KR100414149B1 - Manufacturing method of Photocatalytic action clay brick - Google Patents

Manufacturing method of Photocatalytic action clay brick Download PDF

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KR100414149B1
KR100414149B1 KR10-2001-0001923A KR20010001923A KR100414149B1 KR 100414149 B1 KR100414149 B1 KR 100414149B1 KR 20010001923 A KR20010001923 A KR 20010001923A KR 100414149 B1 KR100414149 B1 KR 100414149B1
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tio
titanium dioxide
photocatalytic
clay
bricks
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KR20020061075A (en
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한삼화
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주식회사 삼한 씨원
김화중
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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
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/131Inorganic additives
    • EFIXED CONSTRUCTIONS
    • E04BUILDING
    • E04CSTRUCTURAL ELEMENTS; BUILDING MATERIALS
    • E04C1/00Building elements of block or other shape for the construction of parts of buildings
    • E04C1/40Building elements of block or other shape for the construction of parts of buildings built-up from parts of different materials, e.g. composed of layers of different materials or stones with filling material or with insulating inserts
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00474Uses not provided for elsewhere in C04B2111/00
    • C04B2111/0081Uses not provided for elsewhere in C04B2111/00 as catalysts or catalyst carriers
    • C04B2111/00827Photocatalysts
    • 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
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/04Clay; Kaolin
    • 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
    • C04B33/00Clay-wares
    • C04B33/30Drying methods
    • 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
    • C04B33/00Clay-wares
    • C04B33/32Burning methods

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Structural Engineering (AREA)
  • Architecture (AREA)
  • Inorganic Chemistry (AREA)
  • Dispersion Chemistry (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Civil Engineering (AREA)
  • Catalysts (AREA)

Abstract

본 발명은 신소재인 초미립의 이산화티타늄(TiO2)의 특성인 태양빛에 노출되면 주변의 유해물질을 분해하는 성질을 이용하여 질소산화물(N0x)를 정화시키고 살균,향균, 탈취의 효능과 오염물질을 분해시키고 자외선을 차단하는 효과가 있는 광촉매 물질인 이산화티타늄(TiO2)을 점토제품의 주원료에 혼합하여 환경친화적인 건축용 벽돌 및 바닥벽돌로 만든 점토벽돌의 제조방법에 관한 것이다.The present invention purifies nitrogen oxides (N0x) by decomposing harmful substances around when exposed to sunlight, which is a characteristic of ultrafine titanium dioxide (TiO 2 ), a new material, and sterilization, antibacterial, deodorization efficacy and pollution The present invention relates to a method of manufacturing clay bricks made of environmentally friendly building bricks and floor bricks by mixing titanium dioxide (TiO 2 ), a photocatalytic material having an effect of decomposing substances and blocking ultraviolet rays, from main materials of clay products.

즉, 점토제품의 주원료 90∼98%에 광촉매물질인 이산화티타늄(TiO2)이 2∼10% 중량비로 함유되어 있는 것을 특징으로 하는 광촉매작용을 하는 점토벽돌과 점토제품의 주원료 90∼98%에 광촉매물질인 이산화티타늄(TiO2)의 파우더 (Pouder)를 2∼10%중랑비로 첨가혼합한후 진공사출기로 성형하여 50∼100℃의 온도에 50∼60시간 건조시킨후 1100∼1160℃의 온도에 30∼40시간 예열 및 소성냉각시켜서 된 광촉매작용을 하는 점토벽돌의 제조방법이다.In other words, 90-98% of the main raw material of clay products contains 2-10% by weight of titanium dioxide (TiO 2 ), a photocatalyst, and 90-98% of the main raw materials of clay brick The powder of powder of titanium dioxide (TiO 2 ), a photocatalytic material, was added and mixed in a 2-10% neutral ratio, and then molded in a vacuum injection molding machine, dried at a temperature of 50 to 100 ° C. for 50 to 60 hours, and then at a temperature of 1100 to 1160 ° C. This is a method for producing a clay brick which has a photocatalytic effect obtained by preheating and plastic cooling for 30 to 40 hours.

