• 제목/요약/키워드: $SO_4^{2-}$

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불산석고-고로슬래그계의 수화반응 (Hydration in the System of Fluorogypsum-Blast Furnace Slag)

  • 송종택;고상열;노재성
    • 한국세라믹학회지
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    • 제35권9호
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    • pp.933-938
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    • 1998
  • The hydration for the system of fluorogypsum and 20wt% blast furnace slag was investigated at liquid/soild ratio of 0.45 for 1, 3, and 7 days by using 3 kinds of accelerators such as K2SO4 Al2(SO4)3 $.$16-18H2O and AlK(SO4)2$.$12H2O After curing the hardened specimen was characterized by the compressive strength the content of combined water XRD, DTA and SEM It was found that the activating effect was increased in the order of K2SO4

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$Li_2SO_4-Na_2SO_4$ 용융염에 의한 $Pb(Mg_{1/3}Nb_{2/3})O_3$의 합성 (Synthesis of $Pb(Mg_{1/3}Nb_{2/3})O_3$ by $Li_2SO_4-Na_2SO_4$ Molten Salts)

  • 윤기현;조용수;남윤우;강동헌
    • 한국세라믹학회지
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    • 제30권7호
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    • pp.543-548
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    • 1993
  • Stability and formation of Pb(Mg1/3Nb2/3)O3 (PMN) phase synthesized in Li2SO4-Na2SO4 molten salts have been investigated. And powder characteristics of PMN have been studied with a variation of processing parameters such as temperature, time, amount of the salts, and excess PbO. More ratio of Li2SO4 to Na2SO4 influences the percentage of perovskite phase due to the difference of the eutectic point of the salts, but does not influence the powder characteristics. The shape of PMN particles shows faceted morphology with bimodal distribution consisting with large and submicron parts. Particle size of PMN increased greatly with increasing soaking time or amount of salts rather than temperature. The addition of excess PbO resulted in round PMN crystallites without submicron particles. These results are discussed by XRD, SEM and thermal analyses.

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$3CaO.SiO_2$ 생성반응과 미세조직에 있어서 Alkali Oxide와 $SO_3$의 상호작용 (Interaction of Alkali Oxide and $SO_3$ on $3CaO.SiO_2$ Formation and Microstructure)

  • 정해문;최상흘
    • 한국세라믹학회지
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    • 제30권12호
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    • pp.1071-1079
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    • 1993
  • Interaction of alkali oxides and SO3 and C3S formation and microstructure was studied using K2CO3 and Na2CO3 as alkali sources and (NH4)2SO4 for SO3. When SO3/K2O=1.43 as mole ratio, K2O and SO3 react to form K2SO4, this phase is immiscible with other oxide melt and thus could not affect C3S formation as well as its microstructure. In a condition of SO3/K2O 1, C3S crystals were round and grown in a much larger size. With addition of Na2O and SO3 by only 1wt% each, C3S formation was strongly hindered. Since C2S was stabilized by Na+ and SO4-2, it could not react to give C3S formation. However in the condition of SO3/Na2O=1.43, a little amount of C3S was formed. It is considered that small amount of Na2SO4 was formed, this phase was immiscible with clinker liquid, and the C3S crystals were formed locally in the liquid part of relatively low Na2O and SO3 compositions. These crystals had irregular and rough surfaces and contained more inclusions than those grown from K2O.SO3 system.

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강화도 지역에서 겨울철 $PM_{205}$의 화학적 성분 특성 (Characteristics of Chemical Species in $PM_{205}$ during the Winter in Kangwha)

