• 제목/요약/키워드: flowing amount

검색결과 210건 처리시간 0.023초

하천의 유황에 관한 수문학적 연구 (A Hydrological Study on the Flow Characteristic of the Keum River)

  • 박성우
    • 한국농공학회지
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    • 제16권2호
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    • pp.3438-3453
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    • 1974
  • Unmeasured value of water for human lives is widely approved, but the water as one of natural resources cannot be evaluated with ease since it changes itself ceaselessly by flowing-out or transforming the phase. Major objectives of the study concerned consequently with investigating its potentiality and evaluating its time seriesly availabity in a volumatic unit. And the study was performed to give the accurate original data to the planners concerned. Some developed rational methods of predicting runoff related to hydrological factors as precipitation, were to be discusseed for their theorical background and to be introduced whether they needed some corrections or not, comparing their estimation with actual runoff from synthetic unit-hydrograph methods. To do so, the study was performed to select Kongju Station, located at the watershed of the Keum River, and to collect such hydrological data from 1962 to 1972 as runoff, water level, precipitation, and so on. On the other hand, the hydrological characteristics of runoff were concluded more reasonably in numerical values, with calculating the the ratio of daily runoff to annual discharge of the flow in percentage, as. the distribution ratio of runoff. The results of the study can be summarized as follows; (1) There needed some consideration to apply the Kajiyama's Formula for predicting monthly runoff of rivers in Korea.(2) The rational methods of predicting runoff might be recommended to become less theorical and reliable than the unique analyzation of data concerned in each given water basin. The results from the Keum River prepared above would be available to any programms concerned. (3) The most accurate estimation for runoff could be suggested to synthetic unithydrograph methods calculated from the relation between each storm and runoff. However it was not contained in the study. (4) The relations between rainfall and runoff at KongJu Station were as following table. The table showed some intersting implications about the characteristics of runoff at site, which indicated that the runoff during three months from July to September approached total of 60% of quantity while precipitation concentrated on the other three from June to August. And there were some months which had more amount of runoff than expected values calculated from the precipitation, such as Febrary, March, August, September, Octover, and December, shown in the table. Such implications should be suggested to meet any correction factors in the future formulation concerned with the subjects, if any rational methods would be required.

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저수위시 노출된 저수지 저니 상의 식생과 구리(Cu)의 흡수 (Absorption of Copper(Cu) by Vegetation on Reservoir Sediment Exposed after Drawdown)

  • 이충우;차영일
    • 한국환경과학회지
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    • 제2권2호
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    • pp.123-133
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    • 1993
  • Shingal reservoir is a relatively small (211ha) and shallow impoundment, and approximately 25 ha of its sediment is exposed after spring drawdown. At least 14 vascular p13n1 species germinate on the exposed sediment, but Persimria vulgaris Webb et Moq. quickly dominates the vegetation. In order to estimate the role of the vegetation in the dynamics of heavy metal pollutants in the reservoir, Cu concentration of water, fallout particles, exposed sediment, and tissues of p. vulgaris, Ivas analyzed. Cu content in reservoir water decreased from $13.10mg/m^2$ on May 15 (before dralvdown) to $3.08mg/m^2$ in June 1 (after drawdown), mainly due to the loiwering of water level. Average atmospheric deposition of Cu by fallout particles was $10.84 {\mu}g/m^2/day$. Cu content in the surface 15cm of exposed sediment decreased from $5.094g1m^2$ right after drawdown, to $0.530g/m^2$ in 41 days, which is a 89.6% decrease. Therefore up to 99.7% of Cu in the reservoir appears to exist in the sediment. only 0.3% in water If the rate of atmospheric Input by fallout particles is assumed to have been the same since 1958, when the reservoir was completed, cumulative input of Cu during the 38 years would have been $150.35mg/m^2$, which is only 3.0% of Cu content in sediment right after drawdown. Therefore, most of Cu in the Shingal reservoir must have been transported by the Shingal-chun flowing into the reservoir, Standing crop of vegetation on the exposed sediment 41 days after drawdown was $730.67g/m^2$, of which 630.91g/m2 was p. vulgaris alone, and Cu content in P vulgaris at this time was $6.612mg/m^2$. This was only 0.13% of Cu in the exposed sediment, but was 50.5% of Cu in water before drawdown, or 167% of the average annual input of Cu by atmospheric deposition. If other plants were assumed to absorb Cu to the same concentration as p. vulgaris, total amount of Cu absorbed in 41 days by vegetation on the exposed sediment is estimated to be 1913.3 g, which is a considerable contribution to the purification of the reservoir water.