Description

광촉매작용을 하는 점토벽돌의 제조방법{Manufacturing method of Photocatalytic action clay brick}Manufacturing method of photocatalytic action clay brick

본 발명은 신소재인 초미립의 이산화티타늄(TiO2)의 특성인 태양빛에 노출되면 주변의 유해물질을 분해하는 성질을 이용하여 질소산화물(N0x)를 정화시키고 살균,향균, 탈취의 효능과 오염물질을 분해시키고 자외선을 차단하는 효과가 있는 광촉매 물질인 이산화티타늄(TiO2)을 점토제품의 주원료에 혼합하여 환경친화적인 건축용 벽돌 및 바닥벽돌로 만든 점토벽돌의 제조방법에 관한 것이다.The present invention purifies nitrogen oxides (N0x) by decomposing harmful substances around when exposed to sunlight, which is a characteristic of ultrafine titanium dioxide (TiO 2 ), a new material, and sterilization, antibacterial, deodorization efficacy and pollution The present invention relates to a method of manufacturing clay bricks made of environmentally friendly building bricks and floor bricks by mixing titanium dioxide (TiO 2 ), a photocatalytic material having an effect of decomposing substances and blocking ultraviolet rays, from main materials of clay products.

일반적으로 많은 자동차에서 발생되는 배출가스의 주요인인 질소 산화물(NOx)은 대기중에 존재하는 탄화수소 등과 반응하여 광화학스모그 (Photochemical Smog)을 유발하거나 산성비의 원인이 되는 유해 대기오염물질로서 대도시 및 산업공단등의 주요 대기오염의 주원인을 차지하고 있는 실정이다.In general, nitrogen oxides (NOx), a major source of emissions from many automobiles, react with hydrocarbons in the atmosphere to cause photochemical smog or cause acid rain. Is the main cause of major air pollution.

특히 질소산화물(NOx)중 NO2가 위험한 성분으로서 대기중에 50ppm정도 존재하면 생명체의 죽음을 초래하고 0.05ppm 와 0.02ppm 사이의 낮은 농도에서도 호흡기 장애를 일으키는 것으로 알려져 있으며 대기중의 낮은 농도에서도 수분 및 탄화수소와 더불어 광화학(Photocatalytic)반응으로 대도시의 가장 심각한 문제인 스모그(Smog)현상을 일으키는 것으로 더 잘 알려져 있다.In particular, NO 2 in nitrogen oxides (NOx) is a dangerous component and it is known to cause death of life and respiratory failure even at low concentrations between 0.05 ppm and 0.02 ppm. Photocatalytic reactions, along with hydrocarbons, are better known to cause smog, the most serious problem in large cities.

또한 고온의 배기가스중에서 대부분 NOx가 NO로 존재하는데, 그 이유는 NO가 고온에서 비교적 안정된 상태에 있기 때문이고, 상온에서는 쉽게 No2로 산화되어 공해의 직접적인 원인이 된다.In addition, most of the NOx is present as NO in the high-temperature exhaust gas because the NO is in a relatively stable state at a high temperature, and easily oxidizes to No 2 at room temperature, which is a direct cause of pollution.

이러한 질소산화물(NOx)에 의한 대기오염을 정화할수 있는 방법으로 광촉매(Photocatalytic)작용을 이용한 질소 산화물(NOx)의 고정화 또는 무력화를 들수 있으며 광촉매(Photocatalytic)가 태양에너지와 반응하여 질소산화물(NOx) 및 유기염소 화합물에 의한 대기의 오염물질을 산화하여 제거하는 원리를 이용하여 점토벽돌 및 바닥벽돌 제조시에 광촉매(Photocatalytic)물질을 투입하여 상기와 같은 질소산화물(N0x)을 정화시키는 제품을 생산하여 환경오염으로 인한 공해를 조금이라도 줄이고저 하는데 목적이 있다.The method of purifying air pollution by NOx may be immobilization or neutralization of NOx using photocatalytic action, and photocatalytic reacts with solar energy to NOX. And by using the principle of oxidizing and removing the air pollutants by the organic chlorine compounds in the production of clay and floor bricks by adding a photocatalytic material to produce a product that purifies the nitrogen oxides (N0x) as described above It aims to reduce any pollution caused by environmental pollution.

