• 한국건설순환자원학회논문집
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• 제5권2호
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• pp.116-123
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• 2010

현행 "건설폐기물의 재활용 촉진에 관한 법률" 시행규칙에서는 가연성 건설폐기물의 재활용에 대한 명확한 규정 없이 배출규정만을 제안하여 대부분의 가연성폐기물이 단순 소각 또는 혼합폐기물의 형태로 소각 또는 매립되고 있는 실정이다. 따라서 가연성 건설폐기물의 단순 소각을 최대한 억제하여 연료화 등으로 재활용 할 수 있는 제도적 방안의 마련이 필요한다. 본 연구에서는 이를 위하여 가연성 건설폐기물의 발생 및 처리현황을 분석 조사하였고 국내 폐기물 고형연료관련 제도 및 법규를 검토하였다. 그리고 이를 토대로 국내 가연성 건설폐기물의 연료화를 위한 문제점을 분석하여 가연성 건설폐기물을 활용한 고형연료의 정착을 위한 정책적 방안을 제시하였다.

• 한국환경보건학회지
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• 제28권2호
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• pp.99-108
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• 2002

This study was carried out to evaluate the Physicochemical characteristics of mined waste(separated waste and soil) and to predict environmental effect of an old landfill site located at north of Seoul. Municipal solid waster(MSW) had been disposed of at the old landfill site used in this study for about 2 years(1990-1992). The old landfill site selected for this study had accepted mainly municipal solid waste. The landfill-mined waste contained separated waste (40.9%) and soil(59.1%) by wet weight basis. The separated waste consisted of combustible(91.0%) and non-combustible(9.0%). The combustible waste was mainly non-biodegradable plastics. The low heating value of the separated combustible waste, which is calculated by Dulong's equation, was as high as 3,470kcal/kg. According to the Korean Extraction Procedure, separated waste and soil were proved to be not hazardous. The total content of heavy metal in the separated waste and soil met standard of California State, USA. Therefore the separated waste may be relandfilled at a sanitary landfill site and/or burned up at an incinerator, and the separated old soil may be used ad landfill cover-soil at a sanitary landfill site. Water quality of two streams was grade IV, of which water could be used as industrial and agricultural water. The streams near the landfill site might not be contaminated by leachate from the old landfill site. It was estimated that organic matter in the old landfill site would not be actively biodegraded within a short period of time.

• 한국재난정보학회 논문집
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• 제4권1호
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• pp.86-100
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• 2008

It is needed to classify the kinds of construction and demolition(c&d) debris to 6 catagories of waste concrete, waste asphalt concrete, waste wood, scraps, combustible waste and incombustible waste in order to properly do a separate discharge and to estimate unit generation rate in construction site. Also, in this case, the unit treating cost for mixed wastes should be applied with the unit treating cost for combustible waste. The construction standard materials estimation data is used for basic data for estimating unit generation rate. The mixed wastes in this data should be classified to waste wood, combustible waste and incombustible waste, and their ratio is obtained by using the unit generation rate of Asia Pacific Environment and Management Institute and Seoul Metropolitan Development Institute. The waste amounts generated from newly-built construction can be obtained from multiplying the loss rate by the amount of materials used from construction standard estimation data. Also, those from dismantling construction can be obtained by subtracting waste amount generated during newly-built construction from total input amount of materials in newly-built construction. Those in two cases can be used in construction site. It can be used for estimating the amount generated and establishing the treating plan in the case of setting up the policy of waste management and doing the environment impact assessment.

• 한국농촌건축학회논문집
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• 제21권3호
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• pp.17-24
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• 2019

