• Applied Biological Chemistry
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• 제44권2호
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• pp.73-80
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• 2001

저장 중 온도$(20,\;60^{\circ}C)$), pH(4.5, 7.0), 기체조성$(N_2,\;0_2)$, 광도(0 lux, 5,000 lux), 항산화제 및 포장조건이 시금치 및 동결 건조 시금치의 클로로필 색소 성분에 주는 영향을 조사하였다. 시금치에 함유된 클로로필 a 및 클로로필 b 함량은 각각 710.54(mg/100g dry weight) 및 280.15(mg/100g dry weigllt)이었다. 저장온도를 $20^{\circ}C$에서 $60^{\circ}C$로 올리면 다른 조건에 관계없이 시금치의 클로로필 a 및 클로로필 b함량은 유의적으로(P<0.05) 감소하였으며, pH를 7.0에서 4.5도 낮추면 시금치의 클로로필 a, b 함량도 모두 유의성(P<0.05) 있게 감소하였다. 시금치의 클로로필 분해는 높은 온도와 낮은 pH에서 잘 일어났다. 질소로 치환된 저장 조건에서 저장된 시금치의 클로로필 a 및 클로로필 b 색소 성분의 분해는 질소 처리를 하지 않은 조건에서 저장된 시금치와 비교해서 유의성(P<0.05) 있게 억제되었으며, 빛(5,000 lux)을 조사한 조건에서 저장한 시금치의 클로로필 a 및 클로로필 b 성분은 빛이 차단된 상태에서 저장된 시금치와 비교해서 유의적으로(P<0.05) 감소하였다. 저장 중 시금치의 클로로필 파괴는 산소와 빛이 있는 조건에서 잘 일어난다. 암 저장$(25^{\circ}C,\;15\;min)$ 조건에서 항산화제는 시금치의 자동산화에 의한 지용성 클로로필 a 성분의 분해를 억제하였는데, 억제 효과는 알파-토코페롤>ascorbic acid>${\beta}-carotene$>catechin>quercetin>rutin>kaempherol>caffeic acid>chlorogenic acid>p-coumaric acid>ferulic acid 순이었다. 항산화제는 빛 저장(5,000 lux, 6 min)조건에서도 singlet oxygen oxidation에 의한 클로로필 a의 분해를 억제하였는데, 억제 효과는 ${\beta}-carotene$>알파-토코페롤>ascorbic acid>catechin>quercetin>rutin>kaem-pherol>caffeic acid>chlorogenic acid>p-coumaric acid>ferulic acid의 순으로 감소하였다. Polyethylene bag으로 포장하지 않은 동결건조 시금치에 잔존하는 클로로필 a 및 클로로필 b 함량은 polyethylene bag으로 포장한 조건에서 동결건조 시금치에 잔존하는 클로로필 a 및 클로로필 bb함량에 비해 유의적으로(P<0.05) 낮게 나타났다. 시금치는 항산화제를 첨가한 다음 polyethylene bag에 포장한 상태로 저장하는 것이 클로로필 성분의 파괴를 최소화하는 방법이 될 수 있다.

• 대한환경공학회지
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• 제30권8호
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• pp.789-797
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• 2008

