• Proceedings of the KAIS Fall Conference
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• 2000.10a
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• pp.241-242
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• 2000

본 연구는 폐수처리공정에서 경량기포콘크리트를 이용하여 폐수 중에 존재하는 음이온계면 활성제와 총인 그리고 총질소성분을 제거하기 위하여 실시되었다. 경량기포콘크리트는 폐수 처리공정에서 반응기에 충진하여 사용하였으며, 이때 사용된 폐수는 인공폐수(음이온계면활성제 : 10-31 mg/L, 총인 : 66-73 mg/L 그리고 총질소 : 56-163 mg/L)를 사용하였다. 실험결과 경량기포콘크리트를 사용하여 폐수를 처리한 결과 음이온계면활성제의 85-95 %, 총인성분의 92 %, 그리고 총질소 성분의 90 % 정도가 제거되었다.

• Proceedings of the KAIS Fall Conference
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• 2006.05a
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• pp.599-601
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• 2006

본 논문에서는 용액의 농도가 이온교환 특성에 미치는 영향을 조사하기 위하여 농도는 $Na^+\;50$, 125, 250ppm, $Cl^-\;165$, 315, 610ppm, 입자성 물질의 유입 농도 0ppm, 유속 500ml/min, 이온교환 수지는 ROHM&HAAS IR 120 양이온 수지와 ROHM&HAAS IRA 402 음이온 수지를 사용하였다. 수지탑 배열은 혼상-혼상-음이온 수지탑 순으로, 이온교환 수지탑의 양 음이온교환 수지의 조성 비율은 1:2 로 실험한 결과 이온교환 수지탑 성능은 유입 용액 성분 및 농도에 영향을 받는 것으로 나타났다. 이온교환 수지탑 배열 순서에 따라 파과시점이 연장되며, 파과순서는 음이온의 경우 $Cl^-\;<\;NO_3\;^-\;<\;F^-$, 양이온의 경우 $Na^+\;<\;K^+\;<\;Ca^{2+}$ 순 이였으며, 용액의 농도가 증가할수록 파과시간이 단축되었다.

• Proceedings of the Korean Institute of Surface Engineering Conference
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• 2015.05a
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• pp.109-110
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• 2015

알루미늄 합금의 종류중 하나인 ADC12는 가공성이 좋고 가격이 저렴하기 때문에 산업의 많은 분야에 이용할 수 있지만 양극산화를 진행할 시 합금의 주요 구성성분인 실리콘(Si)으로 인해 균열(Crack)이 생기는 문제가 발생하여 이에 따라 균일한 산화막이 생성되지 않다는 단점을 가지고 있다. 이 단점을 극복하기 위해 양극산화를 진행할 때 금속 음이온 성분이 첨가된 전해질을 이용하면 실리콘이 떨어져 나간 부분을 자가치료(Self-healing)할 수 있어 피막의 경도를 포함한 각종 특성이 증가하는 결과를 확인할 수 있다. 본 연구에서는 ADC12를 양극산화할 때 황산 수용액을 기본 전해질로 하여 전해질에 타이타늄(Ti), 마그네슘(Mg), 몰리브덴(Mo)이 포함되어 있는 금속 음이온 물질을 첨가하였고, 금속 음이온 전해질의 농도와 양극산화 진행 시간을 변수로 하여 제조한 산화막의 전기화학적 특성을 SEM(Scanning Electron Microscope), Tafel plot, 그리고 Microvickers hardness tester를 통해 평가하였다.

• Analytical Science and Technology
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• v.25 no.6
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• pp.350-363
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• 2012

To determine ionic species in snowpit samples using ion chromatography system, we described the performance of ion chromatography(IC) system, cleaning method of bottle, and interference by filtering procedure. The limit of detection, reproducibilities, and accuracies determined with BCR$^{(R)}$-408 were 0.01-0.26 ${\mu}g$/L, 0.4-17.4%, 4.5-12.0% for cations and 0.02-0.26 ${\mu}g/L$, 0.1-27.6%, 1.3-5.6% for anions, respectively. Lab blank test for sample bottle indicated that $CH_3CO_2{^-}$, $HCO_2{^-}$, and $NH_4{^+}$ can be easily contaminated in the lab environment. The positive interferences of $NO_3{^-}$ were partly attributed to the cleaning method of bottle. The filtering of melted snow sample should be carefully applied because it can positively affect the concentration levels of some ionic species. Finally, this method was applied to measure ionic species in snowpit samples from the upward area near NEEM camp and the uncertainties of measurement data of $F^-$ were also estimated.

• Journal of the Korea Academia-Industrial cooperation Society
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• v.4 no.3
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• pp.307-311
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• 2003

The test did for the determine the optimized ratio of cation to anion in mixed ion exchange demineralizers. Binary, ternary, quaternary, and quinary cation and anion adsorption was performed to develop a comprehensive experimental data set from small-volume batch tests to obtain the selectivity coefficients of many cations and anions. The quantitative run time might be estimated by such ion exchange models as semi-empirical mass action and surface complexation models. The demineralizer can be used longer by increasing the ratios of cation to anion exchange resins in the bed.