따라서 본 발명자는 광촉매(Photocatalytic)물질을 점토제품의 소지에 일정량 투입하여 건축용벽돌 및 바닥벽돌도 광촉매(Photocatalytic)반응에 의한 유해가스정화기능을 할수 있도록 수 많은 시험과 연구를 거듭하였다.Accordingly, the present inventors have repeatedly conducted a number of tests and studies to add a certain amount of photocatalytic material to the possession of clay products so that building bricks and floor bricks can also function as a harmful gas purifying by the photocatalytic reaction.

그 결과 건축용벽돌 및 바닥벽돌용으로 사용하고자 하는 벽돌원료인 점토 및 규사(보명토)또는 고령토에 광촉매(Photocatalytic)물질인 이산화티타늄(Tio2, Anatase)을 사용하면 소성시에 벽돌원료인 점토 및 규사(보명토)또는 고령토 성분중 Fe2o2, Al2o3, Cao, Mgo 등의 원소와 결합하여 자연스러운 유색발생과 태양에너지(열)가 닿으면 반응이 촉진되어 광촉매(Photocatalytic)작용을 한다는 사실을 발견하게 되었다.As a result, if the photocatalytic material of titanium dioxide (Tio 2 , Anatase) is used in clay and silica sand (Visible soil) or kaolin, which are intended to be used for building bricks and floor bricks, clay and The combination of elements such as Fe 2 o 2 , Al2o3, Cao, and Mgo in silica sand or kaolin component, promotes the reaction when natural color generation and solar energy (heat) are in contact, thus acting as photocatalytic. Found out.

또한 광촉매 종류는 TiO2, ZNO, Nd2O5, WO3, SnO2, ZrO2, Ru2+, CdS, ZnS등이 있으며 이러한 광촉매(Photocatalytic)들은 태양광중 자외선을 받았을 때 전자의 이동이 일어나며 발생된 전자와 전공은 주변의 산소나 수소 혹은 OH등과 여러 가지 반응을 하게 되며 생성된 물질들은 강한 산화력을 가지고 있어 실내의 유해가스를 분해하는 정화능력을 갖고 있으며 이들중 이산화티타늄은(TiO2, Anstase)은 대기와 물에 들어 있는 유기오염물질을 인체에 무해한 물질로 산화분해 시켜주며, 산.염기 유기용매에 침식되지 않는 화학적인 안정성을 가지는 동시에 다른 광촉매 (Photocatalytic)와는 달리 중독성이 없고 발암성물질도 포함되어 있지 않다는 사실을 알게 되었다.In addition, photocatalysts include TiO 2 , ZNO, Nd 2 O 5 , WO 3, SnO 2 , ZrO 2 , Ru 2+ , CdS, and ZnS. These photocatalytics are caused by the movement of electrons when subjected to ultraviolet rays in sunlight. The electrons and majors react with the surrounding oxygen, hydrogen, or OH, and the produced materials have strong oxidizing power and have the ability to decompose harmful gases in the room. Among them, titanium dioxide (TiO 2 , Anstase) ) Oxidizes and decomposes organic pollutants in the air and water into harmless substances.It has chemical stability that does not corrode in acid and base organic solvents.It is not addictive and carcinogenic unlike other photocatalytics. It is also found that it is not included.

따라서 본 발명은 건축용벽돌 및 바닥벽돌에 광촉매(Photocatalytic)재를 첨가하여 벽돌원료에 포함되어 있는 산화철(Fe2O3)과 광촉매(Photocatalytic)재의 원소결합 변화로 인한 벽돌고유의 색상이 아닌 다른 유색발색과 공해가스 및 유기물 분해등 환경친화적인 건축용 벽돌 및 바닥벽돌을 제공하여 환경개선효과 및 건축물을 구성하는 재료자체에 환경오염을 정화할수 있는 기능을 부여하고자 하는데 있다.Therefore, the present invention adds a photocatalytic material to building bricks and floor bricks, and the color is different from brick's unique color due to the change of elemental bond between iron oxide (Fe 2 O 3 ) and photocatalytic material included in the brick material. By providing environmentally friendly building bricks and floor bricks such as color development and decomposition of pollution gas and organic matter, it is intended to give environmental improvement effect and the function to purify environmental pollution to the material itself.

