일러 비산회를 단독 혹은 수화처리 후 인산석고와 혼합하여 강 산성의 인산석고를 중화시키고 또한 비산회에 포함되어 있는 알칼리성의 생석회(CaO)성분을 활용하여 수용성 인산을 난 불용성의 인산3석회 (Ca3(PO4)2)로 전환시켜 수용성 인산량을 줄임으로써 지나친 응결지연 문제를 해결할 수 있음을 발견하였고, 단독으로는 시멘트 응결지연제로 사용하지 못하는 유동층 보일러 비산회와 인산석고를 시멘트 응결지연제로 재활용할 수 있음을 확인하였다.Accordingly, the inventors of the present invention have found that when the fluidized-bed boiler fly ash is mixed with phosphoric acid gypsum alone or hydration-treated to neutralize the strong acid phosphate gypsum and furthermore, by using the alkaline calcium oxide (CaO) component contained in the fly ash, (Ca 3 (PO 4 ) 2 ) to reduce the amount of water soluble phosphoric acid. In addition, it was found that the fluidized bed boiler fly ash and phosphate plaster Can be recycled as a cement retarding agent.

따라서, 본 발명은 재활용이 되지 않는 유동층 보일러 비산회를 단독 혹은 수화처리 후 인산석고와 혼합 반응시켜, 중화하여 pH를 중성 이상으로 안정화하고 수용성 인산 농도를 낮춘 인산중화석고를 제조하고 이를 시멘트 응결지연제로 활용하는 것을 목적으로 한다. Accordingly, the present invention provides a phosphoric acid neutralization gypsum which is neutralized to stabilize the pH to neutral or higher and to lower the concentration of soluble phosphoric acid by mixing or reacting the fluidized bed boiler fly ash which is not recycled, The purpose is to utilize.

또한 본 발명은 전술한 응결 지연제를 포함하는 시멘트의 제조 방법을 제공하는 것을 목적으로 한다. Another object of the present invention is to provide a method for producing cement comprising the above-mentioned coagulation retarding agent.

상기와 같은 목적을 달성하기 위하여 본 발명은, 인산 추출 공정에서 발생하는 pH 4.0이하의 인산석고를 출발물질로서 준비하는 단계; 및 상기 인산석고에 순환유동층 보일러 비산회를 혼합하여 상기 인산석고를 pH 7 이상으로 중화하는 단계를 포함하는 시멘트 응결 지연제의 제조 방법을 제공한다.In order to accomplish the above object, the present invention provides a method for producing a phosphate gypsum, And mixing the phosphate gypsum with a circulating fluidized bed boiler fly ash to neutralize the phosphate gypsum to a pH of 7 or higher.

본 발명은 상기 비산회를 수화 처리하는 단계를 더 포함할 수 있다. The present invention may further include hydrating the fly ash.

본 발명에서 상기 유동층 보일러 비산회 또는 그 수화 처리물은 상기 인산석고 100 중량부에 대하여 내할로 3중량부 내지 40중량부 포함할 수 있다. In the present invention, the fluidized bed boiler fly ash or the hydration product thereof may contain 3 to 40 parts by weight of the internal slurry with respect to 100 parts by weight of the phosphate gypsum.

또한 본 발명은, 제1항에 기재된 제조 방법에 의해 제조된 시멘트 응결 지연제를 시멘트 클링커와 배합하는 것을 특징으로 하는 시멘트 제조 방법을 제공한다.The present invention also provides a method for producing a cement, characterized in that the cement retarding agent produced by the production method according to claim 1 is blended with a cement clinker.

본 발명의 중화방법에 따르면 폐기되는 유동층 보일러 비산회 단독 혹은 수화처리 후 응결지연제로 사용이 불가능한 인산석고를 혼합, 숙성, 건조 하는 단계를 통해 시멘트 응결지연제로 사용 가능한 인산중화석고를 얻을 수 있으며, 이를 통해 폐기되거나 적치되어 있는 자원을 유용하게 활용 하여 폐기나 적치의 문제를 해결하고 자원으로 재활용 할 수 있다.According to the neutralization method of the present invention, it is possible to obtain a phosphoric acid neutralization gypsum which can be used as a cement retarding agent by mixing, aging and drying phosphoric acid gypsum which is not usable as a fluidized bed boiler fly ash after disposal or as a coagulation retarder after hydration treatment. It is possible to utilize resources that have been disposed of or being disposed of, thereby solving the problem of disposal or repatriation and recycling them as resources.

