KR100691428B1 - A color aggregate and artificial fish reef comprising binder for industrial wastes, and method of producing the structures - Google Patents
A color aggregate and artificial fish reef comprising binder for industrial wastes, and method of producing the structures Download PDFInfo
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- KR100691428B1 KR100691428B1 KR1020040049171A KR20040049171A KR100691428B1 KR 100691428 B1 KR100691428 B1 KR 100691428B1 KR 1020040049171 A KR1020040049171 A KR 1020040049171A KR 20040049171 A KR20040049171 A KR 20040049171A KR 100691428 B1 KR100691428 B1 KR 100691428B1
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- industrial waste
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- 239000002440 industrial waste Substances 0.000 title claims abstract description 80
- 238000000034 method Methods 0.000 title abstract description 17
- 241000251468 Actinopterygii Species 0.000 title 1
- 239000011230 binding agent Substances 0.000 title 1
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 50
- 239000007864 aqueous solution Substances 0.000 claims abstract description 40
- 238000004519 manufacturing process Methods 0.000 claims abstract description 29
- 239000002699 waste material Substances 0.000 claims abstract description 26
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 23
- 229920000193 polymethacrylate Polymers 0.000 claims abstract description 19
- 239000007787 solid Substances 0.000 claims abstract description 17
- 239000011083 cement mortar Substances 0.000 claims abstract description 16
- 230000005484 gravity Effects 0.000 claims abstract description 16
- 239000010883 coal ash Substances 0.000 claims abstract description 15
- 239000004848 polyfunctional curative Substances 0.000 claims abstract description 12
- 239000004576 sand Substances 0.000 claims abstract description 11
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims abstract description 9
- 239000000292 calcium oxide Substances 0.000 claims abstract description 9
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims abstract description 9
- 239000002689 soil Substances 0.000 claims abstract description 9
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims abstract description 8
- 235000011941 Tilia x europaea Nutrition 0.000 claims abstract description 8
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 claims abstract description 8
- 239000004571 lime Substances 0.000 claims abstract description 8
- 239000002893 slag Substances 0.000 claims abstract description 8
- 239000000049 pigment Substances 0.000 claims abstract description 6
- 239000004568 cement Substances 0.000 claims description 27
- 238000002156 mixing Methods 0.000 claims description 18
- 239000000203 mixture Substances 0.000 claims description 12
- 239000000835 fiber Substances 0.000 claims description 8
- 238000010304 firing Methods 0.000 claims description 3
- 238000010298 pulverizing process Methods 0.000 claims description 3
- 239000008187 granular material Substances 0.000 claims 1
- 239000002994 raw material Substances 0.000 abstract description 8
- 239000000126 substance Substances 0.000 abstract description 8
- 230000000694 effects Effects 0.000 abstract description 7
- OYPRJOBELJOOCE-BKFZFHPZSA-N Calcium-45 Chemical compound [45Ca] OYPRJOBELJOOCE-BKFZFHPZSA-N 0.000 abstract description 3
- 230000007613 environmental effect Effects 0.000 abstract description 2
- 230000008569 process Effects 0.000 description 11
- 238000010586 diagram Methods 0.000 description 10
- 238000006703 hydration reaction Methods 0.000 description 9
- 238000006243 chemical reaction Methods 0.000 description 7
- 239000011575 calcium Substances 0.000 description 6
- 238000010276 construction Methods 0.000 description 6
- 238000007711 solidification Methods 0.000 description 6
- 230000008023 solidification Effects 0.000 description 6
- 238000001723 curing Methods 0.000 description 5
- 239000000047 product Substances 0.000 description 5
- 238000004064 recycling Methods 0.000 description 5
- 230000008901 benefit Effects 0.000 description 4
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 4
- 239000004567 concrete Substances 0.000 description 4
- 238000003912 environmental pollution Methods 0.000 description 4
- 230000036571 hydration Effects 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 230000000704 physical effect Effects 0.000 description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 3
- 229910052791 calcium Inorganic materials 0.000 description 3
- 239000003638 chemical reducing agent Substances 0.000 description 3
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 239000013535 sea water Substances 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- 230000006641 stabilisation Effects 0.000 description 3
- 238000011105 stabilization Methods 0.000 description 3
- 238000010521 absorption reaction Methods 0.000 description 2
- 230000002776 aggregation Effects 0.000 description 2
- 238000004220 aggregation Methods 0.000 description 2
- 239000010882 bottom ash Substances 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 235000011116 calcium hydroxide Nutrition 0.000 description 2
- 239000000378 calcium silicate Substances 0.000 description 2
- 229910052918 calcium silicate Inorganic materials 0.000 description 2
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 description 2
- 230000015271 coagulation Effects 0.000 description 2
- 238000005345 coagulation Methods 0.000 description 2
- 229920001577 copolymer Polymers 0.000 description 2
- 238000011049 filling Methods 0.000 description 2
- 239000010881 fly ash Substances 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 230000036632 reaction speed Effects 0.000 description 2
- 231100000331 toxic Toxicity 0.000 description 2
- 230000002588 toxic effect Effects 0.000 description 2
- 241000258957 Asteroidea Species 0.000 description 1
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 1
- 238000004566 IR spectroscopy Methods 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- BUACSMWVFUNQET-UHFFFAOYSA-H dialuminum;trisulfate;hydrate Chemical compound O.[Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O BUACSMWVFUNQET-UHFFFAOYSA-H 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 230000003628 erosive effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 239000000383 hazardous chemical Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 229910052745 lead Inorganic materials 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 238000000465 moulding Methods 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000007655 standard test method Methods 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