본 발명은 점토제품의 주원료에 광촉매(Photcatalytic)물질인 이산화티타늄 (TiO2,Anatase)을 제품제조공정에 소량첨가하여 혼합한 다음 성형, 건조, 소성하여 유색발색 및 질소산화물인(NOx)를 정화시키는 효능이 있는 건축용 벽돌과 바닥벽돌제로 만든 점토벽돌 및 그 제조방법이다.In the present invention, a small amount of titanium dioxide (TiO 2 , Anatase), a photocatalytic material, is added to a product manufacturing process and mixed, followed by molding, drying, and firing to purify colored and nitrogen oxides (NOx). Clay bricks made of building bricks and floor bricks having the effect of making, and a method of manufacturing the same.

본 발명에서 사용하고자 하는 광촉매(Photocatalytic)제는 주제품인 건축용 벽돌 및 바닥벽돌의 특성상 많은 광촉매(Photocatalytic)제가 있지만 광분해효과가 가장 높고, 비중이 높아 사용이 용이한 이산화티타늄(TiO2)을 선택하였다.The photocatalyst (Photocatalytic) to be used in the present invention has selected the nature of many photocatalyst (Photocatalytic) I but photolysis effect is highest, and titanium dioxide, the higher the specific gravity is easy to use (TiO 2) of the main products, building blocks and the bottom bricks .

* 이산화티타늄(TiO2,Anatase)의 광분해 반응* Photodecomposition of Titanium Dioxide (TiO 2 , Anatase)

* 광촉매(Photocatalytic)제인 이산화티타늄(TiO2)의 제조방법* Manufacturing method of titanium dioxide (TiO 2 ), a photocatalytic agent

본 발명에서는 주재료인 광촉매(Photocatalytic)이산화티타늄제인(TiO2)의 배합비율등을 달리하는 건축용벽돌 및 바닥벽돌 제조공정에 대하여 구체적으로 설명하지만 본 발명품의 기술적 범위가 제조공정상의 실시예에 제한되는 것은 아니다.Although the present invention will be described in detail with respect to the manufacturing process of building bricks and floor bricks varying the mixing ratio of photocatalytic titanium dioxide (TiO 2 ) as the main material, the technical scope of the present invention is limited to the embodiment of the manufacturing process It is not.

또한 본 발명에서는 사용된 광촉매(Photocatalytic)제인 이산화티타늄(TiO2)의 품위는 아래와 같다.In addition, in the present invention, the quality of titanium dioxide (TiO 2 ) which is a photocatalytic agent used is as follows.

* 이산화티타늄(TiO2)의 단위 입자도(정방정형)* Unit particle diagram of titanium dioxide (TiO 2 )

<실시예><Example>

건축용벽돌 및 바닥벽돌제조용으로 배합, 분쇄된, 점토제품의 주원료 90∼ 98%에 광촉매(Photocatalytic)제인 이산화티타늄(TiO2)의 파우더(Pouder)를 2 ∼10% 제품중량비로 첨가혼합한후 수분함량 19±2%로 하여 진공사출기로 성형하여 성형된물체를 50∼100℃에서 50∼60시간 건조시킨후 800∼1160℃에서 30∼45시간 예열 및 소성, 냉각시켜 유색과 공해가스 및 유기물 분해등의 광촉매효과 (Photocatalytic, effect)가 있는 건축용 벽돌 및 바닥벽돌을 생산한다.After mixing and crushing 90 ~ 98% of the main raw materials of clay products, which are blended and ground for building bricks and floor bricks, powder of titanium dioxide (TiO 2 ), a photocatalytic agent, is added and mixed at a weight ratio of 2-10%. It is made with a vacuum injection molding machine with a content of 19 ± 2%, and the molded object is dried for 50 to 60 hours at 50 to 100 ° C, then preheated, calcined and cooled at 800 to 1160 ° C for decomposition of colored and polluting gases and organic matter. Produce building bricks and floor bricks with photocatalytic effect.

