KR100994335B1 - Manufacturing methods of water purification concrete using micro-organisms and solution - Google Patents

Manufacturing methods of water purification concrete using micro-organisms and solution Download PDF

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KR100994335B1
KR100994335B1 KR20100001019A KR20100001019A KR100994335B1 KR 100994335 B1 KR100994335 B1 KR 100994335B1 KR 20100001019 A KR20100001019 A KR 20100001019A KR 20100001019 A KR20100001019 A KR 20100001019A KR 100994335 B1 KR100994335 B1 KR 100994335B1
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concrete
water
aggregate
curing
molding composition
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Korean (ko)
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전진용
서대석
장영일
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전진용
동산콘크리트산업(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
    • C04B28/02Compositions 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 hydraulic cements other than calcium sulfates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F2003/001Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
    • 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
    • C04B2103/0001Living organisms, e.g. microorganisms, or enzymes
    • 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
    • C04B2111/00793Uses not provided for elsewhere in C04B2111/00 as filters or diaphragms
    • 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
    • C04B2111/74Underwater applications
    • 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)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PURPOSE: A manufacturing method of water-purifying concrete using microbial culture fluid is provided to improve the removal efficiency of water based pollutants by maintaining an odor reducing effect during a curing process of the concrete. CONSTITUTION: A manufacturing method of water-purifying concrete using microbial culture fluid comprises the following steps: preparing a molding product including 5.5~7.6% of binder, 61.3~79.6% of aggregate, 0.2~0.3% of admixture, 3.4~4.8% of microbe culture fluid, 4.3~5.1% of water, and the remainder of air; wet-curing the molding product inside a curing chamber with a humidity of 80~90% at 10~50deg C; and curing the molding product for 7~30 days at room temperature.

Description

미생물배양액을 이용한 수질정화 콘크리트의 제조방법{Manufacturing Methods of Water Purification Concrete using Micro-Organisms and Solution}Manufacturing Method of Water Purification Concrete using Micro-Organisms and Solution

본 발명은 산업부산물로 발생하는 고로슬래그 미분말과 슬래그골재, 플라이애시와 버텀애시, 화산재와 화산석 및 악취제거, 유해물질의 흡착 및 분해작용, 항균작용이 우수하고, 콘크리트의 강알칼리성 및 양생과정에 따른 온도의 변화에 따른 생육환경의 변화에 영향이 적은 미생물을 선택적으로 배양한 배양액을 적정량 혼합하여 질소, 인 등의 수질오염물질의 제거효과가 기존의 수질정화용 콘크리트에 비하여 크고, 장기간에 걸쳐 지속되는 수질정화 기능을 갖는 수질정화 콘크리트의 제조방법에 관한 것이다.The present invention is the blast furnace slag powder and slag aggregate, fly ash and bottom ash, fly ash and bottom ash, volcanic ash and odor removal, the adsorption and decomposition of toxic substances, antibacterial action, and the strong alkali and curing process of concrete The effect of eliminating water pollutants such as nitrogen and phosphorus is greater than that of conventional water purification concrete by mixing appropriate amount of culture medium that selectively cultured microorganism with little influence on the change of growth environment according to the change of temperature It relates to a method for producing water purification concrete having a water purification function.

재생골재 등을 이용하여 수질 정화 기능을 갖는 콘크리트 제품의 제조방법 및 조성물과 관련된 기술로, 적절한 공극을 형성함으로써 수질 정화 기능을 갖도록 한 '재생골재를 이용한 수질정화용 친환경적인 콘크리트'(한국 등록특허공보 제10-0508881호)가 공개된 바 있다.Technology related to the manufacturing method and composition of concrete products having water purification function using recycled aggregates, 'eco-friendly concrete for water purification using recycled aggregates' that has water purification function by forming appropriate voids (Korea Patent Publication) 10-0508881) has been published.

또한, 다수의 공극이 형성된 고기능 콘크리트를 이용하여 수질 정화 기능을 갖도록 한 '폐콘크리트 미분말 및 순환골재와 산업부산물을 이용한 친환경 고기능 콘크리트의 제조방법 및 이에 의해 제조된 친환경 옹벽블록'(한국 등록특허공보 제10-0582770호)이 공개되기도 하였다.In addition, 'a method for producing eco-friendly high-performance concrete using waste concrete fine powder and recycled aggregates and industrial by-products and eco-friendly retaining wall blocks manufactured by using the high-performance concrete with a large number of voids to have a water purification function' (Korea Registered Patent Publication) 10-0582770) have been published.

상기와 같은 기술들은 공극률을 최적화시킴으로써 내부 공극을 이용하여 수질 정화 기능을 갖도록 한 것으로 이러한 기술은 여과 기술과 관련된다 할 것이다.Such techniques have been made to have a water purification function using internal pores by optimizing the porosity, which will be related to the filtration technology.

위와 같은 기술들은 재생골재나 폐콘크리트 등을 이용함으로써 자원재활용의 긍정적인 측면을 가지나, 자체적으로 포함되어 있는 유해물질이 지하수나, 해수, 토양을 오염시킬 수 있는 문제점이 있었다. The above technologies have a positive aspect of resource recycling by using recycled aggregates or waste concrete, but there is a problem that the harmful substances contained therein can contaminate groundwater, seawater, and soil.

결국, 최근 재생골재나 폐콘크리트에서 발생되는 오염물질로 인한 환경문제가 이슈화됨으로써 이러한 재생골재나 폐콘크리트의 재처리에 상당한 시간적, 경제적 소비를 발생시키고 있는 형편이다.As a result, recent environmental issues caused by contaminants generated from recycled aggregates or waste concrete have been raised, causing considerable time and economic consumption to reprocess such recycled aggregates or waste concrete.

특히, 재생골재나 폐콘크리트가 주로 재활용되는 호안블록, 인공어초 등의 오염된 산성화된 수분에 노출될 경우 황산이온이 내부로 이동하여 과포화되면 모노설페이트는 에트린가이트로 화함으로써 조직이 거칠어지고, 균열이 발생하며, 부식물질의 침입을 촉진시켜 콘크리트 수명을 단축시키는 등의 문제가 있었다. In particular, when exposed to contaminated acidified moisture such as reclaimed aggregates or waste concrete, which is mainly recycled, such as rafts and artificial reefs, when sulfate ions move inside and supersaturate, monosulfate becomes roughened by ethrinite. Cracks occur, and there is a problem such as to accelerate the intrusion of corrosive substances to shorten the life of the concrete.

한편, 최근 유용미생물을 콘크리트 제조시 첨가하여 항균 및 탈취능력을 향상시키고, 콘크리트 타설명의 유해미생물 서식을 차단하여 실내 환경 개선 기능을 갖도록 한 '친환경 항균 레미콘'(한국 등록특허공보 제10-0632976호)이 출원되었으며, 유용미생물을 콘크리트에 제조시 첨가하여 하천 및 호소 등의 수질정화작용을 하는 콘크리트의 제조방법인 ‘수질정화용 콘크리트 제조방법’(한국 등록특허공보 제10-0840602호)이 출원되었으나, ‘친항균 항균 레미콘‘의 경우 단지 공기 정화 및 실내 환경 개선 기능이 있는 것으로 알려져 있을 뿐이며, 실제로 유용미생물을 콘크리트에 적용하는 경우에 콘크리트의 양생과정에 있어서 고온상태와 강알칼리성의 영향으로 미생물이 사멸하거나, 미생물의 양이 감소하여 소기의 목적을 달성하기가 매우 어려운 실정이며, ’수질정화용 콘크리트의 제조방법‘의 경우 질소, 인 등의 수질 오염 물질의 제거 효과가 크지 않고, 그 효과가 장기간에 걸쳐 이루어 지지 않기 때문에 이를 이용한 수질정화용 콘크리트의 제조시 근본적인 수질정화를 이루기에는 한계점을 가지고 있다.On the other hand, 'environmental antimicrobial ready-mixed concrete' to improve indoor environment by adding useful microorganisms in concrete manufacturing to improve antibacterial and deodorizing ability and block harmful microbial forms of concrete description (Korea Patent Publication No. 10-0632976 No.) has been filed, and 'Method for manufacturing water quality concrete' (Korea Patent Publication No. 10-0840602), which is a method of producing concrete that adds useful microorganisms to concrete and performs water purification activities such as rivers and lakes, is applied. However, the 'antimicrobial antimicrobial ready-mixed concrete' is known to have only the function of air purification and indoor environment improvement.In fact, when the useful microorganisms are applied to concrete, microorganisms are affected by the high temperature and strong alkalinity in the curing process of concrete. It is very difficult to die, or to reduce the amount of microorganisms, to achieve the desired purpose. In the case of the 'preparation method of concrete for water purification', the removal effect of water pollutants such as nitrogen and phosphorus is not great and the effect is not made for a long time. There is a limit to this.

