KR960011327B1 - Process for the preparation of magnetic tail using paper sludge ashes - Google Patents

Process for the preparation of magnetic tail using paper sludge ashes Download PDF

Info

Publication number
KR960011327B1
KR960011327B1 KR1019930031258A KR930031258A KR960011327B1 KR 960011327 B1 KR960011327 B1 KR 960011327B1 KR 1019930031258 A KR1019930031258 A KR 1019930031258A KR 930031258 A KR930031258 A KR 930031258A KR 960011327 B1 KR960011327 B1 KR 960011327B1
Authority
KR
South Korea
Prior art keywords
weight
paper sludge
sludge incineration
feldspar
clay
Prior art date
Application number
KR1019930031258A
Other languages
Korean (ko)
Other versions
KR950017811A (en
Inventor
이순걸
Original Assignee
한솔제지 주식회사
구형우
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 한솔제지 주식회사, 구형우 filed Critical 한솔제지 주식회사
Priority to KR1019930031258A priority Critical patent/KR960011327B1/en
Publication of KR950017811A publication Critical patent/KR950017811A/en
Application granted granted Critical
Publication of KR960011327B1 publication Critical patent/KR960011327B1/en

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
    • C04B35/00Shaped ceramic products characterised by their composition; Ceramics compositions; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products
    • C04B35/622Forming processes; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products
    • C04B35/64Burning or sintering processes
    • 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
    • C04B35/00Shaped ceramic products characterised by their composition; Ceramics compositions; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products
    • C04B35/01Shaped ceramic products characterised by their composition; Ceramics compositions; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products based on oxide ceramics
    • C04B35/16Shaped ceramic products characterised by their composition; Ceramics compositions; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products based on oxide ceramics based on silicates other than clay
    • 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
    • C04B35/00Shaped ceramic products characterised by their composition; Ceramics compositions; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products
    • C04B35/622Forming processes; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products
    • C04B35/62204Forming processes; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products using waste materials or refuse
    • 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
    • C04B35/00Shaped ceramic products characterised by their composition; Ceramics compositions; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products
    • C04B35/622Forming processes; Processing powders of inorganic compounds preparatory to the manufacturing of ceramic products
    • C04B35/626Preparing or treating the powders individually or as batches ; preparing or treating macroscopic reinforcing agents for ceramic products, e.g. fibres; mechanical aspects section B
    • C04B35/62605Treating the starting powders individually or as mixtures
    • C04B35/6261Milling
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B28WORKING CEMENT, CLAY, OR STONE
    • B28BSHAPING CLAY OR OTHER CERAMIC COMPOSITIONS; SHAPING SLAG; SHAPING MIXTURES CONTAINING CEMENTITIOUS MATERIAL, e.g. PLASTER
    • B28B3/00Producing shaped articles from the material by using presses; Presses specially adapted therefor
    • 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
    • C04B2235/00Aspects relating to ceramic starting mixtures or sintered ceramic products
    • C04B2235/02Composition of constituents of the starting material or of secondary phases of the final product
    • C04B2235/30Constituents and secondary phases not being of a fibrous nature
    • C04B2235/34Non-metal oxides, non-metal mixed oxides, or salts thereof that form the non-metal oxides upon heating, e.g. carbonates, nitrates, (oxy)hydroxides, chlorides
    • C04B2235/349Clays, e.g. bentonites, smectites such as montmorillonite, vermiculites or kaolines, e.g. illite, talc or sepiolite
    • 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

Abstract

The process for preparing magnetic tile comprises mixing 3-10 wt.% paper sludge incineration ash containing 2-10 % non-combustible powder, 30-40 wt.% pottery stone, 21-25 wt.% feldspar, 20 wt.% clay, 6-10 wt.% red earth and 1-5 wt.% kaolinite; pulverizing the raw material into a tile having an average particle size of 8.6-12.6 Pm; and molding the material under the pressure of 200-300 kg/cm2 and firing the molded body at a high temperature of 1,140-1,170 deg.C.

