• Environmental engineer
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• s.174
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• pp.22-26
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• 2001

(1) 토양오염의 특성과 현황 - 토양오염은 지하에서 일어나는 오염문제이므로 눈으로 직접 확인하기가 어려울 뿐만 아니라 한번 오염되면 복원을 위해서 많은 시간과 경제적 노력이 필요함 - 우리나라에서는 폐광지대 그리고 공업단지 내 유류 저장시설 주변 토양이 중금속과 유기화합물로 심각하게 오염되어 있는 것으로 나타남 (2) 오염토양 정화기술의 분류와 주요기술 - 오염토양 정화기술은 크게 비원위치 기술과 원위치 기술로 분류되며 각각 물리적, 화학적, 생물학적

• Proceedings of the Korean Institute of Industrial Safety Conference
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• 1998.05a
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• pp.163-169
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• 1998

휴$\cdot$폐광에 따른 토양오염현상은 폐광의 광미사등에 축적된 중금속이나 화학처리제 등의 오염인자들이 용출수나 지하수, 강수 및 비산분진등에 의해 광범위한 지역으로 확산되는 것으로 알려져 있다. 특히 광산의 갱이나 광미사의 퇴적장으로부터 유출되는 유해 중금속들로 인한 토양오염은 주변하천의 농업용수를 오염시켜 농작물에 피해를 주게 되므로 작물의 생육에 지장을 가져올 뿐만 아니라 수확량이 감소되고 또 오염된 농작물을 섭취한 인간이나 동물들에게 만성적인 장해를 일으키기도 한다. (중략)

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2008.11a
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• pp.472-475
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• 2008

중금속으로 오염된 토양을 안정화하고자 석탄 광산 배수 처리 시 발생되는 슬러지를 이용하여 중금속 용출 실험을 실시하였다. 용출 실험을 위하여 슬러지를 무게비율로 0%, 1%, 3%를 완전혼합하고, 3%슬러지를 오염토양과 층을 이루어 용출 실험을 실시하였다. 유입 pH를 5.5-6.2와 3-4로 조절하여 용출실험을 실시한 결과 Cu, Zn, Pb, Cr의 용출 농토는 3% M<3% S<1% M<0% 순으로 나타났다. 오염토양 무게 비율로 3% 슬러지를 완전혼합 시 중금속 용출 실험 결과 20년 기준 안정성을 확보할 수 있었다.

• Journal of the Korea Organic Resources Recycling Association
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• v.19 no.4
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• pp.90-96
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• 2011

In order to remediate contaminated soils with heavy metals, many techniques have been developed and proposed. However, weakness for the various techniques has been making application for actual process difficult. They have been led to the necessity for novel techniques. Therefore, in this study, novel techniques which are developing and commercializing recently in domestic/foreign country will be introduced, especially it will be focused on remediation technique for contaminated soil with heavy metals using magnetic material.

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2005.05a
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• pp.186-187
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• 2005

본 연구는 대구 ${\cdot}$ 울산을 대상으로 토양 내의 중금속 함량이 서로 다를 것으로 예상되는 주택지역, 도로와 인접한 주거지역, 공단지역으로 구분한 후 지역별 농도분포를 분석하고, 중금속 오염도의 실태를 파악하여 오염된 토양에 대한 효율적인 관리에 그 목적이 있다. 분석항목으로는 인체에 유해한 중금속인 As, Cr, Hg, Zn, Cd, Pb, Cu항목을 선정 하였으며, 기타 일반금속으로는 Fe, Si, Mg, Ca, Al, Na, K항목에 대해 분석하였다. 분석을 토양오염공정시험법에 따라 시행하였고 ICP로 측정하였다. 분석결과 대구 ${\cdot}$ 울산의 지역별 중금속 함량은 공단지역이 가장 높으며, 도로와 인접한 주거지역 및 주택지역 순으로 나타났다. 2003년 전국평균오염도와의 비교 분석 결과 대구의 경우 모든 지역이 전국평균오염도보다 낮게 검출되었으나, 울산의 경우 Cd, As, Zn의 함량이 1.619mg/kg, 75.05mg/kg, 238.707mg/kg으로 기준치보다 초과하여 검출되었다.

