• 한국지하수토양환경학회지:지하수토양환경
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• 제19권3호
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• pp.1-14
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• 2014

It is necessary to decide the pumping rate and pumping well location together with the capture zone in order to determine an appropriate groundwater remediation strategy to manage the contaminated groundwater. The relationship between the capture zone and the drawdown radius of influence ($ROI_s$) was considered. $ROI_{cs}$ is defined as the distance where the criteria of drawdown is cs meter from pumping well in this paper. A method to decide the required pumping rate for the remediation of contaminated groundwater in order to create appropriate $ROI_{cs}$ is suggested by using the Theis equation (1935) and Cooper-Jacob equation (1946). It was shown in this study that $ROI_{cs}$ is in proportion to the pumping rate and the criteria of drawdown, which decides $ROI_{cs}$, is inversely proportional to Ti value (transmissivity ${\times}$ hydraulic gradient). The pumping rate which creates the required $ROI_{cs}$ could be planned through the relationship between the $ROI_{cs}$ and pumping rates ($ROI_{cs}$-Q curve) of the field sites 1, 2 and 3. If the drawdown is investigated along with Ti value and pumping rate at a specific site where pump and treat remediation is planned, it is expected that the required criteria of drawdown can be evaluated by using the relationship between the cs and Ti (cs-Ti curve).

• 한국지하수토양환경학회지:지하수토양환경
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• 제20권1호
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• pp.1-6
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• 2015

The objectives of this study were to calculate the radius of influence (ROI) of well for an air-sparging (AS)/soil vapor extraction (SVE) system and to evaluate the applicability of the system applied for the remediation of the petroleum contaminated rail site. For air permeability test, three monitoring wells were installed at a location of 1.3 m, 2.3 m, 3.0 m from the extraction well. And the pressure of each monitoring well was measured by extracting air from the extraction well with the pressure and flow of $(-)2,600mmH_2O$ and $1.58m^3/min$. The ROI for an extraction well was calculated as 4.31 m. Air was injected into the injection well with the pressure and flow of $3,500mmH_2O$ and $0.6m^3/min$ to estimate the radius of influence for oxygen transfer. Oxygen concentrations of air from three monitoring wells were measured. The ROI of an injection well for oxygen transfer was calculated as 3.46 m. The 28 extraction wells and 19 injection wells were installed according to the ROI calculated. The AS/SVE system was operated eight hours a day for five months. The rail site was contaminated with the petroleum and concentrations of benzene, toluene, and xylene were over the 'Worrisome Standard' of the 'Soil Environment Conservation Act'. The contaminated area was estimated as $732m^2$ and contaminants were dispersed up to (-)3 m from the ground. During the operation period, soil samples were collected from 5 points and analyzed periodically. With the AS/SVE system operation, concentrations of benzene, toluene, and xylene were decreased from 7.5 mg/kg to 2.0 mg/kg, from 32.0 mg/kg to 23.0 mg/kg, from 35.5 mg/kg to 23.0 mg/kg, respectively. The combined AS/SVE system applied to the rail site contaminated with volatile organic compounds (VOCs) exhibited a high applicability. But the concentration of contaminants in soil were fluctuated due to the heterogeneous of soil condition. Also the effect of the remediation mechanisms was not clearly identified.

• 지질공학
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• 제20권2호
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• pp.127-136
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• 2010

본 연구에서는 현장에서 수행한 단계양수시험을 이용하여 최적 양수량, 우물효율 및 양수 영향반경을 산정하였다. 시험결과 최적 양수량은 KDPW 1, KDPW 2에서 수위강하가 0.5, 1.0 m 일어났을 때 각각 9.37, 16.20 $m^3/day$과 8.11, 14.10 $m^3/day$으로 계산되었다. 또 우물효율은 KDPW 1에 대하여 72.02~90.73%의 효율을 그리고 KDPW 2에 대하여 70.62~88.52%의 효율을 보였다. 한편 정류상태 해석으로 영향반경은 KDPW 1에서 양수하였을 경우 관측정에서 3.50~31.92 m로 계산되었다. 또 KDPW 2에서 양수하였을 경우 관측정에서 영향반경이 0.14~37.43 m로 산정되었다. 부정류 해석결과에 따르면 KDPW 1에서 양수하였을 경우 관측정에서 영향반경이 0.02~8.34 m로 계산되었다. 그리고 KDPW 2에서 양수하였을 경우 관측정에서 영향반경이 0.24~9.68 m로 계산되었다. 본 연구에서 적용한 방법론은 오염지하수 양수처리법의 설계에 실용적으로 활용될 수 있을 것으로 사료된다.