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저수위시 노출된 저수지 저니 상의 식생과 구리(Cu)의 흡수 (Absorption of Copper(Cu) by Vegetation on Reservoir Sediment Exposed after Drawdown)

  • 이충우;차영일
    • 한국환경과학회지
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    • 제2권2호
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    • pp.29-29
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    • 1993
  • Shingal reservoir is a relatively small (211ha) and shallow impoundment, and approximately 25 ha of its sediment is exposed after spring drawdown. At least 14 vascular p13n1 species germinate on the exposed sediment, but Persimria vulgaris Webb et Moq. quickly dominates the vegetation. In order to estimate the role of the vegetation in the dynamics of heavy metal pollutants in the reservoir, Cu concentration of water, fallout particles, exposed sediment, and tissues of p. vulgaris, Ivas analyzed. Cu content in reservoir water decreased from $13.10mg/m^2$ on May 15 (before dralvdown) to $3.08mg/m^2$ in June 1 (after drawdown), mainly due to the loiwering of water level. Average atmospheric deposition of Cu by fallout particles was $10.84 {\mu}g/m^2/day$. Cu content in the surface 15cm of exposed sediment decreased from $5.094g1m^2$ right after drawdown, to $0.530g/m^2$ in 41 days, which is a 89.6% decrease. Therefore up to 99.7% of Cu in the reservoir appears to exist in the sediment. only 0.3% in water If the rate of atmospheric Input by fallout particles is assumed to have been the same since 1958, when the reservoir was completed, cumulative input of Cu during the 38 years would have been $150.35mg/m^2$, which is only 3.0% of Cu content in sediment right after drawdown. Therefore, most of Cu in the Shingal reservoir must have been transported by the Shingal-chun flowing into the reservoir, Standing crop of vegetation on the exposed sediment 41 days after drawdown was $730.67g/m^2$, of which 630.91g/m2 was p. vulgaris alone, and Cu content in P vulgaris at this time was $6.612mg/m^2$. This was only 0.13% of Cu in the exposed sediment, but was 50.5% of Cu in water before drawdown, or 167% of the average annual input of Cu by atmospheric deposition. If other plants were assumed to absorb Cu to the same concentration as p. vulgaris, total amount of Cu absorbed in 41 days by vegetation on the exposed sediment is estimated to be 1913.3 g, which is a considerable contribution to the purification of the reservoir water.

유해가스 흡수처리를 위한 저비용 고효율 스크러버의 최적 설계기준 및 현장적용 방안 (Optimal Design Standard and Application of Low Cost, High Performance Scrubber for Absorbing Hazardous Gas)

  • 정가영;임경민;마병철
    • 한국가스학회지
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    • 제25권3호
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    • pp.39-45
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    • 2021
  • 사업장에서 유해가스를 처리하는 스크러버는 처리효율은 높으나 설계가 복잡하고 24시간 펌프를 가동시켜야 하므로 많은 비용이 소모될 수 있다. 따라서, 영세한 사업장에서는 스크러버를 설치하지 않거나 순환펌프의 작동을 중지한 상태로 스크러버를 운용하여 운영비를 최소화하고 있다. 이에, 본 연구에서는 소규모 사업장에서 경제적으로 활용할 수 있는 저비용 고효율 스크러버에 대한 적용방안을 연구하였다. 저비용 고효율 스크러버는 bubble column의 방식을 적용하여 유해화학물질 흡수처리 목적으로 장치를 활용하는 것으로, 이러한 스크러버의 개발을 위하여 실험을 통해 흡수성능을 검토하였으며 특정 조건에서 물리적 조건 변화에 따른 유해가스 흡수효율 변화 및 최적의 적용방안을 연구하였다. 그 결과, 저비용 고효율 스크러버로 유입되는 기체를 어느 정도 처리할 수는 있었으나 처리능력이 저하되는 문제가 발생하여 흡수액 공급을 통해 성능저하를 방지하고 순환량에 따라 일정 수준의 흡수율을 유지할 수 있는 것을 확인할 수 있었다. 이를 기반으로 최종적으로는 적정 순환시점 및 동결 방지방안을 포함한 저비용 고효율 스크러버의 현장 적용방안을 3가지 방식(type)으로 제시하였다.