• Journal of Korea Soil Environment Society
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• v.4 no.2
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• pp.87-101
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• 1999

This study has been carried out to examine the feasibility of washing technique for reducing the heavy metal contamination level of tailing wastes and agricultural soil surrounding abandoned metal mines. Some organic acids with low molecular weight were used as washing solution. Initial contamination levels of copper and lead for some soil samples were found to exceed the standard levels of countermeasure and concern, and those of cadmium to approach the standard level of countermeasure. Experimental results using sequential extraction method revealed that more than half of copper and lead existing in tailing wastes are adsorbed forms available for plants. There are some proportional relationships between metal concentrations determined by using 0.1N HCI solution and those determined by sequential extractions. Citric acid was turned out to be superior to oxalic acid and acetic acid with low molecular weight in washing above three metals. When citric acid is used for washing heavy metals from soil, it is desirable to operate at pH less than 5.5 for better washing effect. Metal removal effect by citric acid solution has been proved to depend upon solution concentration and the mass ratio of solution to soil. Addition of SDS(Sodium Dodecyl Sulfate) to citric acid improved the washing effect of cadmium among three metal most significantly. while copper removal did not change. Washing technique using citric acid for removal of heavy metals from agricultural soil or tailing wastes is recognized to be an effective remediation method.

• Korean Journal of Soil Science and Fertilizer
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• v.43 no.5
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• pp.674-683
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• 2010

The current study was performed to examine the agricultural suitability of the cultivated upland nearby abandoned mining areas in Korea using three different scientific risk assessment models of Korea, USA and UK. For this, three mining sites DM, MG and KS were selected among 687 abandoned mines through preliminary risk assessment. A wide range of parameters were obtained through analysis of both soil and crop samples from the selected areas for heavy metal concentration and questionnaires to the communities along with the selected mining sites. Heavy metal concentration in soil samples was lower than the values previously reported by the Ministry of Environment (ME, 2002). However, both As and Cd concentration in the soil samples exceeded the concern level for agricultural area of the Soil Environment Conservation Act. Judging from the contaminant criteria for the crops, only Zn level in pepper, soybean and corn from the mining area DM exceeded the criteria whereas As, Cd, $Cr^{6+}$, Cu, Hg, Ni, Pb did not exceed the criteria. It was demonstrated that there would be human health risk by Pb accumulated in crops from both mining areas MG and KS when estimated by the risk assessment models of Korea and USA. Against it, results of the risk assessment model of UK showed human health risk by Pb in the crops from all study areas.

• Journal of the Korean Geosynthetics Society
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• v.9 no.4
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• pp.57-66
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• 2010

This study is described in heavy metal pollution by the stony mountain development using field case. The heavy metal pollution is investigated for nearby area (soil and stream) of the developed stony mountain, and then the countermeasure using contamination analysis is suggested. The investigation result indicated that contamination of Sammak stream caused by the stone dust and leachate at the stony mountain development. Therefore, the heavy metal pollution is evaluated by using Pollution Index(PI). The evaluation results confirmed that the contaminated groundwater was the leading cause of the contamination in Sammak stream and nearby soil. Therefore, the Permeable Reaction Barrier(PRB), which has a environmentally-friendly reactant, should be applied to control a heavy metal of groundwater, and it will be a reasonable countermeasure.

• Journal of Soil and Groundwater Environment
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• v.10 no.6
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• pp.56-62
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• 2005

Chemical analyses are generally used to assess contaminated soils and to monitor the efficiency of soil remediation. In this study, the ecotoxicological methods was suggested to evaluate soil pollution by using a battery of bioassay. Plant assay and earthworm assay were conducted to evaluate ecotoxicity o soils contaminated by heavy metals (cadmium and copper) and oil (BTEX compounds, toluene). Test plants were Zea may, Triticum aestivum, Cucumis sativus, and Sorghum bicolor. The presence of heavy metals decreased the seedling growth. Cucumis sativus and Sorghum bicolor seemed to be good indicator plants which are sensitive to heavy metal pollution as well as BTEX contamination. An earthworm bioassay was performed to predict the ecotoxicity in toluene-contaminated soils, based on a simple contact method. Perionyx excavatus was adopted as a test earthworm species, and the severity of response increased with increasing toluene concentration. The present study demonstrated that ecotoxicological methods could be a quantitative approach to evaluate contaminated soils.

• Economic and Environmental Geology
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• v.46 no.6
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• pp.509-520
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• 2013

In this study, heavy metals are removed by soil washing from soils contaminated with Cu, Zn, and Pb, whose maximum concentrations are up to 3350, 1220, and 2240 mg/kg, respectively. Through various soil washing experiments, the optimum conditions, including type and concentration of washing reagent, washing time, mixing ratio of soil and washing reagent, and stirring speed, are derived for effective removal of the heavy metals. It is found that the most effective washing reagent and its concentration are hydrochloric acid and 50 mM, respectively. The most suitable washing time is 30 minutes and the optimal mixing ratio of soil and washing reagent is 1:30 (g/mL). The removal efficiency, on the other hand, is not affected by stirring speed. The removal efficiencies of the heavy metals decrease when washing reagent is reused. Furthermore, the heavy metals are readsorbed onto soil in case of consecutive reuse of washing reagent.