따라서 질소, 인 등의 수질오염 물질의 저거 효율이 높고, 그 효과가 장기간에 걸쳐 지속되며, 그 외의 친환경적인 특성과 콘크리트의 기본 물성이 강도, 내구성이 유지되도록 하기 위한 방법으로 미생물배양액을 이용한 수질정화용 콘크리트의 제조방법인 본 발명을 출원하게 되었다.Therefore, the efficiency of water removal of water pollutants such as nitrogen and phosphorus is high, the effect lasts for a long time, and the water quality using microbial culture liquid as a way to maintain the strength and durability of other eco-friendly properties and the basic physical properties of concrete. The present invention has been applied for a method of manufacturing concrete for purification.

KR, 10-0508881, 2005.08.09KR, 10-0508881, 2005.08.09 KR, 10-0582770, 2006.05.16KR, 10-0582770, 2006.05.16 KR, 10-0632976, 2006.09.29KR, 10-0632976, September 29, 2006 KR, 10-0840602, 2008.06.17KR, 10-0840602, 2008.06.17

본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법은 위와 같은 종래 유용미생물을 사용하여 제조되는 콘크리트에서 발생하는 상기의 문제점을 해결하기 위하여 발명된 것으로서, 하천, 호수 등의 담수역 뿐만 아니라 항구 및 해안 등의 해수역에 있어서 질소, 인 등의 수질오염물질의 제거 효율이 높고, 장기간에 걸쳐 지속되며, 각종 생물의 생육 및 착생이 용이한 수질정화 콘크리트의 제조방법을 제공하려는 것이다.The method for producing water-purified concrete using the microorganism culture medium of the present invention was invented to solve the above problems occurring in concrete prepared using the above-mentioned conventionally useful microorganisms. The present invention aims to provide a method for producing water-purifying concrete that has high efficiency in removing water pollutants such as nitrogen and phosphorus in seawater such as coasts, which lasts for a long time, and is easy to grow and grow various organisms.

보다 구체적으로, 악취제거, 유해물질의 흡착 및 분해작용, 항균작용이 우수하고, 콘크리트의 강알칼리성 및 양생과정에 따른 온도의 변화에 따른 생육환경의 변화에 영향이 적은 미생물을 선택적으로 배양한 배양액을 사용하여 수질정화작용 등 친환경적인 특성이 크고, 이러한 작용을 장기간에 걸쳐 유지될 수 있게 하면서 부가적으로 콘크리트의 사용재료로 인한 2차적인 오염을 방지하고, 콘크리트의 강도 및 내구성을 증가시킬 수 있게 하려는 것이다.More specifically, the culture medium which selectively cultivated microorganisms excellent in removing odor, adsorption and decomposition of harmful substances, and antibacterial effect and having little influence on growth environment due to temperature change according to strong alkalinity and curing process of concrete. It can be used for environmentally friendly properties such as water purification, which can be maintained for a long time and additionally prevent secondary pollution due to the material used in concrete, and increase the strength and durability of concrete. To make it work.

또, 최근 전력수요의 증가 및 석탄화력발전소의 전력생산 의존도 증가에 따라 매년 그 발생량이 크게 증가하고 있는 플라이애시, 버텀애시와 매년 제철소 등의 산업현장에서 대량 부산되고 있는 슬래그파우더 및 슬래그 골재와 화산석 및 화산재를 이용하여 하천용 수질정화 블록, 수로관, 맨홀, 암거 등 콘크리트용 고부가가치 사용 재료 및 성능 향상 요소로 유효 재활용함으로서 천연자원의 고갈방지 및 하천의 수질정화 및 생물의 착생 및 생육을 위한 수질정화 콘크리트의 제조방법을 제공하려는 것이다.In addition, slag powder, slag aggregate, and volcanic stone are being produced in large quantities in industrial sites such as fly ash, bottom ash, and steel mills, which are increasing every year due to the recent increase in electric power demand and dependence on coal-fired power plants. By using and volcanic ash, it is effectively recycled as a high value-added material and performance enhancing element for concrete such as river water purification blocks, water pipes, manholes, culverts, etc. to prevent depletion of natural resources, water purification for rivers, and water quality for living and growing It is to provide a method for producing purified concrete.

본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법은 상기와 같은 과제를 해결하기 위하여, 본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법은, 성형조성물 전체 부피의 5.5 ~ 7.6%의 결합재와, 성형조성물 전체 부피의 61.3 ~ 79.6%의 골재와, 성형조성물 전체 부피의 0.2 ~ 0.3 %의 혼화제와, 성형조성물 전체 부피의 3.4 ~ 4.8%의 선택적으로 배양된 미생물 배양액과 전체부피의 4.3 ~ 5.1%의 물과 잔량으로서 공기를 포함하여 이루어지는 성형조성물을 준비하는 혼합단계와; 상기 성형조성물을 습도 80 ~ 90%, 온도 10 ~ 50℃ 조건으로 양생실에서 12 ~ 24 시간 습윤 양생한 후, 기건상태로 상온에서 7 ~ 30일 동안 양생시키는 양생단계;를 포함하여 구성된,를 포함하여 구성된다.In order to solve the above problems, the method for producing water-purified concrete using the microbial culture medium of the present invention, the method for producing water-purified concrete using the microbial culture medium of the present invention, the binder composition of 5.5 ~ 7.6% of the total volume of the molding composition and , 61.3-79.6% aggregate of the total volume of the molding composition, 0.2-0.3% of admixture of the total volume of the molding composition, 3.4-4.8% of selectively cultured microbial culture medium and 4.3-5.1 of the total volume of the molding composition. A mixing step of preparing a molding composition comprising air as the remaining amount of water and%; Consists of curing the molding composition at a humidity of 80 ~ 90%, temperature 10 ~ 50 ℃ conditions in the curing room for 12 to 24 hours, curing for 7 to 30 days at room temperature in a dry state; It is configured to include.

이때, 상기 미생물 배양액은 미생물과 배양액을 1:2의 중량비로 혼합한 것을 특징으로 한다.At this time, the microbial culture is characterized in that the mixture of the microorganism and the culture in a weight ratio of 1: 2.

또, 상기 골재는 폐콘크리트 순환골재, 부순돌, 버텀애시, 슬래그 골재, 화산석 중 선택된 1종 또는 2 내지 4종의 혼합물로 이루어진 것을 특징으로 한다.In addition, the aggregate is characterized in that consisting of one or two to four selected from the recycled concrete recycled aggregate, crushed stone, bottom ash, slag aggregate, volcanic stone.

