KR20060097429A - Manufacturing methods of protection a block of an ecosystem and the block that use of corrosiveness aggregate of favoring environment - Google Patents
Manufacturing methods of protection a block of an ecosystem and the block that use of corrosiveness aggregate of favoring environment Download PDFInfo
- Publication number
- KR20060097429A KR20060097429A KR20050019757A KR20050019757A KR20060097429A KR 20060097429 A KR20060097429 A KR 20060097429A KR 20050019757 A KR20050019757 A KR 20050019757A KR 20050019757 A KR20050019757 A KR 20050019757A KR 20060097429 A KR20060097429 A KR 20060097429A
- Authority
- KR
- South Korea
- Prior art keywords
- weight
- block
- corrosive
- aggregate
- mixture
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B18/00—Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
- C04B18/02—Agglomerated materials, e.g. artificial aggregates
- C04B18/021—Agglomerated materials, e.g. artificial aggregates agglomerated by a mineral binder, e.g. cement
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B18/00—Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
- C04B18/04—Waste materials; Refuse
- C04B18/16—Waste materials; Refuse from building or ceramic industry
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B18/00—Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
- C04B18/04—Waste materials; Refuse
- C04B18/30—Mixed waste; Waste of undefined composition
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B20/00—Use of materials as fillers for mortars, concrete or artificial stone according to more than one of groups C04B14/00 - C04B18/00 and characterised by shape or grain distribution; Treatment of materials according to more than one of the groups C04B14/00 - C04B18/00 specially adapted to enhance their filling properties in mortars, concrete or artificial stone; Expanding or defibrillating materials
- C04B20/02—Treatment
- C04B20/026—Comminuting, e.g. by grinding or breaking; Defibrillating fibres other than asbestos
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/02—Compositions 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
- C04B28/04—Portland cements
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2111/00—Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
- C04B2111/00017—Aspects relating to the protection of the environment
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Ceramic Engineering (AREA)
- Civil Engineering (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Processing Of Solid Wastes (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
Abstract
본 발명은 음식물 찌꺼기와 건설폐기물의 재활용 과정에서 생산되는 순환골재의 생산과정에서 발생하는 건설폐토사를 이용한 친환경 부식성 골재의 제조방법에 관한 것으로, The present invention relates to a method for producing environmentally corrosive aggregates using construction waste soil generated during the production of recycled aggregates produced during the recycling of food waste and construction wastes.
이물질이 제거된 음식물 찌꺼기를 혼합형 분쇄기를 이용하여 1∼2mm의 메쉬 크기로 분쇄하는 단계; Crushing the food debris from which foreign matters have been removed to a mesh size of 1 to 2 mm using a mixed grinder;
상기와 같이 분쇄된 음식물 찌꺼기 60∼90 중량%와 포틀랜드 시멘트 5∼20 중량% 및 건설폐토사 5∼20 중량%를 휘저음 하여 균일하게 혼합하는 단계; Stirring by mixing 60 to 90% by weight of the ground food waste, 5 to 20% by weight of Portland cement, and 5 to 20% by weight of construction waste soil;
상기 혼합물을 입도가 1∼5mm인 입상물로 건조되어 고형화하는 단계; Drying the mixture to a granule having a particle size of 1 to 5 mm to solidify the mixture;
상기의 입상물을 건조과정을 통하여 경화시켜 제조된 부식성 골재의 고형화 완성단계;Solidification of the corrosive aggregate prepared by curing the granular material through a drying process;
상기 부식성골재 10∼30 중량%와 건설폐기물 중간처리 과정에서 생산되는 순환골재 중 크기가 6∼15mm 메쉬인 비교적 굵은 순환골재 60∼80 중량%, 포틀랜드 시멘트 10∼20 중량% 및 성형성 부여에 필요한 양의 수분을 혼합하는 단계 및 이 혼합물을 블록으로 성형하는 단계를 포함하여 제조됨을 특징으로 하는 것이다.10 to 30% by weight of the corrosive aggregates and 60 to 80% by weight of relatively thick recycled aggregates of 6 to 15mm mesh, 10 to 20% by weight of Portland cement, and moldability, among the recycled aggregates produced during the intermediate treatment of construction waste. Mixing the amount of moisture and molding the mixture into blocks.