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Classifications
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- 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
- C04B18/022—Agglomerated materials, e.g. artificial aggregates agglomerated by an organic binder
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K61/00—Culture of aquatic animals
- A01K61/70—Artificial fishing banks or reefs
-
- 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
-
- 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
-
- E—FIXED CONSTRUCTIONS
- E02—HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
- E02B—HYDRAULIC ENGINEERING
- E02B3/00—Engineering works in connection with control or use of streams, rivers, coasts, or other marine sites; Sealings or joints for engineering works in general
- E02B3/04—Structures or apparatus for, or methods of, protecting banks, coasts, or harbours
- E02B3/043—Artificial seaweed
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Ceramic Engineering (AREA)
- Structural Engineering (AREA)
- Civil Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Biodiversity & Conservation Biology (AREA)
- Animal Husbandry (AREA)
- Zoology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Marine Sciences & Fisheries (AREA)
- Ocean & Marine Engineering (AREA)
- Mechanical Engineering (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
- Processing Of Solid Wastes (AREA)
- Artificial Fish Reefs (AREA)
Abstract
본 발명은 제 1 폴리메타크릴레이트 수용액(고형분; 40±1%, 점도; 200±100cps, 비중(20/4℃); 1.12±0.02, pH; 7±1) 10 내지 20부피%, 제 2 폴리메타크릴레이트 수용액(고형분; 40±1%, 점도; 250±100cps, 비중(20/4℃); 1.13±0.02, pH; 7±1) 10 내지 20부피%, 알루미늄 설페이트 30중량% 수용액 5 내지 15부피%, 산화칼슘 5중량% 수용액 1 내지 10 부피%, 물 45 내지 65부피%를 포함하는 산업폐기물 처리용 고화제와, 시멘트모르타르와, 석탄회, 폐주물사, 슬랙, 폐석회 및 준설토로 구성된 군으로부터 선택한 어느 하나의 산업폐기물과, 색소를 포함하는 유색 골재 및 인공 어초와, 이들 유색 골재 및 인공 어초의 제조 방법에 관한 것이다.In the present invention, the first polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 200 ± 100 cps, specific gravity (20/4 ° C.); 1.12 ± 0.02, pH; 7 ± 1) 10 to 20% by volume, second Polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 250 ± 100 cps, specific gravity (20/4 ° C.); 1.13 ± 0.02, pH; 7 ± 1) 10 to 20% by volume, aluminum sulfate 30% by weight aqueous solution 5 It consists of an industrial waste treatment hardener comprising from 15% by volume to 15% by weight, 5% by weight aqueous solution of calcium oxide, and 45% to 65% by volume water, cement mortar, coal ash, waste foundry sand, slag, waste lime and dredged soil. It relates to any industrial waste selected from the group, colored aggregates containing artificial pigments and artificial reefs, and methods for producing these colored aggregates and artificial reefs.
본 발명에 의한 유색 골재 및 인공 어초는 특정의 고화제를 사용하여 산업폐기물을 원료로 하여 제조되므로, 제조원가가 절감되며, 또한 유해물질 방출이 방지되므로 환경보호의 효과를 기대할 수 있다.Since the colored aggregate and artificial reefs according to the present invention are manufactured using industrial waste as a raw material using a specific solidifying agent, the manufacturing cost can be reduced, and the emission of harmful substances can be prevented, so the effect of environmental protection can be expected.
Description
도 1은 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 원료로 유색골재를 제작하는 공정에 대한 공정흐름도이다.1 is a process flow diagram for a process for producing colored aggregates from industrial wastes using the solidifying agent for industrial waste treatment of the present invention.
도 2는 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 섬유 외피에 채워 구조물을 제작하는 공정에 대한 공정흐름도이다.Figure 2 is a process flow diagram for a process of manufacturing a structure by filling the industrial waste with fiber waste using the industrial waste treatment solidifying agent of the present invention.
도 3은 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 원료로 해서 제조된 구조물(보도블럭)의 개략도이다.Figure 3 is a schematic diagram of a structure (walking block) manufactured using industrial waste as a raw material using the solidifying agent for industrial waste treatment of the present invention.
도 4는 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 원료로 해서 제조된 해중림 구조물의 조립 개략도이다.4 is an assembly schematic diagram of a deforestation structure manufactured using industrial waste as a raw material using the solidifying agent for treating industrial waste of the present invention.
도 5는 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 원료로 해서 제조된 해중림 구조물의 개략도이다.5 is a schematic diagram of a deforestation structure manufactured using industrial waste as a raw material using the solidifying agent for treating industrial waste of the present invention.
도 6은 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 원료로 해서 제조된 불가사리 형태의 해중림 구조물 개략도이다.6 is a schematic view of a sea starch structure in the form of starfish manufactured using industrial waste as a raw material using the solidifying agent for treating industrial waste of the present invention.
도 7은 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 원료로 해서 제조된 해중림 구조물의 개략도이다.7 is a schematic diagram of a deforestation structure manufactured using industrial waste as a raw material using the solidifying agent for industrial waste treatment of the present invention.
도 8은 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 원료로 해서 제조된 해중림 구조물의 조립 개략도이다.8 is an assembly schematic diagram of a deforestation structure manufactured using industrial waste as a raw material using the solidifying agent for treating industrial waste of the present invention.
도 9는 본 발명의 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 섬유 외피에 충전하여 제조된 해중림 구조물의 개략도이다.Figure 9 is a schematic diagram of the deforestation structure produced by filling the industrial shell with industrial waste using the solidifying agent for industrial waste treatment of the present invention.
본 발명은 산업폐기물 처리용 고화제를 사용하여 얻은 유색 골재 및 인공 어초와, 이들 구조물의 제조 방법에 관한 것으로, 더욱 구체적으로는 석탄회, 폐주물사, 슬랙, 폐석회 및 준설토로 구성된 군으로부터 선택한 어느 하나의 산업폐기물을 특정의 산업폐기물 처리용 고화제를 사용하여 얻은 친환경적 유색 골재 및 인공 어초와, 이들 구조물의 제조 방법에 관한 것이다.The present invention relates to colored aggregates and artificial reefs obtained using a solidifying agent for industrial waste treatment, and to a method for manufacturing these structures, more specifically, any one selected from the group consisting of coal ash, waste foundry sand, slag, waste lime and dredged soil. The present invention relates to environmentally friendly colored aggregates and artificial reefs obtained by using industrial solidifying agents for treating certain industrial wastes, and to methods of manufacturing these structures.
