• The Korean Journal of Ecology
• /
• 제9권1호
• /
• pp.33-40
• /
• 1986

The distribution of giant duckweed (Spirodela polyrrhiza) and small duckweed (Lemna aequinoctialis) was investigated at lead-zinc mine area and the limiting factors for their distribution were studied by laboratory experiments. The metal investigated of water affected on the growth of giant duckweed and small duckweed. Under filed conditions, both giant duckweed and small duckweed did not persist at more acidic conditions than pH 4.8 or at conditions more than 0.30 ppm of Cd concentration. Giant duckweeds were intolerable, under conditiions with less than 0.30 ppm of Cd and above than 0.07ppm of Zn, but small duckweeds were tolerable under conditions of more than 0.07 ppm of Zn concentration. However, neither can live above 7.50ppm of Zn concentration. These field observations corresponded with the results of the laboratory experiments.

• 자원환경지질
• /
• 제19권2호
• /
• pp.123-131
• /
• 1986

This study is focused on petrochemistry and petrogenesis of alkali granite which exposed at northern area of the Uljin mine in NE Korea. The rock is corresponded to the range of alkali feldspar granite and alkali feldspar quartz syenite on IUGS classification and contains characteristic Fe-rich biotite (annite) and sodic alkali amphibole (arfvedsonite). The alkali granite is the hypersolvus one-feldspar granite which is characterized by the absence of plagiclase except as a component of perthite and its normatve An contents are less than 5wt%. The bulk compositions of the alkali granite show reverse trends compared to Daly's. Tuttle and Bowen (1958) experimentally support that properties of the hypersolvus granite indicate that they have crystallized at high temperatures from a magma.

• 터널과지하공간
• /
• 제5권4호
• /
• pp.347-362
• /
• 1995

The purpose of this study was that manage effectively the excavation process of the transport tunnel in DONGHAE mine area by investigating the variationof the surface and groundwater flow system around the tunnel and neighbouring villages. Thus, the effect of excavation and water-prrofing process on the water system has been studied through the naked eye survey of the tunnel and the surface outcrop, joint survey, core drilling, the measurement of the surface water quantity, evapotranspiration and precipitation analysis, rock hydraulics approach, the pressure test of boreholes, the variation of the water level, and finally the numerical analysis. From above approachs, we derived the conclusion that the exhaustion of the surface water was not caused by the tunnel excavation on the groundwater system was minimized by effective water proofing process.

• 자원환경지질
• /
• 제40권1호
• /
• pp.15-28
• /
• 2007

이 연구에서는 보은제일광산 주변 밭토양의 오염정도를 주원소, 희토류원소 빛 미량원소를 이용하여 접근해보았다. 이들 연구결과는 충주, 덕평, 보은 및 추부지역의 것들과 비교되었다. 주성분 원소 중 Fe와 S는 비오염예상지역, 충주 및 보은지역 밭토양의 원소보다 높았다. 오염예상지역에서의 미량윈소는 비오염예상지역, 충주, 덕평, 보은 및 추부지역의 함량보다 높았다. 이들 원소들은 상관성과 분산을 기초로 U, Cd, Ni, Sr, V, Zn 등의 원소들과 As, Co, Cu, Mo, Pb, Sb 등의 원소들로 구분되며 두 그룹의 원소들은 원소간에 양의 상관성을 갖는다. 잠재적 독성윈소들의 부화 계수는 오염예상지역에서 5 이상의 값을 갖으며 비오염예상지역에서는 4 미만의 값을 갖는다. 오염예상지역에서 As, Cd, Co, Cu, Mn, Ni, U 및 Zn 원소의 지누적지수는 1 이상의 값을 갖으며, 비오염예상지역에서는 Mn원소를 제외한 모든 미량원소가 1 미만의 값을 갖는다. 잠재적 독성원소에 대한 부화지수에서 오염예상지역($0.3{\sim}87.0$)과 비오염예상지역($0.4{\sim}3.9$)은 차이를 보였다. 전체적인 오염예상지역 밭토양내 원소들(Fe, S, As, Cd, Co, Cu, Ni, U, Zn)의 높은 함량은 광산활동에 의한 오염을 지시한다.

