• 한국전기전자재료학회논문지
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• 제18권9호
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• pp.803-809
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• 2005

Cerium ammonium nitrate (CAN) and nitric acid was used an etchant and an additive for Ru etching and polishing. pH and Eh values of the CAN and nitric acid added chemical solution satisfied the Ru etching condition. The etch rate increased linearly as the concentration of CAN increased. Nitric acid added solution had the high etch rate. But micro roughness of etched surfaces was not changed before and after etching, The removal rate of Ru film was the highest in $1wt\%$ abrasive added slurry, and not increased despite the concentration of alumina abrasive increased to $5wt\%$. Even Ru film was polished by only CAN solution due to the friction. The highest removal rate of 120nm/min was obtained in 1 M nitric acid and $1wt\%$ alumina abrasive particles added slurry. The lowest micro roughness value was observed in this slurry after polishing. From the XPS analysis of etched Ru surface, oxide layer was founded on the etched Ru surface. Therefore, Ru was polished by chemical etching of CAN solution and oxide layer abrasion by abrasive particles. From the result of removal rate without abrasive particle, the etching of CAN solution is more dominant to the Ru CMP.

• 한국지반공학회:학술대회논문집
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• 한국지반공학회 2008년도 춘계 학술발표회 초청강연 및 논문집
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• pp.229-241
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• 2008

In order to investigate stabilization effect on As-contaminated soils treated by zero-valent iron(ZVI) and industrial by-products, batch tests and column tests were carried out with As-contaminated soils collected from farmland around the abandoned mine site. In batch tests, ZVI and industrial by-products(blast furnace slag, steel refining slag and oyster shell powder) were used as treatment materials to reduce As. Industrial by-products were mixed with As-contaminated soils, in the ratio of 1%, 3%, 5% and 7% on the weight base of dried soil. After incubation, all samples showed the reduction of As concentration and it was expected that ZVI and steel refining slag were effective treatment materials to remove As among treatment materials used in batch test. In column tests, columns were made by acrylic with the dimension of diameter=10cm, height=100cm, thickness=1cm and these columns were filled with untreated soils and treated soils mixed with ZVI and steel refining slag(mixing ratio=3%). Distilled water was discharged into the columns with the velocity of 1 pore-volume/day. During test, pH, EC, Eh and As concentration were measured in the regular term(1 pore-volume). As a result, ZVI and steel refining slag were shown 93%, 62% reduction of As concentration respectively by comparison with untreated soils. Therefore, if ZVI and steel refining slag are used as treatment materials in As-contaminated soils, it is expected that the As concentration in soils is reduced effectively.

• 한국환경과학회지
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• 제20권8호
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• pp.963-975
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• 2011

For this research, they were monitored $CO_2$ flux and environmental factors ($CO_2$ concentration, soil temperature, soil moisture, soil organic carbon, soil pH, soil Eh) in foreshore, paddy field and woods sites at the winter season (January 2009) and the summer season (September 2009). Seasonal and spatial variations for monitored data were analyzed, and linear regression functions of $CO_2$ flux as environmental factors were estimated. $CO_2$ fluxes averaged between surface and atmosphere monitored in foreshore and paddy field at the winter season were shown $-8\;mgCO_2m^{-2}hr^{-1}$ and $-25\;mgCO_2m^{-2}hr^{-1}$, respectively. $CO_2$ fluxes averaged between surface and atmosphere monitored in foreshore and paddy field at the summer season were shown $47\;mgCO_2m^{-2}hr^{-1}$ and $117\;mgCO_2m^{-2}hr^{-1}$, respectively. Thus, $CO_2$ was sunk from atmosphere to surface at the winter season and it was emitted from surface to atmosphere at the summer season. $CO_2$ fluxes in woods site were emitted $145\;mgCO_2m^{-2}hr^{-1}$ at the winter season and $279\;mgCO_2m^{-2}hr^{-1}$ at the summer season.