산업폐기물 중 석탄회는 우리나라 열병합 발전소에서 연간 약 200만톤 정도 발생하여 대부분 매립에 의존하여 지금까지 처리해 왔으나 매립으로 인해 환경오염 뿐 아니라 동식물의 중금속 오염에 심각한 영향을 주고 있다. 따라서 산업부산물인 석탄회를 사용하여 구조물을 제조함은 경제적인 이점 이외에 환경보호의 측면에서도 큰 효과가 있다.Among the industrial wastes, coal ash is generated at about 2 million tons per year in cogeneration plants in Korea, and most of them have been treated so far depending on the landfill. However, the landfill has serious effects on not only environmental pollution but also heavy metal pollution of animals and plants. Therefore, manufacturing the structure using coal ash, an industrial by-product, has a great effect in terms of environmental protection in addition to economic advantages.
산업폐기물을 재활용하는데 있어서 문제점은 그것을 사용하여 일정한 구조물을 제작하였을 때 용도에 맞는 규정강도를 얻기가 어려운 점과, 또한 산업폐기물 특히 광산 폐기물인 광미의 경우 유해한 중금속 물질들을 다량으로 함유하고 있어서 광미를 원료로 하여 제작된 구조물로부터 중금속이 방출되어 2차적인 환경오염을 일으킬 수 있다는 점을 들 수 있다.The problem with recycling industrial wastes is that it is difficult to obtain the required strength when using a specific structure to make certain structures, and also because industrial wastes, especially mine tailings, which are mine wastes, contain large amounts of harmful heavy metals. Heavy metals may be released from structures manufactured as raw materials, causing secondary environmental pollution.
일반적으로 건축 및 토목에 사용하는 각종 구조물은 자갈, 모래, 시멘트와 물을 적당량 혼합하는 시멘트 콘크리트 제조방법을 이용한다. 이러한 구조물은 제작 완료 후 육상에서는 상당한 내구성을 지속하나 수중에서는 2 내지 3년 경과 후 시멘트 특성의 수화작용을 억제할 수 없어 시간이 갈수록 마모 진행이 빠르게 이루어진다. 수화현상은 시멘트의 주성분인 칼슘(Ca)과 물(H2O)의 상호반응으로 수산화칼슘(Ca(OH)2)이 발생되는 현상을 의미하는데, 수화 반응된 수산화칼슘(Ca(OH)2)은 pH 12 내지 13의 강알카리로서 수생식물 생장서식에 치명적이며 2차적인 오염의 원인이다.In general, various structures used in construction and civil engineering use a method of manufacturing cement concrete in which an appropriate amount of gravel, sand, cement, and water is mixed. Such structures continue to have considerable durability on land after completion of their fabrication, but they can not inhibit the hydration of cement properties after two to three years in water, so that wear progresses rapidly over time. Hydration refers to a phenomenon in which calcium hydroxide (Ca (OH) 2 ) is generated by the interaction between calcium (Ca) and water (H 2 O), which are the main components of cement, and the hydrated calcium hydroxide (Ca (OH) 2 ) Strong alkalis with a pH of 12 to 13 are fatal to aquatic plant growth and cause secondary contamination.
일반적으로 시멘트 구조물에서 발생하는 유해물질들은 오염 요인으로 작용하고 있으며, 특히 시멘트 구조물이 하천 수나 해수에 장기간 노출되었을 때 수생 동식물 서식에 막대한 영향을 미치게 되므로 시멘트 구조물에 의한 환경오염을 최소화할 수 있는 방법이 요구되고 있다. 모래나 자갈을 이용하여 시멘트와 함께 구조물을 만들 경우 시멘트의 주성분인 칼슘이 수화반응을 일으켜 강 염기성 물질이 용출되고, 이러한 시멘트 구조물이 수중이나 해수에 장기간 노출될 경우 주변 환경을 오염시킬 뿐만 아니라 구조물의 강도를 떨어뜨려 수명을 단축시킨다. 따라서 해수에 장기간 노출이 되는 소파(消波)블록(TTP)이나 인공어초 등의 구조물에 있어서 시멘트로부터 방출되는 유해 폐기물을 최소화하는 것이 매우 중요하다.In general, harmful substances generated in cement structures act as a contaminant. Especially, when cement structures are exposed to river water or sea water for a long time, they have a great influence on aquatic flora and fauna, and thus the method of minimizing environmental pollution caused by cement structures. This is required. When sand and gravel are used to make a structure with cement, calcium, the main component of cement, causes hydration reactions to elute strong basic substances, and if the cement structure is exposed to water or sea water for a long time, it not only contaminates the surrounding environment but also the structure. It reduces the strength of the product and shortens its lifespan. Therefore, it is very important to minimize harmful wastes emitted from cement in structures such as sofa blocks (TTP) or artificial reefs that are exposed to seawater for a long time.
따라서 본 발명이 이루고자 하는 기술적 과제는, 특정의 고화제를 사용함으로써 산업폐기물을 재활용하여 얻은 유색 골재 및 인공 어초를 제공하는 데 있다.
또한 본 발명의 다른 기술적 과제는 상기 유색골재 및 인공어초를 제조하는 방법을 제공하는 데 있다. Therefore, the technical problem to be achieved by the present invention is to provide colored aggregates and artificial reefs obtained by recycling industrial waste by using a specific solidifying agent.
In addition, another technical problem of the present invention is to provide a method for producing the colored aggregate and artificial reef.
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상기 기술적 과제를 달성하기 위하여, 본 발명은 제 1 폴리메타크릴레이트 수용액(고형분; 40±1%, 점도; 200±100cps, 비중(20/4℃); 1.12±0.02, pH; 7±1) 10 내지 20부피%, 제 2 폴리메타크릴레이트 수용액(고형분; 40±1%, 점도; 250±100cps, 비중(20/4℃); 1.13±0.02, pH; 7±1) 10 내지 20부피%, 알루미늄 설페이트 30중량% 수용액 5 내지 15부피%, 산화칼슘 5중량% 수용액 1 내지 10 부피%, 물 45 내지 65부피%를 포함하는 산업폐기물 처리용 고화제 (일명 "GRG21"이라고도 함)와, 시멘트모르타르와, 석탄회, 폐주물사, 슬랙, 폐석회 및 준설토로 구성된 군으로부터 선택한 어느 하나의 산업폐기물과, 색소를 포함하는 유색 골재를 제공한다.
