• Journal of Microbiology and Biotechnology
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• 제20권6호
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• pp.1011-1017
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• 2010

A novel dioscin-glycosidase that specifically hydrolyzes multi-glycosides, such as 3-O-${\alpha}$-L-($1{\to}4$)-rhamnoside, 3-O-${\alpha}$-L-($1{\to}2$)-rhamnoside, 3-O-${\alpha}$-L-($1{\to}4$)-arabinoside, and ${\beta}$-D-glucoside, on diosgenin was isolated from the Absidia sp.d38 strain, purified, and characterized. The molecular mass of the new dioscin-glycosidase is about 55 kDa based on SDS-PAGE. The dioscin-glycosidase gradually hydrolyzes either 3-O-${\alpha}$-L-($1{\to}4$)-Rha or 3-O-${\alpha}$-L-($1{\to}2$)-Rha from dioscin into 3-O-${\alpha}$-L-Rha-${\beta}$-D-Glc-diosgenin, further rapidly hydrolyzes the other ${\alpha}$-L-Rha from 3-O-${\alpha}$-L-Rha-${\beta}$-D-Glc-diosgenin into the main intermediate products of 3-O-${\beta}$-D-Glc-diosgenin, and subsequently hydrolyzes these intermediate products into aglycone as the final product. The enzyme also gradually hydrolyzes 3-O-${\alpha}$-L-($1{\to}4$)-arabinoside, 3-O-${\alpha}$-L-($1{\to}2$)-rhamnoside, and ${\beta}$-D-glucoside from [3-O-${\alpha}$-L-($1{\to}4$)-Ara, 3-O-${\alpha}$-L-($1{\to}4$)-Rha]-${\beta}$-D-Glc-diosgenin into diosgenin as the final product, exhibiting significant differences from previously reported glycosidases. The optimal temperature and pH for the new dioscin-glycosidase is $40^{\circ}C$ and 5.0, respectively. Whereas the activity of the new dioscin-glycosidase was not affected by $Na^+$, $K^+$, and $Mg^{2+}$ ions, it was significantly inhibited by $Cu^{2+}$ and $Hg^{2+}$ ions, and slightly affected by $Ca^{2+}$ ions.

• 한국농공학회지
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• 제16권1호
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• pp.3225-3262
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• 1974