  • 여현구
    • 한국대기환경학회지
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    • 제16권4호
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    • pp.309-316
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    • 2000
  • Chemical compositions of air pollutants with fine particles (<2.5 ${\mu}{\textrm}{m}$, PB2.5) were evaluated at background site. Kangwha. in Korea during the winter season. The data set was obtained for seventeed days with 24-hour sampling from December 11 to 16, 1996 and from January 9 to 1997. The chemical species have been measured {{{{ {SO }`_{4 } ^{2- } }}}}, {{{{ { NO}`_{3 } ^{- } }}}}, {{{{ { NH}`_{4 } ^{+ } }}}}. OC and EC in the particulate phase, NH3 HNO3, HCl and SO2 in the gas phase using the three stage filter pack method. Mean concentration ($\mu\textrm{g}$/m3) of this study were : 35.42 for PM2.5 8.78 for organic carbon (OC) 7.25 for nss {{{{ {SO }`_{4 } ^{2- } }}}}, 4.94 for {{{{ { NO}`_{3 } ^{- } }}}}, 3.58 for {{{{ { NH}`_{4 } ^{+ } }}}} and 1.48 for elemental carbon (EC) respectively. Contributive rates of major particulate components in PM2.5 were OC (25%) nss- {{{{ {SO }`_{4 } ^{2- } }}}}(20%) ,{{{{ { NO}`_{3 } ^{- } }}}}(14%) {{{{ { NH}`_{4 } ^{+ } }}}}(10%) and EC (4%) respectively and these components could be accounted for 73% of PM2.5 mass. Reactive forms of {{{{ { NH}`_{4 } ^{+ } }}}} were considered as NH4HO3 and NH4{{{{ {SO }`_{4 } ^{2- } }}}} during the sampling periods. {{{{ { NO}`_{3 } ^{- } }}}}/({{{{ { NO}`_{3 } ^{- } }}}} + HNO3) and {{{{ {SO }`_{4 } ^{2- } }}}}/({{{{ {SO }`_{4 } ^{2- } }}}} + SO2) were calculated 0.8 and 0.9 respectively. Most of these compounds might be formed in partiiculate phase in the air. Correlation coefficient between OC and EC was 0.866 which might have the same sources during the sampling periods,.

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당근 종자 발아 촉진에 관한 연구 (3) 당근 종자의 발아에 있어서 몇가지 무기염류의 영향 (Studies on the Acceleration of Germination in Carrot Seed (3) Effect of some Inorganic Compounds on the Germination of Carrot Seed)

  • 권오용
    • Journal of Plant Biology
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    • 제14권2호
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    • pp.1-6
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    • 1971
  • When germination beds of carrot seeds were treated with either 0.01M or 0.05M concentrations of Ca(NO3)2, CaSO4, MgSO4, K2SO4 and KH2PO4, an acceleration in the germination rate was observed in the groups treated with 0.01M KH2PO4 and 0.05M MgSO4 and 0.05M Ca(NO2)3. In earlier work by the author with acetone a similar result was observed and reported. The pH range in these experiments was maintained between 5.0 and 6.0. It was found that the groups treated with 0.05M K2SO4, 0.05M Ca(NO3)2, 0.05M Ca(NO3)2, 0.05M MgSO4, 0.01M KH2PO4, 0.01M Ca(NO3)2 germinated earlier than the control group. The acceleration of the germintion rate varied with the inorganic compounds used in the following descending order; 0.01M KH2PO4, 0.05M Ca(NO3)2, 0.05M K2SO4, 0.05M CaSO4 and 0.05M KH2PO4. As a result of these expriments, it occurs to the author that in the germination of carrot seeds some inorganic compounds appear to activate the osmotic function of carrot seeds causing acceleration in the germination rate.

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SCP 생산용 메탄올 자화균주의 연속배양에 의한 배지 최적화 (The Medium Optimization through Continuous Culture of an Methanol Utilizing Bacterium for SCP Production)

