• Journal of the Korean Recycled Construction Resources Institute
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• v.8 no.2
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• pp.161-166
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• 2020

In accordance with the amendment of the Industrial Safety and Health Act of 2007, Korea completely prohibited the import, distribution and manufacture of asbestos like Europe and Japan. Accordingly, the current problem of asbestos is the safe maintenance and disposal of asbestos construction material, the disposal of asbestos, and the final disposal of asbestos building materials. If the asbestos building material is made harmless, it may be classified as general waste or as recyclable waste. Therefore, this study evaluated the physical and chemical characterization of detoxified asbestos powder and the applicability of secondary products. In this study, it was found that applying the appropriate temperature and pressure for catalysis during asbestos desalination through low temperature chemical treatment was the most important factor.

• Journal of the Korean Recycled Construction Resources Institute
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• v.9 no.2
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• pp.223-228
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• 2021

The final disposal method for asbestos building materials is to be landfilled at a designated waste landfill in accordance with the Waste Management Act. However, it is difficult to secure a domestic designated waste landfill site to landfill the entire amount of asbestos waste, which is expected to emit more than 400,000 ton/year by 2044. In this study, a detoxification treatment was performed on a ceiling tex with a density of 1.0 to 1.2g/cm³ containing 3 to 7% of chrysotile, and it was used as a reinforcing fiber for extruded panels. It was confirmed that asbestos components were detoxified through the reaction process using 30% oxalic acid and carbon dioxide, and it was recognized that these detoxifying properties were maintained even after extrusion molding. However, it was found that milling to a fiber size of less than 1mm for complete detoxification of asbestos resulted in a decrease in reinforcing performance. Therefore, in the case of using detoxified asbestos fibers in the extrusion molding process, it is considered desirable to add fibers with a length of 5mm or more to improve the reinforcing performance.

• Proceedings of the Korean Institute of Industrial Safety Conference
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• 2000.06a
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• pp.37-41
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• 2000

폐기물 소각시 발생되는 각종 유해가스 및 비산회재(fly ash)는 후처리 설비에 의해 배출허용기준치 이하로 처리된 후 대기 중으로 방출되도록 환경 규제되고 있다. 그러나 포집된 비산회재(fly ash) 및 노하부 배출재(bottom ash) 내에는 미 연소된 상태로 배출된 유해성 유기물질(다이옥신, 퓨란류 등)과 중금속 성분이 함유되어 있어 이들 소각잔류물(incineration residues)을 안정화나 무해화 처리 없이 단순 매립할 경우 강우에 의해 소각잔류물 내의 유해성분이 침출됨에 따라 토양이나 지하수 등에 2차 환경오염을 일으키게 된다. (중략)

• Journal of the Korean Recycled Construction Resources Institute
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• v.6 no.4
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• pp.324-330
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• 2018

In accordance with the amendment of the Industrial Safety and Health Act of 2007, Korea completely prohibited the import, distribution and manufacture of asbestos like Europe and Japan. Accordingly, the current problem of asbestos is the safe maintenance and disposal of asbestos construction material, the disposal of asbestos, and the final disposal of asbestos building materials. In the past, Korea used 100,000 tons of asbestos every year, and the building materials using it exceeded 1 million tons per year. These asbestos building materials continued to be used until 2006, and the Ministry predicted that these materials would continue to be maintained until 2044. When the permeable hardening agent is applied to the asbestos building material installed in the pre-pretreatment step for the harmless treatment of the asbestos waste and the dismantling is carried out, the scattering of the asbestos is suppressed in the disassembling step, detoxification treatment conditions can be improved. Therefore, permeable hardeners should be stably penetrated into asbestos building materials. In this study, it is suggested that pre - pretreatment methods for the harmlessization of waste asbestos building materials with medium density level can be presented. In order to efficiently perform pre - treatment for chemical harmlessness in the future, the mixing ratio of permeable hardener and middle water Optimization is the most important factor.

• Journal of the Korean Professional Engineers Association
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• v.31 no.3
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• pp.45-48
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• 1998

• Applied Chemistry for Engineering
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• v.31 no.4
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• pp.438-442
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• 2020

Studies on the recovery conditions and optimization process for valuable metal recovery through chemical treatment from detoxified asbestos-containing waste composed of calcium silicate, larnite, merwinite, and akermanite were conducted. The main components, Si, Ca, and Mg, of detoxified asbestos-containing waste (DACW) were separated and recovered in the form of SiO₂, CaSO₄, and Mg(OH)₂ compounds, respectively. Each separated component was confirmed through X-ray diffraction (XRD) and inductively coupled plasma spectrometer (ICP) analysis. The recovery conditions for each component were first treating them with an acid to separate SiO₂ and subsequently with H₂SO₄ to recover Ca in the form of sulfate, CaSO₄. The remaining Mg was recovered by precipitation with Mg(OH)₂ under strong basic conditions. This study suggested that it is possible to convert existing treatment process of asbestos waste by landfill through recovering the components into a resource-recycling green technology.