<비교예>Comparative Example

건축용벽돌 및 바닥벽돌 제조용으로 배합, 분쇄된 원료에 광촉매(Photocatalytic)제를 첨가하지 않고 수분19±2%로 하여 진공사출기로 성형하여 성형된 물체를 50∼100 ℃에서 50∼60시간 건조시킨후 800∼1160℃에서 30∼45시간 예열 및 소성, 냉각시켜 적색의 벽돌 및 바닥벽돌을 생산한다.After drying the molded object at 50 ~ 100 ℃ for 50 ~ 60 hours by molding with vacuum injection machine with 19 ± 2% of moisture without adding photocatalytic agent to the mixed and crushed raw materials for building brick and floor brick It is preheated, fired and cooled at 800 to 1160 ° C for 30 to 45 hours to produce red bricks and floor bricks.

- 시험방법 -- Test Methods -

질소산화물(NOx)농도감소 실험방법Experimental method for reducing NOx concentration

본 발명을 위해 질소산화물(NOx)의 농도감소 시험기구가 전무한 상태이므로 밀폐식 질소산화물(NOx)처리장치를 고안 제작하여 질소산화물(NOx)의 농도감소를 측정하였다.For the present invention, since there is no test for reducing the concentration of nitrogen oxides (NOx), a closed nitrogen oxide (NOx) treatment device was devised and manufactured to measure the concentration reduction of nitrogen oxides (NOx).

실험장치는 밀폐형 스테인레스 용기(상자형)내부에 광(光)효과를 위해 UV램프를 설치하였고 가스의 유입량을 조절하기 위해 유압계와 밸브장치를 구성하였으며 밀폐식 질소산화물(NOx)처리장치의 장치로는 아래와 같다.The experimental device installed UV lamp for light effect inside the sealed stainless steel container (box type), configured the hydraulic system and the valve device to control the flow of gas, and the device of the closed NOx treatment device. Is as follows.

* 밀폐식 질소산화물(NOx)처리장치* Sealed NOx Treatment System

상기 시험결과는 다음표에 나타낸다.The test results are shown in the following table.

* 질소 산화물(NOx)가스의 농도 백분율(%)* Percentage of nitrogen oxide (NOx) gas (%)

상기 표에서 실시예와 비교예의 차이점으로 볼때 질소산화물(NOx)의 농도가 실시예에서는 광촉매(Photocatalytic)제의 배합함량(%)에 따른 질소산화물(NOx)의 농도가 감소됨을 알수 있고 비교예에서는 광촉매(Photocatalytic)제가 배합안된 관계로 인하여 질소한화물(NOx)의 농도가 감소가 없음을 알수 있으며 광촉매(Photocatalytic)제의 배합(%)별 질소산화물(NOX)농도감소는 다음과 같다.In the above table, it can be seen that the concentration of nitrogen oxides (NOx) according to the difference between the example and the comparative example is reduced in the concentration of nitrogen oxides (NOx) according to the blending content (%) of the photocatalytic agent in the examples. It can be seen that there is no decrease in the concentration of nitrogen oxides (NOx) due to the uncatalyzed photocatalytic agent and the NOx concentration decrease by the% of the photocatalytic agent is as follows.

* 초기 질소산화물(NOx)농도에 대한 잔 백분율(%)*% Of residual to initial NOx concentration

- 시험방법 2 --Test Method 2-

흡수율 및 압축강도, 휨강도Absorption rate, compressive strength, flexural strength

한국 산업규격인 KSL 4201의 방법에 따라 실시예의 건축용벽돌 및 바닥벽돌의 흡수율와 압축강도 시험과 한국산업규격 KSF 4419의 방법에 따라 실시예의 바닥별돌의 휨강도를 시험하였다.The absorbance and compressive strength tests of the building bricks and the floor bricks of the examples were tested according to the Korean Industrial Standard KSL 4201, and the flexural strength of the floor stones of the examples were tested according to the Korean Industrial Standard KSF 4419.