본 연구에서는 파쇄된 타이어칩을 담체로 충진한 biofilter를 이용하여 악취의 원인 물질인 trimethylamine(TMA)의 제거특성을 실험하였다. 실험에서 사용된 미생물은 S 수탁폐수 처리업체에서 채취한 활성슬러지를 순응 배양 하였으며, peristatic pump를 이용하여 20일간 바이오필터의 담체에 순환시키면서 접종 하였다. Biofilter의 안정화를 확인한 후 유입 농도와 공간속도를 변화시켜 처리효율을 측정하였으며, 침출수중의 액상 TMA, COD$_{Cr}$, NO$_3{^-}$-N, NO$_2{^-}$-N, NH$_4{^+}$-N, EPS(Extracellular Polymeric Substances)를 측정하여 생물학적인 영향과 처리효율에 대해 평가하였다. TMA의 유입농도를 약 10 ppm의 범위로 고정하고 SV(space velocity)를 120 hr$^{-1}$에서 240 hr$^{-1}$까지 증가시켜 TMA의 제거효율을 검토한 결과 120, 180 hr$^{-1}$에서는 95% 이상, SV 240 hr$^{-1}$에서는 최대 90%, 최소 80%의 제거효율을 얻어 최적 제거 공간 속도는 180 hr$^{-1}$임을 확인 할 수 있었다. 또한, SV를 180 hr$^{-1}$, 유입농도를 5$\sim$55 ppm까지 단계적으로 증가시켜 TMA의 제거효율을 검토한 결과 유입농도 10 ppm까지는 95%, 유입농도 10$\sim$30 ppm에서는 80%의 제거율을 보임을 알 수 있었고, 유입농도 40 ppm 이상에서는 제거효율이 급격히 감소하는 경향을 보여 TMA에 대한 임계 최대 제거 농도는 40 ppm임을 확인 할 수 있었다. Kinetic analysis를 통해 얻은 TMA의 최대 제거 속도($V_m$)와 기질친화상수($K_s$)는 각각 14.3 g$\cdot$m$^{-3}$$\cdot$h$^{-1}$과 0.043 g$\cdot$m$^{-3}$로 나타났으며, 충격부하에 대한 미생물의 순응 기간은 100$\sim$150 hr 정도로 나타났다. 또한, 침출수중의 EPS 농도가 100$\sim$200 ppm의 범위에서 지속적으로 측정되어 반응기내에서 생물막이 지속적으로 생성되어짐을 확인 할 수 있었다.

• 지구물리와물리탐사
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• 제9권1호
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• pp.60-66
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• 2006

세 개의 서로 다른 사암 샘플들 -두 개의 합성 샘플과 한 개의 현장 샘플- 에 대해 현장 저류층의 대표적인 구속압력과 공극압력하에서 초음파 시험이 수행되었다. 세가지 사암 샘플들은 (a) 캘사이트 시멘트(calcite intergranula. cement (CIPS))로 만든 합성사암, (b) 실리카 시멘트(silica intergranular cement)로 만든 합성 사암 (c) Otway Basin 의 Boggy Creek 1 시추공에서 시도되는 $CO_2$ 파일럿 프로젝트의 대상 암석층 중 Waarre 층으로부터 추출한 코아 샘플로 구성되어 있다. 공극률은 각각 32%, 33%, 26%이다. 초기시험은 실내건조(room-dried) 상태에 있는 코아들에 대해 구속응력을 5 MPa 씩 단계별로 65 MPa 까지 증가시키며 이루어졌다. 그리고 나서 모든 코아들에 처음에는 온도 $22^{\circ}C$에서 6 MPa 공극압력으로 기체상의 $CO_2$를, 그 다음에는 온도 $22^{\circ}C$ 에서 7 MPa 부터 17 MPa 까지 5 MPa 씩 증가시키면서 액체상의 $CO_2$를 주입하였다. 구속응력은 10MPa부터 65 MPa까지 달리 하였다. P와 S 초음파 파형들이 유효응력이 증가할 때마다 기록되었다. 속도-유효응력 반응들이 P 파와 S 파에 대해 실험 자료들로부터 계산되었으며, 감쇠(1/Qp)들은 스펙트럼 비 방법을 이용하여 파형들로부터 계산되었다. 각각의 사암들에 대한 이론적인 속도-유효응력 계산은 $CO_2$ 압력-밀도 와 $CO_2$ 체적계수-압력 상 다이어그램(phasediagram), Gassmann 유효 매질 이론(effective medium theory)을 이용하여 구하였다. 기체상의 $CO_2$ 주입은 속도-유효응력에서 건조상태(공기로 포화된 상태)에 비해 거의 무시할만한 변화를 가져왔다. 다양한 공극압력에서 액체상의 $CO_2$ 주입은 공기로 포화된 상태에 비해 속도-유효응력 반응을 평균 약 8% 정도 낮게 한다. 실험자료들은 높은 유효응력에서 Gassmann 계산들과 일치한다. 이러한 이론과 일치하는 "임계" 유효응력은 사암의 종류에 따라 달라진다. 이 차이는 각각의 사암 종류의 미세구조에서 미세 균열 수의 차이에 기인한 것이라 생각된다. 높은 유효응력에서의 이론과 의미있게 일치하였으며, $CO_2$ 주입 시 현장에서의 탄성파 거동을 예상하는데 있어서 어느 정도 확신을 준다.