Description

제지슬러지 소각재를 이용한 자기질 타일의 제조방법Method of manufacturing magnetic tiles using paper sludge incineration

본 발명은 제지 공정중에 폐기물로 발생하는 제지슬러지 소각재를 재활용 하기 위한 것으로서 더욱 상세하게는 제지슬러지 소각재를 건축 자재로 널리 사용되는 타일의 제조에 이용하기 위한 방법에 관한 것이다.The present invention relates to a method for recycling paper sludge incineration ash generated as waste during the papermaking process, and more particularly, to a method for using paper sludge incineration ash in the manufacture of tiles widely used as building materials.

현재 국내 제지 공정중에서 발생되는 제지슬러지는 연간 70만톤 이상에 달하는 상당히 많은 양이며, 이 슬러지는 대부분 소각하여 매립 되어지고 있다. 그러나 제지슬러지 소각재는 외관상으로 좋지 않고, 더욱 매립할 경우 지하수를 오염시킬 수도 있으며 매립지 확보도 쉽지 않아 이의 재활용 방안이 시급한 실정이다.Currently, the paper sludge produced during domestic paper processing is a considerable amount of more than 700,000 tons per year, and most of this sludge is incinerated and landfilled. However, paper sludge incineration is not good in appearance, and if it is further reclaimed, it may contaminate groundwater and it is not easy to secure a landfill.

제지슬러지 소각재는 미연소분이 약간 함유된 무기물로 입도가 미세하고 하기와 같은 화학적 조성을 갖고 있어 건자재, 시멘트 원료 또는 인공경량골재 등에 이용하기 위한 연구들이 시도 되어지고 있다.Paper sludge incineration is an inorganic material containing a little unburned powder and has a fine particle size and has a chemical composition as follows. Therefore, studies have been attempted for use in building materials, cement raw materials or artificial lightweight aggregates.

예를 들면, 대한민국 특허공고 제89-2566호에는 제지슬러지 소각재 중에 포함되어 있는 SiO를 규산 석회질로 유도하여 소석회, 석면, 규산소다 등을 첨가하여 증기 양생시켜 내화성 건축 자재를 제조하는 방법이 개시되어 있으며, 또한 대한민국 특허공고 제91-2580호에도 제지슬러지 소각재에 강산을 가하여 팽윤 처리 후 시멘트, 석고, 석면, 가성소다 등을 첨가하여 양생시켜 내화성 건축자재를 제조하는 방법이 개시되어 있다.For example, Korean Patent Publication No. 89-2566 discloses a method for producing fire-resistant building materials by inducing SiO contained in paper sludge incineration ash to silicate lime, adding cured lime, asbestos, sodium silicate, and the like to steam curing. In addition, the Republic of Korea Patent Publication No. 91-2580 also discloses a method for producing a fire-resistant building material by adding a strong acid to the paper sludge incineration ash and curing by adding cement, gypsum, asbestos, caustic soda after swelling treatment.

그러나 이들 방법들은 양생기간이 2~4주 정도로 너무 길고, 또한 일정 온도와 압력을 가해야 하는 등 양생조건이 까다롭고, 각종 혼합제의 첨가에 따른 원료 가격의 상승과 제조공정이 복잡하여 이들로부터 생산되는 자재의 이용이 경제적이지 못한 문제점이 있다.However, these methods have a long curing period of about 2 to 4 weeks, are difficult to cure conditions such as applying a constant temperature and pressure, and the raw material price is increased due to the addition of various mixtures and the manufacturing process is complicated. There is a problem that the use of the material is not economic.

또한 유사한 폐기물인 플라이애시, 연탄재, 고로슬래그 등을 이용한 재활용에는 많이 있지만 대부분 저부가가치의 벽돌이나 시멘트를 첨가제 등으로 사용되었고, 대한민국 특허공고 제 89-2082호에는 고로슬래그를 이용한 고강도 타일 제조방법에 개시되어 있으나 여러 가지 플럭스와 핵물질인 CrO을 첨가하여 1400℃의 고온에서 용융하여 다시 800℃에서 재열처리 하는 등 제조공정의 복잡성과 비경제성으로 현실성이 부족하다.In addition, there are many recycling materials using fly ash, briquettes, blast furnace slag, which are similar wastes, but most of them are low value-added bricks and cements as additives.In Korean Patent Publication No. 89-2082, a method of manufacturing high strength tiles using blast furnace slag Although it is disclosed, various fluxes and nuclear material CrO are added to melt at a high temperature of 1400 ° C., and then reheated at 800 ° C., thereby causing a lack of practicality due to complexity and economical efficiency of the manufacturing process.

