• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2006.04a
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• pp.128-130
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• 2006

충남 청양군에 위치한 삼광광산의 광미장에서 채취한 것을 사용하여 펄스전원을 이용한 동전기실험 결과 실험경과시간 약 200시간 안에 약 50%의 제거효율을 보여 직류전원을 이용한 동전기 실험보다 빠른 제거속도를 보였다. 또한 직류전원을 이용한 동전기 실험과 펄스전원을 이용한 동전기 실험의 시간당 투입된 전력량을 비교해 보면 각각 5.97W와 1.94W으로 이는 직류전원의 약 30%수준이어서 에너지 절약효과를 기대할 수 있다.

• Economic and Environmental Geology
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• v.37 no.1
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• pp.133-142
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• 2004

The purpose of this study is to evaluate a laboratory test on arsenic removal effciency for ARD(Acid Rock Drain-age) using limestone and apatite, and on heavy metals removal efficiencies for AMD(Acid Mine Drainage) using apatite and fish bone. As a result of the laboratory test, pH, arsenic removal rate of limestone & apatite are inversely proportional to flow rates and apatite removes 100% of arsenic while limestone removes 37% of arsenic at 0.6$m{ell}$/min/kg flow rate in case of ARD treatment. And the dissolution amount of apatite is twenty five times higher than that of limestone. In case of AMD treatment, fish bone shows higher dissolution rate than apatite, and pH of outlet water reacted with fish bone is higher than that reacted with apatite. The heavy metal removal rates of fish bone are also higher than that of apatite except arsenic removal rate. The precipitate resulted from fish bone reaction with AMD seems to be biological sludge type while that resulted from apatite with AMD is inorganic solid which can settle easily compared with the biological sludge and can be cemented by gypsum. As the results, apatite can be used as a precipitant for the polluted mine waters showing wide range of pH and fish bone can be used for highly contaminated AMD.

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2002.05b
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• pp.179-182
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• 2002

기존의 적정 자료로부터 구하는 방법이 아닌 흡착제의 Zeta potential 자료를 바탕으로 구한 값으로도 흡착결과를 잘 모사할 수 있다. 합성 제올라이트의 중금속 이온 제거능은 합성 제올라이트의 종류에 따라서는 중금속 이온의 종류에 관계없이 Na-Pl > SOD > CAN > ANA의 순서로 감소하였다. SCM 모델링의 Fitting을 결정하는 Fitting 변수로서는 총 site 농도(g/$\ell$), site 밀도 (sites/$nm^2$), 비표면적 ($m^2$/g)으로써 결정할 수 있다.

• Proceedings of the Korean Institute of Industrial Safety Conference
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• 1998.05a
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• pp.153-158
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• 1998

산업발달과 더불어 우리의 일상 생활과 밀접한 관계를 갖게된 각종 중금속은 직접적으로는 직업병을 유발함음 물론 간접적으로는 식품류, 수질, 대기 및 토양 등을 오염시켜 만성적 혹은 급성적로 인체에 피해를 가져온다. 이와 관련해서 특히 문제시되는 중금속류로는 납, 카드뮴, 수은, 니켈, 크롬, 비소 등이 있다. 이중에서도 카드뮴에 의한 중독은 대표적인 예의 하나이다. (중략)

• Proceedings of the Korea Air Pollution Research Association Conference
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• 1999.10a
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• pp.92-93
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• 1999

수은은 상온에서 액체상태로 존재하는 유일한 금속으로서, 증기압이 매우 높기 때문에 가장 쉽게 휘발될 수 있는 중금속이다. 다른 중금속들은 거의 입자 상태로 변환되기 때문에 전기 집진기 등과 같은 일반적인 입자 제어시설에서 98％이상이 제거되지만, 증기압이 매우 높은 수은은 다단계 습식 스크러버, 활성탄을 사용하는 전기집진기/습식 스크러버가 결합된 특정한 방지시설에 없는 한 거의 대부분이 그대로 배출된다.(중략)

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 1998.11a
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• pp.245-248
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• 1998

Electrokinetic tests are conducted on laver contaminated with heavy metals to investigate the efficiency of the process in removing Cd, Pb, and Zn. The tests were operated at constant current, and operating time were 0 - 24 hours. The removal efficiency in electro-osmosis with open electrodes is time-dependent. The absorbed Cd, Pb and Zn were removed 50.94-95.75%, 80.78-81.96%, and 48.10-83.83% by the process.