상기 시험결과는 다음표에 나타난다.The test results are shown in the following table.

상기 표에서 실시예와 비교예의 차이점을 볼때 흡수율과 압축강도는 비교예의 벽돌 및 바닥벽돌과 벽차이는 없지만 휨강도는 30%이상 증가되는광촉매(Photocatalytic)작용을 하는 건축용 벽돌 및 바닥벽돌의 제품시험 결과를 알수 있다.As a result of the difference between the examples and the comparative examples in the above table, the absorption rate and the compressive strength are not different from the bricks and the floor bricks of the comparative example, but the flexural strength is increased by more than 30%. You can see.

(가) 흡수율(A) Absorption rate

* 조작방법* How to operate

① 시료를 110±5℃의 공기 중탕속에서 24시간 건조하여 실온까지 방랭한 후 칭량하고, 이것을 건조무게 m1(g)한다.① The sample is dried in an air bath at 110 ± 5 ° C for 24 hours, cooled to room temperature, and weighed, and then weighed to dry weight m 1 (g).

② 이 시료를 20±5℃의 물속에서 24시간 정지한다. 시료상부와 수면사이의 거리를 50∼60mm로 한다.② Stop this sample in water at 20 ± 5 ℃ for 24 hours. The distance between the upper part of the sample and the surface of water is 50 to 60 mm

③ 이것을 물속에서 꺼내어 재빨리 젖은 헝겊으로 표면의 수분을 닦고, 즉시 무게를 달아 이것을 수분을 포함한 무게 m2(g)로 한다.③ Take this out of water and quickly wipe the surface moisture with a damp cloth. Weigh immediately and make it m 2 (g) including water.

* 계 산* Calculation

흡수율은 다음식에 따라 계산하고 KS A 0021에 따라 소숫점 이하 첫째 자리에서 끝맺음을 한다.Absorption rate is calculated according to the following formula and concludes at the first place after the decimal point according to KS A 0021.

a = m1/m2×100a = m 1 / m 2 × 100

여기까지 a : 흡수율(%)So far a: Absorption rate (%)

m1: 건조무게(g)m 1 : dry weight (g)

m2: 수분을 포함한 무게(g)m 2 : Weight including water (g)

(나) 압축강도(B) compressive strength

* 조작방법* How to operate

시료는 미리 110±5℃의 공기 중탕속에서 24시간 후에 꺼내어 실온에서 방랭한다.The sample is taken out in an air bath at 110 ± 5 ° C. in advance after 24 hours and allowed to cool at room temperature.

벽돌의 190×90mm면을 가압면으로 하고, 시료마다 개구부를 포함하는 가압면적A(m3)를 구한다. 가압면에서 필요에 따라 종이 조각등을 끼워 균일하게 가압한다.A 190 x 90 mm face of the brick is used as the pressing surface, and the pressing area A (m 3 ) including the opening for each sample is obtained. If necessary, press a piece of paper or the like to apply pressure evenly.

가압속도는 매초 49-98.1Ncm3{5-10kgf/m3}로 하여, 시료가 파괴되었을 때의 최대하중 WN{kgf}을 측정한다.The pressurization rate is set at 49-98.1 Ncm 3 {5-10 kgf / m 3 } per second, and the maximum load WN {kgf} when the sample is destroyed is measured.

* 계 산* Calculation

압축강도는 다음식에 따라 계산하고 KS A 0021 따라 정수자리로 끝맺음하여 보고한다.Compressive strength shall be calculated according to the following formula and reported by ending with an integer number according to KS A 0021.