또한 제지슬러지 소각재 자체로 그 비중이 1.91~2.46으로 타무기원료(장석류 : 2.57~2.75, 납석 : 2.65~2.9, 카오린 : 2.61, 점토류 : 2.4~2.6)보다 낮고 평균입도가 5~6㎛로 미소하여 소성시 큰 비표면적으로 높은 표면에너지를 갖기 때문에 소결시 표면에너지를 낮추어 열역학적으로 안정화 되려는 구동력이 커서 소성 수축율이 크며, 내화도가 낮고, 선수축율이 크면서도 흡수율이 클 뿐만 아니라, 가소성이 전혀 없어 성형하기 힘든 소재상의 문제점이 있어 상기와 같은 활용 방안이 있음에도 불구하고 적극적으로 이용되지 못하는 난점이 있다.In addition, the paper sludge incinerator itself is 1.91 ~ 2.46, which is lower than other inorganic raw materials (feldspar: 2.57 ~ 2.75, feldspar: 2.65 ~ 2.9, kaolin: 2.61, clay: 2.4 ~ 2.6) and has an average particle size of 5 ~ 6㎛. Because of the high specific surface area during the sintering and micro sintering, the driving force to lower the surface energy during the sintering to stabilize the thermodynamics is large, resulting in large plastic shrinkage, low fire resistance, large shrinkage rate, high absorption rate, and no plasticity. There is a material problem that is difficult to mold because there is a difficult point that can not be actively used despite the above utilization plan.

본 발명은, 상기와 같은 문제점들을 해결하기 위하여 안출된 것으로서, 상기와 같은 소재상의 특성에 따른 문제점을 해결한 새로운 제지슬러지 소각재의 활용 방안을 제시하려는 데에 그 목적이 있다.The present invention has been made to solve the above problems, and an object of the present invention is to propose a method of using a new paper sludge incineration ash that solves the problems according to the characteristics of the material.

상기의 목적에 따라, 본 출원인은 제지슬러지 소각재의 특성을 보다 면밀하게 조사하고 이를 보다 적극적으로 활용하기 위한 방안들을 연구한 결과 제지슬러지 소각제의 화학조성이 건축물 내외장재 및 바닥재로 널리 사용되어지는 타일의 제조에 사용되어지는 점토, 장석, 도석, 카올린 등과 유사함을 발견하고 이를 일정량 첨가하여 사용할 때 타일의 특성을 향상시키고 더욱 소성 온도를 낮출 수 있다는 효과를 발견하게 되어 본 발명에 이르게 되었다.In accordance with the above purpose, the present inventors have investigated the characteristics of paper sludge incinerator more closely and studied ways to use it more actively. As a result, the chemical composition of paper sludge incinerator is widely used as interior and exterior materials of building and flooring materials. Found similar to the clay, feldspar, pottery stone, kaolin and the like used in the preparation of the present invention to achieve the effect of improving the properties of the tile and lower the firing temperature when used in a certain amount.

다음은 타일의 제조에 사용되어지는 점토, 장석, 도석, 카올린 등의 화학 조성을 나타낸 것이다.The following shows the chemical composition of clay, feldspar, pottery stone, kaolin, etc., which are used to make tiles.

즉, 본 발명은 제지슬러지 소각재 3~10중량%, 도석 30~40중량%, 점토 20중량%, 장석 21~25중량%, 적토 6~10중량%, 카올린 1~5중량%를 혼합 분쇄하고 소정의 압력으로 성형하여 고온에서 소성하는 것으로 행하여지는 제지슬러지 소각재를 첨가한 자기질 타일의 제조방법을 제공한다.That is, the present invention is mixed and pulverized 3-10% by weight of paper sludge incineration, 30-40% by weight, clay 20% by weight, feldspar 21-25% by weight, red soil 6-10% by weight, kaolin 1-5% by weight Provided is a method for producing a magnetic tile containing a paper sludge incineration material, which is formed by molding at a predetermined pressure and firing at a high temperature.