아울러, 상기 결합재는 시멘트, 플라이애쉬, 슬래그파우더, 고로슬래그미분말 중 선택된 1종 또는 2 내지 4종의 혼합물로 이루어진 것을 특징으로 한다.In addition, the binder is characterized in that consisting of one or two to four selected from cement, fly ash, slag powder, blast furnace slag powder.

본 발명에 의해, 수질오염물질인 질소, 인 등의 제거효율이 크고 장기간에 걸쳐 지속되며, 악취제거, 유해물질의 흡착 및 분해작용, 항균작용이 우수하고, 콘크리트의 강알칼리성 및 양생과정에 따른 온도의 변화에 따른 생육환경의 변화에 영향이 적은 미생물을 선택적으로 배양한 배양액을 이용하여 폐콘크리트, 슬래그 골재, 버텀애시 및 일반 콘크리트에 포함된 유해성 물질이 수중 환경을 오염시키지 않게 된다. According to the present invention, the removal efficiency of water pollutants such as nitrogen and phosphorus is large and lasts for a long time, and it is excellent in removing odors, adsorption and decomposition of harmful substances, and antibacterial activity, according to the strong alkalinity and curing process of concrete. Hazardous substances contained in waste concrete, slag aggregate, bottom ash and general concrete do not contaminate the aquatic environment by using a culture medium selectively cultured microorganisms with little influence on the change of growth environment according to the change of temperature.

또, 콘크리트의 설치 초기에 기존 수질정화용 콘크리트에 비하여 성능이 우수하고 장기간에 걸쳐 우수한 수질정화 기능을 가짐은 물론, 콘크리트의 양생과정에서 발생하는 강알칼리성에 대한 저항성과 양생과정에서 발생하는 온도변화에 적응하여 미생물이 유지, 생활할 수 있는 요건을 제공하여 미생물의 악취제거, 유해물질의 흡착 및 분해작용, 항균작용이 콘크리트의 제조 후에도 유지된다. In addition, it has better performance than existing water purification concrete in the early stage of concrete installation and has excellent water purification function for a long time, as well as resistance to strong alkalinity generated during curing of concrete and temperature change during curing process. By adapting and providing the requirement for microorganisms to maintain and live, the odor removal of microorganisms, adsorption and decomposition of harmful substances, and antibacterial activity are maintained even after the manufacture of concrete.

또한, 석탄화력발전소 및 제철소 등에서 발생되는 플라이애쉬와 버텀애시, 고로슬래그파우더 및 슬래그 골재, 화산석을 성능 향상 요소로 유용하게 이용하여 천연자원의 고갈을 방지에 이바지할 수 있다. In addition, fly ash, bottom ash, blast furnace slag powder and slag aggregate, and volcanic stone, which are generated in coal-fired power plants and steel mills, etc., may be usefully used as performance enhancing factors to prevent depletion of natural resources.

아울러, 내화학성이 높고, 동결융해 저항성이 높은 콘크리트가 제공된다.In addition, concrete having high chemical resistance and high freeze-thawing resistance is provided.

도 1은 본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법을 나타낸 공정도.1 is a process chart showing a method for producing water-purified concrete using a microbial culture medium of the present invention.

상기한 목적을 달성하기 위한 구체적인 수단으로서 본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법은, 본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법은, 성형조성물 전체 부피의 5.5 ~ 7.6%의 결합재와, 성형조성물 전체 부피의 61.3 ~ 79.6%의 골재와, 성형조성물 전체 부피의 0.2 ~ 0.3 %의 혼화제와, 성형조성물 전체 부피의 3.4 ~ 4.8%의 선택적으로 배양된 미생물 배양액과 전체부피의 4.3 ~ 5.1%의 물과 잔량으로서 공기를 포함하여 이루어지는 성형조성물을 준비하는 혼합단계와; 상기 성형조성물을 습도 80 ~ 90%, 온도 10 ~ 50℃ 조건으로 양생실에서 12 ~ 24 시간 습윤 양생한 후, 기건상태로 상온에서 7 ~ 30일 동안 양생시키는 양생단계;를 포함하여 구성된,를 포함하여 구성된다.
As a specific means for achieving the above object, the method for producing water-purified concrete using the microbial culture medium of the present invention, the method for producing water-purified concrete using the microbial culture medium of the present invention is 5.5 to 7.6% of the total volume of the molding composition. Binder, 61.3-79.6% aggregate of the total volume of the molding composition, 0.2-0.3% of admixture of the total volume of the molding composition, 3.4-4.8% of selectively cultured microbial culture medium and the total volume of the molding composition. A mixing step of preparing a molding composition including air as water and a residual amount of 5.1%; Consists of curing the molding composition at a humidity of 80 ~ 90%, temperature 10 ~ 50 ℃ conditions in the curing room for 12 to 24 hours, curing for 7 to 30 days at room temperature in a dry state; It is configured to include.

이하 본 발명의 본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법에 대해 첨부된 도면을 통해 상세히 설명하기로 한다.Hereinafter will be described in detail with reference to the accompanying drawings for the production method of water purification concrete using the microbial culture medium of the present invention.

도 1은 미생물배양액을 이용하여 본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법을 나타낸 공정도이다.
1 is a process chart showing a method for producing water-purified concrete using the microbial culture medium of the present invention using a microbial culture medium.

1. 혼합단계1. Mixing Step

결합재, 골재, 혼화제, 미생물 배양액, 물, 공기를 혼합시켜 성형조성물을 준비한다.A molding composition is prepared by mixing a binder, aggregate, admixture, microbial culture, water and air.

여기서 결합제는 성형조성물 전체 부피의 5.5 ~ 7.6% 포함되는 것을 특징으로 한다.The binder is characterized in that it comprises 5.5 to 7.6% of the total volume of the molding composition.

이때, 결합재는 시멘트, 플라이애쉬, 슬래그파우더 중 선택된 1종 또는 2내지 3종의 혼합물로 이루어진다.At this time, the binder is composed of one or two or three selected from cement, fly ash, slag powder.

결합재의 보다 바람직한 조성은 시멘트와 고로슬래그미분말을 혼합하여 형성하거나, 시멘트와 플라이애쉬를 혼합하여 형성할 수 있다.A more preferable composition of the binder may be formed by mixing cement and blast furnace slag powder, or by mixing cement and fly ash.

이때, 시멘트와 함께 첨가되는 고로슬래그미분말과 플라이애쉬는 각각 시멘트 100 중량부에 대비하여 1 ~ 30 중량부 혼입된 것이 바람직하다. At this time, the blast furnace slag powder and fly ash added together with the cement is preferably mixed 1 to 30 parts by weight relative to 100 parts by weight of cement.

골재는 성형조성물 전체 부피에서 61.3 ~ 79.6% 포함되는 것을 특징으로 한다.Aggregate is characterized in that it comprises 61.3 ~ 79.6% in the total volume of the molding composition.

골재는 일반 골재를 사용할 수도 있으나, 폐콘크리트 순환골재, 부순돌, 버텀애시, 슬래그 골재, 화산석 중 선택된 1종 또는 2 내지 5 종의 혼합물을 사용하는 것이 바람직하다.Aggregate may be used as a general aggregate, it is preferable to use one or a mixture of 2 to 5 selected from waste concrete recycled aggregate, crushed stone, bottom ash, slag aggregate, volcanic stone.

혼화제는 성형조성물 전체 부피의 0.2 ~ 0.3 % 포함되는 것을 특징으로 한다.The admixture is characterized in that it comprises 0.2 to 0.3% of the total volume of the molding composition.

이러한 혼화제는 분산제, 지방산금속염, 실리카, 촉진제, 가소제, 계면활성제를 규격에 따라 적절히 혼합한 혼합물이 사용될 수 있다. The admixture may be a mixture of a dispersant, a fatty acid metal salt, silica, an accelerator, a plasticizer, and a surfactant as appropriate.