• 한국환경복원기술학회지
• /
• 제6권6호
• /
• pp.72-85
• /
• 2003

The purpose of this study is to establish the basis of the ecological restoration on the limestone mines in Korea, through the research of the revegetation measures of the disturbed slopes in Japanese limestone mines and the analysis of the case of Ibuki and Bukou limestone mines to realize the restoration works successfully. According to the number of mines to carry out the revegetation works increase every year, the revegetation area and amount of planting also go on increasing in Japan. In the small mines the environmental problem is not recognized seriously, but some mines have muchly invested in the revegetation of the damaged land by mines. Ibuki mine in Shiga-gen is practicing the four principles for the restoring of the revegetation in the disturbed slopes by mines. Firstly, the mean slope preserves $37^{\circ}$ in the last rock cut slopes. Secondly, the last rock cut slopes to rehabilitate are covered with the soil dressing 30cm high. Thirdly, the grasses in the mining area are digged up beforehand, and then they are reused to the revegetation works of rock cut slopes. Lastly, from the upper rock cut slopes the revegetation works begin, the process of the above are repeated, as the result, the restoring works will be completed. Upon the ground of these principles, the complex of the original vegetation and the native species seeding, that is, the revegetation technique of Ibuki have established. In the difficult area to revegetate, sodding works, heaping up vegetation-sack, seed-spraying, heaping up soil-sacks and planting works are adapted variously. Bukou mine in Saitama-gen try to maintain the revegetation, the screening and the stability of the enormous mining rock cut slope, and for these works, the activity of 'Chichibu Working Group of Rock Wall for Limestone Mines' contributes largely. The chief technique of the revegetation in Bukou mine is following; after the making the berm on the rock cut slopes, the soil dressing is filled in it, and the trees is planted for the screening of the rock cut slopes. They devide the rock cut slopes into four typical types, and choose the different ways to make the berm and fill the soil dressing in characteristic. Most of the planting trees are consist ofthe native species of Mt. Bukou through the stages of the nursery and transplantation. Not only the revegetation of the demaged land but also the breeding of the conservational plants also are their important business.

• 터널과지하공간
• /
• 제30권5호
• /
• pp.473-483
• /
• 2020

본 연구에서는 3차원 유한차분법(FDM) 프로그램인 FLAC3D를 이용하여 주방식 채광장을 모사하고 채굴적 형성에 의한 현지응력 교란으로 광주에 집중되는 수직응력의 변화를 분석하였다. 오차율과 해석시간을 고려하여 적절한 조합의 요소망 크기를 선정하고 지류론 암반을 모사하여 요소망 조합과 개발 심도에 따른 해석 성능을 검증하였다. 본 해석에서는 개발 영역 내에 1개(1×1)~ 121개(11×11)의 패널 광주가 생성되도록 채굴적을 형성하여 가장 높은 수준의 응력집중이 발생하는 중앙부 광주의 상부 수평단면에 작용하는 수직응력을 측정하였다. 40 m~320 m까지 40 m 단위로 굴착심도를 변경하여 동일한 과정을 반복 수행하였다. 해석 결과, 개발 규모(N_P)가 클수록, 개발심도(H_OB)가 작을수록 중앙부 광주의 수직응력 값이 지류론 추정값에 가까워지는 것을 확인하였다. 또한, 개발 규모가 작고 대심도인 경우에는 지류론에 의한 추정 시 수직응력이 과대평가될 수 있으며, 동일한 개발규모인 경우 심도가 증가할수록 수직응력계수(VSF)가 일정한 값으로 수렴하는 경향이 있음을 확인하였다.