본 발명에서 사용되어지는 제지슬러지 소각재는 미연소분이 2~10% 함유된 무기물로서 입도분포가 분쇄전에는 325메쉬 이하가 50~60중량%이고, 200메쉬 이하는 94~95중량%로 미세한 편이며, 분쇄 후에는 325메쉬 이하가 99.9중량%(평균입도 : 5~6㎛)로 매우 미세하며, 상기한 바와 같이 그 화학적 조성이 기존의 타일 원료로 사용되는 장석류, 점토류 또는 도석류 들과 매우 유사하다.The paper sludge incineration material used in the present invention is an inorganic material containing 2 to 10% of unburned powder, and the particle size distribution is 50 to 60% by weight or less before the pulverization, and 200 or less is 94 to 95% by weight. After grinding, 325 mesh or less is 99.9% by weight (average particle size: 5 ~ 6㎛), very fine, and as described above, its chemical composition is very different from that of feldspar, clay or pottery used as a conventional tile material. similar.

그러나 비표면적이 커서 소결시 소성 수축을 하며 내화도가 낮고 흡수율이 큰 문제점 이외에도 가소성이 전혀 없어 소량이 첨가되더라도 성형하여 소결로를 이동시 성형물이 부서지거나 소성물의 소성 수축이 커지는 문제점이 있다.However, there is a problem in that the plastic surface shrinkage during sintering and the plasticity shrinkage during sintering is low and the degree of fire resistance is low and the absorption rate is large.

본 발명에서는 점토류, 도석류, 카올린, 장석류 등의 기타 부재들과 제지슬러지 소각재의 혼합비를 상기와 같이 적절히 하여 주어 성형물에 가소성을 주거나 내화도를 조정하거나 소성시 조성물 상호간의 결합을 높혀 상기의 문제점을 해결할 수 있다.In the present invention, the mixing ratio of the other members such as clay, pottery, kaolin, feldspar and paper sludge incineration material is appropriately given as described above to give plasticity to the molding, to adjust the degree of fire resistance or to increase the bonding between the compositions during firing. Can be solved.

즉, 점토류는 가소성을 부여하며, 도석류는 소성수축과 내화도를 조정하는 역할을 하며, 장석류는 가열시 용융하여 강한 융체가 되고 냉각시에는 결정화되지 않고 유리 상태로 남아 소성체의 결정립사이의 입계에 들어가 기공을 없애 주고 바인더 역할을 하며, 적토는 특별한 소성특성은 없으나 원가 절감적인 측면이 있고, 카올린은 소성시 핑크색으로 착색되어 타일의 색상을 부여하고 내화도를 조정하는 역할을 하게 된다.That is, clays give plasticity, and pottery plays a role of adjusting plastic shrinkage and fire resistance, and feldspar melts when heated to become a strong melt, and does not crystallize when cooled and remains in a glass state. It enters the grain boundary and eliminates pores and acts as a binder. Red soil has no special plasticity, but it has cost reduction aspect. Kaolin is colored pink during firing to give the color of tiles and adjust the degree of fire resistance.

본 발명에 있어, 상기한 제지슬러지 소각재를 첨가한 자기질 타일의 제조방법에 있어, 각 부재들을 혼합 분쇄한 후, 성형 방법은 통상의 타일 제조공정에서 행하여지는 200~300㎏/㎤의 압력으로 압축 가압 성형한다.In the present invention, in the manufacturing method of the magnetic tiles to which the above-described paper sludge incineration material is added, after mixing and pulverizing each member, the molding method is compressed to a pressure of 200 to 300 kg / cm 3 which is performed in a conventional tile manufacturing process. Press molding.

또한 소결 온도는 1140~1170℃로 행하여진다.Moreover, sintering temperature is performed at 1140-1170 degreeC.

이는 종래 벽 또는 바닥 타일의 제조 공정에서의 소결 온도 보다 5~40℃ 정도 낮은 값이다.This value is about 5 to 40 ° C. lower than the sintering temperature in the manufacturing process of conventional wall or floor tiles.

이와 같이 제지슬러지 소각재를 첨가하여 벽 또는 바닥 타일을 제조할 때 소성온도를 종래의 공정보다 5~40℃ 낮출 수 있는 것은 에너지 절감과 원가절감의 측면에서 매우 의미 있는 발견이 아닐 수 없다.As such, when the paper sludge incineration material is added to produce the wall or floor tiles, the firing temperature can be lowered by 5 to 40 ° C. than the conventional process, which is a significant finding in terms of energy saving and cost reduction.