또한 본 발명은 제 1 폴리메타크릴레이트 수용액(고형분; 40±1%, 점도; 200±100cps, 비중(20/4℃); 1.12±0.02, pH; 7±1) 10 내지 20부피%, 제 2 폴리메타크릴레이트 수용액(고형분; 40±1%, 점도; 250±100cps, 비중(20/4℃); 1.13±0.02, pH; 7±1) 10 내지 20부피%, 알루미늄 설페이트 30중량% 수용액 5 내지 15부피%, 산화칼슘 5중량% 수용액 1 내지 10 부피%, 물 45 내지 65부피%를 포함하는 산업폐기물 처리용 고화제와, 시멘트모르타르와, 석탄회, 폐주물사, 슬랙, 폐석회 및 준설토로 구성된 군으로부터 선택한 어느 하나의 산업폐기물을 혼합하여 섬유 외피에 넣어 양생시킨 인공 어초를 제공한다.
본 발명의 구조물에 있어서, 상기 산업폐기물 처리용 고화제, 시멘트 및 산업폐기물의 중량 혼합비가 1:1:3.5인 것이 바람직하다.In order to achieve the above technical problem, the present invention is the first polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 200 ± 100cps, specific gravity (20/4 ℃); 1.12 ± 0.02, pH; 7 ± 1) 10-20% by volume, second polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 250 ± 100 cps, specific gravity (20/4 ° C.); 1.13 ± 0.02, pH; 7 ± 1) 10-20% by volume 5 to 15% by volume aqueous solution of aluminum sulfate, 1 to 10% by volume aqueous solution of 5% calcium oxide, and 45 to 65% by volume water solidifying agent for industrial waste treatment (also called "GRG21"), Provided are colored aggregates containing any one of industrial waste selected from the group consisting of cement mortar, coal ash, waste foundry sand, slag, waste lime, and dredged soil.
In addition, the present invention is the first polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 200 ± 100 cps, specific gravity (20/4 ℃); 1.12 ± 0.02, pH; 7 ± 1) 10 to 20% by volume, 2 polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 250 ± 100 cps, specific gravity (20/4 ° C.); 1.13 ± 0.02, pH; 7 ± 1) 10 to 20% by volume, 30% by weight aluminum sulfate solution Industrial waste treatment hardener comprising 5 to 15% by volume, 5% to 5% by weight aqueous solution of calcium oxide, and 45 to 65% by volume of water, cement mortar, coal ash, waste foundry sand, slag, waste lime and dredged soil One of the industrial wastes selected from the group consisting of is mixed to provide a cured artificial reef in a fiber shell.
In the structure of the present invention, it is preferable that the weight mixing ratio of the solidifying agent, cement and industrial waste for industrial waste treatment is 1: 1: 3.5.
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상기 다른 기술적 과제를 달성하기 위하여 본 발명은,The present invention to achieve the above other technical problem,
상기 산업폐기물 처리용 고화제, 시멘트모르타르, 산업폐기물 및 색소를 정량하고 이송하는 단계;Quantifying and transporting the industrial waste treatment hardener, cement mortar, industrial waste and pigments;
상기 산업폐기물 처리용 고화제, 시멘트모르타르, 산업폐기물 및 색소를 혼합하여 혼합물을 제조하는 단계;Preparing a mixture by mixing the industrial waste treatment hardener, cement mortar, industrial waste, and a pigment;
상기 제조된 혼합물을 일정 크기의 조립체로 성형하고 소성하는 단계;Molding and firing the prepared mixture into an assembly having a predetermined size;
상기 소성된 혼합물을 분쇄하는 단계를 포함하는 유색골재의 제조방법을 제공한다.It provides a method for producing a colored aggregate comprising the step of pulverizing the calcined mixture.
또한, 상기의 또다른 기술적 과제를 달성하기 위하여 본 발명은, In addition, the present invention to achieve the above another technical problem,
상기 산업폐기물 처리용 고화제, 시멘트모르타르 및 산업폐기물을 정량하고 이송하는 단계;Quantifying and transporting the industrial waste treatment hardener, cement mortar and industrial waste;
상기 정량된 산업폐기물 처리용 고화제, 시멘트모르타르, 산업폐기물을 혼합하여 혼합물을 제조하는 단계; Preparing a mixture by mixing the quantitative industrial waste treatment hardener, cement mortar, and industrial waste;
상기 제조된 혼합물을 일정한 형태를 가진 섬유 외피에 투입하여 고화 양생하는 단계를 포함하는 인공어초의 제조방법을 제공한다.It provides a method for producing artificial reefs comprising the step of curing the prepared mixture to the fiber shell having a predetermined form.
이하, 본 발명의 산업폐기물 처리용 고화제를 사용하여 제조한 유색골재 및 인공어초와, 그것의 제조 방법을 보다 구체적으로 설명한다. 우선 본 발명에 사용하는 산업폐기물 처리용 고화제를 설명한다. Hereinafter, the colored aggregate and artificial reef prepared using the solidifying agent for industrial waste treatment of the present invention, and a manufacturing method thereof will be described in more detail. First, the solidifying agent for industrial waste treatment used in the present invention will be described.
본 발명에서 사용하는 고화제는 최근 심각한 사회문제가 되고 있는 산업폐기물, 준설토 등 부산물 및 폐기물을 재활용하는데 사용하기 위하여 개발된 고화제로서, 액상이므로 운반이 용이하다. 그리고, 상기 고화제는 시멘트의 수화반응에 의해 생성되는 Ca(OH)2와 반응하여 칼슘실리케이트 수화물을 형성하는 포졸란 반응을 통하여 산업폐기물을 응고시킨다.The solidifying agent used in the present invention is a solidifying agent developed for use in recycling by-products and wastes, such as industrial waste, dredged soil, which has become a serious social problem in recent years. The solidifying agent solidifies industrial waste through a pozzolanic reaction which reacts with Ca (OH) 2 produced by the hydration of cement to form calcium silicate hydrate.