• 한국산업보건학회지
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• 제16권1호
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• pp.44-53
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• 2006

This study purposed to investigate air pollution in car shipping yards and, for this purpose, we selected an outdoor open-air yard and an indoor ramp into the ship and measured the concentrations of sulfur dioxide, nitrogen dioxide, carbon monoxide, PM10, PM2.5 and heavy metals in the air. The results of this study are as follows. No significant difference was observed in temperature and humidity between the outdoor and indoor workshop, and the average air flow was 0.52 m/s in the indoor workshop, which is higher than 0.19 m/s in the outdoor workshop(p<0.01). The average concentrations of sulfur dioxide, nitrogen dioxide, carbon monoxide, PM10 and PM2.5 according to workplace were 0.03 ppm(${\pm}0.01$), 0.03 ppm(${\pm}0.01$), 0.46 ppm(${\pm}0.22$), $39.44{\mu}g/m^3$(${\pm}2.45$) and $5.45{\mu}g/m^3$(${\pm}1.15$) respectively in the outdoor workshop, and 0.15 ppm(${\pm}0.05$), 0.22 ppm(${\pm}0.06$), 8.85 ppm(${\pm}3.35$), $236.39{\mu}g/m^3$(${\pm}58.21$) and $152.43{\mu}g/m^3$(${\pm}35.42$) respectively in the indoor workshop. Thus, the concentrations of gaseous substances in the indoor workshop were 4.9-19.2 times higher than those in the outdoor workshop, and the concentrations of fine dusts were 5.9-27.9 times higher(p<0.01). In addition, according to the result of investigating pollutant concentrations according to displacement and the number of car loaded when shipping gasoline cars into the ship, no significant relation between the number of cars loaded and pollutants was observed in shipping passenger cars, but the concentrations of nitrogen dioxide and carbon monoxide got somewhat higher with the increase of the number of cars loaded(p<0.05). In addition, the concentrations of nitrogen dioxide, carbon monoxide, PM10 and PM2.5 in the air were significantly higher when shipping recreational vehicles, the displacement of which is larger than passenger cars, than when shipping passenger cars(p<0.01). On the other hand, the average heavy metal concentrations of the air in indoor workshop were: lead $-0.05{\mu}g/m^3$(${\pm}0.10$); chromium $-0.90{\mu}g/m^3$(${\pm}0.18$); zinc $-0.38{\mu}g/m^3$(${\pm}0.24$); copper $-0.18{\mu}g/m^3$(${\pm}0.22$); and manganese and cadmium not detected. In addition, the complaining rates of 'asthma,' a major symptom of chronic respiratory diseases, were 18.5% and 22.5% respectively in indoor workers and outdoor workers. Thus the rate was somewhat higher in indoor workers but the difference was not statistically significant. The complaining rates of 'chronic cough' and 'chronic phlegm' were very low and little different between indoor and outdoor workers. The results of this study show that the reason for the higher air pollution in indoor than in outdoor workshop is incomplete combustion of fuel due to sudden start and over-speed when cars are driven inside the ship. In order to prevent high air pollution, efficient management measures should be taken including the observance of the optimal speed, the improvement of old ships and the installation of efficient ventilation system.