본 발명의 방법에 의하여 제조되어지는 타일은 밀도가 2.05~2.45, 선수축율이 6~12%, 흡수율이 적정선수출할 때 0%까지 나오고, 꺽일 강도가13㎏f/㎝ 이상으로써, 종래의 도석, 점토, 장석, 카올린 만으로 제조되어진 타일에 비하여 최소한 비등하거나 우수한 특성을 갖는다.Tiles produced by the method of the present invention has a density of 2.05-2.45, 6-12% bower shrinkage, up to 0% when the absorption rate is appropriately drawn, and the breaking strength is 13 kgf / cm or more. It has at least boiling or superior properties compared to tiles made only of clay, feldspar and kaolin.

본 발명의 제지 슬러지 소각재를 첨가한 자기질 타일의 제조방법을 각 공정별로 더욱 상세하게 하면 다음과 같다.The manufacturing method of the magnetic tile to which the paper sludge incineration ash of the present invention is added is described in more detail for each process as follows.

[제 조 공 정][Manufacture process]

1. 원료칭량1. Raw material weighing

제지슬러지 소각재를 3~10중량% 첨가하고, 가소성을 부여하기 위해 점토류를 20중량%, 가열시 용융하여 강한 융체가 되고 냉각시에는 결정화하지 않고 유리상태로 남고 결정립과 결정립 사이의 입계에 들어가 기공을 없애주고 바인더 역할을 하는 장석류를 21~25중량%, 소성수축과 내화도의 조정 및 원료혼합시 소각재와의 친화성을 주기 위해 도석류를 30~40중량%, 원가 절감 측면에서 적토를 6~10중량%, 내화성 조절과 색상 부여를 위해 카올린을 1~5중량% 첨가하여 칭량한다.3 to 10% by weight of paper sludge incineration is added, and to give plasticity, 20% by weight of clay is melted upon heating, which becomes a strong melt, and remains in a glass state without crystallization upon cooling and enters the grain boundary between grains and grains. 21-25% by weight of feldspar acts as a binder and 30 ~ 40% by weight of pottery to reduce the plastic shrinkage and fire resistance and affinity with incineration materials when mixing raw materials. ~ 10% by weight, 1 to 5% by weight of kaolin for the control of fire resistance and color impartment is added.

2. 분 쇄2. grinding

상기 1에서 칭량한 원료에 원료무게의 50%의 물을 첨가하여 볼밀기를 이용해 원료를 분쇄·혼합한다. 분쇄시간은 30분이면 충분하나 그 시간을 늘려 1~3 시간동안 분쇄할 경우 입도가 더욱 미세하게 되어 성형·소결시 입자간의 접촉점을 많게 함으로써 소성수축과 흡수율을 동시에 줄일 수 있다. 기존의 타일소지의 경우 그 평균 입도가 13~15㎛인데 비해 개발된 소지의 평균입도는 소각재의 첨가량이 3%일 때 12.6~14.1㎛, 6%일 때 9.9~10.6㎛, 10%일 때는 8.6~9.1㎛로 훨씬 미세하여 소성속도를 빠르게 해주고 소성온도를 낮추는데 도움을 준다.50% of the weight of the raw material is added to the raw material weighed in 1, and the raw materials are pulverized and mixed using a ball mill. The grinding time is sufficient for 30 minutes, but if the grinding time is increased for 1 to 3 hours, the particle size becomes finer and the plastic shrinkage and the water absorption can be simultaneously reduced by increasing the contact point between the particles during molding and sintering. The average particle size of conventional tile material is 13 ~ 15㎛, whereas the developed particle size is 12.6 ~ 14.1㎛ when the added amount of ash is 3%, 9.9 ~ 10.6㎛ when 6% and 8.6% when it is 10%. It is much finer at ~ 9.1㎛, which helps to speed up the firing rate and lower the firing temperature.

3. 건 조3. Dry

혼합, 분쇄된 원료를 105℃의 건조에서 수분함량 5중량%가 될 때까지 건조시킨다.The mixed and ground raw materials are dried until the water content is 5% by weight at 105 ° C drying.

