• 제목/요약/키워드: Event streams

검색결과 66건 처리시간 0.026초

AvSWAT를 이용한 농촌유역 비점원 오염물질 부하량 예측 (Estimation of Nonpoint Source Pollutant Loads for Rural Watershed by AvSWAT)

  • 김진호;이종식;김원일;정구복;한국헌;류종수;김석철;윤순강;이정택;권순국
    • 한국토양비료학회지
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    • 제40권1호
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    • pp.12-17
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    • 2007
  • 유역관리모형은 유역내 비점원 오염부하를 예측하고, 서로 다른 오염원과 토지이용형태에 따른 영향을 판단하는데 사용 되어진다. 많은 모형들이 비점원오염의 예측이 가능하지만, 각기 서로 다른 한계를 갖고 있다. 모델의 선택의 연구목적과 축적된 가용자료에 부합해야 한다. 최근 한국에서는 SWAT모형이 농촌유역의 비점원오염 유출을 예측하기 위해서, 많이 이용되고 있다. 대부분의 자료들이 GIS를 이용하여 자동적으로 생성되지만, 일부 자료들은 농민들과 연구자들을 통해 직접 수집해야 한다. AvSWAT모형에 의해 시뮬레이션된 유량과 관측유출은 매우 좋은 결과를 나타내었다. 그러나 유출은 경향은 주로 강우와 물부족기간에 의해 그 경향을 따라간다. AvSWAT 모형을 농촌유역에 적용하여 유출을 평가한 결과 모델치는 1023.3 mm이고, 관측치는 967.4 mm인 것으로 나타났다. 또한 수질의 경우 모델치와 관측치의 결정계수는 인이 질소보다 더 높은 값(0.79)을 보여주고 있었다.

한국주요빙계의 소유역에 대한 순간단위권 유도에 관한 연구 (I) (Studies on the Derivation of the Instantaneous Unit Hydrograph for Small Watersheds of Main River Systems in Korea)