또한, 본 발명에서 사용하는 산업폐기물 처리용 고화제는 물로 희석하여 사용할 수 있으며, 농도를 변화시킴으로써 응고 반응속도를 쉽게 조절할 수 있다. 예를 들면 재해용, 군용시설, 터널공사 등에 있어서는 고화제를 고농도로 사용하여 반응 속도를 빠르게 하고, 보도블럭, 벽돌제작에는 저농도로 사용하여 반응속도를 느리게 할 수 있다.In addition, the solidifying agent for industrial waste treatment used in the present invention can be diluted with water, and the coagulation reaction rate can be easily adjusted by changing the concentration. For example, in the case of disasters, military installations, tunnel construction, etc., the solidification agent is used at a high concentration to increase the reaction speed, and in the case of sidewalk blocks and bricks, the reaction rate can be used to reduce the reaction speed.
본 발명에서 사용하는 산업폐기물 처리용 고화제는 특수한 수화반응을 일으키기 때문에 종래 소재에 비하여 폭넓은 반응 온도 범위를 가지며, 고온, 다습, 한냉지 등 에서의 건설시공에도 용이하게 응용할 수 있다.Industrial waste treatment solidifying agent used in the present invention has a wide reaction temperature range compared to the conventional material because it causes a special hydration reaction, it can be easily applied to the construction work in high temperature, high humidity, cold districts and the like.
또한, 본 발명에서 사용하는 산업폐기물 처리용 고화제는 시멘트의 수화반응으로 생성되는 Ca(OH)2와 반응하여 알루미늄 및 칼슘 실리케이트를 수화물로 변화시키는 포졸란 반응을 일으켜 콘크리트의 물성을 개선할 수 있으므로, 상기 고화제를 사용하여 제작된 구조물은 일반적인 콘크리트보다 높은 강도를 나타낸다. 경제적인 면에 있어서, 본 발명은 산업폐기물을 이용하여 구조물을 제작하기 때문에 제조원가를 대폭 절감할 수 있다. 본 발명에서 이용하는 산업폐기물은 석탄회, 폐주물사, 슬랙, 폐석회 및 준설토로 구성된 군으로부터 선택한 어느 하나이다. In addition, since the solidifying agent for industrial waste treatment used in the present invention reacts with Ca (OH) 2 generated by the hydration reaction of cement, it causes a pozzolanic reaction to convert aluminum and calcium silicate into a hydrate, thereby improving physical properties of concrete. In addition, the structure manufactured using the hardener exhibits higher strength than general concrete. In terms of economics, the present invention can significantly reduce the manufacturing cost because the structure is manufactured using industrial waste. Industrial waste used in the present invention is any one selected from the group consisting of coal ash, waste foundry sand, slag, waste lime and dredged soil.
산업폐기물을 재활용하는데 있어서 가장 문제가 되는 점은 산업폐기물에 포함된 유해물질의 방출이다. 본 발명의 연구자들은 상기 고화제와 석탄회, 폐주물사, 슬랙, 폐석회 및 준설토 등으로 구성된 군으로부터 선택한 어느 하나의 산업폐기물을 사용하여 유해물질의 방출을 최소화할 수 있는 경제적이면서도 친환경적인 구조물을 제작하였다. 또한 섬유 외피에 상기 고화제와 산업폐기물 등을 넣고 고화 양생하여 해양 구조물을 제작하는 경우, 구조물의 수화반응으로 인한 해양오염을 최소화할 수 있다.The biggest problem in recycling industrial waste is the release of hazardous substances contained in industrial waste. The researchers of the present invention produced an economical and environmentally friendly structure that can minimize the emission of harmful substances by using any one industrial waste selected from the group consisting of the hardener and coal ash, waste foundry sand, slag, waste lime and dredged soil. . In addition, in the case of manufacturing a marine structure by solidifying and curing the solidifying agent and industrial waste in the fiber shell, it is possible to minimize the marine pollution caused by the hydration reaction of the structure.
상기 고화제의 주요성분인 제 1 폴리메타크릴레이트 수용액 (고형분; 40±1%, 점도; 200±100cps, 비중(20/4℃); 1.12±0.02, pH; 7±1)은 카르복시산 공중합체가 39 내지 41중량% 포함된 수용액이며, 시멘트용 감수제 및 유동화제로서 LG화학에서 제품명 CP-WB로 시판하고 있는 제품이다. 그리고 제 2 폴리메타크릴레이트 수용액 (고형분; 40±1%, 점도; 250±100cps, 비중(20/4℃); 1.13±0.02, pH; 7±1)도 카르복시산 공중합체가 39 내지 41중량% 포함된 수용액이며, 역시 시멘트용 감수제 및 유동화제로서 LG화학에서 제품명 CP-WR로 시판하고 있는 제품이다. 상기 제 1 폴리메타크릴레이트 수용액 및 제 2 폴리메타크릴레이트 수용액은 시멘트 클링커 입자에 물리적 또는 화학적인 흡착을 통하여 입체 장애 효과와 정전기적 반발에 의한 입자간의 분산을 유도하여 감수 효과 및 초기 수화반응 속도를 지연시켜 작업성을 개선시킨다.The first polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 200 ± 100 cps, specific gravity (20/4 ° C.); 1.12 ± 0.02, pH; 7 ± 1), which is the main component of the solidifying agent, is a carboxylic acid copolymer. Is an aqueous solution containing 39 to 41% by weight, and is a product marketed under the product name CP-WB by LG Chemical as a water reducing agent and fluidizing agent for cement. The second polymethacrylate aqueous solution (solid content; 40 ± 1%, viscosity; 250 ± 100 cps, specific gravity (20/4 ° C.); 1.13 ± 0.02, pH; 7 ± 1) also contains 39 to 41% by weight of carboxylic acid copolymer. It is an aqueous solution included and is also marketed under the product name CP-WR by LG Chem as a water reducing agent and fluidizing agent for cement. The first polymethacrylate aqueous solution and the second polymethacrylate aqueous solution induce the dispersion between particles by steric hindrance effect and electrostatic repulsion through physical or chemical adsorption to cement clinker particles, thereby reducing the erosion effect and initial hydration rate. To improve workability.
