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The Study about Pulmonary Function in the last period Pregnancy (임신 말기 임산부의 호흡패턴에 관한 연구)

  • Chae, Jung-Byung;Park, Rae-Joon;Bae, Ji-Hye;Kim, Gwang-Ho;Shin, Sung-Hee;Lee, Hwa-Jin;Lee, Hee-Jeung;Lim, Mi-Jung;Jang, Eun-Jung
    • The Journal of Korean Physical Therapy
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    • v.17 no.4
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    • pp.613-620
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    • 2005
  • Tests of ventilatory function including pulmonary diffusing capacity were made in 18, the last period pregnant women and 20 non pregnant women. During the study was from May 22 to June 4, the subject of study refered 38 women (20 student and the staff of Physical Therapy at Masan college and 18 women who were examined at Masan OO obstetrics Hospital). All the studied subjects had no clinical abnormalities of the cardiorespiratory system. Mean FVC and FEV1.0 were significantly decreased in the last pregnant women compare with that of non pregnant women. All the Other Measurements were not differ from those of non pregnant women. The results of this study were as follows. l. Pregnancy was associated with decrease in mean FVC and FEVl.0, Which at the last period pregnant women were $2.70{\pm}0.58{\iota},\;2.31{\pm}0.53{\iota}$ below the non pregnant women mean $3.03{\pm}0.33,\;2.64{\pm}0.44{\iota}$ : Both changes were statistically significant.(P<0.05) 2. The mean VC, which at the last period pregnant women was $3.15{\pm}0.45{\iota}$ below the non pregnant women mean $3.28{\pm}0.33{\iota}$ and the mean IC $2.21{\pm}0.53{\iota}$ below the non pregnant women mean $2.22{\pm}0.54{\iota}$, but the difference were not statistically significant. 3. The mean ERV, IRV were not statistically significant between non pregnant women and pregnant women. 4. The mean TV were not statistically significant between non pregnant women and pregnant women. 5. The mean FEVl.0(G) were not statistically significant between non pregnant women and pregnant women.

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Effect of Zinc Bioaccumulation on Survival Rate, Activity, Growth and Organ Structure of the Equilateral Venus, Gomphina veneriformis (Bivalvia: Veneridae) (아연의 체내축적이 대복의 생존, 운동성, 성장 및 기관계 구조에 미치는 영향)

  • Ju Sun-Mi;Lee Jae-Woo;Jin Young-Guk;Yu Jun;Lee Jung-Sick
    • Environmental Analysis Health and Toxicology
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    • v.21 no.2 s.53
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    • pp.115-126
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    • 2006
  • This study was conducted to find out survival rate, activity, growth and change of the organ structure of bivalves exposed to heavy metal. The results of the study confirmed that zinc (Zn) induces reduction of survival rate and activity, abnormality of organ structure of the equilateral venus, Gomphina veneriformis. Experimental groups were composed of one control condition and three Zn exposure conditions ($0.64mg\;Zn{\iota}^{1},\;1.07mg\;Zn{\iota}^{-1},\;1.79mg\;Zn{\iota}^{-1}$). As the concentration of zinc increased the accumulation of lipofucin increased in the digestive gland. Survival rate was the lowest in the lowest Zn exposure group at $0.64mg;Zn{\iota}^{-1}$. Growth was not significantly different between the control and exposure group. Activity. with the exception of the lowest Zn exposure group at $0.64mg\;Zn{\iota}^{-1}$, was similar between the control and exposure group. Histological analysis of organ system illustrated expansion of hemolymph sinus, loss of striated border of inner epidermis, increase in the number of mucous cell in the mantle. Also, histological degenerations as epithelial necrosis and hyperplasia of mucous cells are recognized in the gill and foot.

Comparison of Salinity and Composting Efficiency by Washing before and after Aerobic Composting of Food Wastes (음식물쓰레기의 호기성 퇴비화 전과 후의 세척에 따른 염분도와 퇴비화효율 비교)

