• Title/Summary/Keyword: 비산율

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Droplets Splash Related with a Wall Impingement of Liquid Jet (액체 분무의 벽면 충돌분무에 의한 액적 비산)

  • KIM, Young-Il
    • Journal of the Korean Society of Industry Convergence
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    • v.7 no.1
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    • pp.5-11
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    • 2004
  • 벽면에 충돌하는 액체 분무의 충돌 거동과 액적 비산에 관하여 실험을 통하여 조사하였다. 액체 분무는 홀노즐에 의해 직경 40mm의 충돌판에 분사하게 된다. 액체 분무는 반경방향으로 퍼져나가 5개의 영역으로 분류되어 나타내게 된다. 난류 혹은 층류 분무의 경우, 충돌판에 충돌한 후 두꺼운 액막을 형성하게 되며, 이러한 상태에서 충돌하는 분무의 비산량은 매우 적으며 충돌 거리에 영향을 받지 않는다. 한편, 파동이 있는 분무의 충돌은 수력도약(Hydraulic jump)과 함께 반경방향으로 엷은 액막을 형성하게 되며 비산율도 증가하게 된다. 액체분무의 초속도가 증가하면 비산율도 증가하게 된다. 분열이 일어난 후에 충돌하는 파동 분무의 비산율은 분열이 일어나기 전에 비해 약 2~3배 정도 크게 나타난다. 비산율은 웨버수(Weber number)를 이용하여 요약할 수가 있다.

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RADIAL FLOW AND DROPLETS SPLASH OBSERVED ON A WALL IMPINGEMENT JET (벽면 충돌분무의 반경방향 흐름과 액적 비산에 관한 고찰)

  • KIM, Young-Il
    • Journal of the Korean Society of Industry Convergence
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    • v.3 no.1
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    • pp.37-42
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    • 2000
  • 액체 분무가 벽면의 평평한 면에 충돌할 때의 거동에 대해 실험을 통하여 조사하였다. 각 분사노즐과 벽면까지의 거리 그리고 분사 속도에 있어서 충돌점에서의 액체 액막의 비산 거동과 평면에서의 액막의 흐름에 대하여 관찰하였다. 충돌점에서 비산하는 액적의 비산율을 정량적으로 측정하였다. 분사속도가 증가에 의해 충돌 거동은 5개의 영역으로 분류되며, 분사속도가 증가하면 비산율도 증가하게 된다. 또한, 충돌거리가 분무의 분열점보다 길때의 분사량의 약 반 정도가 비산하게 되는 결과가 얻어졌다.

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A Study on the Sound Absorption Characteristic of Glass Wool Structures Covered by Punched Steel Plate (유공함석판으로 보호된 글라스울 흡음구조체의 흡음특성에 관한 연구)

  • 김석홍;이상엽;권형오
    • Proceedings of the Korean Society for Noise and Vibration Engineering Conference
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    • 1991.04a
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    • pp.65-69
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    • 1991
  • 소음제어대책 수립시, 흡음구조는 공조용소음기, 공업용소음기, Enclosure, 실 내 흡음판등에 폭넓게 이용되고 있다. 흡음구조의 재료중 글라스울은 뛰어난 흡음성능과 고온에서의 내구성 및 난연성등으로 인하여 여러 흡음재료중에 서 가장 많이 이용되고 있으나 글라스율 미립자의 비산 및 강도문제로 글라 스율에 글라스 클로스(Glass Cloth), P.E.Film등과 같은 글라스울 비산방지막 과 유공함석판을 붙인 흡음구조체로 제작하여 이용하는 것이 일반적이다. 국 내외적으로 글라스울만의 흡음율 데이타는 각종 문헌등에 많이 발표되어 있 으나 글라스울에 글라스울 비산방지막과 유공함석판을 붙인 흡음구조체의 흡음율데이타는 거의 없는 실정이다. 본 연구에서는 이러한 글라스울 흡음구 조체의 글라스울의 밀도, 글라스울 비산방지막의 종류, 유공함석판의 유공치 수 등에 따른 흡음특성을 잔향실법 흡음율측정방법에 의해 측정 평가하고 이들을 상호 비교검토하여 각종 소음 제어대책의 기초 설계자료로 제시하고 자 한다.