The purposes of this thesis are to clarify experimentally the variation of ground water temperature in tube wells during the irrigation period of paddy rice, and the effect of ground water irrigation on the growth, grain yield and yield components of the rice plant, and, furthermore, when and why the plant is most liable to be damaged by ground water, and also to find out the effective ground water irrigation methods. The results obtained in this experiment are as follows; 1. The temperature of ground water in tube wells varies according to the location, year, and the depth of the well. The average temperatures of ground water in a tubewells, 6.3m, 8.0m deep are $14.5^{\circ}C$ and $13.1^{\circ}C$, respercively, during the irrigation period of paddy rice (From the middle of June to the end of September). In the former the temperature rises continuously from $12.3^{\circ}C$ to 16.4$^{\circ}C$ and in the latter from $12.4^{\circ}C$ to $13.8^{\circ}C$ during the same period. These temperatures are approximately the same value as the estimated temperatures. The temperature difference between the ground water and the surface water is approximately $11^{\circ}C$. 2. The results obtained from the analysis of the water quality of the "Seoho" reservoir and that of water from the tube well show that the pH values of the ground water and the surface water are 6.35 and 6.00, respectively, and inorganic components such as N, PO4, Na, Cl, SiO2 and Ca are contained more in the ground water than in the surface water while K, SO4, Fe and Mg are contained less in the ground water. 3. The response of growth, yield and yield components of paddy rice to ground water irrigation are as follows; (l) Using ground water irrigation during the watered rice nursery period(seeding date: 30 April, 1970), the chracteristics of a young rice plant, such as plant height, number of leaves, and number of tillers are inferior to those of young rice plants irrigated with surface water during the same period. (2) In cases where ground water and surface water are supplied separately by the gravity flow method, it is found that ground water irrigation to the rice plant delays the stage at which there is a maximum increase in the number of tillers by 6 days. (3) At the tillering stage of rice plant just after transplanting, the effect of ground water irrigation on the increase in the number of tillers is better, compared with the method of supplying surface water throughout the whole irrigation period. Conversely, the number of tillers is decreased by ground water irrigation at the reproductive stage. Plant height is extremely restrained by ground water irrigation. (4) Heading date is clearly delayed by the ground water irrigation when it is practised during the growth stages or at the reproductive stage only. (5) The heading date of rice plants is slightly delayed by irrigation with the gravity flow method as compared with the standing water method. (6) The response of yield and of yield components of rice to ground water irrigation are as follows: \circled1 When ground water irrigation is practised during the growth stages and the reproductive stage, the culm length of the rice plant is reduced by 11 percent and 8 percent, respectively, when compared with the surface water irrigation used throughout all the growth stages. \circled2 Panicle length is found to be the longest on the test plot in which ground water irrigation is practised at the tillering stage. A similar tendency as that seen in the culm length is observed on other test plots. \circled3 The number of panicles is found to be the least on the plot in which ground water irrigation is practised by the gravity flow method throughout all the growth stages of the rice plant. No significant difference is found between the other plots. \circled4 The number of spikelets per panicle at the various stages of rice growth at which_ surface or ground water is supplied by gravity flow method are as follows; surface water at all growth stages‥‥‥‥‥ 98.5. Ground water at all growth stages‥‥‥‥‥‥62.2 Ground water at the tillering stage‥‥‥‥‥ 82.6. Ground water at the reproductive stage ‥‥‥‥‥ 74.1. \circled5 Ripening percentage is about 70 percent on the test plot in which ground water irrigation is practised during all the growth stages and at the tillering stage only. However, when ground water irrigation is practised, at the reproductive stage, the ripening percentage is reduced to 50 percent. This means that 20 percent reduction in the ripening percentage by using ground water irrigation at the reproductive stage. \circled6 The weight