  • 이순혁
    • 한국농공학회지
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    • 제19권1호
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    • pp.4296-4311
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    • 1977
  • This study was conducted to derive an Instantaneous Unit Hydrograph for the accurate and reliable unitgraph which can be used to the estimation and control of flood for the development of agricultural water resources and rational design of hydraulic structures. Eight small watersheds were selected as studying basins from Han, Geum, Nakdong, Yeongsan and Inchon River systems which may be considered as a main river systems in Korea. The area of small watersheds are within the range of 85 to 470$\textrm{km}^2$. It is to derive an accurate Instantaneous Unit Hydrograph under the condition of having a short duration of heavy rain and uniform rainfall intensity with the basic and reliable data of rainfall records, pluviographs, records of river stages and of the main river systems mentioned above. Investigation was carried out for the relations between measurable unitgraph and watershed characteristics such as watershed area, A, river length L, and centroid distance of the watershed area, Lca. Especially, this study laid emphasis on the derivation and application of Instantaneous Unit Hydrograph (IUH) by applying Nash's conceptual model and by using an electronic computer. I U H by Nash's conceptual model and I U H by flood routing which can be applied to the ungaged small watersheds were derived and compared with each other to the observed unitgraph. 1 U H for each small watersheds can be solved by using an electronic computer. The results summarized for these studies are as follows; 1. Distribution of uniform rainfall intensity appears in the analysis for the temporal rainfall pattern of selected heavy rainfall event. 2. Mean value of recession constants, Kl, is 0.931 in all watersheds observed. 3. Time to peak discharge, Tp, occurs at the position of 0.02 Tb, base length of hlrdrograph with an indication of lower value than that in larger watersheds. 4. Peak discharge, Qp, in relation to the watershed area, A, and effective rainfall, R, is found to be {{{{ { Q}_{ p} = { 0.895} over { { A}^{0.145 } } }}}} AR having high significance of correlation coefficient, 0.927, between peak discharge, Qp, and effective rainfall, R. Design chart for the peak discharge (refer to Fig. 15) with watershed area and effective rainfall was established by the author. 5. The mean slopes of main streams within the range of 1.46 meters per kilometer to 13.6 meter per kilometer. These indicate higher slopes in the small watersheds than those in larger watersheds. Lengths of main streams are within the range of 9.4 kilometer to 41.75 kilometer, which can be regarded as a short distance. It is remarkable thing that the time of flood concentration was more rapid in the small watersheds than that in the other larger watersheds. 6. Length of main stream, L, in relation to the watershed area, A, is found to be L=2.044A0.48 having a high significance of correlation coefficient, 0.968. 7. Watershed lag, Lg, in hrs in relation to the watershed area, A, and length of main stream, L, was derived as Lg=3.228 A0.904 L-1.293 with a high significance. On the other hand, It was found that watershed lag, Lg, could also be expressed as {{{{Lg=0.247 { ( { LLca} over { SQRT { S} } )}^{ 0.604} }}}} in connection with the product of main stream length and the centroid length of the basin of the watershed area, LLca which could be expressed as a measure of the shape and the size of the watershed with the slopes except watershed area, A. But the latter showed a lower correlation than that of the former in the significance test. Therefore, it can be concluded that watershed lag, Lg, is more closely related with the such watersheds characteristics as watershed area and length of main stream in the small watersheds. Empirical formula for the peak discharge per unit area, qp, ㎥/sec/$\textrm{km}^2$, was derived as qp=10-0.389-0.0424Lg with a high significance, r=0.91. This indicates that the peak discharge per unit area of the unitgraph is in inverse proportion to the watershed lag time. 8. The base length of the unitgraph, Tb, in connection with the watershed lag, Lg, was extra.essed as {{{{ { T}_{ b} =1.14+0.564( { Lg} over {24 } )}}}} which has defined with a high significance. 9. For the derivation of IUH by applying linear conceptual model, the storage constant, K, with the length of main stream, L, and slopes, S, was adopted as {{{{K=0.1197( {L } over { SQRT {S } } )}}}} with a highly significant correlation coefficient, 0.90. Gamma function argument, N, derived with such watershed characteristics as watershed area, A, river length, L, centroid distance of the basin of the watershed area, Lca, and slopes, S, was found to be N=49.2 A1.481L-2.202 Lca-1.297 S-0.112 with a high significance having the F value, 4.83, through analysis of variance. 10. According to the linear conceptual model, Formular established in relation to the time distribution, Peak discharge and time to peak discharge for instantaneous Unit Hydrograph when unit effective rainfall of unitgraph and dimension of watershed area are applied as 10mm, and $\textrm{km}^2$ respectively are as follows; Time distribution of IUH {{{{u(0, t)= { 2.78A} over {K GAMMA (N) } { e}^{-t/k } { (t.K)}^{N-1 } }}}} (㎥/sec) Peak discharge of IUH {{{{ {u(0, t) }_{max } = { 2.78A} over {K GAMMA (N) } { e}^{-(N-1) } { (N-1)}^{N-1 } }}}} (㎥/sec) Time to peak discharge of IUH tp=(N-1)K (hrs) 11. Through mathematical analysis in the recession curve of Hydrograph, It was confirmed that empirical formula of Gamma function argument, N, had connection with recession constant, Kl, peak discharge, QP, and time to peak discharge, tp, as {{{{{ K'} over { { t}_{ p} } = { 1} over {N-1 } - { ln { t} over { { t}_{p } } } over {ln { Q} over { { Q}_{p } } } }}}} where {{{{K'= { 1} over { { lnK}_{1 } } }}}} 12. Linking the two, empirical formulars for storage constant, K, and Gamma function argument, N, into closer relations with each other, derivation of unit hydrograph for the ungaged small watersheds can be established by having formulars for the time distribution and peak discharge of IUH as follows. Time distribution of IUH u(0, t)=23.2 A L-1S1/2 F(N, K, t) (㎥/sec) where {{{{F(N, K, t)= { { e}^{-t/k } { (t/K)}^{N-1 } } over { GAMMA (N) } }}}} Peak discharge of IUH) u(0, t)max=23.2 A L-1S1/2 F(N) (㎥/sec) where {{{{F(N)= { { e}^{-(N-1) } { (N-1)}^{N-1 } } over { GAMMA (N) } }}}} 13. The base length of the Time-Area Diagram for the IUH was given by {{{{C=0.778 { ( { LLca} over { SQRT { S} } )}^{0.423 } }}}} with correlation coefficient, 0.85, which has an indication of the relations to the length of main stream, L, centroid distance of the basin of the watershed area, Lca, and slopes, S. 14. Relative errors in the peak discharge of the IUH by using linear conceptual model and IUH by routing showed to be 2.5 and 16.9 percent respectively to the peak of observed unitgraph. Therefore, it confirmed that the accuracy of IUH using linear conceptual model was approaching more closely to the observed unitgraph than that of the flood routing in the small watersheds.