4. 성 형4. Molding

건조된 원료는 200~300㎏/㎤의 성형압력으로 성형한다. 성형은 일축가압식 프레스기를 사용하며, 가압할 때 내부의 공기를 충분히 빼내어 균일하고 높은 충진밀도를 갖도록 하며 소성수축과 흡수율을 동시에 줄일 수 있다.The dried raw material is molded at a molding pressure of 200 to 300 kg / cm 3. Molding uses a single-screw press machine, and when pressurized, the internal air is sufficiently taken out to have a uniform and high packing density, and plastic shrinkage and absorption rate can be simultaneously reduced.

5. 소 결5. Sintering

승온속도 35~40℃/분, 1140~1170℃에서 3~6분간 유지, 자연 냉각시키는 방식으로 소성하며, 최적온도는 벽타일의 경우 소각재가 3% 함유되었을 때 1155~1165℃, 6%일 때 1150~1160℃, 그리고 10%일 때 1140℃ 이하로 한다. 이 소성온도는 기존의 타일 소성온도 보다 5~40℃ 낮출 수 있다.Heating rate is maintained at 35 ~ 40 ℃ / min, 1140 ~ 1170 ℃ for 3 ~ 6 minutes and fired by natural cooling.The optimum temperature is 1155 ~ 1165 ℃, 6% days when incineration ash is contained 3% in wall tile. When 1150 ~ 1160 ℃, and when 10% to 1140 ℃ or less. This firing temperature can be 5 ~ 40 ℃ lower than the conventional tile firing temperature.

실시예Example

다음에 본 발명의 바람직한 실시예를 통하여 본 발명은 더욱 상세하게 설명하고자 한다. 그러나 다음의 실시예들은 본 발명을 더욱 쉽게 이해하기 위하여 제공되는 것이지 본 발명이 이들 실시예에 한정되는 것은 아니다.Next, the present invention will be described in more detail with reference to preferred embodiments of the present invention. However, the following examples are provided to more easily understand the present invention, but the present invention is not limited to these examples.

실시예 1Example 1

제지슬러지 소각재 3중량%와 점토 20중량%, 도석 37~40중량%, 장석 22~25중량%, 카오린 2~5중량%, 적토 7~10중량%를 혼합하고 볼밀기로 분쇄하여 50메쉬채에 통과시켜 평균입도를 12.61~14.13㎛로 조정하였다.3% by weight of paper sludge incineration, 20% by weight of clay, 37-40% by weight of pottery stone, 22-25% by weight of feldspar, 2-5% by weight of kaolin, and 7-10% by weight of red soil, and crushed by ball mill 50 mesh The particles were passed through to adjust the average particle size to 12.61 to 14.13 µm.

다음에 이 시료를 105℃ 건조기에서 수분함량 5중량%까지 건조시킨 후 200~300㎏/㎤의 압력으로 성형하고 승온속도 35~40℃/분으로 올려 1140~1170℃에서 3~6분간 유지한 후 자연 냉각하여 자기질 타일을 제조하였다.Next, the sample was dried to a moisture content of 5% by weight in a 105 ° C. dryer, and then molded at a pressure of 200 to 300 kg / cm 3, and the temperature was raised to 35 to 40 ° C./min and maintained at 1140 to 1170 ° C. for 3 to 6 minutes. After the natural cooling to prepare a magnetic tile.

실시예 2Example 2

상기 실시예 1에서 기재한 조합에서 소각재를 3중량%에서 6중량%로 늘리고 도석류를 3% 줄여 34~37중량%로 하고 평균입도를 9.96~10.58㎛로 한 것을 제외하고는 실질적으로 실시예 1과 동일하게 처리하였다.Except that the incineration ash in the combination described in Example 1 was increased from 3% by weight to 6% by weight, and the pottery was reduced by 3% to 34 to 37% by weight, and the average particle size was 9.96 to 10.58 µm. Same treatment as 1

실시예 3Example 3

상기 실시예 1에서 기재한 조합에서 소각재를 7% 늘려 10중량%로 늘리고 도석을 6~7중량% 줄여 30~34중량%로 하고 평균입도를 8.62~9.11㎛로 한 것을 제외하고는 실질적으로 실시예 1과 동일하게 처리하였다.In the combination described in Example 1, the incinerator was increased by 7% to 10% by weight, and the coating was reduced by 6 to 7% by weight to 30 to 34% by weight, except that the average particle size was set to 8.62 to 9.11 μm. The same treatment as in Example 1 was carried out.