of 1,000 kernels is found to show a similar tendency as in the case of ripening percentage i. e. the ground water irrigation during all the growth stages and at the reproductive stage results in a decreased weight of the 1,000 kernels. \circled7 The yield of brown rice from the various treatments are as follows; Gravity flow; Surface water at all growth stages‥‥‥‥‥‥514kg/10a. Ground water at all growth stages‥‥‥‥‥‥428kg/10a. Ground water at the reproductive stage‥‥‥‥‥‥430kg/10a. Standing water; Surface water at all growh stages‥‥‥‥‥‥556kg/10a. Ground water at all growth stages‥‥‥‥‥‥441kg/10a. Ground water at the reproductive stage‥‥‥‥‥‥450kg/10a. The above figures show that ground water irrigation by the gravity flow and by the standing water method during all the growth stages resulted in an 18 percent and a 21 percent decrease in the yield of brown rice, respectively, when compared with surface water irrigation. Also ground water irrigation by gravity flow and by standing water resulted in respective decreases in yield of 16 percent and 19 percent, compared with the surface irrigation method. 4. Results obtained from the experiments on the improvement of ground water irrigation efficiency to paddy rice are as follows; (1) When the standing water irrigation with surface water is practised, the daily average water temperature in a paddy field is 25.2$^{\circ}C$, but, when the gravity flow method is practised with the same irrigation water, the daily average water temperature is 24.5$^{\circ}C$. This means that the former is 0.7$^{\circ}C$ higher than the latter. On the other hand, when ground water is used, the daily water temperatures in a paddy field are respectively 21.$0^{\circ}C$ and 19.3$^{\circ}C$ by practising standing water and the gravity flow method. It can be seen that the former is approximately 1.$0^{\circ}C$ higher than the latter. (2) When the non-water-logged cultivation is practised, the yield of brown rice is 516.3kg/10a, while the yield of brown rice from ground water irrigation plot throughout the whole irrigation period and surface water irrigation plot are 446.3kg/10a and 556.4kg/10a, respectivelely. This means that there is no significant difference in yields between surface water irrigation practice and non-water-logged cultivation, and also means that non-water-logged cultivation results in a 12.6 percent increase in yield compared with the yield from the ground water irrigation plot. (3) The black and white coloring on the inside surface of the water warming ponds has no substantial effect on the temperature of the water. The average daily water temperatures of the various water warming ponds, having different depths, are expressed as Y=aX+b, while the daily average water temperatures at various depths in a water warming pond are expressed as Y=a(b)x (where Y: the daily average water temperature, a,b: constants depending on the type of water warming pond, X; water depth). As the depth of water warning pond is increased, the diurnal difference of the highest and the lowest water temperature is decreased, and also, the time at which the highest water temperature occurs, is delayed. (4) The degree of warming by using a polyethylene tube, 100m in length and 10cm in diameter, is 4~9$^{\circ}C$. Heat exchange rate of a polyethylene tube is 1.5 times higher than that or a water warming channel. The following equation expresses the water warming mechanism of a polyethylene tube where distance from the tube inlet, time in day and several climatic factors are given: {{{{ theta omega (dwt)= { a}_{0 } (1-e- { x} over { PHI v })+ { 2} atop { SUM from { { n}=1} { { a}_{n } } over { SQRT { 1+ {( n omega PHI) }^{2 } } } } LEFT { sin(n omega t+ { b}_{n }+ { tan}^{-1 }n omega PHI )-e- { x} over { PHI v }sin(n omega LEFT ( t- { x} over {v } RIGHT ) + { b}_{n }+ { tan}^{-1 }n omega PHI ) RIGHT } +e- { x} over { PHI v } theta i}}}}{{{{ { theta }_{$\infty$ }(t)= { { alpha theta }_{a }+ { theta }_{ w'} +(S- { B}_{s } ) { U}_{w } } over { beta } , PHI = { { cpDU}_{ omega } } over {4 beta } }}}} where $\theta$$\omega$; discharged water temperature($^{\circ}C$) $\theta$a; air temperature ($^{\circ}C$) $\theta$$\omega$';ponded water temperature($^{\circ}C$) s ; net solar radiation(ly/min) t ; time(tadian) x; tube length(cm) D; diameter(cm) ao,an,bn;constants determined from $\theta$$\omega$(t) varitation. cp; heat capacity of water(cal/$^{\circ}C$ ㎥) U,Ua; overall heat transfer coefficient(cal/$^{\circ}C$ $\textrm{cm}^2$ min-1) $\omega$;1 velocity of water in a polyethylene tube(cm/min) Bs ; heat exchange rate between water and soil(ly/min)