도 1은 본 발명의 일실시예에 따른 시멘트 응결 지연제의 제조 방법을 개략적으로 도시한 도면이다.
도 2는 본 발명의 다른 실시예에 따른 시멘트 응결 지연제의 제조 방법을 개략적으로 도시한 도면이다.
도 3은유동층 보일러 비산회를 XRD로 분석한 결과를 나타낸 그래프이다.
FIG. 1 is a view schematically showing a method for producing a cement retarder according to an embodiment of the present invention. Referring to FIG.
2 is a view schematically showing a method for producing a cement retarder according to another embodiment of the present invention.
3 is a graph showing the results of XRD analysis of the fluidized bed boiler fly ash.

이하, 본 발명을 상세히 설명한다.Hereinafter, the present invention will be described in detail.

본 발명은 순환유동층 보일러 비산회를 활용하여 인광석에서 인산을 회수하는 공정에서 발생하는 인산석고를 중화하여 시멘트용 응결지연제로 재활용하는 방법을 제공한다.The present invention provides a method of neutralizing phosphorus gypsum generated in the process of recovering phosphoric acid from phosphorus by utilizing a circulating fluidized bed boiler fly ash and recycling it as a caking retarder for cement.

구체적으로는, 본 발명은 인광석으로부터 인산 추출 공정에서 발생하는 산성의 인산석고에 순환유동층 보일러에서 황을 제거하기 위해 투입하는 석회석과 반응하여 발생되는 알칼리성의 비산회를단독 혹은 수화처리하여 혼합하고 숙성시킴으로서 중화 및 수용성의 인산을 불용성의 인산으로 안정화 시키는 방법을 사용한다. More specifically, the present invention relates to an acidic phosphate gypsum produced from a phosphate extraction process from phosphate ore by mixing an alkaline fly ash produced by reacting with limestone to remove sulfur from a circulating fluidized bed boiler, A method of stabilizing neutralized and soluble phosphoric acid with insoluble phosphoric acid is used.

또한,본 발명에 따라 안정화 된 중화인산석고를 시멘트 클링커에 첨가하여 분쇄하게 되면 시멘트 응결지연제로 재활용할 수 있게 된다.Further, when the stabilized neutralized phosphoric acid gypsum according to the present invention is added to the cement clinker and pulverized, it can be recycled as a cement retarding agent.

도 1은 본 발명의 바람직한 실시예에 따른 중화 인산석고의 제조 방법을 개략적으로 도시한 도면이다. 1 is a schematic view illustrating a method for producing neutralized phosphoric acid gypsum according to a preferred embodiment of the present invention.

도 1을 참조하면, 출발 원료로서 순환유동층 보일러 비산회(S10)와, 인산 추출 공정에서 발생하는 인산석고가 각각 준비된다(S20). 여기서, 상기 인산석고는 통상 pH가 4.0이하이다.Referring to FIG. 1, the circulating fluidized bed boiler fly ash (S10) and the phosphate gypsum generated in the phosphoric acid extraction process are prepared as starting materials (S20). Here, the pH of the phosphate gypsum is usually 4.0 or less.

이어서, 출발물질을 적절한 방식으로 혼합한다(S100). 본 발명에서 혼합 단계는 통상의 혼합 공정 예컨대 혼합용 믹서(Mixer) 등의 공정에 의해 수행될 수 있다. The starting materials are then mixed in a suitable manner (SlOO). In the present invention, the mixing step can be carried out by a conventional mixing step, such as a mixing mixer.