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Removal of Unburned-Carbon from Fly-Ash of Bituminous Coal by Froth Flotation (포말부유선광법에 의한 유연탄 비산회의 미연탄소분 제거연구)

  • Son, Sung-Geun;Kim, Jung-Duk;Park, Byung-Wook
    • Resources Recycling
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    • v.5 no.3
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    • pp.44-49
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    • 1996
  • One of the most serious problems in utilizing the fly-ash produced from damcstic coal-firing power plants is lhc unburned-carbon mntained m the fly-ash In this shldy, the effects of fruther and collector an the yield,recuvery,unburnedcarbon rejectiou peiccntage,and process efficiency of product (cleaned fly-ash) wcrc examined when convzntional froth flotation was applied to rejcct the unburned-carbon included in the fly-ash of bituminous coal Alsa,the ash analysis for both thc raw and the clcaned fly-ash was conducted to review the change in thc major elements of fly-ash. Experimental results shawcd lhat tlle rcjectlon oI the unburned-cubon of thc raw fly-ash sample is available upto 92.4% using fiath flotalian and that the putity ol the pmdud(c1eancd fly-ash) attains up to 99.4%.

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Characterization of Granular Fertilizer Produced by Fly Ash from a Sewage Sludge Incinerator (하수슬러지 소각 비산재를 이용한 입상비료 조립 및 특성분석)

  • Kim, Seong-beom;Lee, Wontae
    • Journal of Korean Society of Environmental Engineers
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    • v.38 no.10
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    • pp.574-579
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    • 2016
  • This study assessed feasibility of making granular fertilizer with fly ash from a sewage sludge incinerator in Korea. Composition, characteristics, strength, and heavy metal contents of the granular fertilizers were investigated. Due to its high contents of phosphorus, fly ash from a sewage sludge incinerator could be used to make fertilizers. Granulation rates (2-4 mm granules) over 80% could be achieved as the fly ash contents were 15% or less of the fertilizer. Leaching tests of the fertilizers, based upon the Korean Standard Methods for Solid Wastes, showed the concentrations of heavy metals less than the risk limits. However, contents analysis of the fertilizers, based upon the Korean Standard Methods for Soils, experienced higher levels of heavy metals than the risk limits as the fly ash content exceeded 7% of the fertilizer. Thus, the fly ash needs to be added less than 7% of the fertilizer if there is no pretreatment to remove heavy metals.

Solidification of municipal solid waste incineration fly ash by hauyne clinker (Hauyne 클링커에 의한 생활폐기물 소각 비산재의 고화 특성)

  • Han, Gi-Chun;You, Kwang-Suk;Um, Nam-Il;Cho, Kye-Hong;Cho, Hee-Chan;Ahn, Ji-Whan
    • Proceedings of the Korean Institute of Resources Recycling Conference
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    • 2005.10a
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    • pp.355-359
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    • 2005
  • 본 연구에서는 OPC 및 hauyne 클링커의 비산재에 대한 고화특성을 검토하였다. 비산재에 대해 OPC 및 OPC에 hauyne 클링커를 20%까지 대체하였을 때의 압축강도, 길이변화율, 중금속 용출량 등을 조사하였다. 결과로서, hauyne 클링커의 첨가량에 따라 고화체의 압축 강도가 증가하였다. hauyne 클링커의 첨가량은 10%내외가 적합하였으며, 그 이상에서는 길이변화율이 증가하며 팽창하였다. 고화체의 중금속 용출시험결과 모든 배합조건에서 환경기준치이하의 값을 나타내었다.

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A Basic Study on the Effective Management for MSWI Fly Ash (II) - Effect of Leaching Parameter - (소각 비산재의 적정처리를 위한 기초연구(II) - 용출인자의 영향 -)

  • Kim, Jin-Beom;Lee, Woo-Keun;Shim, Yeong-Ju
    • Journal of Korean Society of Environmental Engineers
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    • v.22 no.7
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    • pp.1357-1364
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    • 2000
  • Our study was performed to evaluate the effect of leaching parameters including the physicochemical characteristics and the fractionated composition of heavy metals on the release of heavy metals in fly ash discharged from MSWI. Leaching parameters such as pH, CEC, particle size, and exchangeable fraction among the fractional composition classified by sequential extraction procedure are considered. The leaching rate of heavy metal released by KSLT method is largely dependent on the pH of fly ash. The effect of pH on the release of heavy metals is different from elements. It appears that the leaching rate of cadmium and copper decreases with increasing pH, while lead and zinc increases at the condition of neutral or strong alkali condition, which suggests that the leaching of heavy metals are limited by the solubility. It is found that the effect of CEC is similarly to that of pH, $D_{10}$ among the particle size of fly ash is negative correlated with the concentration of heavy metals leached by KSLT method. In the case of exchangeable fraction, the leaching rate of heavy metals is linearly correlated with the exchangeable fraction for the fly ash below 40 meq/l00g of CEC, but not related out of the range.

