• Proceedings of the Korean Fiber Society Conference
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• 1994.10a
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• pp.73-74
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• 1994

• Proceedings of the Membrane Society of Korea Conference
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• 1997.10a
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• pp.53-60
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• 1997

1. 서론 : 촉매막기술은 반응과 분리공정을 동시에 하나의 장치에서 수행할 수 있기 때문에 한 개의 공정을 줄일 수 있는 효과적인 에너지 절약형 기술이다. 생성물중의 적어도 하나가 선택적으로 막을 통해 투과되기 때문에 가역반응의 경우에는 비가역반응에 가까운 거동을 보이게 된다[1-5]. 본 연구는 12-텅스토인산($H_3PW_{12}O_{40}$)를 촉매로 사용하고 막반응시를 비활성촉매막반응기(IMRCF, Inert membrane reactor with catalyst in the feed side)형태, 막으로는 PSF(Polysulfone), PPO(Polyphenylene Oxide)를 사용하여 MTBE(Methyl tert-butyl ether)분해반응을 모사하였다. 막반응기에서 생성된 생성물을 선택적으로 분리해냄으로 인하여 전환율은 고정층보다 증가하였는데 반응온도가 증가할수록, 반응물의 분압은 낮을수록 증가하였다. 반응온도가 높아짐에 따라 막반응기에서의 전환율은 고정층반응에서 나타나는 전환율과의 차이가 줄어드는 것을 볼 수 있었다. 위와같은 결과에 따라서 MTBE 반응물의 분해로 생성되는Isobutene의 수율이 90$\circ$C 이상의 반응온도에서 촉매/반응물비에 대한 최적조건이 나타나는 것을 알 수 있었다.

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2003.04a
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• pp.368-371
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• 2003

Leaking underground storage tanks are a major source of groundwater contamination by petroleum hydrocarbons. Bioremediation of aromatic hydrocarbons in groundwater and sediments is often limited by dissolved oxygen. Aerobic bioremediation has been highly effective in the remediation of many fuel releases, but Many aromatic hydrocarbons degrade very slowly under anaerobic conditions. Nitrate is a good alternative electron acceptor to oxygen and denitrifying bacteria are commonly found in the subsurface and in association with contaminated aquifer materials. Because nitrate is less expensive and more soluble than oxygen. it may be more economical to restore fuel-contaminated aquifers using nitrate rather than oxygen. This study show that biodegradation of BTEX and MTBE is enhanced by the nitrate-amended microcosms under aerobic/anaerobic conditons. Although aromatic hydrocarbons degrade very slowly under anaerobic conditions. Biodegradaton was observed for all of the test compounds.

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2005.04a
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• pp.195-198
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• 2005

A solid-phase microextraction and gas chromatography-mass spectrometry for the extraction and analysis of methyl-tert-butyl ether has been described. methyl-tert-butyl ether was extracted from aqueous solution using SPME fiber coated polydimethylsiloxane and analysed by GC-MS with capillary column. Extraction parameters and chromatographic separation conditions were optimized. The applied method represented good analytical performance in terms of precision (3-8%, RSD) and accuracy(93-102%, mean recovery) with a method detection limit of 0.03 ppb.

• Proceedings of the Korean Society for Applied Microbiology Conference
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• 2005.06a
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• pp.340-340
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• 2005

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2001.05a
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• pp.50-51
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• 2001

• Environmental Analysis Health and Toxicology
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• v.22 no.2 s.57
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• pp.103-109
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• 2007

대기 중 휘발성유기화합물류(VOCs)의 배출원은 매우 다양하며, 특히, 공단에서 배출되는 VOCs 노출로 인한 공단 주변거주지역 주민에게 배출특성 및 물질별 독성에 따라 유해한 건강 영향을 끼칠 가능성이 있다. 또한 일반가정에서의 자체 실내 오염원 또한 휘발성유기화합물류의 노출의 한 원인이다. 본 연구에서는 공단 주변 거주지역 및 동일 행정구역상의 비교지역을 선정하여 공단배출로 인한 실내유입 VOCs 노출 및 자체 실내오염원으로 인한 농도분포 및 기여정도를 조사하였다. 본 연구에서 공단주변 거주지역 및 비교지역의 조사된 실내 평균 농도는 MTBE 2.24, $2.47{\mu}g/m^3$, benzene 9.82, $8.51{\mu}g/m^3$, toluene 103.80, $83.57{\mu}g/m^3$, ethylbenzene 36.45, $15.52{\mu}g/m^3$, xylene 26.27, $1.00{\mu}g/m^34로 비교지역 거주지에 비해 공단지역 주변거주지의 실내공기 중 VOCs 의 농도가 높은 것으로 나타났다. 최종적으로 I/O ratio를 비교한 결과 조사 거주지 모두 자체 실내오염원이 있는 것으로 관찰되었고, 공단지역 주변거주지의 경우 공단의 VOCs 배출로 의해 추가 노출이 되는 것으로 각각 조사되었다.

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2005.10a
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• pp.238-239
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• 2005

• Bulletin of the Korean Chemical Society
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• v.27 no.9
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• pp.1315-1322
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• 2006

The following study describes the gas chromatography-mass spectrometry (GC-MS) based screening and confirmation analysis of urinary androgenic steroids. Four commercially available solid-phase extraction (SPE) cartridges, Serdolit PAD-1, Sep-pak $C_{18}$, amino-propyl, and Oasis HLB, and three different extractive organic solvents, diethyl ether, methyl tert-butyl ether (MTBE), and n-pentane, were tested for sample preparation. Overall, Oasis HLB combined with MTBE extraction provided the highest recoveries in 39 of 46 total androgenic steroids examined and it showed a good extraction yield (>82.1%) for polar steroids, such as metabolites of fluoxymesterone, oxandrolone, and stanozolol, which gave a poor recovery in both n-pentane (9.2-64.3%) and diethyl ether (22.2-73.6%) extractions. All SPE sorbents tested showed potential, because they were efficient in extraction for most or selective steroids. When applied to positive urine samples based on the results obtained, the present method allowed selective and sensitive analysis for detection of urinary androgenic steroids. The experiments showed that the high-resolution MS method is clearly more efficient than the low-resolution MS technique for the detection of many urinary steroids. However, comprehensive sample clean-up procedures also might be needed especially in confirmation analysis to increase detectability.

• Environmental Analysis Health and Toxicology
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• v.18 no.3
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• pp.219-224
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• 2003

1,4-Dioxane is used as a solvent for lacquers, paints, varnish removers, dye baths and printing compositions. And it is also used for detergent preparations, cosmetics, deodorants and fumigants. A method is described for the determination of 1,4-dioxane in water samples by GC/MS. The extraction recoveries were studied for some solvents and solvent volume ratio were investigated using r-butyl methyl ether (MTBE). Optimum condition was obtained by the liquid-liquid extraction using the 10 mL of MTBE for 10 mL of water. Method detection limit of 1,4-dioxane in the 20 mL of water samples was 0.05 ng/mL. It could be determined in the range of 0.24∼240 ng/mL in treated water, and in the range of 0.69∼81.9 ng/mL in raw water, respectively. Risk assessments with 1,4-dioxane exposure by drinking water ingestion were carried out. Based on the results of analysis, chronic daily intake of 1,4-dioxane was 2.22${\times}$10$\^$-4/ mg/kg/day and excess cancer risk was calcu-lated to be 2.44${\times}$10$\^$-6/.