• 자원환경지질
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• 제31권2호
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• pp.101-110
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• 1998

The purpose of this study is to elucidate the source of U anormaly formed in stream water of the drainage system around the Shinbo talc mine area based on the hydrochemical properties of water masses including surface water and groundwater. The hydrochemical properties of water masses in the Shinbo talc mine area are divide into three types; Type I : $Ca(Mg)SO_4$ type with high U content as shown in the stream water flowout from the mine, Type II : $Ca(HCO_3)_2$ type with high U content as in deep groundwater, Type III : $Ca(HCO_3)_2$, type with low U content as in the other stream water and shallow groundwater. It is necessary to emphasize that in deducing the uranium source, a distinct discrimination between type I and type II is showed in their hydrothermal properties in spite of commonly having a high uranium content, which in turn means the occurrence of a different water-rock interaction processes between both type. All evidences suggest that type II groundwater have acted as a primary media in the transport of uranium and that, as the groundwater flows through the talc mineralization zone, water composition of type II was transformed into that of type I water as the results of a secondary water rock interaction process, caused by imposition of new mineralogically controlled thermodynamic constraints. Consequently, in the viewpoint of hydrochemical exploration, the investigation of the hydrologic circulation system and the hydrogeologic properties for the aquifer of type II groundwater shall be done first of all and will provide a crucial clue on tracing the uranium mineralization zone occurred in the Shinbo talc mine area.

• 자원환경지질
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• 제33권2호
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• pp.91-100
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• 2000

It has been more than ten years since Dukun mine was abandoned. Tailings of waste deposits and slime dumps in the abandoned Dukum mine have been left to be deserted for fifty years. The results of fifty years of neglecting are nothing short of major environmental problems. Slime dumps have been exposed to air and water in the mine over ten years and then soil profile has been formed well. Soil in the upper layer (A horizon) is the light gray color due to the leaching of cations. Soil in the lower layer (A2 horizon, 0.2∼0.3m)is tinted with reddish brown and yellowish brown color due to the development of iron oxides and iron hydroxides. Soil in the lower part of B horizon of (1.0∼3.0m) with the growth of copper and zinc oxides exposes to the bluish green, light blue, and dark gray. Ranging from 3m to 8m in depth, 85 samples were taken from 22 sampling sites with 50m intervals located on the slime dump area with hand auger and trench (open cut). As tailings was distributed, heavy metal elements extracted by the process of surface water and ground water move and disperse in to the hydrosphere. Waste dumps were distributed in and around the mine and water draining from those dumps be a potential source of contamination. Soils, thus, can be dispersed into downslope and downstream through wind and water by clastic movement. These materials may be deposited in another horizon if the water is withdrawn, or if the materials are precipitated as a result of differences in pH, or other conditions in deeper horizons. These were primarily associated with acid mine drainage. The characteristics and rate of release of acid mine drainage are influenced by various chemical and biological reactions at the source of acid generations. Prolonged extration of heavy metal elements has a detrimental effect on the agricultural land and residental area. Twenty soil samples were collected from the agricultural land in the area (0∼30 cm). Seventeen samples were also taken from the sediment in the stream running alongside the dumps. The dispersion patterns of heavy metal elements are as follows: The content of As ranged 2∼6 ppm in a horizon, 20∼125 ppm in B horizon with large amount of clay mineral is concentrated and the content of Cd ranged 1∼2 ppm in A horizon, 4∼22 ppm in B horizon. Like Cd, the content of As, Cu, Zn, Pb in B horizon is higher than that in A horizon (approximately 5∼100 times). When soil formation proceeds in stages, it is necessary to investicate the B horizon with the concentration of heavy metal and preventive measures will have to established.

• 한국수처리학회지
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• 제26권6호
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• pp.13-26
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• 2018

This research was conducted to elucidate the removal mechanism of heavy metals and sulfate ion from acid mine drainage(AMD) by porous zeolite-slag ceramics (ZS ceramics) packed in a column reactor system. The average removal efficiencies of heavy metals and sulfate ion from AMD by the 1:3(Z:S) porous ZS ceramics in the column reactor under the HRT condition of 24 hours were Al 97.5%, As 98.8%, Cd 86.1%, Cu 96.2%, Fe 99.7%, Mn 64.1%, Pb 97.2%, Zn 66.7%, and $SO_4{^{2-}}$ 76.0% during 121 days of operation time. The XRD analysis showed that the ferric iron from AMD could be removed by adsorption and/or ion-exchange on the porous ZS ceramics. In addition it was known that Al, As, Cu, Mn, and Zn could adsorb or coprecipitate on the surface of Fe precipitates such as schwertmannite, ferrihydrite, or goethite. The EDS analysis revealed that Al, Fe, and Mn, which were of relatively high concentration in the AMD, would be adsorbed and/or ion-exchanged on the porous ZS ceramics and also exhibited that Al, Cu, Fe, Mn, and Zn could be precipitated as the form of metal hydroxide or sulfate and adsorbed or coprecipitated on the surface of Fe precipitates. The microscopic results on the porous ZS ceramics and precipitated sludge in a column reactor system suggested that the heavy metals and sulfate ion from AMD would be eliminated by the multiple mechanisms of coprecipitation, adsorption, ion-exchange as well as precipitation.