C = A/wC = A / w

C = 압축강도C = compressive strength

A = 가압면적A = pressure area

W = 최대하중W = maximum load

(다) 휨강도(C) flexural strength

* 조작방법* How to operate

휨 시헙은 시료를 24시간 물속에 침수시킨 후 꺼낸 즉시 시험한다. 시료는지점간 거리를 140mm로 취하여 지점간 중앙에 하중을 가한다. 이때, 가압속도는 파괴하중의 약 50%까지는 빠른 속도로 작용시킨 다음 최대휨 압축용량의 증가가 매분9.8N/mm3를 초과하지 않을 정도로 하중을 가하여 시험기에 나타난 최대항중 P를 측정하여 식(1)에 따라 휨 강도를 계산한다.The deflection test is performed immediately after removal of the sample in water for 24 hours. Take a distance of 140 mm between the points of the sample and apply a load to the center of the points. At this time, pressurization speed is applied to high speed up to about 50% of failure load, and then the maximum load P indicated in the tester is measured by applying a load such that the increase in maximum bending compression capacity does not exceed 9.8 N / mm 3 per minute. Calculate the flexural strength according to (1).

* 계 산* Calculation

휨강도 (N/mm3) = 3Pl/2bd2 Flexural Strength (N / mm 3 ) = 3Pl / 2bd 2

여기에서 P : 시료기가 나타낸 최대 파괴하중(N)Where P: Maximum breaking load indicated by the sampler (N)

l : 지점간 거리(mm)l: Distance between points (mm)

b : 지점간에 지각방향의 평균나비(mm)b: average width of the earth's crust between points (mm)

d : 바닥벽돌의 평균무게(mm)d: average weight of floor brick (mm)

<비고><Remarks>

① 시료의 가압면 및 지지면에는 고무판, 기타 이외 유사한 것을 끼워 넣어 하중이 균등하게 분포되도록 하여도 지장이 없다① There is no problem even if the load is distributed evenly by inserting a rubber plate or other similar material on the pressing surface and the supporting surface of the sample.

② 시료는 블록모양 그대로 시험하되 블록의 양 끝단에 중앙점을 연결한 중심에 직각방향으로 가압하여야 한다.② The sample shall be tested as it is in a block shape, but shall be pressurized at right angles to the center where the center point is connected to both ends of the block.

③ 블록모양 그대로 휨강도시험이 불가능한 경우에는 시료를 200×60×60mm로 절단하여 시료의 치수를 측정한, 후 휨 시험을 하여 계산한다.③ If the flexural strength test is impossible as it is in the form of a block, cut the sample into 200 × 60 × 60mm and measure the dimensions of the sample.

④ 시료를 200×60×60mm의 치수로 절단할 수 없을 때에는 더 적은 치수로 절단하여 시험할수 있다.④ If the sample cannot be cut to the size of 200 × 60 × 60mm, it can be cut and tested to the smaller size.

⑤ 휨시험 전 가압단면의 치수측정은 세로방향의 가압선 상하 2곳에서 나비를 측정하고 두께는 세로방향 양끝에서 1/4안쪽 2곳을 측정한다.⑤ For the measurement of the pressure cross section before the bending test, the butterfly is measured at two places above and below the longitudinal line in the longitudinal direction, and the thickness is measured at two places within one quarter at both ends of the longitudinal direction.

⑥ 종래 단위의 시험기 또는 계측기를 사용하여 시험하는 경우 국제 단위게(S1)에 의한 수치환산은 다음에 의한다.⑥ In case of testing by using the conventional unit tester or measuring instrument, the numerical conversion by S1 is as follows.

1kgf= 9.80N1kgf = 9.80N

이와같이된 본 발명은 광촉매(Photocatalytic)작용에 의한 대기오염의 주원인인 질소산화물(N0x)을 정화시키고 유기물을 분해시키며, 자외선차단은 물론 살균, 향균, 탈취의 효능 및 효과가 있는 환경친화적인 건축용 벽돌 및 바닥벽돌을 제공하게 되고 벽돌고유의 색상이 아닌 다른 유색발색(오렌지→노량계열의 색채)의 제품을 제공하게 된다.Thus, the present invention purifies nitrogen oxide (N0x), which is the main cause of air pollution by photocatalytic action, decomposes organic matters, and is an environmentally friendly building brick that has the effect and effect of UV protection as well as sterilization, antibacterial and deodorization. And it provides a floor brick and the product of the color development (orange → the amount of aging series) other than the unique color of the brick.