다음으로, 혼합된 물질을 숙성한다(S110). 본 발명에서 숙성 단계는 대기 하에서 2~3일간 건조함으로써 수행될 수 있다.Next, the mixed material is aged (S110). In the present invention, the aging step can be carried out by drying for 2 to 3 days under the atmosphere.

한편, 도 2는 본 발명의 다른 실시예에 따른 중화 인산석고의 제조 절차를 간략히 나타낸 도면이다.Meanwhile, FIG. 2 is a view illustrating a procedure of manufacturing a neutralized phosphoric acid gypsum according to another embodiment of the present invention.

도 2를 참조하면, 본 실시예에서 비산회는 수화처리 되는 것을 특징으로 한다(S12). 본 발명에서 수화 처리는 물과 유동층 보일러 비산회와 혼합 및 여과 건조과정에 의해 수행될 수 있다. 수화처리시 물과 유동층 보일러 비산회와의 혼합비는 중량비로 1:1~1:5로 하고, 수화시간은 1시간~6시간의 범위에서 실시한다.Referring to FIG. 2, the fly ash is characterized in that the fly ash is treated (S12). In the present invention, the hydration treatment can be performed by mixing with water and a fluidized bed boiler fly ash, and filtering and drying. The mixing ratio of water to the fluidized bed boiler fly ash is 1: 1 to 1: 5 by weight and the hydration time is 1 to 6 hours.

또한, 본 실시예에서 혼합 및 숙성된 혼합물에 포함된 수분은 자연 건조를 시키나 수요자의 요구시 기타 적절한 방법을 적용하여 건조될 수 있다. In addition, in the present embodiment, the moisture contained in the mixed and aged mixture is allowed to dry naturally, or may be dried by other appropriate methods at the request of the consumer.

이하에서는 본 발명을 보다 상세히 설명한다. Hereinafter, the present invention will be described in more detail.

표 1은 유동층 보일러에서 발생하는 비산회의 XRF 분석에 따른 화학성분, pH 및 총유기탄소함량을 중량%로 나타낸 표이다. Table 1 shows the chemical composition, pH, and total organic carbon content of the fly ash produced in the fluidized bed boiler by weight%.

(단위:wt %)(Unit: wt%) SiO2 SiO 2 Al2O3 Al 2 O 3 Fe2O3 Fe 2 O 3 CaOCaO MgOMgO Na2ONa 2 O K2OK 2 O TiO2 TiO 2 SO3 SO 3 P2O5 P 2 O 5 LOILOI TOCTOC 18.7518.75 9.079.07 5.375.37 34.2034.20 5.975.97 2.802.80 0.520.52 0.570.57 14.2514.25 0.240.24 4.764.76 0.180.18

일반적인 발전소에서 발생하는 비산회의 경우 CaO 함량이 5%내외 임에 반해 유동층 보일러 비산회의 경우 CaO 성분이 표 1에 나타낸 바와 같이 34.20%로 높음을 알 수 있다. 또한 SO3함량도 높아 다량의 CaSO4가 포함되어 있음을 추정할 수 있다. 표 1에서 LOI는 강열감량을 의미하는데 이는 950℃에서의 유기물질이나 결합수의 증발에 의해 무게가 감소한 량을 의미한다.In case of fly ash from general power plants, CaO content is about 5%, while that of fluidized bed boiler fly ash is 34.20% as shown in Table 1. In addition, it can be assumed that the content of SO 3 is high and contains a large amount of CaSO 4 . In Table 1, LOI means ignition loss, which means the amount of weight reduction due to the evaporation of organic materials or combined water at 950 ° C.