유용미생물 배양액은 성형조성물 전체 부피의 3.4 ~ 4.8% 포함되며, 악취제거, 유해물질의 흡착 및 분해작용, 항균작용이 우수하고, 콘크리트의 강알칼리성 및 양생과정에 따른 온도의 변화에 따른 생육환경의 변화에 영향이 적은 미생물을 선택적으로 배양한 배양액으로 bacillus firmus계통의 호염기성 미생물들과 배양액을 1:2의 중량비로 혼합된 것이 바람직하다.Useful microorganism culture medium contains 3.4 ~ 4.8% of the total volume of the molding composition, and it is excellent in removing odor, adsorption and decomposition of harmful substances, and antibacterial activity, and the growth environment according to the temperature change according to the strong alkalinity and curing process of concrete. As a culture medium selectively cultured microorganisms with little change, it is preferable to mix basophilic microorganisms of the bacillus firmus system and the culture solution in a weight ratio of 1: 2.

상기 혼합단계에서 모든 재료를 한번에 모두 같이 혼합할 수도 있으나, 가장 바람직한 방법은 골재와 미생물 배양액을 사전에 미리 5 내지 10 분간 혼합한 다음 다른 재료들과 혼합하는 것이 가장 바람직하다 할 것이다.
In the mixing step, all the materials may be mixed together all at once, but the most preferred method is to mix the aggregate and the microbial culture in advance for 5 to 10 minutes in advance and then it is most preferable to mix with other materials.

2. 양생단계2. Curing stage

혼합단계에서 형성된 성형조성물을 습도 80 ~ 90%, 온도 10 ~ 50℃ 조건으로 양생실에서 12 ~ 24 시간 습윤 양생한 후, 기건상태로 상온에서 약 5 내지 10 일 정도 양생시킨다.The molding composition formed in the mixing step is wet cured in a curing room for 12 to 24 hours at a humidity of 80 to 90% and a temperature of 10 to 50 ° C., and then cures about 5 to 10 days at room temperature in a dry state.

이때, 성형조성물을 제품의 특성에 따라 일정한 형상대로 형성하기 위해 다양한 형상의 성형틀을 준비한 후 성형틀에 재료를 투입한 후 양생한다.
At this time, in order to form a molding composition in a certain shape according to the characteristics of the product, after preparing a molding die of various shapes, the material is put into the molding mold and cured.

이하, 본 발명의 미생물배양액을 이용한 수질정화 콘크리트의 제조방법에 대해 실시예 및 비교예를 들어 설명하기로 한다.
Hereinafter, an example and a comparative example will be described with reference to a method for producing water-purified concrete using the microbial culture medium of the present invention.

<실시예 1> 미생물배양액을 이용한 수질정화 콘크리트 1Example 1 Water Purification Concrete 1 Using Microbial Culture Solution

결합재로써 시멘트 98ℓ를 준비하고, 골재는 부순골재 796ℓ, 혼화제 3ℓ를 준비하였다. 98 l of cement was prepared as a binder, and aggregates 796 l of crushed aggregate and 3 l of admixture were prepared.

미생물배양액은 악취제거, 유해물질의 흡착 및 분해작용, 항균작용이 우수하고, 콘크리트의 강알칼리성 및 양생과정에 따른 온도의 변화에 따른 생육환경에 영향이 적은 미생물을 선택적으로 배양한 것으로 미생물과 배양액을 1:2의 중량비로 혼합한 것을 34ℓ 준비하고, 물 51ℓ을 준비한 후 준비된 골재와 미생물 배양액을 5분간 선 혼합한 후 결합재와 혼화제, 물을 혼합한 후 성형틀에 투입한 다음 습도 약 80 ~ 90%, 온도 20 ~ 25℃ 조건으로 양생실에서 18 시간 습윤 양생한 후, 기건상태로 상온에서 7 일간 양생시켜 수질정화 콘크리트를 제조하였다.
The microbial culture medium is excellent in removing odor, adsorption and decomposition of harmful substances, and antimicrobial activity, and selectively cultured microorganisms that have little effect on the growth environment due to the strong alkalinity of concrete and the temperature change according to the curing process. Was prepared by mixing the weight ratio of 1: 2 and 34ℓ, and after preparing 51L of water, the prepared aggregate and the microbial culture solution were pre-mixed for 5 minutes, and then mixed with a binder, admixture and water, and then put into a molding mold, and then the humidity of about 80 ~ After wetting and curing for 18 hours in a curing room at 90% and a temperature of 20-25 ° C., water was cured at room temperature for 7 days to prepare water-purified concrete.

<실시예 2> 미생물배양액을 이용한 수질정화 콘크리트 2Example 2 Water Purification Concrete 2 Using Microbial Culture Solution

실시예 1과 동일하게 진행하되, 결합재로써 시멘트 91ℓ와 플라이애시 7ℓ를 준비하고, 골재는 부순골재 796ℓ, 혼화제 3ℓ를 준비한 채 진행하여 수질정화 콘크리트를 제조하였다.
Proceed in the same manner as in Example 1, 91L of cement and 7L of fly ash were prepared as a binder, and aggregate was prepared with 796L of crushed aggregate and 3L of admixture to prepare water-purified concrete.

<실시예 3> 미생물배양액을 이용한 수질정화 콘크리트 3Example 3 Water Purification Concrete 3 Using Microbial Culture Solution

실시예 1과 동일하게 진행하되, 결합재로써 시멘트 76ℓ와 플라이애시 7ℓ, 슬래그미분말 15ℓ를 준비하고, 골재는 부순골재 796ℓ, 혼화제 3ℓ를 준비한 진행하여 수질정화 콘크리트를 제조하였다.
Proceeded in the same manner as in Example 1, 76L cement and 7L fly ash, 15L slag powder was prepared as a binder, and the aggregate was prepared by crushing aggregate 796L, admixture 3L to prepare water-purified concrete.

<실시예 4> 미생물배양액을 이용한 수질정화 콘크리트 4Example 4 Water Purification Concrete 4 Using Microbial Culture Solution

실시예 1과 동일하게 진행하되, 결합재로써 시멘트 91ℓ와 플라이애시 7ℓ를 준비하고, 골재는 부순골재 796ℓ, 혼화제 3ℓ를 준비하고, 미생물 배양액은 48 ℓ 준비한 채 진행하여 수질정화 콘크리트를 제조하였다.
Proceed in the same manner as in Example 1, 91L of cement and 7L of fly ash were prepared as a binder, aggregate was prepared of 796L of crushed aggregate, 3L of admixture, and 48L of microbial culture was prepared to prepare water-purified concrete.

<실시예 5> 미생물배양액을 이용한 수질정화 콘크리트 5Example 5 Water Purification Concrete Using Microbial Culture Solution 5

실시예 4와 동일하게 진행하되, 결합재로써 시멘트 76ℓ와 플라이애시 7ℓ, 슬래그미분말 15ℓ를 준비하고, 골재는 부순골재 796ℓ, 혼화제 3ℓ를 준비한 채 진행하여 수질정화 콘크리트를 제조하였다.
Proceed in the same manner as in Example 4, 76L of cement, 7L of fly ash, 15L of slag fine powder were prepared as a binder, and aggregate was prepared with 796L of crushed aggregate and 3L of admixture to prepare water-purified concrete.

비교예는 수질정화작용을 하는 콘크리트의 제조방법인 ‘수질정화용 콘크리트 제조방법’(한국 등록특허공보 제10-0840602호)에 따라 다음과 같은 조건에서 제조하였다.
The comparative example was prepared under the following conditions according to the 'preparation method for water purification concrete' (Korean Patent Publication No. 10-0840602), which is a method for producing concrete having a water purification function.