본 발명에서 사용하는 고화제에서 제 1 폴리메타크릴레이트 수용액은 감수제로서의 역할이 크고, 전체 고화제 중 10 내지 20 부피%인 것이 바람직하며, 12 내지 18 부피%인 것이 더욱 바람직한데, 10 부피% 미만이면 충분한 고화가 일어나지 못하므로 바람직하지 못하고, 20부피%를 초과하면 과다 사용으로 인한 제조원가 상승 및 폐기물의 안정화를 오히려 방해하므로 바람직하지 못하다.In the solidifying agent used in the present invention, the first polymethacrylate aqueous solution has a large role as a water reducing agent, preferably 10 to 20% by volume, more preferably 12 to 18% by volume, of 10% by volume. If less than not enough solidification does not occur, it is not preferable, and if it exceeds 20% by volume is rather undesirable because it hinders the increase in manufacturing cost and stabilization of waste due to overuse.
본 발명의 고화제에서 제 2 폴리메타크릴레이트 수용액은 유동화제로서의 역할이 크고, 전체 고화제 중 10 내지 20 부피%인 것이 바람직하며, 12 내지 18 부피%인 것이 더욱 바람직한데, 10 부피% 미만이면 충분한 고화가 일어나지 못하므로 바람직하지 못하고, 20부피%를 초과하면 과다 사용으로 인한 제조원가 상승 및 폐기물의 안정화를 오히려 방해하므로 바람직하지 못하다.In the solidifying agent of the present invention, the second polymethacrylate aqueous solution has a large role as a fluidizing agent, preferably 10 to 20% by volume, and more preferably 12 to 18% by volume, of less than 10% by volume of the total solidifying agent. This is not preferable because it does not cause sufficient solidification, and if it exceeds 20% by volume, it is not preferable because it hinders the increase in manufacturing cost and stabilization of waste due to overuse.
따라서, 제 1 및 제 2 폴리메타크릴레이트 수용액은 산업폐기물의 적절한 고화 및 안정화를 위해서 상기와 같이 균형있는 비율을 유지하는 것이 좋다. Therefore, the first and second polymethacrylate aqueous solution is preferably maintained in a balanced ratio as described above for proper solidification and stabilization of industrial waste.
알루미늄 설페이트 30중량% 수용액은 응고작용을 하며, 전체 고화제 중 5 내지 15 부피%인 것이 바람직하고, 8 내지 12 부피%인 것이 더욱 바람직한데, 5 부피% 미만이면 응고가 충분히 일어나지 못하므로 바람직하지 않고, 15 부피%를 초과하면 침전현상이 일어나므로 바람직하지 않다.The aqueous solution of 30% by weight of aluminum sulfate coagulates, and is preferably 5 to 15% by volume of the total solidifying agent, and more preferably 8 to 12% by volume, but less than 5% by volume is not preferable because solidification does not occur sufficiently. If not more than 15% by volume, precipitation occurs, which is not preferable.
산화칼슘 5중량% 수용액은 시멘트 응고반응인 포졸란 반응에 영향을 미쳐서 물성을 개선시키고 수산화칼슘을 통하여 pH를 조절하는 작용을 하며, 전체 고화제 중 1 내지 10 부피%인 것이 바람직하고, 3 내지 7 부피%인 것이 더욱 바람직한데, 1부피% 미만이면 폐기물의 응집이 충분히 일어나지 못하므로 바람직하지 못하고, 10부피%를 초과하면 물성개선 및 pH 조절을 오히려 방해하므로 바람직하지 않다.5% by weight aqueous solution of calcium oxide affects the pozzolan reaction, which is a cement coagulation reaction, to improve physical properties and to adjust pH through calcium hydroxide, preferably 1 to 10% by volume of the total solidifying agent, and 3 to 7% by volume. It is more preferable that the amount is less than 1% by volume, which is not preferable because the aggregation of waste does not occur sufficiently, and when it exceeds 10% by volume, it is not preferable because it hinders physical property improvement and pH control.
물은 고화제 각 성분의 혼합을 원활히 하고 또한 폐기물 응집에 영향을 미치는 것으로, 45 내지 65 부피%인 것이 바람직하고, 50 내지 60 부피%인 것이 더욱 바람직한데, 45 부피% 미만이면 고화제의 전체 제조 원가가 상승할 뿐만 아니라 각 성분의 혼합이 원활하지 않으며, 65부피%를 초과하면 폐기물의 응집이 잘 일어나지 않아서 바람직하지 않다. Water facilitates the mixing of each component of the solidifying agent and affects waste flocculation, preferably 45 to 65% by volume, more preferably 50 to 60% by volume, and less than 45% by volume of the total amount of the solidifying agent. Not only does the manufacturing cost rise, but the mixing of each component is not smooth, and if it exceeds 65% by volume, it is not preferable because the aggregation of waste does not occur well.
본 발명의 구조물 제조에 있어서, 산업폐기물 처리용 고화제, 시멘트 및 산업폐기물의 중량 혼합비는 1:1:3.5인 것이 바람직한데, 이러한 혼합비율에서 폐기물의 고화가 효과적으로 일어나며 일정 수준 이상의 강도도 유지된다.In the manufacture of the structure of the present invention, it is preferable that the weight mixing ratio of the solidifying agent, cement and industrial waste for industrial waste treatment is 1: 1: 3.5, and solidification of the waste occurs effectively at such a mixing ratio, and the strength above a certain level is maintained. .