비교예 1Comparative Example 1

기존 자기질 타일의 일반적 조성인 납석 25중량%, 도석 40중량%, 점토 20중량%, 적토 10중량%, 카오린 5중량%를 혼합하여 볼밀기로 분쇄(분쇄 후에는 평균입도가 13.57~14.64㎛로 실시예 1~3보다 약간 큼)하였다. 이 시료를 105℃ 건조기에서 수분함량 5중량%까지 건조시킨 후 200~300㎏/㎤의 압력으로 성형하고 승온속도 35~40℃/분으로 올려 1140~1170℃에서 3~6분간 유지한 후 자연 냉각하여 기존의 내장 벽타일을 제조하였다.25% by weight of feldspar, 40% by weight of pottery stone, 20% by weight of clay, 10% by weight of red soil, and 5% by weight of kaolin are ground and milled with a ball mill (average particle size after grinding is 13.57 to 14.64㎛). Slightly larger than Examples 1 to 3). After drying the sample to 5% by weight of moisture in a 105 ℃ dryer, it was molded at a pressure of 200 ~ 300㎏ / ㎠ and raised at a heating rate of 35 ~ 40 ℃ / min and maintained at 1140 ~ 1170 ℃ for 3-6 minutes. Cooling to prepare the existing interior wall tiles.

이상과 같은 실시예 1~3 및 비교예 1에서 제조되어진 타일의 물성을 아래 (표3)와 같았다.The physical properties of the tiles prepared in Examples 1 to 3 and Comparative Example 1 were as shown in Table 3 below.

이상과 같은 방법으로 제조한 제지슬러지 소각재를 3~10중량% 함유한 타일은 다음면에서 장점과 의의를 찾을 수 있다.Tiles containing 3 to 10% by weight of paper sludge incineration ash prepared by the above method can be found in the following advantages and significance.

첫째, 제지슬러지 소각재를 재활용하여 매립물제를 해결할 수 있고 그와 동시에 기존원료를 대체함으로써 타일제조원가를 절감할 수 있으며, 둘째, 제지슬러지 소각재의 저내화도 특성으로 소성온도를 5~40℃ 낮출 수 있어 연료절감 효과를 볼 수 있으며, 셋째, 제지슬러지 소각재의 양호한 소결성으로 꺾일 강도가 KS 기준보다 8~29.5% 증가하여, 흡수율은 0%까지 낮출 수 있고, 넷째, 기존의 타일 보다 외관이 더 매끄럽고 색상이 깨끗하며, 마지막으로, 제지슬러지 소각재의 타일로의 재활용 기술을 기반으로 다른 전자재로의 재활용이 가능하게 되고 또한 모든 무기성 일반폐기물의 재활용으로 확대하여 궁극적으로 환경문제를 해결하는데 일익을 담당할 수 있다.First, it can solve the landfill material by recycling the paper sludge incineration material, and at the same time, it can reduce the tile manufacturing cost by replacing the existing raw materials. Second, the firing temperature of the paper sludge incineration material can be lowered by 5 ~ 40 ℃. Fuel saving effect can be seen. Third, the strength to be sintered by good sinterability of paper sludge incinerator increases by 8 ~ 29.5% compared to KS standard, so that the absorption rate can be lowered to 0%. Fourth, the appearance is smoother and more color than conventional tiles. Finally, based on the recycling technology of the paper sludge incineration ash to the tile, it is possible to recycle to other electronic materials, and also expand to the recycling of all inorganic general wastes and ultimately play a role in solving environmental problems. can do.

Claims (1)

타일 소지의 평균입도가 8.6~12.6㎛이며, 미연소분이 2~10% 함유된 제지슬러지 소각재 3~10중량%, 도석 30~40중량%, 장석 21~25중량%, 점토 20중량%, 적토 6~10중량%, 카오린 1~5중량%를 혼합하여 분쇄하고 200~300㎏/㎤의 압력으로 성형하여 1140~1170℃의 고온에서 소성함을 특징으로 하는 제지슬러지 소각재를 첨가한 자기질 타일의 제조방법.The average particle size of tile is 8.6 ~ 12.6㎛, 3 ~ 10% of paper sludge incineration ash containing 2 ~ 10% of unburned, 30 ~ 40% of pottery, 21 ~ 25% of feldspar, 20% of clay, red clay 6 to 10% by weight, kaolin 1 to 5% by weight of a mixture of crushed and molded at a pressure of 200 ~ 300 ㎏ / ㎠ to bake at a high temperature of 1140 ~ 1170 ℃ characterized in that the magnetic tiles with the addition of paper sludge incineration Manufacturing method.
KR1019930031258A 1993-12-30 1993-12-30 Process for the preparation of magnetic tail using paper sludge ashes KR960011327B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR1019930031258A KR960011327B1 (en) 1993-12-30 1993-12-30 Process for the preparation of magnetic tail using paper sludge ashes