음식물 찌꺼기, 건설폐토사, 생태블럭 Food waste, construction waste soil, eco block
Description
본 발명은 음식물 찌꺼기와 건설폐기물의 재활용 과정에서 생산되는 순환골재의 생산과정에서 발생하는 건설폐토사를 이용한 친환경 부식성 골재의 제조방법에 관한 것으로, 더욱 상세하게는 이물질을 제거하고 분쇄과정을 거친 음식물 찌꺼기와 포틀랜드 시멘트 및 건설폐기물의 재활용 과정에서 생산되는 순환골재의 생산과정에서 발생하는 건설폐토사를 이용하여 입상으로 고형화시킨 친환경 부식성 골재를 제조하고, 상기의 고형화된 친환경 부식성 골재를 이용한 생태계 보호용 블럭(이하 "생태블럭"이라 합니다)의 제조방법 및 그 블럭에 관한 것이다.The present invention relates to a method for producing environmentally corrosive aggregates using construction waste soil generated during the production of recycled aggregates produced during the recycling of food wastes and construction wastes. And eco-friendly corrosive aggregates solidified into granules by using construction waste soil produced in the production process of recycled aggregates produced during the recycling process of cement and construction wastes. It is related to a method of manufacturing " ecological block "
최근 우리 나라는 음식물, 종이, 나무 등과 같은 유기성 폐기물 증가 및 각종 건축물의 신축이나 도로의 확장으로 인한 건설폐기물의 발생으로 쓰레기 종류 및 그 양이 급격히 증가하고 있다.In recent years, our country has rapidly increased the type and amount of garbage due to the increase of organic waste such as food, paper, wood, construction waste caused by the construction of new buildings and the expansion of roads.
이들 중 특히 다량의 수분을 함유하는 음식물 찌꺼기는 자연상태에서 쉽사리 부패하여 악취 및 썩은 물을 발생하는 등 이것의 보관과 운반에서 어려움이 매우 많은 실정이다.Among these, food wastes containing a large amount of water are easily decayed in a natural state, so that odors and rotten water are generated.
우리 나라의 음식물 찌꺼기는 2003년 기준으로 1일 발생량이 11,400톤에 이르고 있으며, 이것의 처리방법으로서 생활쓰레기와 혼합하여 매립하거나 가축용의 사료 또는 퇴비화로 재활용되고 있으나 0.5∼6% 정도로 염분의 농도가 매우 높은 우리나라 음식물 찌꺼기는 그 처리에서 근본적인 문제를 내포하고 있는 실정이다.As of 2003, the amount of food waste in our country is 11,400 tons per day. As a treatment method, it is mixed with household waste or landfilled or recycled as feed or compost for livestock, but the concentration of salt is about 0.5 ~ 6%. The food waste of Korea, which is very high, has a fundamental problem in its disposal.
그리고 건설폐기물은 매립되거나 재활용하는 과정에서 골재로 생산되어 이용되고 있으며, 2003년 기준으로 1일 발생량은 145,000톤에 이르고 있다.Construction waste is produced and used as aggregate in the process of being landfilled or recycled. As of 2003, the daily generation amount is 145,000 tons.
