• Title/Summary/Keyword: Na2S.9H2O

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An experimental study of heat transfer with $Na_4P_2O_7{\cdot}10H_2O$ as P.C.M. ($Na_4P_2O_7{\cdot}10H_2O$의 축열방열시 열전달 특성에 관한 실험적 연구)

  • Lee, C.M.;Yim, C.S.
    • Solar Energy
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    • v.9 no.1
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    • pp.70-77
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    • 1989
  • Sodium pyrophosphate that melting point is $79-80^{\circ}C$ have been Studied on heat storage and heat discharge. In heat storage process, sodium pyrophosphate was kept up initial temperature $50^{\circ}C,\;60^{\circ}C,\;70^{\circ}C$ which melt by heated water at temperature $85^{\circ}C,\;90^{\circ}C,\;95^{\circ}C$. In heat discharge process, initial temperature of sodium pyrophosphate was maintained at temperature $85^{\circ}C,\;90^{\circ}C,\;95^{\circ}C$ which varied cooling temperature $50^{\circ}C,\;60^{\circ}C,\;70^{\circ}C$. The experiment has been reached conclusions as follows. 1) Heat transfer properties of phase change material is controlled by conduction during heating and cooling process. 2) The temperature increased rapidly at initial stage and transient region increase slowly because of characteristic of latent heat. 3) The lower cooling water temperature is the less the time that get to thermal equivalent state take during discharge process. 4) The higher cooling water temperature is the less temperature difference between top and bottom in P.C.M during discharge process.

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An Analysis of Long-term Trends in Precipitation Acidity of Seoul, Korea (서울지역 강수 산성도의 장기적인 경향분석)

  • 강공언;임재현;김희강
    • Journal of Korean Society for Atmospheric Environment
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    • v.13 no.1
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    • pp.9-18
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    • 1997
  • Precipitation samples were collected by the wet- only event sampling method from Seoul during September 1991 to April 1995. These samples were analyzed for the concentrations of the major ionic components (N $O_3$$^{[-10]}$ , N $O_2$$^{[-10]}$ , S $O_4$$^{2-}$, C $l^{[-10]}$ , $F^{[-10]}$ , N $a^{+}$, $K^{+}$, $Ca^{2+}$, $Mg^{2+}$, and N $H_4$$^{+}$), pH, and electric conductivity. During the study period, a total of 182 samples were collected, but only 163 samples were used for the data analysis via quality assurance of precipitation chemistry data. The volume-weighted pH was found to be 4.7. The major acidifying species from our precipitation studies were identified to be non-seasalt sulfate (84$\pm$9 $\mu$eq/L) and nitrate (24$\pm$2 $\mu$eq/L) except for chloride. Because the Cl/Na ratio in the precipitation was close to the ratio in seawater. If all of the non-seasalt sulfate and nitrate were in the form of sulfuric and nitric acids, the mean pH in the precipitation could have been as low as 3.7 lower than the computed value. Consequently, the difference between two pH values indicate that the acidity of precipitation was neutralized by alkaline species. The equivalent concentration ratio of sulfate to nitrate was 3.5, indicating that sulfuric and nitric acids can comprise 78% and 22% of the precipitation acidity, respectively. Analysis of temporal trend in the measured acidity and ionic components were also performed using the linear regression method. The precipitation acidity generally showed a significantly decreasing trend, which was compatible with the pattern of the ratio (N $H_4$$^{+}$+C $a^{2+}$)/ (nss-S $O_4$$^{2-}$+N $O_3$$^{[-10]}$ ).).

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Removal of Chlorine from Fly Ash in Municipal Solid Waste Incineration Ash by Water Washing (수세에 의한 생활폐기물 소각재 중 비산재로부터 염소성분의 제거)