<비교예 1> Comparative Example 1

결합재로써 시멘트 344.0kg을 준비하고, 골재는 굵은골재 942.0kg와 잔골재 845.0kg을 혼합하여 준비하고, 혼화제 1.7kg을 준비하였다. Cement 344.0kg was prepared as a binder, aggregate was prepared by mixing coarse aggregate 942.0kg and fine aggregate 845.0kg, and prepared admixture 1.7kg.

유용미생물 배양액은 배양용액, 바실루스균, 락토바실루스균, 사카로미세스균이 1 : 3 : 3 : 3의 중량비로 혼합하여 총 34.6kg 준비하고, 물 136.4kg을 준비한 후 준비된 결합재, 골재, 혼화제, 유용미생물 배양액, 물을 혼합하여 성형조성물을 제조한 후 성형조성물을 성형틀에 주입하면서 진동기로 110 ~ 130Hz의 진동수로 높이 10 ~ 30cm 마다 층으로 나누어 다져 성형한 다음 양생실에서 4 시간 동안 증기 양생시켜 수질정화 콘크리트를 제조하였다.
Useful microbial cultures were prepared by mixing the culture solution, Bacillus, Lactobacillus, Saccharomyces in a weight ratio of 1: 3: 3: 3 and a total of 34.6kg, 136.4kg of water, and then prepared binder, aggregate, admixture, After preparing the molding composition by mixing the useful microbial culture solution and water, the molding composition is injected into the molding mold, and then divided into layers every 10 to 30 cm in height with a vibration frequency of 110 to 130 Hz, followed by steam curing in a curing room for 4 hours. The water purification concrete was prepared.

<비교예 2> Comparative Example 2

비교예 1과 동일한 방법으로 진행하되, 결합재로써 시멘트 318.0kg와 플라이애쉬 24.0kg을 혼합하여 준비하고, 골재는 굵은골재 942.0kg와 잔골재862.0kg을 혼합하여 준비하고, 혼화제 1.7kg을 준비하였다.Proceed in the same manner as in Comparative Example 1, but was prepared by mixing the cement 318.0kg and fly ash 24.0kg as a binder, the aggregate was prepared by mixing coarse aggregate 942.0kg and fine aggregate 862.0kg, and prepared admixture 1.7kg.

유용미생물 배양액은 동일한 중량을 준비하고, 물은 127.4kg을 준비한 채 진행하여 수질정화 콘크리트를 제조하였다.
The useful microbial culture was prepared with the same weight, and water was prepared while preparing 127.4 kg of water-purified concrete.

<비교예 3> Comparative Example 3

비교예 1과 동일한 방법으로 진행하되, 결합재로써 시멘트 213.0kg와 플라이애쉬 33.0kg, 슬래그미분말 82.0kg을 혼합하여 준비하고, 골재는 굵은골재 888.0kg와 잔골재 877.0kg을 혼합하여 준비하고, 혼화제 1.7kg을 준비하였다. Proceed in the same manner as in Comparative Example 1, as a binder was prepared by mixing cement 213.0kg, fly ash 33.0kg, slag powder 82.0kg, aggregate was prepared by mixing coarse aggregate 888.0kg and fine aggregate 877.0kg, admixture 1.7kg Was prepared.

유용미생물 배양액은 총 34.1kg 준비하고, 물 142.9kg을 준비한 채 진행하여 수질정화 콘크리트를 제조하였다.
A total of 34.1 kg of useful microbial culture was prepared, and 142.9 kg of water was prepared to prepare water-purified concrete.

<비교예 4> <Comparative Example 4>

비교예 1과 동일한 방법으로 진행하되, 결합재로써 시멘트 318.0kg와 플라이애쉬 24.0kg을 혼합하여 준비하고, 골재는 굵은골재 942.0kg와 잔골재 862.0kg을 혼합하여 준비하고, 혼화제 1.7kg을 준비하였다. Proceed in the same manner as in Comparative Example 1, but was prepared by mixing the cement 318.0kg and fly ash 24.0kg, the aggregate was prepared by mixing coarse aggregate 942.0kg and fine aggregate 862.0kg, and prepared admixture 1.7kg.

유용미생물 배양액은 총 69.3kg 준비하고, 물 92.7kg을 준비한 채 진행하여 수질정화 콘크리트를 제조하였다.
A total of 69.3 kg of useful microbial culture was prepared, and 92.7 kg of water was prepared to prepare water-purified concrete.

<비교예 5> Comparative Example 5

비교예 1과 동일한 방법으로 진행하되, 결합재로써 시멘트 217.0kg와 플라이애쉬 35.0kg, 슬래그미분말 88.0kg을 혼합하여 준비하고, 골재는 굵은골재 895.0kg와 잔골재 854.0kg을 혼합하여 준비하고, 혼화제 1.8kg을 준비하였다. Proceed in the same manner as in Comparative Example 1, but prepared by mixing 217.0kg cement and 35.0kg fly ash, 88.0kg slag powder as a binder, the aggregate is prepared by mixing 895.0kg coarse aggregate and 854.0kg fine aggregate, 1.8kg admixture Was prepared.

유용미생물 배양액은 총 68.1kg 준비하고, 물 110.9kg을 준비한 채 진행하여 수질정화 콘크리트를 제조하였다.
A total of 68.1 kg of useful microbial culture was prepared, and 110.9 kg of water was prepared to prepare water-purified concrete.

상기와 같이 준비된 실시예들과 비교예들을 대상으로 수행한 실험 및 그 결과에 대해 설명하면 아래와 같다.
Referring to the experiments performed on the examples and comparative examples prepared as described above and the results are as follows.

<실험예 1> 수질 정화 실험Experimental Example 1 Water Purification Experiment

상기 실시예 1 내지 5 및 비교예 1 내지 5의 수질정화 콘크리트를 가로, 세로 30cm, 높이 10cm로 준비하여 재령 28일부터 탄소 : 질소 : 인이 150 : 50 : 1의 농도가 되도록 염화암모늄과 제2인산나트륨 등의 성분비를 조정한 인공오수를 순환시키는 수로에 설치하여 분당 20 ㎖의 유량으로 순환시키고 일조 조건은 실외의 상황과 유사하게 형광등을 사용하여 6000룩스의 빛을 12시간 간격으로 점등과 소등을 반복하면서 20 ± 2℃로 유지된 항온실에서 1일, 10일, 50일, 100일, 200일, 400일, 600일에 종합수질측정기로 정화된 물의 총질소량(T-N), 총인량(T-P)을 측정하였다.The water-purifying concretes of Examples 1 to 5 and Comparative Examples 1 to 5 were prepared in a horizontal, vertical 30 cm, and 10 cm height, and the ammonium chloride and the agent were prepared so that carbon: nitrogen: phosphorus was 150: 50: 1 at the age of 28 days. It is installed in a circulating water circulating channel of artificial sewage adjusted by adjusting the composition ratio of sodium diphosphate, etc., and it circulates at a flow rate of 20 ml per minute, and the sunshine condition is similar to that of the outdoor environment. Total nitrogen content (TN) and total phosphorus of water purified by comprehensive water quality meter on day 1, 10, 50, 100, 200, 400 and 600 days in a constant temperature room kept at 20 ± 2 ℃ (TP) was measured.

인공오수는 해수와 담수로 나누어 시험이 진행하였고, 해수의 경우 천일염을 사용하여 염분 농도를 해수와 같이 조절하여 사용하였으며, 증발에 의한 오차를 감소시키기 위하여 인공오수가 일정량을 유지하도록 증류수를 보충하였다.
The artificial sewage was divided into seawater and fresh water, and the test was carried out. In the case of seawater, salt concentration was adjusted using sea salt with seawater, and distilled water was supplemented to maintain a certain amount of artificial sewage to reduce errors caused by evaporation. .