• 생태와환경
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• 제36권3호통권104호
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• pp.235-241
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• 2003

자외선에 의한 조류기원 용존유기물의 특성변화를 조사하기 위하여 배양한 남조류 두종 (Microcystis aeruginosa, Oscillatoria agardhii)의 체외배출용존유기물에 자외선 처리전과 처리후의 생분해도와 유기물의 화학적조성을 비교하였다. 자외선처리는 pyrex용기에 시료를 넣고 인공자외선램프(UVA: 40 W/$m^2$, UVB: 2 W/$m^2$)로 24시간 조사하였다. 유기물의 화학적조성은 XAD-8, 양이온, 음이온수지를 이용하여 소수성 산 (hydrophobic acids; HoA), 소수성 중성 (hydrophobic neutrals;HoN), 친수성 산 (hydrophilic acids; HiA), 친수성 염기 (hydrophilic bases; HiB), 그리고 친수성 중성 (hydrophilic neutrals; HiN)의 5개 분획으로 분류하였다. 자외선처리동안 유기물의 농도변화는 거의 없었던 반면 생분해도는 자외선처리 전에 비해 현저히 감소하였다(M. aeruginosa: 17%, O. agardhii: 28% 감소). 또한 자외선 처리 전과 후의 유기물의 화학적조성도 상당한 차이를 보였다. 자외선처리 후 HiB분획(단백질, 아미노산류)은 감소한 반면 HiA분획 (카복실산류)은 증가하였다. 유기산분석에서도 3종류의 카복실산이 자외선처리 후 증가하는 것으로 나타났다. 일반적으로 수체의 유기물은 자외선에 의해 난분해성 유기물이 분해되거나 잘게 쪼개져 이분해성 유기물로 전환되는 것으로 알려졌다. 그러나 본 연구에서는 조류기원의 이분해성 유기물의 경우는 자외선에 의해 완전한 광분해는 보이지 않았지만 난분해성 유기물로 전환되었고 화학적조성도 바뀌었다. 이는 유기물의 기원과 종류에 따라 자외선에 대한 영향이 다르다는 것을 시사한다.0.73, P< 0.001). 본 연구기간동안 동물플랑크톤 섭식에 의한 청수기는 관찰되지 않았으며, 동 ${\cdot}$ 식물플랑크톤의 다양성은 식물플랑크톤의 생물량 증가 시 회복되는 것으로 나타났다. 본 연구결과에서는 부영양 호수에서 동물플랑크톤의 섭식이나 제한영양염의 결핍이 식물플랑크톤의 현존량에 영향을 출 수 있으나 군집의 변화를 야기하지는 못함이 제시되었다.X>$NH_4\;^+$, $NO_3\;^-$, $PO_4\;^{3-}$ 및 $SiO_2$의 용출량 범위는 각각 -9${\sim}$ 105 mgN $m^{-2}day^{-1}$, -156${\sim}$62 $m^{-2}day^{-1}$ -5${\sim}$5 $m^{-2}day^{-1}$, 및 12 ${\sim}$ 117 $m^{-2}day^{-1}$였다. 낙동강과 서낙동강에서 식물플랑크톤의 1차 생산성과 조체의 C:N:P의 Redfield 비율 106: 16: 1을 이용하여 추정한결과 저질에서 용출되는 $NH_4\;^+$는 식물플랑크톤의 요구량의 9 ${\sim}$23%이었고, $PO_4\;^{3-}$는 11 ${\sim}$ 22%를 차지하였다.도로 검출되어 이를 고려한정수공정의 관리가 필요하리라 생각된다.$yr^{-1}$)의 71%가 감소되어야 할 필요성이 제기되었다. 또한 여름철 심층 산소 고갈이 야기되었고, 이 시기에 퇴적물로 용출된 인이 식물플랑크톤 성장에 이용될 수 있기때문에 퇴적물에 대한 관리도 수행될 필요가 있다

• 수산해양교육연구
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• 제27권1호
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• pp.98-107
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• 2015

넙치 육에 혼합야채류(양파, 샐러리, 당근, 마늘)를 넣고 잘 혼합한 후, 혼합부재료(빵가루, 계란, 타임분, 블랑소스, 생크림, 소금, 후추)를 첨가하여 잘 버무린 반죽을 성형하는 등의 공정을 거친 후 넙치 steak 제품을 제조하였다. 최종 제품 Steak-1(성형된 육을 올리브유를 두른 프라이팬에서 2분간 구운 후 폴리에틸렌 필름에 넣어 진공포장하여 7일간 동결 저장한 것을 전자레인지로 해동 및 데우는 공정을 거친 제품)과 Steak-2(성형된 육을 폴리에틸렌 필름에 넣어 진공포장하여 7일간 동결 저장한 것을 해동 후 올리브유를 두른 프라이팬에서 2분간 구운 제품)에 대하여 각각 이화학적 성질과 관능적 평가를 살펴보았다. Steak-1 및 Steak-2 두 제품 모두에서 생균수가 검출되지 않았으며, 일반성분의 경우 수분(69.0% 및 69.2%), 조단백질(21.9% 및 21.4%) 및 조회분(1.9% 및 1.8%)은 함량 차이가 거의 없었으나, 조지방(5.3% 및 7.8%)은 Steak-2 제품의 값이 높았다. TBA 값의 경우는 Steak-1(0.110)에 비해 Steak-2(0.069)의 값이 낮았으며, 아미노질소 함량은 Steak-1이 0.20 mg/100 g, Steak-2가 0.25 mg/100 g 으로 차이가 거의 없었다. Steak-1 및 Steak-2 두 제품의 색차의 경우 명도(L값)는 각각 45.55 및 46.11, 적색도(a값)는 각각 1.20 및 1.78, 황색도(b값)는 각각 8.52 및 9.59 그리고 색차(${\Delta}E$값)는 51.35 및 52.09로 차이는 거의 없었다. 조직감의 경우 Steak-1 보다 Steak-2의 조직감이 더 단단하였다. Steak-1 및 Steak-2의 유리아미노산은 arginine 함량이 가장 많았고, 다음이 glutamic acid, alanine 및 lysine 순이었다. 총유리아미노산 함량은 Steak-1이 346.4 mg/100 g, Steak-2가 240.5 mg/100 g이었다. 관능검사 결과 Steak-2가 Steak-1 보다 관능평가 점수가 높게 나왔으나 큰 기호도의 차이는 없었다는 것이 관능검사요원들의 지배적 의견이었다. 따라서 넙치 steak를 제조하여 판매할 경우 굽기공정 까지 완료하여 단가가 높은 제품을 구입할 것인지 단가는 낮지만 최종공정인 굽기공정을 가정에서 수행해야 하는 제품의 선택은 소비자의 판단에 맡기는 것이 바람직하다고 판단되었다.