• 자원환경지질
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• 제33권3호
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• pp.181-193
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• 2000

This study was undertaken to evaluate the drinking water quality based on physicochemical properties and chemical compositions of the supply water in the Daedeok Campus, and to verify the analytical reliabilities of ICP-MS and IC equipped in the Central Research Facilities at Chungnam National University , Korea. The supply water belongs to $Ca^{2+}-({HCO_3}^-+{SO_4}^{2-})$type, whereas the original water from the Daecheong lake belongs to $(Ca^{2+}-(Mg^{2+})-{HCO_3}^-$ type. Generally, temperature (14.1$^{\circ}C$), pH (6.95), Eh (0 mV), electrical conductivity (117${\mu}$S/cm) and TDS (86.975mg/l) of supply water were higher than those of original lake water . Results using WATEQ4F revealed that potentially toxic ions of the supply water might exist mainly as free metals ($M^{2+}$) and a small amount as ${CO_3}^{2-}$ and $OH^-$ complexes. Also, the water composition belongs to the kaolinite field. Calculated average enrichment indies of the supply water normalized to lake water for anions, mamor cations, toxic cations and total ions are 1.05 , 1.56, 13.05 and 1.17 , respectively. Those values of the ground water in the Daedeok Campus showed 1.71, 4.78, 5.71 and 2.49 , respectively. However , contents of all constituents of these water are within the drinking water standard. All samples were filtered before the chemical analysis. Pale yellow or yellowish brown colored materials of colloidal particles coated the filter paper to thickness of 0.02 to 0.2mm. these are mainly Fe-Cy-Zn compounds with traces of Ni and Pb, the net weights of which compounds range from 0.01to 3.20mg/l. Most elements did not show any conceivable filtering effect of Cu, Fe and Zn. Especially, mean concentration of total Fe decreased considerably from 168.52${\mu}g$/lto 42.58${\mu}g$/l by filtering .

• 한국환경농학회지
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• 제26권2호
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• pp.141-148
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• 2007

Fly ash, a by-product of the coal-burning industry, and a potential source of ferro-alumino-silicate minerals, which contains high amount of ferric oxide and manganese oxide (electron acceptors), was selected as soil amendment for reducing methane $(CH_4)$ emission during rice cultivation. The fly ash was applied into potted soils at the rate of 0, 2, 10, and 20 Mg $ha^{-1}$ before rice transplanting. $CH_4$ flux from the potted soil with rice plants was measured along with soil Eh and floodwater pH during the cropping season. $CH_4$ emission rates measured by closed chamber method decreased gradually with the increasing levels of fly ash applied but rice yield significantly increased up to 10 Mg $ha^{-1}$ application level of the amendment. At this amendment level, total seasonal $CH_4$ emission was decreased by 20% along with 17% rice grain yield increment over the control. The decrease in total $CH_4$ emission may be attributed due to suppression of $CH_4$ production by the high content of active and free iron, and manganese oxides, which acted as oxidizing agents as well as electron acceptors. In conclusion fly ash could be considered as a feasible soil amendment for reducing total seasonal $CH_4$ emissions as well as maintaining higher grain yield potential under optimum soil nutrients balance condition.

• 한국지반공학회:학술대회논문집
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• 한국지반공학회 2008년도 추계 학술발표회
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• pp.1463-1474
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• 2008

In order to investigate stabilization effect and sustainability on As-contaminated farmland soils which were affected the abandoned mine site and stabilized by zerovalent iron(ZVI) and industrial by-products, batch-scale and pilot-scale tests were carried out. In batch tests, ZVI and industrial by-products(blast furnace slag, steel refining slag and oyster shell powder) were used in treatment materials to reduce the As leaching. Industrial by-products were mixed with As-contaminated soils, in the ratio of 1%, 3%, 5% and 7% on the weight base of dried soil. The results of batch-scale tests was shown that the reduction of As concentration was observed in all samples and it was expected that ZVI and steel refining slag were more effective than other treatment materials to stabilize As compounds. In pilot-scale tests, columns were filled with untreated soils and treated soils mixed with ZVI and steel refining slag in the same mixing ratio of 3%. Distilled water was discharged into the columns with the velocity of 0.3 pore volume/day. During the test, pH, EC, Eh and As concentration were measured in the regular term(1pore volume). after six months, pilot-scale tests were retested to investigate sustainability of treatment materials. As a result, It was shown that the leachate from control column was continuously released during the test period and its concentration was greater than $100ug{\cdot}L^{-1}$ which was exceeded the national regulation of water discharged to river or stream ($50ug{\cdot}L^{-1}$). On the other hand, soil treated with ZVI and steel refining slag showed that the concentrations of leachate were lower than national regulation of water discharged to river or stream. Therefore it was expected that ZVI and steel refining slag could be applied to the farmland site as the alternative treatment materials.