  • 안지환;한기천;김형석
    • Resources Recycling
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    • v.10 no.5
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    • pp.36-43
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    • 2001
  • The chlorine component in fly ash from municipal solid waste incineration ash was removed by water washing for the purpose of recycling fly ash as a raw material of ordinary portland cement. The samples were a different kind of 리y ashes using $Ca(OH)_2$and NaOH as media of wet scrubber for flue gas cleaning. The content of soluble salts of fly ash using $Ca(OH)_2$and NaOH was 32.8%, 50.1% and the content of chlorine component, 22.9% and 26.0% respectively, which was KCl, NaCl, CaC1OH mainly. When each fly ash was washed using water under conditions of a agitation speed of 300 rpm, a liquid to solid ratio of 10, most soluble salts in fly ash were dissolved within 30 minutes and the content of chlorine component in ash was diminished to the content of 4.4%, 2.O% at $20^{\circ}C$ and 1.7%, 0.8% at $50^{\circ}C$ respectively. And the main compound of residual chlorine component in ash after water washing was friedel`s salt ($3CaO.A1_2$$O_3$.$CaCl_2$.$10H2$O). From analysis results of water quality for wastewater by water washing, the components exceeding discharged wastewater standard were only Pb and Cd. But As pH was controlled to 10 with addition of $CO_2$(g) or $Na_2$$_CO3$in water, the concentration of heavy metals such as Pb and Cd was also under discharged wastewater standard.

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Synthesis of Sulfonated Poly(phenylene sulfide) via Soluble Precursor and its Ammonia Gas Adsorption (용해성 전구체를 통한 Sulfonated Poly(phenylene sulfide)의 합성과 암모니아가스 흡착)

  • Son, Won Keun;Kim, Hyun Suk;Park, Soo Gil
    • Applied Chemistry for Engineering
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    • v.10 no.5
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    • pp.666-671
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    • 1999
  • In this work, sulfonated poly(phenylene sulfide) (SPPS) was prepared by demethylation with aqueous NaOH solution after poly[methyl[4-(phenylthio)phenyl]sulfonium trifluoromethanesulfonate](PPST) was sulfonated with fumic sulfonic acid(10% $SO_{3}-H_{2}SO_{4}$). PPST soluble in organic solvents was synthesiszed by self-condensation polymerization of methyl-(phenylthio)phenyl sulfoxide(MPPSO). SPPS showed IR bands of asymmetric O=S=O stretching at $1200cm^{-1}$ and S-O stretching at $621cm^{-1}$ from $-SO_{3}H$ group. From the result, it could be known that sulfonic acid groups were introduced to poly(phenylene sulfide). when PPST was sulfonated for 12hr at $150^{\circ}C$, 1.48 sulfonic acid groups were introduced per repeat unit. The weight average molecular weight(Mw) of PPST and SPPS determined by high temperature GPC were 118323 and 131204, respectively. The SPPS exhibited adsorption capacity of ammonia gas $9.67mmol\;NH_{3}/g$ and it was much higher than that of active carbon or silica gel.

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Volatiles Composition from Aerial Parts of the Insect-Pollinated and the Promising Medicinal Plant Spiraea hypericifolia L. Growing Wild in Northern Kazakhstan

  • Kirillov, Vitaliy;Stikhareva, Tamara;Atazhanova, Gayane;Ercisli, Sezai;Makubayeva, Aigerim;Krekova, Yana;Rakhimzhanov, Alimzhan;Adekenov, Sergazy
    • Natural Product Sciences
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    • v.27 no.1
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    • pp.36-44
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    • 2021
  • The essential oils from the aerial parts (leaves and flowers) of Spiraea hypericifolia L. (Rosaceae), collected in Northern Kazakhstan, were obtained by distillation in two dispersion media (distilled water and 15% NaCl solution). The chemical composition of the essential oils was evaluated by GC-MS for the first time. The yield of the essential oil was 0.04% (in fresh growth conditions) and 0.02% (in dry growth conditions) respectively regardless of which dispersion media (H2O or 15% NaCl solution) was used at the isolation of essential oil. The main compounds were aliphatic hydrocarbons (alkanes) (40.6-53.2%), aldehydes (8.4-17.4%), diterpenoids (9.1-16.7%) and ketones (6.2-8.7%). Content of monoterpenoids was depended on dispersion media (2.2-3.6% where H2O was dispersion media and 8.4-8.5% where 15% NaCl solution was dispersion media). n-Heneicosane (17.4-34.1%) and n-tricosane (14.3-19.5%) were the main constituents of the essential oil of S. hypericifolia. There were many insects from different classes in S. hypericifolia at flowering. Important components such as α-methylene-γ-butyrolactone (0.8-2.8%), benzyl cyanide (0.7-1.1%), β-damascenone (1.2-2.9%), (E,E)-4,8,12-trimethyl-1,3,7,11-tridecatetraene (1.8-2.7%), β-ionone (0.5-1.8%) and others were detected in small amounts.