종래부터 음식물 찌꺼기의 재활용 방법은 다양하게 제안돼 왔으며, 그 일례로 국내 특허공개번호 제10-2001-38363호(2001. 2. 15. 공개)는 음식물 찌꺼기와 폐석회를 이용한 토양 생성방법을 제안하면서 음식물 찌꺼기에 함유된 다량의 수분을 제거한 후 부패시키는 공정, 부패한 음식물 찌꺼기에 엠바도모나스 박테리아균과 이콜라이 마르시아노스 박테리아균을 5∼10g 혼합시킨 후 65∼80℃를 유지하며 14-28일간 숙성시켜 일반적인 흙과 나무재, 기타 잎사귀 49%를 넣어 휘저음 하는 방법이 제안되었다.In the past, various methods of recycling food waste have been proposed. For example, Korean Patent Publication No. 10-2001-38363 (published on Feb. 15, 2001) proposes a soil production method using food waste and waste lime. While removing a large amount of water contained in food wastes, the process of decaying, mixing 5-10g of embadomonas bacteria and E. coli marcianos bacteria in the debris of food debris and then aged 65-80 ℃ while aging for 14-28 days A method of stirring the soil by adding 49% of general soil, wood, and other leaves was suggested.
또한, 국내 특허공개번호 제10-2000-24612호(2000. 5. 6. 공개)는 음식물 찌꺼기를 건조 발효시켜 사료로 이용하거나 찌꺼기를 건조시켜 바닥포장재의 혼합제로 이용할 수 있도록 하였다.In addition, Korean Patent Publication No. 10-2000-24612 (published May 6, 2000) was used to dry fermentation of food wastes for use as feed or to dry the residues to be used as a mixture of the floor packaging material.
그리고 건설폐기물은 재활용 과정에서 순환골재로 생산되어 바닥의 다짐과 포장용으로 극히 일부만 활용되고 있고, 용도의 다양성 부재로 상당량은 그대로 매립되고 있는 실정에 있으나, 이 또한 매립지 확보의 어려움 등으로 인하여 재활용을 통한 생산성 재고는 이루고 있지 못한 실정에 있다.In addition, construction waste is produced as recycled aggregate in the recycling process, and only a part of it is used for compaction and packing of floors, and a considerable amount of landfill is still buried due to the lack of diversity of use. Productivity inventory through the situation is not achieved.
한편, 하천은 인간의 삶과 문화에 지대한 영향을 미치며 생태적으로 중요한 가치를 지닌 자연자원임에도 불구하고 급속한 도시화와 산업화로 인하여 장기적이며 구체적인 환경성 문제를 고찰하지 못하고 단순한 치수 위주의 관행적 하천정비만이 진행되어 왔다.On the other hand, although rivers are natural resources that have a great impact on human life and culture and have ecologically important values, they cannot be considered for long-term and specific environmental problems due to rapid urbanization and industrialization. It has been going on.
그러나 최근 하천의 친자연형 정비를 위한 다양한 시도가 이루어지고 있으나 기존의 콘크리트 하천 정비 방식에서 구조적 안정성을 유지하는 동시에 하천 고유의 생태계 보전이나 복원이 용이한 방법의 적용은 아직까지 미흡한 실정이다.Recently, however, various attempts have been made to maintain the natural nature of rivers. However, there is still insufficient application of methods that are easy to preserve or restore the unique ecosystem while maintaining structural stability in existing concrete river maintenance methods.
특히 친환경적 하천정비에 적합한 소재의 개발 및 이를 이용한 공법 개발은 특정지역의 수리학적 특성은 물론 생태적, 경관적 특성 등 기반환경에 대한 장기간의 실험적 감시 결과를 필요로 하기 때문에 현장에 부합된 완성된 공법의 개발에는 많은 어려움이 수반되어 왔다.In particular, the development of materials suitable for environment-friendly river maintenance and the development of construction methods using them require a long-term experimental monitoring of the environment, including ecological and landscape characteristics, as well as the hydraulic characteristics of a specific area. Has been accompanied by many difficulties.