유동층 보일러의 비산회에서 CaO 함량이 높은 이유는 황산화물의 제거를 위해 석회석을 투입하기 때문이다. 투입된 석회석(CaCO3)은 높은 온도에서 생석회(CaO)와 이산화탄소(CO2)로 분해되고 이 생석회가 황산화물과 반응하여 석고(CaSO4)를 생성하게 된다. 한편, 황산화물과 미반응한 CaO가 존재하게 되는데 이것에 의해 알칼리성을 띄게 된다. 그러므로, 이 미반응 CaO는 중화제로 활용할 수 있게 된다. The reason for the high CaO content in the fly ash of a fluidized bed boiler is that limestone is added to remove sulfur oxides. CaCO 3 is decomposed into calcium oxide (CaO) and carbon dioxide (CO 2 ) at high temperature, and the calcium oxide reacts with sulfur oxides to form gypsum (CaSO 4 ). On the other hand, CaO unreacted with sulfur oxides is present, which results in alkalinity. Therefore, the unreacted CaO can be utilized as a neutralizing agent.

인산석고와 혼합하여 중화 및 수용성 인산의 안정화 반응을 위해서는 다소의 수분이 필요하다. 유동층 보일러 비산회를 건조 상태로 혼합하여도 인산석고 자체의 보유 수분에 의해 중화 및 수용성 인산 안정화 반응이 일어난다. 하지만 그 효과를 극대화 하기 위해서는 유동층 보일러 비산회에 물을 가해 수화를 시킨 후 수분이 있는 상태로 인산석고와 혼합하는 것이 반응 측면에서 유효하다. 따라서, 본 발명에서는 유동층비산회를 직접 혹은 물과 반응시켜 수화처리 한 수화처리물을 모두 사용한다. 또한 수화처리시는 시멘트 품질에 영향을 끼칠 수 있는 비산회에 포함된 미연카본의 제거가 가능하기 때문에 시멘트 품질 측면에서도 도움이 된다.
Some water is needed for neutralization and water-soluble phosphoric acid stabilization by mixing with phosphate gypsum. Even when mixed with the fluidized bed boiler fly ash, the neutralization and water soluble phosphate stabilization reaction occurs due to the water content of the phosphate gypsum itself. However, in order to maximize the effect, it is effective in terms of reaction that water is added to the fluidized bed boiler fly ash and mixed with phosphate gypsum in the presence of water. Therefore, in the present invention, all hydrolysis products obtained by reacting the fluidized bed fly ash directly or with water are used. In hydration treatment, it is possible to remove unburned carbon contained in the fly ash which may affect the quality of cement, which is also helpful in terms of cement quality.

도 3은 유동층 보일러 비산회의 XRD 분석결과를 나타낸 그래프이다.3 is a graph showing the results of XRD analysis of the fluidized bed boiler fly ash.

도 3에서 알 수 있는 바와 같이, 분석결과 비산회에는 생석회(CaO) 및 석고(CaSO4)가 존재함을 알 수 있고, 미 분해된 석회석(CaCO3)이 일부 존재하는 것도 확인할 수 있다. As can be seen from FIG. 3, it can be seen that calcium oxide (CaO) and gypsum (CaSO 4 ) are present in the fly ash and that some of the undissolved limestone (CaCO 3 ) is present.

아래 표 2는 인산석고를 XRF로 분석한 화학성분(wt%) 및 pH를 나타낸 표이다. Table 2 below is a table showing the chemical composition (wt%) and pH of the gypsum obtained by XRF analysis.

(단위:wt %, pH 제외)(Unit: wt%, excluding pH) SiO2 SiO 2 Al2O3 Al 2 O 3 Fe2O3 Fe 2 O 3 CaOCaO MgOMgO SrOSrO Na2ONa 2 O K2OK 2 O TiO2 TiO 2 SO3 SO 3 P2O5 P 2 O 5 수용성
P2O5
receptivity
P 2 O 5
pHpH
2.702.70 0.210.21 0.060.06 31.5431.54 0.060.06 0.090.09 0.090.09 0.030.03 0.020.02 44.1644.16 0.330.33 0.170.17 2.502.50

표 2로부터 인산석고의 경우 pH가 2.5정도로 강산성이고, 수용성 P2O5도 Total-P2O5의 50%수준인 0.17%로 높게 나타난다. 이러한 이유로, 인산석고는 단독으로 사용할 경우 강산성 및 높은 수용성 P2O5 함량에 의해 응결이 늦어지는 시멘트 품질 문제가 발생하게 된다. As shown in Table 2, the pH of the gypsum gypsum is strongly acidic to 2.5 and the water-soluble P 2 O 5 is 0.17%, which is 50% of the total-P 2 O 5 level. For this reason, when the phosphate gypsum is used singly, there is a problem of quality of cement which is slow in condensation due to strong acidity and high water-soluble P 2 O 5 content.