알긴산 비드에 혼합된 해파리 면역 반응물질 함량에 따른 중금속 흡착효율 평가에 관한 연구 (A Study on the Evaluation of the Adsorption Efficiency of Heavy Metals by the Content of Jellyfish Extract at Immunity Reaction in Alginate bead)

  • 김종환;박혁진;최인호;김은진;최이송;오종민
    • 환경영향평가
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    • 제32권6호
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    • pp.431-436
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    • 2023
  • 산업이 발전함에 따라 생태계로 유입되는 중금속의 양이 증가하고 있다. 중금속은 분해가 어려워 생태계 내에 장기간 잔류하고 독성을 유발한다. 이러한 중금속은 수처리 시 흡착, 여과, 화학적 침전 등 물리 화학적 방법으로 제거된다. 본 연구에서는 중금속 흡착 및 제거용 킬레이트 수지로 알긴산 비드를 선정하고 이에 따른 중금속 흡착효율을 평가하기 위하여 JEI (Jellyfish extract at immunity reaction)를 혼합하였다. JEI를 혼합한 비드는 알지네이트의 특성에 따라 납(79-99%)과 구리(64-70%)에서 높은 흡착효율을 보였으며 카드뮴(25-37%)과 아연(5-6%)에서 낮은 흡착효율을 나타내었다. 중금속 흡착은 JEI의 함량에 비례하여 증가하지 않았으나 50%와 100% JEI 비드가 유의미한 증가를 나타내었다. 반응 속도식을 적용한 결과 유사 1차 반응식보다 유사 2차 반응식에 더 적합한 것으로 나타났다. 결론적으로 비드의 생산 단가나 중금속 흡착제거 효율을 비교해보면 50% JEI 비드가 중금속 흡착제거에 적합한 것으로 사료된다.

탈질 설비의 성능 개선을 위한 CFD 기법 적용에 관한 연구 (Application of CFD Methods to Improve Performance of Denitrification Facility)

  • 김민규;정희택
    • 청정기술
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    • 제29권4호
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    • pp.305-312
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    • 2023
  • 환경 요구 조건의 강화로 오래된 탈질 설비에 대한 성능 개선이 필요하다. 본 연구에서는 전산 해석 기법을 이용하여 성능 향상의 가능성을 제시하고자 하였다. 입구 안내 깃과 곡확산부 등 설비 내 유로의 기하학적인 형상의 수정과 암모니아 분사량의 제어 등 설계와 운전 조건을 둘 다 변경하여 해석을 수행하였다. 촉매 층에 유입되는 혼합가스의 유동 균일성과 NH3/NO 조성비, 설비의 압력 강하 등 3가지 성능변수 관점에서 기존에 운영되는 조건과 본 연구에서 제시된 조건을 비교하였다. 전산 해석에서 적용된 유동장의 범위는 연소로 절탄기의 출구에서 공기 예열기의 입구까지로 탈질 설비의 전 영역이다. 전산 해석 도구로 열유체 전용 소프트웨어인 ANSYS-Fluent를 사용하여 유동 특성을 해석하여 성능을 도출하였고 최적화 알고리즘인 Design Xplorer를 사용하여 암모니아의 분사량을 노즐별로 조절하였다. 변경된 설비 조건은 기존의 조건과 비교하여 유동 균일성과 NH3/NO 조성비는 각각 45.1%와 8.7% 향상되었으나 전체 압력 강하는 1.24% 증가하였다.

온수 지중가온이 참외의 근권환경 및 생육에 미치는 영향 (Effect of Root Zone Warming by Hot Water on Rhizosphere Environment and Growth of Greenhouse- grown Oriental Melon (Cucumis melo L.))