This study aimed to develop a mobile separating and sorting device for discharge sites to separate and sort mixed construction waste generated in small and medium scale in small provincial cities into inorganic materials and combustible materials. The study results can be summarized as follows: 1) As a result of analyzing the existing domestic technology for the separating and sorting mixed construction waste, a device sorting the waste by fusing the vibration screen, disc screen, air blowing methods and the separating and sorting the combustible waste is applied in Korea. 2) In foreign countries, the air blowing, screen, gravity sorters are used for separating and sorting combustible waste in the same way as in Korea. Especially German T Company suggests a construction waste separating and sorting system using an optical sorter. 3) As for the test device for separating and sorting mixed construction waste to be buried in landfill, the processing capacity was set as 16 tons per day. 4) For separating and sorting inorganic materials by granularity, this study set a trommel with two types of diameter as a basic. To operate the mobile all-in-one system, the device is designed to locate a conveyor, a combustible waste conveying device, inside of the trommel. 5) The device is designed in a mobile mode under the concept of primary separating and sorting device, and it can be transported using a 2.5-ton truck minimum. The diameter and length of the trommel are designed to be within 1500mm and 3000mm, respectively. In a further study, an optimized separating and sorting technology is planned to be presented through an experimental study for processing efficiency analysis at the mixed construction waste site by manufacturing the pilot experiment facility reflecting the design elements in the result of this study.

• 에너지공학
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• 제22권3호
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• pp.270-282
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• 2013

기후변화 및 화석연료 고갈에 대한 국가적 대응 차원으로 가연성 폐기물 에너지화가 진행되고 있다. 가연성 폐기물 에너지화란 비닐, 종이와 같은 폐기물을 전용보일러나 발전소에서 전기나 열을 생산하는 데 연료로 사용 할 수 있도록 고형연료로 제조하여 에너지로 전환하는 것이다. 본 논문은 조건부 가치측정법(CVM, Contingent Valuation Method)을 적용하여 폐기물에너지가 전체 에너지 소비에서 차지하는 비중을 현재의 1.89%에서 2020년까지 5%로 확대하는 정책의 시행으로부터 발생하는 외부적 편익을 추정하고자 한다. 이를 위해 지불의사액(WTP, willingness to pay)을 도출하고자 서울시 500가구를 대상으로 면대면 설문조사를 실시하여 CVM을 적용하였다. 지불의사 유도방법으로 1.5경계 양분선택모형과 영(0)의 WTP를 처리하기 위한 스파이크 모형을 결합한 분석모형을 적용한 결과 폐기물 에너지화에 대한 매월 가구당 평균 WTP는 2,724원으로 유의수준 5%에서 통계적으로 유의하게 추정되었다. 이를 서울시 전체로 확장하면 연간 137억원에 달한다.

• Journal of Nuclear Fuel Cycle and Waste Technology
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• 제1권1호
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• pp.75-82
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• 2013

A large quantity of radioactive waste was generated during the decommissioning of the KRR and UCF. The radioactive waste was packed into 200 liter drums and 4m3 containers and these were temporarily stored onsite until their final disposal in the national repository facility. Some of the releasable waste was freely released and utilized for non-nuclear industries. The combustible wastes were treated by the utilization of an incinerator with a capacity of on average 20 kg/hr.

• 한국건설순환자원학회논문집
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• 제4권1호
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• pp.89-95
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• 2009

현행 "건설폐기물의 재활용 촉진에 관한 법률" 시행령 별표1에서는 다양한 성상으로 배출되는 건설폐기물의 종류를 17가지로 구분하고 이중 제17호의 혼합폐기물은 건설폐토석을 제외한 나머지 15가지 성상의 건설폐기물중 둘 이상의 건설폐기물이 혼합된 것으로 정의하고 있다. 이중 폐콘크리트, 폐아스콘과 같은 건설폐재류는 대부분이 순환골재와 같이 재활용되고 있으며 폐금속과 같은 유가성 자재류는 대부분 분리 판매되어 2차 제품 제조등에 활용되고 있다. 그러나 폐목재, 폐합성수지, 폐섬유 등과 같은 가연성 폐기물의 경우 발열량이 높고 인체에 해로운 중금속 함유량이 적어 RDF나 RPF와 같은 에너지 연료로 활용이 가능하지만 상당량이 혼합폐기물 형태로 배출되어 단순 소각 및 매립되고 있는 실정이다. 그러므로 본 연구에서는 단순하게 외관상의 분류만을 고려하여 설정한 현행 "건폐법"과는 달리 최초 발생단계에서부터 최종처리까지 건설폐기물의 흐름을 보다 효율적으로 제어할 수 있도록 건설폐기물의 분류를 크게 가연성, 불연성, 가연성 불연성 혼합, 기타 등으로 분류하였다. 가연성 폐기물의 경우 기존의 소각 폐기물을 중심으로 폐목재, 폐섬유 등 기존의 소각 폐기물을 중심으로 분류를 하고 불연성은 재활용이 원활한 건설폐재류와 기타로 구분, 혼합건설폐기물은 발생 자체부터 서로 다른 물질이 결합되어 있어 분리 자체가 어려운 폐기물을 대상으로 하였다. 또한 이상에서 폐기물은 지정폐기물을 제외하고 모든 기타 폐기물로 분류하도록 하였으며 기본적으로 건설현장에서 발생하는 폐기물은 1차적으로 가연성, 불연성, 혼합폐기물로 분류하여 배출하는 시스템이 되도록 폐기물의 분류를 실시하였다.