  • 김창호;김태진홍석인
    • KSBB Journal
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    • 제5권4호
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    • pp.355-363
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    • 1990
  • 서울 인근의 생활하수에서 메탄올을 이용하는 박테리아를 분리하였다. 이의 최적 성장을 위한 온도 및 pH는 각각 $33^{\circ}C$ 및 7.1이었다. 최대비성장율은 $0.42hr^{-1}$을 나타내었다. 최소 배지조성은 기본배지의 양을 안정상테에서 연속발효법으로 구하였으며, 그 조성은 다음과 같다(g / l); Methanol 40, $(NH_4)_2\;SO_42,\;KH_2PO_4\;1.5,\;K_2HPO_4\;0.2,\;H_3PO_4\;0.79,\;Na_2HPO_4{\cdot}12H_2O\;0.15,\;MgSO_4{\cdot}7H_2O\;1.5,\;FeSO_4{\cdot}7H_2O\;0.034,\;MnSO_4{\cdot}4H_2O\;0.005,\;CuSO_4{\cdot}5H_2O\;0.0027,\;CaCl_2{\cdot}2H_2O\;0.25,\;ZnSO_4{\cdot}7H_2O\;0.007,\;(NH_4)_6\;Mo_7O_{24}{\cdot}4H_2O\;0.00048,\;H_3BO_3\;0.00068,\;CoCl_2\; 0.00024$ 최적 배지 조건에서 구한 최대 세포생산성은 3.8g / l / hr였으며, 이때의 회석율은 $0.23hr^{-1}$이었다. 최대 세포농도와 그대의 단백질의 함량은 각각 19.5g / l 및 70%였으며, 이때의 회석율은 $0.1hr^{-1}$이었다.

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하소(?燒) 명반석(明礬石)에 의(依)한 고로수쇄(高爐水碎)슬래그의 활성화(活性化) 특성(特性) (Activation Property of Blast Furnace Slag by Calcined Alunite)

  • 김형석;조영도;안지환;목촌방부;한춘
    • 자원리싸이클링
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    • 제15권4호
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    • pp.27-35
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    • 2006
  • 본 연구에서는 명반석 $[K_{2}SO_{4}{\cdot}Al_{2}(SO_{4})_{3}{\cdot}4Al(OH)_{3}]$을 고로수쇄슬래그의 활성화제로서 활용하기 위하여 하소 명반석과 고로수쇄슬래그의 수화반응 특성을 연구하였다. $650{\circ}C$에서 하소시킨 명반석은 $KAl(SO_{4})_{2}$$Al_{2}O_{3}$로 구성되어 있으며 하소 명반석-소석회-석고 계에서 하소 명반석은 소석회 및 석고와 $2KAl(SO_{4})_{2}+2Al_{2}O_{3}+13Ca(OH)_{2}+5CaSO_{4}{\cdot}2H_{2}O+73H_{2}O{\rightarrow}3(3CaO{\cdot}Al_{2}O_{3}{\cdot}3CaSO_{4}{\cdot}32H_{2}O)+2KOH$와 같이 반응하여 ettringite($3CaO{\cdot}Al_{2}O_{3}{\cdot}3CaSO_{4}{\cdot}32H_{2}O)$를 형성한다. 하소 명반석-고로수쇄슬래그 계에서는 하소 명반석에서 용해된 황산이온($SO_{4}^{2-}$)이 소석회와 반응하여 석고를 형성시키고, 석고는 다시 고로수쇄슬래그와 반응하여 ettringite를 형성시키면서 슬래그의 수화반응을 촉진시키기 때문에 하소 명반석을 고로수쇄슬래그의 활성화제로 사용할 수 있다.

알칼리 활성화 결합재 모르타르의 황산염 침식 저항성에 미치는 마그네슘 및 황산 이온의 영향 (Effects of Magnesium and Sulfate Ions on the Sulfate Attack Resistance of Alkali-activated Materials)