또, 점토관련제품인 기와, 블럭, 타일, 판넬등에도 적용할수 있어서 본 발명의 권리범주에 속한다할수 있으며 아울러 생활전반에 대한 삶의 쾌적성 및 건강유지와 공기환경오염정화로 인한 환경개선효과등으로 인한 친환경적인 광촉매(Photocatalytic)작용의 건축재로 기술을 향상시키게 된다.In addition, it can be applied to tiles, blocks, tiles, panels, etc., which are clay-related products, and thus belongs to the right category of the present invention. The technology will be improved by building materials with environmentally friendly photocatalytic action.

Claims (3)

(삭제)(delete) 점토제품의 주원료 90∼98%에 광촉매물질인 이산화티타늄(TiO2)의 파우더 (Pouder)를 2∼10%중랑비로 첨가혼합한후 진공사출기로 성형하여 50∼100℃의 온도에 50∼60시간 건조시킨후 1100∼1160℃의 온도에 30∼40시간 예열 및 소성냉각시켜서 된 광촉매작용을 하는 점토벽돌의 제조방법The powder of titanium dioxide (TiO 2 ), a photocatalytic material, is added and mixed in 2-10% neutral ratio after mixing 90 ~ 98% of the main raw material of clay products, and then it is formed by vacuum injection molding machine for 50 ~ 60 hours. Method of producing clay bricks which act as a photocatalyst after drying and preheating and plastic cooling at a temperature of 1100 to 1160 ° C for 30 to 40 hours (삭제)(delete)
KR10-2001-0001923A 2001-01-12 2001-01-12 Manufacturing method of Photocatalytic action clay brick KR100414149B1 (en)

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Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR950000600A (en) * 1993-06-04 1995-01-03 유병황 Light weight aggregate and its manufacturing method
KR19980023926A (en) * 1996-01-24 1998-07-06 아끼모또 유미 NOx Purification Block for Packaging
JPH1161708A (en) * 1997-08-22 1999-03-05 Fujikon:Kk Concrete product removing nox in atmospheric air by using catalytic effect and manufacture thereof
KR19990088314A (en) * 1998-05-14 1999-12-27 타카하시 시게미쯔 UV blocking Material and Method of fabricating the same
KR20000012864A (en) * 1998-08-01 2000-03-06 고석권 Material for treating water
KR20010086695A (en) * 2000-03-02 2001-09-15 김명환 Complex Catalysts Used For Removing Nitrogen Oxides And Aromatic Halogen Compounds Among Flue Gases And Method For Preparing The Sames
KR20020045856A (en) * 2000-12-11 2002-06-20 윤영진 Photocatalyst coating sol capable of hardening at low temperature and preparation method thereof
KR20020078137A (en) * 2001-04-06 2002-10-18 이승한 method for manufacturing ceramic materials with a sound absorption by using a foaming agent

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR950000600A (en) * 1993-06-04 1995-01-03 유병황 Light weight aggregate and its manufacturing method
KR19980023926A (en) * 1996-01-24 1998-07-06 아끼모또 유미 NOx Purification Block for Packaging
JPH1161708A (en) * 1997-08-22 1999-03-05 Fujikon:Kk Concrete product removing nox in atmospheric air by using catalytic effect and manufacture thereof
KR19990088314A (en) * 1998-05-14 1999-12-27 타카하시 시게미쯔 UV blocking Material and Method of fabricating the same
KR20000012864A (en) * 1998-08-01 2000-03-06 고석권 Material for treating water
KR20010086695A (en) * 2000-03-02 2001-09-15 김명환 Complex Catalysts Used For Removing Nitrogen Oxides And Aromatic Halogen Compounds Among Flue Gases And Method For Preparing The Sames
KR20020045856A (en) * 2000-12-11 2002-06-20 윤영진 Photocatalyst coating sol capable of hardening at low temperature and preparation method thereof
KR20020078137A (en) * 2001-04-06 2002-10-18 이승한 method for manufacturing ceramic materials with a sound absorption by using a foaming agent

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