구조물의 용도에 맞게 성분을 조절할 수 있으며, 또한 용도에 따라 다양한 형태의 구조물을 제작할 수 있다. 아래 표 1은 이러한 구조재 성분에 따른 특징 및 용도를 나타낸 것이다.The components can be adjusted to suit the purpose of the structure, and various types of structures can be manufactured according to the use. Table 1 below shows the features and uses of these structural components.
도 1은 본 발명에 사용하는 고화제를 이용하여 산업폐기물을 고화시키고, 이를 소성 및 분쇄하여 유색 골재를 제작하는 공정을 나타내는 공정 흐름도이다. 이러한 과정을 거쳐 생산된 유색골재는 철도 공사용 자갈 등 각종 토목 및 건설 공사에 활용할 수 있으며, 산업폐기물을 재활용하므로 제조원가가 저렴하다.1 is a process flow diagram illustrating a process of solidifying industrial waste using a solidifying agent used in the present invention, firing and pulverizing the same, and manufacturing colored aggregates. Colored aggregate produced through this process can be utilized in various civil and construction works, such as gravel for railroad construction, and manufacturing costs are low because industrial waste is recycled.
도 2는 본 발명에 사용하는 고화제와 산업폐기물과 시멘트모르타르을 혼합하고, 이 혼합물을 섬유 외피에 넣어 구조물을 제작하는 공정을 나타내는 공정 흐름도이다. 도 2에서와 같이 본 발명에 따른 구조물 제작방법을 이용하여 인공어초를 만들 경우, 기존 구조물 제작방법보다 시멘트로부터 방출되는 유독물질을 크게 줄일 수 있는 장점이 있고, 단시일 내에 포자가 접착하고 수생동식물이 자생할 수 있는 환경을 제공하므로 친환경적인 효과도 기대할 수 있는 장점이 있다.FIG. 2 is a process flow diagram illustrating a process of mixing a solidifying agent, industrial waste, and cement mortar used in the present invention, and putting the mixture into a fiber shell to form a structure. When the artificial reef is made using the structure manufacturing method according to the present invention as shown in Figure 2, there is an advantage that can significantly reduce the toxic substances emitted from the cement than the existing structure manufacturing method, the spores adhere to within a short time Since it provides an environment in which it can grow naturally, there is an advantage that an eco-friendly effect can be expected.
도 3 내지 도 9는 다양한 마대 모양 및 거푸집 형태에 따라 다양하게 제작될 수 있는 구조물의 형태를 나타낸 것이다.3 to 9 show the shape of the structure that can be produced in various ways according to the shape of the form and form.
이하, 실시 예를 통하여 본 발명을 더욱 상세히 설명하기로 한다. 이들 실시 예는 단지 본 발명을 예시하기 위한 것이며, 본 발명의 보호 범위가 이들 실시 예에 의해 제한되는 것은 아니다.Hereinafter, the present invention will be described in more detail with reference to the following examples. These examples are only for illustrating the present invention, and the protection scope of the present invention is not limited by these examples.
실시예Example
<고화제의 제조><Production of Solidifying Agent>
아래 표 2와 같이 각 성분을 혼합하여 산업폐기물 처리용 고화제(GRG21)를 제조하였다.Each component was mixed as shown in Table 2 below to prepare a solidifying agent for treating industrial waste (GRG21).
<구조물 제작 및 물성 측정><Structure Fabrication and Property Measurement>
산업폐기물로서 발전소에서 배출되는 석탄회(플라이 애쉬(fly ash) 및 바텀 애쉬(bottom ash)) 1,000kg, 상기 표 2의 비율로 제조한 고화제(GRG21) 20kg와 시멘트 모르타르 250kg(시멘트: 25kg)을 물과 혼합하여 구조물(공시체)를 제작하였다. 구조물(공시체) 제작과 양생은 시멘트 모르타르 압축강도 표준시험방법(KSL 5105)에 규정된 제작법과 양생방법에 의해 수행하였다.1,000 kg of coal ash (fly ash and bottom ash) discharged from the power plant as industrial waste, 20 kg of solidifying agent (GRG21) prepared in the ratio of Table 2 and 250 kg of cement mortar (cement: 25 kg) The structure (sample) was produced by mixing with water. The construction and curing of the structure (test specimen) were carried out by the manufacturing method and curing method specified in the Standard Test Method for Cement Mortar Compressive Strength (KSL 5105).
다만, 공시체 샘플 A 및 B의 경우 전체 석탄회 중 플라이 애쉬의 함량이 90% 이상이 되도록 함량을 조절하였고, 공시체 샘플 C 및 D의 경우에는 바텀 애쉬의 함량이 90% 이상이 되도록 함량을 조절하였다.However, in the case of specimen samples A and B, the content was adjusted so that the content of fly ash in the total coal ash was 90% or more, and in the case of specimen samples C and D, the content of the bottom ash was adjusted to be 90% or more.
압축강도 측정용 공시체는 고화제와 물의 혼합비 1:200과 1:300에 대하여 각각 12개씩 총24개를 제작하여 표준양생 하였으며, 28일 경과 후 압축강도 측정시험법(KSL 5105)에 의해 압축강도를 측정하였다. 측정 결과를 표 3 및 표 4에 나타내 었다. 표 3은 공시체(혼합비 1:200)의 압축강도(kg/cm2)를 나타낸 것이다.Compressive strength test specimens were prepared by twenty four (12) for the mixing ratio of solidifying agent and water at 1: 200 and 1: 300, respectively. After 28 days, the compressive strength was measured by the compressive strength test (KSL 5105). Was measured. The measurement results are shown in Table 3 and Table 4. Table 3 shows the compressive strength (kg / cm 2 ) of the specimen (mixture ratio 1: 200).