• 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.

• 지질공학
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• 제13권1호
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• pp.29-50
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• 2003

광양 폐 금-은 광산지역의 소규모 하천(초남리천과 사곡리천)에 흐르는 산성광산폐수의 수질 특성을 환경지구화학적 방법을 이용하여 조사하고 비교 연구하였다. 중금속(카드뮴, 구리, 납, 아연) 오염은 초남리천에서 훨씬 심한 것으로 나타난 반면, 용존 알루미늄과 철 함량은 오히려 사곡리천에서 높았는데, 두 하천간의 이러한 차이는 광산폐수의 기원물질, 즉 광석광물의 함량과 특성이 서로 다르기 때문인 것으로 판단된다. 두 하천에서 흐르는 산성광산폐수의 자연정화 기작에 대해 고찰하여 보았다. 주로 단일하천으로 이루어진 초남리천의 경우, 석회석을 사용하여 광산폐수를 정화시키는 소규모의 소택지가 조성되어 있어 소택지 내에서의 pH 증가에 따른 중금속의 흡착과 공침에 의해 중금속이 제거되고 있다. 초남리천에서 채취한 적황색 침전물에 대하여 XRD, SEM-EDS. EPMA 분석 및 화학적 분해법을 이용한 분석 결과, 적황색 침전물은 대부분 침철석으로 구성되어 있으며 알루미늄, 망간, 구리, 아연 등이 부화되어 있음을 확인하였다. 따라서 이들 금속들은 주로 적황색 침전물의 생성에 수반된 흡착이나 공침과 같은 지구화학적 반응에 의해 제거되는 것으로 판단된다. 한편, 소택지의 중금속 제거능은 계절적으로 변화하는 하천의 유량에 의해 영향을 받고 있다. 반면, 사곡리천의 경우에는 오염되지 않은 여러 지류와의 혼합에 수반된 pH 증가에 따라 철수산화물이 침전하면서 중금속의 제거가 일어나고 있다. 오염 하천과 비오염 지류와의 합류 지점에서 발생하는 중금속 제거의 기작은 '특성-특성도(property-property plot)'를 활용한 해석에 의해서도 뒷받침된다.

• 터널과지하공간
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• 제17권5호
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• pp.360-371
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• 2007

이 논문은 GIS 기반의 수리학적 모델링을 통하여 시공측면에서 효과적으로 지표수를 제어하여 배수제어와 사면의 안정성에서의 적용에 관한 것이다. 본 논문에서는 인도네시아 파시르 노천광을 대상으로 연구를 수행한 결과를 제시한다. 신뢰할 수 있는 DEM 자료의 획득을 위하여 상세한 지형측량이 이루어 졌으며, DEM 자료로 부터 빗물의 흐름방향, 누적 흐름양, 집수구역 등의 배수 시스템의 특성을 도출하기 위하여 ArcGIS 9.1 소프트웨어가 제공하는 Hydrology 분석 도구를 사용하였다. 수리학적 모델링과 지형적인 분석의 결과는 현재의 배수처리 설비가 적당하지 않으며 또한 집중되는 지표수의 흐름으로 벤치사면에서 많은 침식이 일어날 수 있음을 보여주고 있다. 마지막으로 배수설비설계의 최적화와 물의 흐름의 제어를 통한 사면의 안전성의 증가와 사면을 감시하기 위한 방법을 제시하였다.

• 자원환경지질
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• 제35권4호
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• pp.325-337
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• 2002