염화암모늄
(NH4Cl)
Ammonium chloride
(NH 4 Cl)
제2인산나트륨
(Na2HPO4)
Dibasic Sodium Phosphate
(Na 2 HPO 4 )
염화칼륨
(Kcl)
Potassium chloride
(Kcl)
황산나트륨
(NaSO4)
Sodium sulfate
(NaSO 4 )
7.6mg/ℓ7.6 mg / ℓ 1.8mg/ℓ1.8mg / ℓ 1.6mg/ℓ1.6 mg / ℓ 1.8mg/ℓ1.8mg / ℓ

상기 표 1은 인공오수의 성분을 나타낸 표이다.
Table 1 is a table showing the components of artificial sewage.

비교
대상
compare
object
경과일수에 따른 소거율Elimination Rate According to Elapsed Days
1일1 day 10일10 days 50일50 days 100일100 days 200일200 days 400일400 days 600일600 days T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P 실시예1Example 1 68.368.3 46.246.2 74.674.6 8080 75.175.1 77.677.6 80.780.7 83.683.6 83.483.4 84.684.6 86.186.1 86.186.1 85.485.4 85.485.4 비교예1Comparative Example 1 5656 2828 6969 3838 7373 5656 79.479.4 6868 8989 7979 7272 6464 2828 1818 실시예2Example 2 63.163.1 45.345.3 72.872.8 7676 73.473.4 80.580.5 76.976.9 79.879.8 84.584.5 86.786.7 83.383.3 84.984.9 82.582.5 84.784.7 비교예2Comparative Example 2 52.252.2 27.227.2 6868 3737 5555 5252 8080 6565 8787 8080 6363 5454 2323 1515 실시예3Example 3 6868 48.548.5 70.870.8 7676 73.473.4 7676 78.778.7 82.282.2 81.381.3 81.181.1 84.284.2 87.587.5 82.782.7 86.686.6 비교예3Comparative Example 3 5353 25.625.6 6666 41.341.3 69.569.5 52.952.9 75.375.3 6666 8686 73.573.5 7171 60.560.5 2525 1616 실시예4Example 4 6565 4444 66.766.7 74.174.1 72.572.5 84.284.2 80.780.7 8484 8383 85.285.2 84.584.5 90.390.3 87.187.1 8989 비교예4Comparative Example 4 5252 1919 5454 25.125.1 5959 4242 6464 5454 7676 6363 6464 5151 1919 1111 실시예5Example 5 6464 40.940.9 72.272.2 77.677.6 71.371.3 82.982.9 8080 84.684.6 84.784.7 83.483.4 81.681.6 87.587.5 82.682.6 8888 비교예5Comparative Example 5 5151 2323 6464 30.930.9 6666 4444 71.371.3 6161 8484 7575 6868 5353 2121 1414

상기 표 2는 담수에서의 수질검사 실험결과로 소거율의 단위는 (%)이다.
Table 2 shows the results of water quality test in fresh water, the unit of scavenging rate is (%).

비교
대상
compare
object
경과일수에 따른 소거율Elimination Rate According to Elapsed Days
1일1 day 10일10 days 50일50 days 100일100 days 200일200 days 400일400 days 600일600 days T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P T-NT-N T-PT-P 실시예1Example 1 24.5 24.5 21.7 21.7 34.0 34.0 31.6 31.6 39.2 39.2 41.0 41.0 39.6 39.6 42.0 42.0 38.7 38.7 46.0 46.0 42.5 42.5 44.3 44.3 44.0 44.0 50.0 50.0 비교예1Comparative Example 1 3.3 3.3 5.2 5.2 5.7 5.7 5.7 5.7 5.7 5.7 4.7 4.7 6.6 6.6 4.7 4.7 5.7 5.7 8.0 8.0 9.0 9.0 8.5 8.5 9.0 9.0 9.0 9.0 실시예2Example 2 27.3 27.3 25.6 25.6 31.7 31.7 30.6 30.6 41.4 41.4 44.2 44.2 42.5 42.5 44.7 44.7 43.3 43.3 49.2 49.2 46.4 46.4 49.4 49.4 48.9 48.9 51.2 51.2 비교예2Comparative Example 2 3.2 3.2 5.1 5.1 4.6 4.6 5.6 5.6 5.1 5.1 6.0 6.0 6.5 6.5 3.2 3.2 5.1 5.1 7.4 7.4 8.0 8.0 8.0 8.0 6.5 6.5 8.8 8.8 실시예3Example 3 33.4 33.4 32.0 32.0 41.0 41.0 36.8 36.8 42.0 42.0 40.5 40.5 42.2 42.2 41.0 41.0 45.8 45.8 42.2 42.2 47.3 47.3 45.6 45.6 47.5 47.5 53.5 53.5 비교예3Comparative Example 3 7.5 7.5 8.5 8.5 7.1 7.1 4.2 4.2 6.0 6.0 2.8 2.8 7.1 7.1 4.2 4.2 6.6 6.6 3.3 3.3 5.2 5.2 4.7 4.7 6.6 6.6 5.7 5.7 실시예4Example 4 36.7 36.7 34.0 34.0 40.7 40.7 37.5 37.5 43.7 43.7 43.6 43.6 48.8 48.8 44.9 44.9 48.6 48.6 48.3 48.3 48.3 48.3 51.4 51.4 51.4 51.4 55.8 55.8 비교예4Comparative Example 4 6.5 6.5 5.1 5.1 8.0 8.0 6.9 6.9 6.9 6.9 4.0 4.0 7.4 7.4 6.0 6.0 3.7 3.7 4.0 4.0 6.0 6.0 4.6 4.6 7.4 7.4 4.0 4.0 실시예5Example 5 36.8 36.8 35.4 35.4 44.0 44.0 38.7 38.7 45.6 45.6 47.0 47.0 44.2 44.2 48.4 48.4 47.5 47.5 50.9 50.9 52.0 52.0 55.7 55.7 53.8 53.8 56.6 56.6 비교예5Comparative Example 5 7.1 7.1 5.2 5.2 6.6 6.6 4.7 4.7 6.6 6.6 5.7 5.7 8.0 8.0 6.0 6.0 6.6 6.6 5.2 5.2 8.0 8.0 5.7 5.7 5.7 5.7 7.1 7.1

상기 표 3은 해수에서의 수질검사 실험결과로 소거율의 단위는 (%)이다.
Table 3 shows the results of water quality test in seawater, the unit of scavenging rate is (%).

표 1과 같은 인공오수의 성분을 갖는 담수중의 인공오수에서의 총질소량과 총인의 감소량을 측정한 결과 비교예들의 경우, 경과시간이 10일 때의 총질소량의 감소량은 54 ~ 69 %, 총인량의 감소량은 25.1 ~ 41.3%의 범위로 나타났으나, 실시예들의 경우, 경과시간이 10일 때의 총질소량의 감소량은 66.7 ~ 74.6 %, 총인량의 감소량은 74.1 ~ 80%의 범위로 나타나 경과일수 초기에 있어서 비교예들에 비하여 총질소 및 총인의 감소량이 커 하천 및 호소 등의 적용시 설치 초기부터 수질정화의 효과를 나타낼 수 있는 것으로 판단된다.As a result of measuring the total nitrogen and total phosphorus reduction in artificial sewage in freshwater with artificial sewage components as shown in Table 1, the total nitrogen reduction in elapsed time was 54 to 69%, The decrease in phosphorus was found to be in the range of 25.1 to 41.3%, but in the case of embodiments, the decrease in total nitrogen when the elapsed time was 10 was 66.7 to 74.6% and the decrease in total phosphorus was in the range of 74.1 to 80%. Compared to the comparative examples in the early days, the total nitrogen and total phosphorus decrease is larger than the comparative examples, it is judged that the effect of water purification from the beginning of the installation when applying the stream and appeal.