따라서,본 발명에서는 강산성의 인산석고에 생석회(CaO) 성분을 함유한 유동층 보일러 비산회를직접 혹은 수화시켜 혼합하여 pH가 7.0이상이 되도록 중화시키는 방법을 사용한다. 또한 생석회(CaO)성분을 활용하여 아래 반응식 2에서와 같이 수용성 인산을 난 불용성의 인산3석회 (Ca3(PO4)2)로 전환시키는 반응을 유도한다. 이에 따라, 수용성 인산량이 감소하여 시멘트 응결지연제로 사용하지 못하는 인산석고를 중화인산석고로 전환, 시멘트 응결지연제로 사용할 수 있게 된다. Therefore, in the present invention, a fluidized-bed boiler fly ash containing a calcium oxide (CaO) component is added to strong acid phosphate gypsum directly or by hydration to neutralize the mixture to a pH of 7.0 or higher. In addition, calcium lime (CaO) is used to induce a reaction to convert water soluble phosphoric acid into an insoluble calcium phosphate lime (Ca 3 (PO 4 ) 2 ) as shown in the following reaction formula 2. As a result, the amount of water soluble phosphoric acid is reduced and the phosphate gypsum which can not be used as a cement retarding agent can be converted to neutralized phosphate gypsum and used as a cement retarding agent.

(반응식 2)(Scheme 2)

3CaO + P2O5(수용성) → Ca3(PO4)2 (난 불용성)
3CaO + P 2 O 5 (water-soluble) → Ca 3 (PO 4 ) 2 (insoluble)

본 발명에서, 인산석고와 유동층 보일러 비산회 단독 혹은 수화 처리물의 혼합비율은 시멘트용 응결지연제로 사용할 경우 품질에 문제가 없는 수준으로 정한다. 바람직하게는, 인산석고 100 중량부에 대하여 유동층 보일러 비산회단독 또는 수화처리물을 내할로 3중량부 내지 40중량부 포함하도록 하는 것이 좋다. 3중량부 미만으로 혼합하는 경우 중화효과를 발휘하지 못하고 40중량부를 초과하여 혼합하는 경우 SO3 함량이 낮아져 응결지연제로의 역할을 발휘하기 어렵다. 더욱 바람직하게는, 인산석고 100 중량부에 대해 유동층 보일러 비산회 단독 혹은 수화처리물을 내할로 5 중량부 내지 10 중량부를 혼합하는 것이 좋다.
In the present invention, the mixing ratio of the phosphate gypsum with the fluidized bed boiler fly ash or the hydration product is set to a level at which there is no problem in quality when used as a caking retarder. Preferably, 3 to 40 parts by weight of the fluidized bed boiler fly ash or water-containing treated water is contained in an amount of 3 to 40 parts by weight per 100 parts by weight of the gypsum. If the mixing ratio is less than 3 parts by weight, the neutralization effect is not exhibited. When the mixing ratio is more than 40 parts by weight, the content of SO 3 is low and it is difficult to exert its role as a coagulation retarding agent. More preferably, it is preferable to mix 5 to 10 parts by weight of the fluidized bed boiler fly ash alone or 100 parts by weight of the phosphate gypsum with water.

본 발명에 따라, 적정 비율로 혼합된 인산석고와 유동층 보일러 비산회는혼합 후 반응 및 안정화를 위해 숙성기간을 거치고 필요에 따라 수분함량을 줄이기 위해 자연건조를 실시한다.
According to the present invention, the phosphate gypsum and the fluidized bed boiler fly ash mixed at a proper ratio are aged for reaction and stabilization after mixing, and natural drying is carried out in order to reduce the water content as needed.

