• 대한화학회지
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• 제46권6호
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• pp.509-514
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• 2002

정지흐름분석법을 이용하여 화학발광법으로 수용액 중의 Fe(II)와 Fe(III)을 분리 정량하는 방법에 대하여 연구하였다. 이 방법은 lucegenin과 $H_2O_2$ 혼합용액에 Fe(III)이온을 첨가하였을 때 화학발광의 세기가 증가하는 것을 기초로 하였다. KO H, $H_2O_2$ 및 Fe(III)의 가리움제로 이용한 citric acid의 농도와 시료의 주입속도가 화학발광의 세기에 미치는 영향을 조사하였다. 전체 철의 정량을 위하여 구한 [$H_2O_2$], [KOH] 및 흐름속도의 죄적조건은 각각 4.0M, 2.0M, 및 3.5mL/min 이었고, 이러한 최적조건 하에서 얻은 검정곡선에서 직선성이 성립하는 범위는 1.0${\times}10^{-6}$M에 서 1.0${\times}10^{-4}$M이었고, 상관계수는 0.996, 검출한계는 1.0${\times}10^{-7}$M이었다. Fe(III)이온의 정량을 위하여 구한 [$H_2O_2$], [KOH], [citric acid] 및 흐름속도의 최적조건은 각각 4.0M, 2.0M, 0.01M 및 3.5mL/min이었고 이러한 최적조건 하에서 얻은 검정곡선에서 직선성이 성립하는 범위는 1.0${\times}10^{-6}$M에서 1.0${\times}10^{-4}$M이었고, 상관관계수는 0.997, 검출한계는 5.0${\times}10^{-7}$M이었다.

• 상하수도학회지
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• 제30권1호
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• pp.87-97
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• 2016

First of all, Fe or/and Mn immobilized granular activated carbons (Fe-GAC, Mn-GAC, (Fe, Mn)-GAC) were synthesized and tested to remove arsenate (As(V)). The results in batch test indicated that Fe-GAC removed As(V) effectively, even though the surface area of Fe-GAC was reduced largely. Moreover, adsorption isotherm test indicated that the experimental data fit well with Langmuir model and the maximum adsorption capacity ($q_{max}$) of Fe-GAC for As(V) was $3.49mg\;g^{-1}$, which was higher than GAC ($2.24mg\;g^{-1}$). In column test, the simulated water, which consisted of As(V), Fe(III), Mn(II) and Ca(II) in tap water, was used. Fe-GAC column with 1 hr of pre-washing time treated As(V) effectively while GAC column removed Fe(III) better than Fe-GAC column. Moreover, the increasing pre-washing time from 1 to 9 hour in Fe-GAC column enhanced Fe(III) removal with little negative impact of As(V) removal. Mostly, the column filled with Fe-GAC and GAC (i.e. the mass ratio of Fe-GAC:GAC = 2:8) showed the higher treatability of both As(V) and Fe(III), even it operated with 1 hr pre-washing time.

• 약학회지
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• 제40권6호
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• pp.670-678
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• 1996

The combinations of N-4-salicyloamido-2-amino-6-piperidinopyrimidine 3-oxide (Salmi) and two transitional metals were colored. Among metals, Fe(III) made a distinct colored comp lex with Salmi. The mole ratio of Salmi and Fe(III) in the complex was 1:1. This Salmi-Fe(III) complex was recrystallized in Hexane/Acetone(=10/1, v/v) and investigated its physicochemical properties. The color of this complex was changed by pH.; deep violet pink in acids, orange in neutral, and yellow in bases. The range of color change was approximately 0.7 pH unit. Acid-base titration of various acidic or basic drugs using Salmi-Fe(III) complex as an indicator showed good accuracy and reproducibility.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 1999년도 추계학술발표회
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• pp.81-84
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• 1999