  • 박광민;조영근;신동철
    • 콘크리트학회논문집
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    • 제29권4호
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    • pp.415-424
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    • 2017
  • 본 연구의 목적은 플라이애시 및 고로슬래그 미분말로 제조한 알칼리 활성화 결합재 모르타르의 황산염 저항성에 미치는 마그네슘(Magnesium, $Mg^{2+}$) 및 황산(Sulfate, ${SO_4}^{2-}$) 이온의 영향을 확인하는 것이다. 이를 위하여 고로슬래그 미분말 치환율을 30%, 50% 및 100%, $SiO_2$$Na_2O$의 몰 비($SiO_2/Na_2O$ molar ratio, Ms)를 1.0, 1.5 및 2.0으로 조정한 시험체를 제작하였다. 그리고 $Mg^{2+}$${SO_4}^{2-}$의 영향을 확인하기 위하여 $Mg^{2+}$ 단독(10% $Mg(NO_3)_2$), ${SO_4}^{2-}$ 단독(10% $Na_2SO_4$), $Mg^{2+}$${SO_4}^{2-}$ 복합(10% [$MgCl_2+Na_2SO_4$], 10% [$Mg(NO_3)_2+Na_2SO_4$]) 및 $MgSO_4$ 수용액(10%, 5% 및 2.5% $MgSO_4$)의 조건에서 압축강도, 길이변화, 질량변화 및 X선 회절 분석을 실시하였다. 그 결과, $Mg^{2+}$${SO_4}^{2-}$가 공존하는 경우에만 황산염 침식에 의한 강도저하 및 팽창 등이 발생하는 것을 확인하였다. 이러한 현상은 $Mg^{2+}$이 규산칼슘 수화물(Calcium Silicate Hydrate, C-S-H)을 분해하여 $Ca^{2+}$이 용출되고, 용출된 $Ca^{2+}$${SO_4}^{2-}$가 결합하여 석고($CaSO_4{\cdot}2H_2O$, Gypsum)를 생성하고, $Mg^{2+}$과 OH가 결합하여 수산화마그네슘(Magnesium hydroxide, $Mg(OH)_2$, Brucite)을 생성하는 것에 기인하는 것을 확인하였다.

과량의 $SO_3$가 존재할 때 $3CaO.SiO_2$의 생성 저하 메카니즘 (Mechanism of $3CaO.SiO_2$ Prevention in Presence of Excess $SO_3$)

  • 정해문;한기성;최상흘
    • 한국세라믹학회지
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    • 제30권7호
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    • pp.527-534
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    • 1993
  • The phenomena that excess sulfate hindred the C3S formation in the presence of clinker liquid phase were investigated. In the case of (NH4)2SO4, assuming SO3 atmospheric condition, sulfate stabilized C2S and was enriched at the surface of C2S grains, so C2S was prevented from being dissolved into clinker melt. CaSO4 showed the similar aspect with (NH4)2SO4, however, the prevention of C3S formation by CaSO4 took more influence that C2AS and C4A3 were formed below 100$0^{\circ}C$, and remained upto clinkering temperature, 145$0^{\circ}C$, thus these intermediate phases caught CaO which would participate the C3S formation.

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3CaO.3A12O3.CaSO4.CaSO4.2H2O - Ca(OH)24 - 3CaO.Al2O3계의 수화 특성 (Hydration Properties of 3CaO.3A12O3.CaSO4.CaSO4ㆍ2H2O - Ca(OH)24 - 3CaO.Al2O3 System)

  • 배승훈;송종택
    • 한국세라믹학회지
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    • 제40권9호
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    • pp.859-866
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    • 2003
  • 칼슘설포알루미네이트계 팽창시멘트는 수화하여 ettringite, monosulfate 등의 수화물을 생성하여 경화체의 수축을 보삼함으로써, 균열 발생을 방지한다. 본 실험에서는 칼슘설포알루미네이트계 팽창시멘트의 수화특성을 규명하기 위하여 화학성법으로 3CaO.$3A1_2$$O_3$.$CaSO_4$($C_4$$A_3$S)을 제조하였으며, $C_4$$A_3$S-Ca(OH)$_2$-CaSO$_4$.2$H_2O$-C$_3$A계의 수화특성을 알아보았다. 화학성법에 의해 $1300^{\circ}C$에서 잘 발달한 $C_4$$A_3$S를 제조할 수 있었고, $C_4$A$_3$S-Ca(OH)$_2$-CaSO$_4$.2$H_{2}O$계의 주요수화 생성물은 ettringite이었으며, $C_4$A$_3$S-Ca(OH)$_2$-CaSO$_4$.$2H_2O$-C$_3$A는 수화초기에 ettringe를 생성하였다가 석고가 소비되면서 monosulfate로 전이하였다.