• 원예과학기술지
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• 제17권2호
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• pp.136-137
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• 1999

신나팔나리의 발아률(發芽率) 및 상품성 향상을 위하여 $GA_3$, 염류(鹽類) 및 저온(低溫) 등을 이용하여 종자 priming 처리한 결과 파종 후 10일째 초기 발아률(發芽率)은 $Ca(NO_3)_2$ 200mM 및 $KNO_3$ 200mM 처리구가 높았으나 최종 발아률(發芽率)에서는 처리구간에 유의차가 없었으며 발아세는 $Ca(NO_3)_2$ 200mM 처리구에서 가장 높게 나타났다. 초기 생육은 $Ca(NO_3)_2$ 200mM, $KNO_3$ 200mM 처리구가 엽수(葉數)가 많았고 구경(球徑)이 컸으며 건물중(乾物重)도 무거웠다.

• 약학회지
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• 제43권6호
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• pp.834-842
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• 1999

The metabolism and pharmacokinetics of M-l, which is metabolite of pentoxifylline, have been studied in human liver microsomes. Biphasic kinetics was observed from the Eadie-Hofstee plot for the formation of both metabolites of M-l. For the kinetics of pentoxifylline, mean values of $V_{max1}{\;}and{\;}V_{max2}$ were 1,648 and 5,622 nmol/min/mg protein, and the estimated values of $K_{ml}{\;}and{\;}K_{m2}$ were 0.180 and 4.829 mM, respectively. For M-3, mean values of $V_{max1}{\;}and{\;}V_{max2}$ were 0.062 and 0.491 nmol/min/mg protein, and estimated values of $K_{ml}{\;}and{\;}K_{m2}$ were 0.025 and 1.216 mM. The formations of pentoxifylline and M-3 from M-1 were indentified by using several selective inhibitors of cytochrome P450 isoformes at 0.05-5 mM concentration of M-1 in human liver microsomes. For the analysis of low (0.05 mM) concentration of M-1, where the affinity was expected as low, indicated that CYPlA2 and CYP3A4 were major P450 isoforms responsible for pentoxifylline and M-3 formation. CYP3A4 and CYP2A6 appeared to be P450 isoforms responsible for M-3 formation at high (5 mM) concentration of M-1.

• Archives of Pharmacal Research
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• 제23권5호
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• pp.525-530
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• 2000

mST3GaIV synthesizes ganglioside GM3, the precursor for simple and complex a- and b- series gangliosides, and the expression and regulation of mST3GaIV (CMP-NeuAc: lactosylceramide $\alpha$2,3-sialyltransferase) activity is central to the production of almost all gangliosides, a class of glycosphingolipids implicated in variety of cellular processes such as transmembrane signaling, synaptic transmission, specialized membrane domain formation and cell-cell interactions. To understand the developmental expression of mST3GaIV in mice, we investigated the spatial and temporal expression of mST3GaIV mRNA during the mouse embryogenesis [embryonic (E) days; 19, E11, E13, E15] by in situ hybridization with digoxigenin-labeled RNA probes. All tissues from 19 and E11 were positive for mST3GaIV mRNA. On E13, mST3GaIV mRNA was expressed in various neural and non-neural tissues. In contrast to these, on E15, the telencephalon and liver produced a strong expression of mST3GaIV which was a quite similar to that of E13. In this stage, mST3GaIV mRNA was also expressed in some non-neural tissues. These data indicate that mST3GaIV is differently expressed at developmental stages of embryo, and this may be importantly related with regulation of organogenesis in mice.

• 생명과학회지
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• 제25권5호
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• pp.487-495
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• 2015