  • Park Seok Hwan
    • Journal of Environmental Health Sciences
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    • v.31 no.2 s.83
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    • pp.160-164
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    • 2005
  • This study was performed to evaluate the effects of washing food wastes before aerobic composting on temperature, pH and salinity, and the effects of washing after composting on salinity of sample mixtures. Weight ratios of food wastes to water in washing were 1:0(Control), 1:1(W-1), 1:2(W-2), 1:3(W-3) and 1:0(N-4), respectively. Ratios of food wastes to wood chips in reactor of Control, W-1, W-2, W-3 and N-1 were $5\;kg:0\iota,\;5\;kg:5\iota,\;5\;kg:5\iota,\;5\;kg:5\iota\;and\;5\;kg:5\iota$, respectively. Reactors were operated for 24 days with 1 hour stirring by 1 rpm and 2 hours of forced aeration per day. The increase in the ratio of water to food wastes resulted in the increase of the maximum reaction temperature and the shortening of the high temperature reaction period. The increase in the ratio of water to food wastes also resulted in faster reaching to the lowest pH and then to the steady state of pH 9.0. The final salinities of Control, N-1, W-1, W-2 and W-3 were $1.04\%,\;0.92\%,\;0.78\%,\;0.64\%\;and\;0.53\%$, respectively. The salinities of the N-l samples which were washed by the weight ratios (water:N-l) of 1:1, 2:1 and 3:1 after composting were $0.72\%,\;0.61\%\;and\;0.51\%$, respectively. Therefore, washing food wastes before aerobic composting is more efficient method than that after aerobic composting.

THERMAL CONDUCTION IN MAGNETIZED TURBULENT GAS

  • CHO JUNGYEON;LAZARIAN A.
    • Journal of The Korean Astronomical Society
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    • v.37 no.5
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    • pp.557-562
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    • 2004
  • We discuss diffusion of particles in turbulent flows. In hydrodynamic turbulence, it is well known that distance between two particles imbedded in a turbulent flow exhibits a random walk behavior. The corresponding diffusion coefficient is ${\~}$ ${\upsilon}_{inj}{\iota}_{turb}$, where ${\upsilon}_{inj}$ is the amplitude of the turbulent velocity and ${\iota}_{turb}$ is the scale of the turbulent motions. It Is not clear whether or not we can use a similar expression for magnetohydrodynamic turbulence. However, numerical simulations show that mixing motions perpendicular to the local magnetic field are, up to high degree, hydrodynamical. This suggests that turbulent heat transport in magnetized turbulent fluid should be similar to that in non-magnetized one, which should have a diffusion coefficient ${\upsilon}_{inj}{\iota}_{turb}$. We review numerical simulations that support this conclusion. The application of this idea to thermal conductivity in clusters of galaxies shows that this mechanism may dominate the diffusion of heat and may be efficient enough to prevent cooling flow formation when turbulence is vigorous.

HEIGHT BOUND AND PREPERIODIC POINTS FOR JOINTLY REGULAR FAMILIES OF RATIONAL MAPS

  • Lee, Chong-Gyu
    • Journal of the Korean Mathematical Society
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    • v.48 no.6
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    • pp.1171-1187
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    • 2011
  • Silverman [14] proved a height inequality for a jointly regular family of rational maps and the author [10] improved it for a jointly regular pair. In this paper, we provide the same improvement for a jointly regular family: let h : ${\mathbb{P}}_{\mathbb{Q}}^n{\rightarrow}{{\mathbb{R}}$ be the logarithmic absolute height on the projective space, let r(f) be the D-ratio of a rational map f which is de ned in [10] and let {$f_1,{\ldots},f_k|f_l:\mathbb{A}^n{\rightarrow}\mathbb{A}^n$} bbe finite set of polynomial maps which is defined over a number field K. If the intersection of the indeterminacy loci of $f_1,{\ldots},f_k$ is empty, then there is a constant C such that $ \sum\limits_{l=1}^k\frac{1}{def\;f_\iota}h(f_\iota(P))>(1+\frac{1}{r})f(P)-C$ for all $P{\in}\mathbb{A}^n$ where r= $max_{\iota=1},{\ldots},k(r(f_l))$.

GENERALIZED QUADRATIC MAPPINGS IN 2d VARIABLES

  • Cho, Yeol Je;Lee, Sang Han;Park, Choonkil
    • Korean Journal of Mathematics
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    • v.19 no.1
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    • pp.17-24
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    • 2011
  • Let X, Y be vector spaces. It is shown that if an even mapping $f:X{\rightarrow}Y$ satisfies f(0) = 0, and $$2(_{2d-2}C_{d-1}-_{2d-2}C_d)f\({\sum_{j=1}^{2d}}x_j\)+{\sum_{{\iota}(j)=0,1,{{\small\sum}_{j=1}^{2d}}{\iota}(j)=d}}\;f\({\sum_{j=1}^{2d}}(-1)^{{\iota}(j)}x_j\)=2(_{2d-1}C_d+_{2d-2}C_{d-1}-_{2d-2}C_d){\sum_{j=1}^{2d}}f(x_j)$$ for all $x_1$, ${\cdots}$, $x_{2d}{\in}X$, then the even mapping $f:X{\rightarrow}Y$ is quadratic. Furthermore, we prove the Hyers-Ulam stability of the above functional equation in Banach spaces.