따라서, 본 발명은 이러한 종래의 결점을 해소하기 위하여 안출된 것으로, 다량의 음식물 찌꺼기와 건설폐기물 재활용에 있어서 공정이 간단하고 환경친화성인 제품의 개발을 목적으로 한다. Accordingly, the present invention has been made to solve such a conventional drawback, and aims at the development of a simple and environmentally friendly product in the process of recycling a large amount of food waste and construction waste.
이에 본 발명은 분쇄한 음식물 찌꺼기와 포틀랜드 시멘트, 건설폐토사를 혼 합하는 것으로서 제조되는 부식성 골재와 이를 이용하여 제조되는 자연부식성의 생태블럭을 제공하기에 이르렀다.Accordingly, the present invention has been made to provide a corrosive aggregate produced by mixing the ground food waste, Portland cement, construction waste soil, and the natural corrosive ecological block produced by using the same.
본 발명은 제1 양태로, 이물질이 제거된 음식물 찌꺼기를 혼합형 분쇄기를 이용하여 1∼2mm의 메쉬 크기로 분쇄하는 단계; 상기와 같이 분쇄된 음식물 찌꺼기 60∼90 중량%와 포틀랜드 시멘트 5∼20 중량% 및 건설폐토사 5∼20 중량%를 교반하여 균일하게 혼합하는 단계; 상기 혼합물을 입도가 1∼5mm인 입상물로 고형화하는 단계; 상기의 입상물을 건조과정을 통하여 경화시키는 단계를 포함하는 친환경의 부식성 골재 제조방법을 제공한다.According to a first aspect of the present invention, there is provided a step of crushing the food debris from which foreign substances have been removed into a mesh size of 1 to 2 mm using a mixed grinder; Stirring and uniformly mixing 60 to 90% by weight of the ground food waste, 5 to 20% by weight of Portland cement, and 5 to 20% by weight of construction waste soil; Solidifying the mixture into granules having a particle size of 1 to 5 mm; It provides an environmentally friendly corrosive aggregate manufacturing method comprising the step of curing the granular material through a drying process.
이와 같은 제조방법에 있어서, 수거된 음식물 찌꺼기에서 쇠, 비닐류 등의 이물질을 제거하는 방법으로는 체가름 방법, 전자석을 이용한 철편 분리, 인력선별 및 고속 풍력 선별하는 방법을 사용한다.In such a manufacturing method, as a method for removing foreign matters such as iron and vinyl from the collected food wastes, a sifting method, iron strip separation using an electromagnet, attraction screening and high speed wind screening methods are used.
이물질을 제거한 음식물 찌꺼기는 믹서 분쇄기를 이용하여 분쇄입자의 크기가 1∼2mm의 메쉬를 통과할 수 있을 정도로 분쇄하는 단계를 수행한다.The food debris from which the foreign matter is removed is pulverized using a mixer grinder so that the size of the pulverized particles can pass through a mesh having a size of 1 to 2 mm.
건설현장에서 수거된 폐기물을 중간처리 재활용 과정에서 불순물을 제거한 후 굵은 순환골재(6∼15mm 정도의 크기)와 건설폐토사(0.3mm 이하)를 준비한다.The waste collected at the construction site is cleaned of impurities during the intermediate treatment recycling process, and then the coarse recycled aggregate (size of about 6 to 15 mm) and the construction waste soil (0.3 mm or less) are prepared.
분쇄된 음식물 찌꺼기 60∼90 중량%와 포틀랜드 시멘트 5∼20 중량% 및 건설폐토사(오니, pH 9∼11) 5∼20 중량%를 휘저음 과정(혼합)을 통하여 펠렛이나 입상화시키기 위해 휘저음 하는 단계를 수행한다.Stir to pellet or granulate 60 to 90% by weight of ground food waste, 5 to 20% by weight of Portland cement and 5 to 20% by weight of construction waste soil (sludge, pH 9-11) through agitation (mixing). Follow the steps.