Pseudomonas pseudoalcaligenes KF707에서 정제한 protocatechuate 3,4-dioxygenase의 특징을 조사하기 위하여 pH안정성, 화학적 저해, 화학적 수식과 pH의존성 반응 상수에 대한 실험을 수행하였다. 이 효소는 pH 4.5~10.7에서 안정하였다. L-ascorbate와 glutathione은 Kis가 각각 0.17 mM과 0.86 mM인 경쟁적 저해제였으며, DL-dithiothreitol은 Kis 1.57 mM 및 Kii 8.08 mM의 비경쟁적 저해패턴을 나타내었다. Potassium cyanide, p-hydroxybenzoate 및 sodium azide는 Kis가 각각 55.7 mM, 0.22 mM 및15.64 mM이었으며, Kii는 각각94.1 mM, 8.08 mM, 및 662.64 mM인 비경쟁적 저해패턴을 나타내었다. $FeCl_{2}$는 Kis가 $29{\mu}M$로 가장 우수한 경쟁적 저해제였으며, $FeCl_{3}$, $MnCl_{2}$, $CoCl_{2}$, $HgCl_{2}$, $AlCl_{3}$도 각각 Kis가 1.21 mM, 0.85 mM, 3.98 mM, 0.17 mM 및 0.21 mM인 경쟁적 저해패턴을 보였다. 한편, 다른 금속이온들은 비경쟁적 저해패턴을 나타내었다. pH의존성 반응상수의 실험결과로부터 pK 6.2와 9.4의 촉매부위와 pK 5.5와 9.0의 결합부위가 존재함을 알 수 있었다. Lysine, cysteine, tyrosine, carboxyl과 histidine은 각각의 고유한 화학적 수식제에 의해 수식되었는데, 이는 이들 잔기들이 결합과 촉매에 관여한다는 것을 나타낸다. 위 결과를 토대로 화학적 메커니즘을 제시한다.

• 환경영향평가
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• 제14권5호
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• pp.355-363
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• 2005

We studied the concentrations of $PM_{10}$ and heavy metal in the incinerators around Dong-hae from December 2003 to April 2004. The seasonal mean of $PM_{10}$ concentration was less than the value of environmental standard, the lowest ($36.59mg/m^3$) in spring and the highest ($78.54mg/m^3$) in fall. The measured seasonal heavy metals were Fe $503,44ng/m^3$, Mg $410.85ng/m^3$, Na $134.14ng/m^3$, Zn $24.58ng/m^3$ in spring and Na $315.29ng/m^3$, Mg $48.36ng/m^3$, Fe $44.78ng/m^3$, Zn $23.34ng/m^3$ in summer and Na $88.53ng/m^3$, Fe $33.80ng/m^3$, Zn $20,43ng/m^3$, Pb $6.16ng/m^3$ in fall and Na $4603.72ng/m^3$, Fe $575,26ng/m^3$, Al $411.01ng/m^3$, Cr $203.51ng/m^3$ in winter. The relationship between measured metals concentrations showed that Na and Fe were associated with natural sources such as soil. Pb, Cr and Zn were strongly related to urban anthropogenic sources such as fuel combustion.

• 대한수학회논문집
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• 제17권3호
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• pp.451-457
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• 2002

Let (R, m, k) be a maximal commutative k-subalgebra of M$\sub$n/(k) where the index of nilpotency i(m) of m is 3. If the socle of R is of special case, then we can construct some isomorphic maximal commutative subalgebras.

• Nuclear Engineering and Technology
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• 제16권2호
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• pp.58-63
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• 1984

특별히 제작한 영동장치를 써서 8면체 구조의 (Ruc $l_{6}$)$^{3-}$ 를 여과지 전기영동 분리하였다. 자지전해질 용액은 다음과 같다. 0.1M-HCl $O_4$, 0.05M-HCl+0.09M-KCI, 0.1M-HCl, 5$\times$$10^{-3}$M-NTA, 0.01M-HCl, 0.01M-HCl $O_4$, 0.01M-시트르산, 0.01M-K $H_2$P $O_4$+0.01M-$Na_2$HP $O_4$, 0.05M-붕사, 0.025M-$Na_2$C $O_3$+0.025M-NaHC $O_3$, 0.01M-$Na_3$P $O_4$, 0.01M-NaOH, 0.1M-NaOH. (Ruc $l_{6}$)$^{3-}$ 은 2-4피크로 나타내며 다음 화학종으로 확인된다. (RuCl($H_2O$)$_{5}$ )$^{2+}$, cis- 및 trans-(RuC $l_2$($H_2O$)$_4$)$^{1+}$ , (RuC $l_3$($H_2O$)$_3$)$^{0}$ , (RuC $l_4$($H_2O$)$_2$)$^{1-}$, (RuC $l_{5}$ ($H_2O$))$^{2-}$ , (RuC $l_{6}$)$^{3-}$ . 리텐숀 값은 0.025M-$Na_2$C $O_3$+0.025M-NaHC $O_3$ 전해질 용액에서 가장 높다.