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Dissemination of Conidiospores of Colletotrichum gloeosporioides, the Anthracnose of Persimmon and the Disease Development (감나무 탄저병균 Colletotrichum gloeosporioides의 분생포자 비산과 농가 포장에서 탄저병의 발생과정)

  • Kwon, Jin-Hyeuk;Park, Chang-Seuk
    • Research in Plant Disease
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    • v.10 no.4
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    • pp.272-278
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    • 2004
  • The disease development of Anthracnose of sweet persimmon in relation to release of conida of Colletotrichum gloeosporioides were observed in a farmer's field located in Jinju from 1998 to 2002. The conidia started to release from early April and reached maximum in June to late July. The amount of conidia production reduced drastically from early August. The number of conidia trapped was closely related to amount of precipitation at the same period and number of new infections on the emerging branches and young fruits in orchard. The conidia released during the April was not effected to disease occurrence of persimmon tree but the spores produced from inoculum source after early May significantly important to the infection of the pathogen on emerging branch and this infection was directly related to infections on young fruits. Consequently the early infections on the branches brought severe occurrence of Anthracnose in the orchard. Most of the infected fruits were dropped in unripe state. The earlier infection caused the earlier fruit drop. The rate of fruit drop was reached up to 84.1% in August when the disease was occurred severely. Anthracnose of sweet persimmon also occurred in market shelf and storage warehouse. The anthracnose fruits are presumed to be infected while in orchard. Because the symptom formed on the fruit was too tiny to eliminate, the infected fruits were involved in storage boxes and anthracnose gradually developed in storage condition. The rate of diseased fruit observed in Jinju area were 1.2 to 1.6%.

The Combustion Safety of Waste CCA Treated Wood (폐 CCA처리재의 소각처리)

  • Son Dong-won;Lee Dong-heub;Lee Hyun-mi;Lee Myung-je
    • Journal of Korea Foresty Energy
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    • v.23 no.2
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    • pp.29-33
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    • 2004
  • This study was carried out to find out safety disposal methods of waste CCA treated wood. The heavy metals of remnant were analyzed after combustion of CCA treated wood at different temperatures. Arsenic volatilized temperature was detected. The removal rate of heavy metals by acid in the ash were examined. Through this study, we could conclude that in order to protect volatilize arsenic, combustion of CCA treated wood should be do under the $300^{\circ}C$. But when CCA treated wood combustion under $300^{\circ}C$, it's weight-loss rate was $55\%$, so land reclamation dependence will be increased. When CCA treated wood combustion at high temperature, the land reclamation dependence could be reduced, but the arsenic that volatilize into the atmosphere should be captured. When it bums with high temperature, the ash contains lots of copper and chromium, so removal of heavy metals should be conducted.

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Formation and Characteristics of Aerobic Granular Sludge Using Polymer in Sequencing Batch Reactor (연속회분식 장치에서 응집제를 이용한 호기성 입상슬러지 생성 및 특성)

  • Lee, Bong-Seob;Choi, Seong-Woo
    • Journal of Korean Society of Environmental Engineers
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    • v.31 no.12
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    • pp.1143-1150
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    • 2009
  • This study was carried out to investigate of aerobic granulation by using sequencing batch reactor(SBR). To make aerobic granular sludge in short period of time, we used polymer. In case of SBR, we have studied on physicochemical characteristics of particle size, settling velocity, surface charge, and specific oxygen utilization rate(SOUR) depending on aerobic particle's formation. The results of running SBR with $5.4kg{\cdot}COD/m^3{\cdot}d$ of COD loading rate and 20 days reaction time showed that aerobic particle size, settling velocity, SOUR, surface charge, polysaccharide/protein(PS/PN) ratio were 2.6 mm, 1.7 cm/s, $346mg{\cdot}O_2/g{\cdot}MLVSS{\cdot}hr,\;(-)0.26{\cdot}meq/g{\cdot}MLVSS$, and 2.06 mg/mg respectively.