• 한국광물학회지
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• 제15권2호
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• pp.85-94
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• 2002

한반도 동남부 일대에 발견된 제4기 단층인 상천, 입실, 왕산단층 비 지대에서 단층운동과 이에 수반된 유체의 영향으로 생긴 미구조 및 광물학적인 변화 양상을 알아보기 위해 단층 비지와 주위 모암의 전암분석과 전자현미분석이 수행되었다. 단층 비지와 주위 모암의 X-선형광분석 결과 유동성이 낮은 원소 즉 $TiO_2$, MgO, $P_2$$O_{5}$ , $Fe_2$$O_3$가 신선한 모암에 비해 비지대에 집적되는데 이는 단층운동과 이에 수반된 유체들의 활동이 활발했음을 이야기 해준다. 단층 비지 물질의 X-선회절분석 결과 관찰되는 광물은 석영, 장석, 방해석과 점토광물이고, 점토광물은 대부분 스멕타이트이며 (060) 회절선의 값은 평균 1.50 $\AA$으로써 이팔면체 구조를 가진다. 전자현미분석 결과 비지대 및 모암내 다양한 종류의 황화, 탄산염 및 인산염광물들이 관찰된다. 상천단층 회색 비지대의 제노타임, 입실단층 접촉부 안산암과 왕산단층 접촉부 회색 안산암의 황화광물은 제4기 이전의 단층운동과 관련된 열수의 유입으로 인해 생성된 것으로 추측 된다. 입실 접촉부 안산암과 비지대의 맥상의 탄산염광물은 제4기 이전의 단층운동과 관련된 유체에 의해 생성되었고, 이들 탄산염광물이 물리적으로 심하게 파쇄되어 있으며 탄산염광물 가장자리에 반응연이 있는 것으로 보아 탄산염광물이 생성되고 난 후에도 단층운동과 유체의 활동이 활발했음을 알 수 있다. 왕산단층의 맥상의 방해석은 제4기 단층운동과 동시기 또는 후기에 생성된 것으로 볼 수 있다.>${\mu}c$-Si:H의 Ea 가 가장 낮은 것을 관찰 할 수 있었다.s derived by combining the numerous rainfall-runoff data. The conclusions are as follows; 1)The oscillations in the derived unit hydrograph are reduced by combining the data from each flood event. 2) The reciprocals of the minimum eigen\value of XTX, 1/k and the condition number CN are increased when the oscillations are active in the derived unit hydrograph. 3)The parameter estimates are validated by extending the model to the Soyang river Dam site with elimination of the autocorrelation in the disturbances. Finally, this paper illustrates the application of the multiple regression model to drive an optimal unit hydrograph dealing with the multicollinearity and the autocorrelation which cause some problems. 우선적으로 고려하여 사용할 농약을 선택해야 할 것으로 보이나, 그 외 약제의 잔류성, 사용량, 사용시기와 함께