• 대한원격탐사학회:학술대회논문집
• /
• 대한원격탐사학회 2004년도 Proceedings of ISRS 2004
• /
• pp.594-597
• /
• 2004

The ground subsidence that occurred in an abandoned coal mining area, Gaeun, Korea, was observed by using 25 JERS-1 SAR interferograms from November 1992 to October 1998. We estimated the subsidence on a subset of image pixels corresponding to point-wise permanent scatters (PSs) by exploiting a long temporal series of interferometric phases. The results were compared it with a distribution map of in situ examined crack level. PSs were identified by means of amplitude dispersion index and coherence of the interferograms. The measured subsidence rate represented the average velocity in a period of image acquisition and excluded complex nonlinear displacements such as an abrupt collapse. The mean line-of-sight velocity in the study area is 0.19cm/yr and an r.m.s. error is 0.18cm/yr. The center of the abandoned Gaeun coal mine (0.49cm/yr) and the area near to the Gaeun station (1.66cm/yr) were observed as most rapidly subsiding areas.

• 자원환경지질
• /
• 제36권6호
• /
• pp.457-467
• /
• 2003

경상북도 군위군에 위치한 고로 폐아연광산에서 폐광산과 연결된 주 하천을 따라 저수댐 건설 예정지까지 직선 길이 약 12km 구간에서 농경지 토양 및 하천 퇴적토에 대한 중금속 오염(비소, 납, 카드뮴, 구리) 토양정밀조사를 실시하였다. 총 조사 면적은 약 950,000$m^2$ 이고 1,500$m^2$ 당 1지점의 조사 밀도를 유지하여, 총 545개 지점에서 표토(0∼10cm 깊이)를 채취하였으며, 192개 지점에서 심토(10∼30cm 깊이)를 채취하였다. 비소를 제외한 구리, 카드뮴, 납 항목은 모든 지점에서 토양오염우려기준 이하를 나타내었으나, 비소는 표토의 경우 토양오염우려기준 이상의 농도를 나타내는 지점이 104지점으로 전체 표토 조사지점의 20.5% 정도이었으며, 토양오염대책기준을 초과하는 지점은 34지점으로 전체 표토 조사지점의 6.7% 이상이어서 조사 지역 중 상당 부분이 비소로 오염되어 있었다. 심토의 경우 토양오염 우려기준 이상 농도를 나타내는 지점이 18지점으로 전체 심토 조사지점의 약 10.4% 정도이었으며, 토양오염대책기준을 초과하는 지점은 1지점으로 전체 심토 조사지점의 약 0.6%를 나타내고 있어 비소오염이 주로 30cm 이내에 집중되어 있는 것으로 나타났다. 조사지점별 비소농도를 기준으로 토양오염대책기준 농도(15mg/kg) 이상 지역, 토양오염우려기준 농도(6mg/kg) 이상 지역, 토양오염우려기준의 40% 농도(2.4 mg/kg) 이상 지역, 주변배경농도(1.23mg/kg) 이상 지역으로 구분하여 하천퇴적토 및 농경지 토양에 대한 오염지도를 자성하였다. 오염지도 결과로부터, 오염 토양을 복원하기 위한 복원 목표를 토양오염우려기준 농도 이상, 우려기준의 40% 농도 (토양오염확인기준 농도)이상, 배경치 농도 이상으로 구분하여 설정하는 경우에 해당되는 토양 복원 면적과 물량을 산출하였다. 토양오염우려 기준 농도 이상의 경우 총 복원 면적과 물량은 264,000$m^2$, 79,200$m^3$이였으며, 우려기준의 40% 농도 이상의 경우 복원 면적과 물량은 779,000$m^2$, 233,700㎥, 배경치 농도 이상의 복원 목표 설정의 경우에는 각각 969,200$m^2$, 290,760$m^3$ 이였다. 토양오염 우려기준 농도의 40%를 복원 목표로 하는 경우와 배경치 농도를 복원 목표로 하는 경우, 복원 물량은 우려기준 농도를 복원 목표로 하는 경우의 3.0배와 3.7배정도 증가하는 것으로 나타나 복원 목표치 설정시 우려기준 농도의 40%와 배경농도의 차이에 다른 복원 물량의 차이는 적어서, 복원 목표 설정시 배경치 농도로 복원계획을 세우는 것이 가장 바람직한 것으로 판단되었다.