• 한국환경과학회지
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• 제18권10호
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• pp.1181-1187
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• 2009

Results for application of RDF(Refuse Derived Fuel) to selected wastes in metropolitan and small and medium cities are as follows. The physical characteristics of waste are paper, plastic, food waste, and so on. The proximate analysis in P city showed 20.2% of moisture, 71% of combustible material, and 8.8% of ash on annual average. That in G city showed 31.6% of moisture, 59.5% of combustible material, and 8.9% of ash. Ultimate analysis in P city showed 52.04% of carbon, 7.02% of hydrogen, 28.80% of oxygen, 0.66% of nitrogen, and 0.09% of sulfur. Heating value was 3,363 kcal/kg. Ultimate analysis in G city showed 50.85% of carbon, 6.56% of hydrogen, 29.86% of oxygen, 0.79% of nitrogen, and 0.12% of sulfur. Heating value in the G city was somewhat lower than that in the P city with 2,632 kcal/kg. Thus, application of RDF in metropolitan city was more effective than that in small and medium cities. Heating value in mixture for the P city was lower than that in waste of the volume rate waste charge system alone by 143 kcal/kg. In proximate analysis, moisture, and combustible material were likely to be more adequate to RDF.

• 한국해양공학회지
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• 제15권2호
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• pp.130-134
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• 2001

Recently environmental pollution at sea becomes serious, so every governmental organization makes its effort to solve this problem. Combustible ocean wastes as of ropes, fishing nets, and tires are usually highly polymerized compound materials. The problem of ocean waste treatment can be solved by using the pyrolysis method. Pyrolysis characteristics of ocean waste was examined to get the basic data for the production system of fuel from the ocean waste. Thermogravimetric experiment showed that residual mass rate decreases as the velocity of temperature-rising becomes lower. The pyrolysis of waste rope and fishing net occurs at 300~450$^{\circ}C $ and the waste tire does at 350~450$^{\circ}C $. Pyrolysis time is estimated about 15 to 20 minutes in the temperature range when lively act of pyrolysis temperature reached.

• 한국환경보건학회지
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• 제16권2호
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• pp.89-95
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• 1990

This study was investigated to the energy recovery by the pyrolysis of waste tyre. the pyrolysis of the waste tyre was made by using the pyrolysis chamber for the gasification and the combustion chamber for the combustion of the pyrolysis gas. In batch system, the amount of waste tyre was put 150kg in the pyrolysis chamber and the proper air flow rate for the stable production of the pyrolysis gas was 0.95Nm$^{3}$ /min. the production time of the pyrolysis gas was stable above 210minutes, and the stable production rate was above 3.8Nm$^{3}$ /min. The production temperature of pyrolysis gas was 170$^{\circ}$C and combustion temperature of pyrolysis gas was 1,000$^{\circ}$C. The combustible component of washing gas in pyrolysis gas of waste tyre was CO, CH$_{4}$, $C_{2}H_{6}$ and $C_{3}H_{8}$, and total amount was 22.7%. Heat value of condensed material was 9,804Kcal/kg. The average concentration of air pollutants between cyclone and scrubber was CO 420.4ppm, SO$_{x}$ 349.8ppm. NO$_{x}$ 68.Sppm, HCl 24.4ppm and Dust 240.0g / Nm$^{3}$, respectively.