• 한국식생활문화학회지
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• 제23권2호
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• pp.235-242
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• 2008

In this study, the physicochemical and microbiological properties of market-available skate (Raja kenojei) kimchi were evaluated in comparison to long-term fermented Baechu kimchi. The comparative results for the skate (Raja kenojei) and Baechu kimchi products are as follows: salt concentrations = 3.40% and 3.95%, respectively; pH and acidity values = 4.01 and 3.90, and 0.65% and 0.82%, respectively; redox potential Eh values = 119.82 mV and 123.08 mV respectively; reducing sugars levels = 15.51 mg% and 13.23mg%, respectively; ascorbic acid levels = 24.21mg% and 22.18mg%, respectively; color L-values = 46.86 and 44.54, a-values = 15.46 and 12.28, and b-values = 29.94 and 28.36, respectively; hardness properties = 11.36 kgf and 10.23 kgf, respectively; hot water soluble pectin (HWSP) contents and sodium hexametaphosphate soluble pectin (NaSP) contents = 15.23% and 17.35%, and 32.51% and 29.64%, respectively; hydrochloric acid soluble pectin (HClSP) contents = 55.1% and 53.2%, respectively; total viable cell counts = $4.78{\times}10^8$ and $1.35{\times}10^8$, respectively; lactic acid bacteria counts = $5.18{\times}10^5$ and $1.32{\times}10^5$, respectively; and yeast levels = $8.52{\times}10^5$ and $5.23{\times}10^5$, respectively.

• 한국광물학회지
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• 제21권2호
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• pp.139-159
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• 2008

지하유류비축기지의 수리안정성 평가를 위하여 비축기지 내 관측공을 포함한 공동 주변 지하수의 지화학분석을 수행하였으며, 결과를 근거로 광물학적 클로깅의 가능성을 평가하고, 아울러 미생물학적인 클로깅 가능성을 함께 고려하여 보았다. 물시료들은 대부분 $Ca-HCO_3$에서 $Ca-HCO_3-SO_4$ 유형에 속하며 물시료의 유형에 따른 차이를 보이지 않는다. 주요 클로깅 유발광물인 방해석은 모든 관측공 및 공동운영수 시료에서 불포화상태로서 탄산염 광물에 대해 침전하지 않는 지화학 환경이다. Fe, Mn은 대부분 낮은 함량을 보이지만 포화지수계산결과에 의하면 대부분 철-산화/수산화 광물에 대해 포화-과포화 상태를 보여주며 높은 용존산소 농도를 보여주기 때문에 장기적으로는 이들에 의한 클로깅의 가능성을 지시한다. 일부 지상 관측공 물시료의 경우에는 철-산화/수산화 광물과 더불어 미세한 열극을 충전할 수 있는 점토광물에 대하여 높은 포화 지수를 보여주어 이들 광물의 침전에 의한 클로깅 가능성을 지시하고 있다. 통계분석 결과, 광물들의 침전/용해 정도는 주로 pH, Eh, DO에 의해 좌우된다. 미생물 분석결과는 대부분의 물시료에서 호기성 미생물과 점액성 세균이 우세하며 황환원세균 등의 혐기성균은 대부분 아주 적거나 검출이 되지 않았다. 클로깅을 유발시키는 미생물로 알려져 있는 점액성 세균은 모든 시료에서 $10^5\;CFUs/mL$ 이하의 값을 나타내고 있지만, 일부 관측공들에서 점액성세균이 우점하고 있기 때문에 장기적 관점에서는 이들이 클로깅의 원인으로 작용할 수 있으며 철 수산화/산화 광물의 침전가능성과 함께 고려하면 클로깅 가능성이 더욱 상승되는 효과를 가져올 수 있기 때문에 지하유류비축기지의 안정적인 운영을 위하여 클로깅 평가와 관련된 체계적이고 장기적인 프로그램이 필요하다.

• 한국미생물·생명공학회지
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• 제34권2호
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• pp.166-173
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• 2006