아울러, 비교예들은 경과시간이 200일 때의 총질소량의 감소량은 84 ~ 89 %, 총인량의 감소량은 63 ~ 80%의 범위로 나타났으나, 경과시간이 600일인 경우의 총질소량의 감소량은 19 ~ 28 %, 총인량의 감소량은 11 ~ 18%의 범위로 나타나 200일 이후에는 총질소 및 총인의 감소량이 적게 되는 것으로 나타났으나, 실시예의 경우, 경과시간이 200일 때의 총질소량의 감소량은 81.3 ~ 84.7 %, 총인량의 감소량은 81.1 ~ 86.7%의 범위로 나타났으며, 경과시간이 600일인 경우의 총질소량의 감소량은 82.6 ~ 87.1 %, 총인량의 감소량은 84.7 ~ 89%의 범위로 나타나 200일 이후에도 총질소와 총인의 감소량이 유지되는 것으로 나타났다.In addition, in the comparative examples, the amount of decrease in total nitrogen amount in the elapsed time of 200 was 84 to 89%, and the amount of decrease in total phosphorus was 63 to 80%. The decrease in total phosphorus was 19 to 28% and the total phosphorus was in the range of 11 to 18%. After 200 days, the decrease in total nitrogen and total phosphorus was reduced, but in the case of the embodiment, the amount of total nitrogen when the elapsed time was 200 The decrease amount was 81.3 ~ 84.7%, the decrease in total phosphorus ranged from 81.1 to 86.7%, and the decrease in total nitrogen amount was 82.6 ~ 87.1% and the decrease in total phosphorus amount was 84.7 ~ 89% when the elapsed time was 600 days. As a result, the decrease in total nitrogen and total phosphorus was maintained after 200 days.

또한, 표 1과 같은 인공오수의 성분을 갖는 해수중의 인공오수에서의 총질소량과 총인의 감소량을 측정한 결과 비교예들의 경우, 경과시간이 10일 때의 총질소량의 감소량은 4.6 ~ 8.6 %, 총인량의 감소량은 4.2 ~ 5.7 %의 범위로 나타났으나, 실시예들의 경우, 경과시간이 10일 때의 총질소량의 감소량은 31.7 ~ 44.0 %, 총인량의 감소량은 31.6 ~ 38.7 %의 범위로 나타나 경과일수 초기에 있어서 비교예들에 비하여 총질소 및 총인의 감소량이 크게 나타났다.In addition, as a result of measuring the total nitrogen and total phosphorus decrease in the artificial sewage in seawater having the components of artificial sewage as shown in Table 1, in the comparative examples, the decrease in total nitrogen amount when the elapsed time was 10 was 4.6 to 8.6%. The decrease in total phosphorus ranged from 4.2 to 5.7%, but in the case of embodiments, the decrease in total nitrogen at elapsed time ranges from 31.7 to 44.0% and the decrease in total phosphorus ranges from 31.6 to 38.7%. In the early days of the elapsed days, the total nitrogen and the total phosphorus decreased significantly compared to the comparative examples.

더욱이, 경과시간이 지남에 따라 비교예들의 총 질소 및 인의 변화는 처음과 유사한 경향을 나타냈으나, 실시예들은 200일 때의 총질소량 감소량은 38.7 ~ 48.6 %, 총인량의 감소량은 42.2 ~ 50.9 %의 범위로 나타났으나, 경과시간이 600일인 경우의 총질소량의 감소량은 44.0 ~ 53.8 %, 총인량의 감소량은 크게 나타나는 것으로 나타났다.Moreover, as the elapsed time, the total nitrogen and phosphorus changes of the comparative examples showed a similar tendency as the first time, but the examples showed that the total nitrogen reduction amount at 200 was 38.7 to 48.6%, and the total phosphorus reduction amount was 42.2 to 50.9. In the case of the elapsed time of 600 days, the decrease in total nitrogen was 44.0 ~ 53.8% and the decrease in total phosphorus was large.

따라서, 실시예들이 비교예들에 비하여 해수중에서의 수질정화 효과가 우수한 것으로 나타나 담수중에서 뿐만 아니라 해수중에서도 이용이 용인한 것으로 판단된다.Therefore, the embodiments are superior to the comparative examples in water quality purification effect in the sea, it is judged that the use is acceptable not only in fresh water but also in sea water.

이에 수질 정화용 콘크리트를 제조하기 위한 최신 기술인 ‘수질정화용 콘크리트 제조방법’(한국 등록특허공보 제10-0840602호)특허에 따른 제조방법에 비하여 본 발명에 의해 제조된 콘크리트가 경과일수 초기와 장기간의 성능이 우수한 것으로 나타났다.Therefore, the concrete produced by the present invention compared to the manufacturing method according to the latest 'method for producing water purification concrete' (Korea Patent Publication No. 10-0840602), which is a state-of-the-art technology for producing concrete for water purification, has shown that the concrete produced by the present invention has an initial period of time and a long term performance. It was found to be excellent.

더불어, 상기와 같이 본 발명에 의해 제안된 새로운 구조를 적용할 경우 하천 및 호수와 해안 및 항구의 수질정화용 콘크리트 공사 등 수변부에 접하는 콘크리트 제품으로 제조할 시 기존의 콘크리트 제품에 비하여 설치 초기와 장기간에 걸쳐 성능이 우수한 콘크리트 제품을 제공하여 환경오염의 방지와 친환경조성에 크게 기여할 수 있을 것이라 판단된다.
In addition, when applying the new structure proposed by the present invention as described above, when manufacturing the concrete products in contact with the waterfront, such as concrete construction for water purification of rivers, lakes, coasts and harbors in the early stages of installation and long-term It is expected to contribute to the prevention of environmental pollution and the creation of environment-friendly products by providing concrete products with excellent performance.

<실험예 2> 산-알칼리 측정 Experimental Example 2 Acid-Alkali Measurement

상기 실시예 1 내지 5 및 비교예 1 내지 5의 콘크리트를 지름 10cm, 높이 20cm의 원주형 공시체로 제작하여 수중 양생을 실시한 후 공시체 상부에 30 ㎖의 증류수를 살포하여 하부에 흘러나온 증류수의 pH를 KS M 0011 '수용액의 pH 측정 방법'에 준하여 측정하여 표 4에 나타내었다.
After the concrete of Examples 1 to 5 and Comparative Examples 1 to 5 were manufactured into columnar specimens having a diameter of 10 cm and a height of 20 cm, the curing was carried out in water, and then 30 ml of distilled water was sprayed on the specimens to determine the pH of the distilled water flowing out from the bottom. It was measured according to KS M 0011 'Method of measuring pH of aqueous solution' and is shown in Table 4.

<실험예 3> 강도 측정 Experimental Example 3 Strength Measurement

상기 실시예 1 내지 5 및 비교예 1 내지 5의 콘크리트를 실험예 2와 같은 형태의 공시체로 제조하여 재량 28일에서 KS F 2405 '콘크리트 압축강도 시험방법'에 준하여 압축강도를 측정하여 표 4에 나타내었다.
The concrete of Examples 1 to 5 and Comparative Examples 1 to 5 were prepared with specimens of the same form as Experimental Example 2, and the compressive strength was measured according to KS F 2405 'Concrete compressive strength test method' at 28 days of discretion. Indicated.