상기 휘저음 단계에서는 탈수효과, 악취제거가 이루어지는 것으로 휘저음 시 포틀랜드 시멘트에 다량의 수분이 필요하며 수화반응과정에서 발생하는 열에 의한 멸균효과가 나타난다.In the stirring step, dehydration effect, odor removal is performed, a large amount of water is required in the Portland cement during the stirring, and the sterilization effect by heat generated during the hydration reaction appears.
또한, 시멘트의 pH(12.5)이며, 건설폐토사 오니는 pH(9∼11)이고, 음식물 찌꺼기의 pH(3∼7)는 휘저음 과정에서 중화반응에 따른 악취의 소멸효과가 나타나므로 탈수효과 및 악취제거 효과를 제공하는 것이다.In addition, the pH of the cement (12.5), the construction waste soil sludge is pH (9-11), the food waste pH (3-7) of the deodorizing effect due to the neutralization reaction in the stirring process, the dehydration effect and It is to provide a deodorant effect.
음식물 찌꺼기와 포틀랜드 시멘트 및 건설폐토사를 휘저음 하여 입상화가 완료되면 자연건조하는 것으로 하절기에는 1∼3일, 동절기에는 7일 정도 자연건조하며, 스팀을 이용한 건초처리의 경우에는 습도가 60∼70%가 유지되도록 하고 온도를 150∼180℃로 유지하면서 12∼24시간 경과시켜 1∼5mm의 입상크기를 갖도록 고형화 완성단계를 수행하여 부식성 골재 입상물을 수득한다.When the granulation is completed by stirring food waste, Portland cement, and construction waste soil, it is dried naturally for 1 ~ 3 days in summer and 7 days in winter, and the humidity is 60 ~ 70% for hay treatment using steam. 12 to 24 hours while maintaining the temperature at 150 ~ 180 ℃ to perform a solidification completion step to have a granule size of 1 to 5mm to obtain a corrosive aggregate granules.
상기와 같은 방법으로 제조된 입상물은 강도가 20∼30kg/㎠ 정도를 제공하게 되므로 이를 포장하여 생태블럭을 제조할 수 있는 재료로 유통할 수 있게 된다. 즉, 본 발명은 제2 양태로 생태블럭의 각종 형태로 정형화될 수 있는 부식성 골재를 제공한다. Since the granular material prepared by the above method provides strength of about 20 to 30 kg / cm 2, it can be packaged and distributed as a material capable of producing an ecological block. That is, the present invention provides a corrosive aggregate that can be shaped into various forms of ecological blocks in a second aspect.
제3 양태로, 본 발명은 전술한 제조방법에 따라 제조된 부식성골재 10∼30 중량%와 건설폐기물 중간처리 과정에서 생산되는 순환골재 중 크기가 6∼15mm 메쉬인 비교적 굵은 순환골재 60∼80 중량%, 포틀랜드 시멘트 10∼20 중량% 및 성형성 부여에 필요한 양의 수분을 혼합하는 단계 및 이 혼합물을 블록으로 성형하는 단계를 포함하는, 생태블럭 제조방법을 제공한다.In a third aspect, the present invention is 10 to 30% by weight of the corrosive aggregate produced according to the above-described manufacturing method and 60 to 80 weight of relatively thick recycled aggregate having a size of 6 to 15 mm mesh of recycled aggregate produced in the middle of construction waste treatment. %, 10 to 20% by weight of Portland cement and an amount of water necessary for imparting moldability, and a step of molding the mixture into blocks.
이와 같은 방법을 통하여 성형된 생태블럭은 하천에 설치된 후 음식물 찌꺼기가 위치한 부분이 자연상태의 박테리아나 곰팡이의 호기성 미생물에 의한 부식, 소멸(풍화작용) 과정이 이뤄지면서 식물의 먹이사슬로 이용하도록 하는 것이다.The ecological block molded through this method is installed in the river, where the food residues are used as the food chain of plants as the process of corrosion and extinction (weathering) caused by aerobic microorganisms of natural bacteria or fungi occurs. will be.
