• 대한환경공학회지
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• 제38권6호
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• pp.317-322
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• 2016

PFOS sodium salt ($C_8F_{17}SO_3Na$)는 28일 동안 미생물에 의한 분해가 이루어지지 않은 반면 4종의 대체물질($C_{25}F_{17}H_{32}S_3O_{13}Na_3$, $C_{15}F_9H_{21}S_2O_8Na_2$, $C_{23}F_{18}H_{28}S_2O_8Na_2$, $C_{17}F_9H_{25}S_2O_8Na_2$)은 각각 21.6%, 20.5%, 15.8% 그리고 6.4% 분해가 이루어졌다. Daphnia magna를 이용하여 48시간 동안 수행한 물벼룩급성독성시험에서 sodium salt ($C_8F_{17}SO_3Na$)의 반수영향농도($EC_{50}$)는 54.5 mg/L 인 것으로 확인된 반면 4종의 대체물질은 500.0 mg/L에서 아무런 영향이 나타나지 않았다. 500.0 mg/L에서 PFOS sodium salt($C_8F_{17}SO_3Na$)의 표면장력은 46.2 mN/m이었으며 대체물질 4종의 표면장력은 모두 PFOS sodium salt 보다 우수한 것으로 확인되었다. $C_{23}F_{18}H_{28}S_2O_8Na_2$ (20.9 mN/m)는 가장 낮은 표면장력을 갖고 있었다. 그 다음은 $C_{15}F_9H_{21}S_2O_8Na_2$ (23.4 mN/m), $C_{17}F_9H_{25}S_2O_8Na_2$ (27.3 mN/m) 그리고 $C_{25}F_{17}H_{32}S_3O_{13}Na_3$ (28.2 mN/m) 순인 것으로 확인되었다. 미생물분해시험, 물벼룩급성독성시험 그리고 표면장력측정 결과를 종합해 보면 4종의 PFOS 대체물질($C_{25}F_{17}H_{32}S_3O_{13}Na_3$, $C_{15}F_9H_{21}S_2O_8Na_2$, $C_{23}F_{18}H_{28}S_2O_8Na_2$, $C_{17}F_9H_{25}S_2O_8Na_2$)은 모두 PFOS sodium salt ($C_8F_{17}SO_3Na$) 보다 우수한 것으로 확인되었으며 특히 3종의 대체물질($C_{15}F_9H_{21}S_2O_8Na_2$, $C_{23}F_{18}H_{28}S_2O_8Na_2$, $C_{25}F_{17}H_{32}S_3O_{13}Na_3$)은 미생물분해율이 15.8~21.6%로 상대적으로 높고, 물벼룩급성독성과 표면장력측정이 PFOS sodium salt 보다 상당히 우수하다. 그러므로 이들 4종의 대체물질은 PFOS 대체물질로 활용이 가능할 것으로 판단된다.

• 한국진공학회:학술대회논문집
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• 한국진공학회 2014년도 제46회 동계 정기학술대회 초록집
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• pp.412-412
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• 2014

Zinc oxide (ZnO) is one of the most powerful materials for purifying organic pollutants using photocatalytic activity. In this study, we have introduced a novel method to design highly photoreactive flexible 3 dimensional (3D) ZnO nanocomposite [F-ZnO-m (m: reaction time, min)] by electrospinning and simple-step ZnO growth processing (one-step ZnO seed coating/growth processing). Significantly, the F-ZnO-m could be a new platform (or candidate) as a photocatalytic technology for both morphology control and large-area production. The highest photocatalytic degradation rate ([k]) was observed for F-ZnO-m at 2.552 h-1, which was 8.1 times higher than that of ZnO nanoparticles (NPs; [k] = 0.316 h-1). The enhanced photocatalytic activity of F-ZnO-m may be attributed to factors such as large surface area. The F-ZnO-m is highly recyclable and retained 98.6% of the initial decolorization rate after fifteen cycles. Interestingly, the F-ZnO-m samples show very strong antibacterial properties against both Gram-negative Escherichia coli (E. coli) and Gram-positive Staphylococcus aureus (S. aureus) after exposure to UV-light for 30 min. The antibacterial properties of F-ZnO-m samples are more effective than those of ZnO NPs. More than 96.6% of the E. coli is sterilized after ten cycles. These results indicate that F-ZnO-m samples might have utility in several promising applications such as highly efficient water/air treatment and inactivation of pathogenic microorganisms.