• 한국지하수토양환경학회지:지하수토양환경
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• 제18권4호
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• pp.19-31
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• 2013

To figure out the decay characteristics of naturally occurring radionuclides, eight sampled groundwaters from a monitoring borehole having high levels of uranium and radon concentrations in a two mica granitic area have analyzed by liquid scintillation counters (LSC) for over 1 year. In December 2011, three groundwater samples (DJ1, DJ2, DJ3) were obtained from each aquifer system located at -20 m, -40 m, -60 m of the monitoring borehole below the ground surface, respectively. Five samples (DJ4, DJ5, DJ6, DJ7, DJ8) were additionally gained from each aquifer positioned -20 m, -40 m, -60 m, -100 m, -105 m of the borehole in February 2012, respectively. Temporal variation characteristics of uranium and radon concentrations have showed over maximum 2.1 times and 1.4 times fluctuations of the values in the same sampling intervals over time, respectively. The intervals of -40 m and -105 m in the borehole have the highest values of uranium and radon concentrations, respectively. This may imply that the concentrations of naturally occurring radionuclides such as uranium and radon in groundwater have been changed over time and indicate that the qualities of groundwaters from the aquifers developed at each interval in the borehole are different each other. This discrepancy, moreover, could be caused by behaviour differences between uranium which is in ionic status having a half life of 4.6 billion years and is transported along with the flowing groundwater, and radon which is in gaseous status having a 3.82 day's half life in the aquifer systems. Physicochemical characteristics of groundwaters from the aquifer systems could be identified by the results of the on-situ measuring items such as pH and Eh, and the major ionic contents. The CPM values of eight groundwater samples analysed by LSC over one year have shown not to follow the theoretical decay curve of the radon. The CPM values of the samples have ranged from 2 to 7.5 after it had passed two months when the theoretical CPM values of the radon started zero since the initial analysis. Alpha and beta particle spectrums have shown the peaks of radium-226, however they have not revealed any peaks of radon and it's daughter products such as polonium-218 and 214, bismuth-214 for the late stage of the analysis. This implies that the groundwater from the borehole may contain radium-226 having a half life of 1,600 years which decays continuously.

• 한국표면공학회:학술대회논문집
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• 한국표면공학회 2009년도 춘계학술대회 논문집
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• pp.111-112
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• 2009