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복합미생물 생물증강법을 이용한 인공해수하천의 친환경 효율적 현장 수질정화 (Eco-friendly and efficient in situ restoration of the constructed sea stream by bioaugmentation of a microbial consortium)

  • 유장연;김인수;김수현;칼루 엑페게어;장재수;박영인;고성철
    • 미생물학회지
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    • 제53권2호
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    • pp.83-96
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    • 2017
  • 부산시 영도구의 혁신지구의 인공해수천은 높아진 하상과 조류의 특성으로 인해 물이 순환되지 않고 더구나 주위의 오수가 유입되고 있어서 수질이 나빠지고 악취를 발생하고 있다. 이 문제를 해결하기 위한 방안으로 가장 오염되고 조류이동을 감안한 하천의 지점에 생물증강법을 적용하여 친환경적, 효율적으로 하천을 정화하고자 하였다. 현장에서 활성화된 복합미생물을 가장 오염된 지점(Site 2)에 7~10일 간격으로 투입하여, 수질의 pH, 온도, DO, ORP, SS, COD, T-N, 및 T-P를 측정하였고 또한 하상퇴적토의 COD 및 미생물군집을 분석하였다. 13개월 후 Site 2의 수질 SS, COD, T-N 및 COD (퇴적토)의 처리효율은 각각 51%, 58%, 27% 및 35%으로 나타났으나 T-P는 오히려 47% 증가를 보였다. 대부분의 측정지점에서 황산염환원세균(sulfate reducing bacteria)그룹 (Desulfobacteraceae_uc_s, Desulfobacterales_uc_s, Desulfuromonadaceae_uc_s, Desulfuromonas_g1_uc and Desulfobacter postgatei)과 Anaerolinaeles의 밀도는 대체적으로 생물증강에 의한 정화가 진행될수록 감소하였으며, 반면에 Gamma-proteobacteria (NOR5-6B_s and NOR5-6A_s), Bacteroidales_uc_s, 및 Flavobacteriales_uc_s의 밀도는 증가하는 경향이었다. 상대적으로 COD가 낮고 DO가 높은 청정지점인 St. 4에서는 호기성미생물인 Flavobacteriaceae_uc_s가 우점하였다. 이러한 미생물군은 하천의 정화과정을 추적할 수 있는 지표미생물로 활용될 수 있을 것으로 판단되었다. 생물증강 시행 후의 대표적 시점 퇴적토시료의 미생물군집 alpha diversity 지수(OTUs, Chao1 및 Shannon 지수)는 시행 전에 비해 감소하는 경향을 보였으며, 또한 beta diversity 분석기법(fast unifrac 분석)으로 분석한 결과 정화 전이나 초기에 비해서 정화가 진행될수록 전반적으로 시료에 무관하게 미생물군집의 유사성을 보여 생물증강이 현장 토착 미생물의 군집구조를 변화시키고 있음을 확인하였다. 이러한 사실로 보아 본 복합미생물에 의한 현장 생물증강법은 brine water 및 담수로 이루어진 오염된 하천을 환경친화적, 경제적으로 정화할 수 있는 대안으로 판단이 되었다.

Earthquake impacts on hydrology: a case study from the Canterbury, New Zealand earthquakes of 2010 and 2011

  • Davie, Tim;Smith, Jeff;Scott, David;Ezzy, Tim;Cox, Simon;Rutter, Helen
    • 한국수자원학회:학술대회논문집
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    • 한국수자원학회 2011년도 학술발표회
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    • pp.8-9
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    • 2011
  • On 4 September 2010 an earthquake of magnitude 7.1 on the Richter scale occurred on the Canterbury Plains in the South Island of New Zealand. The Canterbury Plains are an area of extensive groundwater and spring fed surface water systems. Since the September earthquake there have been several thousand aftershocks (Fig. 1), the largest being a 6.3 magnitude quake which occurred close to the centre of Christchurch on 22February 2011. This second quake caused extensive damage to the city of Christchurch including the deaths of 189 people. Both of these quakes had marked hydrological impacts. Water is a vital natural resource for Canterburywith groundwater being extracted for potable supply and both ground and surface water being used extensively for agricultural and horticultural irrigation.The groundwater is of very high quality so that the city of Christchurch (population approx. 400,000) supplies untreated artesian water to the majority of households and businesses. Both earthquakes caused immediate hydrological effects, the most dramatic of which was the liquefaction of sediments and the release of shallow groundwater containing a fine grey silt-sand material. The liquefaction that occurred fitted within the empirical relationship between distance from epicentre and magnitude of quake described by Montgomery et al. (2003). . It appears that liquefaction resulted in development of discontinuities in confining layers. In some cases these appear to have been maintained by artesian pressure and continuing flow, and the springs are continuing to flow even now. In spring-fed streams there was an increase in flow that lasted for several days and in some cases flows remained high for several months afterwards although this could be linked to a very wet winter prior to the September earthquake. Analysis of the slope of baseflow recession for a spring-fed stream before and after the September earthquake shows no change, indicating no substantial change in the aquifer structure that feeds this stream.A complicating factor for consideration of river flows was that in some places the liquefaction of shallow sediments led to lateral spreading of river banks. The lateral spread lessened the channel cross section so water levels rose although the flow might not have risen accordingly. Groundwater level peaks moved both up and down, depending on the location of wells. Groundwater level changes for the two earthquakes were strongly related to the proximity to the epicentre. The February 2011 earthquake resulted in significantly larger groundwater level changes in eastern Christchurch than occurred in September 2010. In a well of similar distance from both epicentres the two events resulted in a similar sized increase in water level but the slightly slower rate of increase and the markedly slower recession recorded in the February event suggests that the well may have been partially blocked by sediment flowing into the well at depth. The effects of the February earthquake were more localised and in the area to the west of Christchurch it was the earlier earthquake that had greater impact. Many of the recorded responses have been compromised, or complicated, by damage or clogging and further inspections will need to be carried out to allow a more definitive interpretation. Nevertheless, it is reasonable to provisionally conclude that there is no clear evidence of significant change in aquifer pressures or properties. The different response of groundwater to earthquakes across the Canterbury Plains is the subject of a new research project about to start that uses the information to improve groundwater characterisation for the region. Montgomery D.R., Greenberg H.M., Smith D.T. (2003) Stream flow response to the Nisqually earthquake. Earth & Planetary Science Letters 209 19-28.