이하 실시예를 통해 본 발명을 더욱 상세히 설명한다.Hereinafter, the present invention will be described in more detail by way of examples.

(실시예 1)(Example 1)

유동층 보일러에서 얻은 비산회를수화처리한 것과 인산비료 제조공정에서 발생하는 인산석고를 비율별로 혼합하여 인산석고를 중화하였으며, 이렇게 중화된 인산석고의 pH 및 수용성 인산 함량을 측정하였다. 여기서, 비산회의 수화처리는 물과 비산회를 1:2로 혼합하고, 2시간 동안 교반 후 진공여과기로 여과한 것을 105℃에서 건조 후 분쇄한 것으로 하였다. 그리고 비산회수화처리물과 인산석고를 혼합, 그 혼합물을 자연 대기 건조상태에서 2일간 방치하여 숙성과정을 거쳤다.
The pH and soluble phosphate content of the neutralized phosphate gypsum were measured by neutralizing the phosphate gypsum by mixing the fly ash obtained from the fluidized bed boiler with hydrated phosphate and the phosphate gypsum produced by the phosphate fertilizer production process. Here, water and fly ash were mixed with water and fly ash at a ratio of 1: 2, stirred for 2 hours, filtered through a vacuum filter, and dried at 105 ° C for pulverization. The mixture of fly ash water and phosphoric acid gypsum was mixed and the mixture was allowed to stand for 2 days in a natural atmospheric dry condition.

아래 표 3은 측정 결과를 나타낸 표이다.표 3에서 비산회 혼합율은 인산석고에 내할로 첨가한 비산회(수화처리물)의 함량을 나타낸 값이다.
In Table 3, the fly ash mixing ratio is a value indicating the content of fly ash added to the gypsum (hydration treatment).

비산회
(수화처리물)
혼합율(wt%)
Fly ash
(Hydration treated water)
Mixing ratio (wt%)
미혼합Unmixed 55 88 1010 1515 4040
pHpH 2.502.50 9.239.23 10.6110.61 10.9410.94 11.5711.57 12.1612.16 수용성 인산
(wt%)
Soluble phosphoric acid
(wt%)
0.170.17 0.0100.010 0.0070.007 0.0050.005 0.0080.008 0.0070.007

표 3에 나타낸 바와 같이, 인산석고에 유동층 보일러 비산회를 혼합하는 경우 pH가 7.0 이상으로 상승함을 알 수 있었으며, 첨가량 증가에 따라 pH가 증가하여 알칼리성의 인산중화석고가 제조되기 때문에 시멘트 품질 측면에 있어서 상당히 좋을 것으로 생각된다. As shown in Table 3, when the fluidized bed boiler fly ash was mixed into the phosphate gypsum, the pH was increased to 7.0 or more. As the pH was increased with the addition amount, the alkaline phosphate gypsum was produced, And it is considered to be quite good.

또한 시멘트의 굳는 성질인 응결에 영향을 끼치는 수용성 인산의 경우 0.17 wt %에서 0.007~0.010 wt %로 대부분 불용성 인산으로 전환되어 안정화 됨을 확인할 수 있었다.
In addition, it was confirmed that the water soluble phosphoric acid which has the effect of setting the hardening property of cement is converted into 0.17 wt% to 0.007 ~ 0.010 wt% and is converted into insoluble phosphoric acid and stabilized.

(실시예 2)(Example 2)