Diamond-like carbon (DLC) is a convenient term to indicate the compositions of the various forms of amorphous carbon (a-C), tetrahedral amorphous carbon (ta-C), hydrogenated amorphous carbon and tetrahedral amorphous carbon (a-C:H and ta-C:H). The a-C film with disordered graphitic ordering, such as soot, chars, glassy carbon, and evaporated a-C, is shown in the lower left hand corner. If the fraction of sp3 bonding reaches a high degree, such an a-C is denoted as tetrahedral amorphous carbon (ta-C), in order to distinguish it from sp2 a-C [2]. Two hydrocarbon polymers, that is, polyethylene (CH2)n and polyacetylene (CH)n, define the limits of the triangle in the right hand corner beyond which interconnecting C-C networks do not form, and only strait-chain molecules are formed. The DLC films, i.e. a-C, ta-C, a-C:H and ta-C:H, have some extreme properties similar to diamond, such as hardness, elastic modulus and chemical inertness. These films are great advantages for many applications. One of the most important applications of the carbon-based films is the coating for magnetic hard disk recording. The second successful application is wear protective and antireflective films for IR windows. The third application is wear protection of bearings and sliding friction parts. The fourth is precision gages for the automotive industry. Recently, exciting ongoing study [1] tries to deposit a carbon-based protective film on engine parts (e.g. engine cylinders and pistons) taking into account not only low friction and wear, but also self lubricating properties. Reduction of the oil consumption is expected. Currently, for an additional application field, the carbon-based films are extensively studied as excellent candidates for biocompatible films on biomedical implants. The carbon-based films consist of carbon, hydrogen and nitrogen, which are biologically harmless as well as the main elements of human body. Some in vitro and limited in vivo studies on the biological effects of carbon-based films have been studied [$2{\sim}5$].The carbon-based films have great potentials in many fields. However, a few technological issues for carbon-based film are still needed to be studied to improve the applicability. Aisenberg and Chabot [3] firstly prepared an amorphous carbon film on substrates remained at room temperature using a beam of carbon ions produced using argon plasma. Spencer et al. [4] had subsequently developed this field. Many deposition techniques for DLC films have been developed to increase the fraction of sp3 bonding in the films. The a-C films have been prepared by a variety of deposition methods such as ion plating, DC or RF sputtering, RF or DC plasma enhanced chemical vapor deposition (PECVD), electron cyclotron resonance chemical vapor deposition (ECR-CVD), ion implantation, ablation, pulsed laser deposition and cathodic arc deposition, from a variety of carbon target or gaseous sources materials [5]. Sputtering is the most common deposition method for a-C film. Deposited films by these plasma methods, such as plasma enhanced chemical vapor deposition (PECVD) [6], are ranged into the interior of the triangle. Application fields of DLC films investigated from papers. Many papers purposed to apply for tribology due to the carbon-based films of low friction and wear resistance. Figure 1 shows the percentage of DLC research interest for application field. The biggest portion is tribology field. It is occupied 57%. Second, biomedical field hold 14%. Nowadays, biomedical field is took notice in many countries and significantly increased the research papers. DLC films actually applied to many industries in 2005 as shown figure 2. The most applied fields are mold and machinery industries. It took over 50%. The automobile industry is more and more increase application parts. In the near future, automobile industry is expected a big market for DLC coating. Figure 1 Research interests of carbon-based filmsFigure 2 Demand ratio of DLC coating for industry in 2005. In this presentation, I will introduce a trend of carbon-based coating research and applications.

• 생명과학회지
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• 제27권2호
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• pp.217-224
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• 2017

Carbon monoxide (CO)는 세포 보호의 기능을 가지는 항산화 효소인 heme oxygenase-1 (HO-1)의 대사산물로 세포성장, 아폽토시스, 염증에 대한 억제 효과를 보이는 것으로 보고가 이어지고 있고, 이에 관련된 연구가 활발히 진행되고 있는 실정이다. 본 연구에서는 CO가 단핵구의 대식세포로의 분화 및 그 활성화 과정에 미치는 영향을 인간 단핵구세포주 THP-1을 이용하여 조사하였다. CO-releasing compound인 CORM-2는 phorbol 12-myristate 13-acetate (PMA)로 자극한 THP-1 세포에서 viability와 증식에는 큰 영향을 주지 않았으나 부착능의 뚜렷한 감소를 보였다. 그리고, CORM-2는 대식세포의 막표면 분화 인자인 CD14, CD11b 및 CD18의 발현과 latex beads를 이용한 포식 기능을 현저히 억제하였다. 다음으로, 배양중인 THP-1 세포를 PMA로 6일 동안 대식세포로 분화시킨 후 inflammatory cytokines의 분비와 포식 기능을 조사하였다. CORM-2의 처리는 lipopolysaccaride (LPS)로 자극한 대식세포로부터 분비되는 IL-6와 $TNF-{\alpha}$의 분비를 감소시켰다. 또한, 분화된 대식세포에 E. coli (K-12 strain) bioparticles를 이용하여 포식 기능을 측정한 결과 CORM-2를 처리한 세포에서는 현저히 감소되는 경향을 보였다. 이를 종합해 볼 때, CO는 항원 인식과 포식 기능에 관여하는 막단백질의 발현을 저해함으로써 단핵구의 분화과정을 억제하였고, 분화된 대식세포의 inflammatory cytokines의 분비 및 포식 기능을 저해함으로써 활성화 과정도 억제하는 것으로 보인다.