• 한국진공학회:학술대회논문집
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• 한국진공학회 2013년도 제45회 하계 정기학술대회 초록집
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• pp.270.1-270.1
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• 2013

Zinc oxide (ZnO) is one of the most powerful materials for purifying organic pollutants using photocatalytic activity. In this study, we have introduced a novel method to design highly photoreactive flexible 3 dimensional (3D) ZnO nanocomposite [F-ZnO-m (m: reaction time, min)] by electrospinning and simple-step ZnO growth processing (one-step ZnO seed coating/growth processing). Significantly, the F-ZnO-m could be a new platform (or candidate) as a photocatalytic technology for both morphology control and largearea production. The highest photocatalytic degradation rate ([k]) was observed for F-ZnO-m at 2.552 h-1, which was 8.1 times higher than that of ZnO nanoparticles (NPs; [k] = 0.316 h-1). The enhanced photocatalytic activity of F-ZnO-m may be attributed to factors such as large surface area. The F-ZnO-m is highly recyclable and retained 98.6% of the initial decolorization rate after fifteen cycles. Interestingly, the F-ZnO-m samples show very strong antibacterial properties against both Gram-negative Escherichia coli (E. coli) and Gram-positive Staphylococcus aureus (S. aureus) after exposure to UV-light for 30 min. The antibacterial properties of F-ZnO-m samples are more effective than those of ZnO NPs. More than 96.6% of the E. coli is sterilized after ten cycles. These results indicate that F-ZnO-m samples might have utility in several promising applications such as highly efficient water/air treatment and inactivation of pathogenic microorganisms.

• 한국전기전자재료학회:학술대회논문집
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• 한국전기전자재료학회 2000년도 하계학술대회 논문집
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• pp.548-551
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• 2000

Spinel phase LiF $e_{y}$M $n_{2-y}$ $O_4$samples are synthesized by calcining a LiOH.$H_2O$, Mn $O_2$and F $e_2$ $O_3$mixture at 80$0^{\circ}C$ for 36h in air. Preparing LiF $e_{y}$M $n_{2-y}$ $O_4$showed spinel phase with cubic phase. The ununiform distortion of the crystallite of the spinel LiF $e_{y}$M $n_{2-y}$ $O_4$was more stable than that of the pure. The discharge capacity of the cathode for the Li/LiF $e_{0.1}$M $n_{1.9}$ $O_4$cell at the first than that of the pure. The discharge capacity of the cathode for the Li/LiF $e_{0.1}$M $n_{1.9}$ $O_4$cell at the first cycle and at the 70th cycle was about 113 and 90mAh/g, respectively. This cell capacity was retained about 82% of the first cycle after 70th cycle. Impedance profile of this cell was more stable than that pure. The resistance, the capacitance and chemical diffusion coefficients of lithium ion showed approximately 80$\Omega$, 36133.87$\mu$F ; 1.4$\times$10$^{-8}$ c $m^2$ $s^{-1}$ , respectively. , respectively.ely.

• Journal of Forest and Environmental Science
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• 제11권1호
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• pp.72-80
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• 1995

강원대학교 부속 연습림의 낙엽활엽수림에서 임상유기물(O층)의 집적에 미치는 표고의 영향을 조사하였다. 표고가 높아짐에 따라 O층의 두께는 증가하였으며, 이러한 경향은 F2층과 H층에서 뚜렷하였다. O층의 두께(X, cm)와 무게(Y, $kg/m^2$)의 관계는 직선회귀식 Y($kg/m^2$) = aX(cm)에 근사였으며, F2층, H층 및 F2 + H층에 대한 계수 "a" 의 값은 각각 0.43, 0.61 및 0.53이었다. 유기물의 용적중은 F2층, H층 및 F2+H층에서 각각 $45g/dm^2$, $60g/dm^2$ 및 $55g/dm^2$ 전후로 추정되었다. O층의 양은 표고 280m에서의 13ton/ha으로부터 표고 710m의 41ton/ha의 범위에 있었으며, F1, F2및 H층은 각각 5~10ton/ha, 5~11ton/ha 및 13~40ton/ha의 범위를 차지하였다.

• The Korean Journal of Ceramics
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• 제4권3호
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• pp.204-206
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• 1998

The Gibbs free energy of formation of $BaThO_3$ from elemental oxides has been measured at temperatures between 853 and 903 K using a $CaF_2$ solid electrolyte galvanic cell. The galvanic cell consisted of Pt, $O_2, CaO+CaF_2 \parallel CaF_2 \parallelBaThO_3+ThO_2+BaF_2, O_2$, Pt EMF gave the standard Gibbs free energy for the reaction $CaF_2+BaThO_3=CaO+BaF_2+ThO_3$ as $\DeltaG^o$,/TEX>=124111.031-117.597 T(J/mol).

• 한국자기학회지
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• 제10권3호
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• pp.106-111
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• 2000

페라이트 도금 방법으로 M $n_{x}$Z $n_{0.22}$F $e_{2.78-x}$ $O_4$(x=0.00~0.08)와 N $i_{x}$Z $n_{0.22}$F $e_{*}$2.78-x/ $O_4$(x=0.00~0.15)의 스피넬 페라이트 박막을 제작하였다. 반응용액의 조성비 변화에 따라 형성된 박막의 조성비와 성장속도를 조사하였다. 제조한 시료들의 결정성과 미세구조는 x-선 회절분석과 전자현미경으로 조사하고, 시료의 자기적 성질을 진동 시료형 자력계를 사용하여 조사했다. 조성비 x가 증가함에 따라 격자상수는 M $n_{x}$Z $n_{0.22}$F $e_{2.78-x}$ $O_4$(x=0.00~0.08) 박막에서 증가하지만, N $i_{x}$Z $n_{0.22}$F $e_{2.78-x}$ $O_4$(x=0.00~0.15) 박막에서 감소한다. M $n_{x}$Z $n_{0.22}$F $e_{2.78-x}$ $O_4$(x = 0.00~0.08) 박막의 포화자화는 419 emu/㎤에서 394 emu/㎤ 의 값을 가져 N $i_{x}$Z $n_{0.22}$F $e_{2.78-x}$ $O_4$(x=0.00~0.15)의 $M_{s}$ 보다 높게 나타났다. 보다 높게 나타났다. 보다 높게 나타났다.