유동층 보일러에서 얻은 비산회를 수화 처리한것과 인산비료 제조공정에서 발생하는 인산석고를 비율별로 혼합하여 제조한 인산중화석고를 시멘트 응결지연제로 사용시 품질에 미치는 영향을 확인하였다. 인산석고 100중량부에 대하여유동층 보일러 비산회(수화처리) 혼합량은내할로 5 중량부, 15 중량부, 40중량부로 하였다. 혼합 후 2일간 상온에서 숙성하여 인산중화석고를 제조하였다. 이렇게 제조된 인산중화석고를 클링커에시멘트 중의 SO3가 2.1 wt %가 되도록 투입하고 Lab. Mill에서 분말도 3,200±50cm2/g이 되도록 분쇄하여 시멘트를 제조하였다. 제조된 시멘트의 모르타르 압축강도 및 응결을 확인하였다. 그 결과를 표 4에 나타내었다.
The effects of phosphoric acid gypsum prepared by hydration of fly ash obtained from fluidized bed boiler and phosphoric acid gypsum produced by phosphoric acid fertilizer production process on the quality of cement retarder were investigated. The mixing amount of the fluidized bed boiler fly ash (hydration treatment) was 5 parts by weight, 15 parts by weight and 40 parts by weight based on 100 parts by weight of gypsum phosphate. The mixture was aged at room temperature for 2 days to prepare phosphoric acid neutralized gypsum. The phosphoric acid neutralization gypsum thus prepared was added to the clinker so that the SO 3 content in the cement was 2.1 wt%. And the powder was pulverized to have a particle size of 3,200 ± 50 cm 2 / g. The mortar compressive strength and coagulation of the cement were confirmed. The results are shown in Table 4.

구분division 모르타르 압축강도 (MPa)Mortar Compressive Strength (MPa) 모르타르 응결Mortar condensation 1d1d 3d3d 7d7d 28d28d 초결
(분)
Fresh
(minute)
종결
(시간:분)
closing
(Hour: minute)
수준 1Level 1 인산석고Phosphate plaster 7.967.96 26.8926.89 34.3634.36 47.5547.55 220220 5:405:40 수준 2Level 2 비산회5wt%Fly ash 5wt% 9.709.70 29.0029.00 37.0337.03 51.4451.44 190190 4:504:50 수준 3Level 3 비산회 15wt%Fly ash 15wt% 9.319.31 28.3528.35 36.9336.93 50.1250.12 180180 4:404:40 수준 4Level 4 비산회 40wt%Fly ash 40wt% 8.968.96 28.4228.42 36.6436.64 49.9849.98 170170 4:204:20

상기 표 4에 나타낸 바와 같이 인산석고를 단독으로 사용하는 수준 1과, 유동층 보일러 비산회수화처리물을 첨가하여 제조한 인산중화석고를 사용한 수준 2~4를 비교할 때, 수준 1에 비해 압축강도가 증가하고 응결은 단축되는 것을 알 수 있다. 이는 CaO에 의한 중화의 효과에 따라 모르타르 강도가 안정적으로 발현이 되어 품질에 영향이 없게 되고, 수용성 인산의 불용화에 따라 응결이 아주 늦어지는 문제를 해결한 것이라고 말할 수 있다.As shown in Table 4 above, when the level 1 using phosphate gypsum alone and the level 2 to 4 using phosphoric acid neutralized gypsum prepared by adding the fluidized bed boiler fly ash water treatment, the compressive strength was increased And the condensation is shortened. It can be said that the mortar strength is stably expressed according to the effect of neutralization by CaO, so that the quality is not influenced, and the problem of slowing of condensation due to the insolubilization of water-soluble phosphoric acid is solved.

따라서, 본 결과로 볼 때 인산석고에 유동층 보일러 비산회를활용하여 혼합하고 숙성시키게 되면 시멘트 품질에 영향을 끼치지 않는 시멘트 제조용 응결지연제로 재활용이 가능함을 확인할 수 있다. As a result, it can be confirmed that mixing and aging by using fluidized bed boiler fly ash in phosphate gypsum can be recycled as a coagulation retardant for cement production which does not affect the quality of cement.