• Resources Recycling
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• v.23 no.2
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• pp.61-70
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• 2014

LCD televisions and monitors use cold cathode fluorescence lamps (CCFLs) to illuminate the screen. Most CCFLs contain mercury and they have to be carefully handled at the end of their lives as per minimum treatment standards under the Waste Electrical and Electronic Equipment (WEEE) and Restriction of Hazardous Substances (RoHS) directives. CCFLs were carefully separated from mold frames of waste LCD units for primary decontamination of mercury/fluorescent compound mixture using CCFL decontamination system designed and fabricated in the present research. Residual mercury was further removed by employing a pyro-process, where crushed CCFL tubes transferred from primary decontamination process were subject to heat treatment at $550^{\circ}C$ in a box furnace: more than 99% of mercury was removable from waste CCFLs.

• Proceedings of the Korea Society for Energy Engineering kosee Conference
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• 2003.05a
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• pp.523-526
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• 2003

본 연구센터에서는 폐기물의 무해화 처리 및 합성가스 제조를 통한 에너지화를 목적으로 가스화용융시스템의 개발을 진행 중에 있다. 현재까지 개발된 가스화용융시스템은 분류층(Entrained bed) 방식의 가스화용융로를 핵심장치로 하고 있으며, 폐유, 중질잔사유, 액상슬러리등의 액상폐기물과 건조하수슬러지, 소각재등의 입자상 폐기물을 대상으로 개발되었다.(중략)

• The Microorganisms and Industry
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• v.16 no.3
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• pp.56-62
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• 1990

일반적으로 산업폐수및 생활하수의 생물학적 처리에 관계하는 미생물의 종류는 약1,000-2,000종에 이르는 것으로 추정된다. 이와 같은 미생물의 범위는 매우 넓어서 세균, 균류는 물론이고, 조류, 원생동물, 후생동물까지 포함한다. 19세기 이전에 미생물을 이용한 폐하수 처리는 생활하수와 같이 쉽게 분해하는 물질로만 구성되어 있기 때문에 간단한 처리 공정으로도 충분히 운영되었으나, 산업혁명 이후 새로운 화학물질이 합성되어 폐하수로 배출되므로 처리효율을 달성하는데 더욱 어렵게 되므로 미생물을 전공한 전문인력의 역할이 가일층 높아지게 되었다. 특히 1970년대 이후에는 생물공학 기법을 이용하여 독성 유해물질을 무해화(Detoxification) 하고, 광물화(Mineralization)할 수 있는 미생물 균류를 연구 개발하여 폐수나 폐기물을 처리하는데 활용코자하는 노력이 활발히 진행되고 있으며 일부는 큰 결실을 맺은 것도 있지만 아직도 연구가 진행 중인 분야가 더 많은 편이다. 그러므로 본 고에서는 지금까지 연구 보고된 결과와 앞으로 미생물을 전공한 우리들이 나아갈 방향을 제시코자 한다.

• The Magazine of the Society of Air-Conditioning and Refrigerating Engineers of Korea
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• v.31 no.9
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• pp.16-23
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• 2002

현재 우리나라는 1980년대 후반부터 도시폐기물 소각시설을 설치하기 시작하여 전국적으로 20 여곳의 대형 소각장이 가동되고 있으며 대기오염 방지 기술도 발전에 발전을 거듭하여 불과 10 여년 동안에 선진국 수준의 대기오염 배출기준을 만족하는데 아무 문제가 없을 정도로 되었다. 그러나 소각후 발생 하는 소각재의 경우 비산재는 고형화등의 처리 후 매립하고 바닥재는 별도 처리없이 매립하는 실정이어서 매립 후 시간이 흐를수록 매립된 소각재에서 용출되는 다이옥신과 소각재 중에 포함된 중금속 등에 의한 토양오염과 수질오염의 우려가 남아 있는 것이 사실이다. 소각후 남는 소각재는 폐기물량의 약 15 %, 비산재는 약 1.5 % 정도 발생하는 것으로 볼 때 매립은, 특히 다음 세대에 유산으로 남겨진다는 점에서 더 이상 적절하지 않은 해결책으로 생각되며 유럽과 일본 등 선진국에서는 이미 이와 같은 소각재에 대한 무해화 처리기술이 개발되고 속속 상용화되고 있으므로 우리나라도 하루빨리 열분해용융시설등 신기술을 개발하거나 도입하여 세계적 환경 기술경쟁 에서 선진국과 어깨를 나란히 함은 물론 청정한 국토를 후손에게 물려줄 수 있도록 하는 대책이 강구되어 야 할 것이다. 본 고에서는 폐기물 처리기술의 세계 적 동향을 살펴보고 폐기물의 완전 자원화에 성공한 대우 써모셀렉트 열분해용융 기술의 특성에 대해 소개하고자 한다.