• Proceedings of the Korea Air Pollution Research Association Conference
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• 2000.04a
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• pp.103-104
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• 2000

수은은 상온에서 액체상태로 존재하는 유일한 금속으로서, 증기압이 매우 높기 때문에 가장 쉽게 휘발될 수 있는 중금속이다. 다른 중금속들은 거의 입자 상태로 변환되기 때문에 전기 집진기 등과 같은 일반적인 입자 제어시설에서 98%이상이 제거되지만, 증기압이 매우 높은 수은은 다단계 습식 스크러버, 활성탄을 사용하는 전기집진기/습식 스크러버가 결합된 특정한 방지시설에 없는 한 거의 대부분이 그대로 배출된다. (중략)

• Proceedings of the KAIS Fall Conference
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• 2006.11a
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• pp.321-323
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• 2006

카드뮴으로 오염된 용액을 대상으로 중금속을 고정화 처리하고자 액상인산염을 투입하였다. 액상인산염을 1몰 투입하였을 때, 42.5%의 고정화율을 보였고 알칼리용액의 추가 주입으로 최대 99.5%의 높은 중금속 제거율을 나타내었다.

• Journal of Korean Society of Environmental Engineers
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• v.30 no.5
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• pp.524-533
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• 2008

Industrial wastewater generated in the electroplating and metal finishing industries typically contain toxic free and complex metal cyanide with various heavy metals. Alkaline chlorination, the normal treatment method destroys only free cyanide, not complex metal cyanide. A novel treatment method has been developed which destroys both free and complex metal cyanide as compared with Practical Plant(I). Prior to the removal of complex metal cyanide by Fe/Zn coprecipitation and removal of others(Cu, Ni), Chromium is reduced from the hexavalent to the trivalent form by Sodium bisulfite(NaHSO$_3$), followed by alkaline-chlorination for the cyanide destruction. The maximum removal efficiency of chromium by reduction was found to be 99.92% under pH 2.0, ORP 250 mV for 0.5 hours. The removal efficiency of complex metal cyanide was max. 98.24%(residual CN: 4.50 mg/L) in pH 9.5, 240 rpm with 3.0 $\times$ 10$^{-4}$ mol of FeSO$_4$/ZnCl$_2$ for 0.5 hours. The removal efficiency of Cu, Ni using both hydroxide and sulfide precipitation was found to be max. 99.9% as Cu in 3.0 mol of Na$_2$S and 93.86% as Ni in 4.0 mol of Na$_2$S under pH 9.0$\sim$10.0, 240 rpm for 0.5 hours. The concentration of residual CN by alkaline-chlorination was 0.21 mg/L(removal efficiencies: 95.33%) under the following conditions; 1st Oxidation : pH 10.0, ORP 350 mV, reaction time 0.5 hours, 2nd Oxidation : pH 8.0, ORP 650 mV, reaction time 0.5 hours. It is important to note that the removal of free and complex metal cyanide from the electroplating wastewater should be employed by chromium reduction, Fe/Zn coprecipitation and, sulfide precipitation, followed by alkaline-chlorination for the Korean permissible limit of wastewater discharge, where the better results could be found as compared to the preceding paper as indicated in practical treatment(I).

• Economic and Environmental Geology
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• v.40 no.5
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• pp.575-585
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• 2007

Microbial control of the geochemical behavior of heavy metals (Cd, Cu, Pb, and Zn) and As in contaminated subsurface soil and sediment was investigated through activation of indigenous bacteria with lactate under anaerobic condition for 25 days. The results indicated that dissolved Cd, Pb and Zn were microbially removed from solutions, which was likely due to the formation of metal sulfides after reduction of sulfate by indigenous sulfate-reducing bacteria. Soils from the Dukeum mine containing a large amount of sulfate resulted in complete removal of dissolved As after 25 days by microbial activities, while there were gradual increases in dissolved As concentration in soils from the Hwabuk mine and sediments from the Dongducheon industrial area which showed low $SO_4{^2-}$ concentrations. Addition of appropriate carbon sources and sulfate to contaminated geological media may lead to activation of indigenous bacteria and thus in situ stabilization of the heavy metals; however, potential of As release into solution after the amendment should be preferentially investigated.