Recovery of Phosphorus in Animal Wastewater by Struvite Forming (Struvite 형성에 의한 축산폐수의 인 회수기술 개발)

  • Oh, I.H.;Lee, J.H.;Choi, B.H.;Myung, N.S.;Burns, R.T.
    • Journal of Biosystems Engineering
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    • v.31 no.1 s.114
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    • pp.46-51
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    • 2006
  • This study was carried out to recover phosphorus in animal wastewater using a magnesium source. $MgCl_2$, as a magnesium source, was shown a SP (soluble phosphorus) recovery rate of 98% in both the aeration and the NaOH tests to adjust pH around 8.5. In case of MgO, the recovery rate of SP were 88% with the aeration and 58% with the NaOH. In case of ammonia nitrogen recovery, $MgCl_2$ was shown the recovery rate of 17% with aeration and 18% with NaOH. MgO was shown the ammonia recovery rate of 18% with aeration and 11% with NaOH. At low temperature of $6-8^{\circ}C$ with the animal wastewater from piglet stall, the recovery rate of SP was shown 95% with NaOH and 92% with aeration using $MgCl_2$. The recovery rate of ammonia nitrogen was shown 9% with NaOH and 12% with aeration, respectively. It was observed that the pH can be raised by aeration. The reaction was completed within 5 minutes and the struvite cristal structure was formed and could be observed with an electronic microscope.

Fluid Inclusion and Stable Isotope Studies of Mesothermal Gold Vein Deposits in Metamorphic Rocks of Central Sobaegsan Massif, Korea: Youngdong Area (소백산 육괴 중부 지역의 변성암에서 산출되는 중온형 금광상에 대한 유체 포유물 및 안정동위원소 연구. 영동지역)

  • Chip-Sup So
    • Economic and Environmental Geology
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    • v.32 no.6
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    • pp.561-573
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    • 1999
  • Mesothermal gold deposits of the Heungdeok, Daewon and Ilsaeng mines in the Youngdong area occur in fault shear zones in Precambrian metamorphic rocks of central Sobaegsan Massif, Korea, and formed in single stage of massive quartz veins (0.3 to 3 m thick). Ore mineralogy is simple, consisting dominantly of pyrrhotite, sphalerite and galena with subordinate pyrite, chalcopyrite, electrum, tetrahedrite and native bismuth. Fluid inclusion data indicate that hydrothermal mineralization occurred at high temperatures (>240$^{\circ}$ to 400$^{\circ}$C) from $H_{2}O-CO_{2}(-CH_{4})$-NaCI fluids with salinities less than 12 wt. % equiv. NaC!. Fluid inclusions in vein quartz comprise two main types. These are, in decreasing order of abundance, type I (aqueous liquid-rich) and type II (carbonic). Volumetric proportion of the carbonic phase in type II inclusions varies widely in a single quartz grain. Estimated $CH_4$ contents in the carbonic phase of type II inclusions are 2 to 20 mole %. Relationship between homogenization temperature and salinity of fluid inclusions suggests a complex history of fluid evolution, comprising the early fluid's unmixing accompanying $CO_2$ effervescence and later cooling. Estimated pressures of vein filling are at least 2 kbars. The ore mineralization formed from a magmatic fluid with the ${\delta}^{34}S_{{\Sigma}S}$, ${\delta}^{18}O_{water}$ and ${\delta}D_{water}$ values of -2.1 to 2.2$\textperthousand$, 4.7 to 9.3$\textperthousand$ and -63 to -79$\textperthousand$, respectively. This study validates the application of a magmatic model for the genesis of mesothermal gold deposits in Youngdong area.