• 유기물자원화
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• 제21권4호
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• pp.33-43
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• 2013

해양에서 발생하는 해양폐기물의 효율적인 관리와 해양오염방제시스템에 대한 진일보한 전략수립이 필요하다. 2011년에 발생한 해양오염사고 건수는 총 287건이며, 유출량은 369 kL로 나타났으며 이는 전년 대비 각각 13%, 39%가 감소하였다. 해양물질별 5년 평균량을 살펴보면, 오일 유출량 310.5 kL(중유 106.0 kL, 경유 178.9 kL, 선저폐수 22.3 kL, 기타유 7.7 kL)이고, 폐기물 62.3톤, 위험유해물질(HNS) 510.6 kL로 나타났다. 2011년도 폐기물 종류별 해양배출은 총 투기된 양은 3,972 $m^3$이고, 가축분뇨 795 $m^3$(20%), 폐수 1,431 $m^3$(36%), 하수슬러지 887 $m^3$(22%), 폐수슬러지 813 $m^3$(21%), 분뇨 5 $m^3$(0.1%), 기타 41 $m^3$(0.9%)로 나타났다. 해양폐기물의 개념을 보다 명확히 할 필요가 있다. 유해화학물질관리에 따른 통합사고관리체계를 구축해야 한다. 해안오염을 제거하기 위하여 방제책임자가 활용 할 수 있는 한국형 해안방제시스템의 필요하다. 해상방제와 마찬가지로 해안방제도 단계적 대응체제 구축이 필요하다.

• 약학회지
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• 제30권1호
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• pp.42-46
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• 1986

The binding characteristics of five cephalosporins, cefamandole, ceftriaxone, cefoxitin, latamoxef, and cefotetan to bovine serum albumin (BSA) was examined by UV difference spectrophotometry. 2-(4'-hydroxybenzeneazo) benzoic acid was used as the spectrophotometric probe. Competitive bindings between the probe and cephalosporins were observed. Based on the Scatchard plot, the BSA appeared to have two classes of binding sites in BSA binding with cephalosporins. The number of primary binding sites appears to be one, secondary binding sites appears to be three. The binding constants were found as follows: BSA-HBAB; $K_1^{obs}$=8.39$\times$$10^4$ $M^{-1}$, $K_2^{obs}$=1.60$\times$$10^4$ $M^{-1}$, BSA-Cefamandole; $K_1^{obs}$=5.44$\times$$10^3$ $M^{-1}$, $K_2^{obs}$=0.74$\times$$10^3$ $M^{-1}$, BSA-Cefotriaxone; $K_1^{obs}$=6.78$\times$$10^3$ $M^{-1}$, $K_2^{obs}$=0.88$\times$$10^3$ $M^{-1}$, BSA-Cefoxitin; $K_1^{obs}$=7.24$\times$$10^3$ $M^{-1}$, $K_2^{obs}$=1.13$\times$$10^3$ $M^{-1}$, BSA-Latamoxef; $K_1^{obs}$=8.87$\times$$10^3$ $M^{-1}$, $K_2^{obs}$=1.92$\times$$10^3$ $M^{-1}$, BSA-Cefotetan; $K_1^{obs}$=15.41$\times$$10^3$ $M^{-1}$, $K_2^{obs}$=2.7$\times$$10^3$ $M^{-1}$.

• 한국신재생에너지학회:학술대회논문집
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• 한국신재생에너지학회 2007년도 춘계학술대회
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• pp.456-459
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• 2007

Thermal conductivities (TC) of 57 Jurassic muscovitic granite samples (KIGAM) and 149 porphyritic granite samples (Yeonki: BE-2, BE-3) were measured with LFA-447. Ranges of TC values are $2.429{\sim}3.878$ W/mK (KIGAM), $2.220{\sim}3.767$ W/mK (Yeonki, BE-2) and $2.019{\sim}3.990$ W/mK (Yeonki, BE-3); arithmetic means are 2.924 W/mK (KIGAM), 2.907 W/mK (Yeonki, BE-2), and 2.881 W/mK (Yeonki, BE-3), respectively. In this study, harmonic mean values were calculated to estimate the average value of TC. Harmonic mean values are 2.883 W/mK (KIGAM), 2.886 W/mK (Yeonki, BE-2), and 2.866 W/mK (Yeonki, BE-3), respectively. Heat extraction rates of a borehole heat exchanger strongly depend on TC values. Heat-extraction rates from re values are expected to be a little lower than 84 W/m in all sites. However, considering ground water flow, it is expected that actual heat extraction rate would be higher than the expected value.