CLPP of Biofilm in Free Chlorine Residual and Monochloramine (유리잔류염소와 모노클로라민에서의 생물막의 CLPP)

  • Lee Dong-Geun
    • Journal of Environmental Health Sciences
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    • v.31 no.2 s.83
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    • pp.147-151
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    • 2005
  • The disinfection effect of free residual chlorine and monochloramine on biofilm communities were investigated by CLPP (community level physiology profile) using Biolog GN plates. Low concentration of disinfectant, $0.5\;mg/\iota$ free chlorine and $1.0\;mg/\iota$ monochloramine, stimulated the growth of bacteria rather than disinfection. Bacterial concentrations were decreased at more than $1.0\;mg/\iota$ of disinfectants. CLPP was different with the type and concentration of disinfectant and sampling time. Common and different carbon sources were actively used with similar bacterial concentration in free chlorine and monochloramine. This represents the differences of bacterial communities with tap water contact times and disinfectant.

HEARING OF RAINBOW TROUT TO COMMERCIAL SIZE IN A INDOOR AQUARIUM (실내수조를 이용한 무지개송어의 사육실험)

  • KIM In-Bae;JO Jae-Yoon
    • Korean Journal of Fisheries and Aquatic Sciences
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    • v.11 no.4
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    • pp.233-238
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    • 1978
  • Rainbow trout were reared in a stainless steel aquarium from Nov. 11, 1977 to June 12, 1978, and the following results were obtained : 1. The volume of water was about $400\iota$ in a aquarium measuring $1m\;(Length)\times1m\;(Width)\times67cm(Height)$ and water depth 40 cm. Water was supplied for about 16 hours daily at a rate $3\iota/min$ and was drained through the conical settling part in the middle of the aquarium bottom. Filter tank was about $23cm(W)\times23cm(L)\times40cm(D)$ and contained pebbles 30 cm in depth. Water recirculation rate was at)out $1,030\iota/hr$, or 2.6 turn-over per hour. 2. During the first period (77 days), the trout grew from 88.3g to 229g in average, the total weight attaining 30.7kg. The food coefficient was 1.249, average daily increment 243.3g, average daily growth rate 1.245%, and the mortality was 2 smallest fish weighing 53 g, owing to unknown reason. During the second period (135 days), the trout grew from 239g to 555g in average, the total weight attaining 57.2 kg. The food coefficient was 1.447, average daily increment 279.8g, average daily growth rate $0.65\%$ and the mortality was 31 fish weighing 11,255 g, owing partly to miss-handling and partly to disease. 3. The feed consisting of fully domestic materials was prepared in this laboratory, and the feed conversion was not inferior to high protein commercial feed available in foreign countries. 4. The result of whole period for 212 days was 56.5 kg in gross increment, and based on this result, when $1\iota/min$ full day inflowing water available, the net production will become 28.25 kg. So, if a 5000kg production is planned, $180\iota/min$ or about $10.8m^3/hr$ be reauired, and the production in value frill become 15million won at local price at the expense of about 5.3 million won. From the result of this experiment, rainbow trout is feasible for commercial production in Korea with relatively small amount of well water and simplified water recirculation system.

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The Excavating Performance of Jet Steram for the Ground (분사류의 저질에 대한 굴삭성능에 관한 연구)

  • KIM Cheol-Ho;KO Kwan-Soh
    • Korean Journal of Fisheries and Aquatic Sciences
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    • v.22 no.4
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    • pp.201-213
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    • 1989
  • This study is just to be carried out to grasp the efficiency of jet stream excavating for the ground. Changing the dynamic pressure, nozzle diameter, distance off the ground, we measured the impulse, the excavated depth, the excavated width. According as each dynamic pressure increases from 100 to $500gf/cm^2$, the impulse of the jet stream increases from 43 to 114gf, from 52 to 227gf, from 114 to 506gf, from 137 to 768gf, in 4, 6, 8, 10mm nozzles respectively, but it makes no difference in the value of distance within 50cm off ground. The excavated depth increases at the invariable rate in accordance with nozzle diameter, dynamic pressure, nozzle distance. We obtain the equations relevant to the ground I, II as follows: $$L_I=[0.01(H/r-100) -0.43\cdot\iota+11.78]{\cdot}D/4$$ $$L_{II}=[0.03(H/r-100) -0.34\cdot\iota+6.39]{\cdot}D/4$$ where, $L_I,\;L_{II}$ are respectively the excavated depths of the ground I, II, cm; H is the dynamic pressure, $gf/cm^2\;:\;\iota$ is the distance off the ground, cm; D is Nozzle diameter, mm; r is the specific weight, $1gf/cm^2$.

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