백운 폐광산 주변에 방치된 폐석으로 인한 하천수 및 하상퇴적물의 중금속오염정도를 알아보고자 하였다. 광산활동과 관련되어 발생하는 주변 하천수의 Al 및 Pb, Zn, Cu, Cd, Mn, Fe 등의 중금속 및 기타 이온의 부화현상은 하천수의 TDS를 높이며 또한, 수질을 악화시키는 요인이 된다. 백운광산 주변의 하천수는 Ca와 SO$_4$가 주를 이루는 Ca-SO$_4$형을 보이며, 부분적으로 황화광물의 화학적 풍화로 인한 중금속부화현상을 보인다. 광산을 경유해서 흐르는 하천수는 알카리 및 알카리 토류원소에 의한 중화작용의 영향으로 pH는 6.S-7.1의 약산성내지 중성을 띤다 폐갱구로부터 홀러나오는 갱내수 또한 약산성 내지 중성을 띠며, 광산내의 광석과 맥석광물과의 화학적 풍화로 인해 높은 원소함량을 보인다. 백운 폐광산 주변의 하천수는 갱내수가 유입되는 지역에서 높은 농도를 보이다 하류로 갈수록 농도가 급격히 낮아진다. 이온농도가 낮아지고 pH가 중성을 띠는 것은 자연적으로 오염을 조정해주는 희석 및 침전, 흡착 등으로 인한 완충작용의 결과이다. 토양내에서 중금속의 이동성이나 생물학적 이용능력을 알아보기 위하여 단계별 추출법을 이용하여 하상퇴적물에서 Cd, Cu, Zn, Pb의 존재형태를 5가지 단계로 분류하였다: 이온교환형태, 탄산염형태, 철-망간 산화물형태, 유기물형태, 잔류상형태. 대부분의 퇴적물에서 Cu(21-92%) 및 Zn(28-89%), Pb(23-94%)는 잔류상형태가 우세하였으며, Cd는 퇴적물에서 다른 원소에 비해 낮은 농도(2.7-52.8 mg/kg)를 보여주었으나 대부분 불안정한 형태(68-97%)가 우세하였다. 상류 퇴적물에서는 폐석으로 인해 Pb의 농도가 높게 나타나며, 하류 퇴적물은 Zn이 높은 농도를 보여, Zn 과 불안정한 형태가 우세한 Cd이 이동성이 높은 원소임을 알 수 있었다.thing construction. The presentation coverages and relative difficulties of textbooks were, however, diverse. It is somewhat noticeable that, while fewer professors majoring in clothing construction participated in writing, generally more pages were allocated to clothing construction than other areas. While presentations on anthropometrics method, construction theory, draft theory, usage of sewing machine and fitting theory were insufficient most textbooks were dealing with drafting of basic slopers and sewing procedure, etc. Making-up techniques on the apparels items such as Korean traditional men's pants, pajamas, shirt vest skirt, pants, apron and Korean pouch were handled closely in each textbook.different from the one in the l980s worn by the demonstrators of popular movements and democratic movements, and it emerged as a new symbol with the characteristics of cultural movement like community consciousness and nature affiliation.

• 자원환경지질
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• 제31권6호
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• pp.499-508
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• 1998

The Imgok Creek is located in the Gangreung coal field, which has been known that sulfides are more abundant than other coal fields in Korea, and it has been severly contaminated by acid mine drainage (AMD) discharging from the abandoned coal mines, such as the Youngdong, the Dongduk and the Waryong coal mines. The purposes of this study are to synthetically assess the contamination of natural water, stream sediment and cultivated soils, and to provide the basic data for AMD treatment. Geochemical samples were collected in December, 1996 (dry season) and April, 1997 (after three day's rainfall). TDS of the Youngdong mine water was remarkably higher than those of other mine waters. In the Imgok Creek, concentrations of most elements, except Fe decreased with distance by dilution caused by the inflow of uncontaminated tributaries. From the results of NAMDI and $I_{geo}$ calculation, the Youngdong coal mine was the main contamination source of the study area. Groundwater pollution was not yet confirmed in this study and the paddy and farm land soils were also not yet contaminated by mining activity based on the pollution index ranging from 0.27 to 0.47.

• 한국지하수토양환경학회지:지하수토양환경
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• 제15권6호
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• pp.81-90
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• 2010

In this study, primary investigation for evaluation of abandoned metal mine effect on watershed has been done. 64 abandoned mines have been selected for primary investigation through literature and field survey. 216 soil and 90 water samples were collected and metal pollution concentrations were analyzed. 24 mines have mine water in the pits and acid water below pH 5 was not observed. Soils from 35 mines were over the soil basis of concern and 16 mines were over the soil basis of action. Arsenic average concentration was 188 times of average concentration of the natural background. Drinking water samples from 3 mines were over the drinking water standard and surface water samples from 12 mines were over the river water standard. Integrated pollution index, which was resulted from the integration of field survey, soil and water pollution concentration, showed that, abandoned metal mines had affected on watershed greatly in the order of Samgeum, Daedeok, Cheongdalgeum, Heungsin, Yeongdae and Myeongbong mines.

• 한국자원공학회지
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• 제55권6호
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• pp.546-552
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• 2018

금번 6차 광해방지 국제심포지움 발표사례로 볼 때, 국가별 광산개발의 역사, 지리여건, 경제상황 등이 상이하나, 과거 개발된 광산으로 인해 발생한 산성광산배수로 인한 수질오염, 광물찌꺼기 유실로 인한 토양오염 및 수질오염, 사면파괴로 인한 산사태, 지하갱도 붕괴로 인한 지반침하 등으로 인간의 생활이 위협당하고 있다. 나라별로 기술력과 법제도의 차이가 있고, 광해복구가 진행 중인 나라와 이제 시작하려고 제도마련 및 기술지원을 받아야 하는 나라도 있다. 광해복구를 시작하려는 나라에서는 국제사회에 도움을 요청하고 있어 기술적 제도적으로 앞선 선진국에서는 복구를 시작하려는 나라와 공조를 통해 광해를 복구해야할 필요가 있다.