또한, 10∼30% 정도의 기공 비율을 갖는 기공을 통하여 식물의 뿌리가 식생되도록 하는 것이다.In addition, the root of the plant is to be vegetated through the pore having a pore ratio of about 10 to 30%.
상기 포틀랜드 시멘트는 강도를 결정하는 요인으로 작용하므로 배합비율을 다변화하여 강도를 조절할 수 있는 것이며, 상기와 같은 방법으로 제조하는 경우에는 강도가 100∼150kg/㎠ 정도를 제공하게 된다.Since the portland cement acts as a factor for determining the strength, it is possible to control the strength by varying the blending ratio, and when manufactured in the same manner as described above, the strength is about 100 to 150 kg / cm 2.
또한, 강도를 향상시키기 위해서는 제조가 완성된 생태블럭의 표면에 포틀랜드 시멘트를 코팅하는 횟수를 증가시킴에 따라서 강도를 향상시킬 수 있게 되는 것이다.In addition, in order to increase the strength it is possible to improve the strength by increasing the number of times the portland cement is coated on the surface of the finished ecological block.
제4 양태로, 본 발명은 전술한 제조방법에 따라 제조되어 기공율이 10∼30% 정도인 생태블록을 제공한다.In a fourth aspect, the present invention provides an ecological block having a porosity of about 10-30% by being prepared according to the above-described manufacturing method.
이와 같은 생태블록은 해안이나 강 또는 하천, 호수 등 수로의 유실을 방지하고 보호하기 위해 설치된 옹벽이나 석축, 호안블록 등에 시공될 수 있다. Such an ecological block may be installed in a retaining wall, a stone wall, a raft block, etc. installed to prevent and protect the loss of waterways such as coasts, rivers, rivers and lakes.
한편, 본 발명은 전술한 제조 방법에 따라 제조할 때 포틀랜드 시멘트를 코팅하지 않고 외부로 드러나도록 하는 예를들면, 누드화분과 같은 다양한 제품으로 제조하는 것이 가능하다.On the other hand, the present invention can be produced in a variety of products, such as for example nude nude to be exposed to the outside without coating Portland cement when manufactured according to the above-described manufacturing method.
본 발명은 다량으로 배출되는 음식물 찌꺼기와 건설폐기물을 재활용하여 해안이나 강 또는 하천, 호수 등 수로의 유실을 방지하고 생태 보호에 유용한 본 발명의 생태블럭은 음식물 찌꺼기를 그대로 활용하여 수분을 대체하므로 수분에 의한 환경오염을 방지할 수 있으며, 포틀랜드 시멘트와 건설폐토사의 탈수효과 및 악취제거와 산도를 중성화시킬 수 있다. The present invention recycles food waste and construction waste discharged in large quantities to prevent the loss of waterways such as coasts, rivers, rivers, lakes, etc. The ecological block of the present invention useful for ecological protection replaces moisture by using food waste as it is Environmental pollution can be prevented, and the dewatering effect of portland cement and construction waste soil, odor removal and neutralization can be neutralized.
또한, 다양한 형태의 생태블럭을 제조하여 설치된 후 자연상태의 박태리아나 곰팡이의 호기성 미생물에 의한 장기간의 부식, 소멸 등과 같은 풍화작용이 이루어지면서 식물의 먹이사슬로 이용될 수 있어 자원재활용과 환경보호 측면에서 매우 바람직하다.In addition, after manufacturing and installing various types of ecological blocks, weathering such as long-term corrosion and extinction caused by aerobic microorganisms of natural bacteria and fungi can be used as a food chain of plants. Very preferred.