표 3에서 보는 바와 같이, 혼합비가 1:200일 때 최대 압축강도는 199.2kg/cm2(A-8)이었고 최소압축강도는 107.5kg/cm2(A-10)이었으며, 평균압축강도는 141.4kg/cm2이었다. 표 3의 결과로부터 시료채취장소에 따라 압축강도의 편차가 심하다는 것을 알 수 있었다. 아래 표 4는 공시체(혼합비 1:300)의 압축강도(kg/cm2)를 나타낸 것이다.As shown in Table 3, when the mixing ratio is 1: 200, the maximum compressive strength was 199.2kg / cm 2 (A-8), the minimum compressive strength was 107.5kg / cm 2 (A-10), and the average compressive strength was 141.4. kg / cm 2 . From the results in Table 3, it can be seen that the variation in compressive strength is severe depending on the sampling location. Table 4 below shows the compressive strength (kg / cm 2 ) of the specimen (mixing ratio 1: 300).
표 4에서 보는 바와 같이, 혼합비가 1:300일 때 최대압축강도는 125.9kg/cm2(B-5)이었고, 최소압축강도는 99.9kg/cm2(B-3)이었으며, 평균압축강도는 117.6kg/cm2이었다. 표 3과 표 4의 결과를 비교해보면, 고화제와 물의 혼합비가 1:300일 때 압축강도의 편차가 1:200인 경우보다 상대적으로 적다는 것을 알 수 있었다. As shown in Table 4, when the mixing ratio is 1: 300, the maximum compressive strength was 125.9kg / cm 2 (B-5), the minimum compressive strength was 99.9kg / cm 2 (B-3), and the average compressive strength was 117.6 kg / cm 2 . Comparing the results of Table 3 and Table 4, it can be seen that when the mixing ratio of the hardener and water is 1: 300, the variation in compressive strength is relatively smaller than that of 1: 200.
또한, 다양한 형태의 입방체 몰드(210×100×60m3)를 KSF4004에 따라 제작한 후 공시체의 압축강도(kg/cm2), 흡수량(%) 및 단위중량(kg/cm2)을 측정하였으며, 그 결과를 표 5, 표 6 및 표 7에 정리하였다.In addition, various types of cube molds (210 × 100 × 60m 3 ) were prepared according to KSF4004, and then the compressive strength (kg / cm 2 ), absorption (%) and unit weight (kg / cm 2 ) of the specimens were measured. The results are summarized in Table 5, Table 6 and Table 7.
상기와 같이 실험을 실시한 결과, 발전소에서 배출된 석탄회의 품질은 물리적 성질과 화학적 성분은 비교적 양호한 것으로 판단되었다. 고화제 : 시멘트 : 석탄회의 최적 중량 배합비는 1 : 1 : 3.5가 적절한 것으로 나타났다.As a result of the experiment as described above, the quality of coal ash discharged from the power plant was determined to be relatively good physical properties and chemical components. Hardener: Cement: Coal ash optimum weight ratio of 1: 1: 3.5 was found to be appropriate.
고화제를 사용하지 않은 공시체는 양생과정에 여러가지 물질이 용출되어 부유물질이 나타났으며 압축강도도 사용한 경우보다 30 내지 50% 낮았다. 그리고, 공시체 강도의 편차가 20 내지 30%로 나타나는 것은 사용 시료의 품질이 문제이므로 경화체 제조시 석탄회의 균일한 품질작업이 사전에 필요한 것으로 판단되었다.The specimen without the solidifying agent was suspended in various materials during curing, resulting in suspended solids and 30-50% lower than the compressive strength. In addition, since the quality of the sample used is a problem in which the variation in the specimen strength is 20 to 30%, it was determined that uniform quality work of coal ash is required in advance in preparing the cured product.
성분용출 분석은 적외선 분광분석(FT-IR)방법을 사용하였으며 JIR-100형 기기에 의하여 분석하였다. 분석 결과, 유독성분인 Cd, Pb, Cr, T-Hg, P-Hg, As, O-P, CN, 등이 전혀 용출되지 않았다.Component dissolution analysis was performed using an infrared spectroscopy (FT-IR) method and analyzed by a JIR-100 type instrument. As a result, no toxic components Cd, Pb, Cr, T-Hg, P-Hg, As, O-P, CN, etc. were eluted.
한편 구조물 제조 과정에서 수중의 공기입자가 골재와 접합된 시멘트 수화물 과 결합하여 구조물의 유동성을 감소시키며, 구조물 내부의 공간에는 수화물이 생성되었다. 이 과정에서 물과 시멘트의 비율에 따라 약 1.45 내지 2.05의 체적변화가 관찰되었다.Meanwhile, in the process of manufacturing the structure, the air particles in the water combine with cement hydrate bonded to the aggregate to reduce the fluidity of the structure, and the hydrate is generated in the space inside the structure. In this process, a volume change of about 1.45 to 2.05 was observed depending on the ratio of water and cement.
이상 설명한 바와 같이, 본 발명에 따른 산업폐기물 처리용 고화제를 사용하여 산업폐기물을 고화시켜 구조물을 제조하면, 칼슘의 수화반응을 현저히 감소시킬 수 있어 유해물질 방출로 인한 환경오염을 예방할 수 있을 뿐만 아니라 구조물의 강도를 유지시킴으로서 구조물의 수명을 연장시킬 수 있다. 또한 산업폐기물을 재활용함으로서 친환경적일 뿐만 아니라 제조원가를 절감할 수 있는 장점이 있다. 또한, 섬유 외피를 이용하여 해양 구조물을 제작 설치할 경우 기존 콘크리트 구조물보다 유독성분의 방출량을 줄일 수가 있으며, 단시일 내에 포자가 접착하고 수생동식물이 자생할 수 있는 환경을 제공하므로 환경친화적인 효과도 기대할 수 있다.As described above, by manufacturing the structure by solidifying the industrial waste by using the industrial waste treatment solidifying agent according to the present invention, it is possible to significantly reduce the hydration reaction of calcium can prevent environmental pollution due to the release of harmful substances. However, maintaining the strength of the structure can extend the life of the structure. In addition, by recycling industrial waste is not only environmentally friendly, but also has the advantage of reducing manufacturing costs. In addition, when fabricating and installing marine structures using fiber shells, emissions of toxic components can be reduced compared to existing concrete structures, and environmentally friendly effects can be expected as they provide an environment in which spores adhere and aquatic plants and plants grow in a short period of time. have.
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