• 한국대기환경학회지
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• 제34권4호
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• pp.567-587
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• 2018

A severe haze event occurred in October 2015 in Gwangju, Korea. In this study, the driving chemical species and the formation mechanisms of $PM_{2.5}$ pollution were investigated to better understand the haze event. Hourly concentrations of $PM_{2.5}$, organic and elemental carbon, water-soluble ions, and elemental constituents were measured at the air quality intensive monitoring station in Gwangju. The haze event occurred was attributed to a significant contribution (72.3%) of secondary inorganic species concentration to the $PM_{2.5}$, along with the contribution of organic aerosols that were strongly attributed to traffic emissions over the study site. MODIS images, weather charts, and air mass backward trajectories supported the significant impact of long-range transportation (LTP) of aerosol particles from northeastern China on haze formation over Gwangju in October 2015. The driving factor for the haze formation was stagnant atmospheric flows around the Korean peninsula, and high relative humidity (RH) promoted the haze formation at the site. Under the high RH conditions, $SO{_4}^{2-}$ and $NO_3{^-}$ were mainly produced through the heterogenous aqueous-phase reactions of $SO_2$ and $NO_2$, respectively. Moreover, hourly $O_3$ concentration during the study period was highly elevated, with hourly peaks ranging from 79 to 95ppb, suggesting that photochemical reaction was a possible formation process of secondary aerosols. Over the $PM_{2.5}$ pollution, behavior and formation of secondary ionic species varied with the difference in the impact of LTP. Prior to October 19 when the influence of LTP was low, increasing rate in $NO_3{^-}$ was greater than that in $NO_2$, but both $SO_2$ and $SO{_4}^{2-}$ had similar increasing rates. While, after October 20 when the impact of haze by LTP was significant, $SO{_4}^{2-}$ and $NO_3{^-}$ concentrations increased significantly more than their gaseous precursors, but with greater increasing rate of $NO_3{^-}$. These results suggest the enhanced secondary transformation of $SO_2$ and $NO_2$ during the haze event. Overall, the result from the study suggests that control of anthropogenic combustion sources including vehicle emissions is needed to reduce the high levels of nitrogen oxide and $NO_3{^-}$ and the high $PM_{2.5}$ pollution occurred over fall season in Gwangju.

• 한국추진공학회:학술대회논문집
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• 한국추진공학회 2003년도 제20회 춘계학술대회 논문집
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• pp.91-93
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• 2003

A comprehensive numerical study is carried out to investigate for the understanding of the flow evolution and flame development in a supersonic combustor with normal injection of ncumally injecting hydrogen in airsupersonic flows. The formulation treats the complete conservation equations of mass, momentum, energy, and species concentration for a multi-component chemically reacting system. For the numerical simulation of supersonic combustion, multi-species Navier-Stokes equations and detailed chemistry of H2-Air is considered. It also accommodates a finite-rate chemical kinetics mechanism of hydrogen-air combustion GRI-Mech. 2.11[1], which consists of nine species and twenty-five reaction steps. Turbulence closure is achieved by means of a k-two-equation model (2). The governing equations are spatially discretized using a finite-volume approach, and temporally integrated by means of a second-order accurate implicit scheme (3-5).The supersonic combustor consists of a flat channel of 10 cm height and a fuel-injection slit of 0.1 cm width located at 10 cm downstream of the inlet. A cavity of 5 cm height and 20 cm width is installed at 15 cm downstream of the injection slit. A total of 936160 grids are used for the main-combustor flow passage, and 159161 grids for the cavity. The grids are clustered in the flow direction near the fuel injector and cavity, as well as in the vertical direction near the bottom wall. The no-slip and adiabatic conditions are assumed throughout the entire wall boundary. As a specific example, the inflow Mach number is assumed to be 3, and the temperature and pressure are 600 K and 0.1 MPa, respectively. Gaseous hydrogen at a temperature of 151.5 K is injected normal to the wall from a choked injector.A series of calculations were carried out by varying the fuel injection pressure from 0.5 to 1.5MPa. This amounts to changing the fuel mass flow rate or the overall equivalence ratio for different operating regimes. Figure 1 shows the instantaneous temperature fields in the supersonic combustor at four different conditions. The dark blue region represents the hot burned gases. At the fuel injection pressure of 0.5 MPa, the flame is stably anchored, but the flow field exhibits a high-amplitude oscillation. At the fuel injection pressure of 1.0 MPa, the Mach reflection occurs ahead of the injector. The interaction between the incoming air and the injection flow becomes much more complex, and the fuel/air mixing is strongly enhanced. The Mach reflection oscillates and results in a strong fluctuation in the combustor wall pressure. At the fuel injection pressure of 1.5MPa, the flow inside the combustor becomes nearly choked and the Mach reflection is displaced forward. The leading shock wave moves slowly toward the inlet, and eventually causes the combustor-upstart due to the thermal choking. The cavity appears to play a secondary role in driving the flow unsteadiness, in spite of its influence on the fuel/air mixing and flame evolution. Further investigation is necessary on this issue. The present study features detailed resolution of the flow and flame dynamics in the combustor, which was not typically available in most of the previous works. In particular, the oscillatory flow characteristics are captured at a scale sufficient to identify the underlying physical mechanisms. Much of the flow unsteadiness is not related to the cavity, but rather to the intrinsic unsteadiness in the flowfield, as also shown experimentally by Ben-Yakar et al. [6], The interactions between the unsteady flow and flame evolution may cause a large excursion of flow oscillation. The work appears to be the first of its kind in the numerical study of combustion oscillations in a supersonic combustor, although a similar phenomenon was previously reported experimentally. A more comprehensive discussion will be given in the final paper presented at the colloquium.