• Proceedings of the Korean Institute of Surface Engineering Conference
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• 2016.11a
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• pp.190.1-190.1
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• 2016

봉공처리법은 다공성 알루미나를 제조 후에 내마모성의 증가, 침지된 염료의 봉인 등을 필요로 하여 이용하는 후처리 공정 중 하나이다. 상업적으로는 물 봉공처리나 니켈-아세트산 용액을 이용한 봉공처리를 주로 이용하지만 고온을 필요로 하거나 인체에 유독한 용액을 사용, 혹은 추가적인 봉공처리를 해주어야 한다는 단점들을 가지고 있다. 이에 본 연구에서는 독성이 적고 상온에서도 다공성 알루미나와 쉽게 반응할 수 있는 알루미늄 음이온 용액을 봉공처리에 이용하였다. 알루미늄 음이온 용액을 이용한 봉공처리는 알루미늄의 양극 산화를 진행한 이후에 알루미늄 음이온을 포함한 봉공처리제를 제조 후, 침지 처리하는 방식으로 봉공처리하였다. 봉공처리제의 pH 변화, 온도 변화, 침지 시간 등의 변수 요소에 따라서 최적화를 진행하였으며, 이 용액으로 봉공처리가 가능한지 주사 전자 현미경 분석을 통해 평가하였다. 이후 최적화된 조건과 기존에 상업적으로 사용하던 봉공처리법을 거친 후에 경도, 부식전위 검사, 내화학성 검사를 통해 성능의 변화를 확인하였으며 광전자 분광기를 통해 성분과 메카니즘을 예측하였다.

• Korean Journal of Environmental Agriculture
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• v.19 no.2
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• pp.110-115
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• 2000

This study was conducted to monitor the irrigation water qualities along Dong-Jin river watershed. The water quality was surveyed at 6 sites from April to september during $1994{\sim}1998$. And the results were as follows : In July and August, water quality was better than that of any other months due to dilution with rainwater. Whereas, it became worse in April but it involved lower contents than limitted contents affected to the crop damage. Content of inorganic components was higher at Jeong-up and Won-pyeong stream. The reason for it that Jeong-up stream was deteriorated with sewage water from Jeong-up city, and Won-pyeong stream has narrow width. Water quality in upstream of Dong-Jin river, was evaluated best conditions in all sampling sites. For investigated period, water quality got worse from 1994 to 1995 but it was getting better to 1998 after 1995, especially at Jeong-up stream. The total equivalent of cation and anion was the highest at April through all months and at Jeong-up stream in sampling sites. Equivalent ratio of cation to $anions({\Sigma}C/{\Sigma}A)$ was higher at May than any other months and lower at Won-pyeong streams than any other sites. The value of most inorganic components was highly correlated with those of other components. But the value of $NO_3\;^--N$ was not correlated with that of most components, and $PO_4\;^{3-}-P$ was not correlated with COD, $NH_4\;^+-N$, $NO_3\;^--N$, $SO_4\;^{2-}$.

• Journal of the Korea Academia-Industrial cooperation Society
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• v.7 no.4
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• pp.727-732
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• 2006

The object of this study was to investigate the influence of composition and concentration of electrolyte, ratio of cation to anion exchange resin of mixed ion exchange column in the performance of ion exchange. Also this work examined the removal capability of suspended solids by ion exchange resin and the effect of particule on the characteristics of ion exchange. Breakthrough time was extended as the amount of ions and particles present in liquid was decreased. The case of anion, the breakthrough sequence is $Cl^{-}, but the case of cation, the breakthrough sequence is $Na^{+}. As for the ratio of cation to anion exchange resin of 1:2, the breakthrough time was prolonged compared with that of 1:1 and 1:3. For the electrolyte of equal concentration containing suspended solid, breakthrough time was contracted less than 20%. It results in the increase in the removal capacity of cation exchange resin. For the higher ratio of cation exchange resin, suspended solids are shorten the cation's breakthrough time so that the runtime of ion exchange resin tower is increased.

• Proceedings of the Korean Radioactive Waste Society Conference
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• 2005.06a
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• pp.248-254
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• 2005

This paper presents a quantitative method of sequential separation of $^{90}Sr,\;^{241}Am$ and Pu nuclides with an anion exchange resin and a Sr-Spec resin. The Pu isotopes were purified with an anion exchange resin. The americium and strontium fractions were separated from the matrix elements with an oxalate co-precipitation method. Americium fraction was separated from the strontium fraction with iron co-precipitation method and purified from lanthanides with anion exchange resin. Strontium-90 was purified from other hindrance elements with the Sr-Spec resin after oxalate co-precipitation. The measurement of Pu and Am isotopes was carried out by an ${\alpha}$-spectrometer. Strontium-90 was measured by a liquid scintillation counter. The radiochemical procedure of $^{90}Sr,\;^{241}Am$ and Pu nuclides investigated in this study has been validated by application to IAEA-Reference soils.

• Journal of the Korean Chemical Society
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• v.17 no.6
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• pp.428-433
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• 1973

The quantitative separations of a mixture containing equal amount of each anion such as Si(IV), As(V), P(V), S(VI), W(VI) and Cr(VI) are carried out by the elution through 20${\times}3.14cm^2$ column of anion exchange resin, Dowex 1${\times}$8. The eluents are a mixture of 0.07 M hydrochloric acid and 0.03 M sodium chloride (pH = 1.30) for Si(IV), As(V) and P(V) species, a mixture of 0.6 M sodium chloride and 0.3 M sodium hydroxide for S(VI), W(VI) and Cr(VI) species, and 0.1 N sodium sulfite (pH = 3.48) for P(V) and As(V) species. The subsidiary anions in a standard mixture such as Si(IV), As(V), S(VI), P(V) and W(VI) are separated together from large amount of Fe(III) by the elution through 30cm${\times}3.14cm^2$ column of the resin, Dowex${\times}$50w${\times}$12, using a mixture of 0.1 M sodium nitrate and 2 percent dimethylsulfoxide aqueous solution as an eluent. Si(IV), As(V), S(VI), P(V) and W(VI) eluted together are separated quantitatively under the same conditions as in the separations of the anion mixture. By the conditions obtained in the separations of the standard mixture, Fe(III) and all of the subsidiary anions in steel are quantitatively separated.