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An X-ray Diffraction Study of Na, Ag-A Reduced by Hydrogen. Ag$_3\;^+$and Ag$_3\;^{2+}$ Clusters

  • Kim, Yang;Seff, Karl
    • Bulletin of the Korean Chemical Society
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    • v.5 no.4
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    • pp.135-140
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    • 1984
  • The reduction of vacuum-dehydrated $Na_xAg_{12-x}-A, 0 {\le} x {\le} 9.2$, and its reoxidation by O$_2$, have been studied by X-ray powder diffraction. Also, the structure of $Na_6Na_6-A$ treated with hydrogen at room temperature has been studied by single crystal methods in the cubic space group Pm3m at $24{\circ}C (a = 12.221(2) {\AA})$. The diffraction pattern of dehydrated Ag$_{12}$-A reduced by H$_2$ contains only the (111) and (200) reflections of silver metal, indicationg that the zeolite structure has been lost, but the zeolite's diffraction pattern and structural integrity can be fully restored by oxidation with O$_2$ at 100 or 200${\circ}C$. In contrast, the structures of $Na_xAg_{12-x}-A$, x = 4.5 and 9.2, were not destroyed by treatment with hydrogen. Dehydrated Na$_6Ag_6$-A treated with 50 Torr of hydrogen gas at 24${\circ}C$ for 30 minutes has $6\; Na^+\;and\;1.27\;Ag^+$ ions at 6-ring sites. These $Ag^+ ions are associated with 2.54 Ag${\circ}$ atoms to form 1.27 $Ag_3^+$ clusters per unit cell. Also found were 0.7 $Ag_3^{2+}$ clusters per unit cell near the 8-rings. The structure was refined to the final error indices R$_1$ = 0.134 and R$_2$ (weighted) = 0.147, using 168 independent reflections for which $I_0 >3{\sigma}(I_0)$.

The Study of Nano-texturing Process for Crystalline Silicon Solar Cell Using Ag Catalyst Layer (결정질 실리콘 태양전지의 Ag 촉매층을 이용한 나노 텍스쳐링 공정에 관한 연구)

  • Oh, Byoung-Jin;Yeo, In-Hwan;Kim, Min-Young;Lim, Dong-Gun
    • Journal of the Korean Institute of Electrical and Electronic Material Engineers
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    • v.25 no.1
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    • pp.58-61
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    • 2012
  • In our report a relatively simple process for fast nano-texturing of p-type(100) CZ- silicon surface using silver catalyzed wet chemical etching in aqueous hydrofluoric acid (HF) and hydrogen peroxide solution($H_2O_2$) at room temperature. The wafers were saw-damaged by NaOH(6 wt%) at $60^{\circ}C$ for 150s. To obtain a nano-structured black surface, a thin layer of silver with thickness of 1 - 10 nm was deposited on the surfaces by evaporation system. After this process the samples were etched in HF : $H_2O_2$ : $H_2O$ = 1:5:10 at room temperature for 80s - 220s. Due to the local catalytic of the Ag clusters, this treatment results in the nano-scale texturing on the surface. This resulted in average reflectance values less than 9% after the silver on the surface of the wafers were removed.

Growth characteristics of pathogens isolated from surface of carcass (도체표면에서 분리한 병원성 미생물의 성장특성)

  • 정영숙;박나영;이신호
    • Food Science and Preservation
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    • v.9 no.4
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    • pp.434-440
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    • 2002
  • The growth characteristics of 5. coli O157:H7 CDFI, A. sobria CDF3 and S. aureus CDF2 isolated from surface of carcass were investigated to improve hygienic quality of beef. The total count of carcass surface before washing was higher than that of after washing. Total count of after cooling decreased about 10$^1$∼ 10$^2$/㎠ compare with before cooling. Total count of carcass surface after transfer increased regardless seasons. The growth E. coli O157:H7 CDF1 occurred at pH 4 and 6% NaCl but A. sobria CDF3 and S. aureus CDF2 did not grow at the same conditions. Although the growth of E. coli O157:H7 CDF1 and S. aureus CDF2 was inhibited by 0.3% lactic acid, but A sobria CDF3 did not grow in TSB containing 0.3% lactic acid. E. coli O157:H7 CDF1 grew rapidly after 3 days incubation at 10$\^{C}$ but did not grow at 4$\^{C}$. But A. sobria CDF3 grew rapidly after 3 days incubation at 4$\^{C}$. E. coli O157:H7 CDF1 and A. sobria CDF3 were destroyed by heat treatment for 3 min at 60$\^{C}$. S. aureus CDF2 did not detect after heat treatment for 2 min at 70$\^{C}$.