The aqueous geochemical characteristics of Cr(III) and Cr(Ⅵ) in environmental systems are very different from one another: Cr(Ⅵ) is highly soluble, mobile and toxic relative to Cr(III) Reduction of Cr(Ⅵ) to Cr(III) are beneficial in aquatic systems because of the transformation of a highly mobile and toxic species to one having a low solubility in water, thus simultaneously decreasing chromium mobility and toxicity. Fe(II) species are excellent reductants for transforming Cr(Ⅵ) to Cr(III), and in addition, keeping Cr(III) concentrations below the drinking water standard of 52 ppb at pH values between 5 and 11. Investigations of the effects of NOM on Cr(Ⅵ) reduction are for examining the feasibility of using ferrous iron to reduce hexavalent chromium in subsurface environments. Experiments in the presence of soils, however, showed that the solid phase consumes some of the reducing capacity of Fe(II) and makes the overall reduction kinetics slower. The soil components bring about consumption of the ferrous iron reductant. Particular attention is devoted to the complexation of Fe(II) by NOM and the subsequent effect on Cr(Ⅵ) reduction. Cr(Ⅵ) reduction rate by Fe(II) was affected by the presence of NOM (humic acid), The effects of humic acid was different from the solution pH values and the concentration of humic acid. It was probably due to the reactions between humic acid and Cr(Ⅵ), humic acid and Fe(II), and between Cr(Ⅵ) and Fe(II), at each pH.

• 대한화학회지
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• 제20권1호
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• pp.35-42
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• 1976

사면체 구조를 갖는 철(III)-옥살산 착화합물 5개와 팔면체 구조를 갖는 착화합물을 3개를 합성한 후 화학분석과 적외선스펙트럼을 이용하여 이들 착이온의 구조에 관하여 연구하였다. 이들중 $[FeC_2O_4Br_2]^-,$ $[FeC_2O_4(NCS)_4]^{3-}$ 및 $[Fe_2(C_2O_4)_3Cl_4]^{4-}$등의 3개의 피리딘염은 아직 보고되지 않은 새로운 착물이며, 특히 이합체로 생각되는 착물 $(PyH)_4[Fe_2(C_2O_4)_3Cl_4]$는 광화학 반응성이 아주 큼을 알 수 있었다. 이들 여러 철(III)-옥살산 착물의 물전기전도도와 자기화율에 관한 측정결과도 함께 보고하였다.

• Journal of Pharmaceutical Investigation
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• 제24권3호spc1호
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• pp.11-18
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• 1994

We have studied the iron uptake by the purified brush-border membrane vesicles (BBMVs) to determine the effect of fructose on the absorption of iron. BBMVs were prepared by the modified calcium precipitation method, The degree of purification was routinely assessed by the marker enzyme, alkaline phosphatase, and the functional integrity was tested by $D-[1-^3H]glucose$ uptake. The appearance of membrane vesicles was shown by transmission electron microscopy (TEM). The uptakes of complexes of labeled iron $[^{59}Fe]$ with fructose and ascorbate were measured with a rapid filtration technique, The uptake rate and pattern of the two iron-complexes, Fe(III)-fructose and Fe(III)-ascorbate, were also observed. A typical overshooting uptake of D-glucose was observed with peak value of $2{\sim}3$ times higher concentration than that at equilibrium. This result was similar to other studies with BBMVs. TEM showed that the size of BBMVs was uniform and we can hardly find any contaminants, Fe(III)-fructose has the higher value of $V_{max}$ and the lower value of Km than those of Fe(III)-ascorbate, respectively. It may be concluded that D-fructose is more effective in promoting the iron absorption than ascorbate.

• Journal of Microbiology and Biotechnology
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• 제24권4호
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• pp.534-544
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• 2014

The effects of microbial iron reduction and oxidation on the immobilization and mobilization of copper were investigated in a high concentration of sulfate with synthesized Fe(III) minerals and red earth soils rich in amorphous Fe (hydr)oxides. Batch microcosm experiments showed that red earth soil inoculated with subsurface sediments had a faster Fe(III) bioreduction rate than pure amorphous Fe(III) minerals and resulted in quicker immobilization of Cu in the aqueous fraction. Coinciding with the decrease of aqueous Cu, $SO_4{^{2-}}$ in the inoculated red earth soil decreased acutely after incubation. The shift in the microbial community composite in the inoculated soil was analyzed through denaturing gradient gel electrophoresis. Results revealed the potential cooperative effect of microbial Fe(III) reduction and sulfate reduction on copper immobilization. After exposure to air for 144 h, more than 50% of the immobilized Cu was remobilized from the anaerobic matrices; aqueous sulfate increased significantly. Sequential extraction analysis demonstrated that the organic matter/sulfide-bound Cu increased by 52% after anaerobic incubation relative to the abiotic treatment but decreased by 32% after oxidation, indicating the generation and oxidation of Cu-sulfide coprecipitates in the inoculated red earth soil. These findings suggest that the immobilization of copper could be enhanced by mediating microbial Fe(III) reduction with sulfate reduction under anaerobic conditions. The findings have an important implication for bioremediation in Cu-contaminated and Fe-rich soils, especially in acid-mine-drainage-affected sites.