Claims (5)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR20050019757A KR100667163B1 (en) | 2005-03-09 | 2005-03-09 | Manufacturing methods of protection a block of an ecosystem and the block that use of corrosiveness aggregate of favoring environment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR20050019757A KR100667163B1 (en) | 2005-03-09 | 2005-03-09 | Manufacturing methods of protection a block of an ecosystem and the block that use of corrosiveness aggregate of favoring environment |
Publications (2)
Publication Number | Publication Date |
---|---|
KR20060097429A true KR20060097429A (en) | 2006-09-14 |
KR100667163B1 KR100667163B1 (en) | 2007-01-12 |
Family
ID=37629209
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR20050019757A KR100667163B1 (en) | 2005-03-09 | 2005-03-09 | Manufacturing methods of protection a block of an ecosystem and the block that use of corrosiveness aggregate of favoring environment |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR100667163B1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN115075081A (en) * | 2022-04-18 | 2022-09-20 | 长沙学院 | Pavement mainly built by using construction waste and kitchen waste and construction method |
-
2005
- 2005-03-09 KR KR20050019757A patent/KR100667163B1/en not_active IP Right Cessation
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN115075081A (en) * | 2022-04-18 | 2022-09-20 | 长沙学院 | Pavement mainly built by using construction waste and kitchen waste and construction method |
Also Published As
Publication number | Publication date |
---|---|
KR100667163B1 (en) | 2007-01-12 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP3268324B1 (en) | Method of dust control | |
AU639044B2 (en) | Ash and paper treatment | |
KR100917452B1 (en) | The methods to manufacture an environmentally friendly, highly durable and high-functional concrete utilizing multi-component-blended cement, na type - artificial zeolite and new-materials for performance improvement | |
JP2008308396A (en) | Water-containing composition, utilization and treatment method, and non-polluting water-resistant treated object | |
KR102294033B1 (en) | Eco-friendly concrete composition | |
CN102503253A (en) | Lake and river sludge processing method | |
CN110156426B (en) | Method for utilizing oyster shells as curing material for residual mud and muck | |
CN101575183A (en) | Processing method of incinerated flying ash | |
CN101704650B (en) | Resource recycling method of calcium-adding drying sludge | |
KR100667163B1 (en) | Manufacturing methods of protection a block of an ecosystem and the block that use of corrosiveness aggregate of favoring environment | |
KR20060097427A (en) | Favoring environment corrosiveness aggregate of use scraps of food and the manufacturing methods | |
KR100378528B1 (en) | Cover Soil Composition for the Modification of Land Fill Soil Capable of Lowering Ordor and Preventing Vermination | |
KR101836823B1 (en) | Method for solidifying sewage sludge using fallen leaves | |
KR100753852B1 (en) | Food dirt, the pro-environment block where a microorganism was used and this production technique | |
CN106927656A (en) | A kind of method of Fenton sludge filler | |
CN106142318A (en) | A kind of slow-release oxygen material layer of concave herbaceous field and preparation method thereof | |
KR100900024B1 (en) | Lowering offensive odor manhole using shell and recycled aggregate and manufacturing method thereof | |
CN113826528B (en) | High-permeability spongy soil and preparation method and application thereof | |
CN113994855B (en) | Application of high-permeability sponge soil in plant maintenance | |
RU2819792C1 (en) | Method of restoring technogenically disturbed urbanized lands | |
EP0837039B1 (en) | Construction of material for carrier structure for group of effective microorganisms and group of products | |
Shahinuzzaman et al. | Plastic Waste Bottle in Mortar Block for River Bank Protection Work | |
El-Haggar | Industrial solid waste utilization and disposal | |
Rosli et al. | Sewage sludge recycling and disposal | |
KR101221637B1 (en) | Cover soil composition for the land fill soil |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
E902 | Notification of reason for refusal | ||
E701 | Decision to grant or registration of patent right | ||
GRNT | Written decision to grant | ||
FPAY | Annual fee payment |
Payment date: 20100201 Year of fee payment: 4 |
|
LAPS | Lapse due to unpaid annual fee |