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남한강 보 구간 유수성 저서성 대형무척추동물의 시·공간적 분포 특성 (Spatio-temporal Distribution Patterns of Lotic Benthic Macroinvertebrate Communities in Namhan-River Weir Section)

  • 김진영;이승현;이경락;노성유;신유나;이수웅;이재관;원두희;임성호;권용주;공동수
    • 생태와환경
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    • 제51권4호
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    • pp.331-344
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    • 2018
  • 한강수계 남한강의 보(강천보, 여주보, 이포보) 공사 후 수변부 여울 구간의 물리적 환경의 변화에 따른 유수성 저서동물의 군집 변화를 확인한 결과 다음과 같은 결론을 얻었다. 첫째, 보에 의한 여울구간의 소실은 유속, 하상 등 물리적 환경의 변화를 야기하여 수질요인과는 독립적으로 수생태계에 영향을 미칠 수 있다. 둘째, 남한강 보 구간의 수변부 물리적 서식환경의 복합적인 변화는 유수성 분류군의 군집구성에 영향을 미친 것으로 판단된다. 셋째, 저서성 대형무척추동물 유수성 지표 후보종 157 분류군은 수생태계 변화의 원인 분석을 비롯한 하천 수생태계 복원 및 재자연화 등에 유용한 지표로 활용될 수 있을 것으로 기대된다. 넷째, 향후 유속변화에 대한 수생태계 영향을 면밀하게 파악하기 위해서는 분류군별 유속에 대한 저항성 또는 선호도를 바탕으로 한 지표연구가 필요할 것으로 사료된다.

전국 하천수 중 잔류우려 농약 실태조사 (Monitoring of Pesticide Residues Concerned in Stream Water)

  • 황인성;오예진;권혜영;노진호;김단비;문병철;오민석;노현호;박상원;최근형;류송희;김병석;오경석;임치환;이효섭
    • 한국환경농학회지
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    • 제38권3호
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    • pp.173-184
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    • 2019
  • 우리나라 주요 하천수의 사용 중인 농약의 실태조사를 위해서 전국 50지점을 선정 후, 1차 (농약 사용 비성수기, 4/5월)및 2차(농약 사용 성수기, 8/9월)로 나누어 실시를 하였다. 하천수 모니터링 결과 농약 1차, 2차 때 각각 11, 28개의 농약이 검출되었다. 농약은 7월부터 기온이 올라가면서 병 해충 방제를 위해 농약사용량이 증가하기 때문에 2차시기에 농약검출량이 증가한 것으로 판단된다. 검출빈도 10회 이상의 농약은 1차 시기에는 butachlor, carbofuran, 2차 시기에는 tricyclazole, azoxystrobin, chlorantraniliprole, thiamethoxam, isoprothiolane 5종이었다. 검출농약은 대부분 수도용 농약으로 검출비율은 90%, 81%로 높게 나타났다. 이러한 이유는 하천수 중 잔류농약은 논에서 사용된 농약이 비산되어 직접적으로 하천수로 잔류되기도 하며 또는 토양에 잔류된 농약이 논물을 방류하면서 하천수로 이동하기 때문이다. 네 개의 scenario를 이용하여 위해성 평가를 진행하였을 때, butachlor, carbofuran, carbendazim, chlorantranilprole 및 oxadiazon에서 잠재위해성 및 위해성이 있는 것으로 평가되었다. 추후 모니터링 연구와 수서생물에 위해성이 나타나지 않는 농도 이하로 잔류할 수 있도록 농약안전사용기준 설정연구가 필요할 것으로 보인다.