Claims (4)

인산 추출 공정에서 발생하는 pH 4.0 이하의 인산석고를 출발물질로서 준비하는 단계; 및
상기 인산석고에 순환유동층 보일러 비산회를 혼합하여 상기 인산석고를 pH 7 이상으로 중화하는 단계를 포함하는 시멘트 응결 지연제의 제조 방법.
Preparing phosphoric acid gypsum as a starting material at a pH of 4.0 or lower which is generated in the phosphoric acid extraction step; And
And mixing the phosphate gypsum with a circulating fluidized bed boiler fly ash to neutralize the phosphate gypsum to a pH of 7 or higher.
제1항에 있어서,
상기 비산회를 수화 처리하는 단계를 더 포함하는 것을 특징으로 하는 시멘트 응결 지연제의 제조 방법.
The method according to claim 1,
Further comprising the step of hydrating the fly ash. ≪ RTI ID = 0.0 > 21. < / RTI >
제1항 또는 제2항에 있어서,
상기 유동층 보일러 비산회는 상기 인산석고 100 중량부에 대하여 내할로 3중량부 내지 40 중량부 포함하는 것을 특징으로 하는 시멘트 응결 지연제의 제조 방법.
3. The method according to claim 1 or 2,
Wherein the fluidized bed boiler fly ash comprises 3 to 40 parts by weight of the internal mortar with respect to 100 parts by weight of the phosphate gypsum.
제1항에 기재된 제조 방법에 의해 제조된 시멘트 응결 지연제를 시멘트 클링커와 배합하는 것을 특징으로 하는 시멘트 제조 방법.A method for producing a cement according to claim 1, wherein the cement retarding agent produced by the production method according to claim 1 is blended with a cement clinker.
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CN108715441A (en) * 2018-06-01 2018-10-30 四川省雷波明信化工有限公司 A kind of fluidized bed process phosphoric acid production technique and system
CN108996937A (en) * 2018-07-09 2018-12-14 铜陵菻科工业石膏综合利用有限责任公司 A method of cement retarder is prepared with industry by-product gypsum
CN109320117A (en) * 2018-10-18 2019-02-12 中国葛洲坝集团水泥有限公司 Modified ardealite and preparation method thereof as cement retarder
CN109734344A (en) * 2019-03-05 2019-05-10 昆明川金诺化工股份有限公司 A method of cement retarder is prepared using half water ardealite
KR20190112617A (en) * 2018-03-26 2019-10-07 신유근 Manufacturing method of Gypsum for Cement using Phospho-gypsum
CN110981275A (en) * 2019-12-16 2020-04-10 宁国市锦泰环保科技有限公司 Phosphogypsum cement retarder and preparation method thereof
CN111807745A (en) * 2020-07-20 2020-10-23 铜仁学院 Modified phosphogypsum and preparation method thereof
CN111960710A (en) * 2020-08-24 2020-11-20 荆门新洋丰中磷肥业有限公司 Method for reducing water content of finished phosphogypsum retarder
CN112408896A (en) * 2020-11-21 2021-02-26 湖北云海混凝土有限公司 Super-retarding concrete and preparation method thereof

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KR20190112617A (en) * 2018-03-26 2019-10-07 신유근 Manufacturing method of Gypsum for Cement using Phospho-gypsum
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CN108996937A (en) * 2018-07-09 2018-12-14 铜陵菻科工业石膏综合利用有限责任公司 A method of cement retarder is prepared with industry by-product gypsum
CN109320117A (en) * 2018-10-18 2019-02-12 中国葛洲坝集团水泥有限公司 Modified ardealite and preparation method thereof as cement retarder
CN109734344A (en) * 2019-03-05 2019-05-10 昆明川金诺化工股份有限公司 A method of cement retarder is prepared using half water ardealite
CN110981275A (en) * 2019-12-16 2020-04-10 宁国市锦泰环保科技有限公司 Phosphogypsum cement retarder and preparation method thereof
CN111807745A (en) * 2020-07-20 2020-10-23 铜仁学院 Modified phosphogypsum and preparation method thereof
CN111960710A (en) * 2020-08-24 2020-11-20 荆门新洋丰中磷肥业有限公司 Method for reducing water content of finished phosphogypsum retarder
CN112408896A (en) * 2020-11-21 2021-02-26 湖北云海混凝土有限公司 Super-retarding concrete and preparation method thereof
CN112408896B (en) * 2020-11-21 2022-05-13 湖北云海混凝土有限公司 Super-retarding concrete and preparation method thereof

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