본 연구는 매립지 침출수로 오염된 지하수에서 수지화학적 분석결과와 미생물 군집구조 사이의 관계를 밝히기 위해 수행되었다. 이 연구를 위해 5개의 시료, 즉 침출수(KSG1-12), 처리수(KSG1-16), 두 개의 오염 지하수(KSG1-07과 KSG1-08), 비오염 지하수(KSG1-13)를 채취하여 분석하였다. 각 시료의 pH는 순서대로 8.83, 8.04, 6.87, 6.87, 6.53이였으며, 산화환원전위(Eh)는 각각 108, 202, 47, 200, 154 mV 이였고, 전기전도도(EC)는 3710, 894, 1223, 559, 169.9 $\mu$S/cm이였으며, 부유물질(SS)의 농도는 각각 86.45, 13.74, 4.18, 0.24, 11.91 mg/L이었다. KSG1-12 시료의 음이온 농도가 전체적으로 높았는데, 특히 염소이온($Cl^-$)와 중탄산염 ($HCO_3^-$)이 높았다. 기타 전자수용체와 관련 있는 이온들의 농도에서, 철(Fe), 망간(Mn), 황산염($SO_4^{2-}$)은 KSG01-08보다 KSG1-07에서 더 높았고 질산염은 반대로 나타났다. DGGE fingerprint 분석을 통한 유사도 비교는 KSG1-13과 KSG1-16이 57.2%로 가장 높았는데, 둘 다 오염도가 낮거나 오염이 전혀 없기 때문으로 추정된다. 한편, KSG1-08은 KSG1-13과 25.8% 그리고 KSG1-12와 27.6%의 유사성을 나타냈는데 이는 오염도의 차이 때문일 것으로 사료된다. 각 시료 별 우점종들의 가장 많이 분포된 계통발생학적 집단을 보면 KSG1-12는 분석된 클론 중 55.6%가 $\alpha$-Proteobacteria에 속하였고, KSG1-16은 50.0%가 $\gamma$-Proteobacteria, KSG1-07은 66.7%가 $\beta$-Proteobacteria, KSG1-08은 54.5%가 $\gamma$-proteobacteria, KSG1-13은 36.4%가 $\beta$-Proteobacteria에 속하였다. 이러한 결과를 통해 매립지 침출수가 지하수를 따라 흐르면서 미생물 군집구조가 바뀌었음을 알 수 있었는데, 오염물질의 농도변화, 이용 가능한 전자수용체, 및 기타 여러 환경요인들의 차이에 의한 것임을 추측할 수 있다.

• 한국광물학회지
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• 제19권4호
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• pp.265-275
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• 2006

미생물을 이용한 원석 또는 폐석으로부터 인류에 유용한 원소 및 중금속의 용출은 초기 연구단계에 있는 새로운 생물학적 기술 중의 하나이다. 본 연구의 목적은 갯벌 퇴적물에서 분리한 미생물(Microcosm)을 이용하여 자철석으로부터 철의 용출 및 용출된 철의 생광화작용에 따른 2차 물질의 형성을 규명하고자 한다. 갯벌퇴적물에서 분리한 철 환원 박테리아(Microcosm)가 글루코스($10{\sim}20mM$)를 이용하여 성장하는 동안 자철석으로부터 철의 용출 및 2차 물질의 형성을 ICP, XRD, SEM-EDX 및 TEM을 이용하여 연구하였다. 미생물배지에 상업용 자철석(미생물배지 : 자철석 = 100 : 1)과 철환원 박테리아를 넣고 혐기성 및 호기성 조건하에서 철 용출 및 2차 물질의 형성실험을 실시한 결과, 철의 용출 실험동안 미생물배지의 Eh는 호기성 조건에서 +250 mV에서 -520 mV 까지 감소하고, pH 7.3에서 5.5까지 감소하였다. 혐기성 환경에서 박테리아의 활동에 따라 15일째 자철석으로부터 94 ppm의 Fe를 용출하였으며, 박테리아가 없는 혐기성 조건 하에서는 0.9 ppm의 Fe의 용출을 보여 주었다. 호기성 환경에서 박테리아의 활동에 따라 자철석으로부터 15일째 107 ppm의 Fe를 용출하였다. 배양을 시작한지 1개월이 지난 시점에서는 미생물배지에 용출되어 있는 Fe가 혐기성 조건에서는 57ppm의 Fe가, 호기성 조건하에서는 6.5 ppm의 Fe 각각 존재하였다. 박테리아가 배양되는 동안 용출된 철의 감소는 2차물질의 형성에 철이 소비된 것으로 사료되며, 호기성 조건하에서는 적갈색의 2차 물질 형성을 보여주었다. 미생물에 의한 자철석으로부터 철과 망간의 용출은 미생물의 활동에 따른 미생물배지의 열역학적인 조건(Eh/pH)의 변화 및 유기물의 산화에 따른 유기산의 형성에 기인한 것으로 사료된다. 미생물을 이용한 결정질의 자철석으로부터 철의 용출 및 비정질의 2차물질의 형성은 미생물의 퇴적물 내에서 철의 순환에 중요한 역할을 담당할 뿐만 아니라 미생물을 이용한 유용물질의 침출(Bioleaching) 및 생광화작용에 따른 광물의 합성 가능성을 시사한다.