<실험예 4> 휨강도 측정 Experimental Example 4 Measurement of Flexural Strength

상기 실시예 1 내지 5 및 비교예 1 내지 5의 콘크리트를 가로, 세로 15㎝, 높이 55㎝의 보 공시체로 제조하여 재령 28일에서 KCI-SF-104 '섬유보강 콘크리트의 휨강도 및 휨인성 시험방법'에 준하여 측정하여 표 4 에 나타내었다.
Test method of bending strength and flexural toughness of KCI-SF-104 'fibre-reinforced concrete at 28 days of age by preparing the concrete of Examples 1 to 5 and Comparative Examples 1 to 5 with a horizontal, vertical 15 cm, and 55 cm height specimens It measured according to 'and shown in Table 4.

<실험예 5> 내화학성 실험Experimental Example 5 Chemical Resistance Experiment

상기 실시예 1 내지 5 및 비교예 1 내지 5의 콘크리트를 지름 10cm, 높이 20cm의 원주형 공시체로 제작하여 재령 6개월까지 1%의 황산 용액에 침지시켜 재령별에 따른 중량변화율을 측정하여 표 4에 나타내었다.
The concrete of Examples 1 to 5 and Comparative Examples 1 to 5 were manufactured in columnar specimens having a diameter of 10 cm and a height of 20 cm and immersed in 1% sulfuric acid solution for up to 6 months of age to measure the weight change rate according to age. Shown in

<실험예 6> 동결융해 실험Experimental Example 6 Freeze-thawing Experiment

상기 실시예 1 내지 5 및 비교예 1 내지 5의 콘크리트를 가로, 세로 10cm, 높이 40cm의 공시체로 제작하여 재령 28일에서 동결융해실험을 실시하여 300 싸이클 후의 외관 및 강도변화를 측정하여 표 4에 나타내었다.
The concrete of Examples 1 to 5 and Comparative Examples 1 to 5 were prepared as specimens having a width of 10 cm, a height of 40 cm, and a freeze thaw test at 28 days of age to measure the appearance and strength change after 300 cycles. Indicated.

비교대상comparison target 알칼리용출량(pH)Alkali elution (pH) 압축강도Compressive strength 휨강도Flexural strength 내산성Acid resistance 동결융해저항성Freeze thaw resistance 실시예1Example 1 8.98.9 32.832.8 6.66.6 우수Great 우수Great 비교예1Comparative Example 1 9.59.5 29.429.4 5.75.7 우수Great 우수Great 실시예2Example 2 8.78.7 34.334.3 6.76.7 우수Great 우수Great 비교예2Comparative Example 2 9.69.6 31.131.1 5.85.8 우수Great 우수Great 실시예3Example 3 8.38.3 29.729.7 6.36.3 우수Great 우수Great 비교예3Comparative Example 3 9.19.1 26.626.6 4.94.9 우수Great 우수Great 실시예4Example 4 8.18.1 37.437.4 7.17.1 우수Great 우수Great 비교예4Comparative Example 4 8.98.9 33.333.3 6.26.2 우수Great 우수Great 실시예5Example 5 8.08.0 33.933.9 6.46.4 우수Great 우수Great 비교예5Comparative Example 5 8.78.7 30.130.1 5.65.6 우수Great 우수Great

상기 표 4는 실험예 2 내지 6의 실험결과로써, 압축강도와 휨강도는 MPa이다.Table 4 is an experimental result of Experimental Examples 2 to 6, the compressive strength and the flexural strength is MPa.

표 4를 분석하면, 비교예들은 알칼리용출량의 경우에 있어서 pH는 8.7 ~ 9.5로 약알칼리성으로 나타났으나, 본 발명에 따른 수질정화 콘크리트의 경우 8.0 ~ 8.9로 중성에 가까운 것으로 나타났다.Analyzing Table 4, the comparative examples showed a weak alkalinity in the case of alkali elution amount of 8.7 to 9.5, but was close to neutral at 8.0 to 8.9 for the water purification concrete according to the present invention.

아울러, 압축강도와 휨강도의 경우에 있어서도 실시예들의 경우 비교예들에 비하여 비하여 10.2 ~ 28.5 % 정도 증진되는 것을 알 수 있다.In addition, it can be seen that even in the case of compressive strength and flexural strength, the embodiments are increased by about 10.2 to 28.5% compared to the comparative examples.

또한, 내산성 및 동결융해 저항성 실험 결과는 비교예들과 실시예들 모두 우수한 내구성능을 갖는 것으로 나타났다.
In addition, the results of the acid resistance and freeze thaw resistance test results showed that both the comparative examples and the examples have excellent durability.

Claims (4)

콘크리트의 제조방법에 있어서,
성형조성물 전체 부피의 5.5 ~ 7.6%의 결합재와, 성형조성물 전체 부피의 61.3 ~ 79.6%의 골재와, 성형조성물 전체 부피의 0.2 ~ 0.3 %의 혼화제와, 성형조성물 전체 부피의 3.4 ~ 4.8%의 미생물 배양액과 전체부피의 4.3 ~ 5.1%의 물과 잔량으로서 공기를 포함하여 이루어지는 성형조성물을 준비하는 혼합단계와;
상기 성형조성물을 습도 80 ~ 90%, 온도 10 ~ 50℃ 조건으로 양생실에서 12 ~ 24 시간 습윤 양생한 후, 기건상태로 상온에서 7 ~ 30일 동안 양생시키는 양생단계;를 포함하여 구성되되,
상기 미생물 배양액은 미생물과 배양액을 1:2의 중량비로 혼합하고,
상기 골재는 폐콘크리트 순환골재, 부순돌, 버텀애시, 슬래그 골재, 화산석 중 선택된 1종 또는 2 내지 5종의 혼합물로 이루어지며,
상기 결합재는 시멘트, 플라이애쉬, 슬래그파우더, 고로슬래그미분말 중 선택된 1종 또는 2 내지 4종의 혼합물로 이루어진 것을 특징으로 하는,
미생물배양액을 이용한 수질정화 콘크리트의 제조방법.
In the manufacturing method of concrete,
5.5 to 7.6% binder in the total volume of the molding composition, 61.3 to 79.6% aggregate in the total volume of the molding composition, 0.2 to 0.3% admixture in the total volume of the molding composition, and 3.4 to 4.8% microorganisms in the total volume of the molding composition. Mixing step of preparing a molding composition comprising the culture medium and the air and the remaining amount of 4.3 ~ 5.1% of the total volume;
Consists of curing the molding composition in the condition of humidity 80 ~ 90%, temperature 10 ~ 50 ℃ wet curing in the curing room for 12 to 24 hours, and curing for 7 to 30 days at room temperature in air condition;
The microbial culture medium is mixed with the microorganism and the culture medium in a weight ratio of 1: 2,
The aggregate is composed of one or two to five kinds of waste concrete recycling aggregate, crushed stone, bottom ash, slag aggregate, volcanic stone selected from,
The binder is characterized by consisting of a mixture of cement, fly ash, slag powder, blast furnace slag fine powder or one or two to four kinds,
Method for producing water purification concrete using microbial culture medium.
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KR101188100B1 (en) * 2012-05-30 2012-10-08 동산콘크리트산업(주) Water purification concrete using micro-organisms and solution system and manufacturing methods of it
KR101336711B1 (en) 2012-02-17 2013-12-04 전남대학교산학협력단 A composition of cement zero nature-friendly dry mortar
KR101553044B1 (en) * 2014-02-27 2015-09-15 동산콘크리트산업(주) Water Purification Bio Concrete using Hidrophilic Fiber and Industrial By-Products and Manufacturing Methods of it
KR101620075B1 (en) * 2015-03-27 2016-05-13 동산콘크리트산업(주) Mortar for 3D Printing, Concrete and Manufacturing Method of the Concrete using it
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KR101336711B1 (en) 2012-02-17 2013-12-04 전남대학교산학협력단 A composition of cement zero nature-friendly dry mortar
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