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1019930031258A KR960011327B1 (en) 1993-12-30 1993-12-30 Process for the preparation of magnetic tail using paper sludge ashes

Publications (2)

Publication Number Publication Date
KR950017811A KR950017811A (en) 1995-07-20
KR960011327B1 true KR960011327B1 (en) 1996-08-22

Family

ID=19374259

Family Applications (1)

Application Number Title Priority Date Filing Date
KR1019930031258A KR960011327B1 (en) 1993-12-30 1993-12-30 Process for the preparation of magnetic tail using paper sludge ashes

Country Status (1)

Country Link
KR (1) KR960011327B1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100403817B1 (en) * 1999-12-23 2003-11-01 이성심 Manufacturing method of tiles using incineration ash (floor ash)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100588488B1 (en) * 2004-11-05 2006-06-09 박종원 Pulpsludge ash composite for producing construction materials
KR102355172B1 (en) 2021-01-25 2022-02-09 유하비 Method for Manufacturing Paper Powder, Paper Powder Manufactured by the same and Dried Materials Comprising the Same

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100403817B1 (en) * 1999-12-23 2003-11-01 이성심 Manufacturing method of tiles using incineration ash (floor ash)

Also Published As

Publication number Publication date
KR950017811A (en) 1995-07-20

Similar Documents

Publication Publication Date Title
JPH10152356A (en) Artificial lightweight aggregate and its production
KR19990031198A (en) Manufacturing method of artificial lightweight aggregate
KR960011327B1 (en) Process for the preparation of magnetic tail using paper sludge ashes
KR20110125913A (en) Bricks for interior containing stone sludge and methods for preparing thereof
KR0153376B1 (en) Process for the preparation of a brick
JPH09100151A (en) Feedstock composition for producing ceramic product and ceramic product made therefrom
KR101451501B1 (en) Composition of artificial aggregate and making method using inorganic sludge particle
KR20000072111A (en) Composition for lightweight aggregate and method for manufacturing the same
CN113213890B (en) Architectural ceramic tile prepared by using fine iron tailing powder and preparation method thereof
KR960011326B1 (en) Process for the preparation of magnetic tail-board using paper sludge ashes
KR100237349B1 (en) The process of manufacturing ceramics using wastes
KR20020082321A (en) Concrete 2th production using waste lime
JP2001253740A (en) Artificial aggregate and its production process
KR20020044899A (en) Composition for lightweight aggregate and method for manufacturing the same
JPH06227853A (en) Body composition for ceramic
CZ134494A3 (en) Method of improving fly ash from brown coal
KR100392933B1 (en) Composition for lightweight aggregate
KR100241564B1 (en) Artificial light weight aggregate and method for making the same using sludge ash and/or sludge
JP2603599B2 (en) Artificial lightweight aggregate and manufacturing method thereof
JP3552173B2 (en) Manufacturing method of lightweight aggregate using sewage sludge incineration ash
JPH0794342B2 (en) Method for manufacturing dry-molded roof tile
JP3055899B1 (en) Artificial aggregate and method for producing the same
KR100432775B1 (en) Compositions and manufacturing of low temperature calcined brick
JPH1095658A (en) Production of ceramic material and ceramic tiles by effectively recycling garbage incineration molten-ash slag
JPH08108162A (en) Granular material produced from waste and waste treatment method

Legal Events

Date Code Title Description
A201 Request for examination
E902 Notification of reason for refusal
G160 Decision to publish patent application
E701 Decision to grant or registration of patent right
GRNT Written decision to grant
FPAY Annual fee payment

Payment date: 20090803

Year of fee payment: 14

LAPS Lapse due to unpaid annual fee