• 대한환경공학회지
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• 제27권7호
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• pp.697-703
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• 2005

본 연구에서는 주문진사 입경, 일차 및 이차 코팅온도, 코팅시간, 및 초기 3가철 주입농도를 변화시키면서 철을 코팅시킨 모래흡착제(Iron-Coated Sand, ICS)를 제조하였다. ICS 제조의 최적조건은 코팅효율, 코팅된 철의 안정성, 및 비소제거능 으로부터 선정하였다. 철코팅 효율은 입경이 작은 모래를 지지체로 사용하고 일차코팅온도를 높여주었을 때 뚜렷이 향상되었다. 철의 코팅효율은 이차코팅온도 및 코팅시간에는 크게 영향을 받지 않았지만 As(V) 흡착능은 이차코팅온도가 증가됨에 따라 크게 감소하는 것으로 나타났다. 이러한 결과들을 고려하여 ICS의 최적 이차코팅 조건을 $150^{\circ}C$ 온도조건과 1시간의 가열시간으로 선정하였다. Fe(III) 주입농도 변화에 따른 철 코팅효율은 0.8 Fe(III) mol/kg sand 될 때 까지는 뚜렷이 증가하였지만 그 이상에서는 큰 차이가 없었다. 기리고 Fe(III) 주입농도를 증가시킬수록 As(V) 흡착능도 증가하였으며 0.8 Fe(III) mol/kg sand 조건에서 최대값을 보여주었다. 이차 코팅온도 및 시간은 ICS 안정성의 주요변수로서 코팅온도를 높이고 코팅시간을 길게 할수록 ICS로 부터 용출되는 철의 양은 감소하였다. ICS에 대한 As(V)의 흡착은 낮은 pH에서 흡착량이 증가하는 전형적인 음이온형 흡착경향을 보여서 ICS는 강한 산성을 띄는 오염수내에 함유된 As(V)를 제거하는데 적용이 가능함을 알 수 있었다.

• 자원리싸이클링
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• 제30권2호
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• pp.31-38
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• 2021

철(III)과 란타넘(III)이 혼합된 황산용액에서 황산나트륨에 의한 란타넘 복염의 침전 및 분리를 조사했다. 복염 침전에 영향을 줄 수 있는 여러 요인 중 황산나트륨 및 란타넘(III)의 농도, 반응온도 및 시간, 그리고 철(III) 농도에 대해 조사했다. 용액 중 Na+, SO42- 이온 및 란타넘(III) 농도가 높을수록 희토류 복염의 침전률이 증가했고, 반응온도가 100℃까지 증가함에 따라 란타넘 황산염 이온의 형성을 촉진해 희토류 복염의 침전률이 증가했다. 또한 반응시간이 증가할수록 철(III)의 침전률이 감소해 3시간 이후에는 거의 침전되지 않았고, 철(III) 농도는 복염 침전에 큰 영향을 미치지 않았다. 황산용액에 황산나트륨을 첨가하면 란타넘(III)을 선택적으로 침전시켜 철(III)과 분리할 수 있다.

• 대한자원환경지질학회:학술대회논문집
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• 대한자원환경지질학회 2003년도 춘계 학술발표회 논문집
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• pp.236-236
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• 2003

Anaerobic Fe(III)-reducing bacteria are known to be able to reduce crystalline and amorphous Fe(III) oxides. Anaerobic Fe(III)-reducing bacterial reduction can induce several kinds of secondary minerals (Fe(II) containing minerals) such as magnetite, siderite, vivianite [($Fe_{3}(PO_{4}{\cdot}2H_{2}O$], and iron sulfide (FeS) according to variety of geochemical and biological conditions. (omitted)