  • 신용습;이우승;도한우;배수곤;최성국
    • 생물환경조절학회지
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    • 제6권2호
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    • pp.103-109
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    • 1997
  • 참외 금싸라기은천을 신토좌 대목에 호접하여 저온기 참외 시설재배시 지중가온의 효과를 구명하고자, 비닐 하우스내에 온수보일러를 설치하여 지하 35cm 부위에 15mm 엑셀파이프를 180cm 이랑에 2열 매설한 후, 지하 20cm의 최저 지온을 17$^{\circ}C$, 21$^{\circ}C$$25^{\circ}C$로 설정하고 1월 18일부터 4월 18일까지 일정하게 유지 관리하여 무가온구와 비교 시험한 결과는 다음과 같다. 1. 지중가온에 의한 정식 후 1개월간의 지중 20cm 부위의 적산온도는 무가온구가 441$^{\circ}C$, 17$^{\circ}C$구는 558$^{\circ}C$, 21$^{\circ}C$구는 648$^{\circ}C$ 그리고 $25^{\circ}C$구는 735$^{\circ}C$였다. 2. 지중가온에 따른 터널내 보온효과는 지온이 높을수록 높았는데 2월 5일 무가온구의 터널내 야간 최저 기온은 9.5$^{\circ}C$인데 비하여 17$^{\circ}C$구에서는 11.$0^{\circ}C$, 21$^{\circ}C$구에서는 13.5$^{\circ}C$ 그리고 $25^{\circ}C$구에서는 16.5$^{\circ}C$였다. 3. 정식 30일까지의 초기생육은 지온이 높을수록 초장, 경경, 엽수 및 엽면적이 증가하였으며 특히 고지온구에서 엽면적의 증가가 뚜렷하였다. 정식 30일 후 무가온구의 엽면적 279.5$\textrm{cm}^2$에 비하여 17$^{\circ}C$구에서는 153.4%, 21$^{\circ}C$구에서는 745.6a 그리고 $25^{\circ}C$구에서는 879.4% 정도 증가하였다. 4. 정식 30일 후 지제부를 절단하여 24시간 동안 채취한 목부일비액량은 무가온구의 8.1$m\ell$에 비해 17$^{\circ}C$구에서는 1.2배, 21$^{\circ}C$구에서는 1.3배 그리고 $25^{\circ}C$구에서는 4.8배 많았으나 정식 67일 후에는 무가온구의 10.4$m\ell$에 비해 각각 1.1배, 3.2배 및 3.3배 많았다.

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암모니아의 재생 및 농축을 위한 금속 전구체에 따른 금속 첨착 활성탄의 흡착 및 탈착 특성에 관한 연구 (A Study on the Adsorption and Desorption Characteristics of Metal-Impregnated Activated Carbons with Metal Precursors for the Regeneration and Concentration of Ammonia)

  • 조광희;박지혜;;윤형철;이광복
    • 청정기술
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    • 제26권2호
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    • pp.137-144
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    • 2020
  • 저농도 암모니아의 재생 및 농축을 위하여 초음파 함침법으로 금속 첨착 활성탄을 제조하였다. 금속으로는 마그네슘과 구리를 선정하였고, 염화물(Cl-)과 질산염(NO3-) 전구체를 사용하여 활성탄 표면에 첨착하였다. 흡착제의 물리 및 화학적 특성은 TGA, BET 그리고 NH3-TPD를 통해 분석되었다. 암모니아 파과실험은 고정층 반응기를 사용하여 암모니아(1000 mg L-1 NH3, balanced N2)를 100 mL min-1으로 주입하였으며, 온도변동 흡착법(TSA)과 압력변동 흡착법(PSA, 0.3, 0.5, 0.7, 0.9 Mpa)에서 수행하였다. 암모니아의 흡착 및 탈착 성능은 NH3-TPD와 TSA 및 PSA 공정에서 AC-Mg(Cl) > AC-Cu(Cl) > AC-Mg(N) > AC-Cu(N) > AC 순으로 나타났다. 그 중 MgCl2를 사용한 AC-Mg(Cl)은 TSA에서 평균 흡착량 2.138 mmol g-1을 나타내었다. 또한 PSA 0.9 Mpa에서 3.848 mmol g-1로 가장 높은 초기 흡착량을 나타내었다. 활성탄 표면에 금속이 첨착되면 물리흡착뿐만 아니라 화학흡착이 수반되어 흡착 및 탈착 성능이 증가하는 것을 확인하였다. 또한 흡착제는 반복적인 공정에도 안정적인 흡착 및 탈착 성능을 나타내어 TSA와 PSA 공정에서의 적용 가능성을 확인하였다.

