• 자원환경지질
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• 제36권3호
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• pp.177-189
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• 2003

서보광산의 폐광석에 대한 황화광물의 산화작용과 용해된 금속이온들의 이동을 제한하는 메카니즘을 밝히고자 광물학적 연구를 수행하였다. 광물학적 연구를 위해서 반사현미경 관찰, XRD 분석, SEM/EDS 분석을 실시하였다. 폐광석에 대한 광물학적 연구를 통해 앵글레사이트(anglesite), 코벨라이트(covellite), 침철석(goethite), 자연황(native sulfur), 엔소타이트(nsutite) 등의 2차광물을 확인하였으며, 이들 2차광물은 용해된 비소, 구리, 철, 망간, 납, 아연의 확산을 제어한다. 용해된 비소, 구리, 철, 망간, 납, 아연은 철수산화광물과 망간수산화광물에 흡착되거나 공침되기도 한다. 철수산화광물은 결정도가 낮은 것과 높은 것(침철석)으로 분류된다. 비소는 결정도가 낮은 철수산화광물에서 9∼24 wt.%가 검출되며, 결정도가 더 높은 철수산화광물(침철석 등)에서는 상대적으로 낮은 함량(0.6∼7.7wt.%)이 검출되었다. 이것은 결정도가 낮은 철수산화광물에 흡착되었던 비소가 철수산화광물의 결정도가 높아지면서 비소를 방출하기 때문이거나 비표면적의 차이에 기인한 것으로 해석된다. 폐광석으로부터 용해된 중금속과 미량금속원소들은 침전(Fe, Mn, Cu, Pb), 공침(Fe, Mn) 및 흡착(As, Cu, Pb, Zn) 등의 화학반응을 통하여 다시 고정화됨으로써, 현장에서 자연적으로 정화되고 있다. 이러한 광물학적 연구결과들은 광산 폐기물의 지화학적 환경 영향평가에 이용할 수 있고, 가능한 광산복원 계획을 세우는 데 유용한 자료로 사용될 수 있다.

• 자원리싸이클링
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• 제21권3호
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• pp.3-14
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• 2012

중국의 도시광산 재자원화산업을 파악 검토하기 위하여 ELV(사용후자동차), E-waste(Waste Electric Electronic Equipment) 및 비철금속의 리싸이클링을 조사하였다. 중국의 자동차 판매대수가 1,000만대를 넘어서고, 폐차대수도 증가하고 있으나 리싸이클링은 원활하지 못하다. 중국 도시의 가전 보유량은 선진국 수준으로 농촌과의 격차가 크다. 세계 E-waste의 많은 량이 중국으로 유입되어 세계의 E-waste 리싸이클링센터를 형성하고 있다. 비철금속의 소비량은 계속 증가하고 있지만 리싸이클링 수준은 낮다.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2004년도 총회 및 춘계학술발표회
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• pp.260-265
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• 2004

Acid mine drainage(AMD) is one of the most serious environmental concerns associated with the mining industry around the world. The objective of this study is to assess the potential of sewage sludge as a carbon source for sulfate reducing bacteria and waste lime and steel slag as a neutralize agent for acid mine drainage bioremediation for use in permeable reactive materials. The study was performed using synthetic AMD in six column experiments. The effluent solution was systematically analysed throughout the experiments. The results of the study indicated that sewage sludge, waste lime and steel slag were the most effective for the AMD treatment as a permeable reactive materials.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2003년도 추계학술발표회
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• pp.386-390
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• 2003

To evaluate the potential capacity of mine wastes in the production of heavy metal containing acid water, samples from depths of 0, 30 and 60cm were collected and analyzed. The waste from surface showed the lowest pH which indicates the oxidation of wastes and the capacity of contamination of the area around the waste file. And the lower pH values of leachate of the wastes through the leaching tests with pH controlled water(3, 4, 5) may indicate that minerals producing the acidity still exist. Reduction of sulfur contents in wastes after the leaching test well fit to the increased contents of iron oxide.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2006년도 총회 및 춘계학술발표회
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• pp.183-193
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• 2006

Several metalliferous and coal mines, including Seojin and Okdong located at the Kangwon province, were abandoned or closed since 1989 due to the mining industry promotion policy and thus disposed an enormous amount of mining wastes without a proper treatment facilities, resulting in water and soil pollution in the downstream areas. However, no quantitative assessment was made on soil and water pollution by the transport of mining wastes such as acid mine drainage, mine tailing, and rocky waste. In this research, total and fractional concentrations of heavy metals in mining wastes were analyzed and accordingly the degree of water and soil pollutions in the stream area were quantitatively assessed employing the several pollution indices. Concentrations of Ni, Cd, and Pb in soils near the abandoned coal mine areas were 1,240.0, 25.0 and 1,093.0 mg/kg, respectively, and these concentrations were higher than those in soils near the closed metalliferous mine areas. Also Cu concentrations in soils near the tailing dams were about 1967 mg/kg, which is considered as very polluted level. Results demonstrated that soil at the abandoned mine areas were highly contaminated by AMO, tailing, and effluents of the mining wastes. Therefore, a prompt countermeasure on the mining waste treatment and remediation of the codntaminated water and soil should be made to the abandoned or closed metalliferous and coal mines located at the abandoned mine area.