• 멤브레인
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• 제21권1호
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• pp.22-29
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• 2011

중전기의 유지 보수 및 교체 과정에서 절연체로 사용된 $SF_6$ 가스는 교체 충전과 정제과정에서 유입되는 공기와의 아크 방전에 의해 많은 종류의 부산물($N_2$, $O_2$, $CF_4$, $SO_2$, $H_2O$, HF, $SOF_2$, $CuF_2$, $WO_3$ 등)이 발생된다. 부산물 중에서도 대부분을 차지하는 것이 $N_2$, $O_2$, $CF_4$이며, $SF_6$가스를 재사용하기 위해서는 이들을 효과적으로 분리 회수하는 공정이 필요하다. 주요 부산물인 $N_2$, $O_2$, $CF_4$와의 분리 효율 측면에서 분리막법은 기존의 흡착, 심냉법에 비하여 상대적으로 높은 효율을 보이고 있어 이에 대한 관심 또한 증가하고 있다. 따라서 본 논문에서는 중전기 산업에서 발생되는 $SF_6$ 가스 함유 농도 90 vol% 이상의 가스에 대하여 분리막법을 적용하여 $N_2$, $O_2$, $CF_4$와 $SF_6$ 가스의 온도와 배출유량의 변화에 따른 분리 회수 가능성을 관찰하였다. PSF와 PC 중공사 분리막을 이용하여 고농도 $SF_6$에 대한 분리 회수 실험 결과, PSF 분리막의 최대 회수율은 압력 0.3 MPa, 온도 $25^{\circ}C$, 배출유량 150 cc/min에서 92.7%를 나타내었으며, PC 분리막에서는 압력 0.3 MPa, 온도 $45^{\circ}C$, 배출유량 150 cc/min 일 때 74.8%의 최대 회수율을 나타내었다. 또한, 사용된 두 가지 분리막과 운전 조건에서 주요 부산물인 $N_2$, $O_2$, $CF_4$의 최대 제거율은 각각 약 80%, 74%, 그리고 58.9%가 관찰되었다. 이로부터 분리막 공정은 고농도 폐 $SF_6$ 가스에서 주요 부산물로부터 $SF_6$의 효과적인 분리 및 회수가 가능한 공정으로 적용할 수 있는 가능성을 파악 할 수 있었다.