안동시 저수지에서의 대량 어류 폐사에 대한 원인과 대책에 관한 연구 (Study on Causes and Countermeasures for the Mass Death of Fish in Reservoirs in Andong-si)

  • 배수호;황선진;김연정;정철호;김성윤;유건상
    • 한국환경농학회지
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    • 제42권1호
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    • pp.52-62
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    • 2023
  • This study focused on determining the specific causes and prevention methods of mass fish deaths occurred in five reservoirs (Gagugi, Neupgokgi, Danggokgi, Sagokji, and Hangokji) in Andong-si. For this purpose, a survey of agricultural land and livestock in the upper part of the reservoirs and analysis of water quality in the reservoir irrespective of whether it rains or not were conducted. We attempted to examine the changes in dissolved oxygen (DO) in the surface and bottom layers of reservoirs and changes in DO depending on the amount of livestock compost and time. Based on the above investigations, treatment plans were established to efficiently control the inflow of contaminated water into reservoirs. The rainfall and farmland areas in the upper part of the reservoir were investigated using Google and aviation data provided by the Ministry of Land, Infrastructure, and Transport. The current status of livestock farms distributed around the reservoirs was also examined because compost from these farms can flow into the reservoir when it rains. Various water quality parameters, such as phosphate phosphorus (PO4-P) and ammonium nitrogen (NH3-N), were analyzed and compared for each reservoir during the rainy season. Changes in the DO concentration and electrical conductivity (EC) were also observed at the inlet of the reservoir during raining using an automated instrument. In addition, DO was measured until the concentration reached 0 ppm in 10 min by adding livestock compost at various concentrations (0.05%, 0.1%, 0.3%, and 0.5% by wt.), where the concentration of the livestock compost represents the relative weight of rainwater. The DO concentration in the surface layer of reservoirs was 3.7 to 5.3 ppm, which is sufficient for fish survival. However, the fish could not survive at the bottom layer with DO concentration of 0.0-2.1 ppm. When the livestock compost was 0.3%, DO required 10-19 h to reach 0 ppm. Considering these results, it was confirmed that the DO in the bottom layer of the reservoir could easily change to an anaerobic state within 24 h when the livestock compost in the rainwater exceeds 0.3%. The results show that the direct cause of fish mortality is the inflow of excessive livestock compost into reservoirs during the first rainfall in spring. All the surveyed reservoirs had relatively good topographical features for the inflow of compost generated from livestock farms. This keeps the bottom layer of the reservoir free of oxygen. Therefore, to prevent fish death due to insufficient DO in the reservoir, measures should be undertaken to limit the amount of livestock compost flowing into the reservoir within 0.3%, which has been experimentally determined. As a basic countermeasure, minerals such as limestone, dolomite, and magnesia containing calcium and magnesium should be added to the compost of livestock farms around the reservoir. These minerals have excellent pollutant removal capabilities when sprayed onto the compost. In addition, measures should be taken to prevent fish death according to the characteristics of each reservoir.

단위유량도와 비수갑문 단면 및 방조제 축조곡선 결정을 위한 조속계산 (Calculation of Unit Hydrograph from Discharge Curve, Determination of Sluice Dimension and Tidal Computation for Determination of the Closure curve)