• 자원환경지질
• /
• 제32권6호
• /
• pp.611-631
• /
• 1999

Enviromental geochemisty and heary metal contamination at the Kongjueil mine creek were underaken on the basis of physicohemical properties and mineralogy for various kinds of water (surface, mine and ground water),soil, precipitate and sediment collected of April and December in 1998. Hydrgeochemical composition of the water samples are characterized by relatively significant enricant of Ca+Na, alkiali ions $NO_3$ and Cl inground and surfore water, wheras the mine waters are relatively eneripheral water of the mining creek have the characteristics of the (Ca+Mg)-$(HCO_3+SO_4)$type. The pH of the mine water is high acidity (3.24)and high EC (613$\mu$S/cm)compared with those of surface and ground water. The range of $\delta$D and $\delta^{18}O$ values (relative to SMOW) in the waters are shpwn in -50.2 to -61.6% and -7.0 to -8.6$\textperthousand$(d value=5.8 to 8.7). Using computer program, saturation index of albite, calcite, dolomite in mine water are nearly saturated. The gibbiste, kaolinite and smectite are superaturated in the surface and ground water, respectively. Calculated water-mineral reaction and stabilities suggest that weathing of silicate minerals may be stable kaolinite owing to the continuous water-rock reaction. Geochemical modeling showed that mostly toxic heavy metals may exist larfely in the from of metal-sulfate $(MSO_4\;^2)$and free metal $(M^{2+})$ in nmine water. These metals in the ground and surface water could be formed of $CO_3$ and OH complex ions. The average enrichment indices of water samples are 2.72 of the groundwater, 2.26 of the surface water and 14.15 of the acid mine water, normalizing by surface water composition at the non-mining creek, repectively. Characteristics of some major, minor and rate earth elements (Al/Na, K/Na, V/Ni, Cr/V, Ni/Co, La/Ce, Th/Yb, $La_N/Yb_N$, Co/Th, La/Sc and Sc/Th) in soil and sediment are revealed a narrow range and homogeneous compositions may be explained by acidic to intermediate igneous rocks. And these suggested that sediment source of host granitic gneiss colud be due to rocks of high grade metamorphism originated by sedimentary rocks. Maximum concentrations of environmentally toxic elements in sediment and soil are Fe=53.80 wt.% As=660, Cd=4, Cr=175, Cu=158, Mn=1010, Pb=2933, Sb=4 and Zn=3740 ppm, and extremely high concentrations are found are found in the subsurface soil near the ore dump and precipitates. Normalizing by composition of host granitic gneiss, the average enerichment indices are 3.72 of the sediments, 3.48 of the soils, 10.40 of the precipitates of acid mine drainage and 6.25 of the soils near the main adit. The level of enerichment was very severe in mining drainage sediments, while it was not so great in the soils. mineral composition of soil and sediment near the mining area were partly variable being composed of quartz, mica, feldspar, chlorite, vermiculite, bethierin and clay minerals. reddish variable being composed of quartz, mica, feldspar, chlorite, vermiculite, bethierin and clay minerals. Reddish brown precipitation mineral in the acid mine drainage identifies by schwertmanite. From the separated mineralgy, soil and sediment are composed of some pyrite, arsenopyite, chalcopyrite, sphalerite, galena, malachite, goethite and various kinds of hydroxied minerals.

• 환경영향평가
• /
• 제5권2호
• /
• pp.59-70
• /
• 1996