• 한국환경보건학회지
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• 제42권2호
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• pp.112-117
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• 2016

Objectives: In this study, we investigated the biodegradation rates of 8 perfluorooctanesulfonate (PFOS) alternatives synthesized at the at Changwon National University in comparison to those of PFOS potassium salt and PFOS sodium salt. Methods: A biodegradability test was performed for 28 days with microorganisms cultured in the good laboratory practice laboratory at the Korea Environment Corporation following the OECD Guidelines for the testing of chemicals, Test No. 301 C Results: While $C_5H_8F_3SO_3K$, $C_8F_{17}SO_3K$ and $C_8F_{17}SO_3Na$ were not degraded after 28 days, the 3 alternatives were biodegraded at the rates of 31.4% for $C_8H_8F_9SO_3K$, 25.6% for $C_{10}H_8F_{13}SO_3K$, 23.6% for $C_{25}F_{17}H_{32}S_3O_{13}Na_3$, 20.9% for $C_{15}F_9H_{21}S_2O_8Na_2$, 15.5% for $C_{23}F_{18}H_{28}S_2O_8Na_2$, 8.5% for $C_{17}F_9H_{25}S_2O_8Na_2$ and 4.8% for $C_6H_8F_5SO_3K$. When the concentration was the same(500 mg/L), $C_{23}F_{18}H_{28}S_2O_8Na_2$ had the lowest tension with 20.94 mN/m, which was followed by $C_{15}F_9H_{21}S_2O_8Na_2$ (23.36 mN/m), $C_{17}F_9H_{25}S_2O_8Na_2$ (27.31 mN/m), $C_{25}F_{17}H_{32}S_3O_{13}Na_3$ (28.17 mN/m), $C_{10}H_8F_{13}SO_3K$ (29.77 mN/m) and $C_8H_8F_9SO_3K$ (33.89 mN/m). Having higher surface tension of 57.64 mN/m and 67.57 mN/m, respectively, than those of the two types of PFOS salts, $C_6H_8F_5SO_3K$ and $C_5H_8F_3SO_3K$ were found valueless as substitute for PFOS. Conclusion: The biodegradation test suggest that 6 compounds could be used as substitutes for PFOS. $C_{23}F_{18}H_{28}S_2O_8Na_2$ and $C_{15}F_9H_{21}S_2O_8Na_2$ were found to be the best substitutes based on biodegradation rate and surface tension, followed by $C_{25}F_{17}H_{32}S_3O_{13}Na_3$, $C_8H_8F_9SO_3K$ and $C_{10}H_8F_{13}SO_3K$. $C_{17}F_9H_{25}S_2O_8Na_2$ was found to have relatively low value as an alternative but it still had a potential to substitute the conventional PFOS.

• 대한수학회보
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• 제52권5호
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• pp.1559-1568
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• 2015

The relative class number $H_d(f)$ of a real quadratic field $K=\mathbb{Q}(\sqrt{m})$ of discriminant d is the ratio of class numbers of $O_f$ and $O_K$, where $O_K$ denotes the ring of integers of K and $O_f$ is the order of conductor f given by $\mathbb{Z}+fO_K$. In a recent paper of A. Furness and E. A. Parker the relative class number of $\mathbb{Q}(\sqrt{m})$ has been investigated using continued fraction in the special case when $(\sqrt{m})$ has a diagonal form. Here, we extend their result and show that there exists a conductor f of relative class number 1 when the continued fraction of $(\sqrt{m})$ is non-diagonal of period 4 or 5. We also show that there exist infinitely many real quadratic fields with any power of 2 as relative class number if there are infinitely many Mersenne primes.

• 대한수학회논문집
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• 제20권2호
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• pp.339-350
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• 2005

We obtain the following two inequalities on a strongly pseudoconvex domain $\Omega\;in\;\mathbb{C}^n\;:\;for\;f\;{\in}\;O(\Omega)$ $$\int_{0}^{{\delta}0}t^{a{\mid}a{\mid}+b}M_p^a(t, D^{a}f)dt\lesssim\int_{0}^{{\delta}0}t^{b}M_p^a(t,\;f)dt\;\int_{O}^{{\delta}O}t_{b}M_p^a(t,\;f)dt\lesssim\sum_{j=0}^{m}\int_{O}^{{\delta}O}t^{am+b}M_{p}^{a}\(t,\;\aleph^{i}f\)dt$$. In [9], Shi proved these results for the unit ball in $\mathbb{C}^n$. These are generalizations of some classical results of Hardy and Littlewood.