• 한국지하수토양환경학회지:지하수토양환경
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• 제15권6호
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• pp.29-36
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• 2010

Several mines including Namil, Solim and Jungbong which are located in the Gyeonggi and Kangwon province have been abandoned and closed since 1980 due to "The promotion policy of mining industry". An enormous amount of mining wastes was disposed without proper treatment, which caused soil pollution in tailing dam and ore-dressing plant areas. However, any quantitative assessment was not performed about soil and water pollution by transporting mining wastes such as acid mine drainage, mine tailing, and rocky waste. In this research, heavy metals in mining wastes were analyzed according to leaching method which used 0.1 N HCl and total solution method which used Aqua-regia to recognize the ecological effect of distance from hot spot. We sampled tailings, rocky wastes and soils around the abandoned mine. Chemical and physical parameters such as pH, electrical conductivity (EC), total organic carbon (TOC), soil texture and heavy metal concentration were analyzed. The range of soil's pH is between 4.3 and 6.4 in the tailing dam and oredressing plant area due to mining activity. Total concentrations of As, Cu, and Pb in soil near ore dressing plant area are 250.9, 249.3 and 117.2 mg/kg respectively, which are higher than any other ones near tailing dam area. Arsenic concentration in tailing dams is 31.0 mg/kg, which is also considered as heavily polluted condition comparing with the remediation required level(RRL) in "Soil environment conservation Act".

• 한국지구물리탐사학회:학술대회논문집
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• 한국지구물리탐사학회 2001년도 정기총회 및 제3회 특별지포지움
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• pp.75-89
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• 2001

국내 폐석탄 광산은 334 개, 폐금속 광산은 약 900 여개로 알려져 있다. 이러한 폐광산에서는 환경오염과 지반침하 등 안전문제가 발생하고 있다. 폐광산에서 환경오염은 주로 폐갱도, 채굴적 그리고 광산폐기물 적치장에서 유출되는 산성광산배수 문제와 중금속이 함유된 광산폐기물의 침식 및 유실로 인한 주변 토양오염 등을 들 수 있다. 폐석탄 광산 및 폐금속 광산의 갱내수를 조사 분석한 결과, 일부 폐광산 갱내수들은 산성수이며 금속성분이 고농도로 함유된 폐수로 나타나고 폐탄광 배수의 수질은 지역적으로 차이가 있다. 폐광산배수의 정화는 물리화학적 처리시 막대한 운영비가 소요되므로 폐갱도 석회석 충전과 소택지 등 자연정화처리법으로 처리되고 있다. 현재 폐금속 광산 폐기물은 환경오염 방지를 위해 주로 매립법으로 복구되고 있다.

• 자원리싸이클링
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• 제20권6호
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• pp.3-18
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• 2011

우리나라의 도시광산 재자원화실태와 전망을 파악하기 위하여 금속소비량을 산출하였다. 년간 금속소비량으로부터 금속 축적량을 추정할 수 있고, 도시광산자원을 전망할 수 있다. 금속소비량을 산출함에 있어 다양한 자료 즉 비철협회, 철강협회, 관세청 HS 코드, 연구용역 보고서, 학술회의자료 및 생산회사 탐문자료 등을 인용하였다. 도시광산개발의 요건(key point)을 설명하기 위하여 T.E.Graedel에 의해서 작성된 표(Principle Uses and Recycling Potential of Metals in the Periodic Table)를 인용하였다.

• 대한전자공학회:학술대회논문집
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• 대한전자공학회 2001년도 The 6th International Symposium of East Asian Resources Recycling Technology
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• pp.427-431
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• 2001

In this research, porous materials were made from mine's waste slime. As a temperature changes, a phase changes, a porosity, and a mechanical strength of porous materials were observed and measured. The process of pore-formation was observed by SEM according to the change of heat-treatment temperature and time. It fumed out that the foaming reaction of mine's waste slime was resulted from liquid phase by decomposition of the sanidine and the muscovite-3T. When heat- treated at over 120$0^{\circ}C$, it appeared high porosity. And, to activate the foaming reaction, an alkaline oxide concerned with liquid formation was added and its effects were examined.

• 한국세라믹학회지
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• 제45권7호
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• pp.395-400
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• 2008

This paper indicates the investigation about the development of ET (Environmental Technology) industrial geopolymeric materials from mixture silica mine waste, coal fly ash and alkali activator solution (sodium silicate) by the geopolymer technique at ambient temperature. The results showed that higher compressive strength of geopolymeric mortar increased with a reduce of L/S ratio and increased along with an increase of coal fly ash content. The compressive strengths of geopolymer mortar on low silica of C Silica Mine and K Silica Mine are 18.7 MPa, 20.4 MPa, respectively. Compressive strength of geopolymeric mortar depends on L/S ratio and coal fly ash content added.. Additionally, scanning electron microscope (SEM) techniques are used to characterize the microstructure of the geopolymeric mortars. SEM observation shows that it is possible to have amorphous aluminosilicate gel within mortar. XRD patterns indicate the fact that geopolymeric mortar is composed of amorphous aluminosilicate phase, calcite and quartz.