  • 최귀열
    • 한국농공학회지
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    • 제7권1호
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    • pp.861-876
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    • 1965
  • During my stay in the Netherlands, I have studied the following, primarily in relation to the Mokpo Yong-san project which had been studied by the NEDECO for a feasibility report. 1. Unit hydrograph at Naju There are many ways to make unit hydrograph, but I want explain here to make unit hydrograph from the- actual run of curve at Naju. A discharge curve made from one rain storm depends on rainfall intensity per houre After finriing hydrograph every two hours, we will get two-hour unit hydrograph to devide each ordinate of the two-hour hydrograph by the rainfall intensity. I have used one storm from June 24 to June 26, 1963, recording a rainfall intensity of average 9. 4 mm per hour for 12 hours. If several rain gage stations had already been established in the catchment area. above Naju prior to this storm, I could have gathered accurate data on rainfall intensity throughout the catchment area. As it was, I used I the automatic rain gage record of the Mokpo I moteorological station to determine the rainfall lntensity. In order. to develop the unit ~Ydrograph at Naju, I subtracted the basic flow from the total runoff flow. I also tried to keed the difference between the calculated discharge amount and the measured discharge less than 1O~ The discharge period. of an unit graph depends on the length of the catchment area. 2. Determination of sluice dimension Acoording to principles of design presently used in our country, a one-day storm with a frequency of 20 years must be discharged in 8 hours. These design criteria are not adequate, and several dams have washed out in the past years. The design of the spillway and sluice dimensions must be based on the maximun peak discharge flowing into the reservoir to avoid crop and structure damages. The total flow into the reservoir is the summation of flow described by the Mokpo hydrograph, the basic flow from all the catchment areas and the rainfall on the reservoir area. To calculate the amount of water discharged through the sluiceCper half hour), the average head during that interval must be known. This can be calculated from the known water level outside the sluiceCdetermined by the tide) and from an estimated water level inside the reservoir at the end of each time interval. The total amount of water discharged through the sluice can be calculated from this average head, the time interval and the cross-sectional area of' the sluice. From the inflow into the .reservoir and the outflow through the sluice gates I calculated the change in the volume of water stored in the reservoir at half-hour intervals. From the stored volume of water and the known storage capacity of the reservoir, I was able to calculate the water level in the reservoir. The Calculated water level in the reservoir must be the same as the estimated water level. Mean stand tide will be adequate to use for determining the sluice dimension because spring tide is worse case and neap tide is best condition for the I result of the calculatio 3. Tidal computation for determination of the closure curve. During the construction of a dam, whether by building up of a succession of horizontael layers or by building in from both sides, the velocity of the water flowinii through the closing gapwill increase, because of the gradual decrease in the cross sectional area of the gap. 1 calculated the . velocities in the closing gap during flood and ebb for the first mentioned method of construction until the cross-sectional area has been reduced to about 25% of the original area, the change in tidal movement within the reservoir being negligible. Up to that point, the increase of the velocity is more or less hyperbolic. During the closing of the last 25 % of the gap, less water can flow out of the reservoir. This causes a rise of the mean water level of the reservoir. The difference in hydraulic head is then no longer negligible and must be taken into account. When, during the course of construction. the submerged weir become a free weir the critical flow occurs. The critical flow is that point, during either ebb or flood, at which the velocity reaches a maximum. When the dam is raised further. the velocity decreases because of the decrease\ulcorner in the height of the water above the weir. The calculation of the currents and velocities for a stage in the closure of the final gap is done in the following manner; Using an average tide with a neglible daily quantity, I estimated the water level on the pustream side of. the dam (inner water level). I determined the current through the gap for each hour by multiplying the storage area by the increment of the rise in water level. The velocity at a given moment can be determined from the calcalated current in m3/sec, and the cross-sectional area at that moment. At the same time from the difference between inner water level and tidal level (outer water level) the velocity can be calculated with the formula $h= \frac{V^2}{2g}$ and must be equal to the velocity detertnined from the current. If there is a difference in velocity, a new estimate of the inner water level must be made and entire procedure should be repeated. When the higher water level is equal to or more than 2/3 times the difference between the lower water level and the crest of the dam, we speak of a "free weir." The flow over the weir is then dependent upon the higher water level and not on the difference between high and low water levels. When the weir is "submerged", that is, the higher water level is less than 2/3 times the difference between the lower water and the crest of the dam, the difference between the high and low levels being decisive. The free weir normally occurs first during ebb, and is due to. the fact that mean level in the estuary is higher than the mean level of . the tide in building dams with barges the maximum velocity in the closing gap may not be more than 3m/sec. As the maximum velocities are higher than this limit we must use other construction methods in closing the gap. This can be done by dump-cars from each side or by using a cable way.e or by using a cable way.

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